Număr | 192 |
---|---|
An | 2016 |
Data emiterii | 15.11.2016 |
Link oficial | Primăria Timisoara |
Proces verbal | PV din 15.11.2016 |
Hotararea Consiliului Local 192/15.11.2016 privind aprobarea încheierii unui Acord de parteneriat între Municipiul Timişoara şi Asociaţia pentru Promovarea Valorilor Naturale şi Culturale ale Banatului şi Crişanei "Excelsior" Consiliul Local al Municipiului Timisoara Având în vedere Referatul nr.SC2016-27034/04.11.2016 al Primarului Municipiului Timişoara - Domnul Nicolae ROBU; Având în vedere avizele Comisiei pentru studii, prognoze, economie, buget, finanţe, impozite şi taxe, Comisiei pentru dezvoltare urbanistică, amenajarea teritoriului şi patrimoniu, Comisiei pentru administrarea domeniului public şi privat, servicii publice şi comerţ, regii autonome şi societăţi comerciale, Comisiei pentru cultură, ştiinţă, învăţământ, sănătate, protecţie socială, turism, ecologie, sport şi culte din cadrul Consiliului Local al Municipiului Timişoara; Având în vedere Adresa Asociaţiei pentru Promovarea Valorilor Naturale şi Culturale ale Banatului şi Crişanei "Excelsior", înregistrată la Primăria Municipiului Timisoara cu numărul CDM2016-568/20.09.2016, prin care propune încheierea unui Acord de parteneriat cu Municipiul Timişoara; Având în vedere Strategia pentru Infrastructura ecologică COM/2013/249 "Comunicarea Comisiei către Parlamentul European, Consiliu, Comitetul Economic şi Social European şi Comitetul Regiunilor - Infrastructurile ecologice Valorificarea capitalului natural al Europei" din anul 2013; În conformitate cu prevederile art.36 alin.2 lit.(e) şi alin.7, lit.a) din Legea nr.215/2001 privind administraţia publică locală, cu modificările şi completările ulterioare; În temeiul art.45 alin.2, lit.f), din Legea nr.215/2001 privind administraţia publică locală, cu modificările şi completările ulterioare; HOTARASTE Art.1: Se aprobă încheierea unui Acord de parteneriat între Municipiul Timişoara şi Asociaţia pentru Promovarea Valorilor Naturale şi Culturale ale Banatului şi Crişanei "Excelsior", de colaborare şi dezvoltare în comun a unor acţiuni şi activităţi pentru studiul şi dezvoltarea reţelei pentru infrastructură ecologică, verde (Green Infrastructure - GI) în Municipiul Timişoara. Art.2: Se împuterniceşte Domnul Nicolae ROBU - Primarul Municipiului Timişoara, să semneze Acordul de parteneriat cu Asociaţia pentru Promovarea Valorilor Naturale şi Culturale ale Banatului şi Crişanei "Excelsior", prevăzut în Anexa 1 care face parte integrantă din prezenta hotărâre. Art.3: Cu aducere la îndeplinire a prezentei hotărâri se încredinţează Direcţia de Mediu din cadrul Primăriei Municipiului Timişoara. Art.4: Prezenta hotărâre se comunică: Instituţiei Prefectului Judeţului Timiş; Primarului Municipiului Timişoara; Serviciului Juridic; Direcţiei Economice; Direcţiei Tehnice; Direcţiei Urbanism; Direcţiei Clădiri, Terenuri şi Dotări Diverse; Direcţiei Dezvoltare; Direcţiei Comunicare; Direcţiei de Mediu; Corpului de Control şi Antifraudă al Primarului; Biroului Managementul Calităţii; Biroului Audit; Asociaţiei pentru Promovarea Valorilor Naturale şi Culturale ale Banatului şi Crişanei "Excelsior"; Mass- media locale.
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Supporting the Implementation of
Green Infrastructure Final Report
Supporting the Implementation of Green Infrastructure
May 2016 2
Contract details:
European Commission, Directorate-General for the Environment
ENV.B.2/SER/2014/0012
Service Contract for “Supporting the Implementation of Green Infrastructure”
Presented by:
In association with:
Contact:
Trinomics B.V.
Westersingel 32A
3014 GS, Rotterdam
The Netherlands
T: +31 10 341 45 92
Date:
Rotterdam, 31 May 2016
Disclaimer:
The views expressed in this report are purely those of the writer and may not in any
circumstances be regarded as stating an official position of the European Commission.
Supporting the Implementation of Green Infrastructure
May 2016 3
Table of Contents
Table of Contents .............................................................................................. 3 Executive summary ........................................................................................... 6
Task 1: Ensuring a more effective promotion of GI at all levels .......................... 6 Task 2: Capacity building, training, education for GI ......................................... 6 Task 3: Improving information exchange mechanisms for GI ............................. 6 Task 4: Assessing technical standards and innovation possibilities...................... 7 Task 5: Exploratory work on a TEN-G ............................................................. 7
Introduction .....................................................................................................11 Context ........................................................................................................11 Approach and objectives .................................................................................12
Task 1: Ensuring a more effective promotion of GI at all relevant levels .............12 Task 2: Capacity building, training, education for GI ........................................13 Task 3: Improving information exchange mechanisms .....................................14 Task 4: Assessing technical standards and innovation possibilities.....................15 Task 5: Assessing costs and benefits of establishing a TEN-G ...........................16
1 Task 1 – Ensuring a more cost-effective promotion of GI at all levels ...................18 Chapter summary ..........................................................................................18 Introduction ..................................................................................................19 1.1 GI promotion in Member States .................................................................19
1.1.1 Development of country fact sheets ......................................................19 1.1.2 Insights and lessons learnt from developing the country factsheets ...........20
1.2 Communication of costs and benefits of GI to sector groupings ......................20 1.2.1 Production of 6 sector factsheets and 4 topic factsheets ..........................21 1.2.2 Sector workshops ...............................................................................21 1.2.3 IEREK – Urban planning and architecture design for sustainable development
................................................................................................................22 1.2.4 Arad Workshop – GI implementation in Romania ....................................23 1.2.5 Helsinki Sector Workshop - CBD Business Forum ....................................26
1.3 Supporting key actions of GIIR WG .............................................................28 2 Task 2 – Capacity building, training, education for GI .........................................29
Chapter summary ..........................................................................................29 Introduction ..................................................................................................30 2.1 EU-28 Quick Scan of existing training and information initiatives ....................30 2.2 Development of a Massive Open Online Course (MOOC) on GI .......................31 2.3 “Train the trainers” workshops ...................................................................32
2.3.1 Training on GI & Wetland Restoration in Budapest, Hungary ....................32 2.3.2 Training at the event ‘Implementation of the Strategy for Green
Infrastructure in Romania: Nature – our health our wealth’ ..............................33 3 Task 3 – Improving information exchange mechanisms ......................................37
Chapter summary ..........................................................................................37 Introduction ..................................................................................................41 3.1 Problem analysis and objectives of Task 3 ...................................................43 3.2 The digital GI information landscape ...........................................................45
3.2.1 Policy sectors .....................................................................................45 3.2.2 Stakeholders ......................................................................................55 3.2.3 National and international platforms on GI .............................................62
3.3 Increasing GI visibility for selected platforms ...............................................63 3.3.1 BISE .................................................................................................64 3.3.2 NWRM/WISE ......................................................................................70 3.3.3 Climate-ADAPT ...................................................................................74
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3.3.4 Sustainable cities platform ...................................................................79 3.3.5 International Council of Landscape Architecture Schools ..........................80 3.3.6 World Green Building Council ...............................................................81 3.3.7 Green Roof Association ........................................................................81 3.3.8 European Council of Spatial Planners .....................................................82
3.4 Technical and governance aspects of BISE, NWRM and Climate-ADAPT ...........83 3.4.1 BISE .................................................................................................83 3.4.2 NWRM ...............................................................................................87 3.4.3 Climate-ADAPT ...................................................................................91
3.5 Recommendations ....................................................................................93 3.5.1 BISE to become a GI information hub....................................................93 3.5.2 GI as a common vocabulary across platforms .........................................94 3.5.3 Have GI relevant information made available to the end-users of the various
platforms ...................................................................................................95 3.5.4 Stronger connect across platforms ........................................................96 3.5.5 Long-term: machine to machine communication .....................................97
3.6 Further steps for BISE, NWRM and Climate-ADAPT .......................................99 3.6.1 BISE ............................................................................................... 100 3.6.2 NWRM ............................................................................................. 100 3.6.3 Climate-ADAPT ................................................................................. 101
4 Task 4 - Assessing technical standards and innovation possibilities .................... 102 Chapter summary ........................................................................................ 102 Introduction ................................................................................................ 105 4.1 Problem analysis and objectives of Task 4 ................................................. 106 4.2 Setting .................................................................................................. 107
4.2.1 Advantages and disadvantages of working with standards ..................... 107 4.2.2 Broader context: sustainability ........................................................... 107
4.3 Methodology .......................................................................................... 108 4.4 Overview of standards for GI for different sectors ....................................... 111
4.4.1 GI standards and the financial sector .................................................. 111 4.4.2 GI standards and the building sector ................................................... 116 4.4.3 GI standards and the water sector ...................................................... 121 4.4.4 GI standards and the transport sector ................................................. 124 4.4.5 GI standards and the public health sector ............................................ 132 4.4.6 GI standards and the industry sector................................................... 135 4.4.7 GI standards and climate adaptation ................................................... 139 4.4.8 GI standards and rural abandonment .................................................. 143 4.4.9 GI standards and the energy sector .................................................... 145 4.4.10 General findings on integration of GI in standards ............................... 149
4.5 General recommendations ....................................................................... 150 4.5.1 Integrated spatial planning ................................................................ 150 4.5.2 Green procurement ........................................................................... 151 4.5.3 Finding the appropriate standard ........................................................ 151 4.5.4 Harmonization across infrastructure sectors ......................................... 152
5 Task 5 - Assessing costs and benefits of establishing a TEN-G ........................... 153 Chapter summary ........................................................................................ 153 Introduction ................................................................................................ 154
Key GI features suitable for capturing European added value ......................... 154 GI implementation progress by Member States ............................................. 157 The rationale for developing a TEN-G .......................................................... 160
5.1 Learning from the Trans-European Networks (TENs) ................................... 161 5.1.1 Learning from the Trans-European Network for Transport (TEN-T) .......... 162 5.1.2 Learning from the Trans-European Network for Energy (TEN-E) .............. 167 5.1.3 Conclusions regarding the future design of TEN-G ................................. 169
5.2 Developing the current TEN-G baseline ..................................................... 170
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5.2.1 The methodology to estimate and assess the baseline ........................... 170 5.2.2 Analysis of funds allocated to GI in the period 2007-2013 (analysis of the
Excel file) ................................................................................................. 171 5.2.3 Differences between the programming periods 2007-2013 and 2014-2020
.............................................................................................................. 175 5.2.4 The Baseline - Extrapolation of the results for 2007-2013 into the new
programming period 2014-2020 ................................................................. 178 5.2.5 Challenges and limitations of the baseline ............................................ 184
5.3 Assessment of the costs and benefits of establishing a TEN-G ...................... 185 5.3.1 Purpose and scope ............................................................................ 185 5.3.2 Methodological approach in a nutshell ................................................. 186 5.3.3 Results ............................................................................................ 190 5.3.4 Conclusions and discussion ................................................................ 193
5.4 Policy implications .................................................................................. 196 Conclusions ................................................................................................... 197
Task 1 ........................................................................................................ 197 Task 2 ........................................................................................................ 197 Task 3 ........................................................................................................ 198 Task 4 ........................................................................................................ 199 Task 5 ........................................................................................................ 202
Annexes ........................................................................................................ 203
Supporting the Implementation of Green Infrastructure
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Executive summary
The EU Green Infrastructure Strategy adopted in May 2013 foresees a number of
actions to be carried out under the lead of the European Commission in the following
years. They include, for example, integrating green infrastructure (GI) into key policy
areas, improving the knowledge base and encouraging innovation in relation to GI,
and assessing opportunities for developing a trans-European GI network (TEN-G).
The service contract reported on in this Final Report aimed at supporting the
implementation of these actions, in particular actions which require new knowledge.
This report presents the outputs of the five distinct tasks conducted during this service
contract, namely:
Task 1: Ensuring a more effective promotion of GI at all relevant levels;
Task 2: Capacity building, training, education for GI;
Task 3: Improving information exchange mechanisms;
Task 4: Assessing technical standards and innovation possibilities;
Task 5: Assessing costs and benefits of TEN-G.
Task 1: Ensuring a more effective promotion of GI at all levels
The first task (summarised in Chapter 1 of this Final Report) aimed to raise awareness
of GI among the general public, Member States and a range of relevant sectors
through the development and dissemination of GI information material. The project
team produced factsheets regarding the implementation and potential of GI in ten
selected Member States, as well as six factsheets presenting the costs and benefits of
GI to specific sectors (i.e. finance, industry, transport, energy, public health, and
water). In addition, four thematic factsheets were produced, portraying GI in relation
to the construction of buildings, abandonment of rural areas, job creation, and climate
change adaptation. The project also contributed to the dissemination of GI knowledge
and awareness through three sectoral workshops. Finally, Task 1 included activities to
support meetings of the Green Infrastructure Implementation and Restoration Working
Group (GIIR WG).
Task 2: Capacity building, training, education for GI
Chapter 2 of this Final Report reports on the second task, which focused on capacity
building and training in relation to GI. It developed and implemented training modules
for two ‘train the trainers’ workshops, one on GI and wetland restoration and one on
better linking GI with existing operational programmes. The task also resulted in
material for a Massive Open Online Course (MOOC) on GI, aimed at disseminating GI
training material to a broader audience across Europe and beyond.
Task 3: Improving information exchange mechanisms for GI
Task 3 presented in Chapter 3 of this Final Report evaluated the current visibility of GI
information on the digital platforms of several EU policy sectors and stakeholders, and
considered means of improving the content of and access to digital information on GI.
In a first step, the task identified the platforms relevant for disseminating GI
information and considered how such information can be (better) integrated. For eight
selected platforms, the accessibility and type of GI information was evaluated. Three
platforms – Biodiversity Information System for Europe (BISE), Natural Water
Supporting the Implementation of Green Infrastructure
May 2016 7
Retention Measures (NWRM) and Climate-ADAPT – were further chosen for a more
detailed analysis of the accessibility and user-friendliness of the GI information they
contained. For these three platforms, the team assessed the technical and governance
requirements for implementing a series of recommendations and discussed the
feasibility of the recommendations with the officials responsible for their
implementation.
Task 4: Assessing technical standards and innovation possibilities
Task 4 presented in Chapter 4 of this Final Report examined how technical standards,
particularly in relation to physical building blocks and methodologies and procedures,
could increase the deployment of GI. The study covered nine sectors: finances,
buildings, water, transport, public health, industry, climate, rural abandonment and
energy. It explored the extent to which GI is currently covered in the standards of
these sectors and assessed the need for (further) harmonising, adapting or developing
GI-related standards. A series of sector-specific sheets were developed, including
concrete recommendations concerning the need for harmonisation between standards,
the potential for including or strengthening the concept and principles of GI in different
standard categories (performance, procedure, methodology), and the interoperability
between technical standards applied in different project phases (planning, design, and
construction). A number of cross-sectoral recommendations were also formulated.
Task 5: Exploratory work on a TEN-G
Finally, Task 5 presented in Chapter 5 of this Final Report included all exploratory
work related to the potential introduction of a Trans-European Network for Green
Infrastructure (TEN-G).
The overall objective of the EU’s GI related policy ambitions is to have an EU network
of green infrastructure in optimal condition to deliver essential ecosystem services
throughout Europe. However, in practice priorities will need to be identified. To
promote sustainability, recovery and maximum effectiveness, there should be an
interlocking, coherent and co-ordinated approach across the different spatial scales
(local, regional, national, EU) to the mapping and assessment of the ecosystem
condition and to the identification of priorities for GI intervention/investment.
At the level of the EU, a TEN-G would involve the promotion of strategic investments
in the EU network of Green Infrastructure motivated by:
1. the need to protect, restore and enhance the overall quality of the network and
to maintain certain minimum quality levels to ensure the continued delivery of
ecosystem services;
2. the need to protect, restore and enhance the delivery of priority ecosystem
services in identified geographic locations at a scale which transcends
administrative boundaries, taking into account in particular trans-boundary
impacts; and
3. social and/or cultural considerations that transcend administrative boundaries
(e.g. the Green Belt initiative following the line of the "iron curtain" or the
pilgrimage route to Santiago de Compostela).
To this end, Chapter 5 of this Final Report captures the analysis and results from the
TEN-G exploratory work that has been carried out under the service contract. Chapter
5.1 first summarises what we can learn from existing trans-European infrastructure
networks (energy and transport) in terms of the possible design options of a TEN-G.
As a second step (as presented in Chapter 5.2), the team developed a baseline
Supporting the Implementation of Green Infrastructure
May 2016 8
estimating the current EU funding levels for GI under the existing GI policy and
funding structures in order to compare and contrast the expected costs and benefits of
a TEN-G to a situation without it.
The key outputs for the GI baseline scenario can be summarised as follows:
During the 2014 – 2020 programming period, we estimate that green
infrastructure will likely receive EU finance amounting approximately
to €6,397 million by public EU funds through various funding mechanisms,
namely: LIFE+; the European Regional Development Fund (ERDF), the
European Social Fund (ESF) and the Cohesion Fund1; the European Agricultural
Fund for Rural Development (EAFRD); and the European Fisheries Fund (EFF)2.
This is an average of approximately €915 million per year.
Although in monetary terms the fund contributing most to GI by far appears to
be the agriculture fund EAFRD, less than 1% of its total budget (€418 billion)
was allocated to GI between 2014 and 2020. That accounted for €4,967
million (77% of the total EU-funded GI). In fact, proportionally speaking, LIFE
is the biggest contributor to GI implementation. For 2014-2020, funding from
LIFE would amount to €1,248 million (19% of the total EU-funded GI), which
means that 36% of the total LIFE budget is allocated to activities that can be
considered GI.
In terms of the distribution of funding across the various GI components,
current funding is primarily allocated to finance the conservation of green areas
(€5,010 million of all GI funding; 78% of all GI funding) and restoration of
green areas (€78 million of all GI funding; 12%). By contrast, connectivity
issues, sustainable use green zones and green urban and peri-urban areas are
underfunded in the baseline situation, as these building blocks receive only
approximately 1%, 4% and 4% of all EU funds allocated to GI projects
respectively. Investments in greening urban and peri-urban areas are mostly
spent on green roofs, city parks, urban forestation and the like. Connectivity
mostly funds fish passes and animal corridors while there is no indication of
financing having been provided to projects dealing with other connectivity-
related GI such as eco-ducts, green bridges, areas along energy and transport
networks.
Against this backdrop, TEN-G could focus on promoting projects that
enhance natural and artificial connectivity, as this is an underfunded
area under the current set-up and could also contribute to reducing
fragmentation.
Building on this baseline, the team implemented a first-phase assessment of costs
and benefits of a potential TEN-G versus continuing the current GI policy and
funding structures. It should be noted that the assessment carried out did not focus
on finding out the best design set-up option for a TEN-G, but rather provides initial
evidence on whether or not the costs of introducing and running a TEN-G would be
outweighed by the expected economic, social and environmental benefits delivered via
such a network. This means that the assessment first established knowledge on the
current status quo scenario, the GI baseline. As a next step, the cost-benefit
assessment focused on comparing the different proposed GI components in terms of
what can deliver the greatest level of benefit if promoted under a Trans-European
network structure. The results therefore can be used for informing policy discussions
and next steps with regards to developing a TEN-G framework, the most relevant
ambition level, component focus, etc.
1 These three funds present their project beneficiaries together, without specifying which amounts come from CF, ERDF and ESF. 2 For the period 2014-2020, the EFF is replaced by so-called European Marine and Fisheries Fund (EMFF)
Supporting the Implementation of Green Infrastructure
May 2016 9
Whilst the assessment process is high level and subject to a number of uncertainties,
the findings indicate that a TEN-G has the potential to provide greater benefits
per € invested than the current GI policy implementation and funding
allocation (as described under the baseline scenario). Considering only the top five
ranked components in the assessment, the benefit-cost ratio (BCR) for TEN-G is more
than double the BCR under the current funding allocation. If the goal is to maximise
the BCR (as opposed to focusing on particular environmental or social priorities), then
the top five priority components that could make up a TEN-G network are: Natura
2000 sites, Extensive agricultural landscapes, Regional and National parks, Multi-
functional sustainable managed agricultural landscapes, and Wilderness zones. The
ranking of priority components changes when the aim is to maximise the level of
environmental or social benefits delivered.
A TEN-G network based on the components that were ranked in the top ten at least
twice in this assessment (based on benefit-cost ratio, level of qualitative benefits,
based on social priorities or based on environmental priorities) alongside those that
could generate sufficient benefits to attract private funding would include3:
Natura 2000 sites
Regional and National parks
Multi-functional sustainably managed agricultural landscapes
Wilderness zones
High nature value farmland
Ecological networks with cross-border areas
Local nature reserve
Sustainable forest management
Multi-use forests (such as watershed forests)
Water protection areas
Restored landscape systems covering a substantial part of agricultural/forestry
areas
Allotments and orchards
Storm ponds and sustainable urban drainage
City reserves
Metropolitan park systems
Wildlife strips
3 The following components reached the Top10 list due to their suitability for private funding: Water protection areas; Restored landscape systems covering a substantial part of agricultural/forestry areas; Allotments and orchards; Storm ponds and sustainable urban drainage; City reserves; Metropolitan park systems; Wildlife strips. The following components could also be included in the Top10 list if only focusing on one of the prioritisations: Extensive agricultural landscapes; Functional riparian systems; Transboundary landscape features on river basin; Substantial share of structure-rich agricultural, forestry or natural landscapes; Supra-regional corridors; Sustainable coastal and marine management zones related to the respective sea basin; Restored areas which were before fragmented or degraded natural areas; Protection forests (against avalanches, mudslides, stonefalls, forest fires); Natural buffers such as protection shorelines with barrier beaches and salt marshes; Mountain range level (sustainable use zones).
Supporting the Implementation of Green Infrastructure
May 2016 10
The above list of potential priority components for a TEN-G incorporates a range of
different types of components, thus would be suitable for implementation in a variety
of areas across the EU.
Other findings of the assessment include:
Overall, the results indicate that directing money towards components already
known for their high environmental value (e.g. Natura 2000 sites) can result in
benefits. However, if the list of components funded is extended to consider
the top components in terms of maximising the BCR, contributing to social
priorities and contributing to environmental priorities, the results show that a
wider variety of components should be prioritised under a TEN-G.
Operating at an EU scale rather than at Member State level enables the
network to focus on those components that will provide the most benefits to
Europe for the money invested, since the area of land available for
implementation of such components is far greater than that available to one
Member State. Therefore, at a theoretical level, the overall benefits of setting
up a TEN-G would outweigh the costs, since the network could focus on
implementing those components that provided the greatest benefits. At a
practical level, considerations other than space would need to be taken into
account to ensure that the TEN-G was comprehensive and inclusive, and
shared benefits across the EU-28. However, such a network could still be far
more cost beneficial than the current allocation of funding across the various GI
components. Factors to take into account in the development of TEN-G would
include the existing spread of GI components across the EU (to avoid
imbalances between Member States), the condition of existing components,
and the location of settlements and their current access to GI components
(which affects the value of some of the benefits provided).
Furthermore, the location of components in combination with the types of
benefits they are expected to provide is likely to affect the level of private
investment the components may attract. Components that provide
marketable services (e.g. crops, livestock) are likely to attract private
investment, whereas those which provide universal but non-exclusive services
(e.g. regulating services related to air quality, climate regulation) may be more
reliant on public investment.
While restricted by certain limitations, the first-phase cost-benefit assessment of the
potential environmental, social and economic advantages of introducing a TEN-G
versus continuing the status quo has generated food for further thought and
discussion on the matter. In the next follow-up steps it will be important to start
looking in more detail into the possible design options including potential locations
where components could be implemented, realistic ambition levels in terms of funding
for TEN-G, that could be taken forward by DG Environment.
Supporting the Implementation of Green Infrastructure
May 2016 11
Introduction
Context
Target 2 of the EU Biodiversity Strategy4 aims to ensure that "by 2020, ecosystems
and their services are maintained and enhanced by establishing Green Infrastructure
and restoring at least 15% of degraded ecosystems." Action 6b of the Strategy
contains a pledge by the European Commission to develop a Green Infrastructure
Strategy, a commitment which was also recalled in the Roadmap to a Resource
Efficient Europe.5 The Commission delivered on this commitment in May 2013 by
adopting the Communication Green Infrastructure (GI) – Enhancing Europe's Natural
Capital.6 The GI strategy aims to create an enabling framework in order to promote
and facilitate GI projects within existing legal, policy and financial instruments.
Defined as “a strategically planned network of natural and semi-natural areas with
other environmental features designed and managed to deliver a wide range of
ecosystem services”,7 GI can contribute to the effective implementation of a range of
policy areas, including regional policy, climate action, disaster risk management, water
policy, health policy, and the Common Agricultural Policy. Indeed, one of the key
attractions of GI is its multifunctionality, i.e. its ability to perform several functions
and provide several benefits on the same spatial area, in contrast to its ‘grey’
counterparts, which tend to be designed to perform only one function such as
transport or drainage. The functions of GI can be environmental, such as conserving
biodiversity or adapting to climate change, social, such as providing water drainage or
green space, and economic, such as providing jobs and raising property prices.8
4 Communication from the European Commission to the European Parliament, the Council, the Economic and Social Committee and the Committee of the Regions: Our life insurance, our natural capital: an EU biodiversity strategy to 2020, COM (2011) 0244 final. 5 Communication from the European Commission to the European Parliament, the Council, the Economic and Social Committee and the Committee of the Regions: Roadmap to a Resource Efficient Europe, COM (2011) 0571 final. 6 Communication from the European Commission to the European Parliament, the Council, the Economic and Social Committee and the Committee of the Regions: Green Infrastructure (GI) – Enhancing Europe's Natural Capital, COM (2013) 249 final. 7 Ibid. 8 European Commission (2012) The Multifunctionality of Green Infrastructure. Science for Environment Policy. In-depth report. Available at http://ec.europa.eu/environment/nature/ecosystems/docs/Green_Infrastructure.pdf
What is Green Infrastructure?
Green Infrastructure (GI) is a strategically planned network of natural and semi-
natural areas with other environmental features designed and managed to deliver a
wide range of ecosystem services. It incorporates green spaces (or blue if aquatic
ecosystems are concerned) and other physical features in terrestrial (including
coastal) and marine areas.
GI is a tool for providing ecological, economic and social benefits through natural
solutions. It helps avoid relying on ‘grey infrastructure’ that is expensive to build
when nature can provide cheaper, more durable alternatives.
European Commission (2013) Green Infrastructure (GI) – Enhancing Europe’s Natural Capital
Supporting the Implementation of Green Infrastructure
May 2016 12
The GI Strategy foresees a number of actions to be carried out under the lead of the
Commission in the following years. They include, for example, integrating GI into key
policy areas, improving the knowledge base and encouraging innovation in relation to
GI, and assessing the opportunities for developing an EU TEN-G initiative (i.e. trans-
European priority axes for GI in Europe, similar to the trans-European networks in
grey infrastructure sectors including TEN-T for transport and TEN-E for electricity
infrastructure). To support the implementation of these new actions – particularly with
regard to actions which require new knowledge – the Commission launched the
present service contract in 2014. This final report brings together the outputs of the
five tasks conducted during the service contract, as outlined below.
Approach and objectives
The service contract was structured around five independent tasks:
1. Ensuring a more effective promotion of GI at all relevant levels;
2. Capacity building, training, education for GI;
3. Improving information exchange mechanisms;
4. Assessing technical standards and innovation possibilities;
5. Assessing costs and benefits of TEN-G.
The results of each task are included as separate chapters in this Final Report. Below,
we present an overview of the objectives and outputs per task.
Task 1: Ensuring a more effective promotion of GI at all relevant levels
The contract’s first task was aimed at raising awareness of GI among
the general public, Member States, and a range of relevant sectors,
via the development and dissemination of GI information material.
As part of this task, the project team produced ten country factsheets aimed at
providing Member States with a promotional tool which they could use in their own GI
promotion efforts, as well as informing economic policy activities at European level,
such as greening the European Semester process. Given this purpose, the country
factsheets include information on the aims of the EU Green Infrastructure Strategy
and related actions, figures on costs and benefits of investing in GI relevant for
Member States’ policy priorities, as well as good practice examples from the respective
country. The selection of countries sought to target (a) Member States with a
currently low level of GI awareness or commitment, (b) country involvement in the
European Semester process, as well as (c) an adequate geographical coverage across
Europe. Thus, factsheets were developed for: Denmark, Germany, Italy, Latvia, Malta,
Poland, Portugal, Romania, Slovenia, and Spain.
A further action under this task was the preparation of six sector factsheets
presenting the costs and social, economic and environmental benefits of GI to six
specific sector groups with further GI uptake potential. The factsheets covered the
following sectors: finance, industry, transport, energy, public health, and water (water
supply and waste water treatment). In addition, four thematic factsheets were
produced, focusing on GI in relation to the construction of buildings, abandonment of
rural areas, job creation, and climate change adaptation. The factsheets are intended
to serve stakeholders in the respective sectors, as well as policy-makers.
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May 2016 13
The country-specific, sectoral and thematic fact sheets are included in Annex 1.
In addition to the factsheets, the project also contributed to the dissemination of GI
knowledge and awareness through the implementation of three sectoral
workshops, held in:
Lecce, Italy – focused on GI and the health sector;
Arad, Romania – focused on GI and various sectors faced with green/grey
infrastructure decisions; and
Helsinki, Finland – focused on GI and businesses.
Finally, Task 1 also included activities to support meetings of the European Green
Infrastructure Implementation and Restoration Working Group (EU WG GIIR)
– namely, the 3rd and 4th GIIR WG meetings and the joint meeting with the MAES
Working Group – through the preparation of background materials and follow-up
deliverables assisting the client with its contributions to the group. The team also
presented preliminary findings of all tasks during each of the sessions, inviting
participants to provide feedback and suggestions.
Task 2: Capacity building, training, education for GI
The contract’s second task focused on capacity building and training
in relation to GI. In particular, the goal was to ‘train the trainers’ and
therefore provide the necessary background material and toolset to
‘pass on the message’ about GI in Europe and to ensure a
continuation in the efforts to increase GI uptake beyond the
timeframe of this service contract. To this end, the task developed
training material that can be re-utilised in various combinations to
create tailored training modules for different stakeholders.
In a first step, the project team conducted a ‘quick scan’ of existing trainings and
awareness raising initiatives across the EU-28 in order to gain a better
understanding of the current availability and the types of training workshops which
could be developed under this service contract. The resulting training database can be
seen as a living document that could be updated by representatives of the EU WG
GIIR on an annual basis.
As a next step, training material was developed, based on other tasks in this service
contract. The developed training material was subsequently ‘test-run’ in two
workshops which were selected based on opportunities to link up with an already
planned event. The two workshops were:
A training on GI & Wetland Restoration as part of CEEWeb’s Academy event on
Building Blue-Green Infrastructure: Restoring and protecting wetlands and their
ecosystem services in Budapest, Hungary.
A training on better linking GI with existing operational programmes, as part of an
event organised in Arad, Romania on ‘Implementation of the Strategy for Green
Infrastructure in Romania: Nature – our health our wealth’.
In addition to the two workshop events, it was agreed with the client to develop
material for a broader Massive Open Online Course (MOOC) on GI in order to
make training more widely available for a larger audience across Europe (and
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beyond). The developed lectures (7 in total) can also be easily amended or
complemented with lectures on additional GI topics in the future. It should be noted
that this contract only developed the lecture scripts, not the actual video material to
deliver the MOOC.
The MOOC lecture scripts are included in Annex 7.
Task 3: Improving information exchange mechanisms
Task 3 evaluated the current visibility of GI information on digital
platforms of European policy sectors and other stakeholders and
considered means of improving the content of - and access to -
digital information on GI.
This part of the study was structured around four subtasks:
Exploring the current digital GI information landscape and identifying the
policy sectors and stakeholder platforms that are relevant for disclosing
GI information at an EU level: this included identifying priority policy sectors
and stakeholders for which GI information should be available and identifying the
linked communication and information exchange platforms. It also included
describing what may be the ideal platform and how it could be implemented.
Furthermore, the team examined how the existing platforms are organized and
how GI information could best be integrated and made available.
Evaluating the accessibility of GI information among a selection of eight
platforms and the type of information available (such as data, indicators,
maps, libraries, etc.): this assessment evaluated which GI content the selected
platforms provide or do not provide, whether its visibility can be improved and
whether the information available can be linked to the European Biodiversity
Information System (BISE). This exercise led to recommendations on how to
improve the content and visibility of GI information.
Determining the technical or governance requirements for implementing
recommendations for a subset of three shortlisted platforms: the aim of
this subtask was to provide a file for each of the three selected platforms – i.e.
BISE, Natural Water Retention Measures (NWRM) and Climate-ADAPT – where a
description of the technical specifications and properties for the platform are
elaborated. After outlining the technical details, an analysis and proposal was
made to conduct the necessary adjustments to receive data, process the data and
finally publish the data targeted to the existing governance and technical
processes. Proposals, processes, approaches and recommendations were
discussed with the technical and administrating levels of the selected platforms, in
order to assess and estimate the most suitable mechanisms and procedures for
sharing GI-relevant information.
Discussing with the representatives of the EU information systems to
what extent the recommendations provided in the report can be
implemented: with respect to content, deliverables of the other tasks within this
contract, in particular outputs from tasks 1, 2 and 4, may allow for material
being ready to use and available for being uploaded directly. It remains the
responsibility of the respective services to actually upload and incorporate the
information received.
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The task resulted in a series of recommendations related to the various platforms
examined, as well as more general recommendations for improving the online visibility
of GI.
As a final step, the analyses and recommendations made in this report were
distributed to the responsible services of BISE, NWRM and Climate-ADAPT. In an
iterative process, the team explored with them how to succeed in implementing the
recommendations made.
Task 4: Assessing technical standards and innovation possibilities
The objective of Task 4 was to support the Commission’s assessment
of how (and under which circumstances) technical standards,
particularly in relation to physical building blocks and methodologies
and procedures, could increase the deployment of GI.
The study covered nine sectors, namely, finances, buildings, water, transport, public
health, industry, climate, rural abandonment and energy. For these sectors, we
assessed how technical standards in use by each of these sectors could increase the
deployment of GI. This included an exploration of the extent to which GI is currently
covered in the standards of these sectors, as well as an identification of the gaps, i.e.
areas where GI is insufficiently covered in the standards. We thereby investigated in
depth the need for (further) harmonising, adapting or developing GI-related
standards.
The research combined desk review and interviews with representatives of the
different sectors. In addition to the evaluation of the nine sectors, representatives of
the Joint Research Centre and the Institute for Environmental Protection and Research
were interviewed with regard to ongoing initiatives related to GI and standardisation.
Where relevant, these initiatives were included in the sector fact sheets or in the
general outcomes of the report.
Based on the various inputs, sector sheets were developed clarifying the current state
for the sector and commenting on the possible way forward. These sector sheets
include concrete recommendations regarding:
The need for harmonisation between standards;
The potential for including or strengthening the concept and principles of GI in the
different standard categories (performance, procedure, methodology);
The interoperability between technical standards applied in different project
phases (planning, design, and construction).
A series of cross-sectoral recommendations were also identified and discussed.
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Task 5: Assessing costs and benefits of establishing a TEN-G
The objective of Task 5 was to carry out TEN-G exploratory work, in
particular focusing on a first-phase assessment of costs and
economic, social and environmental benefits of establishing a Trans-
European Green Infrastructure Network.
The first part of this task reviewed the existing Trans-European Networks for
transport (TEN-T) and energy (TEN-E) since these networks may potentially
provide valuable feedback from existing experience for the establishment of a TEN-G
in terms of governance and financing mechanisms. The lessons learnt from this review
are reported for consideration when deliberating on the most suitable set-up options
of a TEN-G for Europe.
Building on this review, the remainder of the task consisted of a first-phase
assessment of costs and benefits of a potential TEN-G versus continuing the
current GI policy and funding structures. It should be noted that the assessment
carried out did not focus on finding out the best design set-up option for a TEN-G, but
rather provides initial evidence on whether or not the costs of introducing and running
a TEN-G would be outweighed by the expected economic, social and environmental
benefits delivered via such a network. This means that the assessment first
established knowledge on the current status quo scenario, the GI baseline. As a next
step, the cost-benefit assessment focused on comparing the different proposed GI
components in terms of what can deliver the greatest level of benefit if promoted
under a Trans-European network structure. The results therefore can be used for
informing policy discussions and next steps with regards to developing a TEN-G
framework, the most relevant ambition level, component focus, etc.
The first step during the assessment was the development of the status quo
scenario, the current GI baseline of what the existing GI policy and funding
approach already delivers in terms of GI initiatives and how much these cost (across
the various funds). This step involved identifying the costs and benefits associated
with different GI components. Existing funds that have been allocated to each of the
GI components have been estimated using the projects that have been funded under
LIFE+, the European Regional Development Fund (ERDF), the European Social Fund
(ESF), the European Agricultural Guarantee Fund (EAGF), the European Agricultural
Fund for Rural Development (EAFRD), the European Marine and Fisheries Fund (EMFF)
and the Cohesion Fund. This information was then used in combination with identified
data on the costs of each GI component (in € per ha) to estimate the area of each
component delivered, and hence the ecosystem service benefits under the existing
situation (the current baseline). The assessment in the next step then looked at
whether a TEN-G would provide greater benefits than those estimated under the
current baseline.
As mentioned above, the cost-benefit assessment then focused on comparing the
potential additional European added value a TEN-G could theoretically deliver
compared to the baseline scenario. This involved comparing the benefits of the various
GI components against their costs to identify which offered the best ‘value for money’
if promoted on a European scale, and hence to prioritise where funding might be
allocated under a TEN-G. Under a theoretical prioritisation exercise for TEN-G funding,
those GI components with the highest benefit-cost ratio were ranked highest, so more
funding was allocated to those components that delivered a higher level of benefits for
Supporting the Implementation of Green Infrastructure
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every € spent. The GI components were also ranked in terms of the non-monetary
benefits that they could provide. As well as ranking on all ecosystem service benefits,
the GI components were compared with how they performed against existing social
and environmental priorities, such as the ones identified by the 7th Environmental
Action Programme.
It should be noted that the narrative provided in this Final Report is supported with
the developed Excel calculation sheets and a technical methodological report as
annexes.
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1 Task 1 – Ensuring a more cost-effective promotion of GI at all levels
Chapter summary
In the bigger picture of supporting the implementation of Green Infrastructure via this contract, Task 1 is aimed at raising awareness on a general level – via the development and dissemination of information to a broad audience from various backgrounds (= catered to ‘the wider audience’ to gain further attention and buy-in from non-experts). In order to make the information material more accessible, the material and workshops are geared towards various target groups, namely: 10 Member States with little GI information available, 6 sectors with further GI uptake potential, and 4 topic areas offering interesting linkages to other policy areas to gain attention and link policy debates with other ‘hot topics’. 20 Factsheets: The development of the 20 factsheets (10 countries, 6 sectors, 4 topics) has generated additional information as regards the status of implementation, good practice cases, and the level of awareness for those selected countries, sectors and topics. However, the development process has also highlighted some challenges as regards the availability and accessibility of GI information for specific countries, sectors and/or topics. Feedback received for the factsheets has been very positive, with requests whether such factsheets will be made available for additional countries and sectors/topics. Sectoral workshops: In addition to the factsheets, another avenue for supporting DG ENV with the dissemination of GI knowledge and awareness was the implementation of three sectoral workshops. In addition to raising awareness, the workshops were also used to ‘test-run’ the relevant sector (and topic/country) factsheets. The three workshops were held as part of on-going workshops/events in order to maximise participation. The three sectoral workshops were as follows:
1. Lecce, Italy – focused on GI and the health sector;
2. Arad, Romania – focused on GI and various sectors faced with green/grey infrastructure decisions; and
3. Helsinki, Finland – focused on GI and businesses.
Key generalised lessons learned from the sectoral workshops are:
Content: Participants really appreciated the wealth of usable information provided. As a next step, the client could possibly provide access to all workshop material via their website, BISE, etc. Additionally, further workshops of this type could be implemented in the future.
Organisation: Low attendance and other organisational challenges can primarily be associated with the fact that we were dependent on the ‘hosting’ event. A lesson learnt here is that it might be better to organise future sessions independently, taking the risk of lower attendance rates (which are also not guaranteed when linking up with an existing event, see Helsinki).
Status of GI awareness: All three workshops have shown that there is an urgent need to further raise awareness and build capacity on the linkages between GI and other sectors. While some steps have been taken, further efforts are needed to present good examples and provide training on how to include GI elements in other policy areas. For example, the sector factsheets can be used as an information source and further promoted not only in Romania but also in other Member States facing similar problems. Another major barrier to GI that has become very apparent during the workshops is insufficient understanding amongst stakeholders of the way natural ecosystems function which often results in an underused potential for GI development. Better use of integrated spatial planning processes, improved capacity of decision-makers and better institutional cooperation are important elements to address this challenge.
Supporting the EU WG GIIR: The contractor has supported the client with the preparation, hosting and follow-up of all WG GIIR meetings throughout the duration of the contract. This close interaction between the contractor and the WG GIIR has allowed maximisation of cross-fertilisation of ideas and sharing of knowledge on both sides.
Supporting the Implementation of Green Infrastructure
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Introduction
The key objective of Task 1 was to ensure a more cost-effective promotion of GI at all
levels. This translated into three main support tasks the team was asked to implement
throughout the duration of the service contract.
The first sub-task focused on supporting the promotion of GI in Member States via the
development of promotional materials, namely GI factsheets. Similarly, the
communication towards sectors (both policy-makers and private actors) of costs and
benefits of GI as compared to grey alternatives within their respective fields has been
deemed as an area that needed improvement. The team also developed sectoral and
thematic factsheets, which can now be used as GI promotional material.
Finally, via interactions at sectoral workshops, but also during the various EU WG GIIR
meetings, the team was able to gather valuable feedback on current barriers to
further GI take-up, engage in discussions and test-run developed promotional
materials.
The outputs of these activities are captured in the remaining sections of this chapter.
1.1 GI promotion in Member States
1.1.1 Development of country fact sheets
As part of this task we have produced ten country factsheets whose aim is two-fold:
To serve MSs, which can use the sheet as a promotional tool for their GI efforts;
To feed information into MS-specific information delivered to the EC for the
Semester process.
Given this purpose, the country factsheets include information on the aims of the EC
GI Strategy and actions, figures on costs and benefits of investing in GI relevant for
Member States’ policy/topic priorities, good practice examples in the country of
concern.
The selection of Member States has been based on the following selection criteria (in
order of importance):
Low level of GI awareness i.e. we should focus on those countries we do not
hear/know about;
Inclusion mainly of those countries with low level of GI commitment;
Country involvement in European Semester process;
Geographical spread (to the extent possible).
In coordination with the representatives present during the inception meeting, the
following Member States were selected for the production of country factsheets:
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Table 1 MS selection for Task 1.1
# Member State
Selection reason Geographical Coverage
1 Poland Pilot case East
2 Romania Semester process; planned national GI conference in 2015
East
3 Slovenia Semester process East
4 Italy Semester process South
5 Germany Semester process West
6 Latvia 2015 Presidency North
7 Denmark Little info known to EC North
8 Portugal Little info known to EC South
9 Malta Island state South
10 Spain High vs low commitment regions South
The draft factsheets were developed by the project team and reviewed by the client.
At a second iteration, they were also reviewed by country experts and circulated
amongst the EU WG GIIR for comments. After the progress call held on 5 August
2015, all the factsheets have gone through a final thorough grammar and spelling
check by an English native speaker from our consortium partner Stella Consulting. An
additional check has been done to enhance the readability of the factsheets in a way
that the message can get across in a clear and effective way. Further, we have
adjusted all factsheets to include pictures tailored to each country and type of GI
measure.
All final country factsheets can be found in Annex 1.
1.1.2 Insights and lessons learnt from developing the country factsheets
Looking back at the process of developing the factsheets, the content development
and review by country experts ran smoothly. The decision to include ‘standardised’
paragraphs introducing the concept of GI as well as the European policy context for
each factsheet, followed by a common structure to be filled with country-specific
information and illustrative cases worked well not only for the development of content,
but also for visual unity across all promotional sheets.
We have tested and distributed the factsheet to various types of users within the
national context and received very positive feedback as regards the usefulness of the
content, as well as the visual ‘attractiveness’ of the material, which entices the reader
to study the contents.
The Italian and Romanian sheets, in particular, have also been included as part of the
workshops delivered as part of Tasks 1.2 and Task 2 in Lecce, Italy and Arad,
Romania respectively. Participants had been asked to give feedback on the usefulness
of the factsheets. Commentary has been very positive, with requests on whether such
factsheets will be made available for additional countries and sectors/topics.
1.2 Communication of costs and benefits of GI to sector groupings
The outputs of Task 1.2 concerned the production of 10 sector and thematic factsheets
and the implementation of sectoral workshops with the aim of disseminating green
infrastructure knowledge and awareness across selected sectors.
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1.2.1 Production of 6 sector factsheets and 4 topic factsheets
We have created 10 factsheets which provide GI information relevant for selected
sectors and topics. The sectors and topics have been selected and agreed upon
together with the client during the inception phase of the project:
In addition to the sectors proposed by the European Commission (finance,
industry, transport, energy and public health), a sector sheet for the water sector
(water supply, waste water treatment) has been produced. This choice has been
driven by the fact that water supply companies often manage large infiltration
areas with large GI potential (i.e. GI-based alternative waste water treatment)
and the fact that water-related ecosystems often deliver multiple benefits.
The thematic sheets deal with GI in relation to the construction of buildings,
abandonment of rural areas, job creation, and climate adaptation.
The factsheets are aimed to serve sector actors as well as policy-makers. These
factsheets contain information about the aims of the EC GI Strategy and actions
(similar to the country factsheets). Furthermore, they include indications on costs and
benefits of investing in GI for the specific sector/topic and good practice examples.
Similar to the country factsheets, the study team took the lead in developing draft
content for the sector and topic sheets. Drafts were then reviewed by the client,
relevant sector experts, as well as circulated amongst the EU WG GIIR
representatives. It should be noted that (as agreed during the 21 May 2015 progress
meeting) the finance, energy, public health, jobs, and climate adaptation sheets have
been reviewed and updated based on a second round of expert feedback. After the
progress call held on 5 August 2015, all the factsheets have gone through a final
thorough grammar and spelling check by an English native speaker. An additional
check has been done to enhance the readability of the factsheets in a way that the
message can get across in a clear and effective way. Further, we have adjusted all
factsheets to include pictures tailored to each sector and the specific illustrative
examples.
All final sector and thematic factsheets can be found in Annex 1.
1.2.2 Sector workshops
As a second step for increasing the awareness about GI among sectors, the study
team was asked to run three sectoral workshops. As agreed during the inception
phase of the project, these workshops would be ‘hooked onto’ an existing sectoral
event in order to maximise the number of participants and to encourage engagement
with other organisations running relevant sectoral workshops.
The project team has run the following three sector workshops:
IEREK – Urban planning and architecture design for sustainable development (14-
16 October 2015) http://www.ierek.com/events/urban-planning-architecture-
design-sustainable-development/, Lecce, Italy.
Implementation of the Strategy for Green Infrastructure in Romania: Nature – our
health our wealth (29-30 October 2015), Arad, Romania. (Combined sector
workshop & train-the-trainer event).
CBD Business Forum (11-12 November 2015)
https://www.cbd.int/business/bc/2015forum.shtml, Helsinki, Finland.
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We now elaborate on the summary of each workshop, present the lessons learnt and
suggest next steps accordingly.
1.2.3 IEREK – Urban planning and architecture design for sustainable
development
Summary of the workshop
The sector workshop was organised for an IEREK conference called Urban Planning
and Architectural Design for Sustainable Development (UPADSD), organised in Lecce,
Italy. Our audience mainly consisted of urban planners, architects and technical
engineers. Some sessions were very specific on e.g. green roofs, but many of them
were not about nature based solutions at all.
Unfortunately, due to logistical issues, our well prepared interactive workshop had to
be transformed into a (although quite interactive) presentation. On our arrival, we
were informed that the schedule was very much delayed and that they could offer us a
slot on the day after. Due to our travel schedule, that was not an option for us.
Consequently, we were offered a room when one of the parallel sessions finished a bit
early. Our time slot was reduced to no longer than 20 minutes. To make matters
worse, our workshop had to start before the scheduled moment and in an unknown
room, so participants came in only during the presentation. However, given that the
presentation started slowly, with extra emphasis on the first introduction slides, late
comers did not miss substantial parts. Although we had prepared a wonderful
presentation with internet voting and interaction by Mentimeter9 (so that the audience
would answer different questions by choosing options, or scaling the importance of
different types of GI), as a consequence of the limited time we were granted from the
organisers, we decided to skip the interactive slides. Although the speaker interacted
with the audience verbally, given the poor ability of many participants to express
themselves in English, the interaction was less informative than the Mentimeter polls
would have been.
Although the audience in the beginning consisted of approximately 20 people, by the
time the workshop came to an end the room was filled with about 60-80 people. We
decided to go on and take considerably more time than the 20 minutes we had been
given. The audience only grew, nobody left the room and participants became very
engaged and asked many questions, both during the session and afterwards (for
example, during lunch some of the session’s attendees engaged with us in a
discussion about green/nature-based solution for cooling school yards, for climate
change adaptation and storm water management). Most participants came from the
Mediterranean countries and experienced different problems than the north-western
European examples we presented.
The 30 sets of factsheets we brought printed with us were gone in a few moments and
many people asked for the digital versions. We provided a link to them in the
presentation, so that participants could download them.
Lessons learnt
The concept of a sector workshop worked well. Even though the audience was quite
diverse and mostly originating from other climatic zones, many of them recognised the
urban examples and discussed the solutions Green Infrastructure could offer.
9 Service to create interactive presentations online that allow the audience to vote with smartphones during the presentation.
Supporting the Implementation of Green Infrastructure
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The presentation we prepared was targeting primarily urban planners and architects.
The replicability of the workshop is not straightforward for other sectors and would
need some adjustments to the presentation, for instance new examples. The structure
of the presentation and the Mentimeter questions need less changes.
The factsheets were useful in preparing the presentation and raised a wealth of
interest. We mentioned many examples addressed in those and in this way we were
able to refer to the sheets during the session.
It was unfortunate that our workshop time had to be reduced, but the interactive
Power Point presentation developed for the workshop could be used for other events.
All workshop materials (presentations and pictures) can be found in the accompanying
Annex 2 ‘Task 1.2 - Lecce Workshop Material’.
1.2.4 Arad Workshop – GI implementation in Romania
Summary of the workshop
The workshop was held within the two-day conference “Implementing the Green
Infrastructure Strategy in Romania - policy and practice.” The conference was
organized by Excelsior NGO in partnership with CEEweb for Biodiversity, supported by
the Arad Municipality and took place on 29-30th October 2015 in Arad City Hall.
The purpose of the conference was to promote the implementation of the EU Green
Infrastructure Strategy, and to identify the means of integrating the strategy in
national development plans, financing options and sectors including environment,
agriculture, forestry, transport and territorial development. The event was attended by
representatives of the European Commission, Romanian ministries and authorities.
Attendants had the opportunity to present their experience with respect to GI
implementation, exchange views and ideas on how to tackle challenges.
The sectoral workshop on green infrastructure implementation was designed to be in
line with the overall objectives of the conference. Specifically, the workshop aimed to
highlight the wider benefits of GI and stimulate a discussion on mainstreaming GI in a
number of sectors considering the Romanian context. The topics of the workshop
complemented other themes addressed during the conference such as: vision and
state of play of EU Green Infrastructure strategy, financing GI and opportunities for
businesses, GI aspects in Romanian OPs for transport, CBC OP between Romania and
Hungary, etc. In addition, the workshop served as an opportunity to inform the
participants about the ongoing DG Environment contract on supporting the
implementation of the GI Strategy and how they can benefit from its outcomes and
deliverables.
Presentations
The presentation on mainstreaming GI into projects financed under ESI Funds (2014-
2020) was delivered by Venelina Varbova from the REC and outlined the linkages
between GI and the following policy areas: climate adaptation, transport, agriculture,
industry, energy. The important role of GI for job creation was also highlighted. The
presentation included a host of examples for different sectors that were mostly taken
from the sector factsheets prepared under the DG Environment contract on supporting
the implementation of the GI Strategy.
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Kristin Faurest, external expert to the REC, gave a presentation on the multiple
benefits (social, ecological and economic) of Green Infrastructure. The presentation
also focused on GI as an integrated solution and highlighted the value of and
approaches to stakeholder mapping. Kristin Faurest also presented three European
green infrastructure case studies at the regional landscape, local institutional and
neighbourhood level: 1) Landscape Park Rems (Landscape Park Stuttgart Region); 2)
Miskolctapolca spa complex, Hungary; and 3) Ekostaden Augustenborg (urban
regeneration initiative), Malmö, Sweden. The examples provided further insight into
cross-sectoral cooperation, multidisciplinary approach, broad spectrum of benefits
designed to solve existing social, environmental and economic problems.
The presentations were very well received by the participants and aimed to provide a
basis for the subsequent group break-out sessions.
Group break-out sessions
Due to the reduced number of participants, three group break-out sessions were held
instead of the originally planned six. The participants were split into three groups, as
follows:
Green Infrastructure and adaptation to climate change;
Green Infrastructure and transport;
Green Infrastructure and agriculture.
The groups were asked to consider the following key questions:
What are the underused resources for GI development in Romania?
What are the opportunities and challenges?
Identify ideas for GI projects in Romania;
Identify opportunities for incorporating GI as a part of other projects.
As an output the groups were requested to formulate policy ideas for development of
GI in Romania. A representative of each of the working group presented the outcomes
of the group work and discussions in plenary.
Working group: Transport and green infrastructure
Underused resources, opportunities and challenges with regards to GI and the
transport sector:
The underused resources for GI development are also opportunities.
Romania possesses rich diversity of nature, but it is not considered from the
transport point of view.
There is potential in integrating GI solution in public transport (e.g. introducing
green tram lines).
Local communities are not sufficiently engaged in GI development.
There is a need to build capacity of state administrations with regards to GI
opportunities and implementation.
There is a need to consider GI in local development plans.
There is a need for incorporating GI in transport master plans.
There is insufficient funding for GI solutions.
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There is a need for better institutional cooperation with regards to applying GI
solutions in the transport sector.
Suggestions for policy improvement:
Mapping existing GI (ecological corridors);
Development of cycle network across borders;
Integration of GI into transport policy at national and regional level;
Analysis of the Impact of GI on the development of metro infrastructure, e.g. with
regards to underground water system, drainage, greening of metro stations;
Provide sufficient Institutional resources for the development of GI.
Working group: Agriculture and green infrastructure
Underused resources:
There is non-utilized agricultural land/structures (e.g. canals);
Much land is under small-scale biodiversity-rich and culturally valuable
cultivation;
The local products are not promoted enough;
Traditional landscapes and opportunities for tourism;
Heterogeneous landscape – allows for cultivating different types of crops.
Problems:
There is no access to financing for high quality products;
There is insufficient national financial support for product certification;
There is erroneous or lack of support for small-scale farmers;
Lack of farmers’ cooperatives/associations;
Depopulation of villages;
Invasive species on abandoned land.
Opportunities exist with regards to:
Agri-environmental schemes (eco-conditionality);
Greening agricultural practices;
Empowering local action groups;
Limiting excessive fertilization.
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Suggestions for further interventions:
More investments in nature protection are needed.
There is a need to revive water mills and canals.
There is a need to develop short producers-buyers chains.
Support needs to be provided to learning farms.
There is a need to develop a database with information about local traditions.
Working group: Adaptation to climate change and green infrastructure
The following suggestions for policy actions have been outlined:
There is a need to stimulate biomass production and use.
There is a need to eliminate waste pollution from canals.
The focus should be on the implementation of the WFD.
Funding is needed for refurbishment of old buildings with focus on green
roofs/walls. Such funding can come from OPs or municipal budgets.
There is a need to raise awareness about the linkages between GI and adaptation
to climate change.
Lessons learnt
Feedback on the quality of presentations, presented examples and facilitation of the
workshop was positive. The group discussion was lively, and the participants were
stimulated to think about GI development and what policy actions are needed to
address challenges and unlock potential for GI implementation in Romania. Some of
the ideas that resulted from the group work were quite innovative and could be further
developed in a future working session.
We understood that the wider benefits of GI are poorly understood among authorities
who are not dealing directly with nature conservation. The workshop was an
opportunity to raise their awareness of economic and social benefits that GI projects
deliver and the collaborative and multidisciplinary approach needed to achieve these
goals.
All workshop materials (presentations and photos) can be found in the accompanying
Annex 3 ‘Task 1.2 – Arad Workshop Material’.
1.2.5 Helsinki Sector Workshop - CBD Business Forum
Summary of the workshop
This sector workshop was attached to the CBD business and biodiversity forum in
Helsinki on 11 and 12 November 2015. Communication was started early with the
organisers. However, we only received green light to give the presentation a couple of
weeks before the event.
In addition, while our aim was to have the session as a parallel session during the
forum (to attract a large set of the 270 registered participants), our session was at the
very last minute re-scheduled to take place right after the forum on 12 November
2015, later afternoon. Many participants were already flying home or were satisfied
Supporting the Implementation of Green Infrastructure
May 2016 27
with having had 2 full days of presentations and discussions. Unfortunately, this led to
only 3 participants attending the session on GI.
Despite the low turn-out rate, the session was very lively, with good sharing of
expertise and discussions on aspects relating to what was shown in the presentations.
The feedback from participants was also very positive:
“The session was an excellent opportunity to get us thinking and discussing about
GI, and in particular the following points:
Monitoring of GI: there is a tendency to assess GI from a quantitative
perspective (e.g. number of hectares implemented), whereas the quality of the
infrastructure itself is key and also needs to be assessed and monitored over
time.
New sets of skills are required to ensure the maintenance of GI. Training a wide
range of stakeholders – from architects to gardeners - to managing GI will be
critical to ensure success of the projects.
I have found the EC approach of embedding GI as a solution in different European
platforms an interesting one. At the moment, the WBCSD is developing a specific
and distinct project on “Natural Infrastructure for Business”, and we should also
start considering infusing GI in different existing WBCSD projects, such as the
Climate Change or Sustainable Cities ones.”
(Violaine Berger, World Business Council on Sustainable Development)
“Interesting and inspiring session on Green Infrastructure. The movie on green
infrastructure (third movie) showed very clearly the different options and benefits.
Clearly presented with enthusiasm which helps to deliver the message. The work for
the EC is interesting but not as interesting as the first and last part of the
presentation. Good to show the report from 2013, I will definitely have a look.
Company example at the end is interesting but maybe a bit too long/detailed (end
of the day...). Maybe too detailed on the methodology of biodiversity assessment.
Would be good to see if you can capture this story in two slides using pictures of the
area and putting the numbers in the picture or using infographics. Also good to
show/indicate the results from an ecosystem services perspective and the
beneficiaries. This also allows you to end with something which is a bit closer to the
concept of green infrastructure (focus last part is now very much on biodiversity).”
(Wijnand Broer, Crem)
The presentation was shared with the participants by e-mail after the event.
Afterwards, it was also agreed with the hosts of the CBD business and biodiversity
forum that they would share the GI presentation with all participants to the forum by
including it in the Forum materials made available on the Forum’s webpages:
www.ym.fi/BBDF2015. (The Forum materials include: Discussion paper, Added Value
from Nature to Sustainable Business, presentations - PDF and web-stream
recordings.) In this way, we hope for a wider dispersal and usage of the prepared
information.
Lessons learnt
One of the key lessons learnt from this session relates to the fact as to how best to
communicate with the private sector. Business agendas are typically quite full and
Supporting the Implementation of Green Infrastructure
May 2016 28
people’s targets relate to turnover. They are very careful attending meetings if they do
not see direct benefits on their end. To this end, it is important to locate the right
outlet for such information to be disseminated. Additionally, the information should be
as tailored as possible to the individual participants so as to maximise the benefit they
can get out of the session.
All workshop materials (presentations and pictures) can be found in the accompanying
Annex 4 ‘Task 1.2 – Helsinki Workshop Material’.
1.3 Supporting key actions of GIIR WG
The consortium has been present during the 3rd and 4th GIIR WG meetings, as well as
the joint day with the MAES working group. The team has delivered draft minutes for
these meetings as well as provided various requested preparatory and follow-up
deliverables assisting the client with its contributions to the group. In addition, the
team has presented preliminary findings of all tasks during each of the sessions,
inviting participants to provide feedback and suggestions.
The separate file entitled ‘Annex 5: Task 1.3 – WG GIIR support documents’
contains all draft minutes, presentations, edited documents, etc. created during the
course of the project.
Lessons Learnt
The participation in the WG GIIR has been a very valuable experience for the team.
The participation has allowed us to gain insights into the current debates on GI across
Europe, as well as direct access to the main representatives per Member State, sector
organisations and NGOs. From our perspective, we have maximised these insights and
direct networking opportunities in order to improve deliverables via sharing ideas,
asking for feedback and giving exposure to the overall contract amongst the relevant
stakeholders.
From the perspective of the WG GIIR participants, we have gathered that they have
appreciated the involvement of the contractor as part of the WG GIIR as this showed
them the European Commission’s deep commitment to the group and to delivering
progress across various topics the WG is engaged in. Various members have
acknowledged that the facilitation of drafting documents and the continuous updates
regarding the status of this contract have been highly appreciated.
From the perspective of the client, the request for involvement in the WG GIIR has
delivered positive results in terms of having had support for preparatory actions,
during the events, as well as with follow-up action points. In addition, the client and
contractor were able to maximise lessons learnt and the cross-nurturing of thought
processes / developments between this project and ongoing work of the WG.
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2 Task 2 – Capacity building, training, education for GI
Chapter summary
In the bigger picture of supporting the implementation of Green Infrastructure via this contract, Task 2 is targeted at a deeper level of understanding and more focused target group (in comparison to Task 1). The goal of this task is to ‘train the trainers’ and thus provide the necessary background material and toolset to ‘pass on the message’ about GI in Europe and – in turn – ensure a continuation in the efforts to increase GI uptake beyond the timeframe of this project. This was also highlighted during the inception meeting, where the client emphasised that Task 2 was included in the service contract to try and fill a missing link between the existing trainings on various relevant topics and the inclusion of ‘GI’ considerations within existing sectoral trainings. To this end, the task contains the preparatory research and development of training material that can be re- utilised in various combinations to create tailored training modules for different sectors, Member States, etc. The first sub-task focused on gathering a brief overview of existing trainings and awareness raising initiatives across the EU-28 in order to gain a better understanding of the current availability and what types of training workshops could be developed under this service contract. The resulting training database can be seen as a living document that could be updated by representatives of the EU WG GIIR on an annual basis. The two workshops to ‘test-run’ developed training material were chosen based on opportunities to link up with an already planned event. Material was then tailored to the level of GI knowledge of the audience as well as to the sector/theme covered by the broader conference. In addition to these tailored workshop modules, the team had agreed with the client to develop one broader GI module that can be accessed by a wider range of audience as an online training course. This MOOC (Massive Open Online Course) material could be a tool to reach and train many people from across the EU- 28 (and beyond) on GI. The developed lectures (7 in total) can also easily be amended with lectures for additional GI topics in the future.
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Introduction
Task 2 of the contract focused on capacity building, training and education in relation
to GI. On the one hand, the task set out to identify the existing initiatives that already
exist across Member States and NGOs/educational institutions. On the other hand, the
task also included steps to generate new training material to be ‘test-run’ in
workshops.
To achieve these overall goals, the team first conducted a ‘quick scan’ of existing
training and awareness raising initiatives in the EU-28. As a next step, training
material was developed (based on other tasks in this service contract) and tailored to
the two events where the training workshops were held. In addition to the two
workshop events, it was agreed with the client to develop the material for a broader
GI MOOC (Massive Open Online Course) to make training more widely available for a
larger audience across Europe (i.e. not event dependent).
2.1 EU-28 Quick Scan of existing training and information initiatives
As part of Task 2, we have reviewed existing training programmes across the EU-28
Member States. The aim of this quick-scan was to identify a short-list of measures
(activities in this case) which are particularly relevant to enhancing capacities for GI.
The ‘EU-28 quick-scan’ was presented in an Excel sheet to the Commission in April
2015 with name, target area, target group, short description of measure, and entity
responsible for the measure. The result was a list of 20 existing training programmes /
facilities. This list was circulated amongst the WG GIIR members in order to gather
any additional initiatives the team may not have been aware of. The final EU-28 Quick
Scan (document entitled “EU-28 Quick Scan final.xls”) can be found in Annex 6. The
exercise should be seen in combination with some of the inventory relevant for
training/awareness that has been gathered in parallel as part of the WG GIIR (see
Annex 6 for Task 2, document entitled “MTR_target 2_GI_31032015.xls”).
Conclusions from this scanning exercise have indicated that there is a need for a
greater availability of tailored GI information sessions that can teach decision-makers
the practical application of ‘green options’ as an alternative to their traditional grey
infrastructure solutions. To this end, it was agreed to develop two train-the-trainer
workshops and test-run them as a parallel session linked to an existing event in order
to draw sufficient participants.
In addition to these tailored sector- and/or country/city/region- specific trainings, it
was agreed with the client that a broader GI course available for a wider public
throughout Europe could help those interested in the topic gain the necessary
knowledge to then teach/inform others. To this end, it was agreed to develop the
content for a freely accessible Massive Open Online Course (MOOC) that could
eventually be run by a university, NGO or another European institution via commonly
known platforms, such as COURSERA or edX.
In practice the above has materialised into:
Preparatory documents for a Massive Open Online Course (MOOC) on GI
A training on GI & Wetland Restoration as part of CEEWeb’s Academy event on
Building Blue-Green Infrastructure: Restoring and protecting wetlands and their
ecosystem services in Budapest, Hungary.
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A training on better linking GI with existing operational programmes, as part of an
event organised in Arad, Romania on ‘Implementation of the Strategy for Green
Infrastructure in Romania: Nature – our health our wealth’ (combined sector
workshop & training event).
These three trainings are further explained in the remaining chapters of this Task 2
report.
2.2 Development of a Massive Open Online Course (MOOC) on GI
The development of a so-called Massive Open Online course (MOOC) on GI included
the conceptualisation of what content information would be suitable to be conveyed in
this type of training format, what type of target audience the material should be
designed for, and the preparation of all scripts for the MOOC sessions. The actual
implementation (launching and running) of the online course on GI was not within the
scope of the service provided. The documentation that has been produced as a final
deliverable can, however, be picked up by a professor/facilitator (e.g. University of
Wageningen), recorded and easily transformed into the online MOOC once a hosting
organisation has been found. During the preparatory work for the MOOC the team had
close contact with the ATENS Resource Centre in France, as well as CEEWeb in
Hungary who are both interested in participating in the implementation of such an
online training opportunity.
As regards the target audience, the MOOC was developed to appeal to a wide range of
individuals: from trainers to practitioners in the field, to local decision-makers, to
architects, urban designers and planners, etc.
The format of the training module should resemble online courses in platforms such as
‘Coursera’. The format we propose reads as follows:
The course would run for 7 weeks;
The course would consist of a total of 6 lectures, one per week;
Lectures would be in the form of videos and text in English (videos have not been
developed within this contract);
Each week there will be a piece of homework given to students, in the form of a
practice-driven assignment based on the lecture;
Each lecture includes a quick test in the form of a quiz;
The course should offer the possibility to obtain a certification upon request, when
all assignments have been completed and tests passed;
There will be a support email for content related questions.
We have developed all the materials that would together compose a full-fledged online
course on GI, namely:
1 syllabus incl. a brief overview of the course; and
Written lecture scripts (7 sessions), including short exam/test quizzes for each
lecture, as well as recommended readings.
Aside from these materials, depending on the chosen MOOC hosting organisation, the
organisers may want to consider adding a final exam and certificate to acknowledge
the successful completion of the course.
The final MOOC materials can be found in Annex 7 under the name “MOOC GI”.
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2.3 “Train the trainers” workshops
This chapter provides summarised overviews of the two training workshops and
lessons learnt as regards their implementation. The material for each workshop has
been developed by a team of experts based on existing knowledge and preliminary
outputs of other tasks under this service contract so as to maximise the cross-feeding
of information material. It should be noted that the information has been specifically
tailored to match the events that the trainings were ‘hooked onto’. As such, they
cannot be replicated in the same manner elsewhere. However, much of the
information and presentations can be adjusted for new settings with relatively minimal
efforts, given the trainer team is aware of the context (e.g. country, sector, theme) it
needs to be tailored to.
2.3.1 Training on GI & Wetland Restoration in Budapest, Hungary
Workshop Summary
The workshop was fun, everyone seemed to have a good time, working in the role
play worked really well and the evaluation gave rise to some interesting cases and
examples some of the participants could provide.
We had about 18 participants, which allowed us to create three groups. As the room
was small, it would not have been possible to fit in more participants. The schedule of
the morning programme was very much delayed, so we only started after lunch, but
by merging some of the presentations and shortening the time for some of the
assignments, we could finish right on time (by the time the energy level dropped and
everyone got hungry).
Since the group consisted mostly of ecologists, the programme worked well. We did
not have to explain the concept of Green Infrastructure, but they were very much
interested in working with stakeholders. The session involved a mix of working and
listening; Kristin Faurest, external expert to the REC, gave an inspiring presentation
about multi-functionality after some intensive discussions within the groups, to give
some new insights.
Lessons Learnt
We provided an evaluation sheet and asked participants to give their opinion about
three parts of the workshop. The roleplay was evaluated in a short plenary moment.
Most participants’ feedback was positive; they know their own role as an ecologist, but
now had to think from a different perspective and negotiate with other stakeholders,
some of which may not be in favour of ‘all green’. As some of the participants said,
that was a very inspiring part of the workshop. Other reactions included the
observation that stakeholders need to be involved in the process, not only informed.
Especially the stakeholders that can provide financial or political support should not be
forgotten in the early stages of the process.
By the time the workshop took place, the factsheets were not yet finalised and
available in print. We provided a link to the digital set of factsheets. It is not clear how
many participants actually downloaded and used them.
Although the presentation was good and informative, the timing of the workshop
(right after lunch) and the crammed room made it difficult for some participants to
stay awake. Although we had planned a speed-date, the room did not allow for that.
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All workshop materials (presentations and photos) can be found in the accompanying
file under Annex 8 ‘Task 2 – Budapest Workshop Material’.
2.3.2 Training at the event ‘Implementation of the Strategy for Green
Infrastructure in Romania: Nature – our health our wealth’
Workshop summary
The workshop was held within the two-day conference “Implementing the Green
Infrastructure Strategy in Romania - policy and practice. The conference was
organized by Excelsior NGO in partnership with CEEweb for Biodiversity, supported by
the Arad Municipality and took place on 29-30th October 2015 in Arad City Hall.
The purpose of the conference was to promote the implementation of the EU Green
Infrastructure Strategy, and to identify the means of integrating the strategy into
national development plans, financing options and sectors including environment,
agriculture, forestry, transport and territorial development. The event was attended by
representatives of the European Commission, Romanian ministries and authorities.
Attendants had the opportunity to present their experience with respect to GI
implementation, exchange views and ideas on how to tackle challenges.
The sectoral workshop on green infrastructure implementation was designed to be in
line with the overall objectives of the conference. Specifically, the workshop aimed to
highlight the wider benefits of GI and stimulate a discussion on mainstreaming GI in a
number of sectors considering the Romanian context. The topics of the workshop
complemented other themes addressed during the conference such as: vision and
state of play of the EU Green Infrastructure strategy, financing GI and opportunities
for businesses, GI aspects in Romanian OPs for transport, CBC OP between Romania
and Hungary, etc. In addition, the workshop served as an opportunity to inform the
participants about the ongoing DG Environment contract on supporting the
implementation of the GI Strategy and how they can benefit from its outcomes and
deliverables.
Presentations
The presentation on mainstreaming GI into projects financed under ESI Funds (2014-
2020) was delivered by Venelina Varbova from the REC and outlined the linkages
between GI and the following policy areas: climate adaptation, transport, agriculture,
industry, energy. The important role of GI for job creation was also highlighted. The
presentation included a host of examples for different sectors that were mostly taken
from the sector factsheets prepared under the DG Environment contract on supporting
the implementation of the GI Strategy.
Kristin Faurest, external expert to the REC, gave a presentation on the multiple
benefits (social, ecological and economical) of Green Infrastructure. The presentation
also focused on GI as an integrated solution and highlighted the value of and
approaches to stakeholder mapping. Kristin Faurest also presented three European
green infrastructure case studies at the regional landscape, local institutional and
neighbourhood level: 1) Landscape Park Rems (Landscape Park Stuttgart Region); 2)
Miskolctapolca spa complex, Hungary; and 3) Ekostaden Augustenborg (urban
regeneration initiative), Malmö, Sweden. The examples provided further insight into
cross-sectoral cooperation, multidisciplinary approach, broad spectrum of benefits
designed to solve existing social, environmental and economic problems.
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The presentations were very well received by the participants and aimed to provide a
basis for the subsequent group break-out sessions.
Group break-out sessions
Due to the reduced number of participants three group break-out sessions were held
instead of the originally planned six. The participants were split into three groups, as
follows:
Green Infrastructure and adaptation to climate change;
Green Infrastructure and transport;
Green Infrastructure and agriculture.
The groups were asked to consider the following key questions:
What are the underused resources for GI development in Romania?
What are the opportunities and challenges?
Identify ideas for GI projects in Romania;
Identify opportunities for incorporating GI as a part of other projects.
As an output the groups were requested to formulate policy ideas for development of
GI in Romania. A representative of each of the working groups presented the
outcomes of the group work and discussions in plenary.
Working group: Transport and green infrastructure
Underused resources, opportunities and challenges with regards to GI and the
transport sector:
The underused resources for GI development are also opportunities.
Romania possesses rich diversity of nature, but this is not considered from the
transport point of view.
There is potential in integrating GI solution in public transport (e.g. introducing
green tram lines).
Local communities are not sufficiently engaged in GI development.
There is a need to build capacity of state administrations with regards to GI
opportunities and implementation.
There is a need to consider GI in local development plans.
There is a need for incorporating GI in transport master plans.
There is insufficient funding for GI solutions.
There is a need for better institutional cooperation with regards to applying GI
solutions in the transport sector.
Suggestions for policy improvement:
Mapping existing GI (ecological corridors);
Development of cycle network across borders;
Integration of GI into transport policy at national and regional level;
Analysis of the Impact of GI on the development of metro infrastructure, e.g. with
regards to underground water system, drainage, greening of metro stations;
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Provide sufficient institutional resources for the development of GI.
Working group: Agriculture and green infrastructure
Underused resources:
There is non-utilized agricultural land/structures (e.g. canals);
Much land is under small-scale biodiversity-rich and culturally valuable
cultivation;
The local products are not promoted enough;
Traditional landscapes and opportunities for tourism;
Heterogeneous landscape – allows for cultivating different types of crops.
Problems:
There is no access to financing for high quality products;
There is insufficient national financial support for product certification;
There is erroneous or lack of support for small-scale farmers;
Lack of farmers’ cooperatives/associations;
Depopulation of villages;
Invasive species on abandoned land.
Opportunities exist with regards to:
Agri-environmental schemes (eco-conditionality);
Greening agricultural practices;
Empowering local action groups;
Limiting excessive fertilization.
Suggestions for further interventions:
More investments in nature protection are needed.
There is a need to revive water mills and canals.
There is a need to develop short producers-buyers chains.
Support needs to be provided to learning farms.
There is a need to develop a database with information about local traditions.
Working group: Adaptation to climate change and green infrastructure
The following suggestions for policy actions have been outlined:
There is a need to stimulate biomass production and use.
There is a need to eliminate waste pollution from canals.
The focus should be on the implementation of the WFD.
Funding is needed for refurbishment of old buildings with focus on green
roofs/walls. Such funding can come from OPs or municipal budgets.
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There is a need to raise awareness about the linkages between GI and adaptation
to climate change.
Lessons learnt
Feedback on the quality of presentations, presented examples and facilitation of the
workshop was positive. The group discussion was lively, and the participants were
stimulated to think about GI development and what policy actions are needed to
address challenges and unlock potential for GI implementation in Romania. Some of
the ideas that resulted from the group work were quite innovative and could be further
developed in a future working session.
We understood that the wider benefits of GI are poorly understood among authorities
who are not dealing directly with nature conservation. The workshop was an
opportunity to raise their awareness of economic and social benefits that GI projects
deliver and the collaborative and multidisciplinary approach needed to achieve these
goals.
All workshop materials (presentations and photos) can be found in the accompanying
file under Annex 3 ‘Task 1.2 – Arad Workshop Material’.
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3 Task 3 – Improving information exchange mechanisms
Chapter summary
Green infrastructure (GI) is a successfully tested tool for providing ecological, economic and social benefits through natural solutions. GI helps to understand the value of the benefits that nature provides to human society and to mobilise investments to sustain and enhance them. It also helps avoid relying on infrastructure that is expensive to build when nature can often provide cheaper, more durable solutions. GI is based on the principle that protecting and enhancing nature and natural processes, and the many benefits human society gets from nature, are consciously integrated into spatial planning and territorial development. Compared to single-purpose grey infrastructure, GI has many benefits. It can sometimes offer an alternative, or be complementary, to standard grey solutions. GI has ties with agriculture, forestry, nature, water, marine and fisheries, regional and cohesion policy, climate change mitigation and adaptation, transport, energy, disaster prevention and land use policies. Further, GI information may range from content on policy, to costs and benefits of measures and very technical input serving designers and engineers. Also, GI-relevant information might vary in its format: e.g. maps, indicators, articles, web pages, published documents, etc. In this report, the current visibility of GI information on digital platforms of European policy sectors and other stakeholders has been evaluated. The availability of solutions for improving access to digital information on GI has also been addressed. Four subtasks have been distinguished in this work:
Exploring the current digital GI information landscape and identifying the policy sectors and stakeholder platforms that are relevant for disclosing GI information at an EU level. This included identifying priority policy sectors and stakeholders for which GI information should be available and identifying the linked communication and information exchange platforms. It also included describing what may be the ideal platform and how it could be implemented. Further, it was researched how the existing platforms are organized and how GI information could best be integrated and made available.
Evaluating the accessibility of GI information among a selection of eight platforms and the type of information available (such as data, indicators, maps, libraries, etc.). This assessment evaluated which GI content they provide or do not provide, whether its visibility can be improved from a GI perspective and whether the information available can be linked to BISE (the European Biodiversity Information System). This exercise led to recommendations on how to improve the content and visibility of GI information.
Determining the technical or governance requirements for implementing recommendations for a subset of three shortlisted platforms. The aim of this task was to provide a file for each of these three platforms, where a description of the technical specifications and properties for the platform are elaborated. After outlining the technical details, an analysis and proposal was made to conduct the necessary adjustments to receive data, process the data and finally publish the data targeted to the existing governance and technical processes. Proposals, processes, approaches and recommendations were discussed with the technical and administrating levels of the selected platforms, in order to asses and estimate the most suitable mechanisms and procedures for sharing GI relevant information.
Discussing with the representatives of the EU information systems to what extent the recommendations provided in the report can be implemented. With respect to content, deliverables of the other tasks within this contract, in particular outputs from tasks 1, 2 and 4, may allow for material being ready to use and available for being uploaded directly. It remains the responsibility of the respective services to actually upload and incorporate the information received.
The recommendations that were given are split over three time horizons:
Recommendations that can be implemented in the short term: i.e. can be realized during the duration of the contract;
Recommendations that can be implemented in the mid-term: i.e. can be initiated during the duration of the contract but will require final efforts shortly following the finalization of the contract; and
Recommendations that can be implemented in the longer term, i.e. recommendations which need to be aligned with the technicalities and governance the different platforms have (however, it is not a request to dig deep into the governance of the various platforms).
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For the first subtask, from a policy sector perspective, platforms were searched at the EU level relating to nature, water, climate, agriculture, health and consumers, disaster risk management, mobility and transport, and regional and cohesion policy. In addition, GI may be important to a variety of stakeholders that are either involved in working on infrastructure and design of open space or otherwise are users of open space. For the first group, stakeholder groups that will have large impact through their activities on the environments-we-live-in are landscape architects, building professionals and spatial planners. Focusing on the users of open spaces, relevant groups to consider are land owners, foresters, farmers, fishermen, hunters, nature NGOs and businesses. For each of the digital platforms that were identified, a brief description was provided of the available GI information. Next, for each of the platforms an evaluation was made of the GI information that is available. For platforms hosted by the European Commission’s policy sectors, the evaluation shows the relatively weak availability of GI information. The GI information that is available across the studied EC platforms is relatively dispersed and not presented in a coherent way. A common aspect for the reviewed platforms is that there is a lot of information that is highly relevant to GI but not defined and labelled as such. With respect to the available policy information, GI is only visible on a limited number of EC-related websites and platforms. Much progress therefore can be made by having the concept, its relevance for the sector and a link to the GI section on BISE integrated across the relevant policy sectors. Based on the stakeholder platforms that were evaluated, it was found that except CEEweb none of them qualifies as an information or knowledge sharing platform. It may be explored whether links can be made from BISE to CEEweb and vice versa. Next to CEEweb, FACE and WBCSD are best in class with limited but clear and inspiring information on GI. On some other platforms GI is mentioned, however very little could be retrieved. Also for those platforms that have related information (biodiversity, ecosystem services, nature- based solutions, etc.), the link to GI is made in some documents. However, GI is not included on these platforms in a dedicated manner. Altogether, the visibility of GI on platforms and websites at the EU scale of stakeholder groups for which GI is considered very much relevant can be considered poor. A future ‘ideal world’ could be one where GI visibility has increased substantially for a large selection of the platforms hosted by stakeholders. It is evident that if constructed appropriately, portals can positively contribute to distributing relevant information to the public and to various end-users. A major question is where to disclose information and how to make information accessible such that end-users can locate what they search for in a straightforward and easy way. Thus, the link has to be made between the “what” and “why” of information with the “where” and “how”.
Therefore, it is necessary to gain thorough insights in where end-users may be assisted by specific information.
Further, it has to be acknowledged that end-users will not necessarily look for GI related information from a GI perspective. Indeed, for example, a farmer may simply be looking for ways to diversify and thereby be aided by knowing that a GI focus can be one option.
Knowing which end-users may need GI-related information and understanding the online paths they may choose to reach that information can aid in providing the required information at the places where end-users are likely looking for it.
This concerns information available from various departments at the EU and the national level, but also the information provided at regional and local levels.
Different groups of end-users have very different ways in which they interact with GI and many of them will not be inclined or have a natural tendency to go and dig into technical information provided on a website dedicated to GI, for example under BISE.
The web portals they usually visit (for example about support to agriculture or industries) should point towards the websites providing relevant GI information.
For the second subtask eight platforms were selected to be explored in more depth and addressing which of the content that is presented or can be presented relates to GI. Also, we explored in more depth the accessibility and user friendliness of the platform in general and from a GI perspective more specifically for three of the eight platforms: BISE, NWRM and Climate-ADAPT. For each of the eight platforms, the analysis addressed the end-users and their expectations, what is available on GI and what is lacking, whether there is potential to connect across platforms and how to improve the visibility of GI.
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The following conclusions could be drawn regarding the three major platforms that were researched (BISE, NWRM and Climate-ADAPT):
With respect to BISE, although not labelled as such, most information of the BISE platform is highly relevant from a GI perspective as preserving biodiversity is an important result and building block of GI measures, because ecological networks are GI and because it concerns ecosystem services for delivering goods and services. One of the key conclusions from the analysis is that the GI relevant sections need to be made more visible, including through better labelling of the many sub-sections that have GI relevance. Moreover, by providing further interlinkages between the various GI-related sections, the usefulness of BISE for the end-users would increase, and a more holistic picture will be given. The platform hosts the nice feature of the GI library which has a lot of potential to be further developed into a rich source of information. The library, however, needs to be made more visible and accessible to be able to provide its full potential. There is a lot of GI relevant information available on BISE, but its coherence, visibility and user-friendliness needs to be improved. By structuring the information, increasing interlinkages, extending the integration of other GI platforms, BISE could become a good source of GI information. The GI information available should be extended to encompass policy aspects as well as greater depth with regard to the different GI options and measures that are available. These aspects need to be addressed before BISE can claim to be a user friendly, exhaustive source of GI knowledge in Europe.
NWRM (Natural Water Retention Measures) is all about GI. It is well-placed under WISE and only needs to be indicated on BISE with a link and short explanation. In other words, no integration into BISE is necessary and only a connection should be established. Considering the NWRM platform from a GI perspective, it could be improved by better introducing and integrating the GI concept and the strong supportive relationship of GI and NWRM, as this is currently missing. All information on the website is highly relevant to GI as NWRM per se are green infrastructure solutions. The information is however not labeled as such and the user might not be aware that this is in fact GI. This aspect should be given further attention to make the context clear for the end-users. Currently, there are not many linkages made to external sources, and it would be useful to have many more links to other GI platforms and sources of information. A technical challenge is how to integrate NWRM into WISE. The NWRM platform, which is entirely GI, could serve as inspiration for setting up/renewing other GI- related platforms such as BISE or the new platform on sustainable cities that will be organised. The structure of the measures section, and to some extent the case studies section, can be used as an illustrative example of how to create interlinkages within a platform and how it is making links to the relevant case studies, benefits etc.
In the context of climate, GI is among the most widely applicable, economically viable and effective tools to support climate change adaptation. The integration of GI into climate adaptation management, also called ecosystem-based adaptation, contributes to achieving the EU climate adaptation goals. The Climate-ADAPT platform contains a few references to GI, however not sufficiently to reflect its significance. A clear introduction of GI is missing. In its current state the few GI references are scattered across the platform. These aspects are making the GI relevant information on the platform difficult to locate resulting in a low usefulness for the user. The website contains knowledge which would be highly relevant to GI and that could provide useful information and guidance on sectors, measures, processes etc. relevant for GI, and in particular GI measures supporting climate adaptation. Presenting the GI concept in a visible and structured way is needed. The available information related to GI should be highlighted as GI relevant. It would also be important to increase the interlinkages across the platform to provide a fuller overview of GI and to help the user to find their way to the information. It would be beneficial to create a separate section on GI and adaptation which could present all these aspects in a coherent and visible way. These improvements would be necessary to establish links with other platforms, such as BISE.
Very specific recommendations have been made for the various platforms researched as well as more general recommendations for improving the online visibility of GI, including:
In the short-term, BISE should be developed into a GI information hub, while considering it will and should not be the only access point for GI knowledge. Therefore, it is a crucial aspect to decide on which GI information to make available through BISE, and which through other platforms (such as, for example, NWRM or Climate-ADAPT). For GI information disclosed through other platforms it requires attention to assure this to be connected to BISE such that it is accessible also for end-users that do access through BISE. In addition, there is a rather weak presence of both the term GI and the information that relates to GI across platforms linked to either the EC or to stakeholders. In fact, many platforms that can be considered as relevant do not contain any reference at all to the concept of GI. Much progress therefore can be made by having the concept, its relevance for the sector or stakeholder group and a link to the GI section on BISE integrated across the relevant policy sectors and stakeholder platforms.
In the mid-term, it was discussed that the ‘ideal’ future situation has GI information made available through the different websites/platforms linked to specific policy sectors/stakeholder groups. It will be important to consider end-user needs when deciding where to disclose which GI information. Another
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challenge is to connect the different sources available on the various platforms. For end-users, rather than having to search for GI information on various platforms, it may be beneficial to have user- relevant GI information become available through a single search or from a single page with convenient links to where other information is available. To improve user access to GI information, a search function in combination with a single repository where all GI related information is centralized, would be the most effective solution. However, the feasibility of this option is rather low, as it is very unlikely that all platforms involved would be willing to share all information in an agreed manner. This brings us to a long-term recommendation: machine to machine communication.
While most websites have some degree of structure, the language in which they are created, HTML, is oriented towards structuring textual documents rather than data. As data is intermingled into the surrounding text, it is hard for software applications to extract snippets of structured data from HTML pages. Linking data distributed across the Web requires a standard mechanism for specifying the existence and meaning of connections between items described in this data. "Structured data markup" is a standard way to annotate your content so machines can understand it. When your web pages include structured data markup, Google (and other search engines) can use that data to index your content better, present it more prominently in search results, and surface it in new applications like voice answers, maps, and Google Now. A more generic approach to making structured data available on the Web are Web APIs. Web APIs provide simple query access to structured data over the HTTP protocol.
As a final step, the analyses and recommendations made in this report were distributed to the responsible services of BISE, NWRM and Climate-ADAPT. In an iterative process it was explored with them how to succeed in implementing the recommendations that were made.
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Introduction
The overall purpose of this task report is to look for very pragmatic solutions for
improving the digital information sharing/presentation on green infrastructure (GI). In
short, solutions are needed for making relevant digital content on GI more visible.
Before further considering where GI information should be digitally present, we feel
the need to concisely consider what GI is. A challenge is that GI is not a sector and
that the language can be different in the various sectors where it is relevant. Indeed,
GI is a concept not easily defined, with broad ties to a variety of sectors and policy
fields (see BOX 1 and the glossary developed by the expert Working Group on Green
Infrastructure Implementation and Restoration (WG GIIR)10).
More specifically, GI has ties with agriculture, forestry, nature, water, marine and
fisheries, regional and cohesion policy, climate change mitigation and adaptation,
transport, energy, disaster prevention and land use policies. Therefore, GI information
may need to be dispatched through all these channels. In addition, GI information
may range from content on policy, to costs and benefits of measures and very
technical input serving designers and engineers. Therefore, GI information should not
only be present in a variety of disciplines, but also serve a variety of needs (decision
makers, designers, engineers, businesses, users, etc.). GI-relevant information may
also vary in its format: e.g. maps, indicators, articles, web pages, published
documents, etc. Considering the relevance of GI to a variety of sectors and
stakeholders, determining the most relevant sectors and platforms for providing
information on GI at the EU level needs to be prioritized.
At this moment there is a lack of a coherent availability of digital GI information to the
relevant stakeholders. Experience shows that clearing house mechanisms and other
means of experience sharing and information hosting are not dedicated to GI or the
relevant context has not been targeted towards the needs of GI stakeholders, and
therefore is only of limited use for GI implementation. Indeed, target groups which are
important for GI implementation in the field, such as land owners, project developers
and businesses, are only informed to a very limited degree about benefits and trade-
offs in using GI, ways to get GI measures approved and implemented, funding
possibilities, etc. Therefore, the European Commission aims to better integrate GI-
relevant issues into existing or planned platforms visited by stakeholder groups. In
this context it is relevant to note that there will not be a central repository where all
GI information will be available. The aim is to identify the different repositories that
are available (i.e. locating the main GI information on a European scale today) and
connecting these.
10http://ec.europa.eu/environment/nature/ecosystems/docs/green_infrastructures/GI%20webpage%20glos
sary.pdf
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Box 1 What is GI?
Many definitions of GI have been developed11. In its 2013 Green Infrastructure strategy12, the European Commission defines Green Infrastructure as “a strategically planned network of natural and semi-natural areas with other environmental features designed and managed to deliver a wide range of ecosystem services. It incorporates green spaces (or blue if aquatic ecosystems are concerned) and other physical features in terrestrial (including coastal) and marine areas. On land, GI is present in rural and urban settings.”
In addition, many countries may have had a form of GI in place for many years, but do not label it ‘GI’ or see the need to evaluate it as such. For example, in their report on the design, implementation and cost elements of GI, Naumann and colleagues13 found that out of the 127 GI initiatives that they assessed only 20% explicitly identified themselves as GI. In the report, GI is defined as the network of natural and semi- natural areas, features and green spaces in rural and urban, and terrestrial, freshwater, coastal and marine areas, which together enhance ecosystem health and resilience, contribute to biodiversity conservation and benefit human populations through the maintenance and enhancement of ecosystem services. GI can be strengthened through strategic and coordinated initiatives that focus on maintaining, restoring, improving and connecting existing areas and features, as well as creating new areas and features. Further, many initiatives might cover specific purposes (e.g. re-connecting areas with high biodiversity values, restoring riparian forests to protect against floods, promoting green roofs in cities for water retention, planting hedgerows in agricultural areas for landscape enhancement/pollination/erosion control/preventing floods …). They do not, however, fully consider its many benefits for other sectors and citizens, which the very same structure could offer if properly planned and managed. The multi-purpose character of GI therefore is in these instance not acknowledged or communicated.
Owing to its multifunctionality, there is no single science or discipline responsible for GI14. The nearest integrative scientific discipline accountable for its evolution is ‘landscape planning’. GI relies on the theories and practices of numerous scientific and land planning professions, such as conservation biology, landscape ecology, urban and regional planning, geographic analysis, information systems and economists.
GI is widespread in spatial scales as its application can range from individual buildings to neighborhoods and cities to entire regions, even across countries (see Natura 2000 network or European Green Belt). Further, benefit groups are also different at the respective scale of consideration: e.g. carbon storage by peatlands has beneficiaries worldwide; whilst the water retention function of the same peatland is felt locally.
The features or elements are not always simple to define and descriptions of GI can change depending on the stakeholder15.
Related terms are landscape planning, natural infrastructure (US nomenclature), nature-based solution, ecosystem services, natural capital, etc. among many others.
Given the wide span of definitions of GI, and the wide range of the components and parts of the GI, we may define GI as the spatial structure delivering multiple ecosystem services, which might include 'grey' or hybrid elements (such as green roofs or fauna passages).
Through the adoption of the Green Infrastructure strategy in 2013, the common understanding of
terminology and purpose of GI has made significant progress. However, the need for information sharing and communicating about Green Infrastructure will probably go up along with the increased deployment of GI in the EU.
11 Green Infrastructure and territorial cohesion. European Environment Agency (2011). Technical Report No 18/2011. See also http://ec.europa.eu/environment/nature/ecosystems/docs/Green_Infrastructure.pdf 12 http://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:52013DC0249 13 Naumann, S., McKenna D., Kaphengst, T. et al. (2011). Design, implementation and cost elements of Green Infrastructure projects. Final report. Brussels: European Commission. 14 Benedict, M.A. & McMahon, E.T. (2002) Green Infrastructure: Smart Conservation for the 21st Century. Renewable Resources Journal. 20(3: 12-17. 15 Horwood, K. (2011) Green infrastructure: reconciling urban green space and regional economic development: lessons learnt from experience in England’s north-west region. Local Environment 16(10):963-975.
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3.1 Problem analysis and objectives of Task 3
As introduced, the goal of task 3 is to look for very pragmatic solutions for improving
the digital information sharing/presentation of GI. Task 3 consists of four parts. It
concerns (1) identifying platforms and selecting the most useful ones, (2) evaluating
the potential for increasing GI visibility among selected platforms, (3) making
recommendations for improving GI visibility, and (4) making progress towards having
recommendations for the main European-level information systems implemented by
the responsible services, facilitated by technical assistance given by this contract. A
more detailed description of these four subtasks is provided below:
1. Exploring the current digital GI information landscape and identifying the
policy sectors and stakeholder platforms that are relevant for disclosing GI
information at an EU level.
a. Identify priority policy sectors and stakeholders for which GI
information should be available and identify the linked communication
and information exchange platforms.
b. Consider what platform may be ideal and how to implement it, and
then consider how to work with what is available. Which platforms are
there, how are they organized, and how can GI information be best
integrated?
2. Assessing for a selection of eight platforms how accessible the GI information
is and what sort of information is available (such as data, indicators, maps,
libraries, etc.). Specifically, it will be evaluated which GI content they provide
or do not provide, whether its visibility can be improved from a GI
perspective and whether the information available can be linked to BISE16
(see BOX 2). This exercise will lead to recommendations on how to improve
content-wise the visibility of GI information. Note, however, that the analysis
of this set of eight platforms does not include evaluating what the
implementation of recommendations requires from a technical or governance
perspective.
3. For three of the eight selected platforms, this last step will be undertaken;
for each of the recommendations given, the technical or governance
requirements for their implementation will be evaluated. The aim is to
provide a file for each of these three platforms where a description of the
technical specifications and properties for the platform will be elaborated.
After outlining the technical details, an analysis and proposal will be made to
conduct the necessary adjustments to receive data, process the data and
finally publish the data targeted to the existing governance and technical
processes. Proposals, processes, approaches and recommendations will be
discussed with the technical and administrating levels of the selected
platforms, in order to asses and estimate the most suitable mechanisms and
procedures for sharing GI relevant topics. This will result in the development
of an implementation file including a roadmap, technical advice,
recommendations on budget needed, entry points, web design and risks.
4. It will be discussed with the owners of the EU information systems to what
extent the recommendations provided in the report can be implemented.
With respect to content, deliverables of the other tasks within this contract,
in particular outputs from tasks 1, 2 and 4, may allow for material being
16 http://biodiversity.europa.eu/
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ready to use and available for being uploaded directly. It remains the
responsibility of the responsible services to actually upload and incorporate
the information received.
The recommendations will be split over three time horizons:
Recommendation can be implemented in the short term: i.e. can be realized
during the duration of the contract;
Recommendation can be implemented in the mid-term: i.e. can be initiated during
the duration of the contact but will require final efforts shortly following the
finalization of the contract; and
Recommendation can be implemented in the longer-term, i.e. recommendations
which need to be aligned with the technicalities and governance the different
platforms have (however, it is not a request to dig deep into the governance of
the various platforms).
Box 2 BISE – the Biodiversity Information System for Europe
The “Biodiversity Information System for Europe” (BISE), a portal owned by DG Environment and hosted by the EEA, has the objective to provide a single entry point for accessing the best available information to support the implementation of the EU 2020 Biodiversity Strategy and the CBD Strategic Plan for Biodiversity 2011-2020. The main focus of this integrative platform is to better integrate available outcomes from reporting and monitoring from different sources and consolidate the knowledge base for biodiversity-related policies in Europe in a coherent and co-ordinated way. The general objective of BISE is not to duplicate but to integrate and upgrade existing tools and develop new ones as necessary to be shared within the EKC. In short, the aim of BISE is to 'strengthen the knowledge base in support of the implementation of the EU Biodiversity Strategy to 2020'. The system is following and implementing the principles of the 2007 EC Directive establishing an Infrastructure for Spatial Information in the European Union (INSPIRE)17 as well as the 2008 EC Communication concerning a Shared Environmental Information System (SEIS)18. It integrates any relevant content from Environmental Data Centres19 as defined in the EU Environmental Data Centre (EDC) arrangement. Interoperability with thematic data centres and similar portals supporting requirements under other environmental legislation (e.g. WISE20, Climate-ADAPT21) is a main goal to be achieved by 2018. BISE is a partnership between the European Commission DG Environment - Directorate B and the European Environment Agency, supporting the knowledge base for the implementation of the EU 2020 Biodiversity Strategy. It also serves as the Clearing-House Mechanism for the EU within the context of the United Nations Convention on Biological Diversity (CBD) and as such it is supported by the collaboration of the European CHM network and the CBD Secretariat. BISE is a process. Its content and services are being developed in collaboration with key users and information providers so that it meets the information needs of the EU Biodiversity Strategy to 2020 and of the global Aichi Targets. BISE will facilitate the integration of facts and figures on biodiversity, ecosystems and ecosystem services, making links to related policies, interconnecting with environmental data centres, supporting harvesting assessments and research findings from various sources. More generally, it will contribute to strengthening the knowledge base for biodiversity policy and better informed decision-making on biodiversity. The BISE website is complemented by the so called BISE-Catalogue. This catalogue hosts a dedicated library on GI with currently 230 documents being online that can be searched through free search or e.g.
17 Directive 2007/2/EC of the European Parliament and of the Council of 14 March 2007 establishing an Infrastructure for Spatial Information in the European Community (INSPIRE) http://eur- lex.europa.eu/JOHtml.do?uri=OJ:L:2007:108:SOM:EN:HTML http://www.ec-gis.org/inspire/home.html 18 Communication from the Commission to the Council, the European Parliament, the European Economic and Social Committee and the Committee of the Regions - Towards a Shared Environmental Information System (SEIS) COM/2008/0046 final. 19 http://biodiversity.europa.eu/data 20 http://water.europa.eu/ 21 http://climate-adapt.eea.europa.eu/
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language/country options. Even if this tool is accessible and usable, it is not fully operational now. Currently BISE is organising information under six main entry points:
1. Topics: state of species, habitats, ecosystems and their services, genetic diversity, threats to biodiversity, impacts of biodiversity loss, policy responses;
2. Policy: policy, legislation and supporting activities related to EU directives, EU biodiversity policy developments, pan- European and global policy frameworks;
3. Data: data sources, statistics and maps related to land, water, soil, air, marine, agriculture, forestry, fisheries, tourism, energy, land use, transport;
4. Knowledge: important EU-wide research projects or peer-reviewed literature related to biodiversity and ecosystem services, improving the science-policy interface;
5. Countries: national biodiversity reporting activities and information; country profiles based on officially published and regularly updated information from Member States;
6. Networks: sharing by networks across national borders. Under the umbrella of the entry point ‘Topics’ a thematic part of BISE is dedicated to Green Infrastructure: http://biodiversity.europa.eu/topics/green-infrastructure Next to the topic section, information on GI is also available through the 'policy' section, Biodiversity Strategy (there through information on Target 2 in general and on Action 6b in particular).
3.2 The digital GI information landscape
3.2.1 Policy sectors
To answer the question of which digital platforms GI information is or should be
available we need to identify the policy areas which might be relevant in relation to
GI.22 The following may be possibly relevant areas, although this list is not exhaustive
and other areas (for example the area of biodiversity and businesses) can also be
considered:
Agricultural policy with the Common Agriculture Policies (CAP) and its funding
possibilities;
Forestry policy with the Forest Action Plan;
Biodiversity & Nature with the EU 2020 Biodiversity Strategy, the Birds and
Habitats Directive and the Life+ programme;
Water policy with the Water Framework Directive, the River Basin Management
Plans, the Floods Directive, the EU Drought policy, the EU water Blueprint;
Soil policy and the protection of soil;
Climate change policy with the 2050 Low Carbon Roadmap and the programme to
adaptation;
Territorial Cohesion and innovative financing with the regional or cohesion policy
and examples such as the EU Strategies for the Danube Region and for the Baltic
Sea Region;
EU 2020 & Resource Efficiency Flagship: EU 2020 Strategy and Resource
Efficiency Flagship under EU 2020;
Transport & Energy: TEN-T, TEN-E, energy policy, Connecting Europe Facility;
Impact assessment and damage prevention and remediation: EIA and SEA
Directives, Environmental Liability Directive;
Spatial planning: European Spatial Development Perspective, ESPON 2013
Programme, Urban Strategy, Territorial Agenda of the EU 2020;
22 See also: http://ec.europa.eu/environment/nature/ecosystems/studies.htm#implementation
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Marine and coastal zones policy: Marine Strategy Framework Directive, Fishery
policies, EU Maritime Spatial Planning Communication;
Environment & Health: Environment and Health Action Plan 2004-2010;
Research Policy/ Horizon 2020, Framework programme for research and
innovation;
EC external development cooperation.
To further build on this, the European Commission indicated in a communication23 to
the Parliament and the Council “that GI can make a significant contribution in the
areas of regional development, climate change, disaster risk management,
agriculture/forestry and the environment. For promoting GI in the communication,
focus was made on the following main policy areas through which GI should be
promoted: regional or cohesion policy, climate change and environmental policies,
disaster risk management, health and consumer policies and the Common Agricultural
Policy, including their associated funding mechanisms”.
From a policy sector perspective, in our analyses on where GI information is or should
be available we therefore focussed on searching for platforms at the EU level (EC
websites and related agencies) for the following eight themes:
1. Nature-linked platforms such as biodiversity, forest, marine, Natura 2000
2. Water-linked platforms
3. Climate adaptation linked platforms
4. Agricultural linked platforms
5. Health and consumer linked platforms
6. Disaster risk management linked platforms
7. Mobility and transport linked platforms
8. Regional or cohesion linked platforms
In what follows, for each of these eight themes we report our findings on the selected
platforms and provide a brief description of the available GI information. Next, for
each of the platforms we have made an evaluation of the GI information that is
available, its accessibility and its usefulness towards end-users (see 3.3).
Policy sector priorities and identified related EC platforms
A. Nature-linked platforms:
DG Environment GI24: The DG ENV GI site gives a good introduction to GI from a
policy perspective. The policy context is described well and links are provided to
the EC communication on GI. The information on the website is nevertheless brief
and there is limited practical information on economic and technical aspects etc.
However, further information can be found through available links to a number of
relevant studies. The reports and studies include best practice examples. The site
also provides links to other EC websites, e.g. the DG ENV biodiversity site,
CIRCABC and BISE. Maps and standards and classifications are for instance
available through a link to the BISE platform. No specific information for the
different relevant audiences is available. On 06/08/2015 the DG ENV GI web site
has been updated, in particular the conference section, new study uploads,
working groups, better links to climate adaptation, research, water policies and
23 http://eur-lex.europa.eu/legal-content/EN/TXT/?uri=CELEX:52013DC0249 24 http://ec.europa.eu/environment/nature/ecosystems/index_en.htm
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business/financing possibilities such as the B&B/NCFF. It is recommended to
transfer all knowledge-based information from this webpage to BISE (the DG ENV
web page should be limited to policy-relevant information) once BISE is fully
operational (see also 3.5.1).
EC CIRCABC website25: The CIRCABC website library on GI provides a range of
information giving a general introduction to GI, the policy framework, best
practice examples as well as information on financing.
European Environmental Agency26: There is no specific section for GI on the EEA
website. The existing GI information is scattered and can be found under various
sections such as land use, biodiversity, agriculture, urban environment.
Information relevant to GI is in many cases not labelled as such. Three reports on
GI have been produced by the EEA containing some policy background: Exploring
nature-based solutions — The role of green infrastructure in mitigating the
impacts of weather- and climate change-related natural hazards (September
2015); Spatial analysis of green infrastructure in Europe (2014); and Green
infrastructure and territorial cohesion (2011).
BISE27: The amount of GI information on this platform is rather disappointing.
There is a separate section on GI, organized under ‘Topics’ where a definition and
background is provided. The policy context is briefly described and links are
included to a number of policy studies. There is no practical information regarding
GI technical standards. No specific information for the different relevant
audiences. Some of the data on the platform such as the implementation of the
Biodiversity Strategy would be relevant from a GI perspective (e.g. the MAES
data) but this information is not linked from the GI section of the BISE. Existing
and new information can be uploaded on the BISE GI section but it has to be
further linked to other existing tools to guarantee the best use of existing
knowledge sharing possibilities. There is a GI library in the BISE catalogue, but it
is relatively hidden for the user and not easily found as it is not linked from the GI
section.
FISE - the Forest Information System for Europe28: This is a good source of
information on GI in terms of nature connectivity. There is a subsection dedicated
to 'Patterns and Fragmentation' which is directly linked to GI, although not
labelled as such. GI is mentioned in the text. Links are provided to EC GI
strategy. Models (one developed by JRC themselves), indicators and maps for
connectivity assessments are available. Links to examples from MS and relevant
projects are also provided. Information with regards to GI connectivity related to
CAP and WFD is available.
Natura 2000 Communication Platform29: No information on GI. A link is provided
to BISE and to the Eionet platform on biodiversity.
B. Water-linked platforms:
WISE30: There is no GI information available.
NWRM31: Natural Water Retention Measures (NWRM) are measures representing
GI in the water sector, and the website is therefore highly relevant and contains
25 https://circabc.europa.eu/w/browse/76df6314-a37c-4cc9-9fc6-2d9c9d6889fe 26 eea.europa.eu/ 27 http://biodiversity.europa.eu/topics/green-infrastructure 28 http://forest.jrc.ec.europa.eu 29 http://ec.europa.eu/environment/nature/natura2000/platform/index_en.htm 30 http://water.europa.eu/ 31 http://www.nwrm.eu
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valuable information in terms of water related GI. There is no easily accessible
link to information on the fact that NWRM are GI. That being said, the definition of
GI is included in the glossary (http://nwrm.eu/node/3835) and also when doing a
search of GI the concept appears in a number of search results. The website
contains rich information with regards to the policy framework, selection, design
and implementation of measures, a wide catalogue of possible measures (ID
cards). The ID cards are a way of presenting the measures in a synthesised way
but the catalogue of measures online has a lot of information which can be also
downloaded in pdf. The catalogue of measures includes information on biophysical
impacts, ecosystem services, how the measures impact the achievement of
different policy objectives, financing, costs, design and governance aspects. The
website also includes 125 case studies. This information is available directly on
the website and more extensively in the online guidance, ID cards of the
measures and synthesis documents. The platform is linked to a Linkedin
discussion group.
OURCOAST - the European portal for ICZM32: No specific information on GI. There
are a number of case studies related to green and blue infrastructure available in
the database, searchable by themes, key approaches or free text. New
information and case studies can be uploaded to the website. There is a link to
the ICZM Assistant which is an online tool supporting project leaders, policy
makers and water professionals to integrate the ICZM principles in projects and
plans. A number of case studies and documents are available in the ICZM
assistant, although not directly labelled as GI.
C. Climate adaptation linked platforms:
Climate-ADAPT33: There is no specific section on GI and the available information
is relatively sparse. However, the concept and the term is mentioned briefly on a
few occasions with regards to 'Cities and towns' and 'Urban adaptation support
tool'. Although very little information is labelled as GI, the platform is highly
relevant and provides useful information and guidance on sectors, measures,
processes etc. relevant for GI, and in particular GI measures supporting climate
adaptation. A number of adaptation options presented can be linked to GI, such
as green roofs, green spaces and corridors, riparian buffers etc. The tools
presented have information on cost-benefit, legal aspects, success factors etc. A
link to the EC communication on GI is available. Link to best practice on green
and blue infrastructure (Grabs project) is available. New information could be
uploaded to Climate-ADAPT for users with EIONET account. It was discussed with
the responsible services that next to Climate-ADAPT there is also Mayors Adapt
(http://mayors-adapt.eu/). However, it was indicated by the responsible services
that this is intended to be more of an outreach website than a platform,
wherefore it was decided not to be included in the review under the current task.
D. Agricultural linked platforms:
CAP for our roots/ DG Agriculture and Rural development34: No information on GI
and no suitable knowledge sharing platform could be located other than the EC
website. However, there are more potential places where GI could possibly be
made visible. The role of agriculture in GI should be recognised and further
enhanced within the CAP. Agriculture can, for example, assist in watershed
management, the protection of habitats and biodiversity as well as in the
32 http://ec.europa.eu/ourcoast/index.cfm?menuID=3 33 http://climate-adapt.eea.europa.eu/home 34http://ec.europa.eu/agriculture/cap-for-our-roots/index_en.htm and http://ec.europa.eu/dgs/agriculture/index_en.htm
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maintenance and restoration of multifunctional landscapes. With regards to DG
Agriculture and Rural development platform, GI could be highlighted in the policy
areas (especially the section on Agriculture and Environment, Forest Resources,
and Rural Development), the monitoring and implementation of the ecological
focus areas (where the Green Infrastructure Strategy should be taken into
account).
Rural Development Gateway 2014-2020, European Network for Rural
Development35: The platform contains information such as the policy background
and support to ecosystems within RDP programming and implementation. There is
no direct information on GI. There is a section on forestry which includes
information on the multifunctional role of forests and the section Environmental
Services also has relevance and provides several useful documents on Delivering
Environmental Services using Rural Development Policy. Some of the priorities
(Especially priority 3: Ecosystems), related measures and thematic information
sheets of the RDP have some relevance to GI but it is not clear from the
information provided on the platform. There is a database with RDP projects, but
it is difficult to find any GI related information there. This section could potentially
include much more information on GI. For instance GI could be highlighted among
the Focus Areas, examples of RDP implementation and in the theme of
Environmental Services. In addition, it would be relevant to include GI as a key
word in the searchable project database.
E. Health and consumer linked platforms:
EC Public Health Website36: No information on GI and no suitable knowledge
sharing platform could be located other than the EC website. The contribution of
GI to human health is a beneficial outcome that results from the healthy
functioning of ecosystems. Ecosystems provide a variety of services which
promote basic human survival, for example, by limiting the spread of disease or
reducing air pollution but also in terms of improving general wellbeing and quality
of life by e.g. improving the access to green areas in urban environments
benefitting both individuals and communities. With this background, it would be
relevant to include GI in the section on Health in society/healthy environments.
European Food Safety Authority37: No information on GI and no suitable
knowledge sharing platform could be located other than the EC website. Food
production is an important component of green infrastructure and can provide
opportunities e.g. through urban food production, multi-purpose farms and how
innovative food production methods can benefit the natural landscapes. Reference
to GI would therefore be relevant to include in the food related EU platforms.
EC Food Safety Website38: No information on GI and no suitable knowledge
sharing platform could be located other than the EC website.
F. Disaster risk management linked platforms:
Disaster risk management portal39: The purpose of the portal is to provide a
collaborative working space for JRC and its partners in the field of Disaster Risk
Reduction (DRR). There is no information related to GI. GI has vast potential for
alleviating disaster risks such as floods, landslides, avalanches, forest fires and
35 http://enrd.ec.europa.eu/en/policy-in-action/cap-towards-2020/rdp-programming-2014-2020 36 http://ec.europa.eu/health/index_en.htm 37 http://www.efsa.europa.eu/ 38 http://ec.europa.eu/food/safety/index_en.htm 39 http://drr.jrc.ec.europa.eu/
Supporting the Implementation of Green Infrastructure
May 2016 50
droughts which are threatening infrastructure, cost human lives and are the cause
of billions of EUR of damage each year in the EU. GI solutions that boost disaster
resilience of infrastructure form an integral part of the EU policy on disaster risk
management. It would be beneficial to have a better visibility of the benefits GI
has on disaster risk management, as well as information on various GI options
and measures for disaster preventions and it would therefore be advised to
include information and links to GI information from the EU’s portal. This could be
done, for example, by providing a link not only to BISE but also to the Climate-
ADAPT and NWRM platforms as they are strongly linked to risk management
where GI plays an important role. In this context, it would also be relevant to
make a link to the recent EEA report “Exploring nature-based solutions — The role
of green infrastructure in mitigating the impacts of weather- and climate change-
related natural hazards.”40
G. Mobility and transport linked platforms:
DG Mobility and Transport41: No information on GI and no suitable knowledge
sharing platform could be located other than the EC website. GI is an important
instrument for the overarching goal of European transport policy: to reduce the
carbon footprint of transport, mitigate the negative effects of land uptake and
fragmentation, and boost opportunities to better integrate land use, ecosystem
and biodiversity concerns into policy and planning. Avoiding or mitigating the
fragmentation impacts of transport infrastructure on nature is a well-established
GI strategy in the transport sector. Fragmentation of nature networks may be
minimised by choosing specific GI design solutions, e.g., tunnels, or viaducts
which minimise land-take or by allowing watercourses, including natural banks, to
continue under the structure. Developing GI adjacent to infrastructure has the
potential to deliver many ecosystem services. Against this background, it is very
relevant to include a short introduction and links to further readings on GI and its
links to the transport sector on the DG platform on Mobility and transport. A link
should therefore be made to the BISE platform where additional information is
available.
H. Regional or cohesion linked platforms:
InfoRegio42: No direct information on GI. There is one Thematic Guidance Fiche
on biodiversity, green infrastructure, Ecosystem Services and Natura 2000 and
one Guide for investments in Nature and green infrastructure available. The policy
learning database includes one project example on GI.
DG Environment Urban Environment43: No information on GI. There is one link to
an EC report on peri-urban natural spaces which has some GI relevance.
Reference Framework for European Sustainable Cities44: Online toolkit designed to
help cities promote and enhance their work on integrated sustainable urban
development. It offers practical support in integrating sustainability principles into
local policies and actions. The full version is not available to view for unregistered
users. No specific GI information seems to be available. Show-case examples are
available to view, but only few of them are relevant.
40 http://www.eea.europa.eu/publications/exploring-nature-based-solutions-2014 41 http://ec.europa.eu/transport/index_en.htm 42 http://ec.europa.eu/regional_policy/en/ 43 http://ec.europa.eu/environment/urban/home_en.htm 44 http://app.rfsc.eu/
Supporting the Implementation of Green Infrastructure
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Evaluation of GI on EC-related platforms
In our evaluation of the aforementioned platforms we compared the current digital GI
information availability with the GI information that would ideally be available in the
future for each of the identified platforms.
In doing so we have distinguished six different sorts of GI information that may serve
different end-users and purposes:
1. GI policy aspects
2. GI technical aspects (data, maps, standards)
3. GI economic aspects (cost/benefits, funding)
4. GI methodological and implementation aspects
5. Best practices and lessons learned
6. Network and discussion groups
For each of these six sorts of information we scored the current presence of GI and
the ‘ideal world’ future disclosure of GI information on a scale of green, orange or red:
Green: information is available and substantial;
Orange: information is available, however, basic; and
Red: information is not available or very limited.
In addition, each of the platforms/websites were scored for its usefulness for
stakeholders/target groups:
Green: information is available and substantial, high usefulness;
Orange: information is available, however, basic; and
Red: information is not available or very limited, low usefulness.
White: not applicable, considering the absence of GI information.
A last scoring of the platforms/websites was for the accessibility of the GI information:
Green: information easily found on front page or after one-two clicks;
Orange: information found after several clicks; and
Red: information difficult to find.
White: not applicable, considering the absence of GI information.
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Table 2- Evaluation of GI on EC-related platforms
Platform
P o li c y
T e c h n ic
a l
E c o n o m
ic
M e th
o d o lo
g ic
a l
B e s t
p ra
c ti c e s
N e tw
o rk
P o li c y
T e c h n ic
a l
E c o n o m
ic
M e th
o d o lo
g ic
a l
B e s t
p ra
c ti c e s
N e tw
o rk
DG Environment GI
EC CIRCABC website
European Environmental Agency
BISE
FISE
Natura 2000 Communication Platform
DG Environment Urban Environment
WISE
NWRM
OURCOAST - the European portal for ICZM
Climate-ADAPT
CAP for our roots
EC Public Health Website
European Food Safety Authority
EC Food Safety Website
Disaster risk management portal
DG Mobility and Transport
European Network for Rural Development
InfoRegio
Reference Framework for European Sustainable Cities
U s e fu
ln e s s
A c c e s s ib
il it y
GI information 'Ideal world'GI information current situation
Interim conclusions
In this section an interim conclusion is made on how the visibility of GI information
can be improved for the platforms and websites explored. For DG Environment GI,
BISE, WISE/NWRM, Climate-ADAPT and the sustainable cities platform we refer to the
section ‘Increasing GI visibility for selected platforms’, where a more in-depth analysis
will be done for these platforms. For the DG Environment part of the website
dedicated to GI, the aim of the European Commission is to have only policy relevant
GI information being provided here. All other GI information should be moved to BISE.
This is also considered in the next section of this report.
From Table 2 it is obvious that the “ideal world” and the current situation on GI
disclosure in the various platforms are very much dissimilar. In what follows we
comment on the potential of increasing GI disclosure for the websites/platforms that
were evaluated:
1. Table 2 shows the relatively weak availability of GI information on the analysed
platforms. Many platforms, that can be considered as relevant, do not contain
any reference at all to the concept of GI such as WISE and the Natura 2000.
2. The GI information that is available across the studied EC platforms is relatively
dispersed and not presented in a coherent way. A common aspect for the
reviewed platforms is that there is a lot of information that is highly relevant to
GI but not defined and labelled as such.
3. With respect to the available policy information, GI is only visible on a limited
number of EC-related websites and platforms. The current available information
is relatively scattered, and in principle only DG ENV can be considered to have
the policy aspect appropriately covered (this would be ok, but then appropriate
links should be provided).
4. Much progress therefore can be made by having the concept, its relevance for
the sector and a link to the GI section on BISE integrated across the relevant
policy sectors. The policy aspects would deserve to be briefly explained on all
Supporting the Implementation of Green Infrastructure
May 2016 53
EC catered platforms that were researched here, this at least with a link
directing the user to more information. More restricted it could be done only for
these platforms/websites that in Table 2 are marked green for the “ideal world”
situation. Ideally this would be done in a language and vocabulary that
considers the specific sector. Exactly this approach was taken under Task 1 of
this contract where factsheets were produced on the GI relevance for a variety
of sectors. Next steps therefore would include identifying who to contact for
reaching GI disclosure through the EU websites/platforms on sectors such as
agriculture, health and consumer, mobility and transport, and disaster risk
management.
5. Across DG ENV linked platforms by the EC and the related agencies again there
is much potential for improving GI visibility. For example, typically these
platforms have much information on nature and biodiversity for example in a
Natura 2000, forest, or marine context. However, in many instances it is not
made explicit that this information links to GI and is GI relevant. One example
is the NWRM website which is all about GI but which is not immediately
apparent or clearly highlighted on the website. This makes the knowledge
search on GI difficult for the end-users and also risks that a lot of useful
information for the GI stakeholders is left unseen. Therefore, with an ambition
to having GI becoming a more used vocabulary and its linked information
becoming more broadly and widely disclosed much can be done on platforms
and websites within the immediate reach by DG ENV. For example, for FISE
information under ecosystem services can be indicated to be GI relevant and
GI visibility could be improved by more strongly labelling GI relevant
information, potentially even including a dedicated section on the platform to
GI (cf. the BISE example).
6. The CIRCA website provides a good collection of relevant GI literature sorted
under different categories. This source should be used when further developing
the GI library on the BISE catalogue. The resources available on the CIRCA
website should be cross-linked (integrated) with the GI library, ensuring that
the GI library contains all GI information produced in the EC framework up to
date. Meanwhile, all relevant documents of the CIRCABC library have been
transferred to the BISE GI library, wherefore it has become obsolete and is not
updated anymore. It remains a possibility that a section with restricted access
will be kept active on CIRCABC to allow to share 'grey literature' and non-
official or sensitive information. The CIRCABC site also hosts publically
available information of the Working Group on Green Infrastructure
Implementation and Restoration.
7. A methodological problem with CIRCABC was its strict hierarchical order, i.e. no
cross-links for documents covering more than one topic was possible. When
moving the information towards the BISE library, the documents 'lost' their
attribution to a topic as it is using a 'google-style' search engine. However, all
documents are indexed/tagged and key terms are indicated, which could make
up partly for this loss (this means that if a document is tagged as relevant for
'forest', a search through the free search field with 'forest' will list all GI-
relevant documents which either contain the term 'forest' in its text or have
been tagged as forest-relevant, even if the term 'forest' does not appear in the
document itself).
8. The available information on technical, economic and methodological aspects is
poor. This is catered for only by the EC CIRCAB library and to some extent by
the NWRM, which however only cover water related GI measures. For NWRM
the entry point is on water retention but there are many measures (53) that
initially one would not think have an effect in water resources, or which would
Supporting the Implementation of Green Infrastructure
May 2016 54
be just categorised as GI with little information on the impacts on water. There
are 13 measures for example for the agricultural sector with information on
costs. These aspects should also be better covered and it should be indicated
and linked on the key platforms where further information could be found.
9. Further use of best-practices would be important across the platforms as a way
to provide real life examples on implementation and inspiration for selection of
measures etc. This is an aspect that would be needed for most of the thematic
platforms. There are already a significant number of case studies spread out
over the analysed platforms. These should be interlinked and a best
practices/case studies on GI catalogue could be built in the framework of the
GI catalogue with options for detailed filtering according to the users need. I.e.
Climate-ADAPT would have a link to the climate change adaptation relevant
case studies.
10. The accessibility of the GI information on the reviewed platforms is in general
not particularly good. As mentioned, GI is often not placed in a central place on
the homepage. Rather, the information can be found a number of clicks away.
This is the case, for example, on BISE. The GI information is there, but it is not
immediately apparent to the user. The situation is worse on Climate-ADAPT
where the user has to search closely to be able to find the available GI
information.
11. There are only a few available networks for GI stakeholders. Except the
working groups relating to NWRM the others are not facilitated through
platforms. One workgroup was set up to contribute to the development of a
European Green Infrastructure policy (2011) and provided concrete
recommendations. The revised Working Group on Green Infrastructure
Implementation and Restoration (2014) will develop documents supporting
Green Infrastructure in particular on national and regional levels. Further, there
is a dedicated discussion group on LinkedIn which was developed in the context
of the NWRM pilot project initiative launched in October 2013 by the EC. The
forum is aimed at supporting the development of networks of experts and
practitioners on NWRM. In addition, the WG on Programmes of Measures and
the WG on Floods under the Common Implementation Strategy of the WFD and
FD worked extensively on NWRM between 2013 and 2014 to develop the Policy
Document on NWRM45. WG Floods and the Strategic Coordination group will
continue sharing information and experiences on its implementation in the next
work programme of the CIS.
It is clear that if constructed appropriately, portals can positively contribute to
distributing relevant information to the public and to various end-users. A major
question is where to disclose information and how to make information accessible such
that end-users can locate what they search for in a straightforward and easy way.
Thus, the link has to be made between the “what” and “why” of information with the
“where” and “how”.
Therefore, it is necessary to gain thorough insights in where end-users may be
assisted by specific information.
Further, it has to be acknowledged that end-users will not necessarily look for GI
related information from a GI perspective. Indeed, for example, a farmer may
simply be looking for ways to diversify and thereby be aided by knowing that a GI
focus can be one option.
45 https://circabc.europa.eu/sd/a/2457165b-3f12-4935-819a- c40324d22ad3/Policy%20Document%20on%20Natural%20Water%20Retention%20Measures_Final.pdf
Supporting the Implementation of Green Infrastructure
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Knowing which end-users may need GI-related information and understanding the
online paths they may choose to reach that information can help in providing the
required information on the places where they are likely looking for it.
This concerns information available at the various departments at the EU and the
national level, but also the information provided at regional and local levels.
Different groups of end-users have very different ways in which they interact with
GI and many of them will not be inclined or have a natural tendency to go and dig
into technical information provided on a website dedicated to GI, for example
under BISE.
The web portals they usually visit (for example about support to agriculture or
industries) should point towards the websites providing relevant GI information.
3.2.2 Stakeholders
GI may matter to a whole variety of stakeholders that are either involved in working
on infrastructure and design of open space or otherwise are users of open space. For
the first group stakeholder groups that will have large impact through their activities
on the environments-we-live-in are landscape architects, building professionals and
spatial planners. Focussing on the users of open spaces, relevant groups to consider
are land owners, foresters, farmers, fishermen, hunters, nature NGOs and businesses.
In the following section we collect information about these various audiences and the
platforms they have at the EU geographic scale and evaluate to what extent GI is
visible on these platforms. We first provide an overview of EU-scale platforms for the
various stakeholder groups. Secondly, we indicate some national and international
platforms while searching for where GI information is provided and how this is done.
For each of the organisations we also provide a short explanation of their coverage
and end-users.
Stakeholder priorities and identified EU scale platforms
Landscape architects:
International Federation of Landscape Architects46: Umbrella organisation for
professional landscape associations (38 organisations from 33 CoE nations, >
10,000 professional practitioners + students and associates, c. 180 accredited
academic courses, The European arm of IFLA’s global network). GI is not highly
visible on this platform. Using the search box only 6 hits resulted when entering
GI. The most significant hit is that in the ‘About’ section where it is indicated that
landscape architects consider green, nature and habitats.
International Council of Landscape Architecture Schools47: ECLAS exists to foster
and develop scholarship in landscape architecture throughout Europe by
strengthening contacts and enriching the dialogue between members of Europe's
landscape academic community and by representing the interests of this
community within the wider European social and institutional context. From their
website GI is not visible, with just a few instances where it is mentioned if green
is entered in the search tool. However, for members, ECLAS is having a member-
only accessible platform where GI information is available http://www.le-
notre.org/. The original LE:NOTRE Projects were co-funded by the European
Union's Socrates and Lifelong Learning Programmes. With funding ceasing, to
maintain the gathered information alive it was decided to make this member-only
accessible.
46 http://iflaeurope.eu/ 47 www.eclas.org
Supporting the Implementation of Green Infrastructure
May 2016 56
Building professionals:
World Green Building Council48: The World Green Building Council is a network of
national green building councils in more than one hundred countries, making it
the world’s largest international organisation influencing the green building
marketplace. They have specific information for each region, including with a
focus on Europe: http://www.worldgbc.org/regions/europe. Green in this context
should be understood as sustainable and not being limited to working with GI.
There is no indication on the webpages on GI, neither is there a sitemap or search
box allowing for quick access to possible GI information. One specific aspect that
is mentioned is the benefits in terms of health, wellbeing and productivity thanks
to views of nature. We could not find GI being mentioned anywhere upfront.
European Federation of Green Roof Associations (EFB)49: The ten associations
promote and encourage the uptake of green roofs in their countries to help
address issues related to climate change, ecosystem services, green
infrastructure and lack of green space in the built environment. While it is clear
from this first statement and the further information provided on the website
pages that EFB cares about GI and ecosystem services, the website is not a hub
for information on GI relating to green roofs.
Spatial planners:
European Council of Spatial Planners50: Umbrella association (1985) of 25
professional planning associations and institutes from 23 European countries as
well as corresponding members. In total representing c. 40,000 planning
professionals, ECTP-CEU focuses on planning practice, it engages in dialogues
with local, national and European governments, identifies, and rewards good
practices (European Planning Awards), Charter of European Planning. Entering GI
or green did not lead to GI relevant hits. They have a working group on climate,
but no information could be located on a working group or pages being dedicated
to GI or related terms such as nature or ecosystem services.
Land owners:
European Landowners’ Organization (ELO)51: ELO is committed to promoting a
sustainable and prosperous countryside and to increasing awareness relating to
environmental and agricultural issues. ELO represents a large number of rural
family business and enterprises as well as individual actors in Europe involved in
activities such as farming and agriculture, forestry and cork, wine production,
hunting and fishing as well as water and waste treatment. They have a large set
of links to other organisations. Under the topic section, they cover N2000. GI
information could not be retrieved.
Foresters:
European State Forest Association (EUSTAFOR)52: Their members represent one
third of the EU forest area, including large, protected areas (established in 2006,
currently 29 members from 21 European countries, total land area managed ~ 49
million ha (~ 30% of EU forests), total forest area managed ~ 42 million ha
(including French overseas departments and territories), protected and protective
forests ~ 16 million ha). Under the publications entry there are 2 reports on
48 http://www.worldgbc.org/ 49 http://www.efb-greenroof.eu/ 50 http://www.ectp-ceu.eu/index.php/en/ 51 http://www.europeanlandowners.org/ 52 http://www.eustafor.eu/
Supporting the Implementation of Green Infrastructure
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ecosystem services and 1 on N2000. Using GI in the search box did not give any
results.
Confederation Européenne des Propriétaires Forestiers/Confederation of European
Forest Owners (CEPF)53: This is the umbrella association of national forest owner
organizations in Europe. It works as the representative of family forestry in
Europe, by promoting the values of sustainable forest management, private
property ownership and the economic viability of the forest holding. CEPF serves
the interests of the approximately 16 million forest owners. They are private
individuals, families and cooperatives who take care of about 60% of the forest
area within Europe. They indicate on their website that Environment / Natura
2000 and Forest ecosystem services are among the main policy areas and
processes CEPF is currently following. GI information could not be located on the
platform.
European Forest Network (EFN)54: This is an unofficial network of national forest
societies and associations of Europe. The main goal is to promote the exchange of
information relevant to forests, forestry and forest policy among its members.
There is very little information on the website and no information on GI.
Forest-based Sector Technology Platform (FTP)55: FTP was established in 2005 as
the very first initiative in which European forest owners, woodworking industries
and pulp & paper industries came together to share one common goal: to
advance the competitiveness of the whole sector. In their vision and strategy
documents they consider forest ecology and ecosystem services. They also have
the FTP Research and Innovation Portal (http://www.forestplatform.net) which is
an advanced and comprehensive Internet database of EU-funded projects
involving the forest-based sector. For that portal there were no results matching
the query GI.
European Forest Institute56: They are an international organisation, established by
European States (25 European States have ratified the Convention on EFI, c.120
Associate and Affiliate Member organisations in 35 countries). EFI's Virtual Library
contains a variety of free services and materials (databases, publications,
information services). The query GI rendered 34 results where GI is mentioned in
reports or in news items. There is no direct information or topic on GI.
Farmers:
The European farmers (COPA) and the European agri-cooperatives (COGECA)57:
COPA is made up of 60 organisations from the countries of the European Union
and 36 partner organisations from other European countries such as Iceland,
Norway, Switzerland and Turkey. This broad membership allows COPA to
represent both the general and specific interests of farmers in the European
Union. Since its inception, COPA has been recognised by the Community
authorities as the organisation speaking on behalf of the European agricultural
sector as a whole. COGECA, now called the “General Confederation of Agricultural
Cooperatives in the European Union”, currently represents the general and
specific interests of some 40,000 farmers’ cooperatives employing some 660,000
people and with a global annual turnover in excess of three hundred billion euros
throughout the enlarged Europe. Since its creation, COGECA has been recognised
by the European Institutions as the main representative body and indeed the
spokesman for the entire agricultural and fisheries cooperative sector. In line with
53 http://www.cepf-eu.org 54 http://www.forestrysocieties.eu/ 55 http://www.forestplatform.org/ 56 http://www.efi.int/portal/ 57 http://www.copa-cogeca.be/
Supporting the Implementation of Green Infrastructure
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the recent European Union enlargements, COPA and COGECA have together
further reinforced their position as Europe’s strongest farming representative
organisations. On the homepage there is a direct link to Environment information.
This information concerns statements on various issues by COPA-COGECA-, but
the statements are not available. Entering GI in the search box did render 11 hits,
including a brochure on farming biodiversity. Certainly GI information is not easily
accessible and GI is only sparsely mentioned in brochures or statements.
Fishermen and hunters:
European Anglers Alliance (EAA)58: This is a pan-European organisation for
recreational angling, which defends European recreational anglers' interests at the
European level and beyond. There are about 3 mill. affiliated members to EAA's
18 member organisations and affiliates (2014) from 17 European nations. There is
no highly visible GI information, neither a related-term entrance through the
sitemap. Entering GI in the search function rendered no results. However, some
relevant information on GI was found such as http://www.eaa-
europe.org/positions/small-scale-hydropower-2013.html or http://www.eaa-
europe.org/topics/eel.html.
European Federation of Associations for Hunting & Conservation (FACE)59:
Established in 1977, it represents the interests of Europe’s 7 million hunters as an
international non-profit-making non-governmental organisation. FACE is made up
of its Members: national hunters’ associations from 36 European countries
including the EU-28. They have a webpage dedicated to GI:
http://www.face.eu/nature-conservation/green-infrastructure. From this page
there is a link to the EC pages on GI and also a statement and perspective on GI
by the hunting association. The page on GI is accessible though the higher level
called “nature conservation” to be found in the banner.
Nature NGOs:
Birdlife Europe60: This is a global Partnership of independent organisations
working together as one for nature and people. While in the top menu several
entries are GI relevant, for someone looking for GI information there is no
dedicated page or information section on GI. Entering GI in the search box gave
35 hits.
International Union for Conservation of Nature (IUCN)61: IUCN is the world’s
oldest and largest global environmental organisation, with more than 1,200
government and NGO Members and almost 11,000 volunteer experts in some 160
countries. In the top menu GI is not mentioned and there is no dedicated page to
GI. Under priorities there is a direct link to nature-based solutions and under
‘work by topic’ there are many more teams directly relating to GI. Entering GI in
the search box rendered 214 hits.
World Wildlife Fund (WWF)62: WWF’s mission is to stop the degradation of the
planet’s natural environment and to build a future in which humans live in
harmony with nature, by: conserving the world’s biological diversity, ensuring
that the use of renewable natural resources is sustainable and promoting the
reduction of pollution and wasteful consumption. Entering GI in the search box
gave 3 hits, none of which to a dedicated page on GI on the WWF website.
58 http://www.eaa-europe.org/ 59 http://www.face.eu/ 60 http://www.birdlife.org/europe-and-central-asia 61 http://iucn.org/about/union/secretariat/offices/europe/ 62 http://www.wwf.eu/
Supporting the Implementation of Green Infrastructure
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Eurosite63: This is a network of site managers, non-governmental and
governmental organisations, and individuals and organisations committed to
create a Europe where nature is cared for, protected, restored and valued by all.
They do this by providing practitioners with opportunities to network and
exchange experience on practical nature management. There is no direct
information or topic on GI. GI entered in the search box resulted in 12 hits.
Businesses:
World Business Council on Sustainable Development (WBCSD): This is a CEO-led
organization of forward-thinking companies that galvanizes the global business
community to create a sustainable future for business, society and the
environment. The WBCSD has been working on ecosystems issues for 15 years
and a formal Focus Area on Ecosystems was established in 2007. They have a
dedicated part of the platform on GI (here called natural infrastructure)64 with a
definition, the business cases, challenges and opportunities, events, a case
example and 3 reports.65 In addition, since December 6, 2015 the Natural
Infrastructure for Business platform has been launched.66 The aim of this platform
is to strengthen the business case for investing in natural infrastructure. It has
entries on the business case, tools, case studies and resources.
Further relevant stakeholders:
ICLEI (Local Governments for Sustainability)67 is the only network of sustainable
cities operating worldwide. The organisation facilitates local government input to
United Nations (UN), processes such as the UN Framework Conventions on
Climate Change, and Biodiversity. In partnership with the UN and other
organisations, as well as national governments, ICLEI puts in the groundwork for
more ambitious and more responsible international commitments - and seeks
global recognition and support for local action. In Europe ICLEI has dedicated
pages on biodiversity, climate adaptation and water. On the biodiversity page GI
is not specifically mentioned. Among the ICLEI activities are Greensurge (Green
Infrastructure and Urban Biodiversity for Sustainable Urban Development and the
Green Economy; http://www.greensurge.eu/) and URBES (Urbanization,
Biodiversity and Ecosystem Services; http://urbesproject.org/index.html).
CEEweb for Biodiversity68 is a network of non-governmental organizations in the
Central and Eastern European region working for 20 years in 20 countries. Our
mission is the conservation of biodiversity through the promotion of sustainable
development. They have part of their platform dedicated to GI:
http://www.ceeweb.org/work-areas/priority-areas/green-infrastructure/. This part
of the platform has inspiring YouTube fragments on GI and also they have a
colourful board on Pinterest with pictures of great GI projects, various elements of
GI, GI street-art or do it yourself GI. Further on the GI page they have an online
course on GI, a GI training manual, a news and events section on GI, a section on
experts also including a LinkedIn community – the European Green Infrastructure
Practitioners’ Network and a section on funding. The platform is not rich in
providing access to literature on GI or in providing links to other platforms that
have information on GI.
63 http://www.eurosite.org/ 64 http://www.wbcsd.org/naturalinfrastructure.aspx 65 http://www.wbcsd.org/ 66 Accessible through http://www.naturalinfrastructureforbusiness.org/ 67 http://www.iclei-europe.org/ 68 http://www.ceeweb.org/
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Infra Eco Network Europe (IENE)69 is a network of experts working with various
aspects of transportation, infrastructure and ecology. The network was initiated in
1996 to provide an independent, international and interdisciplinary arena for the
exchange and development of expert knowledge – and with the aim to promote a
safe and ecologically sustainable pan-European transport infrastructure. IENE
arranges international conferences, workshops and symposia, initiates
collaboration projects and helps answering questions that require a joint
international expertise. The platform links to a discussion and a mailing list and a
forum. Information on conferences, workshops and meetings. Under the project
section information is available on the COST 341 Action, “Habitat Fragmentation
due to Transportation Infrastructure” and also on a project on Planning and
Applying Mitigating Measures to Green Transport Infrastructure in Myanmar and
Thailand. The platform has a literature section which unfortunately is empty.
European Network of Environmental Professionals (ENEP)70 represents 22
European Environmental Organisations and over 45,000 individual professionals.
ENEP is the leading environmental professional networking organisation across
Europe. ENEP believes environmental professionalism is one of the essential
prerequisites for achieving sustainability, so they have created a Platform to help
build a professional community which promotes knowledge sharing, cross-border
integration and an arena to positively influence and implement policy, science and
education. The platform includes a link to the European Green Week and a word
cloud in tags71 which includes ecosystem services, green procurement and green
capital, but not GI; further, they have a working group on biodiversity and one on
climate-proof cities to which access is available through the members’ area. One
of the reasons for having created the biodiversity working group was to
encourage the use of GI, ecosystem and catchment approaches and tools. The
working group has discussed in detail the Commission’s strategy on GI. For the
working group on climate-proof cities they indicate that adaptation measures are
essential and could include increasing the area and attractiveness of ‘green’
(nature, parks, trees) and ‘blue’ (water) in and near cities (increasing the water
storage capacity and reducing the heat stress), energy-saving buildings and new
sustainable energy technologies, such as solar cells or thermal energy storage.
Evaluation of GI at stakeholder platforms
Only FACE, WBCSD and CEEweb have dedicated pages on GI.
For FACE, GI information is available at: http://www.face.eu/nature-
conservation/green-infrastructure. From this page there is a link to the EC pages
on GI and also a statement and perspective on GI by the hunting association.
Together, this is clear, however, limited information on GI that is made available.
For the WBCSD, where GI is referred to as natural infrastructure,
http://www.wbcsd.org/naturalinfrastructure.aspx, a definition, the business
cases, challenges and opportunities, events, a case example and 3 reports are
provided. Although clear in structure and providing a good view on GI, the
information altogether is limited and rather to be called providing GI information
and not being a knowledge or information hub on GI. In addition, since December
6, 2015 the Natural Infrastructure for Business platform has been launched and is
accessible through http://www.naturalinfrastructureforbusiness.org/.
69 http://www.iene.info/ 70 http://www.efaep.org/ 71 http://www.efaep.org/md-taxonomy/page/1
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For CEEweb, GI information is available at http://www.ceeweb.org/work-
areas/priority-areas/green-infrastructure/. This part of the platform has inspiring
Youtube fragments on GI and also they have a colourful board on Pinterest with
pictures of great GI projects, various elements of GI, GI street-art or do it
yourself GI. Further on the GI page they have an online course on GI, a GI
training manual, a news and events section on GI, a section on experts also
including a LinkedIn community – the European Green Infrastructure
Practitioners’ Network and a section on funding. The platform is not rich in
providing access to literature on GI or in providing links to other platforms that
have information on GI.
At the ECLAS platform, GI is not very much visible. More on GI may be available
under http://www.le-notre.org/ which is a member-only accessible platform hosted by
ECLAS. The EFB emphasises the link between green roofs and GI strongly, however,
the platform cannot be considered a hub on GI information.
For all other platforms and websites of the various organisations that were researched,
no or very little could be retrieved on GI. This indicates that there is large potential for
increasing GI visibility, however, at the same time this indicates there is only limited
information that is easily available on these platforms to connect to BISE.
Interim conclusions
Based on the organisations and platforms that were evaluated, the conclusion is that
except CEEweb and the new platform on natural infrastructure by the WBCSD, none of
them qualify as an information or knowledge sharing platform. It may be explored
whether links can be made from BISE to CEEweb and WBCSDs dedicated platform on
natural infrastructure and vice versa. Next to CEEweb and WBCSD, FACE is best in
class with limited, but clear and inspiring information on GI. On some other platforms
GI is mentioned, however, mostly nothing could be found. Also for those platforms
that have related information (biodiversity, ecosystem services, nature-based
solutions, etc.) in some documents the link is made to GI, however, GI is not included
on the platforms in a dedicated manner. Altogether, the visibility of GI on platforms
and websites at the EU scale of stakeholder groups for which GI is considered very
much relevant, is considered poor. A future ‘ideal world’ could be one where GI
visibility has increased substantially for a large selection of the platforms that were
mentioned. In the introductory section, we have indicated which types of GI
information can be distinguished. Further consultations with the representatives and
the end-users of the various platforms (or a selection) can provide insight on what
type(s) of GI information they consider useful to be disclosed.
It must be mentioned here that the Green Infrastructure Network (GreenInfraNet) is a
EU co-funded partnership of 11 regions from across Europe. The partners are working
together to promote the development and implementation of GI in EU regions.72 One
of the aims of this project is to create a permanent European Network for Green
Infrastructure Knowledge and Experience (ENGINE), which will enable GI stakeholders
across Europe to capitalise on project achievements and continue to exchange and
transfer experience, expertise and good practices after the end of the GreenInfraNet
project. Possibly, this could become a needed central hub for GI information and
knowledge. In this case, information from this platform can be connected to others
where less information on GI is provided. Also, in recent years the partnership had
regular communication with DG ENV (specifically with Marco Fritz) indicating the aim
of ENGINE closely collaborating with the GI section on BISE.
72 http://www.greeninfranet.org/
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3.2.3 National and international platforms on GI
On the national and international level there are examples of hubs where GI
information is disclosed in a more exhaustive manner. These may provide inspiration
on how to disclose GI information and/or may provide sources of information to be
linked to BISE. In what follows we only provide some inspirational examples. An
extensive survey of available national or international (outside of the EU) platforms on
GI or relating to GI is not within the scope of the current exercise. Because this is a
limited exercise, for national platforms, we focussed on English platforms (UK and
Ireland) in order to provide examples that any reader of this document most likely can
understand (from a language perspective). This does not suggest that there are no
good examples on GI platforms in other EU Member States.
The platforms on the national scale that we would like to introduce are the following
two:
Green Infrastructure North West73: This is a UK website disclosing GI information
organised in projects (4 examples), resources, contact, links, glossary and
partners. They also provide information on the benefits and values of GI, the key
opportunities, the challenges and the complementarity.
Green Infrastructure Partnership (GIP)74: GIP brings together a network of over
300 stakeholder organisations and individuals. It provides a platform for members
to share their research, news, and best practice and to co-ordinate influencing
key decision makers about the value of GI. This could be mainly seen as a social
network on GI with newsletters, twitter and a calendar as main items.
The platforms on an international scale that may provide inspiration are:
Green Infrastructure Collaborative: The Green Infrastructure Collaborative
consists of more than 20 organizations in the US committed to advancing the
adoption of green infrastructure as a means of supporting water quality and
community development goals. This broad group of signatories includes
academia, non-governmental organizations, and the private sector. In the top bar
they have entries on the basics, tools, case studies, research and a library.75
Green4Cities76: This is an international centre of excellence for GI in urban areas.
With experience in research, development, education and installed projects, the
platform provides signposts to guide cities towards resilience to climate change.
We would suggest including the three platforms mentioned here in the section on BISE
GI on networks. This section on networks could steadily grow by also including
examples of GI platforms from other Member States or continents. Also, the platforms
indicated here may provide perspective on how to organize the section on BISE GI.
For example, a combination of how the GI North West and the GI Partnership disclose
GI information and connect to a community would cover much of the needs of many
GI end-users.
In case the desire is to have information that is available on the above indicated
platforms to also be uploaded or connected to BISE there are three immediate options
for this:
73 http://www.greeninfrastructurenw.co.uk/ 74 http://www.gip-uk.org/ 75 http://water.epa.gov/infrastructure/greeninfrastructure/gi_partners.cfm 76 www.green4cities.com
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The easiest one is to link to the information from BISE and to provide guidance on
BISE to the user on what to expect when visiting either of the other platforms or
sections within.
A second possibility would be to upload information manually (copy/paste
procedure). This is because the various platforms have different technicalities (for
example, BISE is based on Plone).
For a last, however more challenging option, we refer to the recommendation
section, in particular where we comment on machine-to-machine communication.
3.3 Increasing GI visibility for selected platforms
For each of the eight platforms we will explore in more depth which GI content is or
could be presented. Three platforms (BISE, NWRM and Climate-ADAPT) were further
chosen for a more detailed analysis of the accessibility and user friendliness of each
platform in general and from a GI perspective more specifically. The following set of
questions were considered:
1. Who are the end-users of the platform and what sort of information do they
expect?
2. Are these end-users provided with information/explanation on GI?
3. For each division/subdivision of the platform, it will be evaluated whether the
information is GI relevant or not. This will be approached through the sitemap.
4. Are there ideas on GI information that are lacking and could enrich the specific
platform?
5. Is the GI information presented easy to be located (for this see also further)?
6. Is this information on GI similar to other information on other platforms and
therefore relevant to be integrated with that other information?
7. Is this information that is also relevant to be integrated available through BISE,
or only through a link, or not at all? For BISE this question will be answered
from the perspective of linkage to NWRM and Climate-ADAPT.
8. Which recommendations can be made to improve the visibility of GI?
For an end-user it is important not only that information is available, but also that it is
easy and straightforward to find the information that suits users’ needs. Therefore,
accessibility and user friendliness are important. In what follows we will explore in
more depth for the different platforms the following five overall performance
dimensions (for more detail, see Box 3), each time approached from a general
perspective and a GI specific perspective:
Ease of navigation, inter-operability and user friendliness for finding GI
information;
Structure allowing to navigate easily for finding GI information;
Searchability and geo-referencing;
Accuracy, objectivity and historical depth;
Coverage and coherence.
In Annex 9 we include the specific set of questions that will be answered for each of
these performance dimensions. Considering that for platforms of stakeholders there
was little information available on GI we have not conducted this detailed survey on
accessibility and user friendliness. If GI information would become more abundant on
these platforms the principles that are indicated here and the evaluations of BISE,
NWRM and Climate-ADAPT may provide guidance and inspiration.
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Box 3 Accessibility and user-friendliness of the studied platforms
Ease of navigation, inter-operability and user friendliness for finding GI information These aspects are linked and highly important for the effective dissemination of information. Even if a portal contains a lot of information, the manner of presenting the information determines whether the users will ever find the correct GI data. An element that can greatly increase the ease of navigation is the presence of a sitemap, providing information on the structure and content of the portal. Simplifying the website to make it more inter-operable and increase user friendliness is highly important. The structure is for instance simplified by including menus that show dropdown attributes once they are selected. To improve the navigation through the portal, presenting the users’ location through a so-called breadcrumb trail is highly effective. Visual properties of the portal are highly supportive in making the portal more user friendly and attractive. Both the provision of intuitive pictures and an interactive homepage can aid the user in understanding the content of a specific page or part of the portal. For navigation purposes it is often convenient to have fixed items or an explanation of the structure of the portal on the homepage. Structure allowing to navigate easily for finding GI information A clear and logical structure of a website supports the effective dissemination of information. If the structure is not logical or comprehensive, this will have a direct impact on the user search effectiveness. This starts already with whether the first level subdivision of the website is intuitive and logical. For the structure of the website it is also important to get quick access to either new information items or to other relevant GI portals. Searchability and geo-referencing For finding relevant information with regard to GI, the search functions on a portal are of great importance. If the search bar is not easily located or the search engine is not sufficient, then this could significantly hamper the visitors in achieving the relevant information. The presence of a simple search box on the home page is important for the user to perform a quick search for relevant information. The further content and properties of the search engine are also important. When the quick search results are for instance not sufficient, then the potential for an advanced search could greatly increase the chance for finding the desired information. Besides the advanced search option, the results could also be presented in categories. This helps the user in distinguishing between different types of information of his search. Besides specifically searching for information, the portal could also present information via an interactive map. Accuracy, objectivity and historical depth Providing inaccurate information or erroneous links could hamper users to find the relevant information. For an accurate portal it is first of all important to be regularly updated. Objectivity is often supported with scientific information. It is therefore important to have evidence or research based results supporting statements on portals. Also relevant is that data are provided in a standardized format or manner. Coverage and coherence In considering the envisioned end-users, a major question is whether the portal gives an overall coverage of relevant information. Further, as a portal can be seen as a center for providing further directions, it is expected that a portal will contain many references to other websites.
3.3.1 BISE
Before discussing the standard set of questions on content and accessibility, the
reader may wish to refer back to Box 2 for more details on the BISE platform. The
results of the nine analysis questions relating to the content of this platform are
provided below:
1. Who are the end-users of the platform and what sort of information do they
expect?
The end-users are policy-makers, practitioners (both national, local and regional
governance levels) in Europe working with or interested in strengthening the
knowledge base in support of the implementation of the EU Biodiversity Strategy to
2020.
1. Are these end-users served by GI information/explanation?
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Yes, there is a separate section on GI, organised under ‘Topics’. It provides a
definition, a brief background on why GI is important, provides a reference to the EC
GI strategy, links to further reading as well as links to relevant EC and JRC sites.
2. For each subcategory the question needs to be asked as to which information is
GI relevant, which not.
Before answering the question, it is important to note that the platform is difficult to
navigate. The platform’s sitemap often does not correspond to the actual pages, drop
down menus or sub-sections of the different sections. The analysis provided here is
departing from the sitemap but in several cases it was necessary to divert from that
and consider what is the logical overview of the content and categories of the
platform.
In the table below (Table 3) we comment on the GI relevance of the available
information for each of the divisions/subdivisions on BISE. In the column on relevance
this is indicated through categories (High – high GI relevance, Medium – some aspect
relevant to GI, Low – low GI relevance), while in the comment section further
explanation is provided:
Table 3: GI relevance of the divisions/subdivisions on BISE
First level
heading
Second level
heading
GI Relevance
Comments and recommendations
HOME
TOPICS General Medium The site structure is not so clear. There are quick
links on the left column, links presented in the
main text and a drop down menu which overlap
with each other. Some of the links are missing.
E.g. GI appears only under ‘quick links’ but not
under ‘Responses’ as is outlined in the sitemap,
and in the dropdown menu.
Climate change Medium/high No reference to GI. The page describes the threat
and impact of climate change on biodiversity and
have relevance as GI is one instrument to apply to
mitigate and adapt to changes. Link is provided to
Climate-ADAPT platform.
Ecosystem
services
High This page should be interlinked to the GI section, in
both directions. Both from the GI section site as
ecosystem services are mentioned on the GI site (A
hyperlink would be easily added). Link should also
be provided from this site to the GI section. Link
could also be provided to NWRM.
Ecosystems
habitat
Medium/high Link should be provided to GI site.
Contains subsections which in general have some
GI relevance:
Cropland and grassland, coastal, woodland and
forests (Link should be added to FISE), heathlands
and scrubs, sparsely vegetated land, islands,
wetlands (link should be added to NWRM), marine,
mountains, urban, GI concept is introduced. (Link
should be provided to GI site. A link to the Climate-
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ADAPT page on cities and towns should be added)
croplands, rivers and lakes (link should be added to
NWRM).
Fragmentation High Add link to GI, as a response measure.
Genetic
resources
Low
Green
Infrastructure
High This section could be further strengthened by
extending the currently available material. Add
internal links to LIFE+, policy site and the
interactive presentation on the Biodiversity
strategy on BISE. Add links to Climate-ADAPT,
NWRM. Links could be provided directly to the
relevant sites on the above mentioned platforms
such as to case studies and the catalogue of
measures. See further recommendations below.
Invasive species Low
Land use
change
High GI concept is introduced. The link to the GI site is
not working
LIFE+ Nature
and Biodiversity
projects
High
Overexploitation Medium No reference to GI. Is relevant as background.
Pollution Low/Medium
Protected areas High Add link to GI site.
SEBI Medium Good source of biodiversity indicators that can be
useful for GI stakeholders.
Species Low/Medium Divided into sub-categories of selected species
groups.
Tipping points Low/medium
POLICY Policy, general
page
High Relevant, although GI is not directly linked.
The site structure is not clear and it is difficult to
navigate. Sitemap, drop down menu and the
general page does not correspond.
Overview of the EU biodiversity strategy. Especially
Target 2 is GI relevant. Add link to GI site.
Global High References and links to UN Convention on
biodiversity, Ramsar Convention
Pan European High Links to Pan European Initiatives and European
conventions.
Interactive
presentation of
EU Biodiversity
Strategy
overview
High Good and easy overview of the EU strategy
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DATA DATA Medium/High The section gathers selected entry points to data
and information related to Biodiversity; the EEA’s
Biodiversity data centre (BDC) as well as to other
environmental data centers from the EU. The scope
is set to information infrastructure supported by
the EU.
KNOWLEDGE Knowledge Medium/high Has GI relevance, but not as specified and difficult
to navigate. Collection of links to science-policy
interfaces, key research funding, networks,
relevant bodies and projects related to biodiversity.
Clearer division of categories is needed and GI
should be better highlighted.
COUNTRIES Medium/low EU Member State national reports related to
biodiversity and information related to indicators
organized by country.
No specific information on GI, but still with some
GI relevance
NETWORKS High Information on networks supporting the current
developments of BISE and their products relevant
to the EU biodiversity strategy.
BISE
CATALOGUE
High There is a GI catalogue available. It is however
difficult to find.
Link from GI site needed. It does not appear in
sitemap, search results and needs to be connected
through the search function as well as included in
sitemap.
3. Are there ideas on GI information that are lacking and could enrich the specific
platform?
See recommendations below.
4. Is the GI information presented easy to be located (for this, see also further)?
Relatively. All GI information is gathered in one section which is beneficial. However,
with increasing GI information becoming available, it will be important to maintain this
easiness to locate by the end-user searching for information. The interlinkages
between the different sub-sections on BISE are currently not so strong, which would
need to be addressed to further ease the access to GI information for the end-user.
5. Is this information that is similar to other information on other platforms and
therefore relevant to be integrated with that other information?
The information is similar to the information on the DG ENV GI site. As the European
Commission indicated a desire to have much of the DG ENV GI information moved to
BISE, with only policy-relevant GI information being disclosed through the DG ENV GI
location. The BISE GI site could be strengthened by the information on DG ENV.
6. Is this information that is also relevant to be integrated available through BISE,
or only through a link, or not at all? For BISE this question will be answered
from the perspective of linkage to NWRM and Climate-ADAPT
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The information on BISE is highly GI relevant and also very relevant in the context of
the themes covered on Climate-ADAPT and the NWRM platform. Further integration of
the three platforms would be desirable.
7. Which recommendations can be made to improve the visibility of GI?
Short-term
Ease the navigation to and increase the visibility of the GI section on the BISE
platform. As the general ease of navigation on the platform is difficult, it also
makes it difficult to easily access the GI section. It is not immediately apparent
where it is to be found. A more visible link to GI should be offered on the home
page; in the short term, under ‘BISE highlights’, but in the long run through a
separate box or similar.
Enrich the current GI section on BISE. The information available needs to be
enhanced to provide a fuller picture, e.g. the policy aspects should be
strengthened, as they are currently only described by a reference to the EC
Communication on GI. Information on GI measures and links to case studies
should also be added to further strengthen the section.
Increase the attractiveness and user-friendliness of the website. The section
would benefit, for example, from separating the text with headings or using
textboxes or similar to make it more user-friendly. Links to case studies,
measures, etc. should be added.
Enable the user to quickly find its way to the right reports/links by grouping them
under themes such as “Making the case for GI”, GI and “green economy”, GI and
Climate change”, etc.
Add a calendar of events and a news section.
It would be important to give toolkits and guidance materials a more central place
and highlight them on the website. Gathering the available practical support tools
for developers would also make it easier to define the need for additional ones to
be developed.
Further increase the interlinkages between relevant sections across the BISE
platform. Many of the sections would benefit from a link to the GI section and this
would also allow to accentuate the potential gains GI applications could provide.
Currently, only on a few occasions there is a link to GI. Vice-versa, additional
links should also be provided on the GI site, e.g. to the Biodiversity Strategy
sections as well as to the many sections that contribute to understanding the
background and current situation with regards to GI (for example, such as
relevant indicators etc.). Please see table above for additional comments on the
interlinkages.
Further increase the integration of other GI platforms such as Climate-ADAPT,
NWRM, FISE on the website, on the GI section and across the BISE platform.
Links should be added to relevant case studies, primarily from NWRM and
Climate-ADAPT. Please see table above for further details on links.
Further promote and visualize the GI library on the BISE catalogue. The library
has more than 220 documents and is a good source of GI information that can be
filtered down to match the users’ need, according to geographical region, topic, or
specific year. However, the library is not easy to find for the user as there is no
reference at all to the library on the GI relevant sections. It does not appear in
the sitemap either. A highly visible link should be provided from the GI section, as
well as in all other relevant sections. Linkages between the GI library and the
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CIRCAB catalogue on GI should be explored. This recommendation may also be
extended to other platforms where it would beneficial to link to the GI catalogue.
Mid-term
Consider applying all of the above in creating a separate section for GI on BISE to
further streamline the GI information on the website and to develop it into an
accessible, useful and inviting knowledge hub for GI. However, given that the
expert Working Group on Green Infrastructure Implementation and Restoration
(WG GIIR) has concluded that there will not be a separate repository dedicated to
GI and serving as a central gateway, it will be essential from a governance point
of view to decide on which information to centralize on BISE and for which
information to limit the linkage to cross-referring across platforms.
Much of the information on BISE is relevant to GI but is not labelled as such. To
support the above points, the website needs to be reviewed and the information
which can be related to GI should be identified and highlighted as such. This could
provide a good example for other GI platforms where a similar need has been
identified.
It would be helpful to make the GI section (and the platform itself) more inviting.
This could be achieved by e.g. introducing interactive presentations and
illustrations. One inspiring example is provided by NWRMS’s interactive illustration
of sectoral measures which after clicking on a chosen measure presents more
detailed information and links to potential benefits of measures and case studies
(http://nwrm.eu/urban).
Long-term
Establish a network for GI practitioners and experts for which BISE provides the
platform. Synergies should be sought with ENGINE (the European Network for
Green Infrastructure Knowledge and Experience). Inspiration could also be taken
from the the Green Infrastructure Partnership (GIP) set up by Defra, UK
(http://www.gip-uk.org/).
Enable a knowledge sharing function where users could upload best practice
examples or new reports. This would facilitate the BISE GI section to stay up to
date with the continuous development of GI information and help to build BISE
into a relevant knowledge base.
Define the end-users and conduct an assessment among them to define their
needs and expectations of the GI section on BISE to see what type of information
and/or functions they are expecting or missing from the platform.
Consider developing the use of social media to reach out to a wider audience but
also to keep the end-users informed about news, developments and updates.
NWRM use of Linkedin might provide inspiration.
Consider to develop a GI newsletter.
Answers to the specific questions of Annex II on accessibility and user friendliness are
included in Annex III and have been covered in the recommendations provided under
8.
Concise summary
Although not labelled as such, most information of the BISE platform is highly relevant
from a GI perspective as preserving biodiversity is an important result and building
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block of GI measures, because ecological networks are GI and because it concerns
ecosystem services for delivering goods and services. Some of the key conclusions
from the analysis is that the GI relevant sections need to be made more visible, which
includes that the many sub-sections that have GI relevance should be better labelled
as such. Moreover, by providing further interlinkages between the various GI related
sections the usefulness of BISE for the end-users would increase as well as a more
holistic picture will be given. The platform hosts the nice feature of the GI library
which has a lot of potential to be further developed into a rich source of information.
The library however needs to be made more visible and accessible to be able to
provide for its full potential.
There is a lot of GI relevant information available on BISE but its coherence, visibility
and user-friendliness needs to be improved. By structuring the information, increasing
interlinkages, extending the integration of other GI platforms, BISE could become a
good source of GI information. The GI information available should be extended to
also encompass policy aspects. In addition, a deeper dive in the different GI options
and measures that are available would be needed. These aspects need to be
addressed before BISE can claim to be a user friendly, exhaustive source of GI
knowledge in Europe.
3.3.2 NWRM/WISE
Today there is no GI information available at the Water Information System Europe
(WISE). This is despite the fact that including GI information on the WISE site is very
relevant as ‘blue infrastructure’ is an important physical building block of GI. GI
contributes to achieving and maintaining healthy water ecosystems and offers
multiple-benefits to the water sector including providing regulation of water flows,
water purification and water provisioning, i.e. significantly contributes to achieving the
objectives of the EU water related directives. It would thus be suitable to have
information on technical standards and on how to design and construct biodiversity
friendly waterways and water bodies on WISE. However, today there is no GI
information available on this platform. Neither are any links to external GI platforms
provided.
The Natural Water Retention Measures (NWRM) platform, on the other hand, contains
a great deal of relevant GI information. This platform was initially thought to be part
of WISE but is currently separate. Therefore, for evaluating which GI information is
available and how the visibility can be improved, focus has been placed not on WISE
but on NWRM. It is a possibility to explore how NWRM can be integrated into WISE in
the long-term.
The stated objective of the NWRM platform is to gather and provide information at the
EU level. The platform was developed within a DG ENV project with the objective to
develop a sound and comprehensive European (web-based) knowledge base on NWRM
in order to improve the uptake of these measures in the 2nd and 3rd River Basin
Management Plans under the WFD and the Flood Risk Management Plans. The
platform was set up after the first cycle on River Basin Management Plans were
reported by the Member States. The knowledge base structures available information
on technical, environmental, socio-economic, governance and implementation aspects
of NWRM, mobilizing existing practical experiences, studies and stakeholders’
knowledge. During the second cycle of reporting (to be done by March 2016) more
information on GI/NWRM will be included. NWRM are defined as one of the key type
measure to be reported under the Programmes of measures of the River Basin
Management Plans (RBMPs). GI or NWRM may also be included under other key types
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of measures. This reporting will provide an updated picture of the measures planned
to be implemented by MS in the upcoming years.
1. Who are the end-users of the platform and what sort of information do they
expect?
The platform is targeted to all parties interested in the design and implementation of
NWRM in the context of the planning process of the Water Framework Directive (WFD)
or the Floods Directive, the development of a climate change adaptation strategy or
the establishment of sustainable urban plans, such as:
practitioners who are or have been involved in the design and practical
implementation of NWRM in different sectors (urban, agriculture, forestry…);
managers involved in the development of River Basin Management Plans (RBMPs)
or Flood Management plans;
technical service staff (for example, from a large city engaged in a “sustainable
city” initiative);
representatives from funding agencies that can support NWRM implementation;
representatives from economic sectors that can implement NWRM;
environmental NGOs; researchers and independent experts, etc.
In short, the end-users are existing and future NWRM practitioners and stakeholders
looking for practical examples for implementing NWRM measures and
recommendations on how to select and prioritise measures.
2. Are these end-users served by GI information/explanation?
The relation between NWRM and GI is explained in the ‘About the project’ section as
well as throughout the information available, such as the practical guide, the synthesis
documents, the ID cards, measures etc. There is also a GI definition provided in the
Glossary and in the Relations graph. This information is however not easily accessible
and it is not immediately clear for the user that NWRM is GI. The user needs to have
some background knowledge and know what to search for in order to find the
information.
3. For each subcategory, the question needs to be asked as to which information
is GI relevant, which not
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Table 4: GI relevance of the divisions/subdivisions on NWRM
First level heading Second level heading GI Relevance
HOME High
IMPLEMENTING NWRM The Practical Guide High
The ID Cards High
Communication material High
Synthesis documents High
CATALOGUE OF NWRM NWRM per sector High
NWRM per benefits High
Benefits tables High
CASE STUDIES High
GLOSSARY Relations graph High
ABOUT THE NWRM PROJECT About High
The regional networks High
4. Are there ideas on GI information that are lacking and could enrich the specific
platform?
It would be useful to add a section on the GI concept and the links between GI
and NWRM. It should include a GI definition and provide a more holistic
overview of GI and the water sector, include links to other platforms and
information sources. A sentence on GI as a concept and the links to NWRM
should be included on the home page introduction to immediately catch the
attention of the user.
The Policy section on NWRM is not so strong, as the user has to go to the
Guidance or to additional documents to get the full picture. See further
recommendations below.
5. Is the GI information presented easy to be located (for this, see also further)?
All information on the website is related to GI, as NWRM per se are green
infrastructure solutions. The information is however not presented as such and
the user has however to be aware of that as it is not immediately, explicitly
mentioned on the front page of the platform. The specific GI references are
dispersed and spread out in the online guidance and in other documents
(available as pdf documents). Otherwise, the website has a logical and clear
structure.
In the NWRM catalogue/NWRM per type of benefit, there is an option to filter
NRWMs according to policy objective, and here it is possible to choose the
priority of “Better protection of ecosystem and more use of Green
Infrastructure”. But also here, the user has to search specifically for GI to be
able to find it.
6. Is this information that is similar to information on other platforms and
therefore relevant to be integrated with that other information?
This is the most detailed information resource with regards to water related GI
among the EC GI platforms. Some of the NWRM measures supporting climate
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change adaptation could be linked to Climate Adapt. Also the ones related to
habitats could be linked to the Biodiversity Strategy.
7. Is this information that is also relevant to be integrated available through BISE,
or only through a link, or not at all?
This information is highly relevant to BISE and an overview of the NWRM
information should be integrated to BISE in addition to clear and visible links to
the in-depth NWRM information.
8. Which recommendations can be made to improve the visibility of GI?
Short-term
To enhance and facilitate the end-users’ understanding of the GI concept and the
strong supporting relationship to NWRM by:
Adding an introduction on GI as a concept and its links to NWRM on the home
page.
Adding links to related information and external information portals for further
relevant readings on GI, such as BISE, Climate-ADAPT, DG ENV GI and FISE page
would increase the coverage of the GI concept and would enable users interested
in GI to find additional information, beyond NWRM. In particular, stronger links
should be made to Climate-ADAPT and the sections on e.g. water management
and urban sector to benefit from the capacity of NWRM to contribute to climate
change adaptation. The links should be made easily accessible and appear in
sections where related information is presented (in the future, ideally on the
suggested separate GI section). E.g. targeted links to Climate-ADAPT should
appear under the adaptation section in the NWRM catalogue/NWRM per type of
benefit provided as well as in the Case Study. Links to BISE should appear in the
section on Biodiversity under the NWRM catalogue.
Organise case studies in a similar way as with the NWRM measures, i.e. according
to benefits and sectors to facilitate finding the most relevant ones for the specific
user.
Establish deep links with WISE; there should be a clear and visible link to the
NWRM platform from WISE.
Mid-term
Adding a separate section on GI to highlight the links between GI and NWRM
where a definition and an overall introduction to the GI concept is provided. This
section could possibly be added under ‘About the project’ or ideally by creating a
new sub-section on GI.
It should be ensured that the information material from the NWRM is available
through the GI library on BISE.
Answers to the specific questions of Annex 9 on accessibility and user friendliness are
included in Annex 10 and have been covered in the recommendations provided under
8.
Concise summary
NWRM is all about GI. It is at its place under WISE and only needs to be indicated on
BISE with a link and short explanation. In other words, no integration into BISE is
necessary and only a connection should be established.
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Considering the NWRM platform from a GI perspective, it would be helpful to improve
the platform by better introducing and integrating the GI concept and the strong
supportive relationship of GI and NWRM, as this is currently missing. All information
on the website is highly relevant to GI as NWRM per se are green infrastructure
solutions. The information is however not labeled as such and the user might not be
aware that this is in fact GI. This aspect should be given further attention to make the
context clear for the end-users.
Currently, there are not many linkages made to external sources, and it would be
useful to have much more links being made to other GI platforms and sources of
information, thereby considering to not flood it such that its attractiveness in making
available what is needed is not being lost. A technical challenge is how to integrate
NWRM into WISE.
The NWRM platform, which is entirely a GI, could through the way it has been set-up
serve as inspiration for setting up/renewing other GI related platforms such as BISE or
the new platform on sustainable cities that will be organised. The structure of the
measures section, and to some extent the case studies section, can be used as an
illustrative and good example on how to create interlinkages within a platform and in
how it is making links to the relevant case studies, benefits etc.
3.3.3 Climate-ADAPT
The European Climate Adaptation Platform (Climate-ADAPT) aims to support Europe in
adapting to climate change. It helps users to access and share information on i.e.
adaptation case studies and potential adaptation options, etc. It is obvious that GI
plays a crucial role in climate change adaptation.
More in detail, Climate-ADAPT is a partnership between the European Commission (DG
CLIMA, DG Joint Research Centre and other DGs) and the European Environment
Agency.
Climate-ADAPT aims to support Europe in adapting to climate change. It is an
initiative of the European Commission and helps users to access and share data and
information on:
Expected climate change in Europe
Current and future vulnerability of regions and sectors
National and transnational adaptation strategies
Adaptation case studies and potential adaptation options
Tools that support adaptation planning
The platform includes a database that contains quality checked information that can
be easily searched.
1. Who are the end-users of the platform and what sort of information do they
expect?
The end-users are policy-makers, practitioners (national, local and regional
governance) in Europe working with or interested in adapting to climate change.
2. Are these end-users served by GI information/explanation?
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There is no specific section on GI and no proper background overview of the concept is
provided. The GI concept is mentioned briefly on a few occasions with regards to
'Cities and towns' and 'Urban adaptation support tool' as well as being mentioned in a
number of case studies.
3. For each subcategory question needs to be asked as to which information is GI
relevant, which not
Table 5: GI relevance of the divisions/subdivisions on Climate-ADAPT
First level heading
Second level heading
GI Relevance
Comments
HOME High Introduction to the platform. Link to BISE and WISE is available.
ADAPTATION INFORMATION
General Medium There is no specific GI information.
Recommendation: Include general introduction of benefits of applying GI for adaptation to increase the relevance. The information should be accompanied with links to relevant GI platform and information sources such as DG ENV GI site, BISE and NWRM.
Observations and scenarios
High The sub-section is further divided in 6 categories. Each category contains links to selected indicators, relevant reports and links. In particular the sections on Water Systems, Terrestrial biosphere, Urban areas and Health are relevant to GI.
Recommendation: Link to NWRM should be added under Water system sector (if possible directly to the relevant sections of adaptation on NRWM, i.e. case studies, benefits tables). A link should be made to the NWRM guidance in the report section. A link to BISE should be made available in the Urban areas and health and terrestrial biosphere sections.
Vulnerabilities and risks
Medium Not directly relevant to GI, but interesting background for GI stakeholders.
Adaptation options
High Some adaptation options presented are highly relevant, such as:
- Improved water retention in agricultural areas,
- Adaptive management of natural habitats
- Agro-forestry and crop diversification
- Dune construction and strengthening
- Green roofs and walls
- Adaptation or improvement of dikes and dams
- Water sensitive urban and building design
- etc.
Recommendation: Link should be provided to NWRM website and reports and BISE. Include GI as an adaptation sector to be applied in the search function.
Adaptation strategies
Low
Research projects
Medium There is a link to the Curriculum Adaptive Water Management which is relevant to GI.
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Recommendation: current or future projects on GI and adaptation could be included here.
Uncertainty guidance
Medium The guidance has some relevance for handling uncertainty issues when using GI for adaptation measures.
EU ADAPTATION POLICY
EU adaptation policy and funding
Medium Link to the EC communication on GI information is provided.
EU Adaptation Strategy
Medium Although not addressing GI specifically, it can serve as background for GI stakeholders.
EU sector policies
High The section is organised into 9 sectors. Some of the sectors are more GI relevant than others, such as biodiversity, forestry, water management, coastal areas, urban areas, infrastructure, disaster risk reduction.
Recommendation: Green infrastructure could potentially be added as a separate section to increase the visibility of GI and enable easy access to GI information.
Synergies could be established with the NRWM sections on sectors (in particular the water management and coastal areas) by providing visible links between the two websites. For Forestry link should be provided to FISE. Link to BISE should be added to biodiversity, water management.
EU funding of adaptation
Medium There is a reference under the LIFE funding section for Climate Action where green infrastructure is cited as a potential action to be funded.
COUNTRIES, REGIONS, CITIES
General Low/medium
Countries Low/medium
Transnational regions
Low/medium
Cities and towns
High The site contains some information on GI and its co- benefits for tackling climate change, including improved air quality, support for biodiversity and enhanced quality of life. Funding opportunities for urban mitigation and adaptation are presented which have some relevance to GI stakeholders, although not directly targeted to GI.
Recommendation: - The information on GI could be enhanced, potentially as a separate section. - The text should also highlight the capacity of GI to contribute to adaptation, not only mitigation. - The relevance would be increased by including links to active links to other GI platforms (would be easily done by including hyperlinks in the text where GI is mentioned).
TOOLS General Medium Have some relevance for GI measures supporting adaptation. E.g. a link is provided to the Grabs toolkit for adaptation using green and blue infrastructure. The visibility would be increased if it was highlighted as a tool for GI.
Adaptation Medium/high Tool could be relevant for selecting GI relevant
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support tool measures and drafting strategies. Relevant links to e.g. GRABS guidance and PLUREL Xplorer.
Case study search tool
High Several case studies on GI could be find.
Recommendation: Make GI searchable by adding GI as an adaptation sector.
Map viewer Low
Uncertainty guidance
Medium See above
Guidelines for project managers
Medium Have relevance for project managers and developers of physical assets and infrastructure and could thus be relevant for GI project managers.
Urban vulnerability map book
Medium Pilot version. Good illustration on some issues such as floods and droughts. Could be relevant for planning GI measures.
Urban adaptation support tool
High Provides practical guidance and knowledge support on urban adaptation. Includes several references to GI. Offers links to case studies and adaptation options.
Recommendations: The introduction could indicate that the link and relevance of the tool to GI.
Time series tool
Gives good illustration of the development of some climate indicators such as land-use and water stress. Could be relevant for planning GI measures.
4. Are there ideas on GI information that are lacking and could enrich the specific
platform?
A visible and coherent presentation of GI and its relevance to climate change
adaptation is not available on the platform. Such section would enrich Climate-
ADAPT. See further recommendations below.
5. Is the GI information presented easy to be located (for this, see also further)?
The specific GI relevant information to be found is relatively scattered and not
easy to locate.
6. Is this information that is similar to other information on other platforms and
therefore relevant to be integrated with that other info?
Yes, the information is relevant to other information platforms and the Climate-
ADAPT would benefit from a further integration with related platforms such as
DGENV GI site, BISE, NWRM and FISE.
7. Is this information that is also relevant to be integrated available through BISE,
or only through a link, or not at all?
Part of the information would be highly relevant to BISE, however the GI
information on Climate-ADAPT needs to be made more coherent and visible in
order to provide meaningful linkages from BISE. Ideally, an overview of the GI
information available on the Climate-ADAPT should be integrated to BISE in
addition to clear and visible links to the most relevant, in-depth, GI information
on Climate-ADAPT.
8. Which recommendations can be made to improve the visibility of GI?
Short term
Increase the integration with other platforms on GI by making links across the
Climate-ADAPT platform to relevant sections of external GI platforms such as the
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DGENV GI site, BISE, NWRM and FISE. Please see Table 5 above for additional
specifications on the linkages.
Consider adding GI as a sector under ‘EU Sector Policies’. As the integration of GI
into climate adaptation management, contributes to achieving the EU climate
adaptation goals it would be relevant to include it.
Add GI to the ‘Glossary’.
Mid-term
Increase the accessibility and coherence of GI on the Climate-ADAPT platform to
highlight the significance and benefits of GI as an effective measure for climate
change adaptation. This could preferably be achieved by adding a separate
section on GI and adaptation where a short overview and its high relevance for
climate change is provided. This section would in addition to the overview also
interlink the climate change options related to GI, the relevant case studies as
well as links to further reading e.g. at DG ENV GI page, BISE and NWRM, i.e. also
gather the relevant links which are already available across the platform but in
most cases not presented as GI. This could possibly be placed in the ‘Adaptation
Options’ section, or in the section on ‘Cities and Towns’ to further strengthen the
short reference to GI which is already available there. Streamlining the GI
information in such way would also increase the possibilities for creating synergies
and integration of Climate-ADAPT GI relevant information with other GI relevant
platforms, thus contributing to the awareness raising of GI and its possibilities.
See http://www.greeninfrastructurenw.co.uk/climatechange/ for further
inspiration.
Review the information in the database to increasingly label case studies etc.,
with the key word GI to make them searchable. Currently, only a couple of case
studies and adaptation options are identified as GI.
To further refine the ‘Search the Database’ function and to add GI as an
adaptation sector used as a search filter would facilitate the search and enable the
users to more easily find the relevant GI information and increase the visibility of
GI as a valid adaptation measure. Such improvements would improve the search
function on several sections on the platform, such as the Adaptation Options’, the
‘Case Study Search Tool’ and the ‘Map viewer’. See also
http://www.greeninfrastructurenw.co.uk/climatechange/search_start.php for
inspiration on how GI filters can be used in a search function.
It should be made sure that the information material from the NWRM is available
through the GI library on BISE.
Long-term
Assess the need for new materials to be developed and consider developing
targeted guidance material or toolkit on GI and climate change adaptation.
Answers to the specific questions of Annex 9 on accessibility and user friendliness are
included in Annex 10 and have been covered in the recommendations provided under
8.
Concise summary:
GI is among the most widely applicable, economically viable and effective tools to
support climate change adaptation. The integration of GI into climate adaptation
management, also called ecosystem-based adaptation, contributes to achieving the EU
climate adaptation goals.
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The Climate-ADAPT platform contains a few references to GI, however not sufficiently
to reflect its significance. A clear introduction of GI is missing. In its current state, the
few GI references are scattered across the platform. These aspects are making the GI-
relevant information on the platform difficult to locate resulting in a low usefulness for
the user. The website contains knowledge which would be highly relevant to GI and
that could provide useful information and guidance on sectors, measures, processes
etc. relevant for GI, and in particular GI measures supporting climate adaptation.
Presenting the GI concept in a visible and structured way is needed. The available
information which is related to GI should be highlighted as GI relevant. It would also
be important to increase the interlinkages across the platform to provide a fuller
overview of GI and to help the user to find its way to the information. It would be
beneficial to create a separate section on GI and adaptation which could present all
these aspects in a coherent and visible way. These improvements would be necessary
to establish links with other platforms, such as BISE.
3.3.4 Sustainable cities platform
The DG REGIO Sustainable Cities platform is currently under reconstruction due to
expired software. We can therefore not evaluate it from a GI perspective. A new
platform will be set up. For that new platform we provide guidance here from a GI
perspective on how to populate it.
GI use has much potential for urban areas. Indeed, boosting GI in cities and towns
has large capacity to contribute to sustainable urban development as it has numerous
co-benefits, including improved air quality, support for biodiversity and enhanced
quality of life. In addition, it has big potential in mitigating and adapting to the effects
of climate change and can deliver benefits such as flood alleviation, strengthening
ecosystems resilience, carbon storage and sequestration, mitigation of urban heat
island effects, disaster prevention (e.g. storms, forest fires, landslides), among others.
For the platform to be constructed we consider the following recommendations:
Add a separate section on GI, where the concept is defined and a short
background including policy aspects, implementation aspects highlighting the wide
range of possibilities and benefits GI has for urban development.
Make apparent and visible links to:
o BISE GI section
o BISE GI library
o Climate-ADAPT platform, and in particular the section on Cities and towns.
o NWRM, highlighting the urban related NWRM measures having climate
change mitigation and adaptation as key benefit.
With regards to content:
Provide user-oriented materials that can support the practical work, such as
toolkit and guidance, etc. for local planners as GI should be a key consideration in
planning, developing and maintaining sustainable cities.
GI standards, targets and performance indicators.
Information on funding opportunities.
Catalogue of measures. It would be beneficial to take inspiration from NWRM and
its catalogue of measures in presenting GI options.
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Catalogue of relevant case studies. Plenty of case studies could be
collected/linked from the DG ENV GI, NWRM and Climate-ADAPT.
3.3.5 International Council of Landscape Architecture Schools
The European Council of Landscape Architecture Schools (ECLAS) exists to foster and
develop scholarship in landscape architecture throughout Europe by strengthening
contacts and enriching the dialogue between members of Europe's landscape
academic community and by representing the interests of this community within the
wider European social and institutional context. In pursuit of this goal ECLAS seeks to
build upon the Continent's rich landscape heritage and intellectual traditions to:
Facilitate the exchange of information, experience and ideas within the discipline
of landscape architecture at the European level, stimulating discussion and
encouraging co-operation between Europe's landscape architecture schools
through, amongst other means, the promotion of regular international meetings,
in particular an annual conference;
Foster and develop the highest standards of landscape architecture education in
Europe by, amongst other things, providing advice and acting as a forum for
sharing experience on course and curriculum development, and supporting
collaborative developments in teaching;
Promote interaction between academics and researchers within the discipline of
landscape architecture.
Provided these goals and the relevance of GI for the landscape planning it is rather
surprisingly that from the ECLAS website GI is not visible, with just a few instances
where it is mentioned if “green” is entered in the search tool.
For members, ECLAS has a member-only accessible platform where GI information is
available at http://www.le-notre.org/. The original LE:NOTRE Projects (2002-2013)
were co-funded by the European Union's Socrates and Lifelong Learning Programmes.
The project web site provides a richly interactive platform for communication and the
sharing of information between all project members. With funding ceasing, to maintain
the gathered information alive it was decided to make this member-only accessible.
www.le-notre.org is the web site of the LE:NOTRE Thematic Network Project in
Landscape Architecture. It is a key tool for sharing information and communicating
within this global network. The LE:NOTRE Directory comprises a series of inter-linked
databases providing a European 'Who is Who' information of universities and other
organisations involved in landscape architecture teaching research and practice. The
LE:NOTRE channels collect and view information of various fields of interest and
identify each member as a member of 12 sub-communities. These sub-communities
include the entries ‘vegetation’ and ‘infrastructure’. From these sub-communities it is
not clear, however, how well information on GI is presented and how well practitioners
of GI are linked to each other. The Resource databases represent a growing collection
of user-editable databases which are developing into a common resource where
Network members can enter and share a wide range of information.
We recommend that once the GI section on BISE has been further developed that
from www.le-notre.org users easily will find their way to the information on the BISE
platform. Also, with the information on BISE growing, it may be beneficial to explore
in more depth the information available on GI at LE:NOTRE and the way it is
presented. Potentially, in the long-term, this may provide an opportunity for having a
win-win realized in the information sharing of these two platforms. For the ECLAS
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website we would recommend having a minor section on GI being included, covering
issues such as definition, advantages/disadvantages, relevance and a link to BISE.
3.3.6 World Green Building Council
The World Green Building Council is a network of national green building councils in
more than one hundred countries, making it the world’s largest international
organisation influencing the green building marketplace. They have specific
information for each region, including with a focus on Europe:
http://www.worldgbc.org/regions/europe. “Green” in this context should be
understood as sustainable and not being limited to GI only. This is very clear also from
the cases that illustrate the report on the “Business case for green building.”77
There is no indication on the webpages on GI, neither is there a sitemap or search box
allowing for quick access to possible GI information. One specific aspect that is
mentioned is the benefits in terms of health, wellbeing and productivity thanks to
views of nature. We could not find GI being mentioned anywhere upfront.
Nevertheless, there are several points of entry which encompass GI despite not
mentioning it directly. For example, with the Sustainable Cities Initiative (SCI) the
WGBC supports national green building councils (GBCs) in their relationships with local
governments around the world, with the aim of creating greener, more sustainable
cities everywhere.
We do not think that the platform is waiting for GI to be put in the picture. Therefore,
the best way to bring more attention to GI would be to first integrate it better in
different sectors of EU policy. With GI becoming a more widely used term, as has been
the case with climate or sustainability, then it will likely be covered more specifically
on the WGBC’s platform. It is relevant in this context that the WGBC’s website is
mainly aimed at facilitating a network and less so at providing content.
3.3.7 Green Roof Association
The ten associations promote and encourage the uptake of green roofs in their
countries to help address issues related to climate change, ecosystem services, green
infrastructure and lack of green space in the built environment. While it is clear from
this first statement and the further information provided on the website pages that
EFB cares about GI and ecosystem services, the website is not a hub for information
on GI relating to green roofs.
Links are provided to the websites/platforms of each of the 10 member associations.
Although these national websites vary in the information offered, in several instances
they provide much more content on the green roof industry (producers and suppliers),
on the pros and cons of green roofs, guidance (such as on
http://greenrooftraining.com/the-guide/). Also, newsletters and connection to blogs
on green roofs, and information on funding are provided for some of the national
associations. On several occasions also a library is included, for example
http://www.aivep.it/bibliografia. While some of this information may be rather country
specific or only available in the country’s language, there certainly is potential to
further disclose some of the available information among countries.
Therefore, we recommend to make http://www.efb-greenroof.eu/index.html a central
hub on GI information that is relevant to be shared across countries. In particular, we
would recommend having the platform become “the” one-stop-shop for information on
green roofs and the pros and cons this GI element provides. Providing a link from
77 http://www.worldgbc.org/activities/business-case/case-studies
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BISE, NRWM and Climate-ADAPT to the EFB’s website would allow practitioners to
directly find what they need. In the links section on the EFB website, a link should also
be made to BISE, NRWM and Climate-ADAPT to provide end-users with the broader
picture on GI and building with nature.
3.3.8 European Council of Spatial Planners
ECTP-CEU is the umbrella organisation for spatial planning institutes in Europe. From a
networking perspective, it is an achievement and benefit that the services ECTP-EU
provides include a register of experts from across Europe specifically on planning
issues. Specifically, planning practitioners all over Europe are increasingly confronted
with new challenges. Globalisation, environmental problems, accessibility of urbanised
areas, immigration and social tensions, identity and cultural heritage, natural heritage,
water management and climate change, all affect spatial development of cities and
regions. Different European regulations and processes deal with these challenges
differently and devising integrated approaches or balancing development with
sustainability can be a problem. ECTP-CEU experts offer their knowledge, insight and
experience in these issues to individuals and organisations all over Europe looking for
guidance in these fields. This may be an opportunity to easily bring GI to attention and
to create a community of practice or working group on GI. Also, this provides an
opportunity for involving such experts in a network of experts that would be created
as part of the GI section on BISE. In fact, the ECTP-EU has working groups on specific
teams already, including a group on climate. They have an url-entry,78 however, little
information is available on the topic.
The current work of the ECTP-CEU includes:
Dissemination of the revised New Charter of Athens on planning European cities in
the 21st century;
The design of a Vision enhancing the quality and efficiency of cities and urban life
in Europe;
The production of a guide to spatial planning and territorial cohesion;
The publishing of the proceedings of major conferences on European spatial
development and the preparation of forthcoming conferences;
The preparation of the European Urban and Regional Planning Awards.
There is a member only area on the platform at http://www.ectp-
ceu.eu/index.php/en/members-area
From this work description it is clear that the ECTP-EU does not aim to be a content
hub, but rather aims at bringing attention to major approaches and outcomes of
events such as conferences. Therefore, our recommendation is not to have a specific
content-rich section included on the platform that deals with GI. Rather, we would
recommend having a minor section on building with nature, where the possibilities and
benefits of GI and making use of nature are brought to attention. In addition, for this
section it would be beneficial to also include a selection of inspiring examples on
spatial planning and GI and include visible links to the GI section on BISE and to the
NWRM and Climate-ADAPT platform.
78 http://www.ectp-ceu.eu/index.php/en/about-us-2/working-groups-19/climate-change
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3.4 Technical and governance aspects of BISE, NWRM and Climate-
ADAPT
3.4.1 BISE
The server signature for BISE is Zope/(2.13.21, python 2.6.6, linux2) ZServer/1.1.
BISE is running on top Plone. The CMS correct version of Plone could not be identified.
In other words, it is unclear on what version of Plone BISE is built. Further technical
specificities of BISE features are that:
On BISE most of the content is based on data presentation of simple text using
WYSIWYG mechanisms exposed by standard “Add Page” functionalities. More
information on how to add a Page with content in Plone is available at:
http://docs.plone.org/working-with-content/adding-content/adding-pages.html
Other web resources such as Images, Links, files, are done with the help of
standard content processing mechanisms (see: http://docs.plone.org/working-
with-content/adding-content/index.html).
The map under countries (http://biodiversity.europa.eu/countries) is a standard
map found under the EC maps portofolio. For other maps in the EC portofolio,
see: https://webtools.ec.europa.eu/fusionmapsxt/Tools/GUI/FusionMapsGUI.html
or http://www.eea.europa.eu/data-and-maps/data/biogeographical-regions-
europe-1.
We could not identify any modules present that are facilitating communication with
citizens in order to gather data for further processing or for presentation of data such
as news and/or newsletters. Where there is a hint of such mechanisms, they are
rather poor in presentation or difficult to read; i.e. the “BISE - Clearing House
Mechanism (CHM) network of Europe” page (http://biodiversity.europa.eu/chm-
network) does not present data categorised by language and the order of news should
be descending.
Figure 1 – Unordered news and hard to identify relevant information between different languages.
The “Knowledge” page is a rather poor page in design, presenting a group of links into
a simple page. Most of the links are outside of the biodiversity.europa.eu domain.
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The menu on top in BISE cannot be reached on a mobile device.
Figure 2 – Submenu on Data section may not be reached on mobile device
The result of searches are not relevant. For example, searching for “Fragmentation”
renders 5 pages with links where the title of the page is the only information
presented to the user that needs to make a choice on how to proceed. Clearly, this is
not very user-friendly in terms of using key words and having rapid access to the
relevant pages or information.
In what follows we provide recommendations on how to technically improve the
functioning of BISE such that GI information can become easily available to end-users
of the BISE platform.
Short-term recommendations:
Make the BISE portal HTML5 compatible and change its presentation based on a
responsive design79. Opening the application on a mobile device, this would give a
user a better experience together with an easiness of navigation. There are
different themes with responsive mechanism available on the plone.org website:
https://plone.org/products/plonetheme.diazo_responsivetheme
79 Responsive web design (RWD) is an approach to web design aimed at crafting sites to provide an optimal viewing and interaction experience—easy reading and navigation with a minimum of resizing, panning, and scrolling—across a wide range of devices (from desktop computer monitors to mobile phones).
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A better order of events has to be achieved by presenting upcoming events in an
ascending order and past events in descending order. For News items the
standard is in descending order.
Improve the Knowledge page by adding categories and lists with different sections
to improve information visibility and the finding of information.
For easy technical maintenance of BISE, we recommend to have the modules and
vulnerability fixes updated (currently the most recent version of Plone is 4.3.6).
Improve the search function by showing under the main link or title the context
part of the paragraph where the search word is found. There does not seem to be
a search engine on offer in Plone modules, however an open source search engine
that delivers a better experience by searching is http://sphinxsearch.com/.
Figure 3 - A search in Google reveals a better way of presenting of the found expression
Long-term recommendations:
On plone.org there are multiple plugins for Plone including one developed by EEA
in order to facilitate machine to machine communication:
https://plone.org/products/eea.daviz
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Figure 4 - DaViz plone module app facilitating machine-to-machine communication
It is recommended to create a data warehouse exposing data in RDF format with
immediate availability to SPARQL queries; Data may be visualized in different
formats such as Interactive charts, dashboards, tables, URLs. A way of doing this
may be to gather a warehouse with GI related information in RDF format. Such
data can then be analysed with tools like Cytoscape (cytoscape.org).
Cytoscape is an open source software platform for visualizing complex networks
and integrating these with any type of attribute data. A lot of Apps are available
for various kinds of problem domains, including bioinformatics, social network
analysis, and semantic web.
Figure 5 – Cytoscape LOD modelling
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3.4.2 NWRM
The nwrm.eu website uses Drupal 7 (http://drupal.org) as a development platform,
hosted on an Apache/2.2.15 (CentOS) server powered by PHP 5.3.5.
Drupal is an open source content management platform powering millions of websites
and applications. It is built, used, and supported by an active and diverse community
of people around the world.
Drupal is powerful in the availability of modules allowing a high degree of website
customisation. See https://www.drupal.org/project/project_module for a full list of
modules (i.e., more than 17000). On that page, tools are available to allow filtering
for specific types of modules.
We noticed some problems with the presentation to users of the NWRM platform
depending on the browser/device used. These are issues that would best be fixed in
the short-term to provide the best experience to users of the platform. We have
included an overview of our experiences in Annex 11.
Most of the pages on the NWRM platform that display text data have links to either
flash applications, pdf documents or, in most cases, simple text.
With regard to machine to machine communications, Drupal offers various modules
allowing exchange of information with other Sites, Systems, Data and APIs. A list of
modules is available at https://www.drupal.org/node/627270.
Drupal has support for RDF format content: https://www.drupal.org/project/rdfx. An
introduction to this in Drupal is https://www.drupal.org/node/219862. A SPARQL
module is also available at https://www.drupal.org/project/sparql. Simple RDF
(https://www.drupal.org/node/1393378) automatically maps values of Drupal objects
(e.g. nodes) to RDF properties. Simple RDF provides RDF mapping configuration for
the node, user, and term object types per classification, such as content type in the
case of nodes. However, simple RDF has been stopped with development of Drupal 6
level. More on RDFx module for Drupal 7 is available at
https://www.drupal.org/project/rdfx. Simple RDF also comes with an RDF document
display module: Simple RDF View. This module publishes the RDF document for an
object on a configurable path under the object's path, e.g. `node/123/rdf. In NWRM,
RDF visualization is present; see http://nwrm.eu/page/relations-graph. This page
shows RDF data (it is however not clear if data presented in these nodes are limited to
the NWRM website only). For browser presentation some fixes are needed (see Figure
6): nodes are exceeding the presentation (IE, the graph should be aligned centered
(FireFox and Chrome), and connection points are not visible (IE9).
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Figure 6 – RDF visualisation on the NWRM websites with IE
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Specifically with respect to GI a node is displayed under Glossary->Relations graph
(see Figure 7). It was not entirely clear from the research how this graph is
generated. This was either by using GraphAPI
(https://www.drupal.org/project/graphapi) or the JIT (http://philogb.github.io/jit/).
Figure 7 – GI RDF node present in graph
Short-term recommendations:
Fix the layout issues encountered with the different browsers.
Implement a responsive design theme allowing mobile users to properly
experience the NWRM platform. In fact, there are several themes available out-of-
the-box on the Drupal website or alternatively other low-priced commercial ones.
For example:
- AdaptiveTheme - https://www.drupal.org/project/adaptivetheme;
- Zen - https://www.drupal.org/project/zen
- AdaptiveTheme - http://adaptivethemes.com/
Improve the size of thumbnails (small pictures links) on the platform. A maximum
size of 15-20KB for this would be more suitable.
The page at http://nwrm.eu/catalogue-nwrm/benefit-tables needs revision.
Pictures need to be resized and it would be more convenient if by clicking on the
links the big image would be loaded on another page. Also, use can be made of a
free and open source picture library slider from http://bxslider.com. Many other
similar libraries are available on the internet. For example, another recommended
free open source library is: http://www.jssor.com/download.html.
Open links that are not part of nwrm.eu in another window.
Long-term recommendation:
Choose for a mechanism to display the already existing RDF data (or existing
mechanism in Drupal for generating RDF content) in a more formatted way. The
graph visualization of LOD (http://nwrm.eu/page/relations-graph) may be useful
to display the complexity of link relations, but may not be the best way of
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showing data to the final users. This would allow for all GI related data and
information to be presented in a structured way. With the help of Drupal RDF
modules, all pages and information may be exposed easily to RDF related
warehouses on the EEA servers. Further, these data may then be immediately
available to other publishing engines like BISE, Climate- ADAPT, WISE, etc.
3.4.3 Climate-ADAPT
Climate adapt is built on top of the Liferay community edition CMS available at
http://www.liferay.com (but to be changed to Plone in 2015). The version of the portal
is Community Edition 6.2.0 CE GA1 (Newton / Build 6200 / November 1, 2013).
Liferay contains a lot of modules that may be used to enrich content such as Web
Content, Documents and Media, Message Boards, Dynamic Data Links, Pools,
Categories etc. On the continuous integration EEA platform http://ci.eionet.europa.eu/
it can be researched which portlets (modules) have been used with Climate-ADAPT.
Also, Liferay is strong on social network connectivity. More information is available at:
https://dev.liferay.com/discover/portal/-/knowledge_base/6-2/social-networking.
On Climate-ADAPT most of the content is based on data presentation of simple text
using WYSIWYG mechanisms exposed by standard Web Content functionalities. More
about web content management is available at:
https://dev.liferay.com/discover/portal/-/knowledge_base/6-2/web-content-
management. Data on Climate-ADAPT is well presented, based on categories and lists
with different filters easing the information search. The map under adaptation -
http://climate-adapt.eea.europa.eu/adaptation-strategies - is a standard map found
under the EC maps portfolio. For other maps in the EC portfolio, see:
https://webtools.ec.europa.eu/fusionmapsxt/Tools/GUI/FusionMapsGUI.html or
http://www.eea.europa.eu/data-and-maps/data/biogeographical-regions-europe-1.
We encountered two minor issues that need to be solved:
1. On Android 5 with Google Chrome there is no website header and top menu (see
Figure 8). With Firefox and Chrome, the page is loaded well.
Figure 8 – Android 5 view of the climate-ADAPT homepage
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2. Browsing with IE9 the map under http://climate-adapt.eea.europa.eu/tools/map-
viewer does not appear at all (see Figure 9). With Firefox and Chrome the page is
loaded well. The responsible services of Climate-ADAPT indicated more problems
have been reported for IE9.
Figure 9 – Uses experience on IE9 for the map-viewer on Climate-ADAPT
Short-term recommendations:
Implement a responsive layout for the correct display of the climate-ADAPT
website to mobile users. This can, for example, be done though the theme
available within the Community edition of Liferay: AlloyUI 2.0 TagLib and
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Bootstrap Migration https://dev.liferay.com/develop/tutorials/-
/knowledge_base/6-2/alloyui-2-0-taglib-and-bootstrap-migration .
Some small layout fixes such as the search textbox where “Search” is not
properly aligned and the search icon has an improper size; see:
3.5 Recommendations
Based on the previous chapters we are now in the position to provide general
recommendations for improving the online visibility of GI. This chapter will not bring
together all the previous, sometimes very specific recommendations which have been
made throughout this document. Therefore, we recommend to also consult the
previous chapters in taking up actions for improving the GI visibility for the various
platforms that have been researched. Specifically, for BISE, NWRM and Climate-
ADAPT the preceding sections provide detailed information on actions that can or need
to be done in the short-, mid- or long-term for improving the online visibility of GI.
As in previous chapters, we distinguish between short, mid and long-term timelines for
implementation. Some of the recommendations entail a combination of actions,
starting with actions that can be addressed in the short-term, followed by actions to
be taken in the mid- and long-term time horizon.
In each of the recommendations below, we comment on the ‘why’, ‘what’, ‘how’,
‘when’, ‘who’, technical advice, governance, roadmap and risks. Only for the long-term
recommendations we do not follow this structure and provide our insights on how
progress can be made on increasing the online visibility and interconnectivity of GI
information.
Short-term
3.5.1 BISE to become a GI information hub
The amount of GI information on this platform today is rather disappointing. In the
previous sections it has been extensively discussed which actions can be taken. In
making BISE a GI hub it needs to be considered that the Commission prefers not to
create a central repository on GI but to use existing facilities: e.g. BISE covering the
biodiversity aspects, WISE/NWRM the water aspects, Climate-ADAPT the climate
aspects etc. Therefore, it is crucial to decide on which GI information to disclose
through BISE, and which through other platforms (such as NWRM or Climate-ADAPT).
GI information disclosed through other platforms should be connected to BISE such
that it is also accessible for end-users who access through BISE. In practical terms, GI
information will be more visible on BISE than on other platforms, as currently the GI
file is hosted by the Biodiversity Unit of DG ENV, which has a steering role in BISE
(but less on water and climate policies). While this approach may work well for linking
to NWRM and Climate-ADAPT, it may need to be reconsidered when GI uptake is also
increasing in other policy sectors. The reason is that other sectors are not necessarily
familiar with terminology used on BISE or inclined to search for information on a
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‘nature’ platform. Therefore, evaluation may be needed on how GI information needs
to be provided (e.g. language, setting) to attract users that relate to these other
policy sectors.
Why?: BISE should become an inspirational and exemplary platform on how to
optimally provide online GI information and connect this to other platforms.
What?: See sections ‘Increasing GI visibility for selected platforms’ and ‘Technical
and governance aspects of BISE, NWRM and Climate-ADAPT’.
How?: A combination of improving content, paying particular attention to user
friendliness and accessibility, and establishing good connections at least to NWRM
and Climate-ADAPT, and by extension to other platforms or sources of GI
information (see national or international - outside the EU - examples).
When?: See sections ‘Increasing GI visibility for selected platforms’ and ‘Technical
and governance aspects of BISE, NWRM and Climate-ADAPT’.
Who?: DG Environment and the EEA have a key role.
Technical advice: See ‘Technical and governance aspects of BISE, NWRM and
Climate-ADAPT’ and corresponding longer term recommendation (3.5.5).
Governance?: This requires DG Environment and the EEA to agree on how to
bring this forward.
Roadmap: Drafting a detailed roadmap is suggested to be a first action after the
governance issue has been settled.
Budget: Budget needs for implementing this short-term recommendation are low.
With increasing time horizons and considering the ambition levels that are
decided on, budget needs will be higher, andnot only for DG Environment and
EEA. When working towards recommendation 3.5.5, several organisations and
initiatives may be connected.
Risks?: Similarly as for budget, the first steps to take have little risks, however,
for implementation of longer-term recommendations budgets are required and
also several parties have to agree on how to proceed and on how to structure the
information on their platform.
3.5.2 GI as a common vocabulary across platforms
There is a rather weak presence of both the term GI and the information that relates
to GI across platforms linked to either the EC or to stakeholders. In fact, many
platforms that can be considered relevant do not contain any reference at all to the
concept of GI. Much progress therefore can be made by having the concept, its
relevance for the sector or stakeholder group and a link to the GI section on BISE
integrated across the relevant policy sectors and stakeholder platforms.
Why?: To create a community and connect across policy sectors and
stakeholders, having a common terminology and understanding can be a catalyst
for GI information to become labelled as such, disclosed and, most importantly,
applied.
What?: GI information may be present at a variety of websites/platforms,
however, it will often be available as very specific information and not necessarily
named GI. Therefore, it is not evident to retrieve all the available information by
using the term GI. Indeed, often other search terms (such as ecosystem-based
adaptation, nature-based solutions, natural capital, ecosystem services, etc.) are
needed or in use for GI related information.
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How?: (1) Introduce the concept where it is not present today and link it to the
expectations/language of the end-user (see also the fact sheets on GI that were
produced in task 1 for various policy sectors). (2) Identify which information is GI
relevant and take the necessary actions to label it as such. (3) Provide at least a
link to BISE and possibly to other platforms relevant for that sector.
When?: This can start now with a focus on BISE, NWRM and Climate-ADAPT, then
further extended across EC websites and platform (mid-term) and ultimately lead
to GI visibility also on many stakeholder platforms or information hubs (long-
term).
Who?: DV ENV will need to facilitate this until a community has been built that
may start doing this.
Technical advice: There are no real challenges from a technical perspective,
unless ambition is to cater for this also more directly through recommendations
3.5.3, 3.5.4 and 3.5.5.
Governance: Not each representative may welcome the idea to have GI as a
common label and to indicate where it links to related information.
Roadmap: (1) Step 1 would be to have BISE as a representative platform on GI
such that it can be an inspiration and that links can be provided. (2) Step 2 would
be to have GI become commonly used and more visible on NWRM and Climate-
ADAPT, such as to illustrate how connections can be made. (3) Step 3 would
involve the same for other platforms/websites of EU policy sectors. (4) Step 4
would involve the same for stakeholder platforms.
Budget: Efforts to be mainly expressed in terms of manpower to discuss this with
representatives of the various organisations and a limited effort of each in terms
of providing the information on the various platforms.
Risks: See ‘Governance’.
Mid-term
3.5.3 Have GI relevant information made available to the end-users of the
various platforms
For the majority of the studied platforms there is limited availability of GI information.
In Chapter 3 we have indicated the ‘ideal’ future situation on the way GI information
could be made available through the different websites/platforms linked to specific
policy sectors. For the stakeholder platforms, the exercise that was made for the
policy sectors can provide inspiration. However, to define exactly which GI information
to disclose is something that is best considered in terms of the needs of end-users and
of the platform’s function for end-users (for example, is it included in the aims of a
specific platform to also provide technical information?).
Why?: Various end-users have different needs for GI information. Also, not each
end-user may be expected to search for GI information on BISE, which is a
platform on biodiversity.
What?: Provide end-user oriented GI information. Distinguish between
information on policy, techniques, economics, methods, best practices and
network/discussion groups, and consider for each information type which needs
end-users may have and whether these can best be satisfied through the platform
for which this analysis is being made or by connecting to other platforms/sources
of information (for example BISE).
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How?: After or parallel to recommendation 3.5.2, identify which GI information
needs to be disclosed where.
When?: This can start now with a focus on BISE, NWRM and Climate-ADAPT, then
further extended across EC websites and platforms (mid-term) and ultimately
lead to GI information also being shared on many stakeholder platforms or
information hubs (long-term).
Who?: DG ENV will need to facilitate this process and likely stay involved for a
longer-term.
Technical advice: Depending on the long-term ambitions, this may directly be
catered for also through starting implementation of the long-term machine-to-
machine recommendation described below.
Governance: It will need to be discussed with the various representatives of the
different platforms whether they agree on providing GI information. An alternative
decision could be to go for recommendation 3.5.2 and not for 3.5.3. In the latter
case, connecting from the platform to BISE may still satisfy end-users’ needs. In
this case, the way information is provided on BISE and whether that appeals to
end-users, different policy sectors or fields of expertise will be critical.
Roadmap: 1) Step 1 would be to make BISE a representative platform on GI such
that it can be an inspiration and that links can be provided to the available
information. (2) Step 2 would be to render GI information more visible on NWRM
and Climate-ADAPT and well-connected to BISE. (3) Step 3 would involve doing
the same for other platforms/websites of EU policy sectors. (4) Step 4 would
involve doing the same for stakeholder platforms.
Budget: Further budget needs will depend on how much GI information will be
disclosed and on how much effort will be made in catering the information
towards the end-user. However, in case BISE, NWRM and Climate-ADAPT further
grow to be strong sources for GI information, this may also provide an
opportunity for a rapid start on other platforms. When catering for specific end-
users, efforts will be needed to collect and disclose GI information in an adequate
way with respect to the different categories of GI information (policy, technical,
economic, methodological, best practices and network/discussion groups).
Risks: See ‘Governance’.
3.5.4 Stronger connect across platforms
The GI information that is available across the studied EC platforms is relatively
dispersed and not presented in a coherent way. By introducing the GI concept (3.5.2)
and providing end-user specific information on the various platforms (3.5.3) much
more GI information is expected to become available. A challenge then becomes to
connect the different sources of information (for example for green roofs there may be
very technical information on the digital platforms for the construction sector, e.g. on
how to construct these, while more information on their biodiversity values may be on
BISE, more information on the water buffering capacity on NWRM and more on the
climate consequences and calculations on Climate-ADAPT. For some end-users it may
be desirable to make such information available through a single search or from a
single page with convenient links to where other information is available. To improve
user access to this information, a search function in combination with a single
repository where all GI related information is centralized, would be a most effective
solution. However, the feasibility of this option is rather low, as it is very unlikely that
all platforms involved will be happy to share all information in an agreed manner. A
different option is provided under recommendation 3.5.5. A different approach (less
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preferable) is indicated here and would involve the manual connection of all the
different types of information through deep links (for example, not simply from BISE
to NWRM, but from BISE green roofs to NWRM green roofs).
Why?: Connecting platforms would assist in GI becoming more broadly and widely
disclosed.
What?: Create and extend connection across the analysed platforms as this is not
properly done.
How?: This can be done by creating separate entries on GI on the different
platforms and by streamlining the disclosure of GI information. Start this process
with connecting between BISE, NWRM and Climate-ADAPT.
When?: Mid-term for BISE, NWRM and Climate-ADAPT, more long-term for other
platforms.
Who?: At the onset, DG ENV and EEA. For the long-term, representatives of the
other platforms.
Technical advice: Considering this is a manual option, technical advice is not
applicable.
Governance: For each platform, agreement is needed on doing this and also on
who will be doing this (budget-wise). For example, a connection can be made
from BISE to a variety of other platforms. The vice versa operation will require
approval and efforts by the other organisations.
Roadmap: This could be something that grows, with mid-term efforts for
connecting BISE, NWRM and Climate-ADAPT and more long-term efforts for other
platforms. It is not sufficient to have this as a one-time investment. Indeed, this
action requires follow-up and maintenance of the links that are established.
Budget: If many deep links are installed and require maintenance, this will result
in a long-term budget need. Also, it needs to be addressed who will cover the
costs.
Risks: When a platform is redesigned or pages are differently located, links will
need to be renewed. In short, there is a high risk that links will not function after
some time.
3.5.5 Long-term: machine to machine communication
Linking data distributed across the Web requires a standard mechanism for specifying
the existence and meaning of connections between items described in this data. This
mechanism is provided by the Resource Description Framework (RDF).
Key is that RDF provides a flexible way to describe things in the world – such as
people, locations, or abstract concepts – and how they relate to other things. These
statements of relationships between things are, in essence, links connecting things in
the world.
While most websites have some degree of structure, the language in which they are
created, HTML, is oriented towards structuring textual documents rather than data. As
data is intermingled into the surrounding text, it is hard for software applications to
extract snippets of structured data from HTML pages.
To address this issue, a variety of microformats (http://microformats.org/) have been
made. Microformats can be used to publish structured data describing specific types of
entities, such as people and organizations, events, reviews and ratings, through
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embedding of data in HTML pages. As microformats tightly specify how to embed data,
applications can unambiguously extract the data from the pages. Weak points of
microformats are that they are restricted to representing data about a small set of
different types of entities; they only provide a small set of attributes that may be used
to describe these entities; and that it is often not possible to express relationships
between entities, such as, for example, that a person is the speaker of an event,
rather than being just an attendee or the organizer of the event. Therefore,
microformats are not suitable for sharing arbitrary data on the Web.
One of the most important implementations of the micro formats technology is in the
Google search engine that has called this Structured Data Markup. "Structured data
markup" is a standard way to annotate your content so machines can understand it.
When your web pages include structured data markup, Google (and other search
engines) can use that data to index your content better, present it more prominently
in search results, and surface it in new experiences like voice answers, maps, and
Google Now.
Structured data markup makes your content eligible for two kinds of Google features:
Enhanced Presentation in Search Results: By including basic structured data
appropriate to your content, your site can enhance its search results with Rich
Snippets, Breadcrumbs, or a Sitelinks Search Box.
Answers from the Knowledge Graph: If you are the authority for certain content,
Google can treat the structured data on your site as factual and import it into the
Knowledge Graph, where it can power prominent answers in Search and across
Google properties. Features are available for authoritative data about
organizations, events, movie reviews, and music/video play actions.
More about Google Structured data markup is available here:
https://developers.google.com/structured-data/
The example of Structured Data service from Google may provide a means to expose
data on GI to other machines. This would involve:
To create a microformat standard library covering as much as possible GI data
and relations between data entities;
Enrich the pages on all considered GI platforms/websites, i.e. markup each page;
Explore websites and expose data in data warehouses with slight modifications of
existing RDF based technologies in use by EEA. These modifications would relate
to grabbing the microformat data markups of the pages.
When immediately available in data warehouses, this data may be exposed as a
service to other websites to be consumed via, for example, SPARQL endpoints.
Having an SQPARQL endpoint with GI data, users may use, for example, already
implemented Drupal mechanism to query and expose this information. There are
a series of YouTube presentations of how to do this: https://www.youtube.com/watch?v=RwY_2kmOgUc https://www.youtube.com/watch?v=AsWPm0vpmoI
A more generic approach to making structured data available on the Web are Web
APIs. Web APIs provide simple query access to structured data over the HTTP
protocol. High profile examples of these APIs include the Amazon Product Advertising
API (http://docs.amazonwebservices.com/AWSECommerceService/latest/DG/) and the
Flickr API (http://www.flickr.com/services/api/). The site ProgrammableWeb
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(http://www.programmableweb.com/) maintains a directory containing several
thousand Web APIs.
On the Amazon website the following comment is provided: “Amazon has spent over
ten years and hundreds of millions of dollars developing a world-class web service that
millions of customers use every day. As a developer, you can build Product Advertising
API applications that leverage this robust, scalable, and reliable technology. You get
access to much of the data that is used by Amazon, including the items for sale,
customer reviews, seller reviews, as well as most of the functionality that you see on
www.amazon.com, such as finding items, finding similar items, displaying customer
reviews, and product promotions. In short, Product Advertising API operations open
the doors to Amazon's databases so that you can take advantage of Amazon's
sophisticated e-commerce data and functionality. Build your own web store to sell
Amazon items or your own items.”
From this regard, although more generic, WebAPI may not be considered a pragmatic
approach but a very long term recommendation.
For more on linked data we recommend the following key references:
http://ec.europa.eu/isa/ready-to-use-solutions/index_en.htm; in particular the
section on Highly reusable semantic standards
http://linkeddatabook.com
https://www.youtube.com/watch?v=OM6XIICm_qo
http://www.ted.com/talks/tim_berners_lee_the_year_open_data_went_worldwide
3.6 Further steps for BISE, NWRM and Climate-ADAPT
The analyses and recommendations made in this report were distributed to the
responsible services of BISE, NWRM and Climate-ADAPT. In what follows we provide a
log of what will be next steps and which of the recommendations seem feasible to be
implemented on either of the three platforms. Also, when applicable we have indicated
how issues may be solved or how progress can be made. Before going into the
specifics for each of the three platforms, we also provide here an overview of the
deliverables of the GI contract and make suggestion on how these products can be
displayed on all of the platforms that were reviewed under this task.
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TASK DELIVERABLE DISSEMINATION LEVEL
1a 20 Factsheets on GI Broad dissemination for stakeholders across policy levels, sectors, etc. The sector sheets provide basic backgrounds on GI and its relevance for the specific sectors and can be linked to the policy sectors and also to specific stakeholder groups. The country sheets can have similar purpose, however, with a focus on the national level.
1b Workshop documentation (PDFs, etc.) of 3 sector workshops
Broad dissemination, but with the question on the format and on which of the included information to disclose.
1c Various edited docs of the EU WG GIIR; Minutes of WG meetings
Internal WG (EC has to decide on broader dissemination).
2 - Workshop documentation (PDFs, etc.) of 3 thematic workshops - MOOC (documentation for running an online course on GI)
Dissemination should best be targeted in accordance with the themes and audience of the workshops they were aimed for. That being stated, the presentations are meant to be presented and there is a question of whether they have similar value when just providing them to be read.
In theory the information is interesting for people also to just read; but it is meant to be presented as an online course. Possibly the course can be provided to targeted audiences or at targeted times.
3 Final Task Report Internal use across various EC services. Use for external purposes when connecting to stakeholders. This can mainly be seen as a reflection on the current state of GI
disclosure and a working document for increasing GI visibility.
4 Final Task Report Broad dissemination, but also to specific audiences considering that nine sectors were explored and evaluated independently. The report can be disclosed through BISE; the sector sheets may have value also for the policy sectors or stakeholder groups relating to each of the sectors.
5 Baseline of current EU GI spending TEN-G Assessment
Possibly a wide dissemination for the EC to show what is already being done.
TEN-G assessment: it is up to the EC whether to keep this for internal use or to communicate it at a later stage.
3.6.1 BISE
For BISE, since the first analysis, this platform has already increased in the
information that is provided and the aim is for this platform to grow further in terms of
disclosing GI information. Further, as a service provider hosting the BISE
infrastructure, for EEA there is no conflict from an architectural point of view with
respect to the generic improvement proposals to BISE in sections 3.4 and 3.5.
3.6.2 NWRM
For NWRM most of the recommendations made to the NWRM platform can easily be
done in the next few months. Specifically, in autumn 2015 changes can be made such
as adding an introduction on GI, adding links to external and related information such
as BISE and Climate-ADAPT, fixing the layout and other technical recommendations.
For example, it is also planned during 2015-2016 to:
Improve the following aspects of the platform: fix layout issues for IE 8 to IE 11
users, improve the size of the thumbnails, open documents and external links in
separate windows and improve the search functions.
Improve the accessibility of the data by implementing the INSPIRE Directive by
adding a shapefile with case studies and download service using xls format.
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Include clear references to Green Infrastructure (GI) and climate change
adaptation activities (BISE and Climate Adapt platforms).
Also, NWRM responsible services agree with the recommendations in the report for
BISE and Climate Adapt on the need to make the links with the information included in
the NWRM platform. In this regard it is planned to update the text in the water pages
on Climate-ADAPT by adding these links, which does not prevent from making further
changes as proposed.
With respect to the long-term recommendations made, resources are currently lacking
and the amount of resources needed to successfully make these changes would also
need to be evaluated. Proceeding with this recommendation only starts making sense
when other relevant platforms have also decided to move forward similarly.
The integration of the information on the NWRM platform into WISE should be
considered in the long-term. Information on the planned implementation of measures
coming from the 2nd RBMPs and 1st FRMPs would add to the existing information.
3.6.3 Climate-ADAPT
For Climate-ADAPT we have included full comments by the responsible services
attached in Annex 12 to this report. It has been agreed to have a DG Clima, EEA, DG
ENV meeting to further discuss how to move forward from recommendation to
implementation. Among the various recommendations to be discussed, this may
include looking into how to link GI to ecosystem-based adaptation on the Climate-
ADAPT platform, and vice versa for BISE. Perhaps as a first step one could link the
searches "green infrastructure" and "ecosystem-based adaptation" (EbA). Both
keywords should lead to all the information on both GI and EbA. However, such
retagging may be challenging and also needs to be considered with respect to EEA
migrating the Content Management System of the platform from Liferay to Plone.
From Annex 12 it is clear that several of the recommendations can be implemented by
the responsible services for Climate-ADAPT. It was requested to provide text and link
proposal to the responsible services for Climate-ADAPT. This was done and the input is
included in Annex 13 to this report.
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4 Task 4 - Assessing technical standards and innovation possibilities
Chapter summary
Green infrastructure (GI) is a successfully tested tool for providing ecological, economic and social benefits through natural solutions. GI helps to understand the value of the benefits that nature provides to human society and to mobilise investments to sustain and enhance them. It also helps avoid relying on infrastructure that is expensive to build when nature can often provide cheaper, more durable solutions. GI is based on the principle that protecting and enhancing nature and natural processes, and the many benefits human society gets from nature, are consciously integrated into spatial planning and territorial development. Compared to single-purpose grey infrastructure, GI has many benefits. It can sometimes offer an alternative, or be complementary, to standard grey solutions. GI is therefore very much relevant for a whole set of sectors. Here, a study was conducted for nine sectors, namely, finances, building, water, transport, public health, industry, climate, rural abandonment and energy. For these sectors, we have assessed how technical standards in use by each of these sectors could increase the deployment of GI. This included an exploration of the extent to which GI is currently covered in standards of these sectors, as well as an identification of the gaps, i.e. areas where GI is insufficiently covered in the standards. We thereby investigated in depth the need for (further) harmonising, adapting or developing GI-related standards. For technical standards, we distinguished:
Standards on the performance of physical building blocks, be it a building, a local park or an international river basin. These standards often work with a scoring system. Well-known examples include BREEAM, LEED, DGNB, HQE or the Biotope Area Factor.
Standards on the (development) process or procedure. This type of standard offers a roadmap, a standardised way of working resulting in a set of actions to achieve a pre-defined outcome. Examples are the SEA, EIA and AA procedures in different Member States (MS). Another example is green procurement by administrations.
Standards on the methods one can use to integrate or enhance GI. Technical guidance and codes of conduct in general are part of this category.
The point of departure for the work was the idea that today we are at the start of GI becoming used broadly and that the available information and uptake of GI is very fragmented. Therefore, the output of the work addressed what is happening (overview of initiatives) and what needs to be done (by providing recommendations). When assessing the extent to which GI is included in the standards of the nine sectors, it is expected that GI is often covered as part of sustainability. For several of the sectors GI may be a rather novel concept, indeed. However, all sectors are familiar with sustainability and with standards on sustainability. These standards on sustainability may be the most logical entry for considering inclusion of GI in the standards in use by a sector. Further, for some sectors ‘green’ may have a different connotation. For example, the green in green building refers to sustainable building rather than specifically referring to making use of GI or considering natural or green elements. Therefore, when exploring standards for the nine sectors this broader sustainability spectrum was considered. As for our methodology, a combination was made of literature study, web searches and interviews with representatives of the different sectors. In addition to the evaluation for the nine sectors, it was considered that several initiatives are ongoing. Therefore, representatives of the Joint Research Council and the Institute for Environmental Protection and Research were interviewed on ongoing initiatives. Where relevant, these initiatives were included in the sector fact sheets or in the general outcomes of the report. Based on the various inputs, sector sheets were developed clarifying the current state for the sector and commenting on the possible way forward for the sector. These sector sheets include concrete recommendations regarding:
The need for harmonization between standards;
The potential for including or strengthening the concept and principles of GI in the different standard categories (performance, procedure, methodology);
The interoperability between technical standards applied in different project phases (planning, design,
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and construction).
Following the sector sheets, also cross-sectoral recommendations were identified and discussed. In what follows we first comment on four identified cross-sectoral recommendations. Secondly, we highlight for each of the nine sectors the major findings.
Integrated spatial planning: Several sectors (such as climate adaptation, water, land abandonment and infrastructure) have indicated that the implementation of GI would benefit from integrated spatial planning early in the planning process. Also, it has been increasingly recognized that it is necessary to work at the landscape level to ensure that sectors can capture the benefits of GI and to maintain biodiversity and ecosystem services. A landscape approach can contribute to bringing together sectoral economic development plans and national action plans on biodiversity conservation, water management and climate change.
Green procurement: Europe and the Member States’ public authorities are major consumers. By using their purchasing power to choose environmentally friendly goods, services and works, they can make an important contribution to sustainable consumption and production. Therefore, the way GI is included in Green Public Procurement (GPP) will have a major impact on how GI will be considered in activities and businesses. GPP therefore will be key to ensure GI procurement. What may be needed is to develop and establish a GI Public Procurement (GIPP) to include in public tenders the use of GI as innovative solutions presenting a real alternative to traditional grey infrastructure.
Finding the appropriate standard: There is no obvious, simple and non-time consuming way of understanding which standards are most suitable to meet needs. Therefore, users require assistance in finding the ‘needle in the haystack’ standard that matches their needs. A way forward therefore would be to investigate ways to facilitate the search and access to appropriate standards. There could be a role here for sectorial organisations to facilitate for their members the search for appropriate standards and to provide guidance on what can be achieved with which standard. This is indeed already practiced to some extent and shown by several of the references included in this report. In addition, it may be considered to also work on this with the standards-making bodies. Here, possibilities could be explored for a collaborative interactive database with a hierarchical tree facilitating finding appropriate standards and gaining insight into what can be done with shortlisted standards.
Harmonization across infrastructure sectors: Each of the infrastructure sectors (e.g. buildings, transport, energy, water) have their own standards on performance, procedure and methodology. In the past, each of these sectors was mainly operating in isolation from the other sectors. However, over recent years, integrated approaches have become more common. Therefore, it may be seen as an opportunity that the sectors we reviewed have large potential for improving on the way GI is included in standards. Indeed, rather than each sector working on improving the way GI is included there is potential for collaborative action and harmonization across sectors on including GI into standards on performance, procedure and methodology.
Major findings for each of the nine sectors:
Financial sector: Whilst direct lending for biodiversity projects by financial institutions accounts for a limited proportion of financial markets, retail and investment banks as well as institutional lenders are increasingly applying sustainable investment criteria to their loans that incorporate impacts and dependencies on biodiversity and ecosystem services. However the focus is mainly on conservation and restoration of biodiversity values affected by project developments, rather than actively promoting the deployment of GI as part of these project developments. Even the substantial benefits of GI in the field of climate change adaptation (such as flood risk reduction) are until now largely undervalued by financial and insurance companies. As a consequence, there is substantial room for improvement, starting with increased efforts in awareness raising of the sector, in particular about the long-term financial benefits of GI. Other opportunities are the uptake of GI in performance standards applied by the sector.
Building sector: There is a plethora of sustainability standards in the buildings sector across Europe with varying levels of requirement. Few are known to be legally required but they can often be mandated at country, region, city or local level. Building sustainability standards focus primarily on materials and energy performance and where biodiversity requirements exist they are often not mandated, carry little weight and do not promote high levels of biodiversity. Where GI is integrated into buildings, it often is limited to green roofs, with little focus on other elements of the building or surrounding area to integrate GI. Building standards have an architectural focus with GI almost as an afterthought. Developments that have taken place in the context of green roofs may provide inspiration for broader inclusion of GI in the building process.
Water sector: In the water sector procedural standards for sustainable water management in Europe are available through the Water Framework Directive. In the private sector there is a growing
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awareness for proactive investment in sustainable management water in the catchment in which companies operate. Although GI is not always explicitly mentioned, the application of GI fits well in the ecosystem and catchment based approaches. As a way forward for the implementation of GI it is important to incorporate both ‘green’, ‘grey’, and also hybrid solutions in the initial assessments of options in such a way that actors can compare and make the best choice for their situation. At the moment, there are often already established criteria to evaluate the performance of the more conventional grey options, but not so for GI or for comparing across grey and green options. This forms a barrier for the wider implementation of green options.
Transport sector: Transport infrastructure, in particular road and railway systems, form widespread networks with varying density all over the EU. They have tremendous impacts on biodiversity, both at a local and regional scale. Most visible impacts are collisions with animals. Yet more consequential are the indirect effects of transport infrastructure, including habitat loss and reduced habitat quality (e.g. increased noise levels), habitat fragmentation and barrier impacts. As these impacts often occur simultaneously, the cumulative effects on wildlife populations can be very significant. There is a significant quantity of guidance and good practice on how to address fragmentation and barrier effects by means of overpasses or fauna tunnels etc., which in some cases are supported by GI measures. Also at a landscape level GI offering improved habitat connectivity is often applied as part of wildlife and landscape management, and increasingly incorporated into regional spatial planning. However, guidance on how to reconcile transport networks with ecological networks at a regional scale is very scarce. The same goes for guidance on how to optimize the ecosystem services provided by GI to mitigate impacts of transport infrastructure on biodiversity.
Public health sector: In the public health sector there are many standards, guidelines and protocols outside the scope of the GI/health domain. Examples are safety standards (toxic species, allergenic species, risks of falling branches, pesticide use etc.). Accessibility standards that recommend the availability of GI for citizens form an exception. However, there is a growing body of literature linking GI to human health and wellbeing, but the underlying mechanisms are poorly understood and the knowledge tends to remain in the green sector, not penetrating the health sector. Exceptions are some SMEs and bottom-up local initiatives bridging the gap between the green sector and the health sector. There is a large potential for GI standards for the health sector, but before standardization can take place, the evidence base has to grow stronger, and the results must be dissipated within the health sector rather than only in the green sector.
Industry sector: The industry sector is very familiar with sustainability standards. Although biodiversity, as part of sustainability, has been a rather neglected issue for a long time, the recent increase in specific biodiversity guidance for industry shows a growing interest in the field of ‘business and biodiversity’. However, when zooming in on the topic of GI within this growing amount of biodiversity standards, it’s clear that there is room for improvement. Particular issues which deserve more attention are costs and benefits of GI in an industrial context, as well as guidance on how to implement GI.
Climate sector: Many examples of tools, guidelines and best practices already exist on how to apply GI, or nature-based solutions, in the context of climate change adaptation. Performance standards, which are common practice in for instance the building world, are not a useful way forward in the climate adaptation sector. The reason for this is that the local situation is always too specific. The multi-functionality of GI is a benefit but it makes planning and implementation of GI at the same time very difficult. Integrating a GI framework into Environmental Impact Assessments might be a way forward, as this would guarantee that the potential of GI in landscape planning is considered.
Rural abandonment: GI can offer solutions for both the prevention of farmland abandonment and for minimizing the negative impacts when farmland is already abandoned. There are no specific GI standards in the context of rural abandonment. An indirect way to stimulate GI in rural abandonment areas is for instance through the Common Agricultural Policy (CAP) funding scheme or European structural funds.
Energy sector: Terrestrial energy infrastructure consists of energy production facilities (hydropower, windfarms, gas and coal based power plants, nuclear power plants) as well as the energy transmission infrastructure (oil and gas pipelines, electricity grid). As a consequence, possibilities for developing GI are quite diverse and rather specific for each type of energy infrastructure. The energy sector is under full development and is characterized by increasing investments in renewable energy as well as in electricity transmission infrastructure in the EU. But also existing energy infrastructure is being revitalized. The energy sector might benefit from investments in GI for various reasons, ranging from reducing risks (operational, reputational) to grasping opportunities (cost reduction, reputational), depending on the type of investments. Due to the variety of energy infrastructure generic GI standards for the energy sector are not available, but there are a number of specific standards available.
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Introduction
This project aimed to assess how technical standards (see Box 4), particularly in
relation to performance, methodologies and procedures, could increase the
deployment of Green Infrastructure (GI). This included an exploration of the extent to
which GI is currently covered in standards, as well as an identification of the gaps, i.e.
areas where GI is insufficiently covered in standards. We thereby investigated in depth
the need for (further) harmonising, adapting or developing GI-related standards. In
line with the deliverables that have been completed under Task 1 of this contract, our
work was mainly focused on exploring standards and GI for the different sectors
covered under Task 1: namely, finance, buildings, water, transport, public health,
industry, climate, rural abandonment and energy. Job creation is not included here,
considering that it is not a sector, but a topic across sectors.
Expected outputs of the work were:
a) An insight into the current uptake of GI in standards applied by the various
sectors;
b) Overview of possibilities for improving technical standards, including
harmonization and interoperability between technical standards applied in
different project phases (planning, design, and construction).
Box 4 Terminology
GI in the context of this contract is defined as follows: Green Infrastructure “is a strategically planned network of natural and semi-natural areas with other environmental features designed and managed to deliver a wide range of ecosystem services. It incorporates green spaces (or blue if aquatic ecosystems are concerned) and other physical features in terrestrial (including coastal) and marine areas. On land, GI is present in rural and urban settings.”80 Linked together, these strategically planned networks of green elements are able to provide multiple benefits in the form of supporting a green economy, improving quality of life, protecting biodiversity and enhancing the ability of ecosystems to deliver services such as disaster risk reduction, water purification, air quality, space for recreation and climate change mitigation and adaption. Standards on performance, procedure and methodology are distinguished:
Performance: Standards on the performance of physical building blocks81, be it a building, a local park or an international river basin. These standards often work with a scoring system. Well- known examples include BREEAM, LEED, DGNB, HQE or the Biotope Area Factor.
Procedure: Standards on the (development) process. This type of standard offers a roadmap, a standardised way of working resulting in a set of actions to achieve a pre-defined outcome. Examples are the SEA, EIA and AA procedures in different Member States (MS). Another example is green procurement by administrations.
Methodology: Standards on the methods one can use to integrate or enhance GI. Technical guidance and codes of conduct in general are part of this category.
80 Communication from the European Commission to the European Parliament, the Council, the Economic and Social Committee and the Committee of the Regions: Green Infrastructure (GI) – Enhancing Europe's Natural Capital, COM (2013) 249 final. 81 According to the Technical Document supporting the Communication on GI ‘physical building blocks’ are the network of green spaces in which and through which natural functions and processes are sustained
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4.1 Problem analysis and objectives of Task 4
One of the actions of the GI Strategy as outlined in the Communication on GI is
‘Improving information, strengthening the knowledge base and promoting innovation’.
More specifically “by 2013, the Commission will assess the need and the opportunities
in the context of Horizon 2020 to (…) develop and encourage innovative technologies
and approaches to facilitating the development of GI. It will also assess the
contribution technical standards, particularly in relation to physical building blocks and
procedures, could make to ‘growing the market’ for GI-friendly products.” Task 4
aimed to cover this part of the action described above. In particular, under task 4 it
was assessed how and under which circumstances technical standards could increase
the deployment of GI.
Including GI in technical standards may create a huge leverage effect in the
deployment of GI on the ground. In this context, technical standards not only apply to
design specifications of physical elements (such as green roofs, eco-ducts, etc.) but
also to methodologies such as spatial planning, and to procedures such as (if
applicable) SEA, EIA and AA. Incorporating attention to GI from the very early
planning phase (SEA, spatial planning) to the project design phase (including EIA,
technical standards for buildings, water infrastructure, etc.) and final project approval
(permitting phase) will contribute substantially to GI implementation, and as such to
new GI markets.
The point of departure for the work in this task was the idea that today we are at the
start of GI becoming used broadly and that the available information and uptake of GI
is very fragmented. Therefore, the output of the work addressed what is happening
(overview of initiatives) and what needs to be done (by providing recommendations).
Under this task, nine sectors (finances, buildings, water, transport, public health,
industry, climate, rural abandonment and energy) were explored in more detail, in
particular with regard to the extent GI is included in the standards they use and the
actions that can be taken to further strengthen the uptake of GI. With respect to the
latter this included (1) determining best practices, (2) identifying promising fields to
make progress and (3) addressing how to implement improvements. Also, the
repercussions and possible bottlenecks of using GI in relation to issues such as
legislation and safety issues were assessed.
A distinction was made between three types of standards: standards on performance,
procedure and methodology (see Box 4 on how these are defined in the context of this
study). When evaluating these standards it is clear that a wide spectrum of GI
developments are covered, from small local projects (e.g. a green roof) to large-scale
cross-border projects (e.g. ecological corridors). Indeed, the types of physical features
that contribute to GI are diverse, specific to each location or place and very scale-
dependent. On the local scale, biodiversity-rich parks, gardens, green roofs, ponds,
streams, woods, hedgerows, meadows, restored brown field sites and coastal sand-
dunes can all contribute to GI and may deliver multiple ecosystem services.
Connecting elements are for example green bridges and fish ladders. On the regional
or national scale, large protected natural areas, large lakes, river basins, high-nature
value forests, low intensity agricultural areas, extensive dune systems and coastal
lagoons are just a few of many examples. On the EU scale, transboundary features
such as international river basins, forests and mountain ranges are examples of the
EU’s supranational GI.
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4.2 Setting
4.2.1 Advantages and disadvantages of working with standards
A standard is a repeatable, harmonised, agreed and documented way of doing
something. Standards contain technical specifications or other precise criteria
designed to be used consistently as a rule, guideline, or definition. They help to make
life simpler and increase the reliability and the effectiveness of many of the goods and
services we use.82 Standards result from collective work by experts in a field and
provide a consensus at the time when the standards are developed. As standards in
the international arena are established on a consensus and broad stakeholder basis,
they represent what can be agreed upon. A published standard is therefore the
harmonised synthesis of what the group is prepared to publish. International
standards bring technological, economic and societal benefits83. They help to
harmonize technical specifications of products and services, making industry more
efficient and breaking down barriers for international trade. Compliance to
international standards in the field of environment helps to reassure consumers that
products are good for the environment. Over the years the International Organization
for Standardization (ISO) has made significant efforts to provide proof on the benefits
that standards bring to organizations and, more generally, to citizens and society84. To
illustrate, we indicate some advantages and disadvantages of working with standards
(Table 6). The following sections describe in more detail which strengths and
weaknesses can be identified in relation to the way GI is covered in standards applied
by different sectors.
Table 6: Examples of benefits and disadvantages of working with standards
Benefits of working with standards Disadvantages of working with standards
They set the recognised level of quality The implementation of standards may remove the creative element
May lead to reduced market risks Standards may force people to change their methods
May lead to market growth for new and emerging technologies
Standards reduce productivity by forcing unnecessary actions
May lead to reduced development time and costs and increased productivity and enhanced efficiency
Registration requires an amount of money, time and paperwork
Facilitation of common language and understanding of what the product or service is or is not.
Standards do not prevent bugs
4.2.2 Broader context: sustainability
When assessing the extent to which GI is included in the standards used by the
identified nine sectors, it is expected that GI is often covered as part of sustainability.
For several of these sectors GI may be a rather novel concept. However, all sectors
are familiar with sustainability and with standards on sustainability. These standards
on sustainability may be the most logical entry for considering including GI in the
standards in use by a sector. Also, for some sectors green may have a different
82 Amended from BSI website: What is a standard? http://www.bsigroup.com/en- GB/standards/Information-about-standards/what-is-astandard/ 83 http://www.iso.org/iso/home/standards/benefitsofstandards.htm 84 http://www.iso.org/iso/home/standards/benefitsofstandards/benefits_of_standards.htm
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connotation. For example, the green in green building refers to sustainable building
rather than specifically referring to making use of GI or considering natural or green
elements. Therefore, when exploring standards for the nine sectors this broader
sustainability spectrum was considered.
4.3 Methodology
To approach the work in Task 4 a combination was made of literature study, web
searches and interviews with representatives of the different sectors. The literature
study and web searches were both supporting the preparation of the interviews, the
contextual framing of the outcomes and the formulation of recommendations. The
preparatory work in advance of the interviews included the collection of information on
standards applied by a sector as well as a first evaluation of the extent to which GI is
included in these standards. As mentioned before, for this evaluation a distinction is
made between standards on performance, procedure and methodology. Following this
preparatory work, sector representatives were interviewed. The purpose of these
interviews was to find out if well-placed sector representatives could confirm the
outcomes of the preparatory work and to gain additional insights, for instance on the
potential for including GI more strongly in future updates of the standards. Based on
the literature study, web searches and the interviews, sector sheets were developed
clarifying the current state of the sector and commenting on the possible way forward
for that sector. These sector sheets include concrete recommendations regarding:
The need for harmonization between standards;
The potential for including or strengthening the concept and principles of GI in the
different standard categories (performance, procedure, methodology);
The interoperability between technical standards applied in different project
phases (planning, design, and construction).
As the aim was not to carry out a statistical study, but rather a qualitative study with
useful recommendations on how including GI within standards can improve the
deployment of GI, interviews did not necessarily follow identical questions for each
sector or organisation. Outputs from interviews that took place in an early stage
guided later interviews. Nonetheless, as interviews were done by several people, it
was decided to prepare a standard set of questions (see Box 5), and to use this set as
a guidance for conducting the interview, rather than as a strict scheme to be
thoroughly followed. Further, when arranging for the interview, representatives were
informed on what GI is and how we defined the different standards on performance,
procedure and methodology. This introduction to essential terminology was done by
sharing the content of Box 4 and by verifying whether this content was clear when
starting the interview.
Box 5 Type of questions (non-limitative) to be covered during the interviews
1. Does your sector make use of standards and do these standards include GI? 2. Which are the most important standards in your field of work (if possible on
performance/procedures/methodologies)? Do they yet include GI and to what extent? If not, would these benefit by GI being included? Why?
3. What is the importance of standards in your line of work (very high, high, moderate, low, and very low) (overall + for performance/procedures/methodologies)? Why?
4. Have you experience with standards having a positive impact on GI (yes/no). Why? 5. What are the key elements of a good standard for GI according to you? 6. Do you have suggestions on examples of good GI standards? 7. Do you have examples on GI standards that are not so effective? 8. Are there in your opinion instances were GI currently is not included or covered in standards and
could be a welcome addition? 9. Are you aware/involved in initiatives to harmonize GI standards over the sector? For which
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standard(s)? 10. Have you experienced a situation where the harmonization of standards on GI would have been
beneficial to GI development? 11. What are the main benefits of harmonisation according to you? What exactly should the
standard/harmonisation exercise tackle? 12. What are the threats of harmonization of standards according to you? 13. What are the main steps to be taken in the context of GI standards in your opinion (regional or
national level)? (short, mid, long-term) 14. What are the main steps to be taken in the context of GI standards at the EU level? (short, mid,
long-term) 15. Do you have final recommendations on GI standards? 16. Optional: share a table on the different standards resulting from the literature review and web
search and work on that during or following the interview.
Prior to the interview a working table was made based on the literature and web
search on the extent GI is covered in standards in use by each sector. During the
interview the working table was verified and the scoring adjusted (see Table 7). When
finalised, the table will provide insight in how strongly GI is included today in
standards on performance, procedure and methodology applied by the different
sectors.
Table 7: Working table for interviews
Sector Performance Procedure Methodology
Finances
Building
Water
Transport
Public health
Industry
Climate
Rural Abandonment
Energy
[Note: For each of the nine sectors it is indicated as a working hypothesis to what extent GI is included in standards on performance, procedure and methodology (green: fairly well covered; orange: rather basic; red: little or lacking).]
For each sector the aim was to interview at least one representative, and when
possible to have 2-3 interviews in total. In Table 8 we indicate the different sector
representatives that were included in the interviews. For each of the interviews, a
small report is included in Annex 14.
Table 8: Overview of sector representatives that were interviewed in the context of GI and standards
Sector Representatives
Finance Gavin Templeton (Green Investment Bank)
Buildings Dusty Gedge (European Federation of Green Roof Associations)
Maarten Dansen (Dutch Green Building Council)
Water Maija Bertule (UNEP-DHI Partnership)
Transport Carme Rosell (Infra Eco Network Europe (IENE))
Philip Charles – Operations Director and Ian Nicholson – Technical Director (Civil
Engineering Environmental Quality Assessment and Award Scheme (CEEQUAL))
Public health
Patrick Ten Brink (Head of the Green Economy Programme of the Institute for
European Environmental Policy (IEEP) and project leader of the Health and
Social Benefits of Nature and Biodiversity Protection project for DG
Environment)
Jasperina Venema (green entrepreneur and advisor specialized in urban green
and health)
Sjerp de Vries (senior scientist green health, Alterra Wageningen University and
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Research Centre)
Industry Violaine Berger (World Business Council on Sustainable Development)
Climate Stefan Kleeschulte (Managing Director of Space 4 Environment)
Rural abandonment
No interview was taken considering that rural abandonment not really qualifies
as a sector. The opposite, intensified agriculture indeed is a sector, but falls
outside of the scope here.
Energy Simon Devoghele (LIFE Elia)
In addition to the evaluation for the nine sectors, it was considered that several
initiatives were ongoing and related to the current project on GI. Therefore,
representatives of the Joint Research Council (JRC) and the Institute for
Environmental Protection and Research (ISPRA) were interviewed on ongoing
initiatives. Where relevant, these initiatives were included in the sector fact sheets or
in the general outcomes in the report. Highlighted initiatives by JRC and ISPRA
included:
Green Procurement and road construction;
Standards for constructions and structural design;
Resource efficiency indicators for buildings, with a potential to include GI
indicators;
Safety in relation to including GI.
Furthermore, the European Commission indicated to consider ecosystem services
(MAES working group (Mapping and Assessing Ecosystem Services)), climate change
adaptation (the European Commission’s Directorate General on Climate) and
defragmentation measures for road development (IENE, see also contact for transport
in Table 8).
By combining the information gathered during the literature, web search and
interviews, uniform sectorial fact sheets were produced (see template in Box 6).
Box 6 Template for sector sheets
Page 1 covers the following five elements:
Major findings/conclusion on the extent GI is included today and the possible steps forward (3-4 lines).
Table with examples of standards. The aim was not to provide an exhaustive overview of standards, but rather to show a selection of representative examples of standards on performance, procedure and methodology.
Major outcomes of the interview(s): 3-5 highlights.
The extent GI is integrated in standards and the potential, with a focus on the potential.
Recommendations on the way forward for the sector
Next page(s): major outcomes with respect to GI and standards on performance, procedure and methodology. Here, there is room to provide more detail on the standards that are included in the table on the first page. This section should be a summary overview of the standards and where they apply and the way GI is included or can be included. Understanding the scale and status of the standards is also important, as well as the uptake/market share of the standards and whether the standards compliment/contradict/elevate requirements beyond applicable regulations.
In the final section, we conclude with highlighting some major cross-sector
recommendations, i.e. recommendations that are considered more general and not
specific to a single sector.
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4.4 Overview of standards for GI for different sectors
4.4.1 GI standards and the financial sector
Whilst direct lending for biodiversity projects by financial institutions
accounts for a limited proportion of financial markets, retail and
investment banks as well as institutional lenders are increasingly
applying sustainable investment criteria to their loans that
incorporate impacts and dependencies on biodiversity and ecosystem
services. However, the focus is mainly on conservation and
restoration of biodiversity values affected by project developments,
rather than actively promoting the deployment of GI as part of these
project developments. Even the substantial benefits of GI in the field
of climate change adaptation (such as flood risk reduction) are until
now largely undervalued by financial and insurance companies.
Consequently, there is substantial room for improvement, starting
with increased efforts in awareness raising of the sector in particular
about the long-term financial benefits of GI. Other opportunities are
the uptake of GI in performance standards applied by the sector.
Table 9: Examples of standards applied by the financial sector with indication on the degree of GI coverage (green: GI well covered; orange: GI moderate to basically; red: GI hardly or not covered)
Type Standard Key aspects G I
Performance Natural Capital Declaration (NCD)85
This is a commitment by a limited number (+/- 40) of finance and insurance companies to work towards integrating natural capital and biodiversity criteria into their products and services. The NCD was born out of the insight that financial institutions could benefit from greater guidance to embed specific aspects of environmental, social and governance (ESG) factors in their management, due diligence, loans, investments and insurance activities. While GI is not mentioned it is highlighted that the services nature provides underpin productivity and the global economy. It is open for new signatories since 2012 but apparently the number of signatories is not increasing.
Equator Principles86
The Equator Principles is a risk management framework, adopted by financial institutions, for determining, assessing and managing environmental and social risk in projects. It is primarily intended to provide a minimum standard for due diligence to support responsible risk decision-making. The Biodiversity for Banks (B4B) program is designed to help financial institutions overcome the challenges of incorporating risks associated with biodiversity and ecosystem services into their lending decisions. Here links are provided to a variety of initiatives linked to biodiversity conservation and valuing ecosystem services, however, leaving it to the user to be explored and interpreted. Considering its focus on risks, the framework could be improved by also considering the opportunity perspective of ecosystem services and how working with nature can drive business performance.
International Finance
This is a standard for ‘Biodiversity Conservation’ and ‘Sustainable Management of Living Natural Resources’ adhered
85 http://www.naturalcapitaldeclaration.org/the-declaration 86 http://www.equator-principles.com/
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Corporation Performance Standard 687
to by several major financial institutions. Performance Standard 6 recognizes that protecting and conserving biodiversity, maintaining ecosystem services, and sustainably managing living natural resources are fundamental to sustainable development. In essence the standard is mainly on risks and impacts and only to a limited extent considers GI and the ecosystem services that go with it provide as a business opportunity.
The European Investment Bank Statement on Environmental and Social principles and Standards88
The Statement outlines the standards the EIB is imposing on projects that it finances, and the responsibilities of the various parties. It provides a great sense of urgency about the problems of climate change and gives great recognition to the importance of biodiversity. However the emphasis is on conservation or restoration of biodiversity (according to the mitigation hierarchy), rather than promoting GI as an opportunity to enhance biodiversity and deliver ecosystem services. As the EIB is periodically reviewing this standard to align with new developments under the EU environmental policy and legislation, there might be a chance that future versions put more emphasis on GI.
Procedure Triodos Bank89 The Netherland’s Triodos Bank has established a leadership position in Europe as a provider of retail banking services with a focus on sustainable investment. Triodos Bank has lending criteria for companies operating in sectors with a high risk of negative effects on biodiversity. This approach ensures that businesses have a policy to identify and manage these risks. The list of these companies is published on Triodos’ website. Company performance is reviewed periodically and companies can be removed from this list where they do not meet sustainability criteria. At the same time, Triodos Bank focuses on financing enterprises that protect and encourage biodiversity.
ASN Bank Biodiversity approach90
The ASN Bank has elaborated investment criteria for biodiversity in its issue paper Biodiversity, which it applies for all its investment policies. Sectors that have a negative impact on biodiversity are excluded or are required to show more engagement. ASN Bank’s investment policy also enables them to improve the conservation of species and ecosystem services, for example by investing in the establishment of new forests or even new nature reserves, which is nothing else than investing in GI. The bank has not yet established a policy which takes into account the positive impact of companies on biodiversity. The ASN Bank wishes to develop such a policy together with other financial institutions interested in making a positive impact on natural capital.
Natural Capital Financing Facility91
This is a new financial instrument with a focus on risk-pooling of Natural Capital projects in the areas of PES, GI, biodiversity offsetting and pro-biodiversity business. A key criterion for inclusion of projects within the NCFF Pipeline is that the project design needs to demonstrate either a viable revenue stream or cost savings to the beneficiary, which will to support repayment of the finance provided.
The Environment Bank Ltd.92
This is a UK company which acts as a broker and delivery agent in emerging markets for environmental assets, in particular biodiversity offsetting. It has developed a unique and innovative business model in this respect. EBL is currently operational in the UK but is looking to extend its business operations to other European countries. Research for the Ecosystem Markets Task Force estimated that biodiversity offsetting could deliver 300,000 ha of ecological
87 www.ifc.org 88 http://www.eib.org/attachments/strategies/eib_statement_esps_en.pdf 89 https://www.triodos.com/ 90 https://www.asnbank.nl/web/file?uuid=760e2f4f-c742-40c9-82dc-f7d4204f9d0b&owner=9ccef6a9-c451- 451a-963a-e931fe46c086&contentid=2214 91 http://ec.europa.eu/environment/biodiversity/business/assets/pdf/ncff.pdf 92 http://www.environmentbank.com/
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creation/restoration over 20 years in England alone.
Methodology WBCSD Business Guide to Natural Infrastructure
The WBCSD is preparing a business guide on natural infrastructure (= GI) including the financial institutions as a target audience. This guide will include the business case, case studies, fact sheets on existing tools, decision tree and check list. GI is thereby seen as a cost-effective investment opportunity and solution to benefit from a range of ecosystem services for issues material to companies.
Swiss Re Swiss RE is one of the globally leading re-insurance companies. They are very aware of the risks related to natural disasters as a consequence of climate change and are developing decision- support tools to pro-actively manage total climate risk. The ‘economics of climate adaptation’ methodology as implemented in Climada93 provides decision makers with a fact base to understand the impact of climate on their economies - and identify actions to minimize that impact at the lowest cost to society. Using state-of-the-art probabilistic modelling, it estimates the expected economic damage as a measure of risk today, the incremental increase from economic growth and the further incremental increase due to climate change. It then builds a portfolio of adaptation measures (including ecosystem based ones), assessing the damage aversion potential and cost-benefit ratio for each measure. The adaptation cost curve illustrates that a balanced portfolio of prevention, intervention and insurance measures allows to pro-actively manage total climate risk. This methodological approach is underpinned by the climate change adaptation benefits of GI.
Interview highlights
An interview took place with Gavin Templeton, Head of Sustainable Finance of Green
Investment Bank (GIB). The following issues can be highlighted:
GIB only invests in sustainable projects (until now £2.1 billion investments in the
private sector), such as biomass, energy efficiency, wind energy. They call it
‘green’ infrastructure projects, but it has a completely different meaning than
what is covered under the GI definition as described in the EC Green
Infrastructure Communication. In fact, although the projects they are investing in
are indeed very sustainable, they have not invested yet in GI.
GIB’s 7 Green Investment Principles (Positive contribution to a recognised green
purpose; Reduction of global greenhouse gas emissions; Enduring green impact;
Clear and firm investment criteria; Robust green impact evaluation; Effective
covenants, monitoring and engagement; Transparent reporting) ensure a
commitment to working in an open and transparent way so that investors can be
assured in their investment. Therefore, standardisation of standards can only
assist and encourage use of GIB.
Extent GI is integrated in standards and the potential
The links between financial services, risk and biodiversity (and also climate change)
have, to date, been weak. Resource scarcity, loss of biodiversity and degradation of
ecosystem services such as freshwater availability have, however, started to present
financially material risks and opportunities for bankers, investors and insurers. This is
particularly the case with financial institutions that have a large exposure or client
base in industries directly dependent on biodiversity and ecosystem services, such as
fisheries, agriculture, forestry and tourism, and industries with major biodiversity
footprints, such as the extractive sectors.
93 Climada - the open-source Economics of Climate Adaptation (ECA) tool: https://github.com/davidnbresch/climada/wiki
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At present many financial institutions do not sufficiently understand, account for and
therefore value, the risks and opportunities related to natural capital in their financial
products and services (loans, investments and insurance products) and in their supply
chains. If biodiversity is considered, it is mainly within the philanthropic and
sponsoring domain. Some financial institutions, however, have started to
systematically look into the ecological footprint and exposure to disruptions within the
supply chain, and some banks have developed specific expertise in this area (e.g.
Triodos Bank).
The overall conclusion is that, despite a number of very interesting initiatives (e.g.
Natural Capital Declaration), the uptake of natural capital as a material issue by the
private financial sector is rather poor. Standards related to biodiversity do exist, but
they are only applied by a very limited number of financial companies (e.g. NCD) or
only applied by the International Financial Institutions (IFIs), such as the World Bank
and the EIB. As a result the standards listed in the table above cannot be considered
as standards with a widespread uptake by the financial sector, but – on the contrary –
as standards applied by a minority of the financial sector. And even within this
minority group the promotion of GI as a business opportunity is largely lacking.
Exceptions are the Natural Capital Financing Facility and a number of green banks
(such as Green Investment Bank) and insurance companies. Insurance and re-
insurance companies face huge risks due to the expected increased frequency and
severity of extreme weather hazards, enhanced by climate change. Therefore the
preservation of healthy ecosystems with natural storm regulatory capacities is also in
their interest (e.g. coral reefs and mangroves that mitigate the impact of storm waves
on coastal areas, natural flood areas along river systems).
Way forward
As impacts of climate change and ecosystem degradation will increasingly affect
business performance, it can be expected that financial institutions will pay more
attention to the natural capital impacts and dependencies of companies. Financial
institutions will start realizing that companies with a strong biodiversity policy have
less financial risk and are also performing better on financial and reputational (e.g.
Dow Jones Sustainability index) indices. This is confirmed by the WBCSD, who signals
an important role for banks and accountants as change agents in the transition to the
incorporation of natural and social capital in the governance of companies. The
importance of GI as an effective solution to mitigate the impacts of extreme weather
events and natural hazards due to climate change is already acknowledged by some
re-insurance companies. But there is still a way to go to enhance the uptake of GI by
the financial sector as a tool for decreasing business risks. The Natural Capital
Financing Facility of the EIB is a major step forward, as it aims to explore viable
business models of ecosystem restoration, acknowledging the important role of GI.
On a longer term – considering the variety of initiatives – it would be beneficial to
increase the harmonization of lending or investment criteria against recognized
standards to add credibility and accelerate GI uptake. This may be promoted by a
wider input from the financial community (alongside the conservation community) in
the development and refinement of standards.
Major findings on standards for performance elements
A number of biodiversity related performance standards have been developed and
are applied by the financial sector. However these standards mainly focus on
biodiversity conservation and restoration of biodiversity damage rather than on
actively promoting the deployment of GI. A second observation is that these
standards are not widely applied within the financial sector. Apart from the
international financial institutions and some niche banks profiling themselves as
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green banks, the vast majority of the private financial sector does not take
biodiversity into account in its lending and investment operations.
Non-financial reporting is now mainstream among large companies with the
majority regularly providing reports on their environmental impacts and
performance. This improved reporting informs rating agencies on these
companies’ risks, helping investors to better steer their investment portfolio.
However, reporting on biodiversity and ecosystem services, and even more so on
GI, is relatively underdeveloped in this regard.
Various elements of the financial sector have different roles to play in
championing biodiversity. The development of common standards rewards ‘first
movers’ in the financial sector providing support or advisory services to pro-
biodiversity business. At a higher level, forward-thinking organizations are
increasingly grouping together within associations to promote greater
transparency within and between financial institutions relating to biodiversity,
whilst a number of major stock market indices are launching specialist
biodiversity metrics so as to better inform investors on the exposure of their
investments to biodiversity related risk.
Major findings on standards for procedures
Several green banks have established procedures for screening companies and
projects in the framework of their lending and investment operations. For this
purpose they have set up a number of biodiversity related criteria. Analogous to
performance standards the focus is rarely on opportunities to invest in GI. There
are a few exceptions such as the Natural Capital Financing Facility and the
Environment Bank.
The Natural Capital Financing Facility, financed by the EIB and the EU LIFE fund,
has been created exactly to cover the current gap in possibilities provided by
financial institutions in the field of investing in ecosystem restoration, amongst
which investing in GI. Hopefully the pilot projects which will be supported with
advantageous loans in the coming years, will demonstrate the financial benefits of
investing in GI, and as such open up the market for it in the coming decades.
Because the benefits of GI are usually shared between the public and private
sectors, and provide long-term, relatively low-risk returns on investment, there is
a strong case for public-private partnership models of delivery, whereby risk and
returns are spread over time.
A specific type of banking is habitat banking, and this is the field of play of
organizations such as The Environment Bank. If the concept of habitat banking
exceeds the purely obligatory biodiversity offsets and achieves to create
additional nature, it would definitely enhance the further deployment of GI.
Major findings on standards for methodology
Financial institutions are active mainly on standards that relate to performance
and to some extent also on procedure. They are usually not involved in
developing handbooks or manuals on how to include GI into business or
governmental activities. An exception is the recently developed Climada tool by
Swiss Re. Another example is the WBCSD guidance on Investing in Natural
Infrastructure, which is also intended for use by financial institutions. It contains a
well elaborated business case, as well as case studies and tools which can support
decision-making by businesses.
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4.4.2 GI standards and the building sector
There is a plethora of sustainability standards in the buildings sector
across Europe with varying levels of requirement. Some are known to
be legally required but they can often be mandated at country,
region, city or local level. Building sustainability standards focus
primarily on materials and energy performance and where
biodiversity requirements exist they are often not mandated, carry
little weight and do not promote high levels of biodiversity. Where GI
is integrated into buildings it is often limited to green roofs, with little
focus on other elements of the building or surrounding area to
integrate GI. Building standards have an architectural focus with GI
almost as an afterthought. Developments that have taken place in
the context of green roofs may provide inspiration for broader
inclusion of GI in the building process.
Table 10: Examples of standards for the building sector with indication on whether green infrastructure (GI) is thoroughly included (green: GI well covered; orange: GI moderate to basically; red: GI hardly or not covered)
Type Standard Key aspects G I
Performance Building Research Establishment Environmental Assessment Methodology (BREEAM)94
BREEAM assessments use recognised measures of performance, which are set against established benchmarks, to evaluate a building’s specification, design, construction and use. The measures used represent a broad range of categories and criteria from energy to ecology. GI is covered under the section of ‘Land Use and Ecology’, which addresses value, protection, enhancement and management.
DGNB system95 The DGNB system is an integrated evaluation of economic and environmental aspects and user comfort. GI is covered under the sections of ‘Local Environmental Impact’ and ‘Biodiversity and Interaction’.
PassiveHaus96 Passivhaus is an energy performance standard focusing on thermal performance, airtightness and ventilation. It does not address wider sustainability issues such as biodiversity or GI.
HQE97 HQE is an environmental assessment methodology that pursues sustainable performance objectives while considering impacts on health, personal comfort and the indoor environment. Biodiversity is covered in the section Ecosystems and Biodiversity
ISO 21931 ISO 21931 is an international standard aimed at improving environmental performance. Environmental impacts are addressed at local, global and interregional level
Standard Assessment Procedure98
The Standard Assessment Procedure (SAP) is the UK Government’s recommended method system for measuring the energy rating of residential dwellings. It does not factor broader sustainability requirements such as biodiversity or GI.
Biotope Area Factor99
Biotope Area Factor (BAF) is a calculation undertaken by Berlin city to secure green qualities. BAF targets are applied to various developments and structures to safeguard and improve microclimate and atmospheric hygiene; safeguard and develop
94 http://www.breeam.org/ 95 http://www.dgnb.de/en/ 96 http://www.passivhaus-institut.de/ 97 http://assohqe.org/hqe/ 98 http://www.bre.co.uk/sap2012/page.jsp?id=2759 99 http://www.stadtentwicklung.berlin.de/umwelt/landschaftsplanung/bff/index_en.shtml
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soil function and water balance; create and enhance quality of plant and animal habitat; and improve the residential environment.
Procedure The Town and Country Planning Association (TCPA)100
The Essential Role of Green Infrastructure: Eco-towns Green Infrastructure Worksheet - The Worksheet is designed to provide clear guidance on how to design, incorporate and operate green infrastructure. It is intended to support the emergence of green infrastructure networks that, in terms of their quality, extent and capacity, deliver the widest range of environmental, social and economic benefits.
The London Plan Policy 5.10 Urban Greening – Requires development proposals to include green infrastructure. Elements can include tree planting, green roofs and walls, and soft landscaping. Policy 5.11 Green Roofs and Development Site Environs – Requires major developments to include roof, wall and site planting, especially green roofs and walls where feasible to deliver; adaptation to climate change, sustainable urban drainage, mitigation of climate change, enhancement of biodiversity, accessible roof space, improvements to appearance and resilience of the building, and growing food.
Methodology
International Green Roofs Policies101
Details of a number of green roof policies from around the world are detailed here, which include a number of German, US & Chinese cities; as well as Basel, London, Toronto, Singapore and Australia. These cities are actively promoting GI and it is included at the policy level.
European Federation of Green Roof Associations (EFB)102
The EFB brings European green roof associations together which promote and encourage the uptake of green roofs. The majority of green roof associations have standards based on the German FLL standard, which addresses waterproofing, soils, vegetation, treatment, installation, procedures and maintenance.
Designing for Biodiversity: A Technical Guide for New and Existing Buildings103
This book advises on how to incorporate provision for biodiversity within building developments. Focus is largely on building features, but also limited information is provided on how to increase biodiversity and include green infrastructure in the building surroundings.
Putting the Green in the grey104
UK guide on creating sustainable grey infrastructure by considering GI. A guide for developers, planners and project managers. It is intended to provide a framework that can be used to identify the additional environmental benefits that projects primarily focussed on delivering economic outputs can deliver at the same time.
Demystifying GI UK GBC105
This report consolidates existing information on Green Infrastructure (GI) for those working in the built environment, providing a simple, accessible guide. It helps to define the topic and its scope, and crucially attempts to highlight the business case for creating and maintaining GI – aimed primarily at the developer and client.
Interview highlights
The interviews - with Dusty Gedge, European Federation of Green Roof Associations
(EFB) and Maarten Dansen (Dutch Green Building Council) - revealed the following
interesting findings:
100 http://www.tcpa.org.uk/pages/green-infrastructure.html 101 http://livingroofsworld.com/page22.php 102 http://www.efb-greenroof.eu/ 103 http://products.ihs.com/cis/Doc.aspx?AuthCode=&DocNum=304592 104 http://www.greeninfrastructurenw.co.uk/resources/6b4_Guide.pdf 105 http://www.ukgbc.org/sites/default/files/Demystifying%20Green%20Infrastructure%20report%20FINAL.pdf
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Standards are important in the construction industry to ensure reliability and
consistency – however, they are often also used in a policy context. Performance
criteria and not construction criteria/techniques should dictate policy.
Policy change is required. Cities drive the market and they have the ability to
drive quality – codes and standards generally are the lowest common
denominator – good policy leads to good green roofs. Current codes and
standards are about how they are constructed – not what they deliver.
Dusty recommends the Commission works on policy guidelines that are separate
but refer to industry codes. They are two different beasts. Unfortunately a lot of
policies are written with too much reference to industry codes because of
architects. Policy codes should be written and considered by sustainability officers
and planning officers, not by suppliers and installers.
How GI is included in standards shows much heterogeneity: sometimes focus is
more on the process, the framework and the expertise of an ecologist, while in
other instances focus is on the species and the ticking of a checklist.
Project developers are positive on having green being considered early in the
process for two reasons. One is that by having an early analysis, risk is minimized
that species protected by law are only discovered at a later stage during the
building process and then cause the (temporary) halting of the project. The other
is that they also showcase with the green that is included in the projects they
conduct. In fact, enthusiasm is such that GI could be included even more
strongly.
A challenge is how to decide whether an ecologist is credible. Criteria now include
that either the person can be considered an ecologist due to education (e.g.
biology degree), profession (being an ecologist in a consultancy) or because of
active involvement in nature protection and being an active member of a nature
organization. It is another challenge to have ecologists that are sufficiently
familiar with building specifications and that can provide relevant input when at
the table with the building designer’s team.
Extent GI is integrated in standards and the potential
The level of GI integration in building standards is extremely varied. There can be
none at all, such as the Standard Assessment Process (SAP); some inclusion such as
the Building Research Establishment Environmental Assessment Methodology
(BREEAM) that addresses land use and ecology as part of the assessment; or
completely dedicated to GI, such as the European Federation of Green Roof
Associations that ensures a robust methodology in engineering green roofs and
maximizing biodiversity value.
Where the standards include elements of GI, the requirements are minimal, focusing
on the protection of features and simple enhancement. There is little requirement to
create GI of value and this is never mandatory.
Standards dedicated to GI, such as the FLL for green roofs, ensure that the GI created
has a high standard, creating value in both biodiversity and the wider sustainability
benefits such as reducing pollution, buffering storm water, increasing well-being and
productivity for employees, students, etc.
Way forward
The European Federation of Green Roof Associations (EFB) is an excellent
example of an association bringing together similarly minded organizations to
promote and encourage best practice. Members have recognized the German FLL
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as a leader in the field and have used it as foundation to create their own country
specific standards that suppliers can become registered to, helping spread use of
a common standard.
Harmonization of standards is seen as necessary but should be done so via
associations and common policy, rather than by legislation. Best practice should
be identified and shared amongst the Member States via associations and experts
in their field.
Discussing how to move forward should be led by leaders in their field in
collaboration with buildings experts to ensure integration and to maximize the
benefits of GI at both the building and larger development level.
Major findings on standards for performance elements
Building performance standards are generally voluntary but can be enforced
through local policy, planning or funding requirements. This is often seen as
bureaucratic box ticking with additional expense and no added value. Greatest
value is achieved where companies want to be leaders in sustainability and
recognize the true value of GI.
The standards have an architectural bias with little consideration for GI. For
example, BREEAM weighs Ecology at 10% but only mandates 1%.
Some methods are well established, such as BREEAM and LEED. These schemes
can be used on different types of buildings (new vs. existing; residential vs. non-
residential; etc.) and cover different stages (design, post construction, and
operation). The main target group of such a certification scheme are real estate
companies, investors or property owners. Their motivation is to have a label
demonstrating both the greenness of their buildings and to have a credible
assessment that their building has a low energy demand; as well as adding a
‘green’ premium to sale and rental prices.
The market for voluntary building certification schemes is young. However, it is
important to note that there are differences between European regions. The
western EU countries, many of which have their own national voluntary leading
schemes, e.g. BREEAM in the UK, DGNB in Germany or HQE in France, all report a
steady rise in certification. Furthermore, it appears that in Western Europe
certification of new buildings is considered more or less mandatory for certain
types of development. In contrast, other parts of Europe have only recently
started using the rating schemes.
Many of the building assessment schemes are very similar and can be applied to
any country across Europe creating confusion across the building sector.
Main drivers for using a green building rating schemes are the desire to improve
performance, marketing and competitive advantage. The only significant reason
to not use such rating system is the cost and length of time that it takes for
certification106.
Another German example, this time at the local scale, can be found in Berlin. The
city uses the concept of ‘biotope area factor’ (BAF). The BAF gives an indication of
the quantity of Green infrastructure available at a certain site. In Berlin the BAF is
established in landscape plans as an ordinance. This concept has created an
increase in green roofs, permeable surfaces and living walls in the city. These
106 http://www.worldgbc.org/files/8613/6295/6420/World_Green_Building_Trends_SmartMarket_Report_2013. pdf
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types of procedures, with high potential to be replicated, are very valuable in the
European context.
Major findings on standards for procedures
Embedding GI in regulations is incentivizing the GI market significantly. Since
1998, the German construction law with § 9 (1) no.25a (The German Federal
Building Code) provided a clear opportunity to set requirements for green roofs,
which are used widely in Germany.
Very specific types of procedures apply to taxation and subsidies. There are many
different ‘green taxes’ across Europe. One relevant example for GI is the taxation
of sealed surfaces and water run-off107. There is a taxation in place in Sweden,
France, England and Germany. In the Czech Republic there is a similar system for
industry only.
One third of German cities has a so-called ‘rainwater tax’ (Berlin, Stuttgart, etc.).
This tax is based on surface sealing. Taxpayers can receive a reduction if they
provide water retention and/or filtration. This system is in part responsible for the
amount of green roofs in the cities which has increased from 10 million m² in
1995 to 84 million in 1999.
In Stockholm (Sweden) the tax can be reduced by 50% if there is reduced or
attenuated run-off of rainwater to the urban drainage system. If the building is
autonomic and has no need for the public drainage system, one can receive a
100% reduction.
Many subsidies operate at the local scale, such as the green-roof subsidy in the
city of Ghent108, paying 31 euro/ m² per green roof.
Under UK legislation the Greater London Authority has set out an overall strategic
plan for London setting out an integrated economic, environmental and social
framework for the development of London over the next 20-25 years. It brings
together a number of areas including a range of environmental issues such as
climate change (adaptation and mitigation), air quality, noise and waste. It
recognizes the key benefits of Green Infrastructure (climate change adaptation &
mitigation, improving water quality, flood mitigation, sustainable urban drainage,
appreciation of landscapes and cultural heritage, enhancement of biodiversity),
thereby encouraging buildings to include green roofs & walls as well as the use of
soft landscaping.109 Approximately 47% of London is green and is continuing to be
‘greened’ by the addition of green roofs, walls and other green infrastructure.
Major findings on standards for methodology
Best practices and leaders in their field are recognized and their approach
adopted or used as a framework to develop local methodologies.
Excellent examples of this are the German FLL standard for Green Roofs which
has gone on to be adopted or influence the development of standards in the
Netherlands, Poland, Czech Republic, Hungary, Italy, UK, Sweden, Austria and
Switzerland.
107 http://livingroofsworld.com/page22.php; ARCADIS (2012), Comparison of cost price of water/ waste water/ rain water for users in different EU Member States (Flemish Environmental Agency); Science for environment policy (2012), Soil Sealing, in depth report, European commission 108 http://www.gent.be/eCache/THE/1/32/953.cmVjPTQzNzc0.html 109 http://www.london.gov.uk/priorities/planning/london-plan/further-alterations-to-the-london-plan
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This has also been greatly assisted by the support of the European Federation of
Green Roof Associations (EFB) and that of experts in their field to lobby and
encourage policy change at the city level.
Methodologies such as the FLL, covered by the EFB, and the TCAP worksheet are
holistic, thorough and are developed by collaborative efforts by leaders in their
field
The sheer volume and complexity of guidance that exists promoting GI can be
bewildering. This is often challenging for the non-specialists within the
construction industry, particularly clients and developers, to understand which
information and guidance they should be following.
Many of the methodologies and guides detail the benefits and risks of green
infrastructure and how they can be integrated into the design of buildings and the
surrounding infrastructure. For example, the ‘Demystifying GI UK GBC’ report
details how GI is not only green roof and walls, but also includes sustainable
drainage, city parks, reed beds, swales, urban wetland and urban woodland; and
how these can be used to assist planning applications, reduce installation costs,
flood attenuation, reduced management costs, community and employee
engagement, health & wellbeing, improved air quality, increased land & property
value and crime reduction to mention a few.
4.4.3 GI standards and the water sector
In the water sector, procedural standards for sustainable water
management in Europe are available through the Water Framework
Directive. In the private sector there is a growing awareness for
proactive investment in sustainable management of water in the
catchment where companies operate. Although GI is not always
explicitly mentioned, the application of GI fits well in the ecosystem
and catchment based approaches. As a way forward for the
implementation of GI it is important to incorporate both ‘green’,
‘grey’, and also hybrid solutions in the initial assessments of options
in such a way that actors can compare and make the best choice for
their situation. Currently, there are often already established criteria
to evaluate the performance of the more conventional grey options
but not so for GI or for comparing across grey and green options.
This forms a barrier for wider implementation of green options.
Table 11: Examples of standards for the water sector with indication on the extent to which GI (GI) is included (green: GI well covered; orange: GI moderate to basically; red: GI hardly or not covered)
Type Standard Key aspects G I
Performance The Alliance for water stewardship (AWS) has developed the International Water
This is a globally-consistent framework that outlines the expectations of responsible water stewardship. The standard is one of the first examples of a landscape-based approach to certification, focusing on the health of the entire watershed and balancing the needs of different water users and managers to ensure freshwater use that is socially and economically beneficial as well as environmentally sustainable. Although GI
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Stewardship Standard110
is not explicitly mentioned, it would fit well within the objectives of sustainable water stewardship.
European Water Stewardship Standard111
Growing awareness of water as a reputational risk to the private sector is spurring proactive investment by a number of companies. The European Water Stewardship Standard, a production site voluntary standard that encourages water users to engage with the wider challenges and opportunities of the catchment in which they operate, has been implemented at sites across the EU by large multinationals such as BASF and Coca-Cola. The Standard is independently verified and a performance-based certification scheme can be used in marketing and communication activities in the manner of the Forest Stewardship Council label.
Procedure Water Framework Directive112
The EU Water Framework Directive, adopted in October 2000, is an important piece of EU environmental legislation which aims at improving the water environment. This Directive establishes a framework for the protection of all waters including rivers, lakes, estuaries, coastal waters and groundwater, and their dependent wildlife/habitats under one piece of environmental legislation.
GI & Water Framework Directive in the Association of Greater Manchester 113
The Association of Greater Manchester Authorities (AGMA) supports the use of GI interventions as part of its wider strategy for sustainable growth. Recommendations where GI interventions could potentially be targeted, to address WFD and flood risk as a priority but also contribute to reducing other risk factors contributing to climate resilience.
WANI water and Nature initiative114
WANI, has worked over the past decade towards managing and protecting water reserves and heritage for the future benefit of all. Stretching across 5 continents in 12 river basins, WANI works with governments and local communities to use and manage water resources more sustainably. WANI aims to help reduce poverty and protect the environment by helping people to access and manage river flows. Although GI is not explicitly mentioned, GI fits well within the ecosystem based approach.
Method ology
European Natural Water Retention Measures Platform (NWRM)115
This platform contains rich information with regards to the design and implementation of measures, a wide catalogue of possible measures (ID cards) including financing and costs aspects and case studies. This information is available directly on the website and more extensively in the online guidance, ID catalogue and synthesis documents. The measure presented are all on GI in the context of water.
Water for business116
This online guide by the WBC-SD is specifically designed for businesses to help them manage water more sustainably by providing them with an overview of water tools and initiatives which they can use or engage with. Biodiversity is mentioned but detail is very limited. There is no mention of GI and how it may provide solutions.
GI guide for water management117
UNEP, UNEP-DHI Partnership, IUCN, WRI guidance on GI solutions, tools for quantification and valuation of benefits, barriers and the possible ways ahead.
110 http://www.allianceforwaterstewardship.org/ 111 http://www.ewp.eu/activities/ews/ 112 http://ec.europa.eu/environment/water/water-framework/info/intro_en.htm 113http://www.salford.gov.uk/corestrategy/iw/QA-QA10-Joint-Green-Infrastructure-Project-GI-and-the- Water-Framework-Directive.pdf 114 http:// www.waterandnature.org 115 http://www.nwrm.eu 116 http://www.wbcsd.org/waterforbusiness3.aspx 117 http://www.unepdhi.org/-/media/microsite_unepdhi/publications/documents/unep/web-unep-dhigroup- green-infrastructure-guide-en-20140814.pdf
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Interview highlights
The interview with Maija Bertule (program advisor at UNEP-DHI Partnership) revealed
the following interesting findings:
The application of GI in the water sector is still in the phase of building the
evidence base on the efficiency, costs and co-benefits over time. This knowledge
base is crucial in establishing any kind of standards.
It would be quite complicated to develop common standards for GI in the water
sector, as the green options are highly variable from small urban elements to
large watershed measures. There will always be site-specific elements that cannot
be accounted for in general guidance, such as interaction of the local climate and
geography with vegetation types, etc.
Nevertheless, common standards or guidance covering some of the key aspects of
GI, e.g. cost and benefit analysis and performance measurements (including
performance of delivery of co-benefits), could be useful. These could be in the
form of recommendations, as opposed to binding standards, as there is a lot of
variation in what can be acceptable and desired depending on the local
circumstances. Case study examples of best practices are also an effective way of
sharing experience and establishing ‘best practice’.
Extent GI is integrated in standards and the potential
Although the application of GI fits well in the ecosystem and catchment based
approaches, GI is not always explicitly mentioned in standards. A large potential for
the further uptake of GI lies in the private sector, where awareness is growing for
proactive investment in sustainable water management in the catchment in which
companies operate.
Way forward
A growing number of initiatives are linking GI investments to water management
needs through an integrated catchment management approach. A number of large EU
water utility companies have pioneered the approach of linking agri-environmental
schemes to water source protection measures.
Major findings on standards for performance elements
Several initiatives exist for performance standards, such as the Alliance for Water
Stewardship, that have developed the International Water Stewardship Standard.
Although GI is not explicitly mentioned, it would fit well within the objectives for
sustainable water stewardship.
Major findings on standards for procedures
In the water sector, procedural standards for sustainable water management are
available through the Water Framework Directive and the Floods Directive.
The implementation of GI would gain from a stronger focus on integrated spatial
planning, taking the wide range of ecosystem services related to water and flood
management into account.
A main condition for wider implementation and success of ecological practices is
the systematic integration of biodiversity in investment pathways supported by
policy and funding.
The more widespread use of a cost-benefit analysis that considers the valuation of
ecosystem services could serve as a lever to demonstrate that green, nature-
based solutions are in fact often more cost-effective than traditional
infrastructure. However, this may not be sufficient to include biodiversity concerns
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into water management, as the monetary values that relate to ecosystem services
are generally low, except in densely-populated urban areas.
Major findings on standards for methodology
Several methodology standards for GI in sustainable water management already
exist, such as the guidelines and methods of the European Natural Water
Retention Measures Platform (NWRM) or the GI guide for water management
developed by UNEP, UNEP-DHI Partnership, IUCN and WRI on GI solutions, tools
for quantification and valuation of benefits.
In the private sector there is still a need for awareness raising, for instance
among water and waste water treatment companies about GI-based alternatives
or hybrid solutions (combination of green and grey) to traditional grey
infrastructure investments. An increased use of NWRM would be advantageous in
this context.
It is important to find ways to incorporate ‘green’, ‘grey’ and ‘hybrid’ solutions in the initial assessments of the options in such a way that actors can compare and
make the best choice for their situation. At the moment, there are often already
established criteria to evaluate the performance of the more conventional grey
options but not for GI. This forms a barrier for the wider implementation of green
options.
4.4.4 GI standards and the transport sector
Transport infrastructure, in particular road and railway systems, form
widespread networks with varying density all over the EU. They have
tremendous impacts on biodiversity, both at a local and regional
scale. The most visible impacts are collisions with animals. Yet more
consequential are the indirect effects of transport infrastructure,
including habitat loss and reduced habitat quality (e.g. increased
noise levels), habitat fragmentation and barrier impacts. As these
impacts often occur simultaneously, the cumulative effects on wildlife
populations can be very significant. There is a significant quantity of
guidance and good practice on how to address fragmentation and
barrier effects by means of overpasses or fauna tunnels etc., which in
some cases are supported by GI measures. Also at a landscape level
GI offering improved habitat connectivity is often applied as part of
wildlife and landscape management, and increasingly incorporated
into regional spatial planning. However, guidance on how to reconcile
transport networks with ecological networks at a regional scale is
very scarce. The same goes for guidance on how to optimize the
ecosystem services provided by GI to mitigate impacts of transport
infrastructure on biodiversity.
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Table 12: Examples of standards for the transport sector with indication on whether GI (GI) is thoroughly included (green: GI well covered; orange: GI moderate to basically; red: GI hardly or not covered)
Type Standard Key aspects G I
Performance Civil Engineering Environmental Quality Assessment (CEEQUAL)118
CEEQUAL is an environmental assessment methodology for clients, designers and contractors to deliver improved project specification, design and construction of civil engineering projects. It is an integral part of UK construction industry contribution to support UK government strategy towards sustainable development. Section 6 of the method covers impacts on sites of high ecological value, protected species, surveys conservation & enhancement, habitat creation measures, monitoring and maintenance. Focus therefore is on impact mitigation, but not on making use of the multi- functionality of GI. CEEQUAL is a commercial tool requiring payment.
INVEST119 INVEST was developed by the Federal Highway Administration, United States. It is an assessment system that provide a list of sustainable factors best practices to be incorporated into transportation project and is designed to address sustainability throughout the project stages. The INVEST sustainability factors consist of noise quality, ecology and biodiversity, visual impact, waste management, energy and carbon emissions, erosion and sediment control, flora and fauna, health and safety, life cycle cost, cultural heritage, public access and intermodality of transport. Ecological connectivity (PD-09) is covered from a wildlife perspective, but not considering the ecosystem services GI may provide.
The European Investment Bank Statement on Environmental and Social principles and Standards120
The Statement outlines the standards the EIB is imposing on projects that it finances, and the responsibilities of the various parties. It provides a great sense of urgency about the problems of climate change and gives great recognition to the importance of biodiversity. However the emphasis is on conservation or restoration of biodiversity (according to the mitigation hierarchy), rather than promoting GI as an opportunity to enhance biodiversity and deliver ecosystem services. As the EIB is periodically reviewing this standard to align with new developments under the EU environmental policy and legislation, there might be a chance that future versions put more emphasis on GI.
Procedure Habitats Directive Highly relevant from a procedural point of view are the following articles:
Art 10: The Habitats Directive includes specific measures to maintain or restore the coherence of the Natura 2000 network. In particular, Article 3(3) of the Habitats Directive states that ‘where they consider it necessary, Member States shall endeavour to improve the ecological coherence of Natura 2000 by maintaining, and where appropriate developing, features of the landscape which are of major importance for wild fauna and flora, as referred to in Article 10.’ Article 10 states that ‘Member States shall endeavour, where they consider it necessary, in their land-use planning and development policies and, in particular, with a view to improving the ecological coherence of the Natura 2000 network, to encourage the management of features of the landscape which are of major importance for wild fauna and flora. Such features are those which, by virtue of their linear and continuous structure (such as rivers with their banks or the traditional systems for marking field
118 http://www.ceequal.com/ 119 https://www.sustainablehighways.org/ 120 http://www.eib.org/attachments/strategies/eib_statement_esps_en.pdf
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boundaries) or their function as stepping stones (such as ponds or small woods), are essential for the migration, dispersal and genetic exchange of wild species.’
The less known article 12.4: “Member States shall establish a system to monitor the incidental capture and killing of the animal species listed in Annex IV). (..) shall take further research or conservation measures as required to ensure that incidental capture and killing does not have a significant negative impact on the species concerned”. As a consequence transport infrastructure planning, design and maintenance should include appropriate measures to avoid or mitigate incidental killing of animals. Appropriate design of Green Infrastructure offers at least part of the solution. This should be reflected in the planning and permitting processes and conditions for new infrastructure (e.g. TEN-T project applications for funding must demonstrate that the project respects all EU legislation such as the Nature and Water directives and the impact assessment directives (SEA and EIA)), but in practice a lot more can be done.
SEA/EIA The process ensures a detailed assessment of adverse and beneficial environmental effects for a range of alternative solutions, either at the planning stage (SEA) or the project stage (EIA). While the focus is on the assessment of impacts, an important part of these assessments is dedicated to mitigation measures. Although this offers an excellent opportunity to promote GI, the multi-functionality of it or its societal benefits are often poorly described.
Multi-Annual Defragmentation Programme, the Netherlands121
In 2004, the Multi-Annual Defragmentation Programme was adopted with the aim to remove during the period 2015-2018 the most important barriers for the National Ecological Network formed by the country’s dense road and rail infrastructure as well as major waterways. Relevant defragmentation projects include wildlife passages and crossings, specifically looking at fauna tunnels, green bridges, fish ladders, oversized viaducts and wildlife-friendly verges and river banks. This initiative focuses on ecosystem resilience and improved functional habitat connectivity for targeted species. A guidance has been published (see below under ‘Methodology’).
Methodology Wildlife and Traffic: A European Handbook for Identifying Conflicts and Designing Solutions122
The COST action 341-project has elaborated a handbook (Wildlife and Traffic: A European Handbook for Identifying Conflicts and Designing Solutions, 2003) with detailed ecological solutions to minimise or mitigate wildlife and traffic conflicts, but not on the benefits that can be derived from making us of GI. In annex 5 of the handbook an overview is given of handbooks and guidelines per country.
SAFEROAD – ‘Safe Roads for Wildlife and People’ (CEDR Transnational Road Research Program 2014‐2016)123
This ongoing project aims to publish a guidance by end of 2016, i.e. the ‘European WILDLIFE Road Maintenance Guidelines’. Preliminary findings are the fact that currently Road Maintenance Guidelines (RMG) in most EU countries include only short information about wildlife topics (in sections about fencing, road wildlife awareness signs, road verge management, bridges, drainage, and – exceptionally - wildlife passages). The aim is to bring evidence‐based knowledge from road and wildlife experts together to identify new strategies, practices and technologies to reduce conflicts and costs. As the focus is road safety and biodiversity conservation, GI and its full range of societal benefits will be covered only to a minor extent.
121 http://www.mjpo.nl/ 122 http://www.iene.info/wp-content/uploads/COST341_Handbook.pdf 123 http://www.saferoad-cedr.org/en/saferoad.htm
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Leidraad Natuurtechniek – Ecologisch wegbermbeheer (2011, Flemish Ministry)124
This guidance provides recommendations on how to enhance biodiversity values of road verges and waterway verges. The concept of GI is not explicitly mentioned, neither the multi- functional role of these verges in terms of ecosystem services. However, LNE has prepared two follow-up studies on valuation of ecosystem services provided by road and waterway verges (prepared by Arcadis).125
Leidraad Faunavoorziening en bij infrastructuur (2013, Multi- Annual Defragmentation Programme, The Netherlands)126
This guidance provides recommendations on how to enhance biodiversity values of road, railway and waterway verges. The concept of GI is not explicitly mentioned, neither the multifunctional role of these verges in terms of ecosystem services.
Vilda djur och infrastruktur – en handbok för åtgärder (2005, Swedish Road Administration)127
This guidance provides recommendations on how to enhance biodiversity values of road verges. The concept of GI is not explicitly mentioned, neither the multi-functional role of these verges in terms of ecosystem services.
Restoring ecological networks across transport corridors in Bulgaria128
The main objective of this project (2006-2007) was to develop a long-term programme for defragmentation measures at transport corridors in Bulgaria in order to restore ecological networks and preserve biodiversity. It is not covered what the multi-functional benefits can be from an ecosystem services and GI perspective.
The ecology of transportation: managing mobility for the environment129
This volume brings together international experts from a variety of disciplines to review the ecological effects and their causes in terms of road, rail, ship and aircraft transport. Focus ranges from identification of threats and amelioration of damaging effects through to future design of transport systems to minimize environmental degradation. As with many of the other examples in Table 5-7 coverage is limited to evaluating impact and considering mitigation, however, not taking opportunity to also highlight the potential of including and making use of GI and the ecosystem services it provides.
Green Stormwater Infrastructure Strategies for Airports130
This recent work (2015) presents a synthesis of information that can be valuable in assisting airport decision-makers and professionals responsible for managing the stormwater programs and for the planning and project development of conventional grey infrastructure and new green infrastructure related to stormwater management. Airports urgently need resilient and affordable solutions to address stormwater quantity and quality issues and to promote the triple bottom line of sustainability. Recent years have seen increasing use of green stormwater infrastructure (GSI) strategies at airports. GSI solutions (e.g., bioretention systems, rain gardens, vegetated filter strips, permeable asphalt or concrete pavement, drainage wells, and amended topsoil) are designed to supplement or replace conventional grey infrastructure (e.g., impermeable pavements and curbs, inlets and pipes) that inhibit water filtration or infiltration and related natural treatment and flow attenuation processes. This work aims to
124 http://www.lne.be/themas/milieu-en-infrastructuur/Leidraad%20natuurtechniek%20- %20ecologisch%20bermbeheer.pdf 125 http://www.lne.be/themas/beleid/milieueconomie/kosten-batenanalyses/literatuur-over-mkba 126 http://www.mjpo.nl/nieuws-publicaties/publicaties/leidraad/ 127 http://www.lansstyrelsen.se/stockholm/SiteCollectionDocuments/Sv/miljo-och-klimat/tillstandet-i- miljon/Sjoar-och-vattendrag/Vilda-djur-och-infrastruktur.pdf 128 http://www.ecnc.org/uploads/2012/10/final-report-restoring-ecological-networks-across-transport- corridors-in-bulgaria.pdf 129 http://www.springer.com/us/book/9781402045035 130 Shi, X., Beutel, M., Long, T., Hellenthal, A., and Bristoll-Groll, C. (2015) Green Stormwater Infrastructure Strategies for Airports: Challenges and Opportunities. Environmental Sustainability in Transportation Infrastructure: pp. 1-13. doi: 10.1061/9780784479285.001
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provide a brief overview of the GSI strategies for airports, followed by a discussion of challenges and opportunities in balancing airport priorities in environmental, economic, and social values and operational constraints. The airport challenges in implementing GSI strategies mainly include those related to wildlife attraction, climate change, anti- icing/de-icing compounds, and land use limitations. A research project on this issue is underway in the United States.131
Interview highlights
The interview took place with Carme Rosell. Apart from being an expert associate of
Minuartia (a consultancy in Catalonia) and University of Barcelona, she is a Board
Member of Infra Eco Network Europe (IENE)132. IENE is a network of experts working
with various aspects of transportation, infrastructure and ecology. The network was
initiated in 1996 to provide an independent, international and interdisciplinary arena
for the exchange and development of expert knowledge with the aim to promote a
safe and ecologically sustainable pan-European transport infrastructure. IENE arranges
international conferences, workshops and symposia, initiates collaboration projects
and helps answering questions that require a joint international expertise. Main focus
is on defragmentation solutions and solutions to avoid or reduce animal collisions. She
is involved in the SAFEROAD project (see Table 5-7).
The interview revealed the following interesting findings:
In the transport sector there is a lot of guidance and standards for building and
maintenance, but GI is poorly covered. Topics related to GI are mainly focusing
on defragmentation measures (e.g. design and maintenance of wildlife passages),
and on this issue several EU countries have developed their own guidance. Other
GI related topics are road and waterway verges, drainage systems, water
retention ponds, resting areas, and green areas in airports. Sometimes this
guidance is very fragmented in different types of standards.
If GI is covered it is related to new developments (construction). GI in relation to
maintenance is hardly covered, which is a pity since the extensive network of old
infrastructure (railways, roads) offers a lot of opportunities in the field of
maintenance. The Saferoad project (see Table 5-7) aims to cover this gap.
Most countries have drawn up handbooks on wildlife issues (with some
information about maintenance). However the information is often not included in
general ‘Road Maintenance Guidelines’ (RMG), or in contracts to road
maintenance companies or PPP agreements. Experience shows that if it is not in
the contract, it is not applied. The DBFM (Design, Build, Finance, Maintain) type of
contracts for building and maintenance of roads offers opportunities as conditions
can be imposed to consortia on improving ecological connectivity and on
deploying GI.
Key elements of a good standard for green infrastructure are the following:
o The standard should be produced in cooperation between transport
experts and ecologists, and preferably with experts from different
countries;
o Standards need to be evidence based (monitoring), e.g. on the use of
fauna passages;
o Standards should build on best practices and be promoted (raising
awareness);
131 http://apps.trb.org/cmsfeed/TRBNetProjectDisplay.asp?ProjectID=3835 132 http://www.iene.info/
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o Standards need to adapt to country specificities (different climate,
different animals, …); be careful with general requirements;
o Standards should not only focus on ecological benefits, but also on
economic and social factors; this fits very well with the GI philosophy,
e.g. airports preventing bird strikes by means of habitat management
measures which attract less birds but might be very suitable for other
biodiversity, e.g. insects; this reduces costs for preventing bird strikes.
o Many standards are only available in the country language. Good
standards should include at least a summary in English or French.
An interesting observation is that the wording of ‘green infrastructure’ might be
confusing to civil engineers and non-ecologists in general. Even biologists within
building and construction companies are often not aware. They often confuse its
use with ‘sustainability’ e.g. reducing waste, emissions, etc. (like ‘green policy’).
Therefore the first task is to explain the concept (e.g. by means of material
provided by the EC). The concept of ‘natural infrastructure’ is sometimes better
understood.
Extent GI is integrated in standards and the potential
There are many standards on transport infrastructure construction and maintenance,
but until now GI is poorly covered. Main links are guidelines and prescriptions on
defragmentation measures and anti-collision measures for wildlife, as well as
guidelines on how to enhance biodiversity values of road and waterway verges.
However, transport infrastructure offers enormous opportunities for deploying GI and
its associated range of societal benefits. As nowadays the planning and permitting of
new transport infrastructure roads often faces societal resistance, a smart combination
of grey and green infrastructure (integrated solutions) accompanied with clear
communication of the societal benefits of GI might increase societal acceptance
(license to operate) and overcome resistance. Key elements of these integrated
solutions should include the creation of large GI areas (over-compensation of
biodiversity loss due to construction works is recommended) designed according to the
expectations of different stakeholder groups, and safeguarding the ecological
connectivity of the wider landscape. With regard to existing transport infrastructure an
opportunity is to create GI in order to mitigate negative health impacts created by
transport infrastructure (noise reduction, regulation of air pollution, aesthetics).
Translating these opportunities into standards which have an obligatory character
would be a major step ahead, both for biodiversity and for human health.
Way forward
As described above there is a tremendous opportunity for deploying GI both in the
field of new transport infrastructure developments as well as in the field of existing
transport infrastructure. Regional and local spatial planning processes as well as
dedicated standards on how to link GI to transport infrastructure in order to maximize
biodiversity and societal benefits are key instruments to make this happen.
Major findings on standards for performance elements
Only a few performance standards in relation to GI and transport infrastructure
have been identified, and even in these cases the full concept of GI is not taken
into account. The only link is the mitigation and compensation of biodiversity
impacts, but the multi-functionality of GI, i.e. its full range of societal benefits
next to biodiversity benefits, is hardly covered.
Transportation sustainability is largely being measured by transportation system
effectiveness and efficiency as well as the environmental and climate impacts of
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the system133. Opportunities for including GI are often overlooked and as a
consequence the biodiversity and societal benefits of it (ecosystem services) do
not show up in most sustainability performance measurement systems for
transport infrastructure.
Sustainability performance across the life cycle of construction projects is a crucial
aspect in achieving the goal of sustainable development.
Based on methodologies for the transport sector, the basic philosophy is that
prevention is better than cure in avoiding the negative effects of habitat
fragmentation. Where avoidance is impossible/impractical, mitigation measures
should be designed as an integral part of the scheme. Where mitigation is
insufficient or significant residual impacts remain, compensating measures should
be considered as a last resort. In most large scale transport infrastructure
projects compensatory measures are required. This provides opportunities for
creating GI.
Major findings on standards for procedures
Specific transport infrastructure sector related procedural standards, i.e.
standards on how to include GI in planning and permitting processes for new
transport infrastructure, are poorly available. There is however plenty of generic
spatial planning guidance which increasingly takes into account the concept of
ecosystem services and as such includes links to GI.
SEA provides a perfect instrument to cover GI when comparing alternative
routings or locations for new transport infrastructure, while EIA serves as an
excellent tool to fine-tune the most suitable options at a more detailed level.
However, the concept of GI in SEA and EIA is mostly limited to its biodiversity and
landscape functions, while the full potential of its wide range of positive societal
benefits (ecosystem services) is often only covered to a minor extent. As a
consequence, the opportunities provided by GI e.g. in terms of human health
benefits, are not fully exploited. Initiatives promoting the uptake of the ecosystem
services concept in environmental impact assessment, including the development
of guidance on this issue, would be very beneficial to enhance the uptake of GI in
plans and projects at local or regional level.
A challenge is to reconcile transport infrastructure policies with national or
regional policies on ecological connectivity. The Pan-European Biological and
Landscape Diversity Strategy (PEBLDS) promotes the concept of ‘ecological
networks’ (i.e. connections between habitats via ecological corridors). This has
been specifically identified as an effective strategy for addressing habitat
fragmentation as it promotes the integration of biodiversity conservation into land
use planning procedures. Consideration of these ‘ecological networks’ in the
planning of roads, railways and waterways may help to avoid critical bottlenecks
in habitat connectivity and identify where mitigation measures are required. The
Dutch Multi-Annual Defragmentation Programme is an excellent example, as it
guarantees that within each spatial planning process for new transport
infrastructure ecological connectivity is safeguarded.
Transport infrastructure related procedural standards for including GI in the
maintenance or upgrading of existing transport infrastructure is generally lacking,
apart from the fact that in many countries it is recommended to use existing
methodological guidance in preparatory studies (e.g. EIA) related to a new
development (e.g. building of a fauna overpass on an existing road). We are not
133 http://center.sustainability.duke.edu/sites/default/files/documents/transportation_indicators.pdf
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aware of any legal obligation, embedded in national or regional legislation, to use
existing GI standards. Art 10 and art. 12.4 of the Habitats Directive however
require that appropriate measures are taken.
Major findings on standards for methodology
Many standards are available on defragmentation measures and measures to
avoid animal collisions, i.e. with an exclusive focus on biodiversity conservation
and road safety. Quite some standards are also available on how to improve
biodiversity values of road and waterway verges, water retention basins, etc.
Methodological standards on how to enhance societal benefits with GI associated
to transport infrastructure are far less available. Developing methodological
guidance on how to include GI as a mitigating or compensation measure to
reduce or offset the adverse environmental impacts of transport infrastructure
and to turn them into societal benefits would be very beneficial.
GI can also be applied to reduce costs, or as a climate change adaptation
measure. An example is the article on Green Stormwater Infrastructure Strategies
for Airports, which provides an excellent overview of the benefits of nature-based
solutions compared to traditional grey infrastructure.
An issue that deserves particular attention in these methodological standards is
governance e.g. how to involve stakeholders, how to organize the financing and
maintenance, how to ensure the long-term effectiveness of wildlife corridors (see
Figure 10 below). Very often methodological standards are limited to technical
aspects.
Figure 10: Example of sustainable GI solution in the field of transport infrastructure
[Source: adapted from Schulz et al134]
134 Björn Schulz1, H. Reck2, M. Böttcher3. How to reconnect biodiversity across motorways? Practical experiences of establishing ecological hinterland connections of fauna passages in a highly fragmented
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4.4.5 GI standards and the public health sector
In the public health sector there are many standards, guidelines and
protocols outside the scope of the GI/health domain. Examples are
safety standards (toxic species, allergenic species, risks of falling
branches, pesticide use etc.). Accessibility standards that recommend
the availability of GI for citizens are an exception. However, there is
a growing body of literature linking GI to human health and
wellbeing, but the underlying mechanisms are poorly understood and
the knowledge tends to remain in the green sector, not penetrating
the health sector. Exceptions are some SME’s and bottom-up local
initiatives bridging the gap between the green sector and the health
sector. The health sector demonstrates large potential for GI
standards, but before standardization can take place, the evidence
base must grow stronger, and results must be dissipated within the
health sector rather than only in the green sector.
Table 13: Examples of standards for the public health sector with indication on whether GI (GI) is thoroughly included (green: GI well covered; orange: GI moderate to basically; red: GI hardly or not covered)
Type Standard Key aspects G I
Performance The Natural England Accessible Natural Greenspace Standards (ANGSt) 135
ANGSt recommends that everyone, wherever they live, should have accessible natural greenspace:
of at least 2 hectares in size, no more than 300 metres (5 minutes walk) from home;
at least one accessible 20 hectare site within two kilometre of home;
one accessible 100 hectare site within five kilometres of home; and
one accessible 500 hectare site within ten kilometres of home; plus
a minimum of one hectare of statutory Local Nature Reserves per thousand population.
Accessibility guidelines in Germany 136
Berlin aims at providing at least 6 m² urban green per person while Leipzig aims at 10 m² per capita. Berlin’s Department of Urban Development and the Environment recommends that every resident should have access to urban green of minimum 0.5 ha within a 500 m distance from home.
WHO green space standard137
The WHO is cited to have proposed a standard of 300m maximum distance to green space for every citizen, and or that every city should have a minimum of 9 m2 of green space per person. An optimal amount would sit between 10 and 15 m2 per person.
northern German landscape 1 Schleswig‐Holstein State Foundation for Nature Conservation, 2 University of
Kiel, 3 Federal Agency for Nature Conservation. 135http://webarchive.nationalarchives.gov.uk/20140605090108/http:/www.naturalengland.org.uk/regions/e ast_of_england/ourwork/gi/accessiblenaturalgreenspacestandardangst.aspx 136 GREENSURGE project: compiled in (http://greensurge.eu/working- packages/wp3/files/MS24_update_13022015.pdf) 137 http://www.euro.who.int/en/health-topics/environment-and-health/Housing-and- health/publications/2010/urban-planning,-environment-and-health-from-evidence-to-policy-action
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Accessibility guideline in the Netherlands138
75m2 per household within 500m is used as a guideline.
UK National Playing Fields Association’s six acre standard, now the Fields In Trust (FIT)’s recommendations on Planning and Design for Outdoor Sport and Play 139
The six acre standard suggests that for each 1000 residents there should be 2.4 hectares (6 acres) as follows: 1.6 hectares (4 acres) for outdoor sport and recreation space (including parks); 0.8 hectares (2 acres) for children's play, with about 0.25 ha of this equipped playgrounds. The new FIT publication continues to uphold the original recommendation that 6 acres of recreational space is required for every 1000 people and also provides a detailed framework relating to quantity, quality and accessibility of outdoor facilities for sport and play and the importance of local assessments and standards.
Procedure Managing Risk in Play Provision: Implementation guide140
The Play Safety Forum has produced Managing Risk in Play Provision to help strike a balance between the risks and the benefits of offering children challenging play opportunities.
Methodology HEAT141 Developed by WHO (World Health Organisation) to estimate the economic savings resulting from reductions in mortality as a consequence of regular cycling and/or walking. It enables users to estimate the value of new infrastructure to health policies or programmes.
Interview highlights
Patrick ten Brink, Head of the Green Economy Programme of the Institute for
European Environmental Policy (IEEP) and project leader of the Health and Social
Benefits of Nature and Biodiversity Protection project for DG Environment came
up with the “teaspoon of dirt a day” notion for healthy immune system
development in kids. Evidence is gathering that a certain amount of dirt is
good142. Nature play is a great way to get an ample amount of dirt and germs and
stimulate the immune system. Recently, enhanced immune functioning emerged
as one promising candidate for a central pathway between nature and human
health (Kuo 2015143.)
Jasperina Venema, green entrepreneur and advisor specialized in urban green and
health came up with the disease-resilient landscapes concept: GI can prevent the
spread of infectious disease between farms and from farm animals to humans, or
from wild animals to farm animals. Of course every disease is unique (One health,
FAO144). No standards or guidelines exist yet.
Sjerp de Vries, Alterra scientist and green health expert is worried about the
standard recently proposed by the WHO of 1 ha green space within 300 m from
home. The possible impact of this: large apartment blocks around one ha of green
space. If one of the purposes is to allow people to experience peace and quiet to
reduce their stress levels and improve their mood, it would be better to introduce
an area per 1000 inhabitants instead of only an absolute area and distance
measure.
138 http://www.compendiumvoordeleefomgeving.nl/indicatoren/nl0299-Beschikbaarheid-van-groen-in-de- stad.html?i=13-46 139 http://www.fieldsintrust.org/Product_Detail.aspx?productid=dc291578-50c5-49c5-b0d7-3c376db6b801 140 http://www.playengland.org.uk/resources/managing-risk-in-play-provision-implementation-guide.aspx 141 http://www.heatwalkingcycling.org/ 142 Callahan, G. N. (2003). Eating dirt. Emerging infectious diseases, 9(8), 1016-1021. 143 Kuo, M. (2015). How might contact with nature promote human health? Promising mechanisms and a possible central pathway. Frontiers in psychology, 6. 144 http://www.fao.org/ag/againfo/home/en/news_archive/2010_one-health.html
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Extent GI is integrated in standards and the potential
GI is still hardly integrated in the public health sector, with the exception of standards
for the accessibility of GI for citizens. There is a large potential for GI standards for
the health sector, but before standardization can take place, the evidence base has to
grow stronger, and the results must be dissipated within the health sector rather than
only in the green sector.
Way forward
A gap exists between the green sector and the health sector; the health sector by
large ignores GI. Many initiatives are bottom-up initiatives of patients, caretakers, and
freelancers or small SME’s rooted mostly in the green domain rather than the medical
domain. There is a growing evidence base on the health benefits of GI, but the causal
relationships and effect size remain largely unknown. It is important to first
demonstrate and quantify causal relations between health and GI.
Major findings on standards for performance elements
Performance standards for GI in the health sector so far focus on standards for the
accessibility of GI for citizens in urban areas.
Major findings on standards for procedures
Safety regulations for natural playgrounds are an issue. The safety
standards/safety requirements for play equipment are too strict for outdoor
playing and in conflict with children’s right to play (http://www.righttoplay.com).
A careful risk inventory/risk assessment can be used instead.
Since the health sector is largely unaware of the health benefits of GI, no
standardized procedures exist yet.
There are some guidelines for procedures regarding the construction and use of
e.g. community gardens, gardens surrounding hospitals or other care facilities
(“healing gardens”, therapeutic gardens) or care farms, but these are only shared
locally or in national platforms, there are no widely accepted or commonly used
guidelines.
Major findings on standards for methodology
In the health sector, there are certain standards for research design, such as the randomized control trial (RCT145), the “gold” standard for intervention studies, and
other standards, checklists and guidelines on how to do sound scientific research.
These also apply to GI impact assessments.
Guidance on how to include GI in urban planning do not go beyond accessibility
guidelines on area of green space per 1000 inhabitants (or per household) within
a certain diameter. A national guideline has only been adopted in the UK; in other
countries general recommendations are more common.
No standards on how to include GI in design of care facilities exist (care gardens,
therapeutic gardens or care farm). What happens in practice are mainly bottom-
up initiatives not based on any guidelines or standards.
145 http://www.consort-statement.org/ http://www.fao.org/ag/againfo/home/en/news_archive/2010_one- health.html
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4.4.6 GI standards and the industry sector
The industry sector is very familiar with sustainability standards.
Although biodiversity, as part of sustainability, has been a rather
neglected issue for a long time, the recent increase in specific
biodiversity guidance for industry shows a growing interest in the
field of ‘business and biodiversity’. However, when focussing on the
topic of GI within this growing amount of biodiversity standards, it is
clear that there is room for improvement. Particular issues which
deserve more attention are costs and benefits of GI in an industrial
context, as well as guidance on how to implement GI.
Table 14: Examples of standards for the industry sector with indication on the extent to which GI (GI) is included (green: GI well covered; orange: GI moderate to basically; red: GI hardly or not covered)
Type Standard Key aspects G I
Performance Global Reporting Initiative G4146
GRI is an international independent organization that helps businesses, governments and other organizations understand and communicate the impact of business on critical sustainability issues. Biodiversity is specifically covered under the environmental dimensions (see G4-EN11 to G4-EN15), but also has links with for example water (G4-EN9, G4-EN26). However, most biodiversity indicators describe impacts on biodiversity while only one (G4 – EN13 ‘Habitats protected or restored’) links to active GI implementation, which is very limited.
BBOP Standard on Biodiversity Offsets147
The Standard enables project developers to manage biodiversity related risks by providing an auditable approach to no net loss, as well as enabling auditors and assessors to determine whether an offset has been designed and subsequently implemented in accordance with the BBOP Principles.
Procedure Natural Capital Protocol (NCP)148
Currently, companies that measure and value their impacts and dependencies on natural capital do so in a myriad of different ways. This prevents comparability, consistency and mainstream adoption of these approaches. The overall vision of the NCP is to transform the way business operates through understanding and incorporating their impacts and dependencies on natural capital. Biodiversity as part of natural capital is included in this guidance. The NCP is under preparation.
EIA and AA149 For many industrial activities, as part of the permitting process, an EIA is carried out (and in case Natura 2000 protected habitats and species might be affected, an AA is required). While the focus is on the assessment of biodiversity impacts, an important part of these assessments is dedicated to mitigation measures. However, although this offers an excellent opportunity to promote GI, the multi-functionality of it or its societal benefits are often poorly described.
Environmental Management System -
Many companies operate environmental management systems, often certified to ISO 14001 or EMAS. However, biodiversity issues are frequently neglected or even omitted,
146 https://www.globalreporting.org/ 147 http://bbop.forest-trends.org/pages/guidelines 148 http://www.naturalcapitalcoalition.org/natural-capital-protocol.html 149 AA: Appropriate Assessment according to Habitats Directive Art 6(3) and 6(4)
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European Biodiversity Standard (EBS)150
despite their importance. The EBS provides a process to use in companies, to measure, improve and demonstrate publicly their ecological performance. EBS is a commercial tool requiring payment.
Environmental Management System - Biodiversity Benchmark (BB)151
BB is a standard for assessing and certifying an organisation’s system for achieving continual biodiversity protection and enhancement on its landholdings and their implementation. BB can complement existing environmental management systems such as ISO14001 and EMAS by integrating biodiversity into the systems of an organisation. Alternatively it can operate as a stand-alone system. Using the BB requires payment.
Methodology Cross-sector guide for implementing the Mitigation Hierarchy (CSBI)152
Provides practical guidance, innovative approaches and examples to support operationalizing the mitigation hierarchy effectively. As such it contains guidance on restoration and offsetting measures, and it offers insight into comparing costs and savings.
WBCSD Business Guide to Natural Infrastructure
The WBCSD is preparing a business guide on natural infrastructure (= GI). This guide will include the business case, case studies, fact sheets on existing tools, decision tree and check list. GI is thereby seen as a cost-effective investment opportunity and solution to benefit from a range of ecosystem services for issues material to companies.
WBCSD Eco4BiZ153
Eco4Biz “Ecosystem services and biodiversity tools to support business decision-making" is a structured overview of existing tools and approaches. Tools are identified as primarily focusing on either ecosystem services or biodiversity. The aim is to help companies make better-informed decisions about which tool they could apply when assessing and managing their ecosystem impacts and dependencies, in order to ultimately lower risk. However it provides only limited information on the business case of GI and how to implement it.
Specific GI guidance documents within individual companies
A limited number of businesses (often multinational companies in amongst others the Oil and Gas sector and the Mining sector) have developed their own internal guidance on when and how to implement GI.
Interview highlights
The interview (Violaine Berger, WBCSD) revealed the following interesting findings:
There is a need for raising awareness in the business sector, in particular on the
business case for GI (costs and benefits). Businesses still only look for grey
infrastructure solutions e.g. for waste water treatment and flood protection, while
nature-based solutions such as engineered wetlands and natural or semi-natural
flood protection might be cheaper and might create additional societal benefits.
There is a general lack of suitable guidance for the industry sector on how to
identify suitable GI solutions and how to implement them.
Checklist - type standards (performance) often do not deliver added value, as
they do not provide any information on the benefits of GI.
There is a need to develop the ‘proof of evidence’ by means of demonstration
projects.
150 http://www.europeanbiodiversitystandard.eu/node/4 151 http://www.wildlifetrusts.org/biodiversitybenchmark 152 http://www.csbi.org.uk/tools-and-guidance/mitigation-hierarchy/ 153 www.wbcsd.org/eco4biz2013.aspx
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Extent GI is integrated in standards and the potential
At this moment the industry is increasingly focusing on biodiversity, as it is more and
more acknowledged as a material sustainability issue. As a result there is a rapid
growth in the number of industry standards related to biodiversity. The majority of
these standards, however, deal with methods to identify and assess business impacts
and dependencies on biodiversity, and contains only limited information on methods to
implement mitigation measures. It is clear that creation of GI is an excellent way to
mitigate or to compensate biodiversity impacts. Specific guidance on the mitigation
hierarchy and the concept of No Net Loss (and Net Positive Impact) is provided by the
BBOP and the CSBI (see Table 14). There are very few standards with a clear focus on
GI. Specific guidance is currently being developed by the WBCSD (see Table 14).
There is a huge potential for GI uptake in existing business related biodiversity
standards by including information on how to identify GI solutions, on the business
case for GI and on how to implement GI.
Way forward
In 2013, experts from The Dow Chemical Company, Shell, Swiss Re, and Unilever,
working with The Nature Conservancy and a resiliency expert, evaluated a number of
business case studies, and developed a white paper with recommendations. The
paper154 illustrates the growing awareness and knowledge among the industry sector
on the benefits and potential of GI. The paper provides a number of critical success
factors for implementation of GI solutions, for example:
Employ a more comprehensive economic and environmental footprint analysis to
more accurately compare green versus grey infrastructure;
Engage with the engineering community (utilities/process technology/waste
stream management, etc.) to build organizational capacity and expertise in green
or hybrid infrastructure engineering. Develop learning modules that focus on the
identification of GI opportunities and on the evaluation of typical failure modes of
GI solutions in order to develop internal skill sets;
Establish an external network from academia, R&D institutes and contractors to
facilitate knowledge sharing and skill transfer activities;
Engage with the project community early on in the project development process
to ensure GI solutions are being considered as part of the early field planning
process.
As mentioned in Table 14, the business community is developing specific GI guidance
(WBCSD), which will be promoted amongst all industrial sectors. The fact that this
guidance covers issues such as a decision tree guiding companies throughout the
decision process on GI, a set of case studies which will be regularly updated on a
dedicated webpage, and demonstrating the business case for GI is very promising.
Major findings on standards for performance elements
Current GI performance standards mainly focus on biodiversity offsets and how to
measure No Net Loss. This, however, is only part of the GI business applications.
A performance standard related to the multi-functionality of GI, i.e. including
societal benefits, seems to be missing. Societal benefits could be measured and
valued by means of ecosystem services indicators, but again, these are lacking in
the investigated GI performance standards.
GRI indicators tend to focus mainly on biodiversity impacts, while efforts to
enhance biodiversity e.g. by implementing GI, are only to a limited extent
reflected by GRI indicators.
154 http://www.nature.org/about-us/the-case-for-green-infrastructure.pdf
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Major findings on standards for procedures
Substantial progress could be achieved by putting specific emphasis on GI in EIA
for industry projects and in environmental management systems such as ISO
14001. At this moment some commercial certification systems are established
(see Table 14). Environmental Impact Assessment is typically associated with the
exploration and feasibility stages of project developments, whereas Environmental
Management Systems are more closely associated with operations.
The Natural Capital Protocol is expected to boost standardization of measuring
and valuing approaches of business natural capital impacts and dependencies, as
it provides a framework for a uniform way of natural capital measurement and
valuation based on key principles and a step-by-step approach. It will also provide
ways to deal with biodiversity and will refer to GI as part of the solutions.
Major findings on standards for methodology
Innovative industries integrate nature into their thinking and understand its value
and potential services. This can lead to higher resilience for these companies,
more effective risk management, better relationships with customers and
suppliers and strengthening their image and reputation.
Industry needs to have access to specialist guidance, professional advice and
toolkits on GI and in particular concrete technical solutions for GI, and their
financial costs and benefits. The most appropriate guidance is company specific,
and some companies are developing their own GI guidance material, based on
combined in-house engineering and ecological expertise. The WBCSD business
guide on GI – under development – is also expected to be very concrete. It will
include a decision-tree supporting companies to identify and to decide on the use
of GI and the most suitable type of GI for their specific business applications. It
will contain case studies representing a range of sectors and both aquatic and
terrestrial GI solutions.
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4.4.7 GI standards and climate adaptation
Many examples of tools, guidelines and best practices already exist
on how to apply GI, or nature-based solutions, in the context of
climate change adaptation. Performance standards, which are
common practice in for instance the building world, are not a useful
way forward in the climate adaptation sector. The reason for this is
that the local situation is always too specific. The multi-functionality
of GI is a benefit but it makes planning and implementation of GI
very complex. Integrating a GI framework into Environmental Impact
Assessments might be a way forward, as this would guarantee that
the potential of GI in landscape planning is considered.
Table 15: Examples of standards for the public health sector with indication on whether GI (GI) is thoroughly included (green: GI well covered; orange: GI moderate to basically; red: GI hardly or not covered)
Type Standard Key aspects G I
Performance Climate, Community and Biodiversity Standards (CCB Standards)155
The CCB Standards identify land management projects that deliver net positive benefits for climate change mitigation, for local communities and for biodiversity. The CCB Standards have a two-step process: (1) Validation demonstrates good project design to generate significant climate, community and biodiversity benefits. Successful CCB validation can help build support for the project among stakeholders and investors. (2) Verification is a rigorous independent endorsement of the quality of project implementation and the delivery of multiple benefits. Successful CCB Verification enables the addition of a ‘CCB label‘.
Climate Bond Standard Community and Biodiversity Standards (CCB Standards)156
The Climate Bonds Standard issues certificates which are a screening tool for investors and governments which allows them to easily prioritize climate and green bonds. Recently a new Climate Bond Standard was developed for Agriculture, Forestry and Other Land Uses. Appropriate and responsible investments in these sectors can help developed and emerging economies transition to more sustainable growth pathways, especially where these investments help to increase adaptation capacity and resilience to climate change. Examples include GI: for instance protecting or enhancing natural buffers in coastal and riverine zones (e.g. mangroves, sea grass, corals) and restoring wetlands to reduce impacts of sea level rise, flooding and storm events.
CEN and CENELEC Adaptation to climate change coordination group (ACC- CG)157
The EU Strategy on Adaptation to Climate Change (COM(2013) 216 final) has invited European Standardization Organizations to contribute to the European efforts aiming to make Europe more climate-resilient. The ACC-CG group coordinates standardization activities and fosters collaboration in standardization work in the field of adaptation to climate change. The focus is on transport infrastructure, energy infrastructure and buildings / construction sector.
Procedure UNEP Ecosystem based adaptation guidance;
The UNEP uses the term ecosystem-based adaptation instead of GI. The goals for these two terms are similar. The benefits of ecosystem-based adaptation as a sustainable adaptation
155 http://www.climate-standards.org/ccb-standards/ 156 http://www.climatebonds.net/standards 157http://www.cencenelec.eu/standards/Sectors/ClimateChange/Pages/default.aspx
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Ecosystem-Based Adaptation Decision Support Framework 158
approach are highlighted. In addition to protection from climate change impacts, also the many other benefits to communities are highlighted, for example through the maintenance and enhancement of ecosystem services crucial for livelihoods and human well-being, such as clean water and food.
Integrating climate change into EIA and SEI159
An EC guidance document on how to integrate climate change and biodiversity as a standard procedure in ‘Environmental Impact Assessment’ (EIA) and ‘Strategic Environmental Assessment’ (SEI). Although the guidance focuses on the terms biodiversity and climate change, the recommendations are also valuable for GI.
Methodology Learning Framework for IUCN’s work on Ecosystem Based Adaptation 160
The IUCN has developed a learning framework for the successful implementation of Ecosystem based adaptation to climate change. Among other activities they have developed a database of all project and activities that embrace EBA.
EBA Ecosystem Based Adaptation Program 161
Methodologies and tools how to make use of biodiversity and ecosystem services as part of an overall adaptation strategy to help people adapt to the adverse impacts of climate change. Examples of ecosystem based adaptation are available for agricultural landscapes mountains, coastal areas, river basins, urban and wetlands.
Adaptation support tool European Climate Adaptation Platform 162
Many support tools exist how to successfully implement GI or ecosystem based adaptation measures. This website gives examples of guidance and tools for the different phases of implementation.
Exploring nature- based solutions; the role of GI in mitigating impacts of weather- and climate change- related natural hazards163
A practical methodology is proposed for screening (rather than assessing) ecosystem services in areas where GI may contribute to reducing current (or future) weather- and climate-related natural hazards. The report addresses landslides, avalanches, floods, soil erosion, storm surges and carbon stabilisation by ecosystems.
Interview highlights
The interview with Stefan Kleeschulte (Managing Director Space 4 Environment)
revealed the following interesting findings:
In the climate adaptation sector we are not in the phase of developing GI
standards yet, but more in an exploring phase of how GI, or nature-based
solutions, might contribute to the resilience against extreme weather events.
Performance standards, which are common practice in, for instance, the building
world, are not a useful way forward in the climate adaptation sector. The reason
for this is that the local situation is always too specific. You need to assess the
specific risks, the ecosystems present, the other ecosystem services that might be
required, etc. Too narrowly defined standards could in fact become problematic,
as flexibility is required to adapt to the specific situations.
158 www.unep.org > Climate Change Adaptation > EbA 159 http://ec.europa.eu/environment/eia/pdf/EIA%20Guidance.pdf./ 160 https://www.iucn.org/about/work/programmes/ecosystem_management/climate_change/eba/ 161 http://www.ebaflagship.org/ 162 http://climate-adapt.eea.europa.eu/adaptation-support-tool 163http://www.eea.europa.eu/publications/exploring-nature-based-solutions-2014
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The multi-functionality of GI is a benefit but it also makes planning and
implementation of GI at the same time very difficult. The prerequisites for the
different services provided by the GI, the multiple scales required for the
functioning of different services, make it all very complicated and context
dependent. In this respect integrating a GI framework into Environmental Impact
Assessments might be a way forward, as this would guarantee that the potential
of GI in landscape planning is considered.
Extent GI is integrated in standards and the potential
In climate change adaptation the notion that green adaptation provides sustainable
solutions with multiple benefits is well established. In this context the term ecosystem
based adaptation is the more familiar term for applying green infrastructure as a
climate adaptation measure. Many guidelines and good examples exist on how GI can
be applied in this sector. Most standards involve methodological guidelines and
procedures on how to incorporate GI in decision making.
Way forward
A framework with guidelines on how to assess the potential of GI-solutions and
how to implement GI to reduce vulnerability for climate hazards would be a
welcome product.
A database of good practice is always helpful as it informs local planners on the
solutions that were effective elsewhere and which they might adjust to their
specific situation.
Integrating a GI framework into Environmental Impact Assessments (EIA) and
Strategic Environmental Assessments (SEA) might be a way forward, as this
would guarantee that the potential of GI in landscape planning is considered.
Major findings on standards for performance elements
Performance standards for climate adaptation are being developed, for instance
by the ACC-CG group. However, the focus is on transport infrastructure, energy
infrastructure and the building sector and not on GI.
An exception is the CCB standards that identify land management projects that
deliver net positive benefits for climate change mitigation, for local communities
and for biodiversity. Successful CCB Verification enables the addition of a ‘CCB
label’.
Major findings on standards for procedures
The UNEP uses the term ecosystem-based adaptation instead of GI. The goals for
these two terms are similar. The benefits of ecosystem-based adaptation as a
sustainable adaptation approach are highlighted. In addition to protection from
climate change impacts, also the many other benefits to communities are
highlighted, for example through the maintenance and enhancement of
ecosystem services crucial for livelihoods and human well-being, such as clean
water and food.
There is need for a stronger focus on integrated spatial planning and methods to
stimulate cross-sectoral regional cooperation.
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Major findings on standards for methodology
Many examples of tools, guidelines and best practices already exist on how to apply
GI, or nature-based solutions, in adapting to climate change. For example the EEA164
recently published a practical methodology for screening ecosystem services in areas
where GI may contribute to reducing current (or future) weather- and climate-related
natural hazards.
164http://www.eea.europa.eu/publications/exploring-nature-based-solutions-2014
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4.4.8 GI standards and rural abandonment
GI can offer solutions for both the prevention of farmland
abandonment and for minimizing the negative impacts when
farmland is already abandoned. There are no specific GI standards in
the context of rural abandonment. An indirect way to stimulate GI in
rural abandonment areas is for instance via the Common Agricultural
Policy (CAP) funding scheme or European Structural Funds.
Table 16: Examples of standards related to rural abandonment with indication on whether GI (GI) is thoroughly included (green: GI well covered; orange: GI moderate to basically; red: GI hardly or not covered)
Type Standard Key aspects G I
Performance Common Agricultural practice (CAP)165
The CAP is an indirect instrument to stimulate Green Infrastructure in rural abandonment areas. Green Infrastructure is already well integrated in agricultural policies for instance in Pillar 1 funding and Pillar 2 European Agricultural Fund for Rural Development (EAFRD) funding. Collective Ecological Focus Areas give the opportunity to move from individual farms to implementing GI on a regional level in collective ecological focus areas.
Procedure European Structural Funds166
European Structural Funds form an opportunity to invest in rural abandonment areas. Green infrastructure is not specifically mentioned in these funds.
Integrating green infrastructure into EIA and SEI167
An EC guidance document on how to integrate climate change and biodiversity as a standard procedure in ‘Environmental Impact Assessment’ (EIA) and ‘Strategic Environmental Assessment’ (SEA). Although the guidance focuses on the terms biodiversity and climate change, the recommendations are also valuable for GI. When an environmental impact assessment is made for landscape planning in rural abandonment, the integration of GI in EIA would also stimulate the implementation of GI in rural abandonment areas.
Methodology High nature value farming indicator168
Rural abandonment can be prevented by linking Green Infrastructure to opportunities offered by HNV farming. The HNV Impact Indicator aims to assess changes in the extent and condition of HNV farming and forestry in relation to a baseline established at the start of the programming period. There is no single indicator or data source appropriate for this purpose. In the approach proposed, the Impact Indicator therefore consists of a basket of indicators put in place at the national and/or regional level.
Rewilding Europe examples169
Rewilding Europe aims to bring the variety of wildlife back to Europe’s abandoned lands. Rewilding creates new opportunities for abandoned land, creating new economic models based on wild nature. There are several ongoing pilot projects in Europe.
165 http://ec.europa.eu/agriculture/cap-post-2013/ 166 http://ec.europa.eu/regional_policy/en/funding/ 167 http://ec.europa.eu/environment/eia/pdf/EIA%20Guidance.pdf./ 168 http://ec.europa.eu/agriculture/rurdev/eval/hnv/guidance_en.pdf 169 http://www.rewildingeurope.com
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Interview highlights
No interview was taken because it can be argued rural abandonment does not really
qualify for consideration as a sector. The opposite, intensified agriculture, is indeed a
sector but falls outside of the scope here.
Extent GI is integrated in standards and the potential
There are no specific GI standards in the context of rural abandonment. An indirect
way to stimulate GI in rural abandonment areas is for instance through the Common
Agricultural Policy (CAP) funding scheme, high nature value farming (HNV-farming) or
European Structural Funds. GI is already well integrated in CAP and HNV-farming but
GI is not specifically mentioned in the European Structural Funds.
Way forward
The implementation of GI in the context of land abandonment would gain from
standardized procedures to integrate GI into Environmental Impact Assessments
(EIA) and Strategic Environmental Assessments (SEA), as this would guarantee
that the potential of GI in landscape planning is considered.
A challenge is the development of assessment methods to identify the most
suitable areas for prevention of rural abandonment as well as for use of
opportunities created by rural abandonment.
Major findings on standards for performance elements
There are no specific GI standards in the context of rural abandonment. An
indirect way to stimulate GI in rural abandonment areas is for instance through
the Common Agricultural Policy (CAP) funding scheme. GI standards are already
well integrated in CAP.
Major findings on standards for procedures
The European Structural Funds form a potential to invest in GI in rural
abandonment areas.
Major findings on standards for methodology
HNV-farming and the Rewilding Europe initiative offer best practices for how to
avoid land abandonment or create new opportunities for already abandoned land.
A challenge is the development of assessment methods to identify the most
suitable areas for prevention of abandonment as well as for use of opportunities
created by rural abandonment.
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4.4.9 GI standards and the energy sector
Terrestrial energy infrastructure consists of energy production
facilities (hydropower, windfarms, gas and coal based power plants,
nuclear power plants) as well as the energy transmission
infrastructure (oil and gas pipelines, electricity grid). As a
consequence, possibilities for developing GI are quite diverse and
rather specific for each type of energy infrastructure. The energy
sector is under full development and is characterized by increasing
investments in renewable energy as well as in electricity transmission
infrastructure in the EU. But also existing energy infrastructure is
being revitalized. The energy sector might benefit from investments
in GI for various reasons, ranging from reducing risks (operational,
reputational) to grasping opportunities (cost reduction, reputational),
depending on the type of investments. Due to the variety of energy
infrastructure, generic GI standards for the energy sector are not
available, but there are a number of specific standards available.
Table 17: Examples of standards for the energy sector with indication on whether GI (GI) is thoroughly included (green: GI well covered; orange: GI moderate to basically; red: GI hardly or not covered)
Type Standard Key aspects G I
Performance Hydropower Sustainability Assessment Protocol170
The Hydropower Sustainability Assessment Protocol provides useful guidance for promoting ecological design. This protocol covers technical, environmental, social, economic and integrative sustainability. The protocol covers all stages of a hydropower project, covering 20 performance topics which are each scored based on six criteria. Biodiversity and invasive species is one of the topics covered. All criteria have basic and best practice requirements. This has potential to cover GI and ecosystem services as a best practice requirement.
Procedure European Renewable Energy Source Directive171
This directive establishes an overall policy for the production and promotion of energy from renewable sources in the EU. It requires the EU to fulfil at least 20% of its total energy needs with renewables by 2020, to be achieved through the attainment of individual national targets. Within the directive there is a bonus system for the use of degraded land. Further, there is acknowledgement of the impact of the production of biofuels and bioliquids on biodiversity. However, no further reference is made to consider how to link energy production or transportation to ecosystem services and GI.
European Grid Declaration on Electricity Development and Nature Conservation172
In 2011 Europe’s largest transmission system operators (TSOs) and environmental NGOs signed the European Grid Declaration on Electricity Development and Nature Conservation. This Declaration sets out principles and commitments for ensuring there is no conflict between grid development and nature protection. It recognizes that the European environmental legislation provides a good basis for environmentally sensitive grid planning and delivery. It calls for full and proactive implementation of procedures such as strategic environmental assessment of grid plans. Its focus is
170 http://www.hydrosustainability.org/ 171 https://ec.europa.eu/energy/en/topics/renewable-energy/renewable-energy-directive 172 http://renewables-grid.eu/documents/eu-grid-declaration.html
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on avoiding negative impacts, not touching upon GI or the benefits ecosystem services may provide.
SEA/EIA The process ensures a detailed assessment of adverse and beneficial environmental effects for a range of alternative solutions, either at the planning stage (SEA) or the project stage (EIA). While the focus is on the assessment of impacts, an important part of these assessments is dedicated to mitigation measures. Although this provides an excellent opportunity to promote GI, the multi-functionality of it or its societal benefits are often poorly described.
Wind energy developments and Natura 2000173
This document provides guidance on how best to ensure that wind energy developments are compatible with the provisions of the Habitats and Birds Directives. It is designed for use by competent authorities and developers, as well as consultants, site managers and other practitioners who are involved in the planning, design, implementation or approval. Focus of the document is on avoiding negative impacts on biodiversity, but the document also contains examples of wind farms having delivered overall net benefits for biodiversity, this especially in areas with degraded ecosystems.
Methodology Life Elia174 Life Elia, in collaboration with the French TSO RTE, several environmental NGO’s (Solon, Carah), and the Walloon government, is implementing an EU-funded Life+ project to restore and/or create habitats in Natura2000 sites under existing overhead lines. The overall objective of the project is to restore 130km of corridors under overhead lines in Belgium and France. It aims at fostering innovation in the management of forest corridors. Furthermore, the project wants to prove that active management for biodiversity can reduce the costs of securing and maintaining corridors, thereby making use of the positive benefits of GI. Guidance documents are under preparation.
Connecting energy, protecting nature175
With the report “Connecting energy, protecting nature”, BirdLife Europe and European Environmental Bureau present their ideas on how to protect nature when planning and investing in a low carbon society. It focusses on protecting habitats and vulnerable species, but also provides guidance on how to protect and enhance natural resources, ecosystem services and the natural environment. Unfortunately it does not refer to GI as an opportunity to invest in and to the multiple societal benefits GI may provide.
AECOM for National Grid176
AECOM has developed a tool for National Grid which: (i) quantifies natural capital (NC) assets; (ii) identifies the ecosystem services (ES) provided by these assets; (iii) assesses how these ES change under different management scenarios; (iv) estimates the monetary value of these ES; (v) develops a business case for investing in NC assets.
Interview highlights
The interview with Simon Devoghele (LIFE Elia) confirmed some of the findings of the
other sectors and provided a number of useful additional insights:
There is a general lack of standards related to the maintenance of infrastructure.
For the design and building phase of high voltage electricity transmission
infrastructure there are a number of instruments including safeguards related to
protected areas (e.g. SEA, EIA, Natura 2000 guidance). However, once the route
is decided, there is no further guidance anymore.
173 http://ec.europa.eu/environment/nature/natura2000/management/docs/Wind_farms.pdf 174 http://www.life-elia.eu/ 175 http://renewables-grid.eu/fileadmin/user_upload/Files_RGI/Reports/272-1861-13- 14_Energy_infrastructure_report_w_low_res_final__1_.pdf 176 http://ec.europa.eu/environment/biodiversity/business/assets/pdf/workstream2/aecom-for-national- grid_en.pdf
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Standardisation of maintenance approaches which are beneficial for Green
Infrastructure is more than welcome. Certainly when considering the transnational
character of electricity transmission grids in the EU.
The following key elements of a good standard for GI are mentioned: 1) a good
standard should not only focus on protected species and habitats, but should deal
with common biodiversity too, 2) a good standard for GI related to electricity
transmission should allow continuous maintenance by TSOs (TSO = Transmission
System Operator); as a consequence a balance needs to be found between
practical maintenance possibilities and the required conditions for habitats and
species, 3) a good standard needs to be developed in cooperation with TSOs;
they must be on board.
The LIFE ELIA team is preparing the publication of a guidebook (foreseen early
2017). This guidebook will include best practices on vegetation management
under high voltage lines, and will cover all ecosystem types in Continental and
Atlantic biogeographic areas (another one will focus on Boreal, Alpine and
Mediterranean ecosystems). Key issues include ‘How can we promote biodiversity
under linear infrastructure and increase public acceptance?’, ‘Which (technical)
actions can be taken and how can they be implemented?’, ‘How can stakeholders
be involved?’. It will also include cost issues (at least with reference to the Cost
Benefit Assessment that was conducted under the LIFE ELIA project).
Extent GI is integrated in standards and the potential
In the field of nature protection and restoration there are a number of standards for
specific subsectors of the energy sector, such as for hydropower, windfarms and
electricity grid infrastructure, but not all of them refer to GI as an opportunity to
reduce risks and enhance societal benefits. It has been demonstrated, not at least by
the Life Elia project (see Table 17), that smart development of GI as part of new
project development substantially increases societal acceptance. For existing
electricity transmission systems it significantly reduces the maintenance cost. Hence
there is room for improvement.
Way forward
The energy sector would also benefit from GI standards. The sector needs to be made
aware that GI has multiple benefits: it increases societal acceptance of new
infrastructure which is key to acquire the license to operate, in some cases it reduces
operational costs and it always contributes to a green reputation amongst the
stakeholders. Guidance material including best practices and figures on costs and
benefits should be prepared and made available.
Major findings on standards for performance elements
Very little performance standards on GI in the energy sector have been found.
Only for the hydropower sector has a sustainability performance standard been
traced. Unfortunately it doesn’t contain specific requirements on GI. However a
suitable best practice approach on GI related to hydropower are afforestation
measures in the watershed basin which reduce erosion and the associated
siltation in the lake.
No Net Loss of biodiversity is a requirement for all wind energy projects in France.
Major findings on standards for procedures
The Renewables Grid Initiative (RGI) promotes the integration of 100%
renewably-generated electricity into the European grid. TSOs and NGOs join
forces in RGI to support the build-up of a sufficient grid infrastructure in Europe
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for both decentralized and large-scale renewable energy sources. This grid
development should be efficient, sustainable, timely, environmentally friendly,
and socially acceptable to all stakeholders.
SEA provides a perfect instrument to cover GI when comparing alternative
routings or locations for new energy infrastructure, while EIA serves as an
excellent tool to fine-tune the most suitable options at a more detailed level.
However, the concept of GI in SEA and EIA is mostly limited to its biodiversity and
landscape functions, while the full potential of its wide range of positive societal
benefits (ecosystem services) very often is only covered to a minor extent. As a
consequence the opportunities provided by GI e.g. in terms of human health
benefits, are not fully exploited. Initiatives promoting the uptake of the ecosystem
services concept in environmental impact assessment, including the development
of guidance on this issue, would be very beneficial to enhance the uptake of GI in
plans and projects at all levels (including transboundary).
Major findings on standards for methodology
Most identified GI standards for the energy sector are focusing on methods and
best practices. A most recommendable approach is the Life Elia approach.
Projects that link GI to existing ‘grey’ infrastructure - such as Gaz de France’s creation of ecological networks linked to its gas pipeline infrastructure177 - can
provide tangible early benefits and overcome scepticism amongst decision- makers. In the case of Shell178 GI has been utilized strategically to ensure
protection of coastal gas pipelines against erosion, through natural reclamation
processes, habitat restoration or development of oyster reefs.
177 http://www.gdfsuez.com/en/commitments/climate-environmental/protecting-biodiversity/ 178 www.nature.org/about-us/the-case-for-green-infrastructure.pdf
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4.4.10 General findings on integration of GI in standards
Here, we re-evaluate Table 7. At the start of this work we made best judgements to
what extent GI is included in standards for the different sectors. We based the scores
in Table 7 on our best judgment given our own expertise, and a quick screen of
available literature. Now, we are in position to make new evaluation based on a more
extensive review and information that was collected through the interviews. In Table
18, the upper table shows the results of our initial assessment. The lower table shows
the results of our new evaluation based on the insights we gained through doing the
study.
Table 18: Update of Table 7 based on the interviews
Original (Table 7)
Sector Performance Procedure Methodology
Finances
Building
Water
Transport
Public health
Industry
Climate
Rural
Abandonment
Energy
Revised Scores
Sector Performance Procedure Methodology
Finances
Building
Water
Transport
Public health
Industry
Climate
adaptation
Rural
Abandonment
Energy
[Note: For each of the nine sectors it is indicated to what extent GI is included in standards on performance, procedure and methodology (green: fairly well covered; orange: rather basic; red: little or lacking). The upper table is the original table, while the lower table shows the scores based on review and interview.]
The results in Table 18 provide at a glance to what extent GI is included in sectorial
standards. Also, the table shows several interesting and relevant findings for
improving the way GI is included in technical standards:
For performance standards, none of the sectors scored well. In most instances, if
anything was included in performance evaluations, it was biodiversity and
ecosystem services. Therefore, there is much room for having GI included in
performance standards.
For procedure standards, GI is covered for the building and water sector,
indicating the approaches taken by these sectors may provide inspiration when
including GI in procedure standards for other sectors.
For standards on methodology, results are more positive. For the building, water,
industry, climate adaptation and energy sectors, each have guidance or
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handbooks on how to make use of GI. For the transport sector, it should therefore
be relatively straightforward to also put more emphasis on GI in guidance and
handbooks. With respect to the finance sector it seems reasonable that they focus
mainly on performance and procedure standards, and leave it to the sectors they
finance for developing standards on methodologies.
We are all concerned about public health. There is increasing evidence on the
benefits green living environments provide to our health and productivity.
However, as it appears from our work, there certainly is a gap for the public
health sector when it comes to covering GI in standards.
4.5 General recommendations
4.5.1 Integrated spatial planning
Several sectors (such as climate adaptation, water, land abandonment and
infrastructure) have indicated that the implementation of GI would benefit from
integrated spatial planning early in the planning process. Also, it has been increasingly
recognized that it is necessary to work at the landscape level to ensure that sectors
can capture the benefits of GI and to maintain biodiversity and ecosystem services. A
landscape approach can contribute to bringing together sectoral economic
development plans and national action plans on biodiversity conservation, water
management and climate change. Note, for example, the emergence of Integrated
Water Resource Management (IWRM).
The International Federation of Landscape Architects (IFLA)179 recommends that GI
must become an integral part of policy and decision making. They gave the following
recommendations to achieve this:
GI needs to be integrated into Environmental Impact Assessment (EIA) and
Strategic Environmental Assessment (SEA);
Monitoring of GI delivery from EU funded infrastructure projects;
Funding for GI-related research and training;
Developing an expert service providing guidance and support on GI for public and
community bodies;
Promoting EU GI strategy, advice and guidance through professional
communication channels.
An EC guidance document is available on how to integrate climate change and
biodiversity as a standard procedure in ‘Environmental Impact Assessment’ (EIA) and
‘Strategic Environmental Assessment’ (SEA)180 (EC, 2013a and 2013b). Although the
guidance focuses on the terms biodiversity and climate change, the recommendations
are also valuable for GI. EIAs are legally required and provide an opportunity to
systematically integrate GI into a wide range of public and private projects. The report
observes however that biodiversity (and GI) and climate change are, so far, not being
systematically integrated into EIA/SEA. The main reason for this is that climate
change and biodiversity are not yet explicitly included in the formal requirements of
EIA procedures. In addition, they are multi-faceted issues that do not lend themselves
to simple or quick analyses. In this context, we highlight the Guidance Manual
‘Integrating Ecosystem Services in Strategic Environmental Assessment: A guide for
179 http://iflaeurope.eu/wp-content/uploads/sites/2/2014/03/EU-GI-IFLA-Europe-ECTP-v8-200114.pdf. 180 http://ec.europa.eu/environment/eia/pdf/SEA%20Guidance.pdf
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practitioners’181. The aim of this guidance is to better integrate ecosystem assessment,
scenario development and economic valuation of ecosystem services into development
planning at various scales (national, sub-national and local).
As indicated by IFLA, platforms providing guidance and information on GI are needed.
In this context we link to Task 3 of this contract in which an evaluation was made on
how to improve the digital disclosure of GI information through EC and sector-based
platforms.
4.5.2 Green procurement
European and the Member States’ public authorities are major consumers. By using
their purchasing power to choose environmentally friendly goods, services and works,
they can make an important contribution to sustainable consumption and production –
what is called Green Public Procurement182, or GPP. All of the nine sectors that have
been evaluated will have activities or business ongoing with public authorities.
Therefore, the way GI is included in GPP will have a major impact on how GI will be
considered in activities and businesses. GPP therefore will be key to ensure GI
procurement. What may be needed is to develop and establish a GI Public
Procurement (GIPP) to include in public tenders the use of GI as innovative solutions
presenting a real alternative to standard grey infrastructure.
Although GPP is a voluntary instrument, it has a key role to play in the Europe’s
efforts to become a more resource-efficient economy. It can help stimulate a critical
mass of demand for more sustainable goods and services which otherwise would be
difficult to get onto the market. GPP is therefore a strong stimulus for eco-innovation.
To be a success, GPP needs clear and verifiable environmental criteria for products
and services. A number of European countries already have national criteria, and the
challenge now, as GPP becomes more widespread, is to ensure that the criteria are
compatible between Member States. A level playing field will boost the single market,
ensuring that what is good for the EU is also good for the environment.
The EU GPP criteria are developed to facilitate the inclusion of green requirements in
public tender documents. These criteria have been developed for a variety of different
product groups183. There is a well-defined process for setting criteria including the
possibility for stakeholder participation184. It is also agreed for the possibility of
revising the existing GPP criteria. Therefore, with developments in the field of GI, it is
possible to have criteria designed to be favourably contribute to the deployment of GI.
4.5.3 Finding the appropriate standard
For users of standards, the ability to understand which set of standards is required for
specific applications and to easily find and get access to those standards could be
rather challenging. There is no obvious, simple and non-time consuming way of
understanding which standards are most suitable to meet needs. Therefore, users
require assistance in finding the ‘needle in the haystack’ standard that matches their
needs. A way forward therefore would be to investigate ways to facilitate the search
and access to standards. There could be a role here for sectorial organisations to
facilitate for their members the search for appropriate standards and to provide
181 http://www.proecoserv.org/images/docs/sea/2014Guideline%20ES%20into%20SEA-unep- proecoserv.pdf 182 http://ec.europa.eu/environment/gpp/index_en.htm 183 http://susproc.jrc.ec.europa.eu/product_bureau/projects.html 184 http://ec.europa.eu/environment/gpp/gpp_criteria_process.htm
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guidance on what can be achieved with which standard. This is indeed undertaken in
practice by several of the references included in this report where the overview of
standards is given on methodologies, tools and the like. In addition, it may be
considered to also work on this with the standards-making bodies. For example, this
could lead to exploring possibilities for a collaborative interactive database with a
hierarchical tree facilitating location of standards and gaining insight into what can be
done with shortlisted standards.
4.5.4 Harmonization across infrastructure sectors
Each of the infrastructure sectors (e.g. buildings, transport, energy, water) have their
own standards on performance, procedure and methodology. In the past, each of
these sectors was mainly operating in isolation from the other sectors. However, over
recent years, integrated approaches have become more common. Therefore, it may be
seen as an opportunity that the sectors we reviewed have large potential for
improving on the way GI is included in standards. Indeed, rather than each sector
working on improving the way GI is included there is potential for collaborative action
and harmonization across sectors on including GI into standards on performance,
procedure and methodology.
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5 Task 5 - Assessing costs and benefits of establishing a TEN-G
Chapter summary
Task 5 included all exploratory work related to the potential introduction of a Trans-European Network for Green Infrastructure (TEN-G) in order to determine whether a TEN-G approach is a feasible and sensible way of improving the uptake of GI across Europe.
The rationale for possibly setting up a TEN-G stems from the objective of the EU’s GI related policy ambitions to have an EU network of green infrastructure in optimal condition to deliver essential ecosystem services throughout Europe. To promote sustainability, recovery and maximum effectiveness, there should be an interlocking, coherent and co-ordinated approach across the different spatial scales (local, regional, national, EU) to the mapping and assessment of the ecosystem condition and to the identification of priorities for GI intervention/investment.
At the level of the EU, a TEN G would involve the promotion of strategic investments in the EU network of Green Infrastructure motivated by:
1. the need to protect, restore and enhance the overall quality of the network and to maintain certain minimum quality levels to ensure the continued delivery of ecosystem services;
2. the need to protect, restore and enhance the delivery of priority ecosystem services in identified geographic locations at a scale which transcends administrative boundaries, taking into account in particular trans-boundary impacts; and
3. social and/or cultural considerations that transcend administrative boundaries (e.g. the Green Belt initiative following the line of the "iron curtain" or the pilgrimage route to Santiago de Compostella).
To this end, TEN-G exploratory work that has been carried out under the service contract. Chapter 5.1 first summarises what we can learn from existing trans-European infrastructure networks (energy and transport) in terms of the possible design options of a TEN-G. As a second step (as presented in Chapter 5.2), the team developed a baseline estimating the current EU funding levels for GI under the existing GI policy and funding structures in order to compare and contrast the expected costs and benefits of a TEN-G to a situation without it.
The key outputs for the GI baseline scenario can be summarised as follows:
During the 2014 – 2020 programming period, we estimate that green infrastructure will likely receive EU finance amounting approximately to €6,397 million by public EU funds through various funding mechanisms, namely: LIFE+; the European Regional Development Fund (ERDF), the European Social Fund (ESF) and the Cohesion Fund185; the European Agricultural Fund for Rural Development (EAFRD); and the European Fisheries Fund (EFF)186. This is an average of approximately €915 million per year.
Based on the current distribution of this amount spread across the different types of GI components, a TEN-G could focus on promoting projects that enhance natural and artificial connectivity, as this is an underfunded area under the current set-up and could also contribute to reducing fragmentation.
Building on this baseline, the team implemented a first-phase assessment of costs and benefits of a potential TEN-G versus continuing the current GI policy and funding structures. Whilst the assessment process is high level and subject to a number of uncertainties, the findings indicate that a TEN-G has the potential to provide greater benefits per € invested than the current GI policy implementation and funding allocation (as described under the baseline scenario). Considering only the top five ranked components in the assessment, the benefit-cost ratio (BCR) for TEN-G is more than double the BCR under the current funding allocation. If the goal is to maximise the BCR (as opposed to focusing on particular environmental or social priorities), then the top five priority components that could make up a TEN-G network are: Natura 2000 sites, Extensive agricultural landscapes, Regional and National parks, Multi-functional sustainable managed agricultural landscapes, and Wilderness zones. The ranking of priority components changes when the aim is to maximise the level of environmental or social benefits delivered.
185 These three funds present their project beneficiaries together, without specifying which amounts come from CF, ERDF and ESF. 186 For the period 2014-2020, the EFF is replaced by so-called European Marine and Fisheries Fund (EMFF)
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Other findings of the assessment include:
Overall, the results indicate that directing money towards components already known for their high environmental value (e.g. Natura 2000 sites) can result in benefits. However, if the list of components funded is extended to consider the top components in terms of maximising the BCR, contributing to social priorities and contributing to environmental priorities, the results show that a wider variety of components should be prioritised under a TEN-G.
Operating at an EU scale rather than at Member State level enables the network to focus on those components that will provide the most benefits to Europe for the money invested, since the area of land available for implementation of such components is far greater than that available to one Member State. Therefore, at a theoretical level, the overall benefits of setting up a TEN-G would outweigh the costs, since the network could focus on implementing those components that provided the greatest benefits. At a practical level, considerations other than space would need to be taken into account to ensure that the TEN-G was comprehensive and inclusive, and shared benefits across the EU-28. However, such a network could still be far more cost beneficial than the current allocation of funding across the various GI components. Factors to take into account in the development of TEN-G would include the existing spread of GI components across the EU (to avoid imbalances between Member States), the condition of existing components, and the location of settlements and their current access to GI components (which affects the value of some of the benefits provided).
Introduction
This introduction provides a summarised overview of the key GI features rendering it
suitable for potentially capturing European added value under a common trans-
European network structure. The introduction also highlights the current
implementation and knowledge status as regards the concept of a network of GI. The
introduction concludes with capturing the rationale for investigating the possible costs
and benefits of establishing a TEN-G as compared to retaining the current status quo.
Key GI features suitable for capturing European added value
The cross-sectoral and cross-scale applications of GI solutions make it an
interesting tool to apply across various sectors on local, regional, national as well as
European levels. A coordinated approach for prioritising Green Infrastructure
investment could potentially be beneficial for all stakeholders involved.
Given the wide definition of GI, measures can range from green roofs, to wildlife
overpasses, to urban farming as well as biodiversity-rich business parks. The large
variety of cross-sectoral applications of GI on the one hand is an immense advantage
to offer solutions to various societal and environmental challenges. On the other hand,
the broad coverage also represents a certain challenge as it is difficult for decision-
makers to grasp the comprehensiveness and complexities of the topics and possible
applications involved. Figure 11 overleaf provides a non-exhaustive visual illustration
of different types of GI measures that can be applied as solutions for various sectoral
challenges.
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Figure 11 Illustration of different types of GI measures applied in Europe
[Source: Trinomics]
As mentioned before, GI is a spatial concept providing services at different scales.
Application of GI measures can therefore range from local, to regional, to national and
EU levels. Table 19 depicts the wide range of GI measures/components grouped by
their different types of functions and their applicability on the different scales. This GI
component categorisation is used throughout the Task 5 analysis as the basic units for
attaching cost and benefit measures.
Table 19 GI components by type and scale187
Descriptor Scale
Actions Local Regional/national EU
Core areas – inside protected areas Local nature reserves, water protection
areas, landscape protection areas, Natura
2000 sites
Regional and National parks and
wilderness zones (including Natura 2000
sites)
Ecological networks with cross-border
areas, including Natura 2000 network
Management of sites to maintain or
enhance their conservation status
Core areas – outside protected
areas
Natural and semi-natural ecosystems,
such as pastures, woodland, forest,
ponds, bogs, rivers and floodplains, coastal wetlands, lagoons, beaches,
marine habitats
Extensive agricultural and forest
landscapes, large marsh and bog areas,
rivers and floodplains, shorelines/coastal zones
Freshwater systems, major river basins,
mountain ranges, regional sea basins
Management of land to maintain it in its
current condition
Restoration zones Restored areas which were before
fragmented or degraded natural areas,
brownfield land or disused quarries,
transitional ecosystems due to land
abandonment or regeneration processes
Restored ecosystem types Restored landscape systems covering a
substantial part of agricultural/forestry
areas, and industrialised sites, including
cross-border areas
Actions associated with restoration and
then ongoing management of the land
once it has been restored
Sustainable use zones High nature value farmland and multi-use
forests (such as watershed forests),
protection forests (against avalanches, mudslides, stonefalls, forest fires),
natural buffers such as protection
shorelines with barrier beaches and salt
marshes
Extensive agricultural landscapes,
sustainable forest management on
regional and national levels, functional riparian systems
Transboundary landscape features on
river basin or mountain range level,
sustainable coastal and marine management zones related to the
respective sea basin
Actions associated with moving to
sustainable use and then ongoing
management of the land once it is being used sustainably
Green urban and peri-urban areas Street trees and avenues, city
forests/woodlands, high-quality green
public spaces and business
park/premises, green roofs and vertical
gardens, allotments and orchards, storm
ponds and sustainable urban drainage systems, city reserves including Natura
2000
Greenways, green belts, metropolitan
park systems
Metropolitan areas with substantial share
of high quality, green areas in Europe,
including coherent approaches in cross-
border urban zones
Actions associated with implementing
green urban and peri-urban areas and
then ongoing management of the land
once in place
Natural connectivity features Hedgerows, stone walls, small woodlands,
ponds, wildlife strips, riparian river
vegetation, transitional ecosystems
between cropland, grassland and forests
Multi-functional, sustainably managed
agricultural landscapes, riparian systems
Supra-regional corridors, substantial
share of structure-rich agricultural,
forestry or natural landscapes
Actions associated with implementing
natural connectivity features and then
ongoing management of the land once in
place
Artificial connectivity features Eco-ducts, green bridges, animal tunnels
(e.g. for amphibians), fish passes, road
verges, ecological powerline corridor
management
De-fragmented landscapes, improved
areas along transport and energy
networks, migration corridors, river
continuum
European-wide or transnational
defragmentation actions
Actions associated with implementing
artificial connectivity features and then
ongoing management of the land once in
place
187 Source: http://ec.europa.eu/environment/nature/ecosystems/docs/Table%203%20Gi.pdf
GI implementation progress by Member States
The following map provides an overview of reported GI initiatives across different
scale levels for the EU-28 Member States. The map depicts different levels of GI
initiatives per EU-28 Member State. Orange country outlines are representing the
realisation of GI initiatives on national level. Projects limited to regional or local scale
are visualised by shades of green colour for country territories ranging from 0 to 6
initiatives per Member State. At the highest spatial level transboundary initiatives
connecting multiple countries are described by arrow symbols at the common borders.
As can be seen from the map (Figure 12), cooperation and coordination not only
across regional borders, but also on a national as well as cross-border level is already
being initiated for some GI initiatives when such cooperation is seen as mutually
beneficial – even without a coordinated TEN-G in place. Further, it should be noted
that the total number of GI initiatives reported in this map is not exhaustive and the
types of GI measures implemented also range across a wider spectrum.
Figure 12 Reported GI initiatives across EU-28 by 2015
[Sources: EEA/ETC-ULS, 2015 for the Green Infrastructure Implementation and Restoration Working Group, European Commission, 2015]
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Figure 13 overleaf depicts a cross-check of reported existing GI initiatives versus each
Member State’s primary GI objectives.188 As can be seen from the visualisation, no
general trend patterns can be concluded. While some Member States have solely
worked on national level implementation to date, others have so far only implemented
local measures. Similarly, there is a wide spread across the different types of GI
components that are being implemented; though it seems that to date GI measures
implemented for the objectives of ‘nature protection and ecological networks’,
‘defragmentation’, as well as ‘landscape feature function improvement’ are prioritised
in many MS. However, this prioritisation can also possibly be explained by the
selection of GI measures that has been included here, which are likely those easily
recognisable as ‘GI’, i.e. those that help defragment and build ecological networks.
This brief review of the current GI implementation status by Member States sheds a
light on those areas that may more likely be covered by national / local initiatives and
ambition versus those areas that may be better off if coordinated on a European scale
via a structured approach under a potential TEN-G.
188 It should be noted that the GI initiatives presented in this figure are most likely not a complete overview for every MS. These are the ones that have been reported as GI by the national representatives to the EU Working Group on Green Infrastructure and Restoration. More ‘hidden’ projects, such as those funded under the European Cohesion Fund or the European Fisheries Fund, which may only have a GI component as part of their overall project, have likely not been captured here.
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Figure 13 Cross-check of reported existing GI initiatives versus primary GI objectives, EU-28
[Sources: EEA/ETC-ULS, 2015 for the Green Infrastructure Implementation and Restoration Working Group, European Commission, 2015]
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The rationale for developing a TEN-G
The spatial arrangement of green and grey elements in Europe has been shaped
predominantly by geology, climate, nature and centuries of human intervention. It is
only relatively recently that we have started to explore the opportunities for looking
strategically at the green elements in the landscape and seeing these individual
elements as a part of a network as opposed to a random patchwork. As defined in the
European Commission’s Communication, Green Infrastructure is "a strategically
planned network of natural and semi-natural areas--- designed and managed to
deliver a wide range of ecosystem services" that can maximize the benefits from
ecosystems services to society.
The overall objective of the EU’s GI related policy ambitions therefore is to have an EU
network of green infrastructure in optimal condition to deliver essential ecosystem
services throughout Europe. However, in practice priorities will need to be identified.
To promote sustainability, recovery and maximum effectiveness, there should be an
interlocking, coherent and co-ordinated approach across the different spatial scales
(local, regional, national, EU) to the mapping and assessment of the ecosystem
condition and to the identification of priorities for GI intervention/investment.
At the level of the EU, a TEN-G would involve the promotion of strategic investments
in the EU network of Green Infrastructure motivated by:
1. the need to protect, restore and enhance the overall quality of the network and
to maintain certain minimum quality levels to ensure the continued delivery of
ecosystem services;
2. the need to protect, restore and enhance the delivery of priority ecosystem
services in identified geographic locations at a scale which transcends
administrative boundaries, taking into account in particular trans-boundary
impacts; and
3. social and/or cultural considerations that transcend administrative boundaries
(e.g. the Green Belt initiative following the line of the "iron curtain" or the
pilgrimage route to Santiago de Compostela).
To this end, the remainder of Chapter 5 captures the analysis and results from the
TEN-G exploratory work that has been carried out under the service contract. Chapter
5.1 first summarises what we can learn from existing trans-European infrastructure
networks (energy and transport) in terms of the possible design options of a TEN-G.
Chapter 5.2 builds on the initial broad review provided in this introduction and builds
the baseline scenario reflecting the current status quo in terms of policy and
corresponding GI funding levels. Chapter 5.3 delivers the cost-benefit assessment
evaluating whether a TEN-G can deliver a higher benefit-cost ratio than the current
situation. Chapter 5.4 concludes on the policy implications of Task 5 findings.
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5.1 Learning from the Trans-European Networks (TENs)
The Trans-European Networks (TENs) in the areas of transport (TEN-T), energy (TEN-
E) and telecommunications (eTEN) exist in EU policy since 1993. TENs aim to link
European regions, to support the functioning of the internal market and to connect
Europe with other parts of the world.189 The main EU instruments to carry out this
policy are the Union Guidelines which set out objectives and priorities and outline
measures for establishing and developing networks; and an EU infrastructure fund
(the Connecting Europe Facility) to support projects of common interest.
Title XVI, Articles 170 – 172 of the Treaty on the Functioning of the European Union
(TFEU) provides the current legal basis for establishing the TENs.
Treaty on the Functioning of the European Union, Title XVI: Trans-European Networks
Article 170
1. To help achieve the objectives referred to in Articles 26 [establishing and ensuring the functioning of the internal market] and 174 [strengthening the Union’s economic, social and territorial cohesion] and to enable citizens of the Union, economic operators and regional and local communities to derive full benefit from the setting-up of an area without internal frontiers, the Union shall contribute to the establishment and development of trans-European networks in the areas of transport, telecommunications and energy infrastructures.
2. Within the framework of a system of open and competitive markets, action by the Union shall aim at promoting the interconnection and interoperability of national networks as well as access to such networks. It shall take account in particular of the need to link island, landlocked and peripheral regions with the central regions of the Union.
Article 171
1. In order to achieve the objectives referred to in Article 170, the Union:
- shall establish a series of guidelines covering the objectives, priorities and broad lines of measures envisaged in the sphere of trans-European networks; these guidelines shall identify projects of common interest,
- shall implement any measures that may prove necessary to ensure the interoperability of the networks, in particular in the field of technical standardisation,
- may support projects of common interest supported by Member States, which are identified in the framework of the guidelines referred to in the first indent, particularly through feasibility studies, loan guarantees or interest-rate subsidies; the Union may also contribute, through the Cohesion Fund set up pursuant to Article 177, to the financing of specific projects in Member States in the area of transport infrastructure.
The Union's activities shall take into account the potential economic viability of the projects.
2. Member States shall, in liaison with the Commission, coordinate among themselves the policies pursued at national level which may have a significant impact on the achievement of the objectives referred to in Article 170. The Commission may, in close cooperation with the Member State, take any useful initiative to promote such coordination.
3. The Union may decide to cooperate with third countries to promote projects of mutual interest and to ensure the interoperability of networks.
Article 172
The guidelines and other measures referred to in Article 171(1) shall be adopted by the European Parliament and the Council, acting in accordance with the ordinary legislative procedure and after consulting the Economic and Social Committee and the Committee of the Regions.
Guidelines and projects of common interest which relate to the territory of a Member State shall require the approval of the Member State concerned.
189 http://ec.europa.eu/transport/themes/infrastructure/ten-t-guidelines/legal-basis_en.htm
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The TENs were set up by the 12 Member States at the time. In 1996, the first
“Community guidelines” for setting up a TEN-T were adopted and, subsequently,
modified in 1999.190 A substantial review of TEN-T launched in 2009 and led to the
adoption of a new legislative framework that came into force in 2014.191
Of particular importance for green infrastructure is TEN-T. Compared to other regions
of the world, the European landscape is densely populated and its active land use is
high. Grey infrastructure (roads, railways, bridges and energy networks) has
expanded significantly and, as a consequence, the size and amount of core nature
areas has diminished, leaving remaining reserves fragmented across the continent.
This fragmentation has a negative impact on ecosystems and biodiversity hindering
wildlife from migrating between different habitats. To achieve the ambitious EU target
of halting the loss of biodiversity in the EU by 2020, it is crucial to connect the core
nature areas. Green infrastructure can play a key role in this regard.
The existing Trans-European Networks may provide, to some extent, a model for the
establishment of TEN-G in terms of governance and financing mechanisms, although
the objectives of TEN-G would be broader than those specified in the TFEU for the
TENs.
The following sections provide an overview of TEN-T and TEN-E and the ‘lessons
learnt’ from their establishment which could potentially be applicable to TEN-G. Since
the Trans-European Telecommunications Network (eTEN) is largely based on the same
principles as the other two TENs, but less connected to TEN-G in direct physical terms,
it was not examined in detail in this study.
5.1.1 Learning from the Trans-European Network for Transport (TEN-T)
TEN-T stands for the Trans-European network for Transport (TEN-T) and consists of a
transport infrastructure policy that includes projects on road, rail, maritime, inland
waterways, air, logistics, co-modality and innovation. Understanding the construction
of TEN-T can help us in framing a possible TEN-G.
Objectives and regulation of TEN-T
The main objectives of TEN-T are to close the gaps in the transport networks between
European Member States, to remove bottlenecks that hamper the smooth functioning
of the internal market, and to overcome technical barriers (e.g. incompatible
standards for railway traffic).
TEN-T was first adopted in 1996. The guidelines for the network’s development were
then reviewed in 2009 (with an analysis of strengths and weaknesses) for the period
2014-2020. TEN-T policy is currently laid down in Regulation (EU) No 1315/2013.192
190 http://ec.europa.eu/transport/themes/infrastructure/ten-t-policy/index_en.htm 191 http://ec.europa.eu/transport/themes/infrastructure/ten-t-guidelines/legal-basis_en.htm 192 Regulation (EU) No 1315/2013 of the European Parliament and of the Council of 11 December 2013 on Union guidelines for the development of the trans-European transport network and repealing Decision No 661/2010/EU.
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Revisions to the guidelines
The Green Paper "Towards a better integrated trans-European transport network at the service of the
common transport policy" published in February 2009 prompted the TEN-T policy review process. With a
view to the EU's Financial Framework for 2014–2020, the European Commission launched a policy review in
2009. The review process led to the new legislation on TEN-T, adopted in December 2013. The main novel
aspects that the revision of 2009 brought were: governance at EU level, a strong legal form, a genuine
network approach and a powerful instrument for TEN-T funding. The revised TEN-T approach includes a new
north-south orientation for the corridors recognising that the south of the EU is mostly affected by the
financial crisis of 2007. It also gives priority to transport by sea, for being more environmentally friendly
and reliable.
As foreseen by the 2013 Guidelines, so-called ‘core network corridors’ (see Figure 14)
were introduced to facilitate the coordinated implementation of the core network.
Nine core network corridors are identified in the annex to the Regulation establishing
the Connecting Europe Facility (CEF), which includes a list of projects pre-identified for
possible EU funding during the period 2014 - 2020, based on their added value for
TEN-T development and their maturity status.193 The ultimate objective of such
corridors is to complete seamless connections in order to deliver efficient, future-
oriented and high-quality transport services for citizens and economic operators. The
corridors also aim at integrating rail freight corridors, promoting clean fuel, advancing
telematics, integrating urban areas, and enhancing safety. This ‘core’ transport
network is to be supported by a ‘comprehensive network’ of routes feeding into the
core networks at regional and national level.
Figure 14 European TEN-T core network corridors
[Source: European Commission (2016) http://ec.europa.eu/transport/themes/infrastructure/index_en.htm ]
193 http://ec.europa.eu/transport/themes/infrastructure/ten-t-guidelines/corridors/index_en.htm
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The instruments used in the development of TEN-T – in particular, guidelines adopted
at EU level (through the ordinary legislative procedure) setting out the priorities and
broad lines of measures for developing TEN-T and a framework for identifying projects
of common interest – may provide a model for a future legislative framework on TEN-
G.
Budget and eligibility for TEN-T funding
The Trans-European Networks are partly funded by the EU - through the Connecting
Europe Facility (CEF) adopted in 2013, the Cohesion Fund and the European Regional
Development Fund (ERDF) – and partly by the Member States.194 A similar financing
model could potentially be applied to TEN-G.
The budget allocated to TEN-T for the period 2007-2013 was approximately €8 billion.
For 2014-2020, the TEN-T component of the CEF amounts to €26.25 billion (of which
€11.305 billion will be available only for projects in Member States eligible for the
Cohesion Fund).195 The Commission and the Member States estimated that the
development of the TEN-T network during the period 2014–2020 would require
about €500 billion of investments.196
CEF financing takes the form of grants awarded by the Commission, as well as
contributions to innovative financial instruments such as project bonds issued by the
European Investment Bank (EIB).197 The CEF also includes project support actions, to
help strengthen the Member States' and project promoters' ability to prepare project
pipelines.198 The CEF is intended to act as a catalyst for further private and public
investment by giving infrastructure projects credibility and lowering their risk
profiles.199
As EU funding has been fragmented between the TEN-T Programme (succeeded by the
CEF), the Cohesion Fund and the ERDF, the 2011 White Paper ‘Roadmap to a Single
European Transport Area – Towards a competitive and resource efficient transport
system’ recognised the need for “better coordination of the Cohesion and Structural
funds with the transport policy objectives”.200
TEN-T funding is open to MSs or, with the agreement of the MSs, international
organisations, joint undertakings, or public/private undertakings or bodies. Two legal
acts guide the allocation of EU financial support and provide information regarding the
types of projects funded and amounts: 1) the TEN Guidelines201 and 2) the CEF
Regulation.202
194 http://ec.europa.eu/transport/themes/infrastructure/ten-t-guidelines/project-funding/index_en.htm 195 http://ec.europa.eu/transport/themes/infrastructure/ten-t-guidelines/project-funding/cef_en.htm 196 European Commission (2015) Action Plan. Making the best use of new financial schemes for European transport infrastructure projects. Available at http://ec.europa.eu/transport/themes/infrastructure/ten-t- guidelines/doc/2015_06_03_cbs_action_plan_final.pdf 197 http://ec.europa.eu/transport/themes/infrastructure/ten-t-guidelines/project-funding/financial- instruments_en.htm 198 European Parliamentary Research Service (2015) Connecting Europe Facility. Briefing PE 565.903. 199 http://ec.europa.eu/transport/themes/infrastructure/ten-t-guidelines/project-funding/financial- instruments_en.htm 200 European Commission (2011) White Paper: Roadmap to a Single European Transport Area – Towards a competitive and resource efficient transport system, COM(2011) 144 final. 201 Regulation (EU) No 1315/2013 of the European Parliament and of the Council of 11 December 2013 on Union guidelines for the development of the trans-European transport network and repealing Decision No 661/2010/EU. 202 Regulation (EU) No 1316/2013 of the European Parliament and of the Council of 11 December 2013 establishing the Connecting Europe Facility.
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Eligible projects are projects of common interest and transport-related projects
involving a cross-border section or a part of such a section whenever a written
agreement exists between the MSs (and third countries) concerned. Priority projects
were defined in the 2010 TEN-T Guidelines as projects meeting the following criteria:
(a) intend to eliminate a bottleneck or complete a missing link on a major route;
cross-border projects, cross natural barriers or have a cross-border section;
(b) are on such a scale that long-term planning at European level contributes
significant added value;
(c) present, overall, potential socio-economic net benefits and other socio-
economic advantage
(d) significantly improve the mobility of goods and persons between MSs
(e) contribute to the territorial cohesion of the Union by integrating the networks
of the new MSs and improving connections with the peripheral and island regions;
(f) improve safety and reduce environmental damage caused by transport, by
promoting a modal shift towards railways, intermodal transport, inland waterways
and maritime transport;
(g) demonstrate commitment to carrying out studies and evaluation procedures in
time to complete the work in accordance with a date agreed.203
The 2013 Guidelines define projects of common interest as those which: contribute to
at least two of the four categories of objectives of the trans-European transport
network (i.e. cohesion, efficiency, sustainability, and increasing benefits for the
network’s users); comply with the Regulation’s provisions concerning the development
of the ‘comprehensive network’ and, if applicable, the ‘core network’; are economically
viable; and demonstrate European added value.204
Governance
The Commission’s Directorate-General for Mobility and Transport (DG MOVE) defines
TEN-T policy. The TEN-T Executive Agency205 turns this policy into action by managing
the individual TEN-T projects on behalf of the EC and by monitoring all open TEN-T
projects (in the periods 2000-2006 and 2007-2013 funding schemes).
The transport Ministries of the European Member States remain fully involved in TEN-T
projects because of their strategic importance at the national level. Construction in
fact is often in the hands of national implementing bodies.
The EC nominated a so-called European Coordinator to support the development of
each of the nine core network corridors and for two horizontal priorities: 1) the
European Rail Traffic Management System (ERTMS) and 2) Motorways of the Sea.
Coordinators act in the name of and on behalf of the EC and therefore cannot consist
of individuals whose territory is directly affected by a corridor. The criteria for the
selection is instead based on their knowledge of transport, financing and European
institutions. Their mandate includes an array of tasks:206
Drawing up the relevant corridor plan or the work plan for horizontal priority;
Supporting and monitoring implementation of the work plan, highlighting
difficulties, providing solutions;
203 Decision No 661/2010/EU of the European Parliament and of the Council of 7 July 2010 on Union guidelines for the development of the trans-European transport network, Article 23. 204 Regulation (EU) No 1315/2013, Article 7. 205 Executive Agency established in October 2006 in order to realise the technical and financial implementation of the TEN-T programme. It ceased its activities on 31 December 2013 and was superseded by the Innovation and Networks Executive Agency (INEA). 206 http://ec.europa.eu/transport/themes/infrastructure/ten-t-guidelines/european- coordinators/index_en.htm
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Regularly consulting the corridor forum;
Making recommendations regarding transport development along corridors and
access to financing/funding sources;
Annual reporting of progress to the European Parliament, the European Council,
the EC and the MSs.
In June 2015, the finalised work plans of the 11 European Coordinators for the TEN-T were approved, establishing the basis for action until 2030.207
Implementation experiences and lessons learnt
One of the most remarkable achievements of the experience with TEN-T is the smooth
connection between Eastern and Western Europe in the aftermath of the 2004
enlargement.208 Another success relates to its mode of governance – with an
Executive Agency that turns policy into action - which has resulted in fewer delays and
more influence over the projects.
It should be noted that despite TEN-T governance at the EU level, responsibility for
completing the large numbers of projects rests almost entirely with the Member
States, whose investment decisions are essentially driven by national objectives.
Providing adequate funding for TEN-T has been a key challenge since the programme’s
beginning. The European financial envelope dedicated to TEN-T in 2007-2013 did not
have enough resources to cover the required spending on TEN-T (it amounted to
€8,013 million, while the estimated needs were €250 billion. Funding available under
the CEF for the 2014-2020 is considerably higher (€26 billion) but additional sources
will still be necessary. Innovative financial instruments such as the EIB Loan
Guarantee Instrument and the Risk Capital Facility represent additional promising
ways of supporting TEN-T projects. The lion’s share of investment (73%) between
2007 and 2013 had to come from national budgets or private financing.209
The bulk of the investment in transport infrastructure has been provided traditionally
by the public sector, however in the aftermath of the financial crisis, government
budgets cannot finance the transport infrastructure needs by 2020. At the same time,
the volume of private participation in financing infrastructure projects in the EU
remains relatively modest. The main sources of funding will continue to be national
sources representing over 70% of TEN-T investment requirement, followed by EU
grants and EIB standard loans.210 In the case of cost overruns, the burden is borne by
the Member States.211 The TEN-T programme requires commitment by the project
promoters for EU financial aid and by the MSs concerned to make a financial
contribution to the project, mobilising private funds if necessary. The TEN-T funding
covers only a small part of the total funding of the project and is generally given in the
form of a grant. These considerations would also be relevant when developing funding
instruments for TEN-G.
207 http://ec.europa.eu/transport/themes/infrastructure/index_en.htm 208 http://ec.europa.eu/transport/themes/infrastructure/ten-t-policy/index_en.htm 209 Expert Group (2010) Final report of the expert group 2 – Integration of Transport Policy into TEN-T Planning, 19 April 2010 210 Bodewig, K. and Secchi, C. (2014) Attracting investments towards transport infrastructure: potential lines of action. Brussels: DG MOVE, European Commission. 211 European Commission (2011) Mid-term evaluation of the TEN-T Programme (2007-2013)
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5.1.2 Learning from the Trans-European Network for Energy (TEN-E)
High-quality infrastructure is essential for the economic growth of European Member
States and the EU as a whole. Reasonable prices for electricity, gas and oil in a unified
European energy market depend on the existence of energy transmission grids
covering the individual states and connecting them. Transformation to a sustainable
economy with a large proportion of energy drawn from renewable sources will require
major changes in the transmission grid infrastructure. Upgrading the existing
infrastructure and building new infrastructure thus represents a major challenge for
the coming decades and the EC is actively striving to promote it. TEN-E, which stands
for the Trans-European Networks for Energy would serve this purpose.
Objectives and regulation of TEN-E
The objective of TEN-E is to help build and finance important energy infrastructure in
order to connect EU countries currently isolated from European energy markets,
strengthen existing cross-border interconnections, and help integrate renewable
energy. Concretely, its aim is to:
Ensure effective operation of the internal energy market through the
interconnection, interoperability and development of trans-European networks for
transporting electricity and gas;
Ensure security and diversification of supply for instance by interoperability
with the energy networks of third countries;
Strengthen territorial cohesion through reducing the isolation of the less-
favoured, island, landlocked or remote regions;
Promote sustainable development by improving the links between renewable
energy production installations and through more efficient technologies.
TEN-E is regulated by Regulation (EU) No 347/2013 of the European Parliament and of
the Council of 17 April 2013 on guidelines for trans-European energy infrastructure
repealing Decision No 1364/2006/EC and amending Regulations (EC) No 713/2009,
(EC) No 714/2009 and (EC) No 715/2009. The Regulation’s aim is to facilitate the
timely development and interoperability of trans-European energy networks (TEN-E).
In particular, the Regulation:
addresses the identification of projects of common interest necessary to
implement priority corridors and areas;
facilitates the timely implementation of projects of common interest by
streamlining, coordinating more closely, and accelerating permit granting
processes and by enhancing public participation;
provides rules and guidance for the cross-border allocation of costs and risk-
related incentives for projects of common interest;
determines the conditions for eligibility of projects of common interest for Union
financial assistance.212
Budget and eligibility for TEN-E funding
The total TEN-E budget was 155 million euro in the period 2007-2013.213 Funding
sources are multiple, including the TEN-E budget line (around EUR 20 million per year,
mainly intended for financing feasibility studies), the European Fund for Energy,
Climate change and Infrastructure loans, the Structural and Cohesion Funds, the
212 Regulation EU No 347/2013, Article 1 (2). 213 http://www.crpm.org/pub/agenda/1856_jdh_-_connecting_europe__ten-e.pdf
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European Neighbourhood and Partnership Instrument (ENPI), the Neighbourhood
Investment Facility (NIF), the EU Research Programmes, and the European
Investment Bank (EIB) loans.
In the programming period 2014-2020, the Trans-European Networks in the field of
energy (TEN-E) are financed through the Connecting Europe Facility (CEF). The
amount earmarked for trans-European energy infrastructure in the CEF is
approximately €5.4 billion over the 2014-2020 Multiannual Financial Framework.214
Governance
The main instruments governing the implementation of TEN-E are Regulation
347/2013, which lays down guidelines for trans-European energy infrastructure, and
Regulation 680/2007/EC (as amended by Regulation 347/2013) which sets out
general rules for the financing of Trans-European Networks.
Following close consultations with Member States and stakeholders, the Commission
identified 12 strategic trans-European energy infrastructure priority corridors (for
electricity, gas and oil) and thematic areas whose implementation by 2020 was
deemed essential for the achievement of the Union’s energy and climate policy
objectives. The TEN-E Regulation 347/2013 lays down rules for the timely
development and interoperability of these priority corridors and areas. In particular, it
sets out guidelines for streamlining the permitting processes for major energy
infrastructure projects that contribute to European energy networks. Such projects,
referred to as ‘Projects of Common Interest’ (PCIs), are selected by twelve regional
groups established under the Regulation, composed of representatives from the
Member States, the Transmission Systems Operators (TSO), the Commission, the
Agency for the Cooperation of Energy Regulators and the European Network of
Transmission Systems Operators (ENTSO). Project promoters wishing projects to be
included on the “Union List” of PCIs apply to the regional groups, which adopt a
regional list of proposed PCIs. Each individual proposal for a project of common
interest requires the approval of the Member States to whose territory the project
relates. Based on the Regional Lists, the Commission adopts a Union List of PCIs
through a delegated act. For a project to be included in the list, it has to: have
significant benefits for at least two EU Member States; contribute to market
integration and further competition; enhance security of supply; and reduce CO2
emissions. The Union list of PCIs is updated every 2 years.
The TEN-E guidelines state that PCIs should be implemented as quickly as possible
and closely monitored and evaluated, while keeping the administrative burden for
project promoters to a minimum. It also foresees that the Commission may designate
European coordinators for projects facing particular difficulties.
As in the case of TEN-T, the financing and governance instruments of TEN-E could
potentially provide a model for the development of TEN-G.
Implementation experiences, successes and hindrances
An ex-post evaluation of the TEN-E funding programme for 2000-2006215 concluded
that TEN-E had made a positive contribution towards the integration of gas and
electricity markets, facilitating cross-border collaboration and encouraging greater
public and private investment. However, the evaluation also highlighted a number of
barriers to the programme's impact, including budget limitations and the fact that
214 European Parliamentary Research Service (2015) Connecting Europe Facility. Briefing PE 565.903. 215 Rademaekers, K. et al. (2009) Ex-Post Evaluation of the Trans-European Energy Networks (TEN-E) Funding Programme 2000-2006. Final report, DG TREN Framework Contract TREN/A2/143-2007, Rotterdam: ECOFYS and ECORYS.
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priority actions were not suitably identified in advance. Calls for proposals attracted
few applications, and sometimes of poor quality, so the allocated TEN-E budget often
remained under-spent. These concerns were addressed in the current CEF, whose
budget is substantially greater than that of TEN-E, and includes the identification of
PCIs that outline priority areas for EU action and funding.216
The Impact Assessment accompanying the 2013 TEN-E Regulation217 also highlighted
a number of factors hindering the development of TEN-E under the previous legislative
instruments. In particular, it concluded that lengthy and ineffective permit granting
procedures, along with public opposition to the projects, were amongst the major
reasons impeding the timely implementation of energy infrastructure projects. Long
delays were caused, inter alia, by the complex and fragmented permit-granting
process, the lack of binding time limits for the procedures in many MS, and opposition
by landowners, citizens living in the vicinity of potential installations and stakeholder
organisations. Other obstacles mentioned in the Impact Assessment include the lack of
appropriate regulatory incentives and long-term signals to meet EU priorities, lack of
coordination for cross-border investment approval processes, and the lack of
innovative financial instruments at EU level which would support projects in a different
manner than only by reducing the initial capital expenditure for investors. Since
energy infrastructure projects are different in nature from the building blocks of a
potential TEN-G, it is difficult to assess to what extent similar obstacles would impede
the development of TEN-G. Nevertheless, issues such as budget limitations, the need
for adequate incentives at EU level, and the need to set an effective framework for
identifying and implementing priority projects appear, in principle, relevant in the
context of TEN-G.
5.1.3 Conclusions regarding the future design of TEN-G
The overall lessons to be drawn from the set-up and implementation of TEN-T and
TEN-E with respect to a possible architecture of a TEN-G framework can be
summarised as follows:
A future legislative framework for TEN-G could potentially have recourse to
similar instruments as those used in the development of the existing TENs, i.e.
guidelines adopted at EU level setting out the priorities and broad lines of
measures for developing the network and a framework (including specific criteria)
for identifying priority projects (or ‘projects of common interest’), as well as a
dedicated EU fund to support such projects.
The architecture of TEN-G could potentially be based on similar concepts, such
as ‘core network corridors’ supported by a broader network of features (akin to
the ‘comprehensive network’ in TEN-T) feeding into the core network at
regional/national levels.
Elements of the current TENs’ governance structure could also be mirrored in
TEN-G, for example, the process for including projects of common interest on the
‘Union List’, the appointment of European coordinators, the delegation of
responsibility for managing/overseeing the PCIs to an executive agency.
TEN-G could be based on a similar financing model as the existing TENs, with
funding provided partly by the EU (through a mix of grants and innovative
financial instruments), partly by the Member States and private investors. The
experience with TEN-T and TEN-E has highlighted the need to use EU funding as
216 European Parliamentary Research Service (2015) Connecting Europe Facility. Briefing PE 565.903. 217 Impact Assessment accompanying the Proposal for a Regulation of the European Parliament and of the Council on guidelines for trans-European energy infrastructure, SEC(2011) 1233 final.
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a catalyst for other investment sources and to employ innovative financial
instruments.
In terms of challenges highlighted by the implementation of TEN-T and TEN-E,
the need to secure adequate funding for the network and to set an effective
framework for implementing priority projects (avoiding delays, facilitating the
permitting process, avoiding conflicts among stakeholders, etc.) should also be
borne in mind when designing TEN-G.
5.2 Developing the current TEN-G baseline
The baseline scenario (otherwise known as the no-action scenario or business as
usual) of green infrastructure (GI) implementation in the EU is – for the purpose of
this task - defined as the current scope of and expenditure on GI projects by the EU,
assuming that policies continue as they are, and that a TEN-G network is not going to
be implemented. Therefore, the baseline scenario assumes no new GI activities are
taking place other than those already included in current policies, programmes and
planning.
5.2.1 The methodology to estimate and assess the baseline
Our approach to estimate such a baseline has been twofold:
1) Defining the scope of GI;
2) Quantifying EU funding given to projects that fall under that definition.
We have defined the scope of GI in line with the building blocks of GI (the various
elements or services of GI on the different scales – from local, to regional/national, to European scale - grouped by their function) as elaborated by the EC.218 These are:
core green areas within219 and outside protected areas220, restoration zones221,
sustainable use green zones222, green urban and peri-urban areas223, natural
connectivity features224, artificial connectivity features225. Everything that falls under
those elements has been considered GI.
Subsequently, we have analysed different EU funding mechanisms for potential eligible
projects per component type. GI projects have been sought for under LIFE+, the
European Regional Development Fund (ERDF), the European Social Fund (ESF), the
European Agricultural Guarantee fund (EAGF), the European Agricultural Fund for
218 http://ec.europa.eu/environment/nature/ecosystems/docs/Table%203%20Gi.pdf. 219 GI in protected areas include Nature reserves; Water protection areas; Landscape protection areas; Natura 2000 sites; Regional / National parks; Regional / National wilderness zones; Ecological networks 220 GI outside protected areas includes Pastures; Woodland; Forests; Ponds; Bogs; Rivers; Floodplains; Coastal wetlands; Lagoons; Beaches; Marine habitats; Freshwater systems; River basins; Sea basins; 221 Restored areas of previously fragmented or degraded natural areas; Brownfield land / disused quarries; Transitional ecosystems; Restored ecosystems; Restored landscape systems covering agricultural/forestry areas and industrialised sites 222 High nature value farmland; Multi-use forests (e.g. watershed forests); Protection forests e.g. against avalanches, mudslides, stone fall, forest fires; Protection shorelines (e.g. with barrier beaches and salt marshes); Extensive agriculture landscapes; Sustainable forest management on regional/national level; Functional riparian systems; Transboundary landscape features on river basin or mountain range level; Sustainable coastal and marine management zones 223 Street trees; City forests / woodlands; High-quality green public spaces; Business parks/premises; Green roofs; Vertical gardens; Allotments and orchards; Storm ponds; Sustainable urban drainage systems; City reserves; Greenways; Green belts; Metropolitan park systems 224 Hedgerows; Stone walls; Small woodlands; Ponds; Wildlife strips; Riparian river vegetation; Transitional ecosystems between cropland, grassland and forests; Multi-functional, sustainably managed agricultural landscapes; Riparian systems; Supra-regional corridors; Structure-rich agricultural, forestry or natural landscapes 225 Eco-ducts; Green bridges; Animal tunnels; Fish passes; Road verges; De-fragmented landscapes; Improved areas along energy and transport networks; Migration corridors; River continuum.
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Rural Development (EAFRD), the European Marine and Fisheries Fund (EMFF), and the Cohesion Fund. For each of these funds226, we have accessed databases of project
funding beneficiaries and have screened all projects therein, in order to identify all
those projects that we can consider to be GI projects. Overall, we have looked into
every theme under which GI investments could be going on from environment, to
climate, to urban development, to rural development, to water, etc. For a detailed
overview of the filters applied for each fund, see Annex 17
“Method_LIFE_ERDF_CF_ESF_EAFRD_EFF”. We have only included GI projects
concerning implementation and have excluded awareness-raising and research aimed
projects, as these do not directly expand green infrastructure as such.
For the purpose of the analysis, we have grouped projects according to their objective
so as to grasp which aspects of GI are currently (not) covered by EU funding. The
categories in which we have grouped projects read as follows (inspired by the GI
building blocks of the EU): core green (protected) areas, restoration zones,
sustainable use zones, green urban and peri-urban areas, natural connectivity
features, artificial connectivity features.
For every GI project identified, we have searched for the EU-funded amount. These
amounts have then been recorded in an Excel database for the year they have been
reported. It should be noted that the baseline therefore does not take into account
potential delays in implementation or fund allocation.
The sum of all EU funds allocated to GI projects across all considered funding
mechanisms forms the baseline for the 2007-2013 programming period, which we
have then extrapolated to the current 2014 – 2020 programming period.
The remaining sub-sections of chapter 5.2 provide a more detailed information on the
2007-2013 data available on GI funding levels, an analysis of the differences between
the two funding periods, and a presentation of the GI baseline that was consequently
developed for the purpose of assessing the costs and benefits of establishing a TEN-G.
5.2.2 Analysis of funds allocated to GI in the period 2007-2013 (analysis of
the Excel file)
The analysis presented here is based on the baseline excel file included as Annex 16.
Amounts and origin of GI funding
The result of the analysis of the Excel file entries show that for the period 2007-2013
green infrastructure received EU finance amounting to €6,579 million through
various funding mechanisms, namely: LIFE+; the European Regional Development
Fund (ERDF), the European Social Fund (ESF) and the Cohesion Fund227; the European
Agricultural Fund for Rural Development (EAFRD); and the European Fisheries Fund
(EFF)228. This is an average of almost €940 million per year.
Although in monetary terms the fund contributing most to GI by far appears to be the
agriculture fund EAFRD, only around 1% of its total budget (€420.7 billion) was
allocated to GI between 2007 and 2013. That accounted for €5,631 million (85% of
the total EU-funded GI). Proportionally speaking in fact, LIFE funds are the most
important contributor to GI. Funding from LIFE amounts to almost €774 million for
226 Except for the agricultural funds for which project-level information for the period under consideration is not available 227 These three funds present their project beneficiaries together, without specifying which amounts come from CF, ERDF and ESF. 228 For the period 2014-2020, the EFF is replaced by so-called European Marine and Fisheries Fund (EMFF)
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the period 2007-2013 (more than 20% of the total EU-funded GI) which means that
more than 36% of the total LIFE budget is allocated to activities that can be
considered GI. Less than 1% of the total EFF budget has been invested in activities
that can be considered GI implementation, accounting for €33 million in the period
2007-2013 (less than 1% of the total EU-funded GI). A very small percentage
(0.04%) of all the ERDF, CF and ESF budgets have also funded GI in the EU
(amounting to €140 million for the period 2007-2013; 2% of the total EU-funded
GI).
Figure 15 Contribution of EU funds to GI in total € values (2007-2013)
[Source: Own analysis based on gathered data]
The countries making most use of LIFE funds are Germany, Spain, Italy and Belgium,
in that order (see Figure 16). This indicates that although Germany is not the top
beneficiary of total LIFE funds (the LIFE evaluation available shows that Italy and then Spain are the main beneficiaries of the total LIFE funds and Germany the third229), it
places a greater focus on GI than does, for instance, Italy.
229 http://ec.europa.eu/environment/life/publications/lifepublications/evaluation/documents/LIFEplus_mte_ann exes.pdf
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Figure 16 EU funds per country (in €) (2007-2013)
[Source: Own analysis based on gathered data]
The aspects of GI currently funded and the gaps in such funding
Between 2007 and 2013 funding has primarily been allocated to finance the
conservation of green areas (€5,960 million; 90% of all GI funding) and restoration
of green areas (€462 million; 7% of all GI funding) (see Figure 17). By contrast, GI
funding for sustainable use of zones, green urban and peri-urban areas and natural
and artificial connectivity features was in this period relatively very scarce (less than
1% of all GI funding each). These building blocks of GI can be considered
underfunded in the baseline situation.
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Figure 17 Types of EU-funded GI (in €) (2007-2013)
[Source: Own analysis based on gathered data]
LIFE captures a variety of elements across all realms of GI, especially funding
biodiversity conservation and restoration, but also a few sustainable use, urban and
connectivity-related projects. The projects falling under sustainable use of zones
regarded mainly sustainable management of water habitats and green areas.
Investments in urban and peri-urban areas involve green roofs, city parks, urban
forestation and the like. Connectivity projects under LIFE are wild. There is no
indication of financing having been provided to projects dealing with other
connectivity-related GI such as eco-ducts, green bridges, areas along energy and
transport networks. GI implementation is not the ultimate aim of the projects.
Instead, the implementation of GI is the result or the means though which projects
that aim at, for example, biodiversity conservation/restoration, greening of urban
areas and increased liveability are realised.
For the rest of the funds, a very small part of what it is funded corresponds to GI. The
ERDF covers projects across various elements of GI, from conservation and restoration
to connectivity and urban interventions. It is also the fund in which GI cross-boundary
projects –involving various countries- are funded. The EAFRD on the other hand only
finances aspects of GI that concern conserving, expanding or restoring green (rural)
areas. The EFF is an interesting case for the stark differences found between countries
in the number and the type of projects with a GI component that are implemented.
For instance, while GI projects related to the marine environment were not found in
Austria or Portugal, plenty of these projects were found for Denmark. Spain, which
benefits massively from these funds, has just implemented a handful of projects that
can considered GI. Overall, the focus of the EFF is primarily on funding marine
ecosystems restoration and (re-)stablishing fish passes and artificial riffs.
The above sheds light on the extent to which current funding covers the different
elements of GI. Current funding for conservation and restoration is significantly
greater than for other categories. Certain GI elements have not received any funding.
With regard to sustainable land use, for instance, sustainable agriculture or crop
rotation are currently not covered by EU funding. Investments in greening urban and
peri-urban areas fail to address greenways and green belts. Connectivity mostly funds
fish passes and animal corridors while there is no indication of funding allocated to
projects dealing with other connectivity-related GI such as eco-ducts, green bridges,
areas along energy and transport networks.
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5.2.3 Differences between the programming periods 2007-2013 and 2014-
2020
This section highlights the differences between the two programming periods to be
taken into account when extrapolating the GI funding baseline from the past to the
current programming period.
LIFE
As outlined by the LIFE programme website, the programming period 2007-2013 had
a budget of €2,143 million. The programme consisted of three components: 1) LIFE+
Nature and Biodiversity, 2) LIFE+ Environment Policy and Governance, and 3) LIFE+
Information and Communication. Up to 50% of the budget at least was dedicated
to the LIFE+ Nature & Biodiversity component. This focused on co-financing best
practice or demonstration projects that contribute to the implementation of the Birds
and Habitats Directives and the Natura 2000 network, and innovative or
demonstration projects contributing to the implementation of the objectives of the
Commission’s Communication on "Halting the loss of biodiversity by 2010 – and
beyond". LIFE+ Environment Policy & Governance focused on co-financing
innovative or pilot projects contributing to the implementation of European
environmental policy and the development of innovative policy ideas, technologies,
methods and instruments. It also helped monitor pressures on the environment
(including the long-term monitoring of forests and environmental interactions). LIFE+
Information & Communication co-financed communication and awareness-raising
campaigns on environmental, nature protection or biodiversity conservation issues, as
well as projects related to forest fire prevention (awareness raising, special training).
For the LIFE 2014-2020 programming period, the Commission will allocate €3,456.7 million.230 One innovative aspect of it is that it will include one sub-programme for
environment and another one for climate which will get €2,592.5 million, €864.2 million budget respectively.231 The ‘Environment’ strand covers three priority areas:
environment and resource efficiency (implementation of environment policy and
exclude market replication-oriented innovation); nature and biodiversity (biodiversity
challenges, Natura 2000); and environmental governance and information (knowledge
sharing, dissemination of best practices, better compliance, awareness raising
campaigns). The ‘Climate Action’ strand covers climate change mitigation (reduction of
greenhouse gas emissions); climate change adaptation (increasing resilience to
climate change); and climate governance and information (increasing awareness,
communication, cooperation and dissemination on climate mitigation and adaptation).
ERDF
The ERDF supports programmes that intend to strengthen economic, social and
territorial cohesion in the European Union by correcting imbalances between regions. For the period 2007-2013 the fund amounted €200.7 billion.232 Funding priorities
included research, innovation, environmental protection, risk prevention, and infrastructure investment especially in the least developed regions.233 For 2014-2020
the available budget is €187.4 billion.234 Priority areas are again research and
development, and innovation; and expand to also include topics such as improving
access to and quality of information and communication technologies; climate change
and the transition towards a low-carbon economy; business support to SMEs;
230 http://ec.europa.eu/environment/life/about/documents/life2014-2020.pdf 231 http://ec.europa.eu/environment/life/about/documents/life2014-2020.pdf 232 http://epthinktank.eu/2014/05/07/structural-and-cohesion-funds-in-the-member-states-an- overview/erdf_esf_cf2007-2013/ 233 http://ec.€opa.eu/regional_policy/en/information/legislation/regulations/2007-2013/#erdfregulation 234 https://cohesiondata.ec.€opa.eu/
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telecommunication, energy, and transport infrastructures; enhancing institutional
capacity and effective public administration; health, education, and social infrastructures; and sustainable urban development.235
ESF
The European Social Fund (ESF) contributes to economic, social and territorial
cohesion by investing in people. It increases the employment opportunities of
European citizens, promotes better education, and improves the situation of the most
vulnerable people at risk of poverty. Its focus for 2007-2013 was on four key areas:
increasing adaptability of workers and enterprises, enhancing access to employment
and participation in the labour market, combating discrimination and facilitating access
to the labour market for disadvantaged people, and promoting partnership for reform
in the fields of employment and inclusion.236 Its budget was €76.8 billion.237 For the
period 2014-2020 the available budget amounts to approximately €86.4 billion. The
four thematic objectives read: promoting employment and supporting labour mobility;
promoting social inclusion and combating poverty; investing in education, skills and
lifelong learning; and enhancing institutional capacity and an efficient public administration.238 The innovation is that ESF should in this new programme also
contribute to objectives such as the transition towards a low carbon society, and a
climate-resilient and resource efficient economy; enhancing the use of information and
communication technologies; strengthening research, technological development and
innovation; and enhancing the competitiveness of small and medium-sized enterprises
(SMEs).
CF
The Cohesion Fund contributes to interventions in the field of the environment and
trans-European transport networks (TEN-T).239 In the period 2007-2013, it amounted €70.1 billion.240 For 2014-2020, the fund will have a budget of €63.2 billion.241
EAGF, EAFRD
Common Agricultural Policy (CAP) is financed by two funds: the European Agricultural
Guarantee Fund (EAGF) and the European Agricultural Fund for Rural Development (EAFRD). The CAP budget for 2007-2013 was €420.7 billion.242 In 2014-2020 the CAP
budget is established at around €418.4 billion, €317.2 billion as EAGF to finance
direct payments to farmers and measures to regulate agricultural markets such as
intervention and export refunds; and €101.2 billion as EAFRD, to finance the rural
development programmes of the Member States. Compared to the period 2007-2013,
for the period 2014-2020 funds for EAGF decreased 17.5% and those for EAFRD
increased up to 9%. The decrease of spending on activities related to the natural resources is estimated at 11.3% (€47.5 billion).243
235 http://ec.€opa.eu/maritimeaffairs/policy/sea_basins/atlantic_ocean/atlanticforum/funds_en.pdf 236 http://ec.€opa.eu/regional_policy/en/information/legislation/regulations/2007-2013/#erdfregulation 237 http://epthinktank.eu/2014/05/07/structural-and-cohesion-funds-in-the-member-states-an-
overview/erdf_esf_cf2007-2013/ 238 http://ec.€opa.eu/regional_policy/en/information/legislation/regulations/2007-2013/#erdfregulation 239 http://ec.€opa.eu/regional_policy/en/information/legislation/regulations/2007-2013/#erdfregulation 240 http://epthinktank.eu/2014/05/07/structural-and-cohesion-funds-in-the-member-states-an- overview/erdf_esf_cf2007-2013/ 241 https://cohesiondata.ec.€opa.eu/ 242 Stępień, S., & Mironescu, A. (2013). Budget of the EU for 2014-2020. Results of the Negotiations in the Light of the Polish Agriculture Interests. Romanian Economic Business Review, 8(4.1), 167-178. 243 Stępień, S., & Mironescu, A. (2013). Budget Of The Eu For 2014-2020. Results Of The Negotiations In The Light Of The Polish Agriculture Interests. Romanian Economic Business Review, 8(4.1), 167-178.
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EFF, EMFF
The European Fisheries fund (EFF) had a budget of €4.3 billion for 2007-2013. It targeted all sectors244 of the industry focusing on five priority areas (axes)245 that read:
adjustment of the fleet (e.g. to support scrapping of fishing vessels);
aquaculture, processing and marketing, and inland fishing (e.g. to support the
shift to more environmentally friendly production methods);
measures of common interest (e.g. to improve product traceability or labelling);
sustainable development of fisheries areas (e.g. to support diversification of the
local economy);
technical assistance to finance the administration of the fund.
For the period 2014-2020, the EFF has been replaced by the so-called European Maritime and Fisheries Fund (EMFF). With a budget of around €5.749 billion246 the
EMFF aims to fund: the promotion of sustainable and competitive fisheries and
aquaculture; fostering the development and implementation of the Union's Integrated
Maritime Policy; the promotion of balanced and inclusive territorial development of
fisheries areas (including aquaculture and inland fishing); the contribution to the
implementation of the Common Fisheries Policy. The EMFF is structured around 4
pillars, namely:
Smart Green Fisheries- aid to promote selective gears, discard measures, foster
innovation, economic viability of the sector;
Smart Green Aquaculture- aid to develop aquaculture production;
Sustainable and Inclusive Territorial Development- aid to promote growth, skills
and job diversification to other sectors of the maritime economy;
Integrated Maritime Policy- aid to enhance marine knowledge, maritime spatial
planning, integrated coastal zone management, adaptation to climate change.
It has been argued that the main difference between the EFF and the EMFF is the inclusion of the Integrated Maritime Policy (IMP).247 This IMP includes a number of
cross cutting measures including maritime surveillance, data sharing, Marine Spatial
Planning (MSP) and Integrated Coastal Zone Management (ICZM).
Total available budgets for the two programming periods Figure 18 shows the total available budgets of the analysed EU funds for the 2007-2013 and the 2014-2020 periods respectively, to place the GI baseline into perspective in relation to the overall available budgets per fund.
244 sea and inland fishing, aquaculture (the farming of fish, shellfish and aquatic plants), and processing and marketing of fisheries products. 245 http://€-lex.€opa.eu/legal-content/EN/TXT/PDF/?uri=CELEX:32007R0498&from=EN 246 http://ec.€opa.eu/fisheries/documentation/publications/pcp_en.pdf 247 https://www.gov.uk/government/consultations/€opean-marine-and-fisheries-fund-emff
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Figure 18 Total budget of EU funds (2007-2013 and 2014-2020)
5.2.4 The Baseline - Extrapolation of the results for 2007-2013 into the new
programming period 2014-2020
In order to calculate the baseline, we have parted from the analysis for the period
2007-2013 above (for which accurate project-level information exists), made
assumptions based on the differences described in section 5.2.3 and have accordingly
calculated the baseline of GI funding for the current programming period 2014-2020.
Assumptions for the extrapolation
LIFE
While the priorities within its ‘environment’ strand do not seem to change much for
the new period, the new focus in climate topics is promising for GI solutions targeted
at enhancing ecosystem services that contribute to climate change mitigation or
adaptation (and which were rather lacking in the period 2007-2013).
Throughout 2014-2020, an additional €1313.7 million will be allocated in comparison
to 2007-2013; in other words, the LIFE funding line has been expanded by 60% for
2014-2020. Our assumption is that the focus of the sub-programme accrued to
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environment remains comparable to the previous period (as it again consists of 3 lines
of focus, the third being more concerned with communication – and hence less
relevant for our assessment of GI implementation). Similarly, the sub-programme on
climate is divided in three lines of which the first two (on adaptation and mitigation)
are relevant for GI implementation and the third is not (as it regards governance and
information).
Assumption: It cannot be deducted from the programme’s priorities whether more
funds will be allocated to GI than in the programme before. Thus, the assumption we
are making is that 36%248 of total LIFE funds will be allocated to GI activities for the
period 2014-2020. Yet, due to the new climate investment line within LIFE, the
categories or aspects of GI funded are likely to change, in favour of GI investments
particularly aiming at climate adaptation and mitigation. If we are to make
assumptions of what this could mean for the categories we have classified projects
into, we could argue that projects on climate adaptation and mitigation majorly would
fit under the categories ‘Total sustainable use green zones’ and ‘Total green urban and
peri-urban areas’. Thus, the baseline we propose assumes that 36% of the total funds
that will be allocated to climate (€864.2M) belong to GI investments made in these
two categories.
Figures 19 and 20 show the types of GI funded by LIFE and their relative weighting in
the two programming periods.
Figure 19 Types of GI funded by LIFE 2007-2013
[Source: Own analysis based on gathered data]
248 This is the percentage of the total LIFE budget allocated into GI in the period 2007-2013.
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Figure 20 Types of GI funded by LIFE 2014-2020
[Source: Own analysis based on gathered data]
ERDF, ESF, CF
The ERDF, CF and ESF compose the so called European Regional Policy. For the
programme period 2007-2013, the paid ERDF, CF and ESF amounted respectively to a total of 121,901,735,976; 38,320,126,486 and 48,698,321,829249. The challenge is to
extract from this amount what was allocated to financing green infrastructure.
Unlike the programming period 2007-2013, the new priority areas of the ERDF do not
explicitly mention environmental protection. Yet the new programme includes new
priorities where GI could play a role, namely climate change and sustainable urban
development.
Assumption: In the absence of further evidence, we will assume that the same
percentage of ERDF funds gets allocated to GI as in 2007-2013. The ESF’s priorities,
similar to the previous period, do not include hints of potential for GI investment, yet
the new programming period does mention that ESF investments should contribute to
a low carbon economy. In the absence of further specifications, we will assume the
ESF % accrued to GI remains the same. We will also assume nothing has changed for
the CF.
EAGF, EAFRD
The new program seems to set greater focus on competition and less on rural
development. This might be detrimental for interventions related to GI. The expected decrease of spending on activities related to the natural resources (11.3%)250 will be
taken into account.
249 http://ec.europa.eu/regional_policy/sources/docgener/evaluation/data/financial_execution_by_period_fund_country.xls 250 Stępień, S., & Mironescu, A. (2013). Budget Of The Eu For 2014-2020. Results Of The Negotiations In The Light Of The Polish Agriculture Interests. Romanian Economic Business Review, 8(4.1), 167-178.
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EMFF
It is not straightforward to assess whether the EMFF will involve more GI measures
than its predecessor, the EFF, so our assumption is that the percentage thereof
allocated to GI will remain the same.
Amounts and origin of GI funding in the baseline situation
The extrapolation to the new programming period shows that between 2014 and
2020, green infrastructure would receive EU finance amounting
approximately to €6,397 million by public EU funds through various funding
mechanisms, namely: the European Agricultural Fund for Rural Development (EAFRD);
LIFE+; the European Regional Development Fund (ERDF), the European Social Fund
(ESF) and the Cohesion Fund251; and the European Fisheries Fund (EFF)252. This is an
average of approximately €915 million per year.
Although in monetary terms the fund contributing most to GI by far appears to be the
agriculture fund EAFRD, less than 1% of its total budget (€418 billion) was allocated
into GI between 2014 and 2020. That accounted for €4,967 million (77% of the
total EU funded GI). In fact, proportionally speaking, LIFE is the biggest contributor to
GI implementation. For 2014-2020, funding from LIFE would amount to €1,248
million (19% of the total EU-funded GI), which means that 36% of the total LIFE
budget is allocated to activities that can be considered GI. Less than 1% of the total
EFF budget has been invested in activities that can be considered GI implementation,
accounting for 44 million (less than 1% of the total EU funded GI). A very small
percentage (0.04%) of all the ERDF, CF and ESF budgets have also funded GI in the
EU, amounting to €136 million (2% of the total EU funded GI).
Figure 21 Contribution of EU funds to GI (in €)
[Source: own elaboration based on gathered data]
251 These three funds present their project beneficiaries together, without specifying which amounts come from CF, ERDF and ESF. 252 For the period 2014-2020, the EFF is replaced by so-called European Marine and Fisheries Fund (EMFF)
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Figure 22 captures the distribution of GI funding across countries.
Figure 22 EU funds per country (2014-2020)253
[Source: own elaboration based on gathered data]
Types of GI funded under the baseline situation and identified gaps
Current funding is primarily allocated to finance the conservation of green areas
(5,010 million of all GI funding; 78% of all GI funding) and restoration of green
areas (78 million of all GI funding; 12%) (see Figures 23 and 24). By contrast,
connectivity issues, sustainable use green zones and green urban and peri-urban
areas are underfunded in the baseline situation, as these building blocks receive only
approximately 1%, 4% and 4% of all EU funds allocated to GI projects respectively.
Investments in greening urban and peri-urban areas are mostly spent on green roofs,
city parks, urban forestation and the like. Connectivity mostly funds fish passes and
animal corridors while there is no indication of financing having been provided to
projects dealing with other connectivity-related GI such as eco-ducts, green bridges,
areas along energy and transport networks. Against this backdrop, TEN-G could focus
on promoting projects that enhance natural and artificial connectivity, as this is an
underfunded area and could also contribute to reducing fragmentation.
253 EAFRD has not been included in the graph due to lack of information at the project - and therefore country – level. To estimate the amount of EAFRD funds allocated to GI, we have used aggregate figures from the Commission's annual financial reports, from which we extracted amounts from the categories we presumed to be related to GI activities.
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Figure 23 Funding per type of GI component (2014-2020)
[Source: own elaboration based on gathered data]
Figure 24 Annual funding levels per type of GI component
[Source: own elaboration based on gathered data]
LIFE captures a variety of elements across all realms of GI, especially financing
biodiversity conservation and restoration, but also a few sustainable use, urban and
connectivity-related projects. The projects falling under sustainable use of zones
regarded mainly sustainable management of water habitats and green areas.
Investments in urban and peri-urban areas involve green roofs, city parks, urban
forestation and the like. Projects under the last two categories are often aimed at
climate adaptation and mitigation. Connectivity projects under LIFE are wildlife /
ecological corridors. GI implementation is not the aim of the projects. Instead, the
implementation of GI is the result or the means though which projects that aim at
biodiversity conservation/restoration, greening of urban areas and increased liveability
are realised.
For the rest of the funds, a very small part of what is funded corresponds to GI. The
ERDF covers projects across various elements of GI, from conservation and restoration
to connectivity and urban interventions. It is also the fund in which GI cross-boundary
projects – involving various countries - are funded. The EAFRD on the other hand only
finances aspects of GI that concern expanding (e.g. afforestation) or restoring green
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areas. The EFF is an interesting case for the stark differences found between countries
in the number and the type of projects with a GI component that are implemented.
For instance, while GI projects related to the marine environment were not found in
Austria or Portugal, plenty of these projects were found for Denmark. Spain, which
benefits massively from these funds, has just implemented a handful of projects that
can be considered GI. Overall, the focus of the EFF is primarily on funding marine
ecosystems restoration and (re-)stablishing fish passes and artificial riffs.
5.2.5 Challenges and limitations of the baseline
Projects and their titles do not mention ‘green infrastructure’ despite
being/including GI. GI is very seldom explicitly mentioned and therefore identifying
these projects has been a time-consuming exercise. Out of the 500+ GI projects
identified, only three explicitly mention the term “green infrastructure”.
Identification of projects somewhat subjective. Stemming from the above, one
limitation of the method for the assessment of the baseline is the fact that the
identification of GI projects has been subjective to a certain extent. Whether
something has been considered GI or not has been the result of expert judgement.
When in doubt from the title of the project as to whether a project in question was GI
or not, we have resorted to the project’s website or internet-based research for
clarification.
Some GI projects are hybrid projects which include non GI features. Certain
projects identified are not 100% GI, but a combination of green and grey
infrastructure, or include non-GI implementation related activities such as information
campaigns, making of inventories or other side activities. Consequently, the baseline
might have been somewhat overestimated. Yet, we are confident the assessment has
been done as accurately and rigorously as possible.
Different level of detail for different funds. Another shortcoming is the fact that
the EARDF and EAGF funds have not been considered at project level, but a rougher
estimate has been made based on annual financial reports from which we have
extracted amounts from the categories we presumed GI activities fit, applying a percentage to it254. This might have led to an overestimation of the baseline. In fact,
any choices about whether to include a measure within CAP or not, and whether to
apply one percentage or other to it, leads to considerable differences in the results.
Information not available. Related to the above, in cases such as the EFF,
information is not available. Despite the transparency initiative of the EU requiring
Member States to publish the list of beneficiary projects and amounts assigned to
those, various countries have that information simply not available e.g. Latvia,
Slovenia, France and the UK. We contacted authorities and local representatives such
information, with no success.
Information only available in national language. Next to that, we encountered
that the EFF website and information of beneficiary projects therein is in the national
language of each country. Another hurdle is that each Member State who reports this
information, does that in a different way. In a similar vein, not all beneficiaries’ lists
254 From 2013 onwards the reform of the CAP requires Member States to make information public, about project funding beneficiaries.
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provided a description of the project255 and therefore some GI projects might have
gone unnoticed in our assessment.
GI projects are multi-purpose and therefore hard to categorise. Although we have classified GI projects as conservation projects, restoration projects, and so on256,
most of these are hybrid. Currently the baseline suggest 90% of the projects are
conservation projects. It is likely that some of these projects could have belong to
other categories too. Especially in many LIFE projects, we found that conservation and
restoration go generally hand-in-hand. Our decision to place such projects under one
or the other category has been determined by reading the projects’ description and
objectives and assessing where most stress is placed on. Also, a project to restore e.g.
salt marshes could be classified either under the ‘restoration’ category or under
‘sustainable use zones’ categorise to which salt marshes belong. In that case, we have
chosen for placing such under ‘restoration’. In a similar vein, connectivity projects
might in some cases be result of restoration activities and so on. Therefore, despite
we believe in the accuracy and rigorousness of the baseline presented, the
categorisation of where funds get allocated is partly illustrative.
Potential delays in funding / implementation not taken into account. All
funding has been reported for the year and/or period it has been reported for. Possible
delays have not been taken into account.
The baseline has been calculated as an extrapolation. The baseline has been
calculated extrapolating the results for the programming period 2007-2013 into the
current programming period 2014-2020. Obviously, there is no project level
information for this new programming period. The extrapolation has been done by
having a look at the main characteristics and funding priorities of each programming
period and reflecting on whether consequent changes in funds allocated to GI are
foreseeable. For most of the funds, there is no way to know how much (more or less)
GI will be funded and therefore high uncertainty exists regarding what will happen in
practice. It has been considered a ‘safe’ option to assume in most of the cases that
the percentages accrued to GI will remain the same.
5.3 Assessment of the costs and benefits of establishing a TEN-G
It should be noted that the narrative provided in this section of the Final Report is
supported with the developed excel calculation sheets and a technical methodological
report as annexes 18 and 19 respectively.
5.3.1 Purpose and scope
Purpose
The cost-benefit assessment focused on comparing the potential additional European
added value a TEN-G could theoretically deliver compared to the baseline scenario.
This involved comparing the benefits of the various GI components against their costs
to identify which offered the best ‘value for money’ if delivered on a European network
scale, and hence to prioritise where funding might be allocated under a TEN-G.
255 E.g. the information in the EFF beneficiaries’ lists in Ireland and Portugal is limited to the name of the beneficiary and the funding given, that is there is no mentioning of the projects’ name or description. 256 The decision to make each project belong to one category or another is based on the primary purpose of the project.
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Scope
The assessment of the economic, social and environmental benefits of a TEN-G has
been undertaken at a high level due to the nature of this first-phase exploratory
nature of the work, as well as the timescale and budget available for the analysis. The
components were assessed generically without being fixed to any particular location.
As a result, it was not possible to adjust the benefits or costs to relate to specific
factors that would be relevant were an assessment made of the implementation of GI
in a particular location. Of particular importance is the likely under-estimation of
benefits associated with GI located in urban areas as no population weighting can be
applied. Average (mean) values were used wherever possible to reflect variation
across the EU. Again, this reflects the high level of the assessment and the need to
keep the analysis at a level that is applicable to the EU as a whole, rather than using
information that may be specific to one or more Member States. Wherever possible,
for example, cost data have been used that reflect averages across a number of
Member States and benefits were taken on a per hectare value from sources that
reflect European or even global average values. Such data were not available for all
types of green infrastructure, however, so some specific values were used to fill data
gaps. The uncertainty introduced by this, and other steps within the assessment is
discussed in detail below.
GI components assessed
The assessment of TEN-G involved identifying the costs and benefits associated with
different GI components. The GI components covered by the assessment are set out
in Table 19 in the introductory section of Chapter 5.
GI Baseline as basis for comparison
Existing funds that have been allocated to each of the GI components have been
estimated using the projects that have been funded under LIFE+, the European
Regional Development Fund (ERDF), the European Social Fund (ESF), the European
Agricultural Guarantee Fund (EAGF), the European Agricultural Fund for Rural
Development (EAFRD), the European Marine and Fisheries Fund (EMFF) and the
Cohesion Fund. This information was then used in combination with identified data on
the costs of each GI component (in € per ha) to estimate the area of each component
delivered, and hence the ecosystem service benefits under the existing situation (the
current baseline).
The assessment then looked at whether a TEN-G would provide greater benefits than
those estimated under the baseline. Section 5.3.2 provides further details on the
approach to the assessment of costs and benefits, whilst Section 5.3.3 provides the
results including a comparison of the baseline situation to that envisaged under a TEN-
G.
5.3.2 Methodological approach in a nutshell
The assessment involved comparing the benefits of the GI components against their
costs to identify which offered the best ‘value for money’. This section outlines the
various aspects of the approach. A detailed technical description of the various
assessment steps is included in Annex 18.
Identification of the benefits of the GI components
To determine the benefits of the components, tasks included:
Identifying the increase in ecosystem services predicted to result from
implementation of the GI components; and
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Identifying monetary values for those services.
The benefits of the GI components were assessed using an ecosystem services
framework. This framework looked at the benefits that GI can provide to people
through provision of goods and services (provisioning services), through regulation
and control of environmental resources and risks (regulating services), and through
social benefits such as cultural, recreational and aesthetic services (cultural services).
Each GI component was assessed to identify the ecosystem services it would support.
This assessment was based on a review of the literature as well as the expert
judgement of our team.
Monetary values for each of the ecosystem services were taken from the TEEB (The
Economics of Ecosystems and Biodiversity) database. These monetary values do not
cover all of the ecosystem services, so not all of the benefits can be valued in
monetary terms. Those values that were identified have been evaluated during the
TEEB project, so are considered amongst the best available values to use. However,
there is uncertainty associated with assigning monetary values to ecosystem services.
Therefore, uncertainty ratings were assigned to each of the ecosystem services
considered relevant to each GI component. These uncertainty ratings were used in
the sensitivity analysis to enable the reliability of the results to be tested.
Identification of the costs of the GI components
The estimated costs of the GI components were based on costs of implementation
from previous projects. The reliability of the cost estimates, therefore, depends on
the number of cost estimates that could be used and the variability across those cost
estimates. Whilst many cost estimates were identified from internet research, these
were in a range of units and so could not necessarily be used for the assessment
(which required data in € per ha for consistency and comparability). To take account
of the resultant uncertainty in the data, each GI component was assigned an
uncertainty rating to reflect availability and variability, with this used in the sensitivity
analysis to assess the reliability of the findings.
Prioritisation of the components based on benefits and costs
The estimated monetary costs and benefits of the GI components were used to
prioritise where funding might be allocated. Those GI components with the highest
benefit-cost ratio (benefits divided by costs) were ranked highest so more funding was
allocated to those components that delivered a higher level of benefits for very €
spent. It is important to note that the same benefit value was used whichever GI
component delivered a particular ecosystem service. This was a necessary
simplification given the scale of the assessment (EU wide) and the lack of location
data (the funding baseline indicated which components were being implemented, but
not where these components were implemented). This meant that it was not possible
to determine whether a component was being delivered in an urban area, and so
might benefit a greater population, thus resulting in a higher benefit per ha value. A
more local level assessment with geographical/spatial data would be required to
highlight how delivery of an ecosystem service might differ dependent on where a
component was implemented. Such an assessment would be able to take factors such
as population density into account.
Prioritisation of the components based on qualitative benefits
The benefit-cost ratios estimated only included those ecosystem services that could be
valued in monetary terms. The GI components were also ranked in terms of the
qualitative (non-monetary) benefits that they could provide. This assessment was
linked to the number of ecosystem services that would be enhanced or increased from
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implementation of the components. Those GI components that would result in
enhancement of more of the ecosystem services were, therefore, ranked higher under
the qualitative assessment.
Prioritisation of the components according to social and environmental
criteria
As well as ranking on all ecosystem service benefits, the GI components were ranked
according to how they perform when the emphasis is placed on social or ‘green’
outcomes. The purpose of this approach is to explore if and how this might result in a
different set of GI components and, hence, potentially an alternative focus for future
investments.
The Juncker Commission priorities were used as the basis for assessing the priorities
for social criteria. Each of Juncker Commission priorities is linked to the qualitative
benefits that would be delivered by each of the components in terms of the extent to
which ecosystem services would be enhanced. In this way, those components that
would deliver the highest level of social priorities can be determined. This assumes
that the Juncker Commission objectives provide a good representation of the social
benefits. Some priorities, such as jobs, growth and investment, and internal market
are strongly linked to provisioning services. Energy Union and climate is more
associated with provisioning services such as ‘biomass-based energy sources’ but also
to regulating services such as ‘gaseous/air flows’. The priority objective on justice and
fundamental rights is linked with cultural services such as spiritual, symbolic and other
interactions with biota, ecosystems and land/seascapes. Some priority objectives
have limited links with the environment. This includes the digital single market and
migration (of people). Thus, account is taken of the likely relevance of the Juncker
priorities to social issues that have a possible bearing on the environment.
Environmental criteria were identified from the environmental pressures considered by
the International Union for Conservation of Nature (IUCN) in their European Red List257
and the EEA’s258 priorities for mitigating the impacts of weather and climate change
related hazards. These give the following areas as being of priority:
Pressure on Red Book Species (IUCN):
pollution;
modification of natural systems;
biological resource use;
development;
invasive and problematic species and genes;
human intrusion and disturbance;
climate change and severe weather; and
energy production/mining.
EEA (2015):
protection against landslides and avalanches;
protection against flooding;
protection against storm surges; and
257 IUCN published factsheets for each member state in 2013. Environmental pressures have been identified from these factsheets. Further information is available at: http://ec.europa.eu/environment/nature/conservation/species/redlist and http://www.iucnredlist.org/europe 258 EEA (2015): Exploring nature-based solutions, the role of green infrastructure in mitigating the impacts of weather and climate change related hazards
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global climate regulation.
The use of these existing priorities ensures that the assessment is relevant to other
initiatives and policy areas.
The ecosystem services that were thought to benefit each of the above social and
environmental priorities were identified. The assessment then highlighted the GI
components that would provide the most relevant services (i.e. benefits) to help meet
these priorities.
Assessing different levels of ambition for green infrastructure delivery
Different levels of ambition in terms of green infrastructure delivery were taken into
account through varying the funding intensity, with double the baseline funding and
ten times (x10) the baseline funding both considered (these are referred to as the
medium and high funding intensity scenarios).
The marginal benefits of an extra unit of funding were seen as unlikely to remain
constant if funding was continually allocated to a particular component. This issue
was dealt with through applying assumptions whereby the provision of benefits from a
particular component was decreased once delivery of the component surpassed a
threshold area. Different assumptions were used for each group of components. For
example, for protected areas, once the lower area threshold was reached, each
additional ha of the component was assumed to provide only 50% of the benefits. It
is acknowledged that the threshold areas and associated percentages are uncertain.
However, without such an approach, an increase in the funding available would simply
result in more funding being allocated to those components which had already
received funding. This would not represent good value for money since there would
be a point where the component area and habitat condition would not improve any
further, however much more funding was provided for it.
Uncertainties
As well as uncertainties within the values assigned to the monetary costs and benefits,
the ranking of the assessment highlighted other uncertainties that could affect the
order in which the GI components were ranked. These uncertainties include:
Whether a GI component is assigned an ecosystem service benefit (or not): the
process of assigning services drew on information from existing studies as well as
expert judgement, with a general presumption that a benefit would occur unless it
is clear that this is unlikely to be the case, e.g. wilderness zones are unlikely to
provide direct benefits259 to cultivated crops;
Whether a social or environmental priority is assumed to benefit from the
provision of a particular ecosystem service (or not). The ranking of the
components according to the social and environmental priorities took account of
the fact that some ecosystem services are likely to contribute towards the
priorities more than others. However, the assessment of these services was
subjective (different individuals may feel that different services will contribute
more to the priorities), thus changing the services seen as beneficial for the
different priorities could result in a different ranking of the GI components; and
259 Direct benefits are those that can be linked directly to the GI component, thus, wilderness zones would not result in cultivated crops being grown hence there is no direct benefit. There may be indirect benefits, e.g. due to populations of pollinators or native species that can help reduce pest populations on nearby farmland but these are not included as they would double count with benefits due to pollination or pest control.
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The decline in benefits per unit that was assumed to result where additional
funding was allocated to areas already in good/favourable condition. Assumptions
were developed for the various component groups (e.g. assumptions for protected
areas were based on the status levels used in condition reports (unfavourable
recovering, favourable, etc.)), since there is currently a lack of data on the extent
to which the ecosystem services are currently in favourable condition. Thus the
likely condition of ecosystem services and, hence the extent of benefits that could
be delivered by enhancing these services is based instead on the condition of
habitats. Different assumptions could result in a different allocation of funding.
5.3.3 Results
This section summarises the results of the cost-benefit assessment.
Overall results
Whilst the assessment process is high level and subject to a number
of uncertainties, the findings indicate that:
a TEN-G could provide more benefits than the current allocation of
funding to GI components.
Considering only the top five ranked components in the assessment, the benefit-cost
ratio (BCR) for TEN-G is more than double the BCR under the current funding
allocation.
Table 20 presents the top five and top ten ranked components that could
make up a TEN-G network, assuming the intention is to maximise the BCR (as
opposed to focusing on particular environmental or social priorities). It includes an
indication of the uncertainty associated with the costs and benefits of these
components, as well as the overall uncertainty for the BCRs. Whilst several of the
components identified have high levels of uncertainty associated with the benefits they
provide, many of the components included are designated sites, and thus would be
expected to lead to significant benefits. This suggests that the approach followed is
working, and is not providing anomalous results.
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Table 20: Top-ranked components when aim is to maximise the benefit-cost ratio
Top 5 ranked components Top 10 ranked components
Component Uncertainty
Component Uncertainty
Costs Benefits Costs Benefits
Natura 2000 sites Moderate
Very high Natura 2000 sites Moderate
Very high
Extensive agricultural landscapes
High High Extensive agricultural landscapes
High High
Regional and National parks
Moderate High Regional and National parks
Moderate High
Multi-functional sustainable managed agricultural landscapes
High
High Multi-functional sustainable managed agricultural landscapes
High
High
Wilderness zones High Very high Wilderness zones High Very high
High nature value farmland
Moderate
High
Metropolitan park systems
High Moderate-low
City reserves High Moderate-low
Ecological networks with cross-border areas
High High
Storm ponds and sustainable urban drainage systems
High Very-high
Overall BCR High Very high Overall BCR High Very high
Where the medium and high funding intensity scenarios are considered, the BCR still
remains above the baseline BCR. This suggests that even allowing for decreasing
marginal benefits where more than a threshold area of a particular component is
funded, a TEN-G could still result in more benefits per unit of cost invested than the
current (assumed) funding allocation.
Table 21 highlights the top five and top ten components to fund should green
infrastructure be focused on contributing towards social priorities. Again, the
components which are featuring are those which are generally already recognised for
their environmental value. Whilst urban GI components may provide particular
ecosystem services within a specific location (and thus be extremely valuable to the
surrounding population), they do not tend to provide as many different services as the
components listed in Table 21, thus they do not rank in the top ten within this
assessment. Had a more detailed, local level assessment been undertaken involving
location data, urban GI components may have been ranked more highly than they are
here due to the large populations likely to benefit from the services provided by
features such as green roofs, allotments and orchards, etc.
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Table 21: Top-ranked components when aim is to maximise the level of social benefits delivered
Top 5 ranked components Top 10 ranked components
Substantial share of structure-rich agricultural, forestry or natural landscapes
Substantial share of structure-rich agricultural, forestry or natural landscapes
Multi-functional sustainably managed agricultural
landscapes
Multi-functional sustainably managed agricultural
landscapes
Ecological networks with cross-border areas Ecological networks with cross-border areas
Regional and National Parks Regional and National Parks
High nature value farmland High nature value farmland
Restored landscape systems covering a substantial part of agricultural/forestry areas
Supra-regional corridors
Natura 2000 sites
Sustainable coastal and marine management zones
related to the respective sea basin
Restored areas which were before fragmented or degraded natural areas
Notes: Components have been ranked on the basis of all benefits provided, rather than just those which for which monetary values have been identified
Table 22 presents the top ranked components assuming components are
prioritised towards environmental goals. As would be expected, environmental
priorities are best met through focusing on GI components that relate to protected
areas and sustainable use zones.
Table 22: Top-ranked components when aim is to maximise the level of environmental benefits
delivered
Top 5 ranked components Top 10 ranked components
Wilderness zones Wilderness zones
Local nature reserve Local nature reserve
Natura 2000 sites (=3) Natura 2000 sites (=3)
Regional and National Parks (=3) Regional and National Parks (=3)
Ecological networks with cross-border areas Ecological networks with cross-border areas
Multi-use forests (such as watershed forests)
Protection forests (against avalanches, mudslides, stonefalls, forest fires) (=7)
Sustainable forest management (=7)
Natural buffers such as protection shorelines with
barrier beaches and salt marshes
Mountain range level (sustainable use zones)
Notes: Components have been ranked on the basis of all benefits provided, rather than just those which for which monetary values have been identified
Sensitivity analysis
Sensitivity analysis was used to indicate how the rank order of the components might
change should the unit costs and benefits associated with each component alter. Unit
costs were changed according to the level of uncertainty allocated to a particular cost
or benefit, with uncertainty ranging from low, where values were increased or
decreased by 10%, to very high, where values were increased or decreased by 75%.
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Three sensitivity tests were carried out:
1. Costs and benefits both increased by the percentage indicated by their
uncertainty;
2. Costs and benefits both decreased by the percentage indicated by their
uncertainty; and
3. Costs increased and benefits decreased by the percentage indicated by their
uncertainty.
Even under the worst case scenario, where costs were increased and benefits
decreased, sensitivity testing suggested little change in the rank order of the
components. This is explained by the fact that the top ranking components (e.g.
Natura 2000 sites) have such high benefit cost ratios that considerable changes are
required in costs and benefits before other components take their place in the ranking.
However, if components lower down the ranking list are considered, then the
sensitivity testing does result in significant changes. For example, the component
‘local nature reserve’ moves up nine places when costs are increased and benefits
decreased (sensitivity test 3).
Whilst these sensitivity tests appear to indicate that the results are relatively robust, it
should be acknowledged that benefit values have not been identified for all the
ecosystem services. The sensitivity tests are only able to analyse the impacts on the
results of changing the identified costs and benefits. Where a component provides
several services for which no benefits value has been identified, that component might
actually be lower down the ranking that it would be, were all services monetised.
However, this point is countered by the fact that the assessments focusing on the
social and environmental priorities are based on the qualitative benefits, so all benefits
provided are taken into account. Given that the outcomes from these assessments are
relatively similar to those from the ‘maximise BCR’ assessment, it is assumed that
there are few (if any) key services that are missing a monetary value and would
significantly impact the overall results.
5.3.4 Conclusions and discussion
This section provides a broader reflection of what can be learned from the cost-benefit
assessment findings.
Overall direction of the outcomes
Taking account of the uncertainties associated with the costs and benefits, the
allocation of services to components and the extent to which benefits received per unit
might change with the area funded, a TEN-G network has the potential to provide
greater benefits per € invested than the current GI policy implementation and funding
allocation (as described under the baseline scenario). However, consideration should
be given to the location of existing GI components, as well as their condition, when
determining where and how to invest in an EU wide GI network.
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Clearly, directing money towards components already known for their high
environmental value (e.g. Natura 2000 sites) can result in benefits. However, if a
wider applicability is used for a TEN-G network based on the components that were
ranked in the top ten at least twice in this assessment (based on benefit-cost ratio,
level of qualitative benefits, based on social priorities or based on environmental
priorities) alongside those that could generate sufficient benefits to attract private
funding would include260:
Natura 2000 sites
Regional and National parks
Multi-functional sustainably managed agricultural landscapes
Wilderness zones
High nature value farmland
Ecological networks with cross-border areas
Local nature reserve
Sustainable forest management
Multi-use forests (such as watershed forests)
Water protection areas
Restored landscape systems covering a substantial part of agricultural/forestry
areas;
Allotments and orchards
Storm ponds and sustainable urban drainage
City reserves
Metropolitan park systems
Wildlife strips
The above list of potential priority components for a TEN-G incorporates a range of
different types of components, thus would be suitable for implementation in a variety
of areas across the EU. However, it should be acknowledged that the level of benefit
resulting from each component may vary dependent on factors such as the size of the
local population (in particular, in densely populated urban areas). In terms of funding
and targeting GI initiatives as part of a TEN-G, the location of any existing GI
components is also likely to affect the benefits that could result from newer
components.
In addition, once a threshold area of a particular component is reached, further
investment in that particular component may result in fewer benefits per € of input.
This needs to be borne in mind when considering how best to share costs and magnify
the benefits of GI at the EU level. Failure to take this into account could lead to
certain areas benefiting at the expense of others (for example, if additional investment
continues to be made in a component once it has reached good status).
Challenges relating to the quality and quantity of available data
The key challenge for this assessment is the quality and quantity of available data on
costs and benefits. Where monetary values are available in the desired format (€ per
ha), they have been applied. However, there are many services for which benefit
260 The following components reached the Top10 list due to their suitability for private funding: Water protection areas; Restored landscape systems covering a substantial part of agricultural/forestry areas; Allotments and orchards; Storm ponds and sustainable urban drainage; City reserves; Metropolitan park systems; Wildlife strips. The following components could also be included in the Top10 list if only focusing on one of the prioritisations: Extensive agricultural landscapes; Functional riparian systems; Transboundary landscape features on river basin; Substantial share of structure-rich agricultural, forestry or natural landscapes; Supra-regional corridors; Sustainable coastal and marine management zones related to the respective sea basin; Restored areas which were before fragmented or degraded natural areas; Protection forests (against avalanches, mudslides, stonefalls, forest fires); Natural buffers such as protection shorelines with barrier beaches and salt marshes; Mountain range level (sustainable use zones).
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figures have not been determined (perhaps because data are available, but they are in
a different format and cannot be converted). This obviously affects the ranking of the
components providing these non-monetised services when identifying those
components providing the greatest benefits to costs. Similarities between the
components ranked in the top ten for the ‘maximise BCR’ assessment (based on costs
and benefits) and the environmental and social priorities assessments (based on
qualitative benefits) suggest that the results are relatively robust, but having a full set
of benefits and costs for all components would make the assessment fairer.
The allocation of services to the various components is another key issue which
requires consideration. This has been carried out based on available evidence and
expert judgement. However, the TEN-G is being assessed at the EU level, not the
individual member state or even ecosystem level. A different level of service may be
provided by the same component dependent on where it is implemented (e.g. if it is
close to a large urban based population, or in a sparsely populated rural area). A
more detailed local level analysis is required to tease out such effects and their
impacts for the analysis.
Data and knowledge gaps
There are several areas where data and knowledge gaps need to be addressed to
enhance any future assessment. These include:
The availability of cost values in the necessary format. Whilst many studies have
considered the costs of implementing GI measures, these costs are presented in a
range of units. For example, costs were identified for € per structure or linear
metre. These costs could not be used within this assessment since the monetary
values needed to be in €/ha to enable all GI components to be treated equally;
The availability of benefit values for each ecosystem service. Where values were
not available, the services were assessed qualitatively. However, this did mean
that they were omitted from the ‘maximise BCR’ assessment. Whilst the results of
this assessment are not unexpected in terms of the components coming out at
the top, it should be borne in mind that the assessment is not based on a full set
of data due to availability issues;
The ecosystem service benefits provided by each component in terms of which
services a component is expected to provide, and which it might provide
dependent on certain conditions being fulfilled (e.g. bio-geographical location,
access by a large population);
There is a need for a better understanding of how the benefits provided by the
various components may change as more and more funding is allocated to a
particular component. As the condition of a component improves, it is assumed
that the marginal benefits per unit of investment decline. However, there is little
evidence on the point at which this might occur; and
The variability in terms of provision of benefits according to where a component is
sited. Components in urban areas might attract higher benefits values for some
services (e.g. cultural services) than those in more sparsely populated rural
areas. This assessment has been undertaken at the EU level, and has not been
able to use locational data. However, further work may need to consider what
components are in existence already, and where within the EU these are located.
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5.4 Policy implications
A TEN-G provides the opportunity to consider, plan and prioritise green infrastructure
at the EU level rather than just at the individual Member State level. Operating at
such a scale enables the network to focus on those components that will provide the
most benefits for the money invested, since the area of land available for
implementation of such components is far greater than that available to one Member
State. Therefore, at a theoretical level, as indicated by this assessment, the overall
benefits of setting up a TEN-G would outweigh the costs, since the network could
focus on implementing those components that provide the greatest environmental,
societal and economic benefits.
At a practical level, considerations other than space would need to be taken into
account to ensure that the TEN-G was comprehensive and inclusive, and shared
benefits across the EU28. However, given the benefit-cost ratios identified in this
study, such a network could still be far more cost beneficial than the current allocation
of funding across the various GI components. Careful selection of components to
provide a range of services according to the requirements of both the local area (e.g.
for certain cultural services) and the wider EU (e.g. for regulating services) would
ensure that any investment resulted in considerable benefits. Factors to take into
account in the development of TEN-G would include the existing spread of GI
components across the EU (to avoid imbalances between Member States), the
condition of existing components, and the location of settlements and their current
access to GI components (this affects the value of some of the benefits provided e.g.
cultural services).
Furthermore, the location of components in combination with the types of benefits
they are expected to provide is likely to affect the level of private investment the
components may attract. Components that provide services that are marketable (e.g.
crops, livestock) are likely to attract private investment, whereas those which provide
universal but non-exclusive services (e.g. regulating type services related to air
quality, climate regulation) may be more reliant on public investment. These issues all
require consideration when designing the network to ensure that greatest benefits
possible can be achieved for the money invested.
All these aspects of how to maximise benefits across GI components will need to be
considered – in combination with the lessons that can be drawn from reviewing the
design options and set-up of existing trans-European networks. Together, the analysis
carried out in Task 5 delivered valuable insights and estimates as part of DG
Environment’s exploratory work on the potential implementation of a TEN-G. Results
should be able to contribute to answering the question of whether or not it is ‘worth it’
to build a TEN-G, as compared to continuing the current policy framework.
Supporting the Implementation of Green Infrastructure
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Conclusions This service contract sought to support the implementation of the EU Green
Infrastructure Strategy through a range of actions, including:
the development and dissemination of GI information (through fact sheets and
workshops) targeting Member States with little GI information available, sectors
with further GI uptake potential, and topic areas offering interesting linkages to
other policy areas;
capacity-building and ‘train the trainers’ activities, including the design and
implementation of two workshop modules (on GI and wetland restoration and on
better linking GI with existing operational programmes) and producing material
for a Massive Open Online Course (MOOC) on GI;
evaluating the current visibility and content of GI information on a number of
digital platforms and proposing means of improving the capacity of such platforms
to deliver GI information;
assessing how technical standards in a range of relevant sectors could help
increase the deployment of GI and formulating recommendations to this effect;
assessing the costs and benefits of implementing a Trans-European GI network
(TEN-G).
Below, we outline the key conclusions emerging from each task.
Task 1
The development of 20 factsheets under this task generated additional information
regarding the status of implementation, good practice examples, and the level of
awareness related to GI for the selected countries, sectors and topics. However, the
process of developing the factsheets also highlighted some challenges regarding the
availability and accessibility of GI information for specific countries, sectors and/or
topics. The delivered factsheets will serve as a GI promotional tool across countries,
sectors and various stakeholder groups beyond the timeframe of this project.
The sectoral workshops were appreciated by participants and demonstrated the
usefulness of such events. All three workshops have shown that there is an urgent
need to further raise awareness and build capacity on the linkages between GI and
other sectors. While some steps have been taken, further efforts are needed to
present good examples and provide training on how to integrate GI in other policy
areas, in particular by developing decision-support tools for those stakeholders that
are faced with taking decisions on infrastructure solutions (e.g. grey versus green
options). Another major barrier to the deployment of GI that became evident during
the workshops is the insufficient understanding amongst stakeholders of the way
natural ecosystems function, which often results in an underused potential for GI
development. Better use of integrated spatial planning processes, improved capacity
of decision-makers and better institutional cooperation are important elements to
address this challenge.
Task 2
As part of Task 2, we have reviewed existing GI-related training programmes across
the EU-28. The aim of this quick-scan was to identify a short-list of activities which are
particularly relevant to enhancing capacities for GI. This scanning exercise indicated
Supporting the Implementation of Green Infrastructure
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that there is a need for greater availability of tailored GI information sessions that can
teach decision-makers the practical application of ‘green options’ as an alternative to
traditional grey infrastructure solutions. To this end, materials for two ‘train the
trainers’ workshops were developed and test-run as a parallel session linked to an
existing event.
In addition to these targeted training sessions, it was agreed with the client that a
broader GI course available for a wider public throughout Europe could help those
interested in the topic gain the necessary knowledge to then teach or inform others.
To this end, we developed the lecture scripts with content for a freely accessible
MOOC that could eventually be provided by a university, NGO or other European
institution via commonly known platforms, such as COURSERA or edX.
Task 3
Task 3 evaluated the current visibility of GI information on a range of digital platforms
and considered means of improving the content and accessibility of digital information
on GI.
For platforms hosted by the European Commission, the evaluation shows that GI
information is relatively dispersed across the different platforms and not presented in
a coherent manner. The reviewed platforms contain a large amount of information
that is highly relevant to GI, but not defined and labelled as such. With respect to the
available policy information, GI is only visible on a limited number of EC-related
websites and platforms. Significant progress can, therefore, be made by having the
concept, its relevance for the sector and a link to the GI section on BISE integrated
across the websites of relevant policy sectors. Among the stakeholder platforms
evaluated, only those of CEEweb, FACE and WBCSD contain clear and inspiring
information on GI. On several other platforms, GI is mentioned, but very little
information could be retrieved. Certain platforms containing related information (e.g.
biodiversity, ecosystem services, nature-based solutions) make a link to GI in some
documents; however, the platforms do not include sections dedicated to GI
specifically. Altogether, the visibility of GI on relevant IT platforms and websites can
be considered poor. Improving it can make a significant contribution to distributing GI
information to the public and various end-users.
Eight platforms were explored in more depth, focusing on the end-users and their
expectations, the type of GI information available and lacking, whether there is
potential to connect across platforms, and how to improve the visibility of GI. A more
detailed analysis was conducted and concrete recommendations formulated for three
major platforms: BISE, NWRM and Climate-ADAPT.
With respect to BISE, although not labelled as such, most information of the BISE
platform is highly relevant from a GI perspective. However, the GI relevant sections
need to be made more visible, e.g. by labelling GI-related sub-sections as such. The
coherence and user-friendliness of the available information can also be improved.
Further interlinkages between the various GI-related sections could be provided, in
order to create a more holistic picture and increase the usefulness of BISE for its end-
users. The GI information available should be extended to encompass policy aspects
and provide greater depth with regard to the different GI options and measures
mentioned. The GI library hosted by BISE has the potential to be further developed
into a rich source of GI information, but needs to be made more visible and accessible.
Supporting the Implementation of Green Infrastructure
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All information on the NWRM (Natural Water Retention Measures) website is highly
relevant to GI since NWRM are an example of GI solutions. However, the website
could be improved by better integrating the GI concept and making the connections
between NWRM and GI explicit. Further linkages should be made to other GI platforms
and sources of information.
GI is among the most widely applicable, economically viable and effective tools to
support climate change adaptation. The Climate-ADAPT platform contains a few
references to GI, but not sufficient to reflect its significance. The few GI references are
scattered across the platform, making the GI-relevant information on the platform
difficult to locate by its potential users. The website contains highly relevant
knowledge which could provide useful information and guidance on sectors, measures,
and processes relevant for GI, and in particular GI measures supporting climate
adaptation. However, the GI relevance of this information needs to be made more
explicit. It would also be important to increase the interlinkages across the platform in
order to provide a more complete overview of GI and to help users locate the
information. It would be beneficial to create a separate section on GI and adaptation
which could present all these aspects in a coherent and visible way. These
improvements would be necessary to establish links with other platforms, such as
BISE.
In the short-term, BISE should be developed into a GI information hub, while
considering that it should not become the only access point for GI knowledge.
Therefore, it is important to decide which GI information should be made available
through BISE, and which through other platforms (such as NWRM or Climate-ADAPT).
It should be ensured that GI information presented through other platforms is also
linked to BISE, such that it can also be reached by end-users accessing through BISE.
In the mid-term, it would be desirable for GI information to be made available through
the different websites or platforms linked to specific policy sectors or stakeholder
groups. It will be important to consider end-users’ needs when deciding where to
disclose which GI information. Another challenge is to connect the different sources
available on the various platforms. Rather than having to search for GI information on
separate platforms, it may be beneficial to make GI information available through a
single search or from a single page with convenient links to platforms where other
information is available. To improve user access to GI information, a search function in
combination with a single repository where all GI related information is centralized
would be the most effective solution. However, the feasibility of this option is low, as it
is very unlikely that all platforms involved would be willing to share all information in
an agreed manner. A longer-term recommendation to address this issue is to make
use of the potential of machine to machine communication, for example through the
use of "Structured Data Markup" or Web APIs.
Task 4
Task 4 examined the extent to which GI is currently covered in the technical standards
of nine sectors (finances, buildings, water, transport, public health, industry, climate,
rural abandonment and energy) and assessed the need for (further) harmonising,
adapting or developing GI-related standards. A series of sector-specific fact sheet and
cross-sectoral recommendations were developed.
The key findings for each of the nine sectors are:
Financial sector: Whilst direct lending for biodiversity projects by financial
institutions accounts for a limited proportion of financial markets, retail and
Supporting the Implementation of Green Infrastructure
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investment banks as well as institutional lenders are increasingly applying
sustainable investment criteria to their loans that incorporate impacts and
dependencies on biodiversity and ecosystem services. However, the focus is
mainly on conservation and restoration of biodiversity values affected by project
developments, rather than actively promoting the deployment of GI as part of
project developments. Even the substantial benefits of GI in the field of climate
change adaptation (such as flood risk reduction) are largely undervalued by
financial and insurance companies. As a consequence, there is substantial room
for improvement, starting with increased efforts in awareness raising, in particular
about the long-term financial benefits of GI. Other opportunities are the uptake of
GI in performance standards applied by the sector.
Building sector: There is a plethora of sustainability standards in the buildings
sector across Europe with varying levels of requirement. Few are known to be
legally required but they can often be mandated at country, region, city or local
level. Building sustainability standards focus primarily on materials and energy
performance. Where biodiversity requirements exist, they are often not
mandatory, carry little weight and do not promote high levels of biodiversity.
Where GI is integrated into buildings, it is often limited to green roofs, with little
focus on other elements of the building or surrounding area. Developments that
have taken place in the context of green roofs may provide inspiration for broader
inclusion of GI in the building process.
Water sector: In the water sector, procedural standards for sustainable water
management in Europe are available through the Water Framework Directive. In
the private sector there is a growing awareness of proactive investment in
sustainable water management in the catchment in which companies operate.
Although GI is not always explicitly mentioned, the application of GI fits well in
the ecosystem and catchment-based approaches. As a way forward for the
implementation of GI, it is important to incorporate ‘green’, ‘grey’, and hybrid
solutions in the initial assessments of options in such a way that actors can
compare and make the best choice for their situation. At the moment, criteria are
often established for evaluating the performance of ‘grey’ options, but not of GI or
for comparing across ‘grey’ and ‘green’ options. This poses a barrier to the wider
implementation of green options.
Transport sector: There is a substantial amount of guidance and good practice
on how to address fragmentation and barrier effects of transport infrastructure by
means of, e.g., overpasses or fauna tunnels, which in some cases are supported
by GI measures. Also at a landscape level, GI offering improved habitat
connectivity is often applied as part of wildlife and landscape management, and
increasingly incorporated into regional spatial planning. However, guidance on
how to reconcile transport networks with ecological networks at a regional scale is
very scarce. The same goes for guidance on how to optimize the ecosystem
services provided by GI to mitigate the impacts of transport infrastructure on
biodiversity.
Public health sector: With the exception of accessibility standards that
recommend the availability of GI for citizens, the standards, guidelines and
protocols of the public health sector are outside the scope of GI. However, there
is a growing body of literature linking GI to human health and wellbeing, but the
underlying mechanisms are poorly understood and the knowledge tends to remain
in the green sector, not penetrating the health sector. Exceptions include some
SMEs and bottom-up local initiatives bridging the gap between the green sector
and the health sector. There is a large potential for GI standards for the health
sector, but before standardization can take place, the evidence base needs to be
Supporting the Implementation of Green Infrastructure
May 2016 201
improved, and the results must be dissipated within the health sector rather than
only in the green sector.
Industry sector: The industry sector is very familiar with sustainability
standards. Although biodiversity, as part of sustainability, has long been a rather
neglected issue, the recent increase in specific biodiversity guidance for industry
reflects a growing interest in the field of ‘business and biodiversity’. However,
when zooming in on the topic of GI within this growing amount of biodiversity
standards, it is clear that there is room for improvement. Particular issues which
deserve more attention are the costs and benefits of GI in an industrial context,
as well as guidance on how to implement GI.
Climate sector: Many examples of tools, guidelines and best practices already
exist on the application of GI, or nature-based solutions, in the context of climate
change adaptation. Performance standards, which are common practice in, e.g.,
the building world, are not a useful way forward in the climate adaptation sector.
The reason for this is that the local situation is generally too specific. The multi-
functionality of GI is a benefit, but at the same time makes planning and
implementation of GI very difficult. Integrating a GI framework into
Environmental Impact Assessments might be a way forward, as this would
guarantee that the potential of GI in landscape planning is considered.
Rural abandonment: GI can offer solutions for both the prevention of farmland
abandonment and for minimizing negative impacts on already-abandoned
farmland. There are no specific GI standards in the context of rural abandonment.
An indirect way to stimulate GI in rural abandonment areas is through the
Common Agricultural Policy (CAP) funding scheme or European Structural Funds.
Energy sector: Possibilities for developing GI in this sector are quite diverse and
rather specific for each type of energy infrastructure. The energy sector is under
full development and is characterized by increasing investments in renewable
energy, as well as in electricity transmission infrastructure in the EU. At the same
time, existing energy infrastructure is being revitalized. The energy sector might
benefit from investments in GI for various reasons, ranging from reducing risks
(operational, reputational) to grasping opportunities (cost reduction,
reputational), depending on the type of investments. Due to the variety of energy
infrastructure, generic GI standards for the energy sector are not available, but a
number of specific standards exist.
The study also formulated cross-sectoral recommendations in relation to four aspects:
Integrated spatial planning: Several sectors (such as climate adaptation,
water, land abandonment and infrastructure) have indicated that the
implementation of GI would benefit from integrated spatial planning early in the
planning process. Moreover, it has been increasingly recognized that it is
necessary to work at the landscape level to ensure that sectors can capture the
benefits of GI and to maintain biodiversity and ecosystem services. A landscape
approach can contribute to bringing together sectoral economic development
plans and national action plans on biodiversity conservation, water management
and climate change.
Green procurement: Public authorities are major consumers. By using their
purchasing power to choose environmentally friendly goods, services and works,
they can make an important contribution to sustainable consumption and
production. Therefore, the way GI is included in Green Public Procurement (GPP)
will have a major impact on how GI will be considered in activities and
businesses. GPP will therefore be key to ensuring GI procurement. It may be
necessary to develop and establish a GI Public Procurement (GIPP) to include in
Supporting the Implementation of Green Infrastructure
May 2016 202
public tenders the use of GI as innovative solutions presenting a real alternative
to traditional grey infrastructure.
Finding the appropriate standard: There is no obvious way of understanding
which standards are most suitable to meet specific needs. Therefore, users
require assistance in finding the ‘needle in the haystack’ standard that matches
their needs. A way forward would be to explore ways of facilitating the search for
and access to appropriate standards. Sectorial organisations could play a role in
this respect, by assisting their members in the search for appropriate standards
and providing guidance on what can be achieved with which standard. Standards-
making bodies could also be involved. Possibilities could be explored for a
collaborative interactive database with a hierarchical tree which facilitates the
search for appropriate standards and provides insight into what can be achieved
with shortlisted standards.
Harmonization across infrastructure sectors: Each of the infrastructure
sectors (e.g. buildings, transport, energy, water) have their own standards
regarding performance, procedure and methodology. In the past, each of these
sectors mainly operated in isolation from the other sectors, but integrated
approaches have become more common in recent years. This may be seen as an
opportunity for improving the way GI is included in standards. Indeed, there is
potential for collaborative action and harmonization across sectors as regards the
inclusion of GI in standards.
Task 5
This task included all the exploratory work carried out with regards to the potential
introduction of a TEN-G.
The review and analysis included the consideration of lessons learnt from existing
trans-European networks in terms of informing the design options and set-up of a
TEN-G in terms of governance structures, eligibility criteria, etc. The research showed
that while some of the experiences and feedback could certainly be considered for the
various design options, a more detailed analysis tailored to the much broader GI
objectives (as compared to rather focused energy and transport objectives) will need
to be carried out.
The baseline building exercise has shown the data limitations and access to
information when working with GI. While the baseline has to be seen with these
limitations in mind, it still offers a first consolidated picture of what the current EU-
level spending looks like for GI.
Similarly, while restricted by certain limitations, the first-phase cost-benefit
assessment of the potential environmental, social and economic advantages of
introducing a TEN-G versus continuing the status quo has generated food for further
thought and discussion on the matter. In the next follow-up steps it will be important
to start looking in more detail into the possible design options including potential
locations where components could be implemented, realistic ambition levels in terms
of funding for TEN-G, and chosen priority components for a TEN-G that could be taken
forward by DG Environment.
Supporting the Implementation of Green Infrastructure
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Annexes
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COMISIA EUROPEANĂ
Bruxelles, 6.5.2013 COM(2013) 249 final
COMUNICARE A COMISIEI CĂTRE PARLAMENTUL EUROPEAN, CONSILIU, COMITETUL ECONOMIC ȘI SOCIAL EUROPEAN ȘI COMITETUL
REGIUNILOR
Infrastructurile ecologice — Valorificarea capitalului natural al Europei
{SWD(2013) 155 final}
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COMUNICARE A COMISIEI CĂTRE PARLAMENTUL EUROPEAN, CONSILIU, COMITETUL ECONOMIC ȘI SOCIAL EUROPEAN ȘI COMITETUL
REGIUNILOR
Infrastructurile ecologice — Valorificarea capitalului natural al Europei
1.1. Context Societatea umană depinde de avantajele oferite de natură, cum ar fi alimentele, materialele, apa curată, aerul curat, reglarea climei, prevenirea inundațiilor, polenizarea și activitățile recreative1. Cu toate acestea, multe dintre aceste avantaje, denumite deseori „servicii ecosistemice”, sunt folosite ca și cum disponibilitatea lor ar fi practic nelimitată și sunt tratate ca mărfuri gratuite, valoarea lor reală nefiind pe deplin apreciată. Din această cauză, atunci când sunt confruntate cu probleme precum prevenirea inundațiilor, autoritățile publice pot alege soluția construirii de infrastructuri — așa-numitele „infrastructuri gri” — în locul unor soluții naturale. Astfel, în Europa continuăm să ne degradăm capitalul natural, punând în pericol sustenabilitatea noastră pe termen lung și subminându-ne reziliența la șocurile de mediu. După cum se menționează în Foaia de parcurs privind eficiența utilizării resurselor2, incapacitatea de a ne proteja capitalul natural și de a da o valoare corespunzătoare serviciilor ecosistemice va trebui abordată în cadrul eforturilor de realizare a unei creșteri inteligente, durabile și incluzive, prioritate a strategiei Europa 2020 a UE3. Foaia de parcurs identifică investițiile în infrastructurile ecologice ca fiind un pas important în direcția protejării capitalului natural. Strategia UE în domeniul biodiversității pentru 20204 include angajamentul Comisiei de a elabora o strategie privind infrastructurile ecologice5. După cum se menționează în Foaia de parcurs privind eficiența utilizării resurselor, Comisia va elabora o comunicare privind infrastructurile ecologice. Prezentul document este răspunsul Comisiei la respectivul angajament6, el prezentând modul în care măsurile luate la nivelul UE pot da valoare adăugată inițiativelor locale aflate în curs de desfășurare la ora actuală.
1.2. Ce sunt infrastructurile ecologice? Infrastructurile ecologice sunt un instrument testat cu succes, care oferă avantaje ecologice, economice și sociale bazate pe soluții naturale. Ele ne ajută să înțelegem valoarea avantajelor oferite de natură societății umane și să mobilizăm investiții pentru a le susține și a le consolida. De asemenea, ele ne ajută să evităm dependența de infrastructuri cu costuri de construcție ridicate, atunci când, așa cum se întâmplă deseori, natura poate oferi soluții mai ieftine și mai durabile. Multe dintre aceste infrastructuri creează oportunități de angajare la
1 COM(2012) 710 final, propunere de Decizie a Parlamentului European și a Consiliului privind un
program general de acțiune pentru mediu al UE până în 2020 „O viață bună, în limitele planetei noastre”.
2 COM(2011) 571 final, JO C 37, 10.2.2012. 3 COM(2010) 2020 final, JO C 88, 19.3.2011. 4 COM(2011) 244 final, JO C 264, 8.9.2011. 5 În concluziile sale cu privire la Strategia UE privind biodiversitatea, Consiliul Mediu (6.11) „subliniază
importanța infrastructurilor ecologice și din punctul de vedere al contribuției acestora la mai buna integrare a aspectelor legate de biodiversitate în alte politici ale UE; și salută angajamentul Comisiei de a elabora o Strategie a infrastructurilor ecologice până în 2012”. Parlamentul European (5.12) „îndeamnă cu tărie Comisia să adopte o Strategie specifică a infrastructurilor ecologice până cel târziu în 2012, având drept obiectiv principal protejarea biodiversității”.
6 Documentul de lucru al serviciilor Comisiei adoptat concomitent cu această comunicare [SWD (2013) 155 final] oferă informații tehnice suplimentare detaliate cu privire la infrastructurile ecologice.
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nivel local. Infrastructurile ecologice se bazează pe principiul integrării conștiente a protejării și consolidării naturii și a proceselor naturale, pe de o parte și a numeroaselor avantaje pe care natura le oferă societății umane, pe de altă parte, în amenajarea și dezvoltarea teritoriului. În comparație cu infrastructura gri, care nu vizează decât un singur obiectiv, infrastructurile ecologice prezintă o serie de avantaje. Ele nu reprezintă o piedică în calea dezvoltării teritoriale, ci promovează soluții naturale, atunci când acestea reprezintă cea mai bună opțiune. Uneori, acestea pot oferi o alternativă, sau pot veni în completarea soluțiilor „gri” clasice.
Există o mulțime de definiții ale infrastructurilor ecologice7. De aceea, tratarea tuturor aspectelor în câteva rânduri se dovedește dificilă. În sensul prezentei comunicări, va fi utilizată totuși definiția prezentată în cele ce urmează.
Infrastructură ecologică: o rețea planificată strategic, alcătuită din zone naturale și seminaturale, precum și din alte elemente de mediu, care este concepută și gestionată pentru a oferi o gamă largă de servicii ecosistemice. Ea integrează spații verzi (sau acvatice, în cazul ecosistemelor de acest tip) și alte elemente fizice ale zonelor terestre (inclusiv de coastă) și ale celor marine. Pe uscat, infrastructurile ecologice sunt prezente atât în mediul rural, cât și în cel urban.
2. 2. CONTRIBUțIA INFRASTRUCTURILOR ECOLOGICE LA POLITICILE UE
2.1. Introducere Infrastructurile ecologice pot contribui în mod semnificativ la implementarea cu eficacitate a tuturor politicilor, atunci când unele dintre obiectivele urmărite (sau chiar totalitatea acestora) pot fi atinse integral sau parțial prin soluții bazate pe natură. Investițiile în infrastructurile ecologice au de obicei un randament ridicat, iar evaluările globale ale proiectelor de restaurare arată, în general, un raport costuri/beneficii situat între 3 și 758.
2.2. Politica regională Propunerile Comisiei referitoare la Fondul de coeziune9 și la Fondul european de dezvoltare regională (FEDER)10 identifică în mod specific infrastructurile ecologice drept una dintre prioritățile investiționale. Este recunoscut faptul că infrastructurile ecologice contribuie la politica regională și la creșterea sustenabilă în Europa11 și că (ele) facilitează creșterea inteligentă și sustenabilă printr-o specializare inteligentă12.
7 Infrastructurile ecologice și coeziunea teritorială. Agenția Europeană de Mediu (2011) Raportul tehnic
nr. 18/2011. A se vedea, de asemenea, http://ec.europa.eu/environment/nature/ecosystems/docs/Green_Infrastructure.pdf
8 Nellemann, C., Corcoran, E. (eds) 2010. Dead Planet, Living Planet — Biodiversity and ecosystem restoration for sustainable development. A rapid response Assessment. UNEP, GRID-Arendal.
9 COM(2011) 612 final/2. 10 COM(2011) 614 final. 11 COM (2011) 17 final, „Contribuția politicii regionale la creșterea durabilă în Europa 2020”. Document
de lucru al serviciilor Comisiei, SEC(2011) 92 final. 12 Connecting smart and sustainable growth through smart specialisation. Comisia Europeană, 2012.
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Caseta 1: Patrimoniul natural și cel cultural: componente ale capitalului teritorial și ale identității UE. Valorile ecologice, calitatea mediului și patrimoniul cultural sunt esențiale pentru bunăstare și pentru perspectivele economice. Este recunoscut faptul că exploatarea excesivă a acestor resurse naturale reprezintă o amenințare la adresa dezvoltării teritoriale. Activitățile desfășurate în armonie cu natura și cu peisajul local care își propun să ofere bunuri și servicii esențiale prin intermediul proiectelor de infrastructuri ecologice ce utilizează o abordare de teren sunt rentabile și conservă caracteristicile fizice și identitatea regională13.
Soluțiile bazate pe infrastructurile ecologice sunt deosebit de importante în mediul urban, care găzduiește peste 60 % din populația UE14. Elementele infrastructurilor ecologice prezente în orașe reprezintă avantaje pentru sănătate, cum ar fi aerul curat și o calitate mai bună a apei. Ecosistemele sănătoase reduc de asemenea răspândirea maladiilor cu transmitere prin vectori. Implementarea unor elemente ale infrastructurilor ecologice în zonele urbane creează un simț al comunității mai accentuat, întărește legătura cu acțiunile voluntare întreprinse de societatea civilă și contribuie la combaterea excluderii sociale și a izolării. Ele au un impact benefic asupra cetățenilor și comunității, din punct de vedere fizic, psihologic, emoțional și socio- economic. Infrastructurile ecologice permit conectarea zonelor urbane și a celor rurale și creează medii de viață și (locuri) de muncă atractive15. Prin intermediul producției de alimente în zona urbană și al grădinilor comunitare, care reprezintă instrumente eficiente de educare a copiilor de vârstă școlară și care captează în special interesul tinerilor, infrastructurile ecologice acoperă decalajul existent între producția și consumul de alimente și contribuie la sporirea valorii percepute a acestora. Investițiile în infrastructurile ecologice au un potențial semnificativ de consolidare a dezvoltării regionale și urbane, mai ales prin menținerea sau crearea de locuri de muncă16. Caseta 2: Utilizarea terenurilor în locul aerului condiționat — realizarea de economii. Temperatura din centrul orașelor depășește deseori cu câteva grade temperatura din zonele periferice. Acest fapt se datorează unei umidități scăzute, cauzate atât de absența vegetației în zonele urbane, cât și de absorbția mai mare de energie solară a suprafețelor de culori închise, asfaltate sau din beton. Acest fenomen, cunoscut sub denumirea de „efect de căldură urbană insulară”, poate avea consecințe grave pentru sănătatea grupurilor de persoane vulnerabile, cum ar fi persoanele cu afecțiuni cronice sau cele în vârstă, în special în perioada valurilor de căldură. Aerul umed, pe care natura îl oferă gratuit, ar putea fi recreat artificial, prin utilizarea energiei electrice pentru a evapora apa, dar se estimează că această soluție ar implica un cost de aproximativ 500 000 EUR pe hectar. Lucrând cu natura și utilizând infrastructurile ecologice în mediul urban, de exemplu prin integrarea în orașe a unor parcuri cu o bogată biodiversitate, a unor spații verzi și coridoare de aer proaspăt, putem contribui la atenuarea acestui efect de căldură urbană insulară17.
2.3. Schimbările climatice și gestionarea riscului de dezastre Abordările de tip ecosistemic reprezintă strategii și măsuri care utilizează capacitățile de adaptare ale naturii. Ele se numără printre instrumentele cele mai eficace, cu cea mai largă aplicabilitate și cu cea mai mare viabilitate economică în ceea ce privește combaterea efectelor schimbărilor climatice. Atunci când este oportun, aceste abordări utilizează soluții bazate pe infrastructurile ecologice, deoarece acestea folosesc biodiversitatea și serviciile ecosistemice ca parte integrantă a unei strategii de adaptare, pentru a ajuta cetățenii fie să se adapteze la schimbările climatice, fie să atenueze efectele negative ale acestora. Recenta 13 Agenda teritorială a Uniunii Europene 2020. Spre o Europă inteligentă, durabilă și favorabilă
incluziunii, compusă din regiuni diverse. Reuniune ministerială neoficială a miniștrilor responsabili cu amenajarea și dezvoltarea teritorială. 19 mai 2011, Ungaria.
14 Comunicarea Comisiei către Consiliu și Parlamentul European privind o strategie tematică pentru mediul urban. COM(2005) 718 final.
15 Rapoarte, studii și documente care au primit sprijinul Comisiei Europene — http://ec.europa.eu/environment/nature/ecosystems/studies.htm.
16 În tabelul 2 din Documentul de lucru al serviciilor Comisiei [SWD (2013) 155 final] sunt prezentate exemple de locuri de muncă create grație infrastructurilor ecologice.
17 SWD(2012) 101 final/2, p. 13.
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strategie a UE privind adaptarea la schimbările climatice18 își propune, prin urmare, să analizeze necesitatea furnizării unor orientări suplimentare, adresate autorităților și factorilor de decizie, societății civile, sectorului privat și profesioniștilor din domeniul conservării, în ceea ce privește asigurarea mobilizării depline a abordărilor de tip ecosistemic în materie de adaptare. În cadrul activităților legate de exploatarea terenurilor, schimbarea destinației terenurilor și silvicultură (LULUCF)19 vor fi avute în vedere inițiative privind infrastructurile ecologice în sectorul agricol și cel al silviculturii, cu efect pozitiv asupra rezervelor de carbon și a echilibrului gazelor cu efect de seră în statele membre, contribuindu-se astfel la punerea în practică a politicilor climatice ale UE și CCONUSC. Caseta 3: Contribuția infrastructurilor ecologice la atenuarea și adaptarea la schimbările climatice. Unul dintre exemplele multiplelor avantaje ale restaurării capitalului natural este restaurarea ecologică a pădurilor inundabile. Existența unor păduri inundabile funcționale poate oferi multe avantaje, cum ar fi filtrarea apei, menținerea pânzelor freatice și prevenirea eroziunii. Pădurea atenuează de asemenea efectele schimbărilor climatice prin stocarea dioxidului de carbon și furnizarea de biomateriale care pot înmagazina temporar carbonul (produsele forestiere recoltate), îl pot înlocui, substituindu-se materialelor și combustibililor cu emisii ridicate de carbon sau pot juca rolul de „supapă de siguranță”, stocând apa și reducând riscul de inundații în așezările umane. Din punctul de vedere al costurilor punctuale și al celor de întreținere, restaurarea pădurilor inundabile este adesea mai ieftină decât soluțiile pur tehnice, cum ar fi de exemplu construirea de baraje și de rezervoare în zonele inundabile. Deoarece măsurile de restaurare a pădurilor inundabile reconectează totodată râul cu zonele învecinate inundabile, ele asigură conectivitatea pentru specii de importanță europeană precum vidra și unele specii rare de pești și de păsări.
Infrastructurile ecologice vor reprezenta, de asemenea, o completare necesară la activitatea de reducere a amprentei de carbon a transporturilor și a furnizării de energie, atenuând efectele negative ale ocupării și fragmentării terenurilor și contribuind la mai buna integrare a preocupărilor legate de utilizarea terenurilor, ecosisteme și biodiversitate în cadrul politicilor și al planificării. Soluțiile bazate pe infrastructurile ecologice pot contribui în mod semnificativ la dezvoltarea unor coridoare de transport ecologice, utilizând potențialul oferit de ecosistemele sănătoase, de exemplu pentru a atenua în mod sustenabil emisiile de carbon.
Directiva privind performanța energetică a clădirilor20 va promova dezvoltarea și utilizarea de noi materiale și caracteristici de proiectare în construcția de clădiri, ca parte a efortului de reducere a nivelurilor ridicate ale emisiilor de GES generate de acest sector. Soluțiile bazate pe infrastructurile ecologice, precum acoperișurile și pereții ecologici, pot contribui la reducerea emisiilor de GES. Acestea necesită practic mai puțină energie pentru încălzire și răcire, oferind totodată multe alte avantaje, precum reținerea apei, purificarea aerului și îmbogățirea biodiversității.
Soluțiile bazate pe infrastructurile ecologice care încurajează reziliența în caz de dezastre fac, de asemenea, parte integrantă din politica UE privind gestionarea riscului de dezastre. Din cauza schimbărilor climatice și a dezvoltării infrastructurilor, zonele predispuse la dezastre devin mai vulnerabile la fenomene meteorologice extreme și la catastrofe naturale precum inundațiile, alunecările de teren, avalanșele, incendiile de păduri, furtunile și mareele înalte, care cauzează pierderi de vieți omenești și produc cheltuieli de miliarde de euro sub formă de daune și costuri de asigurări, în fiecare an în UE. Impactul acestor evenimente asupra societății umane și asupra mediului poate fi adesea limitat prin utilizarea de soluții bazate pe infrastructurile ecologice, precum câmpiile inundabile funcționale, suprafețele riverane împădurite, pădurile de protecție din zonele de munte, plajele barieră și zonele umede de coastă, care pot fi asociate cu infrastructuri de prevenire a dezastrelor, cum ar fi lucrările de
18 COM(2013) 216 final, Strategie a UE privind adaptarea la schimbările climatice. 19 Land Use, Land Use Change and Forestry, LULUCF. 20 JO L 1, 4.1.2003, p. 65.
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protecție fluvială. Infrastructurile ecologice pot contribui, de asemenea, la reducerea expunerii la riscuri, sprijinind economiile și mijloacele de subzistență locale. Astfel, investițiile în soluții ecosistemice de reducere a riscului de producere a dezastrelor și investițiile în infrastructurile ecologice pot oferi multe avantaje în cadrul unor abordări inovatoare de gestionare a riscurilor, asigurând adaptarea la riscurile legate de schimbările climatice, garantând mijloace de subzistență sustenabile și promovând creșterea ecologică21. Orașele și autoritățile locale sunt primele care trebuie să facă față consecințelor imediate ale acestor dezastre. Ele joacă, prin urmare, un rol esențial în implementarea unor măsuri de prevenire precum infrastructurile ecologice. Caseta 4: Întărirea rezilienței și ameliorarea mijloacelor noastre de apărare. În ceea ce privește apărarea împotriva inundațiilor în zonele de coastă, proiectul de recul strategic al Alkborough Flats în estuarul Humber din Anglia a favorizat protecția împotriva inundațiilor în zonele de coastă, reducând sau amânând cheltuielile de construcție a unor instalații artificiale de protecție a litoralului. Se estimează că proiectul aduce beneficii anuale de 400 667 GBP (465 000 EUR) în ceea ce privește protecția împotriva inundațiilor, adică o valoare totală actualizată de 12,2 milioane GBP (14 milioane EUR), la care se adaugă alte avantaje pentru faună și serviciile ecosistemice. Proiectul a costat 10,2 milioane GBP (11,8 milioane EUR) și a implicat restaurarea habitatelor din zona de maree pe 440 de hectare de teren agricol.
2.4. Capitalul natural Infrastructurile ecologice pot juca un rol important în protejarea, conservarea și valorificarea capitalului natural al UE, după cum se afirmă în recenta propunere a Comisiei privind un program de acțiune pentru mediu până în 202022.
Terenuri și soluri
Terenurile și solurile sunt componente-cheie ale resurselor naturale ale UE. Cu toate acestea, în fiecare an, peste 1 000 km² din teritoriu sunt afectați construirii de locuințe, industriei, drumurilor sau activităților recreative23. În multe regiuni, solul este erodat în mod ireversibil sau are un conținut scăzut de materie organică. Contaminarea solului reprezintă, de asemenea, o problemă gravă24. Includerea în mod sistematic a considerentelor legate de infrastructurile ecologice în procesul de planificare și de luare a deciziilor va contribui la reducerea pierderii de servicii ecosistemice asociate afectării pe viitor a terenurilor și la ameliorarea și restabilirea funcțiilor solului.
Gestionarea terenurilor destinate agriculturii și silviculturii are un impact major asupra stării capitalului natural al UE. Recunoscând această legătură, politica agricolă comună (PAC) și dezvoltarea rurală oferă instrumente și măsuri de promovare a infrastructurilor ecologice și de valorificare a zonelor cu valoare naturală ridicată în mediul rural. Este vorba atât de sprijinul direct, la scară largă, acordat agricultorilor în cadrul primului pilon al PAC, pentru a preveni abandonarea și fragmentarea terenurilor, cât și de măsurile la scară mai mică, susținute prin intermediul programelor de dezvoltare rurală din cadrul celui de-al doilea pilon, cum ar fi investițiile neproductive, măsurile de agromediu (de exemplu, măsurile de conservare a peisajului cultivat, întreținerea și promovarea gardurilor vii, a zonelor tampon, a teraselor, a zidurilor de piatră uscată, măsurile silvopastorale etc.), plățile destinate promovării coerenței
21 Comunicare a Comisiei către Parlamentul European, Consiliu, Comitetul Economic și Social European
și Comitetul Regiunilor, „O abordare comunitară în privința prevenirii dezastrelor naturale și a celor provocate de om”, COM (2009) 82 final.
22 COM(2012) 710 final. 23 Agenţia Europeană de Mediu, Raport privind starea mediului 2010. http://www.eea.europa.eu/soer. 24 Implementarea Strategiei tematice pentru protecția solului și activitățile în curs. Comunicare a Comisiei
către Parlamentul European, Consiliu, Comitetul Economic și Social European și Comitetul Regiunilor. COM(2012) 46 final.
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cu rețeaua Natura 2000, cooperarea privind întreținerea marginilor valorificabile ale terenurilor agricole precum și conservarea și restaurarea caracteristicilor patrimoniului rural.
Comisia a imprimat un caracter mai ecologic propunerii sale de reformă a politicii agricole comune. Astfel, agricultorii care beneficiază de plăți în cadrul primului pilon trebuie să mențină pajiști permanente pe propriile exploatații, iar 7 % din terenurile arabile și din cele dedicate culturilor permanente trebuie să constituie zone de interes ecologic25. Implementarea corectă a acestor măsuri poate favoriza infrastructurile ecologice. Deoarece implementarea abordărilor bazate pe infrastructurile ecologice necesită o viziune integrată a serviciilor ecosistemice, ea încurajează o abordare echilibrată care pune accentul pe caracterul multifuncțional al zonelor rurale, în special pe accesul la alimente sustenabile, sigure și nutritive, cu ajutorul lanțurilor scurte de aprovizionare cu alimente. Infrastructurile ecologice vor favoriza deci o abordare mai coerentă a procesului decizional în ceea ce privește integrarea aspectelor ecologice și de sustenabilitate în planificarea spațială a peisajului urban și a celui rural. Caseta 5: Acțiuni în zonele agricole. Asociația tinerilor fermieri din Sevilla, Spania a gestionat un proiect LIFE de avangardă, al cărui obiectiv era elaborarea unui model de gestionare mai sustenabilă a solului. Proiectul s-a concentrat asupra domeniilor în care acoperirea crescută a solurilor cu culturi arboricole și producția mai intensivă conduseseră la o creștere a poluării, cauzată de sedimentare, de scurgerile de îngrășăminte și de prezența pesticidelor. Proiectul a identificat tipurile de acoperire vegetală care ofereau cea mai bună protecție împotriva eroziunii. Pe lângă avantajul prezentat de ameliorarea calității apei, datorată diminuării scurgerilor de produse agrochimice, s-a înregistrat de asemenea o capacitate sporită a solului de reținere a apei. Acest lucru a avut un efect pozitiv și asupra calității peisajelor și biodiversității din regiune Pe scară mai largă, modificarea ocupării terenurilor a conferit peisajului agrar un plus de coerență și de reziliență, în special din punctul de vedere al schimbărilor climatice.
Viitoarea strategie forestieră va integra alte preocupări legate de mediu și va trata realizarea obiectivului secundar legat de păduri din cadrul strategiei privind biodiversitatea. Măsurile care vizează reducerea semnificativă a fragmentării și degradării pădurilor și refacerea pădurilor degradate pot contribui totodată la îmbunătățirea stării de conservare a speciilor și habitatelor care depind sau sunt afectate de silvicultură, dar și la îmbunătățirea furnizării de servicii ecosistemice conexe. Infrastructurile ecologice pot aduce o contribuție constructivă în această privință prin furnizarea unui cadru coerent în care caracteristicile și funcțiile naturale sunt conservate și consolidate în zonele forestiere.
Apă
Integrarea considerațiilor referitoare la infrastructurile ecologice în gestionarea bazinelor hidrografice poate contribui în mod semnificativ la asigurarea bunei calități a apei, la atenuarea efectelor presiunilor hidromorfologice și la reducerea impactului inundațiilor și al secetei26. Infrastructurile ecologice oferă totodată opțiuni rentabile27 pentru o mai bună implementare a Directivei privind apa potabilă28 și a Directivei privind apele subterane29.
25 COM(2011) 625 final/2. 26 Plan de salvgardare a resurselor de apă ale Europei. Comunicare a Comisiei către Parlamentul
European, Consiliu, Comitetul Economic și Social European și Comitetul Regiunilor. COM(2012) 673 final.
27 The Economics of Ecosystems and Biodiversity (TEEB). Exemplele Viena, New York, Philadelphia, Vittel, http://www.teebweb.org/.
28 JO L 330, 5.12.1998, p. 32. 29 JO L 372, 27.12.2006, p. 19.
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Totodată, sunt în curs de elaborare soluții ecologice inovatoare, foarte eficiente și rentabile și care oferă avantaje multiple pentru tratarea apelor reziduale30. Caseta 6: acțiune privind măsuri de agromediu legate de apă. În Sint-Truiden, Belgia, au fost luate măsuri pentru a proteja satul de eroziunea solului și de scurgerile de noroi. Ele au inclus canale înierbate, zone tampon înierbate și iazuri de colectare în bazinul hidrografic. Costul total al acestor măsuri a fost scăzut (126 EUR/ha/20 ani) în raport cu costurile de reparare a pagubelor și de curățare în urma scurgerilor de noroi în zona de studiu (54 EUR/ha/an) și cu toate beneficiile secundare, care au inclus o mai bună calitate a apei în aval, costuri de dragare în aval mai mici, mai puțin stres psihologic pentru locuitori și o biodiversitate mai bogată. Creșterea biodiversității și îmbunătățirea calității peisajului au creat noi oportunități de agroturism și ecoturism.
În ceea ce privește mediul marin, infrastructurile ecologice pot contribui la punerea în practică a strategiilor actuale privind amenajarea spațiului maritim și gestionarea integrată a zonelor de coastă31, în special a strategiilor pentru gestionarea sustenabilă a zonelor de coastă și îmbunătățirea sistemelor de protecție a acestor zone. Dezvoltarea abordărilor bazate pe „carbonul albastru”32, benefice pentru stocurile de pește, poate fi favorizată de aplicarea principiilor care reglementează infrastructurile ecologice, pentru promovarea serviciilor ecosistemice multiple în mediul marin.
Conservarea naturii
Natura 2000 este o rețea ecologică creată în temeiul directivelor Habitate33 și Păsări34. Ea cuprinde peste 26 000 de situri răspândite în toate statele membre și ocupă 18 % din suprafața terestră a UE și aproximativ 4 % din apele marine aflate în jurisdicția statelor membre. Ea a fost creată în principal pentru conservarea și protejarea unor specii și habitate esențiale din UE, dar asigură în același timp numeroase servicii ecosistemice în beneficiul societății umane. Valoarea acestor servicii a fost estimată la 200-300 de miliarde EUR pe an35. Grație lucrărilor realizate în ultimii 25 de ani pentru crearea și consolidarea rețelei, baza infrastructurilor ecologice există deja. Rețeaua constituie un rezervor de biodiversitate care poate fi utilizat pentru repopularea și revitalizarea mediilor degradate și pentru catalizarea dezvoltării infrastructurilor ecologice. Acest lucru va contribui totodată la reducerea fragmentării ecosistemelor, la îmbunătățirea conectivității dintre siturile din rețeaua Natura 2000 și la atingerea obiectivelor articolului 10 din Directiva Habitate36.
3. ELABORAREA UNEI STRATEGII A UE PENTRU INFRASTRUCTURILE ECOLOGICE
Așa cum s-a arătat în secțiunile anterioare, infrastructurile ecologice pot aduce o contribuție importantă la atingerea mai multor obiective strategice esențiale ale UE. Prezenta secțiune analizează măsurile care trebuie luate pentru a încuraja dezvoltarea infrastructurilor ecologice, inclusiv la nivelul UE.
Dimensiunea UE — chestiuni legate de amploarea proiectelor și de politici
Dezvoltarea infrastructurilor ecologice în Uniunea Europeană se află într-un punct critic. În ultimii 20 de ani, au fost executate din ce în ce mai multe proiecte de infrastructuri ecologice și există o vastă experiență care demonstrează că abordarea este flexibilă, solidă și rentabilă. 30 Zonele umede artificiale integrate (ICW), un exemplu de infrastructură ecologică, pot contribui la
îndeplinirea obiectivelor strategice ale UE în materie de tratare a apelor reziduale și de protejare a apei pentru scăldat.
31 COM(2013) 133 final. 32 http://www.thebluecarbonproject.com/the-problem-2/. 33 JO L 206, 22.7.1992, p. 7. 34 JO L 103, 25.4.1979, p. 1. 35 http://ec.europa.eu/environment/nature/natura2000/financing/index_en.htm. 36 http://ec.europa.eu/environment/nature/ecosystems/docs/adaptation_fragmentation_guidelines.pdf.
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Proiectele de infrastructuri ecologice sunt realizate la nivel local, regional, național sau transfrontalier. Însă pentru a optimiza funcționarea infrastructurilor ecologice și a maximiza beneficiile acestora, lucrările efectuate la diferite niveluri trebuie să devină interconectate și interdependente. Astfel, beneficiile vor crește considerabil cu condiția existenței unui minim de coerență între diferitele niveluri. În lipsa unei acțiuni la nivelul UE, vor exista doar câteva inițiative independente, care nu își vor concretiza întregul potențial de restabilire a capitalului natural și de reducere a costurilor legate de infrastructura grea37. Acesta este motivul pentru care părțile interesate așteaptă un angajament clar, pe termen lung, din partea UE pentru dezvoltarea și implementarea infrastructurilor ecologice.
Integrarea infrastructurilor ecologice în principalele domenii de politică
Așa cum s-a indicat în secțiunea 2, infrastructurile ecologice pot aduce o contribuție importantă în domeniul dezvoltării regionale, al schimbărilor climatice, al gestionării riscului de dezastre, al agriculturii/silviculturii și al mediului. În cele mai multe cazuri, contribuția pe care acestea o pot aduce este deja recunoscută. În momentul de față este nevoie ca infrastructurile ecologice să devină o componentă standard a amenajării și dezvoltării teritoriului, care să fie pe deplin integrată în implementarea politicilor menționate mai sus. Pentru ca în cadrul următorului pachet bugetar (2014-2020) să fie exploatat întregul potențial al infrastructurilor ecologice, modalitățile de utilizare a acestora trebuie stabilite cât mai curând posibil, pentru a facilita integrarea lor în proiecte finanțate prin mecanisme de finanțare adecvate, cum ar fi politica agricolă comună, Fondul de coeziune, Fondul european de dezvoltare regională, Orizont 2020, mecanismul Conectarea Europei, Fondul european pentru pescuit și afaceri maritime și Instrumentul financiar pentru mediu (LIFE).
Nevoia de date coerente și fiabile
Pentru o implementare eficientă a infrastructurilor ecologice, este esențial să dispunem date coerente și fiabile. Este nevoie de informații cu privire la întinderea și starea ecosistemelor, la serviciile pe care le oferă și la valoarea acestora38, astfel încât serviciile ecosistemice să fie corect evaluate, inclusiv, dacă este cazul, din punct de vedere al prețurilor, pentru a promova soluțiile bazate pe infrastructuri ecologice în amenajarea teritoriului și în procesele de luare a deciziilor în materie de infrastructură. Deși este evident că majoritatea deciziilor privind proiectele de infrastructuri ecologice vor fi luate la nivel local, național și regional, ar trebui promovat un nivel minim de coerență în ceea ce privește datele folosite pentru luarea acestor decizii, în special în cazul proiectelor susținute prin fonduri UE.
Deși la momentul actual există un volum mare de date disponibile, în cele mai multe cazuri, acestea nu au fost generate sau evaluate într-un mod coerent sau coordonat. În contextul strategiei UE în domeniul biodiversității, Comisia depune eforturi, alături de Agenția Europeană de Mediu, de alte agenții și organisme de cercetare, de statele membre și de părțile 37 http://ec.europa.eu/environment/nature/ecosystems/studies.htm#design. 38 Lucrările metodologice pentru cartografierea și evaluarea ecosistemelor și a serviciilor acestora sunt
realizate în cadrul acțiunii 5 din strategia privind biodiversitatea. Aceste informații trebuie însă adaptate la considerentele legate de infrastructurile ecologice (a se vedea exemple la adresa http://ec.europa.eu/environment/nature/ecosystems/index_en.htm). În contextul politicii privind schimbările climatice, UE a adoptat de curând un act normativ care armonizează contabilizarea emisiilor de gaze cu efect de seră din sectorul LULUCF și stabilește o foaie de parcurs pentru îmbunătățirea și extinderea sistemelor contabile ale statelor membre. Acest lucru va garanta disponibilitatea unor date coerente la nivelul UE cu privire la performanța din domeniul emisiilor de gaze cu efect de seră ale ecosistemelor (gestionate): Decizie a Parlamentului European și a Consiliului privind normele de contabilizare și planurile de acțiune referitoare la emisiile și absorbțiile de gaze cu efect de seră care rezultă din activități legate de exploatarea terenurilor, schimbarea destinației terenurilor și silvicultură.
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interesate, pentru a garanta o utilizare cât mai eficace a datelor obținute în urma acțiunilor curente și planificate. Această activitate va continua în viitor, dar ar trebui, în mod ideal, să se intensifice, iar contribuția comunității științifice ar trebui, la rândul său, să crească. UE are un rol important de jucat în acest proces, în special prin acordarea de sprijin financiar pentru programele care își propun remedierea acestui deficit de cunoștințe, cum ar fi Orizont 2020 și fondurile structurale și de investiții europene.
Îmbunătățirea bazei de cunoștințe și stimularea inovării
Cunoștințele noastre despre aspectele tehnice ale implementării infrastructurilor ecologice s- au dezvoltat considerabil în ultimii ani. Însă pentru a înțelege mai bine legăturile dintre biodiversitate (specii/habitate) și starea ecosistemului (vitalitate, reziliență și productivitate), precum și dintre starea ecosistemului și capacitatea sa de a furniza servicii ecosistemice, activitățile de cercetare trebuie să continue. Totodată, o mai bună cunoaștere a evaluării serviciilor ecosistemice, în special a beneficiilor pe care soluțiile bazate pe infrastructuri ecologice le pot avea pentru societate, sănătate și securitate/reziliență, ar fi extrem de utilă pentru a susține dezvoltarea ulterioară a acestor infrastructuri. Investițiile în cercetarea aplicată pentru testarea și implementarea soluțiilor inovatoare bazate pe infrastructurile ecologice trebuie la rândul lor încurajate.
Grație dezvoltării unor tehnologii și proceduri adecvate, în special în sectorul transporturilor, al energiei, al agriculturii, al proiectării și funcționării orașelor noastre, și datorită progreselor din domeniul bioeconomiei39, potențialul infrastructurilor ecologice de a oferi soluții rentabile va crește. În orașe, clădirile „inteligente”, eficiente din punctul de vedere al utilizării resurselor, care încorporează caracteristici ecologice, cum ar fi acoperișuri și pereți ecologici și materiale noi de construcție, pot aduce beneficii pentru mediu, societate și sănătate40. Pe lângă aspectele legate de tehnologie, persoanele care lucrează în domeniul infrastructurilor ecologice trebuie să dobândească competențe adecvate care să le permită să adopte o abordare inovatoare. Remedierea lipsei competențelor prin reconversia profesională și formarea suplimentară a personalului calificat este esențială pentru a asigura existența unei forțe de muncă bine pregătite pe termen mediu.
La nivelul UE, programul Orizont 2020 și Fondul european de dezvoltare regională sunt surse potențiale de sprijin pentru cercetarea și inovarea din domeniul infrastructurilor ecologice.
Sprijin financiar pentru proiectele de infrastructuri ecologice
Integrarea infrastructurilor ecologice în implementarea politicilor din sectoare-cheie ar asigura sprijinul mecanismelor de finanțare aferente pentru încurajarea implementării infrastructurilor ecologice în întreaga UE. Și sectorul privat trebuie să contribuie la finanțarea infrastructurilor ecologice. Proiectele de infrastructuri ecologice sunt însă complexe și, inevitabil, riscante, în mod particular în faza inițială de dezvoltare. UE trebuie să reducă riscul prin intermediul instrumentelor financiare (de exemplu practici de împărțire a riscurilor) și al proiectelor în parteneriat, finanțate prin fonduri publice și private. Investitorii potențiali (autorități locale, regiuni, dezvoltatori privați) au nevoie totodată de asistență tehnică pentru dezvoltarea proiectelor de infrastructuri ecologice41. Comisia și BEI analizează o serie de opțiuni pentru înființarea unui mecanism de finanțare pentru a sprijini investițiile legate de biodiversitate, inclusiv proiectele de infrastructuri ecologice.
39 COM(2012) 60 final. 40 Connecting smart and sustainable growth through smart specialisation (Asocierea creșterii inteligente
cu cea sustenabilă prin intermediul unei specializări inteligente) Comisia Europeană, 2012. 41 http://ec.europa.eu/environment/enveco/biodiversity/pdf/BD_Finance_summary-300312.pdf.
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Proiecte de infrastructuri ecologice la nivelul UE
Multe elemente geografice, cum sunt lanțurile muntoase (Alpii, Pirineii, Carpații), bazinele hidrografice (Rinul, Dunărea) și pădurile (pădurile fino-scandinave) depășesc frontierele naționale și fac parte din patrimoniul natural și cultural comun al UE. Ele necesită acțiuni coordonate, comune și o viziune paneuropeană. Până în prezent, au fost întreprinse inițiative de infrastructură de mare anvergură în domeniul transporturilor, energiei și TIC42. Dezvoltarea unui instrument echivalent, axele prioritare transeuropene pentru infrastructurile ecologice în Europa, TEN-G (pe baza rețelelor transeuropene din sectoarele infrastructurii gri), ar favoriza în mod semnificativ asigurarea rezilienței și vitalității unora dintre cele mai reprezentative ecosisteme din Europa, aducând avantajele economice și sociale aferente. Astfel de inițiative ar constitui totodată inițiative emblematice, care ar putea servi drept exemple la nivel național, regional și local și ar spori importanța acordată dezvoltării infrastructurilor ecologice transeuropene în cadrul deciziilor politice, de planificare și de finanțare. Statele membre și regiunile sunt încurajate să profite de ocaziile de a dezvolta infrastructurile ecologice într-un context transfrontalier/transnațional prin intermediul strategiilor macroregionale sprijinite de FEDER43 și al programelor de cooperare teritorială europeană44. Caseta 7: Proiecte de infrastructuri ecologice la nivelul UE. Inițiativa privind Centura verde europeană reprezintă o rețea ecologică ce se întinde de la Marea Barents până la Marea Neagră. Scopul său este o mai bună armonizare a activităților umane cu mediul natural înconjurător și creșterea posibilităților de dezvoltare socio- economică a comunităților locale. Rețeaua conectează parcuri naționale, parcuri naturale, rezervații ale biosferei, zone transfrontaliere protejate și zone neprotejate care se întind de-a lungul frontierelor sau care le traversează. Ea sprijină inițiative de dezvoltare regională bazate pe conservarea naturii. Rețeaua transformă una dintre cele mai reprezentative bariere din istoria omenirii (Cortina de fier) într-un simbol de reconciliere și cooperare transfrontalieră, prin conservarea și protejarea unora dintre cele mai impresionante și fragile peisaje ale Europei.
4. STRATEGIA UE PENTRU PROMOVAREA INFRASTRUCTURILOR ECOLOGICE Comisia s-a angajat să elaboreze o strategie a UE privind infrastructurile ecologice care să contribuie la conservarea și ameliorarea capitalului nostru natural și la atingerea obiectivelor Strategiei Europa 2020. Pe baza considerentelor expuse mai sus privind beneficiile potențiale ale infrastructurilor ecologice și rolul pe care UE îl poate juca în dezvoltarea acestora, Comisia consideră că strategia ar trebui să ia forma unui cadru care să combine semnalele politice și acțiunile tehnice sau științifice. În acest stadiu, Comisia consideră că strategia poate fi implementată în contextul legislației, al instrumentelor de politică și al mecanismelor de finanțare existente. Ea ar conține elementele menționate mai jos.
Promovarea infrastructurilor ecologice în principalele domenii de politică
Politicile regionale sau de coeziune, cele din domeniul schimbărilor climatice și al mediului, al gestionării riscului de catastrofe naturale, al sănătății și protecției consumatorilor și politica agricolă comună, inclusiv mecanismele de finanțare asociate, vor fi principalele domenii de politică prin care vor fi promovate infrastructurile ecologice. Până la sfârșitul anului 2013, Comisia va elabora orientări tehnice privind modul în care infrastructurile ecologice vor fi integrate în implementarea acestor politici din 2014 până în 2020. În contextul acestor domenii de politică principale, ea va lua măsuri pentru a crește nivelul de informare cu privire la infrastructurile ecologice în rândul principalelor grupuri de părți interesate și pentru a
42 COM(2011) 676 final, COM(2011) 665 final. 43 Strategia pentru regiunea Mării Baltice și Strategia pentru regiunea Dunării. 44 http://ec.europa.eu/regional_policy/cooperate/cooperation/index_en.cfm.
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promova cele mai bune practici, inclusiv prin dezvoltarea unei platforme IT speciale pentru efectuarea schimbului de informații.
Comisia va examina totodată modul în care inovarea legată de infrastructurile ecologice poate fi finanțată printr-o serie de alte instrumente ale UE, cum ar fi mecanismul „Conectarea Europei”. În contextul politicii TEN-T, de exemplu, integrarea infrastructurilor ecologice în proiecte poate fi promovată în cadrul abordării propuse bazate pe coridoare.
Îmbunătățirea calității informațiilor, consolidarea bazei de cunoștințe și promovarea inovării
Pe lângă continuarea lucrărilor de cartografiere și evaluare în contextul strategiei UE privind biodiversitatea, până în 2015, Comisia va analiza amploarea și calitatea datelor tehnice și spațiale de care dispun factorii de decizie în ceea ce privește implementarea infrastructurilor ecologice. Această analiză va examina totodată modul în care ar putea fi îmbunătățit regimul actual care reglementează producerea, analiza și difuzarea acestor informații, în special printr- o mai bună utilizare a structurilor de schimb de informații.
Până la sfârșitul anului 2013, Comisia va evalua necesitatea și posibilitățile, în contextul programului Orizont 2020, de a sprijini din punct de vedere metodologic lucrările curente de cartografiere și evaluare, de a îmbunătăți baza de cunoștințe și de a dezvolta și a încuraja tehnologiile și abordările inovatoare pentru a facilita dezvoltarea infrastructurilor ecologice. Ea va evalua de asemenea contribuția pe care o pot avea standardele tehnice, în particular cele referitoare la modulele fizice și la proceduri, la creșterea pieței produselor compatibile cu infrastructurile ecologice.
Îmbunătățirea accesului la finanțare
Comisia va continua să studieze posibilitățile de înființare a unor mecanisme de finanțare inovatoare în sprijinul infrastructurilor ecologice. Alături de BEI, ea își propune să creeze, până în 2014, un mecanism de finanțare în sprijinul persoanelor care doresc să dezvolte proiecte de infrastructuri ecologice.
Proiecte de infrastructuri ecologice la nivelul UE
Până la sfârșitul anului 2015, Comisia va efectua un studiu pentru a evalua posibilitățile de a dezvolta o inițiativă TEN-G la nivelul UE. Studiul va include o evaluare a costurilor și a beneficiilor economice, sociale și de mediu ale unei astfel de inițiative.
5. CONCLUZII Infrastructurile ecologice pot contribui în mod semnificativ la realizarea unui număr mare de obiective politice esențiale ale UE. Cea mai bună modalitate prin care UE poate promova dezvoltarea infrastructurilor ecologice este crearea unui cadru care să permită încurajarea și facilitarea proiectelor de infrastructuri ecologice în contextul instrumentelor juridice, politice și financiare existente. Statele membre sunt încurajate să valorifice aceste oportunități pentru a impulsiona implementarea infrastructurilor ecologice și a exploata avantajele lor pentru dezvoltarea durabilă. Prezentul document explică motivele promovării infrastructurilor ecologice și descrie elementele viitoarei strategii a UE. Până la sfârșitul anului 2017, Comisia va analiza progresele realizate în dezvoltarea infrastructurilor ecologice și va publica un raport privind experiența dobândită care va conține recomandări pentru acțiunile viitoare.
Cod FO 53-02, Ver.2
SC2016- /___.___.2016.
ACORD DE PARTENERIAT nr. ______ din data de ___/ ___/2016
1. PĂRŢILE
1.1. MUNICIPIUL TIMIŞOARA, cu sediul în Timişoara, B-dul C. D. Loga nr.1, Judeţul Timiş, cod poştal 300030, E-mail: [email protected], Pagina web: www.primariatm.ro,
reprezentat prin Domnul Nicolae ROBU în calitate de Primar al Municipiului Timișoara, Cod Fiscal
14756536, Telefon/Fax: 0256/408451, pe de o parte
şi
1.2. Asociația pentru Promovarea Valorilor Naturale și Culturale ale Banatului și Crișanei ”Excelsior”, denumită în continuare Asociția „Excelsior”, cu sediul în Arad, Strada Suceava nr.18,
cod poștal 310465, Județul Arad, CIF 18483684, Telefon: 0257210192, Fax: 0257210192,
0357780026, Mobil: 0745608905, E-mail: [email protected], Web: www.ongexcelsior.ro,
www.infrastructuraverde.ro, reprezentată prin Domnul Mihai – Sorin PASCU în calitate de
Președinte, pe de altă parte
În conformitate cu prevederile Hotărârii Consiliului Local al Municipiului Timișoara nr.
___/___.___.2016, convenim să încheiem prezentul Acord de Parteneriat
2. OBIECTUL
2.1. Prezentul acord de parteneriat are ca obiect colaborarea și dezvoltarea în comun a unor
acțiuni și activități pentru studiul și dezvoltarea rețelei pentru infrastructură ecologică, verde (Green
Infrastructure – GI) în Municipiul Timișoara.
1.2. Obiectivele acordului de parteneriat sunt următoarele: a) Dezvoltarea unei Strategii pentru infrastructură ecologică, verde (Green Infrastructure – GI) în
Municipiul Timișoara,
b) Dezvoltarea unei Rețele de infrastructură ecologică, verde (Green Infrastructure – GI),
c) Dezvoltarea, implementarea în parteneriat a unui proiect în cadrul Programului Operațional
Capacitate Administrativă (POCA), pentru a veni în sprijinul inițiativei de realizare a strategiei
pentru infrastructură verde și a rețelei TEN-G (Trans-European Network for Green Infrastructure).
3. DURATA ACORDULUI, INTRAREA ÎN VIGOARE
3.1. Prezentului acord se încheie pe o perioadă de 24 de luni calendaristice, cu posibilitate de
prelungire cu acordul părților, până la atingerea obiectivelor parteneriatului.
3.2. Prezentul acord intră în vigoare la data semnării sale de către ambele părţi.
4. OBLIGAŢIILE PĂRŢILOR:
4.1. Ambele părţi se obligă să colaboreze şi să susţină derularea în bune condiții a acordului, prin
furnizarea de expertiză şi resurse umane pentru activităţile de care sunt responsabile, activităţi şi
responsabilităţi stabilite de comun acord, în funcţie de obiectul acestora.
4.2. MUNICIPIUL TIMIȘOARA se obligă:
a) Să asigure comunicarea și schimbul de informații cu Asociația „Excelsior”, asigurând pe întreaga derulare a acordului de parteneriat o persoană de contact din cadrul Direcției de Mediu a
Primăriei Municipiului Timișoara;
ROMÂNIA
JUDEȚUL TIMIȘ
MUNICIPIUL TIMIȘOARA
B-dul C.D. Loga nr.1
Cod FO 53-02, Ver.2
b) Să pună la dispoziția specialiștilor Asociației „Excelsior” informațiile publice relevante de care dispune la momentul semnării acordului de parteneriat și a informațiilor de care va beneficia în
viitor, pe baza cererilor formulate de către asociație;
c) Să asigure participarea reprezentanților Primăriei Municipiului Timișoara la elaborarea ”Strategiei pentru infrastructură verde (Green Infrastructure - GI) a Municipiului Timișoara”;
d) Să asigure participarea reprezentanților Primăriei Municipiului Timișoara la stabilirea ”Rețelei de infrastructură verde (Green Infrastructure - GI) a Municipiului Timișoara;
e) Să elaboreze și să supună dezbaterii publice, analizei și hotărârii Consiliului Local al Municipiului Timișoara documentele privitoare la ”Strategia pentru infrastructură verde a
Municipiului Timișoara” și la ”Rețeaua de infrastructură verde a Municipiului Timișoara”
f) Să nu folosească materialele elaborate în cadrul parteneriatului fără acordul/recenzia partenerului;
g) Să organizeze în parteneriat evenimente, cursuri, ateliere de lucru și alte asemenea evenimente în domeniul infrastructurii verzi;
h) Să promoveze interesele Asociației „Excelsior” ȋn vederea creșterii prestigiului național și internațional, prin elaborarea de materiale, diseminarea de informații prin canalele proprii de
comunicare, evenimente, prezentări, etc.;
4.3. Asociația pentru Promovarea Valorilor Naturale și Culturale ale Banatului și Crișanei ”Excelsior” se obligă:
a) Să asigure legătura cu Primăria Municipiului Timișoara, în persoana președintelui asociației, Biolog Mihai - Sorin PASCU;
b) Să asigure specialiștii necesari pentru desfășurarea tuturor activităților, în vederea atingerii obiectivelor acordului de parteneriat;
c) Să asigure baza/suportul informațional cu privire la politicile europene și naționale în domeniul infrastructurii verzi;
d) Să dezvolte metodologia de lucru necesară pentru evaluarea și desemnarea infrastructurii verzi;
e) Să desfășoare studiile în teren cu specialiștii proprii; f) Să dezvolte cu specialiștii proprii propunerea/proiectul de ”Strategie pentru infrastructură verde a Municipiului Timișoara”, cu participarea și consultarea reprezentanților Primăriei
Municipiului Timișoara;
g) Să dezvolte cu specialiștii proprii propunerea/proiectul privind ”Rețeaua de infrastructură verde a Municipiului Timișoara”, cu participarea și consultarea reprezentanților Primăriei
Municipiului Timișoara;
h) Să dezvolte cu specialiștii proprii aplicația de proiect în cadrul Programului Operațional Capacitate Administrativă (POCA), cu participarea și sprijinul reprezentanților Primăriei
Municipiului Timișoara.
i) Să nu folosească materialele elaborate în cadrul parteneriatului fără acordul/recenzia partenerului;
j) Să organizeze în parteneriat evenimente, cursuri, ateliere de lucru și alte asemenea evenimente în domeniul infrastructurii verzi;
k) Să promoveze interesele Municipiului Timișoara ȋn vederea creșterii prestigiului național și internațional, prin elaborarea de materiale, diseminarea de informații prin canalele proprii de
comunicare, evenimente, prezentări, etc.;
5. MODALITĂŢI DE ÎNCETARE A CONTRACTULUI 5.1. Prezentul acord de parteneriat încetează:
a) Prin acordul ambelor părţi, b) Încălcarea în mod culpabil de către una dintre părţi a obligaţiilor asumate.
6. CONFIDENŢIALITATE
6.1. Părţile convin să păstreze confidențiale informaţiile primite şi sunt de acord să prevină orice
utilizare sau divulgare neautorizată a unor astfel de informaţii.
6.2. Informaţiile confidenţiale vor fi folosite de părţi numai în scopul executării unor contracte şi
vor putea fi dezvăluite numai persoanelor implicate în executarea contractului.
Cod FO 53-02, Ver.2
7. CLAUZE SPECIALE
7.1. Activităţile concrete din cadrul parteneriatului vor fi realizate pe baza consultării şi
acordului reciproc al celor două părţi.
7.2. Realizarea activităţilor va depinde de existenţa resurselor materiale, financiare şi umane de
care dispune fiecare parte.
7.3. Modificarea prezentului acord se va face prin act adiţional încheiat între părţi. Partea care
are iniţiativa modificării prezentului acord va transmite celeilalte părţi, în scris, spre analiză,
propunerile sale.
7.4. Prezentul acord de parteneriat are caracterul unui acord cadru. Acordul cadru va fi
completat, după caz, cu contracte de colaborare specifice pentru activitatea/proiectul/inițiativa
convenită de părți.
8. NOTIFICĂRI
8.1. Orice notificare/corespondenţă adresată de o parte celeilalte părţi este valabil comunicată
dacă este predată sau transmisă la adresa menţionată în partea introductivă a prezentului acord de
parteneriat.
8.2. În cazul în care notificarea/corespondenţa va fi transmisă prin poştă, se va face prin
scrisoare recomandată, cu confirmare de primire şi se consideră primită de destinatar la data
menţionată de oficiul poştal primitor pe această confirmare.
8.3. Schimbarea adresei nu este opozabilă celeilalte părţi decât dacă a fost notificată cu cel puţin
5 zile lucrătoare înainte.
9. LITIGII
9.1. Părţile se vor strădui, de bună credinţă, să rezolve pe cale amiabilă eventualele litigii,
controverse sau diferende apărute din sau în legătură cu acest acord.
9.2. În cazul în care nu se ajunge la o soluţie pe cale amiabilă, litigiile, controversele, diferendele
se vor înainta spre soluţionare instanţelor judecătoreşti competente.
10. DISPOZIŢII FINALE 10.1 Prezentul acord constituie un document cadru de colaborare între părţi, în vederea realizării
obiectivelor propuse, putând fi completat sau modificat prin înţelegerea părţilor.
Prezentul Acord s-a încheiat şi semnat de ambele părţi, la Timişoara, astăzi _______________ în 2
(două) exemplare originale, câte unul pentru fiecare parte.
MUNICIPIUL TIMIŞOARA Asociația pentru Promovarea Valorilor Naturale
și Culturale ale Banatului și Crișanei ”Excelsior”
PRIMAR, PREȘEDINTE,
Nicolae ROBU Mihai – Sorin PASCU
_______________________ _______________________ (semnătura) (semnătura)
L.s.
L.s.
VICEPRIMAR,
Dan DIACONU
_______________________
(semnătura)
DIRECTOR EXEC. DIRECŢIA DE MEDIU,
Adrian – Amedeo BERE - SEMEREDI
_______________________ (semnătura)
SERVICIUL JURIDIC,
_______________________ (semnătura)
Cod FO-53-01, Ver.2
ROMÂNIA APROBAT
JUDEŢUL TIMIŞ PRIMAR,
MUNICIPIUL TIMIŞOARA
DIRECŢIA DE MEDIU Nicolae ROBU
SC2016- / .10.2016
REFERAT
privind propunerea de încheiere a unui acord de parteneriat între Municipiul Timişoara şi
Asociația pentru Promovarea Valorilor Naturale și Culturale ale Banatului și Crișanei
”Excelsior”
Municipiul Timișoara în cooperare cu Oraşul Szeged au implementat pe parcursul anilor 2011 și
2012 Proiectul "Biodiversitatea şi protecţia naturii - o abordare responsabilă a problemelor de
mediu a două oraşe înfrăţite", acronim BIOTOWNS, cod proiect HURO/0901/128/1.3.4., în cadrul
Programului de Cooperare Transfrontalieră Ungaria - România 2007.
Grație acestui proiect cu finanțare europeană, s-a elaborat Studiul de specialitate pentru evaluarea
biotopurilor urbane şi Planul strategic pentru protejarea şi conservarea biodiversităţii în Municipiul
Timișoara, aprobate prin Hotărârea Consiliului Local al Municipiului Timișoara nr.32//31.01.2012,
serviciilor de specialitate fiind prestate de Asociația pentru Promovarea Valorilor Naturale și
Culturale ale Banatului și Crișanei ”Excelsior”.
În anii care au urmat, Direcția de Mediu a colaborat în continuare cu Asociația „Excelsior” în
domeniul protecției mediului și pentru organizarea/derularea unor activități/acțiuni ecologice.
În urma discuțiilor purtate cu conducerea Asociației „Excelsior”, privitor la derularea unor proiecte
în viitor, prin adresa nr.CDM2016-568/20.09.2016 asociația a lansat o propunere de încheiere a
unui acord de parteneriat în vederea dezvoltării rețelei pentru infrastructură ecologică, verde, în
Municipiul Timișoara.
Infrastructura ecologică sau verde (Green infrastructure – GI) reprezintă totalitatea elementelor
unei reţele de spaţii verzi interconectate, cu rolul de conservare a funcţiilor ecosistemului natural şi
de creare de beneficii multiple pentru comunitate. Infrastructura verde se compune din elemente
naturale şi antropice (sau seminaturale), cum ar fi zonele împădurite, reîmpădurite, zonele verzi
(perdele verzi, parcurile, scuarurile, aliniamentele verzi), terenurile agricole cu valoare naturală
ridicată sau pășunile, etc. Trebuie subliniat de asemenea rolul și contribuția pe care infrastructura
ecologică din mediul urban (cum ar fi și acoperișurile verzi, parcurile și „drumurile verzi”) le au
raportat la statusul de sănătate al populației, la aspectele de ordin social, la adaptarea și atenuarea
efectelor schimbărilor climatice dar și drenarea surplusului de apă provenit din precipitații. Este
dovedit faptul că, o mai bună planificare a infrastructurii, inclusiv a celei ecologice, contribuie la
sporirea eficacității politicilor privind mobilitatea și construcțiile.
Astfel, infrastructura ecologică, verde reprezintă o rețea planificată strategic, modelată și gestionată
pentru a asigura comunităților locale o paletă cât mai largă de servicii ecosistemice.
Peisajul urban timișorean a suferit în ultimii 20 de ani modificări substanțiale, ca urmare a folosirii
terenurilor, extinderii zonelor locuite, fragmentării unor ecosisteme, extinderii rețelelor de
comunicații și energie, afectării spațiilor verzi. Astfel de fragmentări și deteriorări ale ecosistemului
au afectat speciile din flora și fauna locală și au redus coerența spațială și funcțională a peisajului. În
urma evaluărilor habitatelor urbane supuse studiului în anii anteriori, a rezultat clar faptul că
ecosistemul Municipiului Timișoara nu mai are aceeași diversitate biologică iar locuitorii nu mai
Cod FO-53-01, Ver.2
beneficiază de servicii ecosistemice la același nivel ca zonele neafectate de activitățile umane, dar
în același timp s-a subliniat faptul că acest neajuns poate constitui o provocare pentru autoritatea
publică locală, printr-o abordare planificată strategic, o gestiune corespunzătoare, prin
implementarea de acțiuni și proiecte de dezvoltare a infrastructurii verzi și a rețelelor de
infrastructură verde, monitorizate corespunzător.
Pentru a sublinia impoartanța infrastructurii ecologice (verzi), Comisia Europeană a apropat în anul
2013 Strategia pentru Infrastructura ecologică COM/2013/0249, anexată alăturat - „Comunicarea
Comisiei către Parlamentul European, Consiliu, Comitetul Economic și Social European și
Comitetul Regiunilor - Infrastructurile ecologice — Valorificarea capitalului natural al Europei”.
Conform comunicării sus-menționate, infrastructura ecologică este „o rețea planificată strategic,
alcătuită din zone naturale și seminaturale, precum și din alte elemente de mediu, care este
concepută și gestionată pentru a oferi o gamă largă de servicii ecosistemice. Ea integrează spații
verzi (sau acvatice, în cazul ecosistemelor de acest tip) și alte elemente fizice ale zonelor terestre
(inclusiv de coastă) și ale celor marine. Pe uscat, infrastructurile ecologice sunt prezente atât în
mediul rural, cât și în cel urban.”
De asemenea, „soluțiile bazate pe infrastructurile ecologice sunt deosebit de importante în mediul
urban, care găzduiește peste 60 % din populația UE. Elementele infrastructurilor ecologice
prezente în orașe reprezintă avantaje pentru sănătate, cum ar fi aerul curat și o calitate mai bună a
apei. Ecosistemele sănătoase reduc de asemenea răspândirea maladiilor cu transmitere prin
vectori. Implementarea unor elemente ale infrastructurilor ecologice în zonele urbane creează un
simț al comunității mai accentuat, întărește legătura cu acțiunile voluntare întreprinse de
societatea civilă și contribuie la combaterea excluderii sociale și a izolării. Ele au un impact
benefic asupra cetățenilor și comunității, din punct de vedere fizic, psihologic, emoțional și socio-
economic. Infrastructurile ecologice permit conectarea zonelor urbane și a celor rurale și creează
medii de viață și (locuri) de muncă atractive. Prin intermediul producției de alimente în zona
urbană și al grădinilor comunitare, care reprezintă instrumente eficiente de educare a copiilor de
vârstă școlară și care captează în special interesul tinerilor, infrastructurile ecologice acoperă
decalajul existent între producția și consumul de alimente și contribuie la sporirea valorii
percepute a acestora. Investițiile în infrastructurile ecologice au un potențial semnificativ de
consolidare a dezvoltării regionale și urbane, mai ales prin menținerea sau crearea de locuri de
muncă”.
În întregul context amintit, Asociația pentru Promovarea Valorilor Naturale și Culturale ale
Banatului și Crișanei ”Excelsior” propune încheierea unui acord de parteneriat care să aibă ca
obiective:
(1) Dezvoltarea unei Strategii pentru infrastructură ecologică, verde în Municipiul Timișoara,
(2) Dezvoltarea unei Rețele de infrastructură ecologică, verde,
(3) Dezvoltarea, implementarea în parteneriat a unui proiect în cadrul Programului Operațional
Capacitate Administrativă (POCA), pentru a veni în sprijinul inițiativei de realizare a strategiei
pentru infrastructură verde și a rețelei TEN-G (Trans-European Network for Green Infrastructure).
În vederea atingerii acestor obiective, Asociația „Excelsior” propune celor două părți implicarea
resurselor proprii pentru desfășurarea activităților precum și încheierea unui acord de parteneriat
ferm care să definească responsabilitățile în atingerea obiectivelor propuse.
Având în vedere interesul municipalității în implementarea măsurilor și acțiunilor aprobate prin
Planului strategic pentru protejarea şi conservarea biodiversităţii, de implementare a unor soluții
naturale, pentru furnizarea de servicii ecosistemice și încurajarea utilizării infrastructurilor
ecologice, propunerea Asociației „Excelsior” de încheiere a unui acord de parteneriat în domeniul
infrastructurii ecologice, verzi reprezintă o oportunitate pentru ambele părți, municipalitatea
extinzându-și aria de colaborare cu organizații specializate în protecția mediului, în domenii de
interes comun și de a aborda și realiza proiecte noi în folosul comunității.
Cod FO-53-01, Ver.2
În conformitate cu prevederile art.36 alin.2 lit.(e) din Legea nr.215/2001 privind administraţia
publică locală, cu modificările și completările ulterioare, consiliul local exercită atribuţii privind
cooperarea interinstituţională pe plan intern şi extern. De asemenea, conform prevederilor art.36,
alin.(7), lit.a), din Legea nr.215/2001, consiliul local hotărăşte asocierea cu persoane juridice
române sau străine în vederea finanţării şi realizării în comun a unor acţiuni, lucrări, servicii sau
proiecte de interes public local.
Având în vedere cele expuse mai sus, PROPUNEM:
1. Aprobarea inițiativei de încheiere a unui Acord de parteneriat între Municipiul Timişoara şi Asociația pentru Promovarea Valorilor Naturale și Culturale ale Banatului și Crișanei ”Excelsior”,
în domeniul Infrastructurii ecologice, verzi;
2. Aprobarea împuternicirii Domnului Primar Nicolae ROBU să semneze Acordul de parteneriat din anexă.
VICEPRIMAR,
Dan DIACONU
DIRECTOR EXECUTIV DIRECȚIA DE MEDIU, Resp. BIROUL MONITORIZARE ȘI
PROTECȚIE MEDIU,
Adrian – Amedeo BERE – SEMEREDI Adina PANC
CONSILIER, SERVICIUL JURIDIC,
Iudit BERE - SEMEREDI
Red./Dact. BSI, Ex.2
Cod FO-53-01, Ver.2
SC2016- /___.___.2016.
ACORD DE PARTENERIAT nr. ______ din data de ___/ ___/2016
1. PĂRŢILE
1.1. MUNICIPIUL TIMIŞOARA, cu sediul în Timişoara, B-dul C. D. Loga nr.1, Judeţul Timiş, cod poştal 300030, E-mail: [email protected], Pagina web: www.primariatm.ro,
reprezentat prin Domnul Nicolae ROBU în calitate de Primar al Municipiului Timișoara, Cod Fiscal
14756536, Telefon/Fax: 0256/408451, pe de o parte
şi
1.2. Asociația pentru Promovarea Valorilor Naturale și Culturale ale Banatului și Crișanei ”Excelsior”, denumită în continuare Asociția „Excelsior”, cu sediul în Arad, Strada Suceava nr.18,
cod poștal 310465, Județul Arad, CIF 18483684, Telefon: 0257210192, Fax: 0257210192,
0357780026, Mobil: 0745608905, E-mail: [email protected], Web: www.ongexcelsior.ro,
www.infrastructuraverde.ro, reprezentată prin Domnul Mihai – Sorin PASCU în calitate de
Președinte, pe de altă parte
În conformitate cu prevederile Hotărârii Consiliului Local al Municipiului Timișoara nr.
___/___.___.2016, convenim să încheiem prezentul Acord de Parteneriat
2. OBIECTUL
2.1. Prezentul acord de parteneriat are ca obiect colaborarea și dezvoltarea în comun a unor
acțiuni și activități pentru studiul și dezvoltarea rețelei pentru infrastructură ecologică, verde (Green
Infrastructure – GI) în Municipiul Timișoara.
2.2. Obiectivele acordului de parteneriat sunt următoarele: a) Dezvoltarea unei Strategii pentru infrastructură ecologică, verde (Green Infrastructure – GI) în
Municipiul Timișoara,
b) Dezvoltarea unei Rețele de infrastructură ecologică, verde (Green Infrastructure – GI),
c) Dezvoltarea, implementarea în parteneriat a unui proiect în cadrul Programului Operațional
Capacitate Administrativă (POCA), pentru a veni în sprijinul inițiativei de realizare a strategiei
pentru infrastructură verde și a rețelei TEN-G (Trans-European Network for Green Infrastructure).
3. DURATA ACORDULUI, INTRAREA ÎN VIGOARE
3.1. Prezentului acord se încheie pe o perioadă de 24 de luni calendaristice, cu posibilitate de
prelungire cu acordul părților, până la atingerea obiectivelor parteneriatului.
3.2. Prezentul acord intră în vigoare la data semnării sale de către ambele părţi.
4. OBLIGAŢIILE PĂRŢILOR:
4.1. Ambele părţi se obligă să colaboreze şi să susţină derularea în bune condiții a acordului, prin
furnizarea de expertiză şi resurse umane pentru activităţile de care sunt responsabile, activităţi şi
responsabilităţi stabilite de comun acord, în funcţie de obiectul acestora.
4.2. MUNICIPIUL TIMIȘOARA se obligă:
a) Să asigure comunicarea și schimbul de informații cu Asociația „Excelsior”, asigurând pe întreaga derulare a acordului de parteneriat o persoană de contact din cadrul Direcției de Mediu a
Primăriei Municipiului Timișoara;
b) Să pună la dispoziția specialiștilor Asociației „Excelsior” informațiile publice relevante de care dispune la momentul semnării acordului de parteneriat și a informațiilor de care va beneficia în
viitor, pe baza cererilor formulate de către asociație;
ROMÂNIA
JUDEȚUL TIMIȘ
MUNICIPIUL TIMIȘOARA
B-dul C.D. Loga nr.1
Cod FO-53-01, Ver.2
c) Să asigure participarea reprezentanților Primăriei Municipiului Timișoara la elaborarea ”Strategiei pentru infrastructură verde (Green Infrastructure - GI) a Municipiului Timișoara”;
d) Să asigure participarea reprezentanților Primăriei Municipiului Timișoara la stabilirea ”Rețelei de infrastructură verde (Green Infrastructure - GI) a Municipiului Timișoara;
e) Să elaboreze și să supună dezbaterii publice, analizei și hotărârii Consiliului Local al Municipiului Timișoara documentele privitoare la ”Strategia pentru infrastructură verde a
Municipiului Timișoara” și la ”Rețeaua de infrastructură verde a Municipiului Timișoara”
f) Să nu folosească materialele elaborate în cadrul parteneriatului fără acordul/recenzia partenerului;
g) Să organizeze în parteneriat evenimente, cursuri, ateliere de lucru și alte asemenea evenimente în domeniul infrastructurii verzi;
h) Să promoveze interesele Asociației „Excelsior” ȋn vederea creșterii prestigiului național și internațional, prin elaborarea de materiale, diseminarea de informații prin canalele proprii de
comunicare, evenimente, prezentări, etc.;
4.3. Asociația pentru Promovarea Valorilor Naturale și Culturale ale Banatului și Crișanei ”Excelsior” se obligă:
a) Să asigure legătura cu Primăria Municipiului Timișoara, în persoana președintelui asociației, Biolog Mihai - Sorin PASCU;
b) Să asigure specialiștii necesari pentru desfășurarea tuturor activităților, în vederea atingerii obiectivelor acordului de parteneriat;
c) Să asigure baza/suportul informațional cu privire la politicile europene și naționale în domeniul infrastructurii verzi;
d) Să dezvolte metodologia de lucru necesară pentru evaluarea și desemnarea infrastructurii verzi;
e) Să desfășoare studiile în teren cu specialiștii proprii; f) Să dezvolte cu specialiștii proprii propunerea/proiectul de ”Strategie pentru infrastructură verde a Municipiului Timișoara”, cu participarea și consultarea reprezentanților Primăriei
Municipiului Timișoara;
g) Să dezvolte cu specialiștii proprii propunerea/proiectul privind ”Rețeaua de infrastructură verde a Municipiului Timișoara”, cu participarea și consultarea reprezentanților Primăriei
Municipiului Timișoara;
h) Să dezvolte cu specialiștii proprii aplicația de proiect în cadrul Programului Operațional Capacitate Administrativă (POCA), cu participarea și sprijinul reprezentanților Primăriei
Municipiului Timișoara.
i) Să nu folosească materialele elaborate în cadrul parteneriatului fără acordul/recenzia partenerului;
j) Să organizeze în parteneriat evenimente, cursuri, ateliere de lucru și alte asemenea evenimente în domeniul infrastructurii verzi;
k) Să promoveze interesele Municipiului Timișoara ȋn vederea creșterii prestigiului național și internațional, prin elaborarea de materiale, diseminarea de informații prin canalele proprii de
comunicare, evenimente, prezentări, etc.;
5. MODALITĂŢI DE ÎNCETARE A CONTRACTULUI 5.1. Prezentul acord de parteneriat încetează:
a) Prin acordul ambelor părţi, b) Încălcarea în mod culpabil de către una dintre părţi a obligaţiilor asumate.
6. CONFIDENŢIALITATE
6.1. Părţile convin să păstreze confidențiale informaţiile primite şi sunt de acord să prevină orice
utilizare sau divulgare neautorizată a unor astfel de informaţii.
6.2. Informaţiile confidenţiale vor fi folosite de părţi numai în scopul executării unor contracte şi
vor putea fi dezvăluite numai persoanelor implicate în executarea contractului.
Cod FO-53-01, Ver.2
7. CLAUZE SPECIALE
7.1. Activităţile concrete din cadrul parteneriatului vor fi realizate pe baza consultării şi
acordului reciproc al celor două părţi.
7.2. Realizarea activităţilor va depinde de existenţa resurselor materiale, financiare şi umane de
care dispune fiecare parte.
7.3. Modificarea prezentului acord se va face prin act adiţional încheiat între părţi. Partea care
are iniţiativa modificării prezentului acord va transmite celeilalte părţi, în scris, spre analiză,
propunerile sale.
7.4. Prezentul acord de parteneriat are caracterul unui acord cadru. Acordul cadru va fi
completat, după caz, cu contracte de colaborare specifice pentru activitatea/proiectul/inițiativa
convenită de părți.
8. NOTIFICĂRI
8.1. Orice notificare/corespondenţă adresată de o parte celeilalte părţi este valabil comunicată
dacă este predată sau transmisă la adresa menţionată în partea introductivă a prezentului acord de
parteneriat.
8.2. În cazul în care notificarea/corespondenţa va fi transmisă prin poştă, se va face prin
scrisoare recomandată, cu confirmare de primire şi se consideră primită de destinatar la data
menţionată de oficiul poştal primitor pe această confirmare.
8.3. Schimbarea adresei nu este opozabilă celeilalte părţi decât dacă a fost notificată cu cel puţin
5 zile lucrătoare înainte.
9. LITIGII
9.1. Părţile se vor strădui, de bună credinţă, să rezolve pe cale amiabilă eventualele litigii,
controverse sau diferende apărute din sau în legătură cu acest acord.
9.2. În cazul în care nu se ajunge la o soluţie pe cale amiabilă, litigiile, controversele, diferendele
se vor înainta spre soluţionare instanţelor judecătoreşti competente.
10. DISPOZIŢII FINALE 10.1 Prezentul acord constituie un document cadru de colaborare între părţi, în vederea realizării
obiectivelor propuse, putând fi completat sau modificat prin înţelegerea părţilor.
Prezentul Acord s-a încheiat şi semnat de ambele părţi, la Timişoara, astăzi _______________ în 2
(două) exemplare originale, câte unul pentru fiecare parte.
MUNICIPIUL TIMIŞOARA Asociația pentru Promovarea Valorilor Naturale
și Culturale ale Banatului și Crișanei ”Excelsior”
PRIMAR, PREȘEDINTE,
Nicolae ROBU Mihai – Sorin PASCU _______________________ _______________________
(semnătura) (semnătura)
L.s.
L.s.
VICEPRIMAR,
Dan DIACONU
_______________________
(semnătura)
DIRECTOR EXEC. DIRECŢIA DE MEDIU,
Adrian – Amedeo BERE - SEMEREDI
_______________________ (semnătura)
SERVICIUL JURIDIC,
_______________________ (semnătura)