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Food-web Implications for Pelagic Top Predators:from Guts and Isotopes to Models
Robert J. OlsonInter-American Tropical Tuna CommissionLa Jolla, California
Photo compliments of Dr. Frederic Menard, IRD, France
Food webs and Ecosystem-based Fisheries Science
• “Ecosystem” “Ecology”: multispecies approaches to management, reduction of bycatch, including environmental factors in stock assessment models.
• Ecosystem: a geographically specified system of organisms, including humans, the environment, and the processes that control its dynamics (NOAA 2005).
• “The time has come for community ecology to replace population ecology as the fundamental ecological science underlying fisheries” (Mangel and Levin 2005).
• Communities are assemblages of species. Interactions makes the community more than the sum of its parts.
• Communities interact via the food web.
NOAA. 2005. New priorities for the 21st century: NOAA's strategic plan. NOAA, Washington, D.C.Mangel, M., and P.S. Levin. 2005. Regime, phase and paradigm shifts: making community
ecology the basic science for fisheries. Phil. Trans. R. Soc. B, 360 (1453): 95-105.
Why study food webs?
• Trophic structure represented in food webs is thought to be the central organizing concept in ecology (Martinez 1995).
• Knowledge of pelagic food webs is still rudimentary, in many aspects. Better food-web models are needed (preferably, spatially-explicit).
• Review an assortment of information about food-web research in eastern Pacific, and (less-so) on modeling efforts.
Eight ecosystem characteristics
1. The ability to predict ecosystem behavior is limited2. Ecosystems have thresholds and limits which, when
exceeded, can effect major ecosystem restructuring3. Once thresholds and limits have been exceeded,
changes can be irreversible4. Diversity is important to ecosystem functioning5. Multiple scales interact within and among ecosystems6. Components of ecosystems are linked7. Ecosystem boundaries are open8. Ecosystems change over time
NMFS Ecosystem Principles Advisory Panel:
Components of ecosystems are linked
How do we determine what the important components and linkages are? Critical food-web connections.
•Keystone species•Dietary specialists•Models can help
The tools for food-web research:•Diet studies (stomach-contents analysis)•Stable isotope analysis•Compound specific stable isotope analysis (amino-acids)•Fatty acid analysis
Stomach-contents analysis (species identification) (and monitoring)
V. Allain, SPCF. Galvan, CICIMARIATTC, Manta, Ecuador
Perc
ent
wei
ght
TunasDolphins
SharksBillfishes
Dorado, Wahoo, R. Runner
0%
20%
40%
60%
80%
100%
Diet data for eastern Pacific predators (’92-’94)
Colleagues:•Felipe Galván-M, CICIMAR, La Paz, BCS, Mexico•Julio Martínez, Cumaná, Venezuela
Diet data formulated food web (ETP)Tr
ophi
c le
vel –
Niv
eltró
fico
Olson, R.J., and G.M. Watters. 2003. A model of the pelagic ecosystem in the eastern tropical Pacific Ocean. Inter-American Tropical Tuna Commission, Bulletin 22 (3): 133-218.
Feeding Ecology of Surface Migrating Myctophid Fishesin the eastern Tropical Pacific
Joel Van Noord, Univ. of San DiegoJessica Redfern et al., NMFS SWFSC
Trophic position: stable isotopes
Isotopic fractionation – the light 14N isotope is excreted more than the heavy 15N isotope, leaving the animal enriched by 3‰ in δ15N relative to its food source.
δ15Npredator 3.0 + δ15Nprey (‰)=δ15N [(15N/14N) / Rstd – 1] x 1000=
Trophic position: stable isotopes,stomach contents
0
2
4
6
8
10
12
14
16
18
-15 -10 -5 0 5 10 15 20 25 30Latitude (degrees)
δ15N
(‰)
Yellowfin tuna (5-deg areas)
Yellowfin tuna (outside 5-deg areas)
Mesozooplankton (5-deg areas)
Mesozoopl. (outside 5-deg areas)
CSIA samples
Mean TP = 4.5
PFRP, B. Popp, B. Graham, C. Hannides, F. Galván, G. López, B. Fry
Copepods δ15N = 6-12‰
YFT δ15N = 13-16‰
Gladis Lopez-I., CICIMAR, Mexico
Yellowfin trophic position (TP)
ΔYFT-COP = 4.0 – 7.6 ‰
TP ≈ 4.3 - 5.3,spanning ~ 1 trophic level
B. Popp, UHB. Graham, UHF. Galvan-Magana, CICIMARC. Lennert-Cody, IATTCPFRP
δ15N of Amino Acids
TL 4.5
Bulk white muscle
Yellowfin tuna – eastern tropical Pacific
(“Source” AA)
(“Trophic” AA)
Popp
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Traditional techniques problematic, e.g. gut content analysis
Prey species have unique lipid / fatty acid compositions
Many fatty acids readily transferred from prey to predator with minimal modification
Constituent fatty acids therefore represent, to some extent, a temporal integration of diet
Can be quantitative and allows temporal integration (cf gut content analysis)
Signature fatty acids: combinations of fatty acids preserved as they pass up the food chain
Complements other approaches
Lipids as Dietary Tracers
* Jock Young, CSIRO
Eight ecosystem characteristics
1. The ability to predict ecosystem behavior is limited2. Ecosystems have thresholds and limits which, when
exceeded, can effect major ecosystem restructuring3. Once thresholds and limits have been exceeded,
changes can be irreversible4. Diversity is important to ecosystem functioning5. Multiple scales interact within and among ecosystems6. Components of ecosystems are linked7. Ecosystem boundaries are open8. Ecosystems change over time
NMFS Ecosystem Principles Advisory Panel:
Can models predict ecosystem behavior?
• Nature is seldom linear, and often unpredictable (Francis et al. 2007) .
• Ecosystem resilience depends on “stability domain” of existing food web: how broad is it, how resistant is it to change, how close is it to reorganizing? (Francis et al. 2007) Models are required.
• How should components of the food web be represented in models?
• Can models highlight key areas for field/lab studies?
Francis, R.C., M.A. Hixon, M.E. Clarke, S.A. Murawski, and S. Ralston. 2007. Ten commandments for ecosystem-based fisheries scientists. Fisheries, 32 (5): 217-233.
Taxonomy in modelsTr
ophi
c le
vel –
Niv
eltró
fico
(Olson, R.J., and G.M. Watters. 2003. A model of the pelagic ecosystem in the eastern tropical Pacific Ocean. Inter-American Tropical Tuna Commission, Bulletin 22 (3): 133-218.)
Qualitative analysis of Pacific Ocean predators
20 N20 N20 N20 N20 N20 N20 N20 N20 N
South-Western Pacific Ocean
Trop
hic
leve
l236
183
119
112
219
153
210
235
126
92
177
71
196
27
185
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232
63
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180
52
142 105
234
193
174
114
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207199 200201 202203 205206
215
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182 228241
165167155 156 161163 157
168
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10293
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64
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83149
2
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1314
69
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66 65
151127117
122115
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121124
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10615277
7574 76
38
96 9495 990
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49
5.0
4.5
4.0
3.5
3.0
2.5
2.0
1.5
1.0
236
183
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219
153
210
235
126
92
177
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196
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232
63
212
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180
52
142 105
234
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174
114
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108
23815
195191192
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215
197
179
182 228241
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168
169
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4 3
64
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116
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7574 76
38
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145
49
5.0
4.5
4.0
3.5
3.0
2.5
2.0
1.5
1.0
Central-Eastern Pacific Ocean
245
219
153
126
231
80
27
82
56
24
239
243
242 217
223
172
103
57 59
32
36
85
7879 81
109
113
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178
246237247 216244
134
91
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194
53
211
204
198 215
226229
165154157 160159
170 168
169
645860 51
37
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20 18
65
127
122115 121
110
124106
125108
118
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95 8889 69
143
47
173
5.0
4.5
4.0
3.5
3.0
2.5
2.0
1.5
1.0
245
219
153
126
231
80
27
82
56
24
239
243
242 217
223
172
103
57 59
32
36
85
7879 81
109
113
98
178
246237247 216244
134
91
222
194
53
211
204
198 215
226229
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170 168
169
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5.0
4.5
4.0
3.5
3.0
2.5
2.0
1.5
1.0
Food webs composed of 200+ taxa
Aggregated food webs composed of 24 nodes with similar predator prey relationships
0 20 40 60 80 100 120 140 160
Producers
Primary Consumers
Secondary Consumers
Misc. Epipelagic Fishes
Flyingfishes
Misc. Mesopelagic Fishes
Crabs
Sea Turtles
Grazing Birds
Rays
Baleen Whales
Auxis spp.
Bluefin Tuna
Misc. Piscivores
Small Swordfish
Cephalopods
Skipjack Tuna
Small Yellowfin Tuna
Small Bigeye Tuna
Small Wahoo
Mesopelagic Dolphins
Large Yellowfin Tuna
Large Mahimahi
Small Sailfish
Small Mahimahi
Pursuit Birds
Large Sailfish
Large Swordfish
Large Wahoo
Large Sharks
Spotted Dolphins
Large Bigeye Tuna
Toothed Whales
Small Marlins
Small Sharks
Large MarlinsLarge marlinsSmall sharks
Small marlinsToothed whales
Large bigeyeSpotted dolphins
Large sharksLarge wahoo
Large swordfishLarge sailfishPursuit birds
Small mahimahiSmall sailfish
Large mahimahiLarge yellowfin
Mesopelagic dolphinsSmall wahooSmall bigeye
Small yellowfinSkipjack
CephalopodsSmall swordfishMisc. piscivores
Bluefin tunaAuxis spp.
Baleen whalesRays
Grazing birdsSea turtles
CrabsMisc. mesopelagic fishes
FlyingfishesMisc. epipelagic fishesSecondary consumers
Primary consumersProducers
Index of Sensitivity
(5.1)(5.1)(5.1)(4.9)(4.8)(4.8)(4.8)(4.8)(4.8)(4.7)(4.7)(4.7)
(5.3)(5.2)
(5.2)
(4.6)(4.5)(4.5)
(4.7)
(4.1)(3.9)(3.9)(3.8)(3.6)(3.6)(3.6)
(4.1)
(4.6)
(3.3)(3.0)
(2.0)(1.0)
(5.5)(5.4)
(5.4)(5.4)
CephalopodsAuxis spp.
Can models highlight research needs?Sensitivity analysis of ETP Ecopath model
Eight ecosystem characteristics
1. The ability to predict ecosystem behavior is limited2. Ecosystems have thresholds and limits which, when
exceeded, can effect major ecosystem restructuring3. Once thresholds and limits have been exceeded,
changes can be irreversible4. Diversity is important to ecosystem functioning5. Multiple scales interact within and among ecosystems6. Components of ecosystems are linked7. Ecosystem boundaries are open8. Ecosystems change over time
NMFS Ecosystem Principles Advisory Panel:
Ecosystems change over time
• Jumbo (Humboldt) squid range expansion
• Are tunas effective biological samplers of the middle trophic levels*? Indicator species in stomach contents?– Squid consumption by tunas has increased over time
– Decadal changes in yellowfin tuna diet composition
* Generalist predators (opportunistic), high energy requirements, food limited, range widely, prey size-predator size ranges widely
Pelagic ommastrephid squids (e.g. Dosidicus gigas): Ecosystem indicators?
Olson, R.J., M.H. Román-Verdesoto, and G.L. Macías-Pita. 2006. Bycatch of jumbo squid Dosidicus gigas in the tuna purse-seine fishery of the eastern Pacific Ocean and predatory behaviour during capture. Fish. Res. 79(1-2): 48-55.
Percent frequency of cephalopods in the stomach contents of yellowfin tuna in the eastern Pacific Ocean
Hunsicker, Essington, Olson, Duffy. Manuscript in prep. “Evidence of increased cephalopod production in a large marine ecosystem.”
1955-1960 1969-1972 1992-1994 2003-2005
Per
cent
freq
uenc
y of
occ
urre
nce
0
20
40
60
80
100
UnidentifiedOctopusSquidAll cephalopods
PFRP, F. Galvan,N. Bocanegra, V. Alatorre, J. Martinez, F. Alverson
Decadal variation in yellowfin tuna diet composition
• Nonparametric: relationships between variables that may include: nonlinearity, high order interactions, lack of balance, missing values
• Combinations of explanatory variables used to explain variation of a response variable (prey groups % weight), by repeatedly splitting the data into groups that are as homogenous as possible
• Each possible value for each explanatory variable is considered as a potential candidate split
• The candidate split which provides the largest decrease in impurity, or minimizes the misclassification rate, is chosen to split the data into two subgroups
• Procedure is repeated with each subgroup until no significant decrease in impurity is possible, resulting in a terminal node (leaf).
• 10-fold cross-validation used to prune trees (1-SE Rule) • The proportions in each category are represented in each leaf
Classification tree model constructed using the Diet library of R written by Petra Kuhnert, CSIRO
Classification tree analysis
Classification tree analysis
Cephalopods• Argonauta spp.• Dosidicus gigas• Sthenoteuthis oualaniensis
Crustaceans• Pleuroncodes planipes• Portunidae family• Other Crustaceans
Fishes• Cetengraulis mysticetus• Engraulis mordax• Phosichthyidae family• Myctophidae family• Exocoetus spp.• Other Exocoetids• Oxyporhamphus micropterus• Carangidae family• Auxis spp.• Scomber japonicus• Cubiceps spp.• Lactoria diaphana
Response variable(18 dominant prey groups)
Explanatory variables
• Year
• Quarter of year
• Purse-seine set time of day
• Latitude
• Longitude
• SST
• Yellowfin size
• Yellowfin sex
• Yellowfin stomach fullness
• Purse-seine set type
Prop
ortio
n Re
lativ
e Im
port
ance
0.0
0.2
0.4
0.6
0.8
1.0
Classification Tree Analysis: Variable Importance Rankings
Predictor variable
Lat = latitude, Lon = longitude, SST = Sea Surface Temperature, YR = year,SA = set type, Qtr = quarter, Time = set time of day, FL = yellowfin fork length,Full = yellowfin stomach fullness
b-DG: Dosidicus gigasc-SO: Sthenoteuthis oualaniensise-PP: Pleuroncodes planipesg-CM: Cetengraulis mysticetush-EM: Engraulis mordaxi-Phos: Phosichthyidae familym-OM: Oxyporhamphus micripterusn-Car: Carangidae familyo-Aux: Auxis spp.p-SJ: Scomber japonicusq-Cub: Cubiceps spp.r-LD: Lactoria diaphana
squids
crustacean
fishes
R2 = 0.45
N of 17.3°N
0%
5%
10%
15%
20%
25%
30%
35%
Mea
n %
Wei
ght (
±2S
E)
north of latitude 17.3N
south of latitude 17.3N
Yellowfin tuna diet composition at first split
b-DG: Dosidicus gigasc-SO: Sthenoteuthis oualaniensise-PP: Pleuroncodes planipesg-CM: Cetengraulis mysticetush-EM: Engraulis mordaxi-Phos: Phosichthyidae familym-OM: Oxyporhamphus micripterusn-Car: Carangidae familyo-Aux: Auxis spp.p-SJ: Scomber japonicusq-Cub: Cubiceps spp.r-LD: Lactoria diaphana
squids
crustacean
fishes
R2 = 0.45
South of 4.8° S
Set Locations
1990s
2000s
North of Latitude 17.3°N
Yellowfin tuna stomach sample locations
South of Latitude 4.8°S
0%
10%
20%
30%
40%
50%
60%
70%
mea
n %
W (±
2SE)
North of Latitude 4.8°SSouth of Latitude 4.8°S
Yellowfin tuna diet composition
Jumbo squid
Anchoveta
Set Locations
1990s
2000s
South of Latitude 17.3°N
Yellowfin tuna stomach sample locations
North of Latitude 4.8°S
b-DG: Dosidicus gigasc-SO: Sthenoteuthis oualaniensise-PP: Pleuroncodes planipesg-CM: Cetengraulis mysticetush-EM: Engraulis mordaxi-Phos: Phosichthyidae familym-OM: Oxyporhamphus micripterusn-Car: Carangidae familyo-Aux: Auxis spp.p-SJ: Scomber japonicusq-Cub: Cubiceps spp.r-LD: Lactoria diaphana
squids
crustacean
fishes
R2 = 0.45
0%
5%
10%
15%
20%
25%
30%
35%
40%
45%
Mea
n %
Wei
ght (
±2S
E)
Yellowfin tuna diet composition at time split (south of latitude 17.3 N, north of latitude 6.1 S, SST ≥23.42
1992-1994 diet composition2003-2005 diet composition
Yellowfin tuna diet composition at year split
Jumbo squid
Auxis spp.
Mesopel. fishesEpipel. fishes
Summary
• Research on pelagic food webs is progressing; should be encouraged.
• Chemical tracer methods are providing insight (SIA, AA-CSIA, fatty acids).
• Stomach contents analyses are still necessary (monitoring indicator prey species).
• Better ecosystem (food web) models are needed (spatially-explicit). Identify critical food-web connections.
• Food-web models should depict taxonomic ecosystem components (indicator species).
• Epipelagic ecosystems appear to change over time.
• Recommendation: low-level, well-designed, continuous stomach sampling of tunas, biological samplers, to monitor changes.
Acknowledgements• Pelagic Fisheries Research Program and John Sibert, Univ.
Hawaii• NOAA Fisheries STAR Project, Lisa Ballance, G. Watters, and
many others• IATTC observers and staff in Ecuador and Mexico• Brian Popp, B. Graham, N. Wallsgrove, E. Gier, J. Tanimoto, T.
Rust, A. Carter, Isotope Biogeochemistry Laboratory, Univ. Hawaii
• Felipe Galván-Magaña, G. López-Ibarra, N. Bocanegra-Castillo, V. Alatorre-Ramírez, CICIMAR, La Paz Mexico
• Tim Essington, M. Hunsicker, Univ. Washington• C. Lennert-Cody, M. Maunder, L. Duffy, M. Román-Verdesoto, C.
Patnode, G.L. Macías-Pita, IATTC • B. Fry, Louisiana State Univ., Baton Rouge• V. Allain, Secretariat of the Pacific Community, New Caledonia• Jock Young, Jeff Dambacher, CSIRO• Jim Kitchell, Univ. Wisconsin