Impacts of Shark Removal on Coral Reef Dynamics

 
Taken out of context: the effects of shark removal in the dynamic
environment of a coral reef
 
Jonathan L.W. Ruppert, Mike Travers, Marie-Josée Fortin and 
Mark G. Meekan
 
High numbers sharks –
high coral cover, absent
– low coral cover
Changes in trophic
structure of fish
communities
Confounding of human
activity (fishing down
food chain) and natural
disturbance
Sandin 
et al. 
2008 
PLoS ONE
 
Coral Reefs: Human Activity or Top–Predators?
Aims
 
1.
Does fishing impact shark abundance?
2.
Do changes in the abundance of sharks affect the structure of
the reef fish community?
3.
How do benthic disturbances (cyclones, bleaching) alter fish
communities?
4.
Are there synergistic effects of these top-down and bottom-up
processes?
Rowley Shoals 
(Non-Fished)
Scott Reefs
(Fished)
 
Ashmore 
(Fished)
 
Fished Reefs: Coral Bleaching
 
Non-Fished Reefs: Cyclonic Event
 
Fishing (Fished vs.
                   Non-Fished)
Shark density
differences between
Rowley and Scott
 
 
Disturbance (Disturbed
vs. Non-Disturbed)
 < 30% coral cover
threshold
Treatments: Fishing and Disturbance
 
Shark Community Data: BRUVS
 
BRUVS (Baited Remote Underwater Video
Station)
All reefs (2003/2004)
Target apex predators & carnivores
Depth range: 5 – 100 m
1 to 1.5 hrs per drop
MaxN statistic
 
AIMS LTMP (Long-Term
Monitoring Program)
Scott and Rowley (1994 –
Present)
6 reefs; 3 sites each (
n
=18)
Northeast reef slope
Benthic surveys alongside
Abundance counts (18
 
families; non-cryptic
 
species; excludes recruits)
 
SOURCE: AIMS
 
Trophic Structure of Coral Reef Fishes
Results: Shark Density (permuted ANOVA)
p 
< 0.01
Fished vs. Non-
Fished:
Carnivores &
Herbivores
(Territorial & Non
– Territorial)
 
Differences in Trophic Structure (RDA)
Disturbance vs.
Non-Disturbance:
Herbivores,
Planktivores,
Corallivores, and
Detritivores
 
Trophic Group Responses: Carnivores
 
*
*
 
p
 
<
 
0
.
0
1
 
*
 
p
 
<
 
0
.
0
5
 
*
 
 
 
 
 
Trophic Group Responses: Herbivores
 
*
*
 
p
 
<
 
0
.
0
1
 
*
 
p
 
<
 
0
.
0
5
 
 
Trophic Group Responses
 
**
 
**
 
**
 
**
 
**
 
Summary
 
1.
Does fishing impact shark abundance?
YES
 
2.
Do changes in the abundance of sharks affect the
structure of the reef fish community?
YES
Meso-predator release of 
carnivores 
and
 
subsequent
trophic cascade during disturbances with 
herbivores
 
3.
Do benthic disturbances alter fish communities?
Are there synergistic effects of top-down and
bottom-up processes?
YES
Herbivores, planktivores 
and 
corallivores
 show
responses to changes in coral and algal cover
Detritivores
 show synergistic responses
 
Herbivores – more abundant on unfished reefs
where more sharks are present
Central to recovery of reefs from processes
that result in the loss of coral cover
Implications for reef resilience
 
Significance: Resilience
 
Acknowledgements
 
F
u
n
d
i
n
g
/
D
a
t
a
 
F
i
e
l
d
/
l
a
b
 
a
s
s
i
s
t
a
n
c
e
 
Dr. Jim Underwood
Mike Cappo
AIMS Monitoring Team
Conrad Speed
Owen O’Shea
Rachelle Ninio
 
P
l
a
c
e
s
 
H
e
l
p
f
u
l
 
I
n
s
i
g
h
t
s
 
Dr. Donald Jackson
Dr. Brian Shuter
Slide Note

Reef shark declines: Consequences for the trophic structure of communities of coral reef fishes

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This study delves into the repercussions of shark removal on the intricate ecosystem of coral reefs. It explores the correlation between shark abundance, reef fish community structure, benthic disturbances like cyclones and bleaching, and the synergistic effects of top-down and bottom-up processes. The research highlights the significant role of sharks in maintaining coral cover and the trophic structure of fish communities in coral reefs subjected to both natural disturbances and human activities like fishing.

  • Coral reefs
  • Shark removal
  • Ecosystem dynamics
  • Fish communities
  • Benthic disturbances

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  1. Taken out of context: the effects of shark removal in the dynamic environment of a coral reef Jonathan L.W. Ruppert, Mike Travers, Marie-Jos e Fortin and Mark G. Meekan

  2. Coral Reefs: Human Activity or TopPredators? High numbers sharks high coral cover, absent low coral cover Changes in trophic structure of fish communities Confounding of human activity (fishing down food chain) and natural disturbance Sandin et al. 2008 PLoS ONE

  3. Aims 1. 2. Does fishing impact shark abundance? Do changes in the abundance of sharks affect the structure of the reef fish community? How do benthic disturbances (cyclones, bleaching) alter fish communities? Are there synergistic effects of these top-down and bottom-up processes? 3. 4.

  4. Ashmore (Fished) Rowley Shoals (Non-Fished) Scott Reefs (Fished)

  5. Fished Reefs: Coral Bleaching 80 South Scott North Scott Seringapatam Coral Cover (Mean 95%CI) 60 40 20 0 1994 1996 1998 2000 2002 2004 2006 2008

  6. Non-Fished Reefs: Cyclonic Event 80 Mermaid Clerke Imperieuse Coral Cover (Mean 95%CI) 60 40 20 0 1994 1996 1998 2000 2002 2004 2006 2008

  7. Treatments: Fishing and Disturbance Fishing (Fished vs. Non-Fished) Shark density differences between Rowley and Scott Scott Reefs Rowley Shoals 80 Coral Cover (%) 60 Disturbance (Disturbed vs. Non-Disturbed) < 30% coral cover threshold 40 30% Coral Cover 20 0 1994 2001 2008

  8. Shark Community Data: BRUVS BRUVS (Baited Remote Underwater Video Station) All reefs (2003/2004) Target apex predators & carnivores Depth range: 5 100 m 1 to 1.5 hrs per drop MaxN statistic

  9. Trophic Structure of Coral Reef Fishes AIMS LTMP (Long-Term Monitoring Program) Scott and Rowley (1994 Present) 6 reefs; 3 sites each (n=18) Northeast reef slope Benthic surveys alongside Abundance counts (18 families; non-cryptic species; excludes recruits) SOURCE: AIMS

  10. Results: Shark Density (permuted ANOVA) 1.6 n = 94 = 9 p < 0.01 1.4 Sharks Hour (mean 95% CI) 1.2 1 n = 46 = 5 n = 28 = 5 0.8 0.6 0.4 0.2 0 Ashmore Reef Scott Reef Rowley Shoals

  11. Differences in Trophic Structure (RDA) 1 0.6 Fished/Disturbance Fished/No Disturbance Non-Fished/Disturbance Non-Fished/No Disturbance Fished vs. Non- Fished: Carnivores & Herbivores (Territorial & Non Territorial) Detritivore 0.4 Carnivore 0.2 RDA 2 (9.5 %) 0.0 0 RDA2 -0.2 Herbivore Herbivore_T Disturbance vs. Non-Disturbance: Herbivores, Planktivores, Corallivores, and Detritivores Planktivore Corallivore -0.4 -0.6 -1 -0.8 -0.5 0.0 0.5 RDA 1 (13.6 %) RDA1

  12. Trophic Group Responses: Carnivores * 60 Density Km-2 (mean 95%CI) 50 * p < 0.05 ** p < 0.01 40 Fished/Disturbance Fished/No Disturbance Non-Fished/Disturbance 30 Non-Fished/No Disturbance 20

  13. Trophic Group Responses: Herbivores 1000 ** ** Density Km-2 (mean 95%CI) * 850 * p < 0.05 ** p < 0.01 700 Fished/Disturbance Fished/No Disturbance Non-Fished/Disturbance 550 Non-Fished/No Disturbance 400

  14. Trophic Group Responses 120 80 ** ** ** Density Km-2 (mean 95%CI) 50 80 20 40 Corallivore ** Detritivore 2200 ** Fished/Disturbance Fished/No Disturbance Non-Fished/Disturbance Non-Fished/No Disturbance 1500 800 Planktivore

  15. Summary 1. Does fishing impact shark abundance? YES 2. Do changes in the abundance of sharks affect the structure of the reef fish community? YES Meso-predator release of carnivores andsubsequent trophic cascade during disturbances with herbivores 3. Do benthic disturbances alter fish communities? Are there synergistic effects of top-down and bottom-up processes? YES Herbivores, planktivores and corallivores show responses to changes in coral and algal cover Detritivores show synergistic responses

  16. Significance: Resilience Herbivores more abundant on unfished reefs where more sharks are present Central to recovery of reefs from processes that result in the loss of coral cover Implications for reef resilience

  17. Acknowledgements Funding/Data Field/lab assistance Dr. Jim Underwood Mike Cappo AIMS Monitoring Team Conrad Speed Owen O Shea Rachelle Ninio Places Helpful Insights Dr. Donald Jackson Dr. Brian Shuter

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