Post on 15-Jan-2016
description
Management plans in the Schelde estuary
Harmonised?
Erika Van den BerghEstuaries and Coastal zones working groupBrussels 8/10/2008
Schelde River Basin district (SRBD)
Schelde-estuary
Very densely populatedDense transport networkPort of AntwerpIntensive agricultureFew nature conservation areas
Management plans
• International River basin district management (ISC-Scaldit)
• National Riverbasin management plans• Integrated Coastal zone management• Strategic planning for the Antwerp
Harbour• Long term Vision for the Schelde (LTVS)• Updated Sigmaplan• Natura 2000 management plan
Scales in Management plans: spatial
Scaldit
Natura 2000SIGMA
SPAH
LTVS
ICZM
Scales in management plans: issues
• Strategic planning:optimal multifunctional spatial planning in the harbour area
• Long term vision: integrated managementof the estuary: accessibility, safety, ecosystem health
• Updated Sigmaplan: Safety against floods
• Scaldit:WFD River Basin Management Plan (RBMP) Natura 2000 management plans: ecological network, habitats and species
Scales in Management plans: time frame
• Strategic planning: 1998-2000-2004
• Long term vision: 1999-2001-2004-2010
• Updated Sigmaplan: 2002-2005-2010-2015
• Scaldit:2001-2008• Natura 2000 management plans:
2007-
Scales in Management plans: initiative
• Strategic planning: Flemish administration & Port authorities
• Long term Vision: Dutch-Flemisch government (TSC)
• Updated Sigmaplan: administration of waterways
• Scaldit: (ISC-EA)• Natura 2000 management plans:
administration for nature and forest
Hierarchical integration of management goals & plans
Environmental quality (WFD)
Estuarine processes(LTVS)
Habitat network (BHD)quantity/connectivity
Habitat quality/type/species(local conservation goals)
• Riverbasin district
• Estuary
• Natura 2000 network
• Individual spa- sac
Ecosystem level
5 0 5 10 Ki l ometers
N
EW
S
Ramsar1976
Bird Directive1988
Habitat Directive1996
Strategic planning for Antwerp Harbour
• Start 1998• Issues: multifunctional spatial planning
• optimal space utilisation • phased port development • participation of stakeholders • maintenance of a functional ecological network• Implementation of BHD
• working groups with representation of all stakeholders: Province, communities, NGOs, administration, port authorities,……
Strategic planning for Antwerp Harbour
Strategic planning for Antwerp Harbour
• Updated principles 2004• Submitted to Spatial EIA, ongoing• Harmonisation: conservation goals
– Integrated for SPA and SAC– Habitat and species– Ranked and quantified
– Parts of SPA & SAC– Regional conservation goals and goals for
complete SPA and SAC area in estuary not finalised
– Ecosystem goals not finalised
Antwerpen
Gent
Vlissingen
Terneuzen
DurmeLokeren Rupel
Zenne
Dijle
Nete
Kleine Nete
Grote Nete
Dutch-Belgian border
Nor
th S
ea
Schelde
B
NL
GB
Het Schelde estuarium
LTVS 2030
Accessibility
Safety
Ecosystem health
Long term Vision For the Schelde LTVS)
• Dutch-Belgian managerial project (1999-2001)• Quality targets for 2030
1999-2001: Definition of vision 2030
“To develop a healthy, multifunctional watersystem, supporting human needs in a sustainable way”
1. Preservation of physical system characteristics2. Safety against floods3. Optimal accessibility for the ports4. Healthy and dynamic estuarine ecosystem5. Flemish-Dutch administrative-political
cooperation
Long term Vision For the Schelde (LTVS)
LTVS Harmonisation: Conservation goals
Current velocity
• Water- and habitat quality• Habitat area and sustainability• Foodweb under pressure
Phytoplankton
Zoöplankton
Benthos
Turbidity
Long term Vision: problem analysis
LTVS Conservation goals: problem analysis
Goal 01 V
lRaa
02 V
lHan
03 H
anG
r
04 G
rBur
05 B
urTm
06 T
mDe
m
07 D
emG
t
08 D
urm
e
09 Z
eDNe
10 s
trSc
Buffer discharge 0 0 0 0 + + ++ ++ ++ ++tidal energy dissipation + ++ ++ ++ ++ + + + + 0Multiple channelsystem 0 ++ ++ 0 0 0 0 0 0 0Optimise natural habitat processes ++ ++ ++ ++ ++ ++ ++ ++ ++ 0minimise turbidity 0 + + ++ ++ ++ + ++ + 0Optimise C cycle 0 0 0 0 0 0 0 0 0 ++Optimise N cycle 0 0 + + + ++ ++ ++ ++ ++Optimise O cycle 0 0 0 + ++ ++ + ++ + ++Optimise Pcycle 0 0 0 0 0 0 + + + ++Optimise Si cycle + ++ ++ ++ 0Optimise primary production 0 + + ++ ++ ++ + ++ + 0Optimise conditions for zooplankton 0 + + + ++ ++ ++ ++ ++ 0Optimise conditions for zoobenthos + ++ ++ ++ ++ ++ ++ ++ ++ 0Optimise fishmigration 0 + + + + + ++ ++ ++ ++Shallow low dynamic water + ++ ++ ++ ++ ++ ++ ++ ++ 0mudflats + ++ ++ ++ ++ ++ ++ ++ ++ 0Lower flats dynamics 0 ++ ++ 0 0 0 0 0 0 0Tidal marshes + ++ + + ++ + ++ + ++ 0Set back tidal marsh succession + ++ ++ ++ ++ ++ ++ 0 0 0Non-tidal wetland 0 0 0 + + + ++ + ++ 0
Code
Maatr
egel
buff
_afv
dis
p_E
turb
C N O2
P Si
prim
_pro
d
zoöpl
benth
os
vis
vogel
habitat
ond_H
2O
slik
schor
wetland
schor_
j
intg
et_
hd
intg
et_
ld
Grens - BurchtM2.1 Ontpolderen: doorlaatmiddel 0 1 1 1 1 0 1 1 2 1 2 2 2 2 1 0 2 0 1M2.2 Ontpolderen: dijk verwijderen 0 2 1 1 1 0 1 1 2 1 2 2 2 2 1 0 2 0 2M2.3 Ontpolderen: afgraven 1 1 0 1 1 1 1 1 1 1 1 2 2 1 1 2M2.4 Sluisbeheer: permanent 0 1 1 1 1 1 1 1 2 1 2 1 2 1 1 0 2 0 1M2.5 Sluisbeheer: occasioneel 1 2 2 2M4.1 Binnendijks natuurontwikkeling 1 1 ? 2 1 1
Burcht - TemseM1.09Schorfixatie: constructie 2 2 1 2 2M2.1 Ontpolderen: doorlaatmiddel 0 2 2 1 1 2 1 2 2 2 1 1 2 2 1 1 2 0 2M2.2 Ontpolderen: dijk verwijderen 0 2 2 0 1 2 1 2 2 2 1 2 2 2 1 1 2 0 2M2.3 Ontpolderen: afgraven 1 1 0 1 2 1 2 1 2 1 1 2 2 1 2 2M2.4 Sluisbeheer: permanent 0 1 1 1 1 2 1 2 2 2 1 1 2 1 1 1 2 0 2M2.5 Sluisbeheer: occasioneel 2 2 2 ? 2M4.1 Binnendijks natuurontwikkeling 1 1 ? 2 1 2M4.2 Binnendijks beheer 1 1 1
Temse - DendermondeM1.09Schorfixatie: constructie 2 2 1 2 2M2.1 Ontpolderen: doorlaatmiddel 1 2 2 2 2 1 2 2 2 2 2 2 2 1 2 2 0 2M2.2 Ontpolderen: dijk verwijderen 1 2 2 2 2 1 2 2 2 2 2 2 2 1 2 2 0 2M2.3 Ontpolderen: afgraven 1 2 2 2 2 1 2 2 2 2 2 2 2 1 2 2 0 2M2.4 Sluisbeheer: permanent 1 2 2 2 2 1 2 2 2 2 1 2 2 1 2 2 0 2M2.5 Sluisbeheer: occasioneel 1 1 1 1 1 1 1 0 0 0 1 1 2 1 0 0 2 0M3.1Natuurlijke overgang: herstel lateraal 0 1 1 1 1 1 1 1 1 1 2 1 2 2 1 1 0 1 0 1M3.4 Dijkverdediging met terrassen 2 2 1 2 2M3.5 Dijkbekleding natuurvriendelijk 2 2 1 2 2M4.1 Binnendijks natuurontwikkeling 1 1 1 ? 2 1 2M4.2 Binnendijks beheer 1 1 1
Dendermonde - GentM1.09Schorfixatie: constructie 2 2 1 2 2M2.1 Ontpolderen: doorlaatmiddel 2 1 1 2 2 1 2 1 2 2 2 2 2 1 2 2 0 2M2.2 Ontpolderen: dijk verwijderen 2 1 1 2 2 1 2 1 2 2 2 2 2 1 2 2 0 2M2.3 Ontpolderen: afgraven 2 1 1 2 2 1 2 1 2 2 2 2 2 1 2 2 0 2M2.4 Sluisbeheer: permanent 2 1 1 2 2 1 2 1 2 2 1 2 2 1 2 2 0 2M2.5 Sluisbeheer: occasioneel 2 0 0 1 1 1 1 0 0 0 1 1 2 1 0 0 2 0M3.1Natuurlijke overgang: herstel lateraal 0 1 1 1 1 1 1 1 1 1 2 1 2 2 1 1 0 1 0 1M3.2Natuurlijke overgang: herstel longitudinaal 2M3.4 Dijkverdediging met terrassen 2 2 1 2 2M3.5 Dijkbekleding natuurvriendelijk 2 2 1 2 2M4.1 Binnendijks natuurontwikkeling 2 1 1 ? 2 1 2M4.2 Binnendijks beheer 1 1 1M5.4 Vismigratie 2
LTVS Harmonisation: measures
Long term Vision for the Schelde (LTVS)
2002-2004: 2010 Development Outline (ProSes-TSC)
• Accessibility:– Deepening and widening of the shipping lane to Antwerp– Mitigation through adapted dumping & dredging strategy
• Flood control: – Space for the river where possible (FCA)– Dike elevation where necessary– Integration with ecological restoration
• Ecosystem health:– Tidal wetland creation – Inland wetland creation– Improvement for fish migration– Definition of specific and quantified conservation goals– SAC designation under the HD
• Cooperation:– Joint monitoring program to assess of the evolution of the estuary and effect of
measures to allow adaptive management
2005 – 2010:
- Schelde treaties for bilateral cooperation- EIA and CBA for each project- Implementation of measures - MONEOS: joint monitoring program
- Integrated for accessibility-safety-ecology - Ecosystem monitoring- Project monitoring- Incorporates EU and national legislation needs
Long term Vision For the Schelde (LTVS)
Long term Vision for the Schelde (LTVS)
2002-2004: 2010 Development Outline (ProSes-TSC)
• Accessibility:– Deepening and widening of the shipping lane to Antwerp– Mitigation through adapted dumping & dredging strategy
• Flood control: – Space for the river where possible (FCA)– Dike elevation where necessary– Integration with ecological restoration
• Ecosystem health:– Tidal wetland creation – Inland wetland creation– Improvement for fish migration– Definition of specific and quantified conservation goals– SAC designation under the HD
• Cooperation:– Joint monitoring program to assess of the evolution of the estuary and effect of
measures to allow adaptive management
Updated Sigmaplan
Conservation goals: Ecosystem functioning
• Minimum oxygen conditions for good biodiversity (benthos-fish) (J.Maes)– Summer: 5mg/l– Winter: 6mg/l
• Primary production under ‘good water quality conditions’ and under ‘pristine’ conditions* (Billen & Garnier; Cox & Maris)
• Benthic invertebrate production/m² under these primary production conditions* (Van Damme & Ysebaert)
• Habitat for benthos (mudflats) needed to support fish and bird populations* (Van Damme et al)
• Tidal marsh needed to prevent Si limitation under present water quality conditions* (Struyff)
• Geometrical requirements along the estuary for* sustainable tidal marshes/mudflats (Brys & Van den Bergh)
Conservation goals: Ecosystem functioning
Conservation goals: habitats
• Habitats of special interest (as habitat and for species of special interest) were ranked according to their relative importance– European: fresh water tidal, 91E0– Regional: Brackish tidal, 3150,6430,6510,7140– Local:2310, 2330,4030, 6410, 9120, 9160, 9190
• Qualitative and quantitative goals were set for each habitat type according to the flemish method (Heutz et al; 2005). – Environmental indicators for favourable conditions– Structural indicators for favourable conditions.
Conservation goals: species
• Species of special interest were ranked according to their relative importance:– European– Regional– Local
• Goals were specified for mammals, breeding birds, amfibians and reptiles, fish and migrating birds
Updated Sigmaplan: selection of measures
OptimalFlood control
plan
OptimalEcologic
Restoration plan
Importance of selected space for agriculture
Synthesis flood control and ecology: 3 scenario’s
Flood control Agriculture check Ecology check
Most desirable scenario for Updated Sigmaplan
Conservation goals
The Updated Sigmaplan: measures
• Flood control: – Space for the river where possible (FCA)– Dike elevation where necessary– Integration with ecological restoration
• Ecosystem health:– Tidal wetland creation – Inland wetland creation– Improvement for fish migration– Definition of specific and quantified conservation
goals
Flood control• Dike fortification
• Flood control area (FCA)
Updated Sigmaplan: Measures
Habitat creation• Tidal wetlands
– realignment
– FCA-CRT
• Inland habitat– wetland
– FCA-Wetland
Updated Sigmaplan: Harmonisation
• Conservation goals:– 3 levels
• Ecosystem functioning• habitat needs• Species
– quantified– Integration of legislation on all levels
• Measures– Integration of different societal aspects
(win-win)– Ranked– Timing
• Monitoring– Nested in MONEOS
Scaldit: River Basin management
• Scaldit I:– Test Common Implementation
guidances
• Scaldit II: – Cooperate for the RBMP– Compare quality status, reference
conditions, classification systems– Compare national RBMP– Joint report
Scaldit II
International Schelde Commission PA1Communicatie (Vlaams Gewest)
PA2 Cartografie (Waals Gewest)
PA3 Coastal and transitional waters
PA4 Fresh surface water bodies (Brussels hoofdstedelijk Gewest) Monitoring (Vlaams Gewest) Homogeen meetnet (Frankrijk)
PA5 Groundwater (Waals Gewest)
PA6 Kosteneffectiviteitsanalyse (Nederland)
PA7 Overstromingen - Droogten PA7a Waterkwantiteitsbeheer
(Frankrijk) PA7b Veiligheid & overstroming
(Vlaams Gewest)
PA3: Coastal and transitional waters
• Harmonisation– Common typology for Coastal and
Transitional waters– Harmonisation of classification
system NL-BE– Harmonisation of monitoring NL-BE– Comparison of ecological status– Compilation of measures
Schelde-estuary
Transitional waters
NLBEFLFR
River River
Daughter directiveEnvironmental quality standards
Scaldit II
Natura 2000 estuaries
Bird directiveHabitat directive
(23)
(40)
Natura 2000 Management plans
CG Schelde: 2005
CG PORT:2003
CG Flanders: 2008
• SPPA: Meadowbirds
• LTVS: tidal wetland
• SIGMA: harmonisation
Natura 2000 Management plans
Conclusions
• In an ideal world harmonised management would be nested in space, time, issues, …………
• Different sectors would share delimitations of management units
• But: – different issues prevail – Some areas are more important than others– Not all sectors share the same ranking– Time frames are political rather than practical– Priorities are often political rather than logical– New issues come up during the process………….
• However, we’ve come al long way along the road of harmonisation