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Overview of Results from the
EU-WETwin Project
István Zsuffa
Rose Kaggwa
Anne van Dam
Stefan Liersch
Jan Cools _____________________________________________
9th INTECOL International Wetlands Conference
Objectives of WETwin
“Enhancing the role of wetlands in IWRM for twinned
river basins in EU, Africa and Latin-America in support
of EU Water Initiatives”
Strategies for:
utilizing provisioning
and regulating services,
while maintaining
ecosystem functions
integrating wetlands
into RBM
adapting wetland
management to changing
environmental conditions
The Consortium
EU partners: Non-EU partners:
‘Twinning’
partnership
Prepared under contract from the European
Commission
Working on case studies
Conceptual Framework RIVER BASIN
MGT CYCLE
WETLAND
MGT CYCLE
Characterisation
& problems
Evaluation
of solutions River basin
management plan
Implementation
of plan
Monitoring
Review of plans
Generation of
alternative
mgt. solutions
Best compromise
solution
INTERACTION
& EXCHANGE Review
of plans
Characterisation
& problems
Generation of
alternative
mgt. solutions
Evaluation
of solutions
Best compromise
solution
Wetland
management plan
Implementation
of plan
Monitoring
Scope of WETwin
The Namatala wetland
Characterisation, problems
Driver State
Impact
Response
Cause-effect link
Population
growth
Improve purification
capacity of the wetland:
Sustainable agriculture
Papyrus buffer strips
Regulated papyrus
harvesting Limited
wastewater
treatment
Unsustainable
farming in
catchment
Increasing
nutrient,
sediment and
pollution loads
Improve wastewater
treatment
Enforce discharge standards
Papyrus buffer zones
Deterioration of WQ
Higher nutrient
concentrations in soil
Changes in natural flora
and fauna
Risk of pollution with
toxic chemicals, heavy
metals, pathogens
Impacts on Ecosystem Services
•Loss of habitats and biodiversity
•Reduction of fish catches
•Poor quality of water downstream
and for household purposes
•Health risks for riparian population
Management
Solution 1
Management
Solution 2
Management
Solution 3
Alternative A.1.1 X
Alternative A.1.2 X
Alternative A.1.3 X
Alternative A.2.1 X X
Alternative A.2.2 X
Alternative D.1.1 x XManagement
Response D
Management
Option D.1
Management
Response A
DP
SIR
Management
Option A.1
Management
Option A.2
Management
Response C
Objective Process
Subjective process
DS
IR
Generation of alternative mgt. solutions
Biophysical
indicators
Value
functions
Criteria
scores
(0-1)
ANALYSIS NORMALIZATION
Models
Mgt
solution
Scenario Investment,
operational and
maintenance
costs
Feasibility of
implementation
and operation
Cost
evaluation
Institutional
analysis
Evaluation of solutions
Wetland model of Hes et al.
Seasonally
flooded wetland
Permanently
flooded wetland
Open water
Seepage
Seepage
River
discharge
Hydrological
Model
Permanent Wetland
N Model
Seasonal Wetland
N Model
Seasonal Wetland
C Model
Permanent Wetland
C Model
0% 10%
D
10%
HBD
10%
LBD
20%
D
20%
HBD
20%
LBD
30%
D
30%
HBD
30%
LBD
S 25 26 35 27 26 35 27 27 35 27
P 29 30 49 46 30 56 53 31 56 54
S+P 46 47 65 59 47 69 64 48 70 65
S = Seasonally flooded
P = Permanently flooded
D = Daily harvest
HBD = Batch harvest at High Biomass Density
LBD = Batch harvest at Low Biomass Density
Cooping with data poor conditions
Biophysical
indicators Value
functions
Criteria
scores
(0-1)
Models
Expert
judgements
WET-Health (Macfarlane et al., 2008)
WET-Ecoservices (Kotze et al., 2009)
Evaluation matrix, Namatala
Seepage
Seepage
Value functions
Total rice production in wetland
t/y 0 35000
1
0
Indicator value
Cri
teri
a s
co
re
Analysis matrix, Namatala
Articulation of stakeholders’ preferences
Weight sets for
Namatala
Stakeholder group: Water Managers
Stakeholder group: Resource Users
mDSS (Guipponi, 2007)
Identification of the best compromise solution
Stakeholder group: Political leaders
Stakeholder group: Environmentalists
Stakeholder group: Civil Society
Stakeholder group: Community Services
Best compromise
solution: MS 2a
Papyrus buffer strips
Awareness campaigns
Papyrus buffer zones
Strict enforcement of
wetland and land
ownership policy
Papyrus harvesting
regime
Buffer strips
Buffer zones
Stabilisation
ponds
Mbale
Vulnerability Assessment
EI = State(BAU) – State(current)
EI : external impact
AC : Adaptive capacity
AC = State(mgt) – State(BAU)
ΔV = EI + AC
ΔV = State(mgt) – State(current)
ΔV : change in vulnerability
ΔV>0: the system moves towards a resilient state
ΔV<0 : the system moves towards a more
vulnerable state
Vulnerability of food production in the
Inner Niger Delta
Scenarios
Population growth
scenarios: 0.7%
and 2.6% annual
growth rates
Water management scenarios: 1. Sélingué reservoir;
2. Sélingué and Fomi reservoirs
Management
Additional 65,000 ha of wetland area will gradually
be converted into rice fields with a productivity of
approximately 5 t/ha.
Estimated values of vulnerability components
(rice production)