26-10-2010
Or in other words:
Is maintaining a sustainable ecosystem = maintaining ecosystem stability? Gideon Gal and Arkadi Parparov Kinneret Limnological Laboratory Israel Oceanographic and Limnological Research
Objectives
if pushed further: is sustainability=stability?
Road map
External forcing or Management measures
Ecosystem sustainability and stability- are they the
same? Ecosystem models as a research and management tool When do abrupt changes occur? What are the acceptable limits for management measures? Examples of the effectiveness of an ecosystem model
to examine beyond observation limits Use of an ecosystem model run in long-term scenario mode
DYCD
Ecol. thresholds Tipping points
Resistance Resilience
WQI & CWQI
Sustainability limits
Stability limits
? Stability = Sustainability
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Lake Kinneret
Lake Kinneret uses
Mediterranean Sea
Recreation and tourism
Drinking water
Altitude (m asl) -210 Surface area (km2) 170 Max. Length (km) 22 Avg. Depth (m) 24 Max. Depth (m) 43 Prim. Prod. (gC m-2 y-1) 640
Dead Sea
(WQIs) for Lake Kinneret (Hambright et al 2000) Underlying assumptions: 1970-1991: serves as a reference period for which
acceptable ranges for ecosystem variables were defined in order insure sustainability
All WQI’s were merged into a composite water quality
index (CWQI) (Parparov & Hambright 2007)
100
250
100
80
240
80
60 40 20 0 100
Rating [Cl], %
Can be defined based on set of water quality indices
WQI approach [Cl-], mg L-1
Ecosystem sustainability
D. Markel
Rating [Cl]
http://earthobservatory.nasa.gov
230 220 210
200
250
300
350
[Cl-], mg L-1
R = f[Cl]
Expert panel (DELPHI Method)
40 20
200
150
60
0 0
1
2
3
4
5
WLL, below -208.0 m
[Cl] = F(WLL)
0
5
10
15
WLL, below -208.0 m
R = V(WLL)
Model Limnological studies
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Permissible ranges
WQI Rating curves (Winter-spring)
Management Measures or External forcing
CWQI Permissible Range
Nitrogen load (gm-2y-1)
?
Phosphorus load (gm-2y-1)
?
Water level (m above sea level)
?
Methodologically: CWQI = F(MM)
Defining ecosystem stability
DYCD Coupled model system Input data
DYRESM
1D
CAEDYM
Chem + Biol
Output
Lake mean value for each layer/ day/variable: ToC, WL, N, P, DO,
Meteorology In & outflows (vol, contents)
Food-web components
Physical Initial conditions
Equation parameters Biogeochemical initial conditions
DYRESM = Dynamic Reservoir Model CAEDYM = Computational Aquatic Ecosystem Dynamics Model.
DYCD
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CAEDYM configuration
Management measures scenarios 20-40 year DYCD simulations (2000-2039) Loading varied over 2 orders of magnitude (x0.1-x10) x1 scenario based on data from year 2000 Variations in N, P and N&P loading Stable conditions or 5-10 y perturbation period No inter-annual variation in other forcing data Last 3-yrs of simulation used
N loading scenarios 30 25 x0.1
N Load (g/m2/y)
State variables • Physics: 6 • Chemistry: 12 • Biology: 19 • Additional derived: 21
20 15
x0.2 x0.5 x1 x2 x5
10
x10
5 0
Gal et al 2009
Sustainable management (winter-spring)
MODELLING EXPERIMENTS Management Measures: P load, N load
0.1 0.01 2
3
4
5
6
-212
0.1
0.1
2
3
4
5
6
-208
-212
0.1 -216
1
7
2
3
4
5
6
7
Scenarios
Scenarios
Scenarios
WL
-210 m
1
0.01
-216
1
7
Nload
10
-208 1
0.01
-216
1
Pload
Pload
-210 m
1
WL
-212
WL
1
WL
10
-208
N&Pload
N&P load
Nload
Nload
1
N&Pload
WL
-210 m
WL
Pload
NPload Scenario
Nload Scenario
Pload Scenario 10
100 WS
100
SA
WQI = f(MM)
60
CWQI
Rating of [TN]
80
40 20 0 0
20
40
Nload, g m-2 yr-1
60
CWQI = F(MM)
60
20 0
30
60 -2
Nload, g m yr
-1
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20
-1
yr Nload, g m
-2
Nload, g m yr
-1
30
Sustainable management policy: %Cyanobacteria 80 -2
Sustainable Management Policy: CWQI
10
0
0 0
0.4
0.8
1.2 -2
Pload, g m yr
1.6
0
2
5 CWQI
40
1
20
Resistance
Resistance
2
80
0.6
60
0.4
40
CWQI
60
CWQI
0.8
CWQI
3
NX01
100.0 100 Resistance
80
-2
yr
1.5
-1
20 yr loading scenarios- %cyano
Resistance
4
1
Pload, g m
1
100
0.5
-1
Stability (resistance) vs sustainability
80.0
60.0
60.0
40.0
40.0
20.0
20.0
0.0
0.0 2010
0.2
PX01
100.0
80.0
2012
2014
2016
2018
2010
2012
2014
2016
2018
20
N scenario
0 NP scenario 0.1
40
0 1
Load multiplication factor
10
0
0 0.1
1
10
Stability: what tips the system?
Load multiplication factor
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20 yr loading scenarios- %cyano NX02
100.0
PX02
100.0
20 yr loading scenarios- %cyano NX05
100.0
80.0
80.0
80.0
80.0
60.0
60.0
60.0
60.0
40.0
40.0
40.0
20.0 0.0 2010
2012
2014
2016
2018
40.0
20.0
20.0
20.0
0.0
0.0 2010
2012
2014
2016
2010
2018
PX05
100.0
2012
2014
2016
2018
0.0 2010
2012
2014
2016
2018
Stability: what tips the system?
Stability: what tips the system?
20 yr loading scenarios- %cyano
20 yr loading scenarios- %cyano
NX1
100.0
PX1
100.0
NX2
100.0
80.0
80.0
80.0
60.0
60.0
60.0
60.0
40.0
40.0
40.0
20.0 0.0 2010
2012
2014
2016
2018
40.0
20.0
20.0
20.0
0.0
0.0 2010
2012
Stability: what tips the system?
2014
2016
2018
PX2
100.0
80.0
2010
2012
2014
2016
2018
0.0 2010
2012
2014
2016
2018
Stability: what tips the system?
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20 yr loading scenarios- %cyano NX5
100.0
PX5
100.0
20 yr loading scenarios- %cyano NX10
100.0
80.0
80.0
80.0
80.0
60.0
60.0
60.0
60.0
40.0
40.0
40.0
20.0 0.0 2010
2012
2014
2016
20.0
0.0
0.0
2018
40.0
20.0
20.0
2010
2012
2014
2016
2018
2010
2012
2014
Stability: what tips the system?
Nscen
0.0
2018
2010
2012
2014
2016
2018
Resilience
Pscen
25
50% Time to return (y)
40% %Cyano
2016
Stability: what tips the system?
%Cyano vs (TN/TP)loads; Lake (1980-2008) and model Lake
PX10
100.0
30% 20% 10% 0%
20 15
TN winter
10
TN summer 5 0
0
40
80
120
160
0.1
0.2
0.5
1
2
5
7.5
10
Load multiplication factor
(TN/TP)load
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Cyanobacteria, % in algal biomass
Conclusions Sustainability: limits for management measures (e.g.
nutrient loading) have been defined (Gal et al. 2009) Stability: Response to management measures were not
trivial …Ecosystem stability limits ≠ sustainability limits Therefore, measures that allow sustaining an ecosystem
will not necessary ensure stability or vice versa However, clear definitions of ecosystem stability and relationship with management measures are still required The results represent some of the potential that can be found in ecosystem models, but are not always utilized
25 20 15 10 5 0 1990
1994
1998
2002
2006
Winter-Spring, 1969-2007 Winter-Spring, 1969-2008
2.5
3.5
2.0
3
1.5 Residuals
Shannon Index
2.5
2
1.5
1.0 0.5 0.0 -0.5
1
-1.0 0.5
0 1965
1970
1975
1980
1985
1990
1995
2000
2005
2010
-1.5 1960
1970
1980
1990
2000
2010
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0.50
2.0 Pload
Shannon Index
Nload
1.0
0.25
WS
0.0
SA
0.00 0.1
1
10
0.1
N&Pload, multipl factor
Lake Kinneret WQI
L-1
Total suspended solids, mg (TSS) Total nitrogen, mg L-1 (TN) Total phosphorus, µg L-1 (TP) Primary production, g C m-2 d-1 (PP) Chlorophyll, µg L-1 (Chl) Cyanobacteria, % total biomass (%Cyano) Biomass of Zooplankton, g m-2 (Bzp)
WinterSpring 1.0-7.1 0.3-1.2 9-38 1.1-3.2 5.5-40.5 0-3.7
SummerAutumn 0.6-4.1 0.2-0.9 5-28 0.7-2.2 1.5-10.1 1-10.8
13-52
7-37
CWQI= weighted sum of WQI’s; 0 < CWQI ≤ 100 Acceptable range: 60 ≤ CWQI
10
Semiannual avg, Summer-Autumn, 1969-2008
Permissible ranges for ecosystem variables Water quality indices (WQI)
1 [NP]load, multiplication factor
60
%cyano
Phyto-biomass, rel. units
N&Pscen, PhytoBiom, normalized
30
0 1969 1974 1979 1984 1989 1994 1999 2004
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x0.1Nload&Pload, %Cyano
x10Nload&Pload, %Cyano 120.0
100.0 x10Nload x0.1Nload
x10Pload
x0.1Pload
90.0 100.0 80.0
80.0
70.0
%Cyano
50.0
60.0
40.0 40.0 30.0
20.0 20.0 10.0
0.0
0.0
Stability EV limits
Managing ecosystem stability% Cyanobacteria
Stability limits Resistance
%Cyano
60.0
ecosystem Management measures
WQ/sustainability
EV
40 38 36 34 32 30 28 26 24 22 20 18 16 14 12 10 8 6 4 2 0 -2 -4 0.1
NP scenario
Resistance
1
10
Load multiplication factor
WQsustainability limits
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40 38 36 34 32 30 28 26 24 22 20 18 16 14 12 10 8 6 4 2 0 -2 -4 0.1
100
NP scenario
80 Resistance % Cyano
60 40
%Cyano
Resistance
Managing ecosystem stability% Cyanobacteria
20 1
10 0
Load multiplication factor
11