| Seabirds | Habitat, bird trophic levels (I-IV, Sc), and food categories | |||||||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Oceanic and offshore neritic | Inshore neritic | |||||||||||||||||||
| II | III | IV | Sc | I | II | III | IV | Sc | ||||||||||||
| C r u s t a c e a n | P o l y c h a e t e | C o e l e n t e r a t e | F i s h - s q u i d e g g s & l a r v a e | F i s h | C e p h a l o p o d | B i r d s | C a r r i o n / o f f a l / d e t r i t u s | P l a n t | C r u s t a c e a n , m i d w a t e r | C r u s t a c e a n , b e n t h i c | C o e l e n t e r a t e | E c h i n o d e r m | M o l l u s c | F i s h / s q u i d e g g s & l a r v a e | F i s h , m i d w a t e r | F i s h , b e n t h i c | C e p h a l o p o d | B i r d s | C a r r i o n / o f f a l / d e t r i t u s | |
| Gavia immer | * | x | x | |||||||||||||||||
| G. adamsii | * | o | x | |||||||||||||||||
| G. arctica | o | x | ||||||||||||||||||
| G. stellata | o | x | ||||||||||||||||||
| Podiceps grisegena | o | x | o | |||||||||||||||||
| P. nigricollis | x | o | ||||||||||||||||||
| P. auritus | x | x | o | |||||||||||||||||
| Aechmophorus occidentalis | o | x | x | |||||||||||||||||
| Diomedea nigripes | x | o | o | o | x | x | x | |||||||||||||
| Fulmarus glacialis | x | o | x | o | x | x | x | |||||||||||||
| Puffinus creatopus | o | x | x | |||||||||||||||||
| P. carneipes | o | x | x | |||||||||||||||||
| P. bulleri | x | x | x | |||||||||||||||||
| P. griseus | x | x | x | o | o | o | ||||||||||||||
| P. tenuirostris | x | o | x | o | o | o | ||||||||||||||
| Oceanodroma furcata | x | o | o | o | x | x | x | |||||||||||||
| Pelecanus occidentalis | x | |||||||||||||||||||
| Phalacrocorax auritus | o | x | o | |||||||||||||||||
| P. penicillatus | o | x | ||||||||||||||||||
| P. pelagicus | x | x | ||||||||||||||||||
| Branta bernicla | x | |||||||||||||||||||
| Clangula hyemalis | o | x | o | o | ||||||||||||||||
| Histrionicus histrionicus | o | x | o | |||||||||||||||||
| Melanitta deglandi | x | o | o | |||||||||||||||||
| M. perspicillata | o | x | o | |||||||||||||||||
| M. nigra | * | o | o | x | ||||||||||||||||
| Mergus serrator | * | x | x | |||||||||||||||||
| Haliaeetus leucocephalus | x | x | x | |||||||||||||||||
| Falco peregrinus | x | |||||||||||||||||||
| Phalaropus fulicarius | x | x | o | x | x | o | ||||||||||||||
| Lobipes lobatus | x | x | o | x | x | o | ||||||||||||||
| Stercorarius spp. | o | x | x | ? | x | x | x | o | x | |||||||||||
| Larus hyperboreus | o | o | o | o | ? | o | o | o | o | o | o | x | x | x | ||||||
| L. glaucescens | o | o | o | o | ? | o | o | o | o | o | x | x | x | x | ||||||
| L. occidentalis | x | x | x | x | o | x | o | o | o | * | * | x | x | o | x | |||||
| L. argentatus | o | o | o | o | o | x | o | o | o | o | o | x | o | x | ||||||
| L. heermanni | x | x | x | |||||||||||||||||
| L. canus | x | o | o | o | x | x | x | |||||||||||||
| L. philadelphia | x | x | o | |||||||||||||||||
| Rissa tridactyla | x | x | x | o | ||||||||||||||||
| Xema sabini | x | x | o | o | ||||||||||||||||
| Sterna paradisaea | x | x | o | o | ||||||||||||||||
| S. hirundo | o | x | ||||||||||||||||||
| Uria aalge | x | o | x | x | o | x | o | |||||||||||||
| U. lomvia | x | o | x | x | o | x | o | x | ||||||||||||
| Lunda cirrhata | ? | x | x | |||||||||||||||||
| Fratercula corniculata | * | x | x | |||||||||||||||||
| Cerorhinca monocerata | x | x | ||||||||||||||||||
| Cepphus columba | o | x | o | |||||||||||||||||
| Brachyramphus marmoratus | x | o | x | |||||||||||||||||
| B. brevirostris | x | o | ||||||||||||||||||
| Synthliboramphus antiquus | x | x | o | |||||||||||||||||
| Ptychoramphus aleuticus | x | x | ||||||||||||||||||
| Oceanographic region (domain) | Number of categories in the diets[36] | ||||||
|---|---|---|---|---|---|---|---|
| 1 | 2 | 3 | 4 | 5-7 | 7 | 8+ | |
| Bering Sea coastal | 3 | 11 | 9 | 6 | 5 | 4 | 5 |
| Bering Sea | 2 | 6 | 5 | 7 | 0 | 5 | 0 |
| Alaskan Stream | 3 | 14 | 14 | 5 | 4 | 4 | 5 |
| Central Subarctic | 1 | 6 | 8 | 4 | 0 | 7 | 0 |
| North American Coastal | 3 | 14 | 17 | 6 | 3 | 4 | 6 |
| Total | 12 | 51 | 53 | 28 | 12 | 24 | 16 |
| Percent total species (196) | 6 | 26 | 27 | 14 | 6 | 12 | 8 |
It is readily apparent from the foregoing comparisons that much overlap exists in the prey eaten by seabirds within each community. The question whether real competition ever exists is academic. Competition perhaps exists only rarely because seabirds partition resources through use of different feeding methods, selection of different-sized prey, and habitat zonation. Table 18 lists feeding methods (after Ashmole 1971 and Ainley 1977) and the body size and bill length of each species considered in this review. Bill length is usually related directly to body size (Ashmole 1968; Bédard 1969b), but note, for instance, that the longer species of the two kittiwakes has the shorter bill. Body weight would be a better measure of relative size than body size, but few reliable weight data are available for seabirds.
The use of different feeding methods by species in each community grossly assigns birds to feeding at different depths. Thus, whereas shearwaters, puffins, and small gulls (Xema sp., Rissa spp.) overlap almost entirely in prey categories and even prey species, the gulls can capture these organisms only at the surface; the shearwaters capture them at shallow depths; and the puffins capture them at much deeper depths. Direct field observations of this phenomenon are few but Gould (1971) and Sealy (1973a) compared the diets of birds feeding in mixed-species flocks. An example of how even finer divergence in feeding methods helps to partition food resources has been provided by Spring (1971) in his comparison of the two murres. Both species feed by diving to great depths, but the thick-billed murre is able to hover over the bottom and thereby is better able to capture benthic organisms.
| Domain | Oceanic/offshore neritic | Inshore neritic | |||||||
|---|---|---|---|---|---|---|---|---|---|
| II | III | IV | Sc | I | II | III | IV | Sc | |
| Bering Sea Coastal | 11 | 17 | 1? | 10 | 6 | 23 | 18 | 6 | 6 |
| Bering Sea | 22 | 21 | 3? | 11 | — | — | — | — | — |
| Alaska Stream | 21 | 19 | 1? | 12 | 5 | 28 | 21 | 6 | 6 |
| Central Subarctic | 23 | 22 | 3? | 12 | — | — | — | — | — |
| North American Coastal | 25 | 24 | 3? | 11 | 3 | 28 | 35 | 7 | 10 |
| Total | 102 | 103 | 11? | 56 | 14 | 79 | 74 | 19 | 22 |
| Proportion | 0.38 | 0.39 | 0.02[37] | 0.21 | 0.07 | 0.38 | 0.28 | 0.09 | 0.10 |
| Species | Body length[38] (cm) | Bill length[39] (mm) | Feeding[40] method |
|---|---|---|---|
| Gavia adamsii | 63.5 | 90-91 | D |
| G. immer | 61.0 | 80-82 | D |
| G. arctica | 45.7 | 51-52 | D |
| G. stellata | 43.5 | 51-52 | D |
| Podiceps grisegena | 33.0 | 48-50 | D |
| P. nigricollis | 22.9 | 24-26 | D |
| P. auritus | 24.1 | 23-24 | D |
| Aechmophorus occidentalis | 45.7 | 65-76 | D |
| Diomedea nigripes | 71.1 | 141-144 | SS |
| D. immutabilis | 71.1 | 102-112 | SS |
| Fulmarus glacialis | 45.7 | 36-37 | SS |
| Puffinus carneipes | 45.7 | 41-46 | PP |
| P. creatopus | 45.7 | 41-46 | PP |
| P. bulleri | 38.1 | 38-45 | PP |
| P. griseus | 40.3 | 41-42 | PP |
| P. tenuirostris | 38.1 | 31-32 | PP |
| Oceanodroma furcata | 19.0 | 15 | Di,SS |
| O. leucorhoa | 19.0 | 16 | Di,SS |
| Pterodroma inexpectata | 29.2 | 26-27 | SS |
| Phalacrocorax auritus | 68.6 | 55-57 | D |
| P. penicillatus | 73.7 | 66-71 | D |
| P. urile | 71.1 | 54-55 | D |
| P. pelagicus | 55.9 | 47-50 | D |
| Pelecanus occidentalis | 104.0 | 294-319 | P |
| Branta spp. (bernicla) | 43.5 | 33-36 | T |
| Philacte canagica | 45.7 | 37-42 | T |
| Anas spp. | 40.0 | 32-35 | T |
| Clangula hyemalis | 38.1 | 25-27 | D |
| Histrionicus histrionicus | 30.5 | 25-28 | D |
| Polysticta stelleri | 30.5 | 37-43 | D |
| Somateria mollisima | 43.5 | 45-55 | D |
| S. spectabilis | 40.3 | 31-33 | D |
| S. fischeri | 38.1 | 22-26 | D |
| Melanitta deglandi | 35.6 | 41-44 | D |
| M. perspicillata | 40.3 | ca. 40 | D |
| M. nigra | 35.6 | 42-47 | D |
| Mergus serrator | 40.3 | 45-54 | D |
| Haliaeetus leucocephalus | 80.0 | 52-54 | X |
| Falco peregrinus | 37.5 | 21-25 | X |
| Phalaropus fulicarius | 16.5 | 22 | SS |
| Lobipes lobatus | 15.2 | 22 | SS |
| Stercorarius pomarinus | 43.5 | 40 | SS,A |
| S. parasiticus | 40.3 | 32 | SS,A |
| S. longicaudus | 38.1 | 29 | SS,A |
| Larus hyperboreus | 61.0 | 55-60 | SS |
| L. glaucescens | 55.9 | 54-58 | SS |
| L. occidentalis | 53.0 | 54-57 | SS,Di |
| L. argentatus | 50.8 | 48-54 | SS,Di |
| L. californicus | 43.5 | 45-50 | SS,Di |
| L. heermanni | 38.1 | 42-46 | SS,Di |
| L. canus | 35.6 | 34-36 | SS,Di |
| L. philadelphia | 27.9 | 30-31 | Di |
| Rissa tridactyla | 34.2 | 39-40 | Di |
| R. brevirostris | 38.1 | 29-30 | Di |
| Xema sabini | 27.9 | 26-27 | Di |
| Sterna paradisaea | 38.1 | 31-33 | Di,SP |
| S. hirundo/forsteri | 35.6 | 36-39 | Di,SP |
| S. aleutica | 33.0 | 33 | Di,SP |
| Uria aalge | 35.6 | 43-47 | D |
| U. lomvia | 35.6 | 39-42 | D |
| Lunda cirrhata | 31.8 | 57-60 | D |
| Fratercula corniculata | 29.2 | 49-51 | D |
| Cerorhinca monocerata | 29.2 | 34-35 | D |
| Cepphus columba | 26.7 | 32-33 | D |
| Brachyramphus marmoratus | 20.3 | 15 | D |
| B. brevirostris | 19.0 | 10 | D |
| Synthliboramphus antiquus | 20.3 | 13 | D |
| Ptychoramphus aleuticus | 17.8 | 19 | D |
| Aethia pygmaea | 16.5 | 8-9 | D |
| A. pusilla | 13.3 | 8 | D |
| A. cristatella | 17.8 | 11 | D |
| Cyclorrhynchus psittaculus | 18.4 | 15 | D |
The scavengers (generalists) offer a good example of how a range of bird and bill sizes is usually represented among species having similar diets and feeding methods. The progression of oceanic scavenger sizes is graded rather evenly from the black-footed albatross down to the northern fulmar, to the scaled petrel, to the storm-petrel. All these species capture prey that occur only at or near the water surface. Recently Sanger (1973) reported appreciable numbers of glaucous-winged gulls (Larus glaucescens) and herring gulls (L. argentatus), noted neritic scavengers, out in the oceanic realm of the petrel. He presented limited data that suggested an overlap between the diet of these gulls and that of black-footed albatrosses, as noted by Miller (1940). It would not be surprising if these gulls were as much generalists in the oceanic habitat as they are in the neritic. Interestingly, their bill and body sizes fall between those of the albatross and the fulmar, thus in theory enabling them to invade the oceanic habitat without great competition. It is likely that their invasion occurred during historical times and is related to their habit of following fishing boats from shore out to sea (Sanger 1973). If so, the gulls might be assuming from other species part of a previously uncontested resource.
Another interesting group of species that shows close similarities in diet consists of the piscivorous loons, grebes, and mergansers. All these birds, including seven or eight species, apparently feed on fish occurring on or near the bottom in the inshore neritic habitat. Again, however, an even progression in size exists: yellow-billed loon (Gavia adamsii), common loon (G. immer), arctic loon (G. arctica), red-throated loon (G. stellata), western grebe (Aechmophorus occidentalis), red-necked grebe (Podiceps grisegena), and common merganser (Mergus merganser). Most likely then, they select different-sized fish. Another example of this phenomenon is provided by the eight neritic gulls, which are largely scavengers and show a remarkably even progression in bill and body size. Finally, as shown clearly by Bédard (1969a, 1969b) and Harris (1970), alcids of different sizes select different-sized prey, often of the same species.
A final important way in which seabirds partition available resources is by inhabiting different zones. Zonation is especially evident during the breeding season when species common to the same breeding site sort themselves out according to the distances they range for food. This phenomenon was discussed by Murphy (1936), Shuntov (1974), Sealy (1972), Cody (1973), and Scott (1973).