Ecological Archives A025-023-A1
Laurel A. Smith, Jason S. Link, Steven X. Cadrin, and Debra L. Palka. 2015. Consumption by marine mammals on the Northeast U.S. continental shelf. Ecological Applications 25:373–389. http://dx.doi.org/10.1890/13-1656.1
Appendix A. Marine mammal abundance estimation summarized from Link et al. 2006.
Abundance estimates were derived for most cetaceans from summer 2004 and 2006 NEFSC marine mammal surveys (Waring et al. 2009). Right whale abundance was the exception, which was based on the 2004 aerial photo census from the North Atlantic Right Whale Sighting Survey (Neimeyer et al. 2008). Shipboard and aerial abundance estimates within the NEUS shelf region were derived from the length of track lines (L), number of sightings (n), and average group size (s) within each of the four ecoregions (Table A1) and the estimates of the effective strip width (esw) and g(0) (the probability that an animal on the track line is detected) derived from the entire survey. Thus, the abundance for a species k within ecoregion i on platform j (ship or plane) was:
where Aij was the area within ecoregion i that was surveyed by platform j. The total abundance for species k within a region was the sum of the aerial and shipboard abundance estimates for that species.
Abundance estimates from these surveys represent the summer season, however each species has different migration patterns and timings of when they utilize the NEUS shelf region. Therefore seasonal residence ratios within each ecoregion were defined as a proportion of the summer population within that region during a given season (Table A2), based on expert opinion and general patterns documented in the Cetacean and Turtle Assessment Program (CETAP 1982) and Department of Navy (2005). The seasons were defined as summer (June to August), fall (September to November), winter (December to February), and spring (March to May).
Literature cited
Lockyer, C. and S. G. Brown. 1978. Biology of fin and sei whales off Iceland. ICES CM N:6.
Schevill, W. E. 1956. Lagenorhynchus acutus off Cape Cod. J. Mammal 37:128-129.
Table A1. Areas of the four ecoregions used to calculate abundance for cetacean species, from Link et al. 2006.
Region |
2004 area (km²) |
2004 track length (km) |
||||
|
total |
ship |
plane |
total |
ship |
plane |
Gulf of Maine |
79,127.953 |
0.000 |
79,127.953 |
2,787.415 |
0.000 |
2,787.415 |
Georges Bank |
43,666.157 |
5,944.480 |
37,721.676 |
1,000.495 |
239.953 |
760.542 |
Southern New England |
64,060.370 |
10,466.536 |
53,593.834 |
2,157.936 |
477.454 |
1,680.482 |
Mid-Atlantic Bight |
59,807.290 |
3,774.530 |
56,032.760 |
875.180 |
131.696 |
743.484 |
TOTAL |
246,661.770 |
20,185.547 |
226,476.223 |
6,821.026 |
849.103 |
5,971.923 |
strata |
2006 area (km²) |
2006 track length (km) |
||||
|
total |
ship |
plane |
total |
ship |
plane |
Gulf of Maine |
79,127.953 |
0.000 |
79,127.953 |
2,989.794 |
0.000 |
2,989.794 |
Georges Bank |
43,666.157 |
0.000 |
43,666.157 |
1,133.424 |
0.000 |
1,133.424 |
Southern New England |
64,060.370 |
0.000 |
64,060.370 |
1,808.127 |
0.000 |
1,808.127 |
Mid-Atlantic Bight |
59,807.290 |
0.000 |
59,807.290 |
0.000 |
0.000 |
0.000 |
TOTAL |
246,661.770 |
0.000 |
246,661.770 |
5,931.345 |
0.000 |
5,931.345 |
Table A2. Seasonally-weighted average abundance estimates of cetacean species found in four ecoregions of the NEUS shelf: Georges Bank (GB), Gulf of Maine (GOM), Mid-Atlantic Bight (MAB) and Southern New England (SNE), from Link et al. 2006.
Species |
Region |
Summer Abundance Estimate |
% of Population in Region by Season |
Seasonally Weighted Average Abundance |
|||
Winter |
Spring |
Summer |
Fall |
||||
Fin or Sei Whale |
GB |
183.96 |
0.2 |
1.3 |
1 |
0.4 |
133.37 |
GOM |
1343.82 |
0.1 |
0.9 |
1 |
0.7 |
907.08 |
|
MAB |
78.82 |
0.21 |
1 |
1 |
0.2 |
47.29 |
|
SNE |
463.05 |
0.1 |
0.8 |
1 |
0.3 |
254.68 |
|
Humpback Whale |
GB |
100.14 |
0.1 |
1.2 |
1 |
0.2 |
62.59 |
GOM |
516.38 |
0.1 |
1 |
1 |
0.3 |
309.83 |
|
MAB |
100 |
0.2 |
1 |
0 |
1 |
55 |
|
SNE |
100 |
0.1 |
1 |
0 |
1 |
52.5 |
|
Minke Whale |
GB |
64.17 |
0 |
1.3 |
1 |
0.1 |
38.5 |
GOM |
753.25 |
0.05 |
0.8 |
1 |
0.2 |
386.04 |
|
MAB |
100 |
0 |
2 |
1 |
0 |
75 |
|
SNE |
117.18 |
0 |
1.5 |
1 |
0.1 |
76.17 |
|
Right Whale |
GB |
325 |
0.2 |
0.4 |
0.2 |
0.3 |
89.38 |
GOM |
325 |
0 |
0.1 |
0.7 |
0.5 |
105.63 |
|
MAB |
325 |
0.3 |
0.3 |
0.1 |
0.1 |
65 |
|
SNE |
325 |
0 |
0.2 |
0 |
0.1 |
24.38 |
|
Pilot Whale |
GB |
2488.99 |
0.1 |
2 |
1 |
0.3 |
2115.39 |
GOM |
2610 |
0.1 |
0.8 |
1 |
0.5 |
1566 |
|
MAB |
174.68 |
0.3 |
1 |
1 |
1 |
144.11 |
|
SNE |
1076.31 |
0.1 |
2 |
1 |
0.3 |
914.86 |
|
Bottlenose Dolphin |
GB |
741.95 |
0.05 |
1 |
1 |
0.2 |
417.34 |
MAB |
8491.67 |
0.05 |
1 |
1 |
0.7 |
5838.03 |
|
SNE |
6232.96 |
0.05 |
1 |
1 |
0.5 |
3817.69 |
|
Common Dolphin |
GB |
10739.24 |
2 |
1.5 |
1 |
2 |
17451.27 |
GOM |
9369.25 |
0.7 |
0.7 |
1 |
1.5 |
9135.02 |
|
MAB |
2634.32 |
2 |
2 |
1 |
0.2 |
3424.62 |
|
SNE |
5862.25 |
2 |
2 |
1 |
2 |
10258.93 |
|
Whiteside Dolphin |
GB |
709.99 |
0.3 |
2 |
1 |
1 |
763.24 |
GOM |
20767.04 |
0.2 |
0.7 |
1 |
0.7 |
13498.58 |
|
SNE |
1317.21 |
0 |
2 |
1 |
0.5 |
1152.56 |
|
Harbor Porpoise |
GB |
30607.5 |
0.05 |
0.6 |
0 |
0.3 |
7269.28 |
GOM |
30607.5 |
0.4 |
0.4 |
0 |
0.3 |
8417.06 |
|
MAB |
30607.5 |
0.4 |
0.4 |
0 |
0.3 |
8417.06 |
|
SNE |
30607.5 |
0.3 |
0.4 |
0 |
0.3 |
7651.88 |
Table A3. Summer abundance estimates, residency ratio and mean individual mass used to calculate consumption estimates within the Northeast US (NEUS) continental shelf study area.
Common Name |
Species name |
Survey Year |
Summer Abundance Estimate* |
CV of Summer Abundance |
Source for Abundance Estimates** |
Residence Ratio* |
Residence Ratio Adjusted* |
Annual Abundance* |
Mean Individual Weight (kg)* |
Fin whale |
Balaenoptera physalus |
2004 |
1,364 |
0.686 |
a |
0.65 |
885 |
50,000 |
|
Humpback whale |
Megaptera novaeangliae |
2006 |
272 |
0.824 |
a |
0.59 |
0.82 |
223 |
30,408 |
Right whale |
Eubalaena glacialis |
2004 |
128 |
b |
0.22 |
0.80 |
102 |
23,383 |
|
Sei whale |
Balaenoptera borealis |
2004 |
1,128 |
0.996 |
a |
0.58 |
655 |
16,811 |
|
Minke whale |
Balaenoptera acutorostrata |
2006 |
2,931 |
0.848 |
a |
0.56 |
1,631 |
6,566 |
|
Pilot whale |
Globicephala sp. |
2004 |
11,388 |
0.490 |
a |
0.75 |
8,502 |
851 |
|
Bottlenose dolphin |
Tursiops truncatus |
2004 |
2,241 |
0.676 |
a |
0.66 |
1,481 |
188 |
|
Atlantic white-sided dolphin |
Lagenorhynchus acutus |
2006 |
8,909 |
0.389 |
a |
0.68 |
6,025 |
92 |
|
Common dolphin |
Delphinus delphis |
2004 |
60,998 |
0.635 |
a |
0.93 |
56,878 |
80 |
|
Harbor porpoise |
Phocoena phocoena |
2006 |
18,358 |
0.564 |
a |
0.26 |
4,762 |
31 |
|
Gray seal |
Halichoerus grypus |
2008 |
10,783 |
0.337 |
c |
1 |
10,783 |
181 |
|
Harbor seal |
Phoca vitulina concolor |
2001 |
99,340 |
0.097 |
d |
1 |
|
99,340 |
75 |
*Methods for calculating these estimates are detailed in the Appendix 1 text.
**a: NEFSC marine mammal surveys (Waring et al. 2009), b: Aerial photo census from the North Atlantic Right Whale Sighting Survey (Neimeyer et al. 2008), c: Aerial pinniped pup counts off of the New England coast (Wood 2009), expanded to total population estimate by using a 4.116 ratio of pups to adults, based on surveys from the United Kingdom (SCOS 2008), d: Aerial pinniped survey (Waring et al. 2009)
Table A4. Prey species included in marine mammal prey groups and for comparisons to commercial fishing catches.
Marine mammal prey group |
Common names of prey |
Scientific names of prey |
Species included for commercial catch |
Squid |
Longfin squid, shortfin squid, other squid, octopus |
Loligo spp., Illex spp., Teuthida, Octopodidae |
Longfin squid, shortfin squid |
Mesopelagic fish |
Lanternfish, pearlsides, myctophids |
Myctophidae, Maurolicus spp. |
|
Clupeids |
Atlantic herring, river herring, saury, anchovies |
Clupea harengus, Alosa spp., Scomberesox saurus, Anchoa spp., Engraulis eurystole |
Atlantic herring |
Scombrids |
Atlantic mackerel, king mackerel, jacks, scads |
Scomber scombrus, Scomberomorus, cavalla, Carangidae |
Atlantic mackerel |
Large gadids |
Atlantic cod, haddock, pollock |
Gadus morhua, Melanogrammus aeglefinus, Pollachius virens |
Atlantic cod, haddock, pollock |
Small gadids |
Red hake, silver hake, white hake, spotted hake, rocklings |
Urophycis chuss, Meluccius bilinearis, Urophycis tenuis, Urophycis regia, Enchelyopus cimbrius |
Red hake, silver hake, offshore hake, white hake |
Shrimp |
Northern shrimp, prawns, krill |
Paldalus spp., Farfantepenaeus spp., Euphausiidae |
|
Zooplankton |
Copepods, amphipods, mysids, caprellids, fish larvae, invertebrate larvae |
Calanus finmarchicus, Pseudocalanus spp., Amphipoda, Mysidae, Caprellidae, Osteichthyes |
|
Benthic invertebrates |
Bivalves, gastropods, decapods |
Bivalvia, Gastropoda, Decapoda |
|
Sandlance |
Sandlance, capelin, silversides, argentine |
Ammodytoides spp., Mallotus villosus, Atherinidae, Argentinidae |
|
Flatfish |
Flounders |
Pleuronectiformes |
Yellowtail flounder, winter flounder, summer flounder, witch flounder, American plaice, Atlantic halibut, windowpane flounder |
Miscellaneous fish |
Skates, dogfish, redfish, lumpfish, ocean pout, hagfish, wolffish, butterfish, cunner, sea raven, unclassified or unidentified fish |
Rajidae, Squalis acanthias, Sebastes fasciatus, Cyclopterus lumpus, Zoarces americanus, Myxine glutinosa, Anarhichas lupus, Peprilus triacanthus, Tautogolabrus adspersus, Hemitripterus americanus, Osteichthyes |
|
Table A5. Diet composition of humpback whales from literature sources.
|
Percent Diet Composition by Source |
|||||||||||||||||
1 |
2 |
3 |
4 |
5 |
6 |
7 |
8 |
9 |
10 |
11 |
12 |
13 |
14 |
|||||
Prey |
b |
g |
h |
i |
j |
j |
a |
b |
k |
l |
c |
d |
e |
f |
m |
l |
n |
|
Herring |
P |
P |
0.17 |
O |
I |
|||||||||||||
Capelin |
P |
P |
P |
0 |
||||||||||||||
Saffron cod |
P |
|||||||||||||||||
Euphausiids |
P |
1.0 |
0.8 |
P |
0.8 |
0.667 |
I |
|||||||||||
Mackerel |
P |
P |
0.2 |
|||||||||||||||
Krill |
P |
|||||||||||||||||
Sand lance |
P |
0.6 |
0 |
I |
||||||||||||||
Fish/white fish |
P |
0.95 |
0.3 |
0.2 |
0.6 |
0 |
||||||||||||
Zooplankton |
0.05 |
0.55 |
0.4 |
|||||||||||||||
Small pelagics |
0.15 |
I |
||||||||||||||||
Copepods |
0 |
0 |
P |
|||||||||||||||
Squid |
0 |
0 |
P |
|||||||||||||||
Alaska pollock |
0 |
|||||||||||||||||
Sardine |
0.333 |
|||||||||||||||||
Demersal fish |
P |
|||||||||||||||||
Nektonbenthonic crustaceans |
P |
|||||||||||||||||
Banded drum |
0.396 |
|||||||||||||||||
Atlantic croaker |
0.564 |
|||||||||||||||||
Spot |
0.023 |
|||||||||||||||||
Weakfish |
0.014 |
|||||||||||||||||
Red drum |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
0.003 |
|
*1:Kawamura 1980, 2:Hjort and Rudd 1929, 3:Mitchell 1974, 4:Overholtz et al. 1991, 5:Kenney et al. 1985, 6:Pauly et al. 1998, 7:Mitchell 1973, 8:Nemoto and Kawamura 1977, 9:Sigurjonsson and Vikingsson 1992, 10:Hain et al. 1982, 11:Christensen et al. 1990, 12:Nemoto 1959, 13:Frost and Lowry 1981, 14:Laerm et al. 1997, 15:Weinrich et al. 1997
**a:North Pacific, b:North Atlantic, c:Nova Scotia, d:Gulf of Maine, e:multiple regions, f:Antarctic, g:Iceland, h:Northeast US, i:Norway, May to early summer, j:Norway, mid-summer to early winter, k:North Pacific, l:waters adjacent to Japan, m:Berring Sea, n:Stellwagen Bank
***P:prey present, I:important prey, O:occational prey
Table A6. Mean diet compositions of marine mammals by standard prey groups, based on literature sources. Minimum and maximum diet compositions from literature are in parenthesis.
Large gadids |
Small gadids |
Flatfish |
Clupeids |
Scombrids |
Sandlance |
Meso-pelagics |
Misc. fish |
Benthic invertebrates |
Squid |
Shrimp |
Zoo-plankton |
Literature Sources |
||
Fin whale |
(0) |
(0) |
|
(0.0015) |
(0.00035) |
(0.015) |
(0) |
(0.00091) |
|
(0.00093) |
(0.40) |
(0.00025) |
3, 5, 9, 12, 13, 16, 19, 22, 26, 31, 33, 49, 53, 78, 86, 96 |
|
0.0040 |
0.0031 |
0.088 |
0.040 |
0.052 |
0.0032 |
0.033 |
0.036 |
0.63 |
0.11 |
|||||
(0.018) |
(0.015) |
|
(0.51) |
(0.25) |
(0.25) |
(0.050) |
(0.20) |
|
(0.20) |
(0.99) |
(0.30) |
|||
Humpback whale |
|
(0.00080) |
|
(0.021) |
(0.0063) |
(0.0030) |
|
(0.025) |
|
(0.00033) |
(0.050) |
(0.00040) |
1, 5, 7, 8, 9, 12, 19, 22, 24, 31, 41, 49, 53, 72, 75, 78 |
|
0.022 |
0.12 |
0.076 |
0.20 |
0.19 |
0.011 |
0.37 |
0.021 |
|||||||
|
(0.25) |
|
(0.13) |
(0.50) |
(0.63) |
|
(1.0) |
|
(0.13) |
(1.0) |
(0.25) |
|||
Right whale |
|
|
|
|
|
|
|
|
|
|
(0.00074) |
(0.25) |
6, 9, 12, 18, 28, 29, 31, 37, 38, 42, 78, 102 |
|
0.15 |
0.85 |
|||||||||||||
|
|
|
|
|
|
|
|
|
|
(1.0) |
(1.0) |
|||
Sei whale |
(0) |
(0.0011) |
|
(0.0051) |
(0.0020) |
(0.0020) |
(0.0002) |
(0.00064) |
|
(0.0015) |
(0.029) |
(0.036) |
5, 9, 12, 11, 13, 16, 18, 19, 26, 19, 33, 53, 78, 79, 86 |
|
0.016 |
0.0016 |
0.070 |
0.017 |
0.038 |
0.017 |
0.039 |
0.055 |
0.33 |
0.42 |
|||||
(0.17) |
(0.0082) |
|
(0.41) |
(0.14) |
(0.33) |
(0.17) |
(0.25) |
|
(0.29) |
(1.0) |
(0.89) |
|||
Minke whale |
(0.000059) |
(0.00023) |
(0) |
(0.0025) |
(0.00019) |
(0.00023) |
|
(0.000066) |
|
(0.00011) |
(0.0048) |
(0) |
22, 25, 30, 32, 47, 48, 49, 50, 52, 59, 62, 65, 70, 74, 78, 108 |
|
0.13 |
0.031 |
0.00010 |
0.30 |
0.039 |
0.16 |
0.015 |
0.0063 |
0.32 |
0.0065 |
|||||
(0.86) |
(0.50) |
(0.0026) |
(1.0) |
(0.82) |
(1.0) |
|
(0.13) |
|
(0.17) |
(1.0) |
(0.17) |
|||
Pilot whale |
|
(0.0013) |
|
(0.00075) |
(0.011) |
|
(0) |
(0.0019) |
(0) |
(0.29) |
|
|
45, 49, 53, 57, 68, 69, 71, 78, 92, 96, 101, 104, 106, 110 |
|
0.012 |
0.027 |
0.14 |
0.0046 |
0.088 |
0.0084 |
0.72 |
||||||||
|
(0.11) |
|
(0.20) |
(0.71) |
|
(0.050) |
(0.46) |
(0.081) |
(1.0) |
|
|
|||
Bottlenose dolphin |
(0.020) |
(0.0014) |
(0.00021) |
(0.00073) |
(0.00050) |
(0.00027) |
(0.00013) |
(0.041) |
(0) |
(0.0014) |
(0.00019) |
|
15, 43, 57, 59, 76, 78, 82, 84, 85, 89, 91, 92, 93, 98, 106, 109 |
|
0.056 |
0.18 |
0.0011 |
0.065 |
0.041 |
0.0073 |
0.00032 |
0.50 |
0.0050 |
0.15 |
0.00043 |
||||
(0.59) |
(0.77) |
(0.010) |
(0.16) |
(0.31) |
(0.082) |
(0.0030) |
(1.0) |
(0.079) |
(0.88) |
(0.0040) |
|
|||
Atlantic white-sided dolphin |
(0.00028) |
(0.0064) |
(0) |
(0.0029) |
(0.0012) |
(0.037) |
(0.014) |
(0.017) |
(0) |
(0.051) |
|
|
2, 4, 14, 21, 67, 73, 78, 105, 108 |
|
0.093 |
0.25 |
0.00053 |
0.18 |
0.048 |
0.079 |
0.080 |
0.050 |
0.0094 |
0.21 |
|||||
(0.56) |
(0.66) |
(0.0057) |
(0.51) |
(0.50) |
(0.60) |
(0.50) |
(0.40) |
(0.10) |
(0.50) |
|
|
|||
Common dolphin |
(0) |
(0.00025) |
(0) |
(0.00042) |
(0.00090) |
(0.00069) |
(0.00067) |
(0.014) |
(0) |
(0.019) |
|
|
45, 49, 57, 59, 60, 67, 78, 88, 92, 97, 99, 100, 105, 106 |
|
0.0010 |
0.15 |
0.00017 |
0.084 |
0.21 |
0.010 |
0.080 |
0.24 |
0.0013 |
0.22 |
|||||
(0.016) |
(0.79) |
(0.0027) |
(0.49) |
(0.90) |
(0.14) |
(0.40) |
(0.78) |
(0.023) |
(1.0) |
|
|
Table A6 (cont.)
|
Large gadids |
Small gadids |
Flatfish |
Clupeids |
Scombrids |
Sandlance |
Meso-pelagics |
Misc. fish |
Benthic invertebrates |
Squid |
Shrimp |
Zoo-plankton |
Literature Sources |
Harbor porpoise |
(0.0010) |
(0.0035) |
(0) |
(0.0093) |
(0.00042) |
(0.0061) |
(0.00038) |
(0.00010) |
(0) |
(0.0030) |
(0.00029) |
|
8, 10, 40, 56, 59, 77, 78, 87, 90, 92, 93, 102 |
0.047 |
0.32 |
0.0012 |
0.27 |
0.054 |
0.092 |
0.021 |
0.15 |
0.0045 |
0.037 |
0.0094 |
|||
(0.33) |
(0.84) |
(0.012) |
(0.50) |
(0.29) |
(0.38) |
(0.20) |
(0.84) |
(0.050) |
(0.20) |
(0.080) |
|
||
Gray seal |
(0.0080) |
(0.00020) |
(0.0025) |
(0.000056) |
(0.000040) |
(0.00011) |
|
(0.000071) |
(0.000029) |
(0.000045) |
(0) |
|
36, 54, 51, 54, 55, 58, 61, 64, 66, 78, 80, 83, 94, 95, 103, 105 |
0.19 |
0.088 |
0.14 |
0.099 |
0.026 |
0.34 |
0.083 |
0.0043 |
0.028 |
0.00032 |
||||
(0.61) |
(0.61) |
(0.98) |
(0.66) |
(0.47) |
(0.85) |
|
(0.58) |
(0.15) |
(0.27) |
(0.012) |
|
||
Harbor seal |
(0.0057) |
(0.0020) |
(0.0019) |
(0.0015) |
(0.000091) |
(0.0040) |
|
(0.0043) |
(0.00011) |
(0.0021) |
(0.0013) |
|
17, 20, 23, 27, 34, 35, 39, 44, 46, 63, 64, 78, 80, 81, 105, 107 |
0.095 |
0.20 |
0.13 |
0.13 |
0.011 |
0.25 |
0.099 |
0.011 |
0.069 |
0.0068 |
||||
(0.32) |
(0.73) |
(0.73) |
(0.50) |
(0.10) |
(0.99) |
|
(0.45) |
(0.10) |
(0.63) |
(0.095) |
|
*(1:Hjort and Rudd 1929, 2:Schevill 1956, 3:Nemoto 1957, 4:Sergeant and Fisher 1957, 5:Nemoto 1959, 6:Klumov 1963, 7:Mitchell 1973, 8:Rae 1973, 9:Mitchell 1974, 10:Smith and Gaskin 1974, 11:Jonsgard and Darling 1977, 12:Nemoto and Kawamura 1977, 13:Brodie 1978, 14:Katona et al. 1978, 15:Leatherwood et al. 1978, 16:Lockyer and Brown 1978, 17:Boulva and McLaren 1979, 18:Watkins 1979, 19:Kawamura 1980, 20:Pitcher 1980, 21:Sergeant et al. 1980, 22:Frost and Lowry 1981, 23:Behrends 1982, 24:Hain et al. 1982, 25:Jonsgard 1982, 26:Kawamura 1982, 27:Bowen and Sergeant 1983, 28:Northridge 1984, 29:Cummings 1985, 30:Kasamatsu and Hata 1985, 31:Kenney et al. 1985, 32:Bushuev 1986, 33:Mitchell et al. 1986, 34:Selzer et al. 1986, 35:Harkonen 1987, 36:Prime and Hammond 1987, 37:Wishner et al. 1988, 38:Murison and Gaskin 1989, 39:Payne 1989, 40:Recchia and Read 1989, 41:Christensen et al. 1990, 42:Mayo and Marx 1990, 43:Mead and Potter 1990, 44:Olesiuk et al. 1990, 45:Waring et al. 1990, 46:Harkonen 1991, 47:Ichii 1991, 48:Lydersen et al. 1991, 49:Overholtz and Waring 1991, 50:Kasamatsu 1992, 51:Murie and Lavigne 1992, 52:Nordoy and Blix 1992, 53:Sigurjónsson and Víkingsson 1992, 54:Bowen et al. 1993, 55:Bowen and Harrison 1994, 56:Fontaine et al. 1994, 57:Gonzalez et al. 1994, 58:Hammond 1994, 59:Santos et al. 1994, 60:Young and Cockcroft 1994, 61:Hammill et al. 1995, 62:Haug 1995, 63:Olsen and Bjorge 1995, 64:Bowen and Harrison 1996, 65:Haug et al. 1996, 66:Mohn and Bowen 1996, 67:Couperus 1997, 68:Gannon et al. 1997, 69:Gannon 1997, 70:Haug et al. 1997, 71:Kenney et al. 1997, 72:Laerm 1997, 73:Palka et al. 1997, 74:Skaug et al. 1997, 75:Weinrich et al. 1997, 76:Barros 1998, 77:Gannon et al. 1998, 78:Pauly 1998, 79:Bowen and Siniff 1999, 80:Ferland 1999, 81:Williams 1999, 82:Barros et al. 2000, 83:Hammill and Stenson 2000, 84:Blanco 2001, 85:Santos 2001, 86:Flinn 2002, 87:Borjesson 2003, 88:Harcourt et al. 2003, 89:Gannon 2004, 90:Santos 2004, 91:Amir et al. 2005, 92:De Pierrepont 2005, 93:Spitz et al. 2006, 94:Bowen 2007, 95:Hammill 2007, 96:Overholtz 2007, 97:Pusineri 2007, 98:Santos 2007, 99:Meynier 2008a, 100:Meynier 2008b, 101:Mintzer 2008, 102:Waring et al. 2008, 103:Ampela 2009, 104:Beatson 2009, 105:Craddock and Polloni 2009, 106:Fernandez 2009, 107:Kopec et al. 2009, 108:Jansen 2010, 109:McCabe 2010, 110:Spitz et al. 2011)
Fig. A1. Regression sensitivity results of input parameters vs. consumption by: (A) fin whale, (B) humpback whale, (C) right whale, (D) sei whale, (E) minke whale, (F) pilot whale, (G) bottlenose dolphin, (H) Atlantic white-sided dolphin, (I) common dolphin, (J) harbor porpoise, (K) gray seal, and (L) harbor seal.