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Widespread omnivory in warmer shallow lakes
determines different food web structures than
observed in temperate ones
Carlos Iglesias , Mariana Meerhoff, Liselotte S. Johansson, Mariana
Vianna, Néstor Mazzeo, Juan Pablo Pacheco, Franco Teixeira de
Mello, Guillermo Goyenola, Iván González-Bergonzoni, Torben L.
Lauridsen, Martin Søndergaard, Thomas A. Davidson & Erik Jeppesen

XIII Congresso Brasilero de Limnologia
4-8 de Setembro 2011, Natal, RN
SUMMARY:
Framework
Objectives
Methodology
Results

Conclusions

XIII Congresso Brasilero de Limnologia
What is a Shallow lake ?
• Medium depht ca. 3 m
• Light can reach bottom
• No or very short-term stratifications
• Strong water-sediments link
• Wide distributed, very important to
humans

P

P

P

Very well studied in cold temperate areas
Theoretical
framework
XIII Congresso Brasilero de Limnologia

ALTERNATIVE STATES
(Scheffer et al., 1993)
Alternative (stable) states hypotheses

Total P(g L-1) concentration
25
only
submerged
plants

50

100

1000

Transparency and plant -associated mechanisms

clear water submerged plants
Forward switches

scarce
plants

Biomanipulation

turbid water

phytoplankton

phytoplankton
dominance

Turbid water-associated mechanisms

higher probability of phytoplankton OR free-floating plants
higher probability of submerged plants dominance

XIII Congresso Brasilero de Limnologia
Role of submerged plants in temperate lakes
 BOTTOM-UP
Nutrients/Light
Sedimentation rate

+

turbidity

+
-

phytoplankton
allelopathy

submerged plants
-

+

+

nutrients

Modified from Scheffer et al. 1993

XIII Congresso Brasilero de Limnologia

+

periphyton
Role of submerged plants in temperate lakes
+

piscivorous fish

submerged plants

planktivorous fish

zooplankton
Modified from Scheffer et al. 1993

 TOP DOWN
Direct trophic Interactions
Cascading effects (Carpenter & Kitchell 1986)

 REFUGE
Diel migrations (Timms & Moss, 1984)
Behavioural cascades (Romare & Hansson 2002)
XIII Congresso Brasilero de Limnologia
Role of submerged plants in warmer lakes

Temperate lakes

Subtropical lakes

high submerged plant cover with low
phytoplankton

loss of clear patterns

high phytoplankton biomass with
low plant %PVI

high plant %PVI simultaneous with
phytoplankton biomass
Jeppesen et al in 2007

XIII Congresso Brasilero de Limnologia
Role of submerged plants in warmer lakes

Subtropical lakes

Effects of macrophytes on trophic interactions more complex and
water clarity less improved

This is apparently a consequence of markedly different trophic web
interactions (zooplankton & fish)

XIII Congresso Brasilero de Limnologia
Changes on fish community structure

High diversity

(TdeM 2009)

High density (specialy in plants)

Small-sized species with high abundances
(Meerhoff et al., 2007)

Few large-sized strict piscivores
(Quiros, 1998)

Dominance of omnivorous species
(Lazzaro, 1997)

Several reproduction events. No window of
opportunity for zooplankton (Van Leeuwen et al.,
2007)

XIII Congresso Brasilero de Limnologia
Food webs changes among climatic regions
Denmark

Uruguay

11x higher density in the subtropical
lakes
temperate fish more “pelagic”
subtropical fish more “littoral”

Large-bodied
zooplankters infrequent
or absent.
5.5x lower density in
subtropical lakes

8x lower density of macroinvertebrates
4x lower periphyton biomass, despite better
growing conditions of light & temperature
(Meerhof et al GChB 2008)

XIII Congresso Brasilero de Limnologia
Food webs changes among climatic regions
More complex and less hierarchically structured
More fish co-ocurred with fewer cladocerans and invertebrates
Lower biomass of periphyton than expected (less grazing high light and temp)

(Meerhof et al GChB 2008)

XIII Congresso Brasilero de Limnologia
Objectives and Methodological approach

Are the food webs more truncated
in subtropical lakes?
and fuelled by periphyton to a larger
extent?

From Hugie & Dill 1994

XIII Congresso Brasilero de Limnologia
Objectives and Methodological approach
Stable isotopes analysis +
Community-wide measures of trophic structure
(Vander Zanden & Vadeboncouer, 2002/Post, 2002/Layman et al., 2007)
dN indicates trophic position and dC carbon sources
Uruguay 30-35 。 S

Denmark 55-57 。N

XIII Congresso Brasilero de Limnologia
Food webs changes among climatic regions
Stable isotopes analysis + Community-wide
measures of trophic structure
• Trophic position
• Trophic web length (Max TP)
• % Littoral Contribution
• Carbon range (amplitude of C sources)
• Total area (niche space ocupied)
• Mean nearest neighbour distance
(redundancy)

CR3

CR2
TA

CR= max –min carbon
TWL
XIII Congresso Brasilero de Limnologia
Food webs changes among climatic regions
%CONT
LITT

TA

NND*

3.5

53.5

10.1

0.4

9.7

5.9

54.7

9.2

0.4

9.9

9.4

7.6

64.5

15.5

0.6

4.1

8.5

7.7

5.1

50.7

16.0

0.6

4

4.4

7

7

3.4

46.1

10.7

0.7

11

4.0

8.5

7.7

5.1

53.5

10.7

0.6

Range

4-13

3.4-4.4

7.0-9.9

4.5-9.7

3.4-7.6

46.1-64.5

9.2-16.0

0.4-0.7

VAENG

8

5.1

4.9

4.3

2.6

52.7

8.6

0.6

TRANEVIG

6

5.8

10.5

7.3

0.6

58.3

16.1

0.9

GAMMELMOSE

4

4.6

4.6

4.4

3.0

98.2

10.2

1.2

DENDERUP

3

4.4

9.9

9.9

4.1

31.6

15.4

0.6

DK Median

5

4.8

7.4

5.9

2.8

55.5

12.8

0.8

3-8

4.4-5.8

4.6-10.5

4.3-9.9

0.6-4.1

31.6-98.2

8.6-16.1

0.6-1.2

Zvalue

1.85

2.2

0.1

0.7

1.96

0.25

0.0

1.98

p

0.06

0.02

0.9

0.5

0.05

0.6

0.99

0.05

Lake

FR*

TLW*

CR

CR 2

CISNE

13

4.0

7.7

4.5

DIARIO

11

3.4

9.7

GARCIA

11

3.9

CLOTILDE

9

BLANCA
UY Median

Range

CR 3*

In warmer lakes

Temperate = Subtropical lakes
Reliance in Littoral (ca. 50%)
Carbon range
Total extent of trophic diversity

2X Fish richness
-1 Trophic Levels

2x CR3
More redundant species

XIII Congresso Brasilero de Limnologia
Food webs changes among climatic regions

Temperate = Subtropical lakes
Reliance in Littoral (ca. 50%)
Carbon range
Total extent of trophic diversity

Implicances on Trophic webs architecture
-1 Trophic Levels
2x CR3
More redundant species
XIII Congresso Brasilero de Limnologia
Food webs changes among climatic regions

(Meerhoff et al,2007)

XII Congresso Brasilero de Limnologia
Food webs changes among climatic regions
Implicances on Trophic webs architecture
-1 Trophic Levels
2x CR3
More redundant species

3 Structural mechanisms

XIII Congresso Brasilero de Limnologia

(Post & Takimoto,2007)
Food webs changes among climatic regions
Omnivory may explain the observed architecture
(Post & Takimoto,2007)
Gonzalez-Bergonzoni subbmited

XIII Congresso Brasilero de Limnologia
Conclusions
submerged plants

piscivorous fish

+

+

piscivorous fish

submerged plants

OMNIVOROUS
fish

planktivorous fish

zooplankton

zooplankton

Modified from Scheffer et al. 1993

Different structure of trophic webs (and probably also functioning).
Omnivory appears as the most plausible explanation
Strong effects to whole system functioning.
Asymmetries in some important feed backs probably weak alternative
states to occur
XIII Congresso Brasilero de Limnologia
Conclusions

ONE FINAL REMARK: We do have plant dominated clear water systems, even
with quite high nutrient levels that seems to be persistent in time.

XIII Congresso Brasilero de Limnologia
Thanks!!

Thanks for finantial support to AU, NERI and the Ministry of Science, Technology and Innovation in
DK. PDT, ANII, CSIC –Udelar in Uruguay

XIII Congresso Brasilero de Limnologia
Methods
Shallow lakes trophic web in contrasting climates Iglesias cbl xiii
Shallow lakes trophic web in contrasting climates Iglesias cbl xiii

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Shallow lakes trophic web in contrasting climates Iglesias cbl xiii

  • 1. Widespread omnivory in warmer shallow lakes determines different food web structures than observed in temperate ones Carlos Iglesias , Mariana Meerhoff, Liselotte S. Johansson, Mariana Vianna, Néstor Mazzeo, Juan Pablo Pacheco, Franco Teixeira de Mello, Guillermo Goyenola, Iván González-Bergonzoni, Torben L. Lauridsen, Martin Søndergaard, Thomas A. Davidson & Erik Jeppesen XIII Congresso Brasilero de Limnologia 4-8 de Setembro 2011, Natal, RN
  • 3. What is a Shallow lake ? • Medium depht ca. 3 m • Light can reach bottom • No or very short-term stratifications • Strong water-sediments link • Wide distributed, very important to humans P P P Very well studied in cold temperate areas Theoretical framework XIII Congresso Brasilero de Limnologia ALTERNATIVE STATES (Scheffer et al., 1993)
  • 4. Alternative (stable) states hypotheses Total P(g L-1) concentration 25 only submerged plants 50 100 1000 Transparency and plant -associated mechanisms clear water submerged plants Forward switches scarce plants Biomanipulation turbid water phytoplankton phytoplankton dominance Turbid water-associated mechanisms higher probability of phytoplankton OR free-floating plants higher probability of submerged plants dominance XIII Congresso Brasilero de Limnologia
  • 5. Role of submerged plants in temperate lakes  BOTTOM-UP Nutrients/Light Sedimentation rate + turbidity + - phytoplankton allelopathy submerged plants - + + nutrients Modified from Scheffer et al. 1993 XIII Congresso Brasilero de Limnologia + periphyton
  • 6. Role of submerged plants in temperate lakes + piscivorous fish submerged plants planktivorous fish zooplankton Modified from Scheffer et al. 1993  TOP DOWN Direct trophic Interactions Cascading effects (Carpenter & Kitchell 1986)  REFUGE Diel migrations (Timms & Moss, 1984) Behavioural cascades (Romare & Hansson 2002) XIII Congresso Brasilero de Limnologia
  • 7. Role of submerged plants in warmer lakes Temperate lakes Subtropical lakes high submerged plant cover with low phytoplankton loss of clear patterns high phytoplankton biomass with low plant %PVI high plant %PVI simultaneous with phytoplankton biomass Jeppesen et al in 2007 XIII Congresso Brasilero de Limnologia
  • 8. Role of submerged plants in warmer lakes Subtropical lakes Effects of macrophytes on trophic interactions more complex and water clarity less improved This is apparently a consequence of markedly different trophic web interactions (zooplankton & fish) XIII Congresso Brasilero de Limnologia
  • 9. Changes on fish community structure High diversity (TdeM 2009) High density (specialy in plants) Small-sized species with high abundances (Meerhoff et al., 2007) Few large-sized strict piscivores (Quiros, 1998) Dominance of omnivorous species (Lazzaro, 1997) Several reproduction events. No window of opportunity for zooplankton (Van Leeuwen et al., 2007) XIII Congresso Brasilero de Limnologia
  • 10. Food webs changes among climatic regions Denmark Uruguay 11x higher density in the subtropical lakes temperate fish more “pelagic” subtropical fish more “littoral” Large-bodied zooplankters infrequent or absent. 5.5x lower density in subtropical lakes 8x lower density of macroinvertebrates 4x lower periphyton biomass, despite better growing conditions of light & temperature (Meerhof et al GChB 2008) XIII Congresso Brasilero de Limnologia
  • 11. Food webs changes among climatic regions More complex and less hierarchically structured More fish co-ocurred with fewer cladocerans and invertebrates Lower biomass of periphyton than expected (less grazing high light and temp) (Meerhof et al GChB 2008) XIII Congresso Brasilero de Limnologia
  • 12. Objectives and Methodological approach Are the food webs more truncated in subtropical lakes? and fuelled by periphyton to a larger extent? From Hugie & Dill 1994 XIII Congresso Brasilero de Limnologia
  • 13. Objectives and Methodological approach Stable isotopes analysis + Community-wide measures of trophic structure (Vander Zanden & Vadeboncouer, 2002/Post, 2002/Layman et al., 2007) dN indicates trophic position and dC carbon sources Uruguay 30-35 。 S Denmark 55-57 。N XIII Congresso Brasilero de Limnologia
  • 14. Food webs changes among climatic regions Stable isotopes analysis + Community-wide measures of trophic structure • Trophic position • Trophic web length (Max TP) • % Littoral Contribution • Carbon range (amplitude of C sources) • Total area (niche space ocupied) • Mean nearest neighbour distance (redundancy) CR3 CR2 TA CR= max –min carbon TWL XIII Congresso Brasilero de Limnologia
  • 15. Food webs changes among climatic regions %CONT LITT TA NND* 3.5 53.5 10.1 0.4 9.7 5.9 54.7 9.2 0.4 9.9 9.4 7.6 64.5 15.5 0.6 4.1 8.5 7.7 5.1 50.7 16.0 0.6 4 4.4 7 7 3.4 46.1 10.7 0.7 11 4.0 8.5 7.7 5.1 53.5 10.7 0.6 Range 4-13 3.4-4.4 7.0-9.9 4.5-9.7 3.4-7.6 46.1-64.5 9.2-16.0 0.4-0.7 VAENG 8 5.1 4.9 4.3 2.6 52.7 8.6 0.6 TRANEVIG 6 5.8 10.5 7.3 0.6 58.3 16.1 0.9 GAMMELMOSE 4 4.6 4.6 4.4 3.0 98.2 10.2 1.2 DENDERUP 3 4.4 9.9 9.9 4.1 31.6 15.4 0.6 DK Median 5 4.8 7.4 5.9 2.8 55.5 12.8 0.8 3-8 4.4-5.8 4.6-10.5 4.3-9.9 0.6-4.1 31.6-98.2 8.6-16.1 0.6-1.2 Zvalue 1.85 2.2 0.1 0.7 1.96 0.25 0.0 1.98 p 0.06 0.02 0.9 0.5 0.05 0.6 0.99 0.05 Lake FR* TLW* CR CR 2 CISNE 13 4.0 7.7 4.5 DIARIO 11 3.4 9.7 GARCIA 11 3.9 CLOTILDE 9 BLANCA UY Median Range CR 3* In warmer lakes Temperate = Subtropical lakes Reliance in Littoral (ca. 50%) Carbon range Total extent of trophic diversity 2X Fish richness -1 Trophic Levels 2x CR3 More redundant species XIII Congresso Brasilero de Limnologia
  • 16. Food webs changes among climatic regions Temperate = Subtropical lakes Reliance in Littoral (ca. 50%) Carbon range Total extent of trophic diversity Implicances on Trophic webs architecture -1 Trophic Levels 2x CR3 More redundant species XIII Congresso Brasilero de Limnologia
  • 17. Food webs changes among climatic regions (Meerhoff et al,2007) XII Congresso Brasilero de Limnologia
  • 18. Food webs changes among climatic regions Implicances on Trophic webs architecture -1 Trophic Levels 2x CR3 More redundant species 3 Structural mechanisms XIII Congresso Brasilero de Limnologia (Post & Takimoto,2007)
  • 19. Food webs changes among climatic regions Omnivory may explain the observed architecture (Post & Takimoto,2007) Gonzalez-Bergonzoni subbmited XIII Congresso Brasilero de Limnologia
  • 20. Conclusions submerged plants piscivorous fish + + piscivorous fish submerged plants OMNIVOROUS fish planktivorous fish zooplankton zooplankton Modified from Scheffer et al. 1993 Different structure of trophic webs (and probably also functioning). Omnivory appears as the most plausible explanation Strong effects to whole system functioning. Asymmetries in some important feed backs probably weak alternative states to occur XIII Congresso Brasilero de Limnologia
  • 21. Conclusions ONE FINAL REMARK: We do have plant dominated clear water systems, even with quite high nutrient levels that seems to be persistent in time. XIII Congresso Brasilero de Limnologia
  • 22. Thanks!! Thanks for finantial support to AU, NERI and the Ministry of Science, Technology and Innovation in DK. PDT, ANII, CSIC –Udelar in Uruguay XIII Congresso Brasilero de Limnologia
  • 23.
  • 24.
  • 25.

Editor's Notes

  1. Present myself, Supervisors and members of the comitee
  2. Quite fast trough these one only mention nutrient control and interactions among plants and phyto and existence of feedbacks. Plants clarify water and clear water promotes plant development.A couple of words on the importance of nutrients in the lower levels and how this effect dissipates going upwards.
  3. Top down-Bottom up Mcqueens model, importance of the strength of trophic links to have feed backs strong enough to create attractors and sustain alternative states hypotesis in shallow lakes. Dependant in key species, like Daphnia. Strength here the importance of plants by affecting interactions among different members of the trophic web
  4. Macrophyte and clear water in warmer lakes not really ocurring this was attributed to strong differences of communities
  5. SIA analysis using Community wide metrics of trophic webs proposed by Layman et al 2007
  6. SIA analysis using Community wide metrics of trophic webs proposed by Layman et al 2007