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Background note - Europa · Background note Summary of linkages between NWRM and CAP post 2014...
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Background note Summary of linkages between NWRM and CAP post 2014
Benoît Fribourg-Blanc (OIEau), Dennis Collentine (SLU), Alistair McVittie (SRUC), Pierre Strosser
(ACTeon)
March 3, 2014, Version for WG Floods
Background
Attention has been given in recent years to the role so-called Natural Water Retention Measures
(NWRM) could play in supporting the achievements of different European Union (EU) Directives, and
in particular the Water Framework Directive (WFD) and the Floods Directive (FD). In particular, the
“Blueprint to Safeguard Europe’s Water Resources” recommends the implementation of these
measures. In addition to being considered as measures under the WFD River Basin Management
Plans (RBMP), the Blueprint suggests that NWRM should become a priority for financing under the
Common Agricultural Policy (CAP) (as well as under the European Structural and Investment Funds
(ESIF))
The present note aims at initiating discussions within the Floods Working Group (WG) on the
potential role of NWRM in flood risk management. The note includes:
1. An overview of what NWRM are.
2. A briefing on the conclusions from the Regional Workshops conducted by the project and main
project findings so far in relation to measures that relate to flood risk management (practices
or land use).
3. The potential for financing NWRM through European Structural and Investment Funds (ESIF)
and the CAP which includes a review of the proposals for the CAP post 2014 that identifies
potential mechanisms which could promote Natural Water Retention Measures (NWRMs).
This review was undertaken through a comparison of the articles of Regulations 1305/2013
(support for rural development, i.e. Pillar II) and 1307/2013 (rules about direct payments, Pillar
I). A draft list of measures under annex 1 of the Rural Development Fund was also reviewed to
identify specific measures of relevance to NWRMs.
4. A series of key questions relevant to the NWRM-flood risk management policy links for
steering discussions within WG Floods. The feedbacks and answers to these questions will help
guide the NWRM project in building a knowledge base that can effectively support future
design and implementation of NWRM in Europe.
Background note for WG Floods
-2-
5. Appendices with summaries of regional case studies for NWRM and tables presenting the links
between NWRM measures and CAP Regulation Articles.
1. NWRM: what are they1?
A working definition of NWRM specifies that Natural Water Retention Measures aim at restoring and
maintaining water related ecosystems by natural means. They are Green Infrastructures intended to
maintain and restore landscape, soils and aquifers in order to improve their natural properties, the
environmental services they provide, and to favour climate change adaptation and reduced
vulnerability to floods and droughts.2
NWRM include a wide range of measures that combine (1) direct interventions in water-
related ecosystems (e.g. restoration/creation of floodplains or the development of
basins/ponds to store runoff) and (2) adaptation or change in land-use practices (e.g. the
development of green roof, afforestation or soil conservation crop practices) so functions of
modified ecosystems are (partially) recovered.
NWRMs use or enhance natural processes, i.e. functions commonly performed by nature
such as slowing down water flows, increasing infiltration rates, controlling storm flows,
storing water, storing and degrading polluting substances, etc.
NWRM are multi-purpose measures: by enhancing the capacity of soils and water-
dependant ecosystems to retain water, nutrients and sediments, they can contribute to the
achievement of different EU environmental Directives and initiatives, i.e. the WFD and the
FD as indicated above, but also the Habitats Directive, the EU Biodiversity Strategy, climate
change adaptation or Water Scarcity and Drought.
Box 1. NWRM: a wide umbrella for many existing measures?
The measures classified as NWRM are not new to operators in the field of nature conservation, agriculture, forestry or
urban development. Depending on your country and/or sector, you might be more familiar with:
Natural flood management, Sustainable Flood Management, Runoff attenuation features, Sustainable Drainage Systems
(either rural or urban or both), Green Infrastructures, Bioengineering, Ecologic Engineering applied to water, Catchment
System Engineering, Soil & Water conservation practices, Decentralised water management measures, No-regret
measures....
... and probably many more! However, more important than the term used, is the focus on maintaining or restoring
natural processes to support the delivery of (ecosystem) services that can respond to a wide range of purposes and EU
policy objectives.
NWRM which restore and enhance water retention can have an effect on both water quality, water
quantity and soil erosion. Measures in rural (in agriculture and forested areas) and urban
environments can provide seasonal storage capacity and reduce the risk for water scarcity, reduce
1 Fore more information on NWRM, consult the concept note written by NWRM partners :
http://nwrm.eu/ressource/concept-note-natural-water-retention-measures 2 Also see http://ec.europa.eu/environment/water/adaptation/ecosystemstorage.htm ; a final definition will
be agreed in WG PoM.
Background note for WG Floods
-3-
nutrient losses and support increased recreation and biodiversity. Investment in retention by
providing temporary storage in the landscape can also reduce the impact of extreme events (floods
and droughts).
2. Findings from regional workshops3
In January 2014 workshops were held in each of the four regions delineated by the NWRM project
(Baltic, Danube, Mediterranean and Western) which brought together members of the project team
with a range of regional experts including academics, environmental agencies and regional and
national governments. The four regional workshops reached some common conclusions on the
application of NWRMs. Most recognised the interlinkages between different Directives (WFD, FD,
Habitats, Birds) that are driving use of NWRMs (or potential NWRM type measures). However this
recognition is often not incorporated into applications, and it was felt that NWRM would achieve the
greatest benefits where multiple outcomes were targeted. The restrictive focus of some Directives
(e.g. WFD and ‘water bodies’) was seen as a potential hindrance and a catchment level approach
was felt to be necessary. Likewise, sectoral boundaries (agriculture, forestry, urban, natural) may not
be helpful for effective implementation. The use ecosystem services as a framework and
identification of positive economic and other benefits of NWRM was seen as key to successful
implementation. The organisation of the project across different regions allows for taking into
account the particular contexts and issues within those regions and how those influence water
management priorities and thus the requirements for NWRMs. Summaries of some of the case
studies presented at the regional workshops are provided in Annex 1.
Discussions in the Baltic region workshop emphasised that agricultural NWRM are often put in place
for reasons other than water retention, for example water quality (specifically nutrient loads) in the
case of catch crops, buffer strips and wetlands; or for climate change mitigation in the case of
peatland restoration. These then have the secondary benefit of increasing water storage within the
landscape. One presenter pointed out the important role that the role of extensive forest cover in
Europe plays by providing hydrological and water quality regulating services. It was also pointed out
that since forests are often upstream of agricultural, urban and flood risk areas there is also a role
for using NWRM in these areas to reduce hydrological pressures downstream. The issue of flooding
in some of the Baltic region countries was more concerned with meltwater from snow rather than
rainfall, with the consequence that the periods of highest flood risk are often concentrated. In
Estonia a case where there are problems with stormwater and snow melt leading to flooded urban
areas and beach erosion. To mitigate these problems Sustainable Urban Drainage Systems (SUDS)
that are NWRMs such as rain gardens, open vegetated drains, dry infiltration basin and system of
ditches and a cobblestone stripe have been introduced. Both agriculture and forestry were
recognised to have contributed to significantly reducing the amount of water retention in the
landscape through drainage.
The Baltic experience contrasts with that of the Western region where much of the understanding
and experience of NWRMs centred around ‘natural flood management’. The region is characterised
3 For more information on regional Workshops see: http://nwrm.eu/first-baltic-region-workshop
http://nwrm.eu/first-danube-region-workshop; http://nwrm.eu/first-mediterranean-region-workshop; http://www.nwrm.eu/first-western-region-workshop
Background note for WG Floods
-4-
on the whole by a relatively wet and mild climate. However problems with water scarcity are also
present, and this may become increasingly prevalent with climate change. Therefore NWRM could
have an increasingly important role to play in helping to regulate the hydrological cycle, in terms of
managing both flood peaks and dry periods. NWRM implementation was also of interest to
workshop participants in relation to river restoration, biodiversity improvements (habitat
restoration) and water quality improvements (sediment management and other aspects of diffuse
pollution control).
Insightful presentations were given workshop participants of their own experiences with NWRM
implementation. This understanding and experience was very focussed on Natural Flood
Management (NFM): while wider benefits of NWRM were well recognised, they were generally not
the main aim or purpose of existing cases of practical implementation.
Catchment-scale implementation of measures was of interest, with selection and placement of
multiple measures in the catchment likely to be important for their overall effectiveness. The case
study presentations (Appendix 1) were mostly based at the catchment-scale and looked at
cumulative benefits from multiple measures. Intensive monitoring networks such as in the
Eddleston Water and Belford catchment examples allowed the cumulative effects to be monitored
throughout the catchment. The placement of measures in the catchment could make a difference to
their effectiveness
One difficulty recognised with cost-benefit assessment of these types of measures is that those who
receive the benefits are not necessarily the same as those who incur the costs: in many cases, it may
be ‘private cost for public benefit’. While multiple benefits were seen as being key to the definition
of NWRM, the wide spread of benefits may make it challenging to identify and incentivise key
parties sitting within a single sector or policy area. There is a risk of NWRM being seen as a burden
rather than an opportunity for those with key roles in implementing them. Partnership working to
see benefits cumulatively and collaboratively was seen as being very important for successful
implementation on NWRM. The need to develop partnerships and get funding in place contributes
to relatively long planning timescales.
The necessity for clarifying links to WFD, which are often less evident than the links to the Floods
Directive, was recognised during discussions throughout the workshop. In the Water Framework
Directive context it was felt that the outputs from the NWRM pilot project, and these types of
measures, were likely to be more relevant for third cycle river basin plans, with not enough time
before the second cycle plans.
The spatiotemporal rainfall and runoff variability shapes the particularities of the Mediterranean
region in terms of water resources availability and distribution. Mediterranean rivers have large
periodic floods, transporting significant amounts of sediments, shaping braided channels, while
many streams are intermittent or ephemeral. These rainfall and runoff patterns concur with the
intensive use of water resources, mostly in agriculture, in some cases due to a quite complex system
of dams and reservoirs, part of which have induced significant hydromorphological alterations.
Downstream reaches are commonly deprived of high flows, which carry sediments, modify channel
morphology, and maintain habitat complexity. The fact that drought events are becoming more
frequent in the Mediterranean basins, where the average annual demand of water is already higher
Background note for WG Floods
-5-
than the long-term renewable resources (i.e. availability), has led to an increased uncertainty about
the reliability of water supply exacerbated by climate change. However, not everything is about
scarcity and droughts in the Mediterranean. Torrential rains are common in Mediterranean
catchments, which lead to hazards of flash floods, stream flooding, and landslides.
River and floodplain restoration contribute to natural water retention in different ways: improving
(3D) eco-hydrological connectivity, increasing the heterogeneity of river environments, enhancing
the role of natural habitats as traps for water and sediments, improving the functionality of the flow
regime to contribute to good status of rivers and floodplains, and supporting public awareness about
the vital role of natural water retention for people. For urban areas, floodplain restoration, wetland
preservation or creation, or urban channel restoration can be seen as likely practices
In urban areas wetland systems for Combined Sewer Overflow on-site treatment, as well as other
SUDS for stormwater management have been used in Italy. Mixed sewers represent the most
adopted solution for the collection of untreated wastewater: the high flux of water eases the
transport of solids and the washout of sediments at every rain event. The relevance of green
infrastructures was pointed out for stormwater management, to increase the water quality in the
receiving water bodies, to take account of public health concerns, and to mitigate flooding risk.
In the Danube region there was recognition of the role of NWRMs with respect to both the WFD and
FD. An important question brought up at the workshop was where to retain water in the system;
upstream areas were generally more rural while urban areas are often downstream. In mountainous
areas NWRM can be important to hold and slow down the movement of water to downstream
urban areas. Upstream river restoration, wetlands and urban measures were all pointed out as
NWRM. In addition, the extensive Danube river system the potential for floodplain restoration was
discussed as an important measure to mitigate flooding in urban areas. There was also explicit
mention of the importance of navigation which was not represented in the workshop agenda.
3. How can ESIF financing and the future CAP support the implementation of NWRM?
Two of the opportunities for financing RBMP measures are through ESIF (partnership agreements)
and the proposed CAP post 2014. EU investment through ESI funds is targeted on long-term goals for
growth and jobs and sustainable development. In the CAP measures may be supported through
Pillar I greening measures and through Pillar II national rural development programs.
ESI funds include the European Regional Development Fund (ERDF), the Cohesion Fund (CF), the
European Agricultural Fund for Rural Development (EAFRD), the European Social Fund (ESF) and the
European Maritime and Fisheries Fund (EMFF). Two of the eleven ESIF thematic objectives related to
sustainable growth are applicable for NWRM;
promoting climate change adaptation, risk prevention and management
and protecting the environment and promoting resource efficiency.
The first of these makes it possible to support measures that promote dedicated investment for
adaptation to climate change and include preserving natural areas, biodiversity, ecosystem services,
water quality and quantity. In addition investments that address ensuring disaster resilience also
have a high priority. Under the second theme above it is also possible to support implementation of
Background note for WG Floods
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RBMPs and FRMPs through investment in green infrastructure including among others floodplains,
river-restoration and wetlands.
The articles contained in the Regulations make either explicit mention of measures that have been
categorised as NWRMs or the link may be implied in the objectives of the articles. However, their
effectiveness as NWRMs is likely to be dependent on the priorities of Member States. As measures
may provide multiple benefits (e.g. nature conservation, nutrient management, climate mitigation)
their implementation may vary depending on the emphasis placed on different rural development
objectives.
Tables 1 and 2 below present alternative matrices showing the links made between NWRMs and the
Articles of Regulations 1305/2013 and 1307/2013.
2.1 Articles related to Pillar I
Regulation 1307/2013 is primarily concerned with the rules covering direct payments to farmers;
consequently there is limited scope for direct links with NWRMs. However, the new CAP includes
new payments for agricultural practices beneficial for the climate and the environment (i.e.
‘greening’ measures); these measures involve a proportion of Pillar I funding and go beyond existing
cross-compliance conditions4. Uptake of these measures will be necessary for farmers to maximise
their payments under Pillar I.
The ‘greening’ measures include crop diversification, permanent pasture and ecological focus areas,
with last two of these being potentially relevant for NWRMs (see following paragraphs). Article 43
sets out general rules for these measures including reference to Annex IX of Regulation 1307/2013
which outlines equivalent practices which may provide an equivalent or higher level of environment
benefit. Article 44 on crop diversification makes no direct or indirect link to NWRMs; however,
relevant equivalent practices (e.g. winter cover and catch crops, which are analogous to the NWRM
‘green cover’) are referred to in paragraphs 3 and 12 of Article 43.
Article 45 covers permanent pasture, specifically the requirement that its extent in each member
state or region should not decrease by more than 5%. Together with equivalent practices on the
management of permanent pastures, this article directly relates to the NWRM ‘Restoring and
maintaining meadows and pastures’. It also links to several forestry NWRMs as the 5% threshold
does not apply where the reduction in permanent pasture is the result of afforestation as indicated
in tables 1 and 2.
Article 46 covers ecological focus areas, which should form at least 5% of the arable area of any
holding. Features listed under this article and the equivalent measures are directly related to a
number of NWRMs including ‘buffer strips’, ‘field margins’, ‘green cover’, ‘traditional terracing’ and
‘beetle banks’ A broader range of rural SuDS measures could be also be included as ecological focus
areas whether as specific measures or in terms of the design of equivalent measures, however these
are not currently addressed in the guidelines.
4 Cross-compliance via good agricultural and environmental condition (GAEC) requirements may indirectly involve NWRMs
for example through soil protection requirements.
Background note for WG Floods
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2.2 Articles and measures related to Pillar II
Article 5 of Regulation 1305/2013 sets out the priorities for rural development and as such makes
implicit reference to the use of NWRM. Paragraph 4 is directly relevant and concerns ‘restoring,
preserving and enhancing ecosystems related to agriculture and forestry’ with a focus on a)
restoring, preserving and enhancing biodiversity; b) improving water management; and c)
preventing soil erosion and improving soil management. NWRMs can deliver these objectives either
as primary or secondary aims. Paragraph 5 indirectly relates to NWRMs through ‘promoting resource
efficiency and supporting the shift towards a low carbon and climate resilient economy in
agriculture, food and forestry sectors’. In this case actions aimed at carbon sequestration or storage
may provide also water retention benefits.
There are a number of key articles that relate to rural development support measures that are of
direct relevance to NWRMs. Agri-environment support is covered by Article 28 ‘Agri-environment-
climate’ which relates to ….. Forestry NWRMs are covered by several articles relating to afforestation
and the establishment of agro-forestry (Articles 21, 22 and 23), the resilience of the environmental
value of forest ecosystems (Article 25) and support for environment-climate commitments (Article
34). Forests are also mentioned with respect to Articles 17 and ‘Investments in physical assets’ and
Article 20. ‘Basic services and village renewal in rural areas’. These articles also have potential links
to ‘Nature’ NWRMs, as does Article 30 ‘Natura 2000 and WFD payments’, as they allow for non-
productive investments and actions for environmental objectives such as biodiversity and habitat
conservation that might include elements of NWRMs.
There are a number of articles that can be indirectly linked to NWRM as supporting actions. These
are important in the ensuring the delivery of NWRM objectives but do not relate to specific
measures. These include Article 35 on co-operation that might be necessary to encourage joint
implementation across farm holdings within a catchment. Articles 36 to 39 on risk management,
crop and animal insurance, mutual funds and income stabilisation, these might be relevant where
NWRMs involve the potential flooding of farmland (e.g. floodplain restoration and reconnection) in
order to encourage implementation of such measures.
Training, advice and dissemination of good practice will be important for successful implementation
and uptake of NWRMs. These are addressed across a number of scales by several articles. Local level
action can be supported by LEADER funding (Articles 42, 43 and 44). National or regional support
networks are covered by Articles 51 and 54. EU level networks and partnerships are covered by
Articles 51, 52 and 53; the last of these covers the establishment of a European Innovation
Partnerships (EIP), the aims, operation and tasks of EIPs are covered by Articles 55, 56 and 57.
Background note for WG Floods
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4. Key issues and questions for WG Floods
Initial suggestions
What are the key issues and challenges faced when implementing flood risk management
NWRM?
Which opportunities are available for financing the implementation of NWRM, for example
under the new CAP?
Which additional measures could be included as NWRM measures? From a flood risk
management point of view, which main features do all these measures share?
What type of knowledge should be produced by the NWRM project for supporting the
design and implementation of flood risk related NWRM in different MS? And which issues
should receive specific attention in the practical guide5 that will be developed under the
project?
What is the best way to mobilise stakeholders in the networks and workshops organised in
different regions (Baltic, Danube, Mediterranean, Western Europe)? What specific initiatives
should the NWRM project establish synergies with for the development of sound knowledge
on flood risk management measures and effective dissemination of the project results?
5 The practical guide aims at supporting the design and implementation of NWRM. Its target audience includes staff from
relevant authorities, experts and stakeholders directly involved in the planning and implementation of NWRM in the context of the implementation of the WFD, of the Floods Directive, and of strategies for climate change adaptation, sustainable agriculture and forestry, or sustainable urban development. The guide will facilitate the access to, and use of, the knowledge available in the NWRM database/collaborative knowledge system. It will be developed in English, and then translated (main text) in all EU languages. The practical guide will be developed in both paper and electronic formats, the electronic version being fully integrated into the knowledge platform developed under the project.
http://www.nwrm.eu
Appendix 1 Table 1 Case study presentations from the first NWRM Pilot Project Western region workshop (Jan 2014)
Natural Flood Management in Scotland
Roy Richardson, SEPA (UK)
Summary of case study: This presentation described the approach
being taken in Scotland to Floods Directive implementation. A full
review of flood risk management was undertaken, and an
integrated catchment-based approach, based on Natural Flood
Management (NFM), is being taken. National ‘opportunity maps’
have been produced, showing areas with potential for runoff
reduction, floodplain storage and sediment management. Four
NFM pilot catchments have been established (see Eddleston
Water presentation below). An NFM handbook will be produced
later this year.
Main driver: Floods Directive
Sustainable Drainage Systems in Northern
Ireland
Peter Close, NIEA (UK)
Summary of case study: Described a pilot study for the
implementation of sustainable stormwater management in the
town of Ballyclare, Northern Ireland, as well as aspirations for a
similar approach in the city of Belfast. The aim of the studies is to
re-direct stormwater out of the sewerage network and waste
water treatment plant, to reduce flooding and help improve water
quality. Retrofit solutions are proposed, as well as stringent
requirements for runoff management for all new developments.
Main driver: flood risk management
Dyke relocation on the River Elbe, Germany
Thomas Borchers, BMU (Germany)
Summary of case study: The main aim of this project was to
restore the floodplain habitats, which was brought together with a
more comprehensive plan incorporating flood benefits. The dykes
containing the River Elbe were to be relocated to allow flooding of
the floodplain. An extensive land consolidation process was
required. The original dykes were breached but not removed,
allowing a dynamic system to evolve over time. Modelling has
shown benefits to flood heights both upstream and downstream.
Main driver: Biodiversity and flood risk management
Background note for WG Floods
-10-
Natural Flood Management in Belford
catchment, England
Mark Wilkinson, James Hutton Institute (UK)
Summary of case study: natural flood management
scheme implemented as a more cost-effective
solution for addressing flooding problems in a small
town downstream. A network of runoff attenuation
features was developed in the upstream catchment,
in a predominantly agricultural area (pasture and
arable). Nested monitoring network allowed the
effectiveness of the measures to be assessed,
showing increased benefits from increased numbers
of measures, and the effects of different sizes of
rainfall events. Benefits to water quality were also
considered, with improved sediment management.
Working with stakeholders and taking time to
develop and implement a sustainable solution have
been important.
Main driver: flood risk management
Flood Mitigation by Forestry, Germany
Gebhard Schueler, Research Institute for
Forest Ecology and Forestry, Rheinland-Pfalz
(Germany)
Summary of case study: Test catchment used to
investigate effectiveness of forestry measures for
controlling runoff. Identification and control of
runoff generation in a forested headwater
catchment. Used a GIS-based system to identify
hotspots for runoff generation, and an inventory of
linear structures (that could accelerate runoff).
These allow prioritisation of appropriate locations
and types of measures. Runoff management
measures considered include a range of silvicultural
practices; road network design and management;
restoration of retention areas (e.g. wetland areas)
Main driver: flood risk management; climate change
Background note for WG Floods
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Appendix 2
Table 2 Matrix of links between NWRM measures (rows) and CAP Regulation Articles (columns)
Pillar I Pillar II a
Art
43
: Gen
eral
ru
les
Art
45
: Per
man
ent
pas
ture
Art
46
: Eco
logi
cal f
ocu
s ar
eas
Art
5: U
nio
n P
rio
riti
es f
or
Ru
ral
Dev
elo
pm
ent
Art
17
: In
vest
men
ts in
ph
ysic
al
asse
ts
Art
18
: Res
tori
ng
agri
cult
ura
l p
rod
uct
ion
po
ten
tial
dam
age
d b
y …
ca
tast
rop
hic
eve
nts
an
d
pre
ven
tati
ve a
ctio
ns
Art
20
: Bas
ic s
ervi
ces
and
vill
age
ren
ewal
in r
ura
l are
as
Art
21
: In
vest
men
ts in
fo
rest
are
a d
evel
op
men
t
Art
22
: Aff
ore
stat
ion
an
d c
reat
ion
of
wo
od
lan
d
Art
23
: Est
ablis
hm
ent
of
agro
fore
stry
sys
tem
s A
rt 2
4: P
reve
nti
on
an
d r
est
ora
tio
n
of
dam
age
to
fo
rest
s fo
rm f
ore
st f
irs
and
nat
ura
l dis
aste
rs a
nd
ca
tast
rop
hic
eve
nts
A
rt2
5:
Inve
stm
ents
imp
rovi
ng
the
resi
lien
ce a
nd
en
viro
nm
enta
l val
ue
of
fore
st e
cosy
stem
s A
rt 2
6: I
nve
stm
ents
in f
ore
stry
te
chn
olo
gies
an
d in
pro
cess
ing,
in
mo
bili
sin
g an
d in
th
e m
arke
tin
g o
f
fore
st p
rod
uct
s
Art
28
: Agr
i-en
viro
nm
ent-
clim
ate
Art
29
: Org
anic
far
min
g
Art
30
: Nat
ura
20
00
an
d W
FD
pay
men
ts
Art
s 3
1 &
32
: A
reas
fac
ing
nat
ura
l or
oth
er s
pec
ific
co
nst
rain
ts
Art
34
: Fo
rest
-en
viro
nm
ent
and
cl
imat
e se
rvic
es a
nd
fo
rest
co
nse
rvat
ion
Art
35
: Co
-op
erat
ion
Art
36
: Ris
k m
anag
em
ent
Art
37
: Cro
p, a
nim
al a
nd
pla
nt
insu
ran
ce
Art
38
: Mu
tual
fu
nd
s fo
r ad
vers
e cl
imat
ic e
ven
ts,…
an
d
envi
ron
men
tal i
nci
den
ts
Art
39
: In
com
e st
abili
sati
on
to
ol
Art
s 42
, 43
& 4
4: L
EAD
ER
Art
51
: Fu
nd
ing
tech
nic
al a
ssis
tan
ce
Art
52
: Eu
rop
ean
net
wo
rk f
or
rura
l d
evel
op
men
t
Art
53
: Eu
rop
ean
Inn
ova
tio
n
Par
tner
ship
net
wo
rk
Art
54
: Nat
ion
al r
ura
l net
wo
rk
Art
s 55
, 56
& 5
7:
EIP
fo
r ag
ricu
ltu
ral
pro
du
ctiv
ity
and
su
stai
nab
ility
Agr
icu
ltu
re
Restoring and maintaining meadows and pastures
Buffer strips
Field margins and headlands
Soil conservation crop practices: crop rotation
Soil conservation crop practices: strip cropping
Soil conservation crop practices: intercropping
No tillage
Reduced/conservation tillage
Green cover
Early sowing
Traditional terracing
Beetle banks
Hedgerows
Controlled traffic farming
Fore
stry
Afforestation of riparian areas
Afforestation of montane areas
Afforestation of reservoir catchments
Targeted planting in Mediterranean areas for “catching” precipitation
Forests as large-scale water pumps
Land use conversion for water quality improvement
Continuous Cover forestry
“Water sensitive” driving
Maintenance of riparian buffers
Appropriate design of roads and stream crossings
Sediment capture ponds
Coarse woody debris
Re-meandering of forestry-affected rivers
Urban forests
Riparian trees in agricultural landscape
Nat
ure
Basins and ponds
Wetland restoration and creation
Floodplain reconnection and restoration
Re-meandering
Revitalisation of flowing waters
Restoration of the flows of temporary tributaries
Reconnection of hydraulic annexes
Restoration of the riverbed (alluvial mattress)
Levelling of dams/ longitudinal barriers
Natural bank stabilisation
Elimination of riverbank protection
Restoration of lakes
Artificial groundwater recharge (AGR)
a Rural SuDS are currenlty omitted from the lists of Pillar II measures but will be added in subsequent revisions
Background note for WG Floods
-12-
Table 2 Matrix of links between NWRM measures (columns) and CAP Regulation Articles (rows)
Agriculture Forestry Nature
Re
sto
rin
g an
d
mai
nta
inin
g m
ead
ow
s an
d
pas
ture
s B
uff
er
stri
ps
Fie
ld m
argi
ns
and
h
ead
lan
ds
Soil
con
serv
atio
n
cro
p p
ract
ices
: cro
p
rota
tio
n
Soil
con
serv
atio
n
cro
p p
ract
ices
: str
ip
cro
pp
ing
Soil
con
serv
atio
n
cro
p p
ract
ices
: in
terc
rop
pin
g
No
till
age
Re
du
ced
/co
nse
rvat
io
n t
illag
e
Gre
en c
ove
r
Earl
y so
win
g
Trad
itio
nal
te
rrac
ing
Be
etl
e b
anks
He
dge
row
s
Co
ntr
olle
d t
raff
ic
farm
ing
Aff
ore
stat
ion
of
rip
aria
n a
reas
Aff
ore
stat
ion
of
mo
nta
ne
area
s
Aff
ore
stat
ion
of
rese
rvo
ir c
atch
men
ts
Targ
ete
d p
lan
tin
g in
M
ed
ite
rran
ean
are
as
for
“cat
chin
g”
pre
cip
itat
ion
Fo
rest
s as
larg
e-
scal
e w
ate
r p
um
ps
Lan
d u
se c
on
vers
ion
for
wat
er
qu
alit
y im
pro
vem
en
t C
on
tin
uo
us
Co
ver
fore
stry
“Wat
er
sen
siti
ve”
dri
vin
g
Mai
nte
nan
ce o
f ri
par
ian
bu
ffe
rs
Ap
pro
pri
ate
de
sign
o
f ro
ads
and
str
eam
cr
oss
ings
Se
dim
en
t ca
ptu
re
po
nd
s
Co
arse
wo
od
y d
ebri
s
Re-
me
and
eri
ng
of
fore
stry
-aff
ect
ed
rive
rs
Urb
an f
ore
sts
Rip
aria
n t
rees
in
agri
cult
ura
l la
nd
scap
e
Bas
ins
and
po
nd
s
Wet
lan
d r
est
ora
tio
n
and
cre
atio
n
Flo
od
pla
in
reco
nn
ect
ion
an
d
rest
ora
tio
n
Re-
me
and
eri
ng
Re
vita
lisat
ion
of
flo
win
g w
ater
s R
est
ora
tio
n o
f th
e
flo
ws
of
tem
po
rary
tr
ibu
tari
es
Re
con
nec
tio
n o
f
hyd
rau
lic a
nn
exe
s R
est
ora
tio
n o
f th
e ri
verb
ed (
allu
vial
m
attr
ess
) Le
velli
ng
of
dam
s/
lon
gitu
din
al b
arri
ers
Nat
ura
l ban
k st
abili
sati
on
Elim
inat
ion
of
rive
rban
k p
rote
ctio
n
Re
sto
rati
on
of
lake
s
Art
ific
ial
gro
un
dw
ate
r
rech
arge
(A
GR
)
Pil
lar
I
Art 43: General rules
Art 45: Permanent pasture
Art 46: Ecological focus areas
Pil
lar
II a
Art 5: Union Priorities for Rural Development
Art 17: Investments in physical assets
Art 18: Restoring agricultural production potential
Art 20: Basic services and village renewal in rural areas
Art 21: Investments in forest area development
Art 22: Afforestation and creation of woodland
Art 23: Establishment of agroforestry systems
Art 24: Prevention and restoration of damage to forests
Art25: Investments improving the resilience and environmental value of forest ecosystems
Art 26: Investments in forestry technologies
Art 28: Agri-environment-climate
Art 29: Organic farming
Art 30: Natura 2000 and WFD payments
Arts 31 & 32 : Areas facing natural or other specific constraints
Art 34: Forest-environment and climate services and forest conservation
Art 35: Co-operation
Art 36: Risk management
Art 37: Crop, animal and plant insurance
Art 38: Mutual funds for adverse climatic events,… and environmental incidents
Art 39: Income stabilisation tool
Arts 42, 43 & 44: LEADER
Art 51: Funding technical assistance
Art 52: European network for rural development
Art 53: European Innovation Partnership network
Art 54: National rural network
Arts 55, 56 & 57: EIP for agricultural productivity and sustainability
a Rural SuDS are currently omitted from the lists of Pillar II measures but will be added in subsequent revisions