ECOSYSTEM SHIFTS IN THE BALTIC SEA - European Parliament · 21/12/2011 Ecosystem Shifts in the...
Transcript of ECOSYSTEM SHIFTS IN THE BALTIC SEA - European Parliament · 21/12/2011 Ecosystem Shifts in the...
21/12/2011 Ecosystem Shifts in the Baltic Sea 1
ECOSYSTEM SHIFTS IN THE BALTIC SEA
Michele CasiniSwedish University of Agricultural Sciences
21/12/2011 Ecosystem Shifts in the Baltic Sea 2
The area
Central Baltic Sea
25
27
29
28
26
Sweden
Latvia
Estonia
Finland
GermanyPoland
Russia
Lithuania
Denm
ark
Gulf of Finland
Gulf of Riga
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Changes in the ecosystem
SpratAcartia
CodHerring
Pseudocalanus
Möllmann et al. 2009
1974 2005Climate
21/12/2011 Ecosystem Shifts in the Baltic Sea 4
Climate
Salinity in spring
6.5
7.0
7.5
8.0
8.5
1960
1965
1970
1975
1980
1985
1990
1995
2000
2005
2010
Year
Salin
ity 0
-60
m (p
su)
7.5
8.0
8.5
9.0
9.5
10.0
10.5
11.0
Salin
ity 6
0-10
0 m
(psu
)
0-60 m60-100 m
Surface temperature in spring
0
1
2
3
4
5
6
7
8
1960
1965
1970
1975
1980
1985
1990
1995
2000
2005
2010
Year
Tem
pera
ture
0-5
0 m
(°C
)
SMHI database
21/12/2011 Ecosystem Shifts in the Baltic Sea 5
Nutrients
0
100000
200000
300000
400000
500000
600000
700000
800000
1850
1860
1870
1880
1890
1900
1910
1920
1930
1940
1950
1960
1970
1980
1990
2000
Year
Nitr
ogen
load
s (to
nnes
/yea
r)
0
5000
10000
15000
20000
25000
30000
35000
40000
45000
50000
Pho
spho
rus
load
s (to
nnes
/yea
r)NitrogenPhosphorus
Winter inorganic nitrogen and phosphorus, Landsort deep 0-10 m
0
4
8
12
16
1950 1960 1970 1980 1990 2000 2010
DIN
(µM
)0.00.10.20.30.40.50.60.70.80.91.0
DIP
(µM
)
DINDIP
Human emissions Concentration in the system
Ulf Larsson (Stockholm University)Baltic Nest Institute
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Oxygen Anoxic areas september 2010
Anoxic areas
SMHI 2010
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0
200
400
600
800
1000
1200
1400
1600
1800
2000
1966
1970
1974
1978
1982
1986
1990
1994
1998
2002
2006
2010
Year
Clu
peid
bio
mas
s (1
000
tons
)
0
100
200
300
400
500
600
700
800
Cod
bio
mas
s (1
000
tons
)
SpratHerringCod
Commercial fish species
From ICES 2011
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Cod
• High fishing pressure• Reduced reproductive volume• Reduced larval prey
Fishing mortality
0.0
0.3
0.6
0.9
1.2
1.5
1.8
1966
1970
1974
1978
1982
1986
1990
1994
1998
2002
2006
2010
Year
F (a
ges
4-7)
Fmsy
Fpa
Reproductive volume
0
100
200
300
400
500
600
700
800
1960
1964
1968
1972
1976
1980
1984
1988
1992
1996
2000
2004
2008
Year
Rep
rodu
ctiv
e vo
lum
e (K
m 3
)
Gotland BasinGdansk DeepBornholm Basin
ICES 2011 Maris Plikshs, Latvian Institute of Food Safety
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Cod
• High fishing pressure• Reduced reproductive volume• Reduced larval prey
Fishing mortality
0.0
0.3
0.6
0.9
1.2
1.5
1.8
1966
1970
1974
1978
1982
1986
1990
1994
1998
2002
2006
2010
Year
F (a
ges
4-7)
Fmsy
Fpa
ICES 2011 ICES 2010
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Sprat
• Reduced cod predation• Increased temperature
0
200
400
600
800
1000
1200
1400
1600
1800
0 80 160 240 320 400 480 560 640 720 800
Cod SSB (1000 tons)
Spra
t SSB
(100
0 to
ns)
ICES 2011
From ICES 2011 ICES 2010
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Herring
• High fishing pressure• Increased competition with sprat• Decreased salinity• Coastal eutrophication
Fishing mortality
0.0
0.1
0.2
0.3
0.4
0.5
0.6
1974
1978
1982
1986
1990
1994
1998
2002
2006
2010
Year
F (a
ges
3-6)
Fmsy
Fpa
Mean body weight
0.00
0.02
0.04
0.06
0.08
0.10
0.12
1974
1978
1982
1986
1990
1994
1998
2002
2006
Year
Mea
n w
eigh
t (K
g)
Age 8+Age 7Age 6Age 5Age 4Age 3Age 2Age 1
Body weight
ICES 2011
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Trophic cascade
• Top-down regulations, driven by predation
• Inverse relationshipsbetween trophic levels
-
+
+
-
+
−
Casini et al. 2008
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Fish body growth:
Side effect of trophic cascade: density-dependence
Mean body weights
0
5
10
15
20
25
30
35
1974
1978
1982
1986
1990
1994
1998
2002
2006
2010
Year
Spr
at w
eigh
t, ag
e 3
(g)
0
10
20
30
40
50
60
70
80
Her
ring
wei
ght,
age
3 (g
)
SpratHerring
From ICES 2011
0
5
10
15
20
0 50 100 150 200 250 300 350 400 450
Sprat abundance (ind. *10 9)
Spra
t wei
ght (
g)
0
10
20
30
40
50
60
0 50 100 150 200 250 300 350 400 450
Sprat abundance (ind. *10 9)
Her
ring
wei
ght (
g)
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Cod
Zooplankton
Phytoplankton
N
Anoxic areas
P
Recent state (1990s-2000s)
HerringSpratT
Fishery
S
Drivers of ecosystem state
Cod
Zooplankton
Phytoplankton
N
Anoxic areas
P
Previous state (1970s-1980s)
HerringSpratT S
Fishery
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Potential feedback loops (“vicious circles”)
Cod
Zooplankton
Sprat
Hydrology
Herring
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Potential feedback loops (“vicious circles”)_1
Cod
Zooplankton
Sprat
Hydrology
Negative effects of sprat on cod• Competition for food • Predation on cod eggs• Effect of cod growth
Herring
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Shift in functioning: alternative stable states?
Sprat-dominated
Climate stressor (Salinity, oxygen, etc...)
Biological feature(Zooplankton,Fish growth,
Cod recruitment)
Cod-dominatedBiological
feature
Hydrology
Sprat
Biologicalfeature
Hydrology
Sprat
1970-1980s
1990-2000s
From Casini et al. 2010
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Phytoplankton
Nutrientsin system
Anoxia
Humanemissions
Potential feedback loops (“vicious circles”)_2
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Phytoplankton
Nutrientsin system
Anoxia
Humanemissions
Low cod
Trophic cascade
Potential feedback loops (“vicious circles”)_3
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Conclusions
• Large changes in the Baltic ecosystem• Effects of fisheries: direct & via trophic cascade• Effects of hydro-climate and eutrophication:
reinforcing the trophic cascade• Change in ecosystem functioning: feedback
loops tend to maintain the new biological state
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Recommendations
Actions for ecosystem recovery• Fishing pressure on cod should be kept low
(EU management plan).• Fishing pressure on herring should be reduced.• Fishing pressure should be adaptive to the
hydro-climate conditions. • Anthropogenic nutrient inputs, both nitrogen
and phosphorus, should be reduced.
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Recommendations
Expected effects• In the current hydro-climate conditions,
recover of cod stock at relatively high levels.• Enhancement of the herring stock. • Increase of total zooplankton.• Decrease of algal blooms and oxygen-
deficient areas.
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Recommendations
Potential external hinders• The effective reduction of anoxia extent may
require periods of oxygen-rich water inflows. • Hydro-climate will aid or counteract the
management actions.• Projected long-term climate changes
(decrease in salinity and increase in temperature) may hinder the ecosystemrecovery in the long run.