Dietary Composition
Snowy Egret (Egretta thula)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Pterophyllum scalare, Ziphophorus maculatus, Hyphessobrycon herbertaxelrod, Megalamphodus megalopterus, Poecilia reticulata, Helostoma temmincki, Puntius tetrazona, Epalzerohycnhos erythrurus, Hypostomus spp. | Fish species consumed from aquaculture ponds | B | Not Reported | See citation | Four commercial aquacutlure operations, Central Florida | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Crayfish: 15, small-bodies fishes: 90, larged-bodied fishes: 35, shrimp: 40, aquatic insects: 10, terrestrial insects: 10, garbage: 5, other vertebrates: 0 | Prey category | Frequency of use, % | Nestling | 20 | Arthur R. Marshall Loxahatchee National Wildlife Refuge, Palm Beach County |
Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Mummichog: 47, shore shrimp: 47, Atlantic silverside: 6 | % total | NR | Adult | Not reported | New Jersey & New York | Exposure Factor Datasets | Breeding | USA |
Pacific Green Turtle (Chelonia mydas)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation Table 1 | Dry weight diet component | 1 | Samandað beach | Exposure Factor Datasets | TURKEY |
Dietary Composition | See citation Table 1 | Wet weight diet component | 1 | Samandað beach | Exposure Factor Datasets | TURKEY |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation Table 1 | % volume | B | Both Adults and Juveniles | 10 | Pelagic | Exposure Factor Datasets | USA |
Dietary Composition | See citation Table 1 | Frequency of occurrence, % | B | Both Adults and Juveniles | 10 | Pelagic | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Chlorophyta (Ulva sp., Enteromorpha sp., Rhizoclonium sp.), Rhodophyta (Lobophora sp., Gracilaria domingensis, Pyropia sp.), Phaeophyceae Sargassum sp., Macrophyta (Halodule wrightii, Avicennias chauerina, unidentified angiosperms), cephalopod beaks, marine debris | List of nutritional items in total digestive tract | B | Both Adults and Juveniles | 120 | Paraná, southern Brazil | Exposure Factor Datasets | BRAZIL |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation Table 1 | Items identifed from gavage | Frequency | B | 94 | Tident Basin, Port Canaveral Inlet | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation Figure 2 | Foregut contents of stranded individuals | Frequency | B | 169 | Middle coast: Colorado River-Mustand Island; Lower coast: North Padre Island-Mexico border | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Gelidiela acerosa: 68.2%, Hypnea muscifornis: 59.1%, Gelidium coarctatum: 50% | Most frequent algae species | % frequency | B | Both Adults and Juveniles | 22 | Tartaruga submerged reef | Exposure Factor Datasets | BRAZIL |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Caulerpa filiformis: 77.8%, Loligo gahi (eggs): 51.9%, Rhodymenia corallina: 44.4% | Most frequent items | % | B | Both Adults and Juveniles | 27 | Sechura Bay | Exposure Factor Datasets | Dead | PERU |
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Location | Type |
---|---|---|---|---|---|
Dietary Composition | Neustonic material | B | Juvenile | Exposure Factor Datasets | |
Dietary Composition | Macroalgae, seagrass and/or mangrove | B | Adult | Exposure Factor Datasets |
California Black Rail (Laterallus jamaicensis)
Exposure Endpoint Type | Endpoint Value | Location | Type |
---|---|---|---|
Dietary Composition | Review | Exposure Factor Datasets |
Coyote (Canis latrans)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Insect: 25.6, reptile: 1.5, bird: 3.0, small rodent: 27.0, large rodent: 27.9, leporidae: 12.2, cattle: 24.1, pronghorn: 1.4, unknown mammal: 0.2, crops: 12.3, other seeds: 5.0, other vegetation: 22.9 | Frequency of occurrence, seasonal mean | % | NR | Both Adults and Juveniles | 280 | Dallam County: continuous short-grass prairie | Exposure Factor Datasets | USA |
Dietary Composition | Insect: 17.0, reptile: 0, bird: 6.7, small rodent: 37.3, large rodent: 30.3, leporidae: 18.2, cattle: 9.7, pronghorn: 1.7, crops: 16.6, other seeds: 2.2, other vegetation: 15.8 | Frequency of occurrence, seasonal mean | % | NR | Both Adults and Juveniles | 186 | Stratford: fragmented short-grass prairie | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Rodents: 64, lagomorphs: 61, deer: 35, carnivores: 56, pets: 41, soricomorphs: 10, unknown: 14, native seeds: 27, non-native seeds: 35, unknown seeds: 19, trash: 27 | Frequency by group | NR | Both Adults and Juveniles | 64 | Denver metro area | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Mammals: 72.7, birds: 7.3, reptiles: 16.4, insects: 12.7, crustaceans: 1, vegetable matter: 60 | Frequency of occurrence | B | Both Adults and Juveniles | 59 | Chamela-Cuixmala Biosphere Reserve | Exposure Factor Datasets | MEXICO |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation for values: Lepus californicus, Peromyscus maniculatus, Reinthrodontomys megalotis, Lemmiscus curtatus, Menniscus curtatus, Perognathus parvus, Dipodomys spp., other rodents | Prey identified by teeth in coyote scat | NR | Not Reported | 39-58 | Curlew Valley | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|
Dietary Composition | See citation Figure 3 for values: Deer, rodent, lagmorph, avian, herptofauna, unknown mammal, plant | 128 | MeadWestvaco Wildlife and Ecosystem Research Forest |
Exposure Factor Datasets | USA |
Kit Fox (Vulpes macrotis)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Leporids: 44.1, kangaroo rats: 31.0, pocket mice: 1.2, antelope squirrels: 2.3, other rodents: 4.1, sheep: 0.8, birds: 2.5, snakes: 1.4, lizards: 0.1, orthopterans: 6.4, colopterans: 1.3, other arthropods: 0.1, other items: 6.9 | Frequency of occurrence | % | Both Adults and Juveniles | 4393 | Naval Petroleum Reserve | Exposure Factor Datasets | Kern | USA |
Pallid Bat (Antrozous pallidus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Acrididae: 16.1, Ceuthophilus californianus: 4.7, Gryllidae: 8.3, Stenopelmatus fuscus: 27.3, Microcentrum rhombifolium: 0.6, Diptera: 0.2, Lepidoptera: 5.8, Carabidae: 8.4, Prionus californicus: 1.0, Chilopoda: 11.8, Solpugidae: 7.8, Lycosidae: 7.8 | Percentage of total volume | % | M | Adult | 116 | Exposure Factor Datasets | Marin | USA | |
Dietary Composition | Tytthotyle maculata: 9.9, Grylliacrididae: 1.0, Gryllus: 4.0, Diptera: 0.3, Lepidoptera: 5.7, Coleoptera: 2.3, Cyclocephla longula: 24.4, Tenebrionidae: 3.6, Edrotes ventricosus: 0.6, Hippomelas: 21.0, Tiphiidae: 1.5, Pentatomidae: 4.3, Geocoris: 0.1, Myrmeleontidae: 4.9, Solpugidae: 14.1 | Percentage of total volume | % | M | Adult | 29 | Exposure Factor Datasets | Kern | USA |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Insecta: 81.3, arachnida: 17.2, reptilia: 0.9 | % | B | Both Adults and Juveniles | Not reported | University of Texas at El Paso Indio Mountains Research Station | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Arachnida: 0.8, insecta: 97.8, other: 1.6 | Perent frequency | B | Both Adults and Juveniles | 93 | Nk'Mip Indian Band Reserve | Exposure Factor Datasets | CANADA |
Willow Flycatcher (Empidonax traillii)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Diptera: 74.6, Hemiptera: 64.4, Coleoptera: 52.5, Oldonata: 40.7, Hymenoptera/flying: 35.6, Cicadellidae: 35.6, Araneae: 30.5, plant: 13.6, Leipidoptera larva: 11.9, unidentified insect: 10.2, Homoptera/other: 8.5, Lepidoptera adult: 6.8, Isoptera: 6.8, Formicidae: 3.4 | Diet based on fecal samples | Percent occurrence in samples | NR | Not Reported | 59 | Kern River Preserve | Exposure Factor Datasets | Kern | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation Figures 1 & 3 | Diet based on fecal samples | Frequency detected | Adult | 100 | Roosevelt Lake | Exposure Factor Datasets | USA |
Dietary Composition | See citation Figure 1 & 4 | Diet based on fecal samples | Frequency detected | Nestling | 98 | Roosevelt Lake | Exposure Factor Datasets | USA |
California Sea Lion (Zalophus californianus)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Cephalopods: 25%, fishes: 65%, crustacean: 7% | % occurrence | NR | Not Reported | 289 scat samples | San Benito Islands | Exposure Factor Datasets | MEXICO |
Snowy Plover (Charadrius nivosus)
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Dietary Composition | Small crabs, sand hoppers, marine worms | M | Adult | 1 | Exposure Factor Datasets | INDIA |
Peregrine Falcon (Falco peregrinus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Turdus migratorius: 11, Leucophaeus pipixcan: 8, Sialia currucoides: 6, Phalaropus fulicarius: 6, Colaptes auratus: 5, Phalaropus tricolor: 5, other Scolophacidae spp.: 7, Icteridae spp.: 7, other picidae spp.: 6, Fringillidae spp.: 5, other birds: 32, other animals: 3 | Percent frequency of prey remains | % | B | Nestling | 9 eyries | Yellowstone National Park | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Units | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | Synthliboramphus antiquus, Streptopelia orientalis, S. qumizusume, Zoothera dauma, Swimhow's Storm-Petrel, Larus crassirostris, Japanese Murrelet, Pitta nympha, Otus sunia, Otus semitroques, Asio otus, Caprimulgus indicus | NA | 393 pellets | Exposure Factor Datasets | SOUTH KOREA (REPUBLIC OF KOREA)+M10 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation Table 2 | Prey types | % prey mass | B | Adult | Exposure Factor Datasets | SPAIN |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Dietary Composition | See citation Figure 4 | Identifiable prey | Adult | Urban: 10, nonurban: 11 nests | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation Figure 2 | Identifiable prey | Coastal: 30, urban: 31 | Coastal vs. urban populations | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation Figure 2 | Seasonal changes in diet | 486 prey remains | Warsaw buildings | Exposure Factor Datasets | POLAND |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Turdus pilaris: 8.34, Turdus merula: 4.82, Columba livia: 12.27, Garrulus gladnarius: 6.87, Stumus vulgaris: 2.75, Corvus corone cornix: 19.50, other Columbidae: 12.48, Other Turdidae: 4.39, Other birds: 28.58 | Percent by mass from pellets/prey remains | % | B | Adult | 249 | Central-eastern Italian Alps | Exposure Factor Datasets | Breeding | ITALY |
Loggerhead Shrike (Lanius ludovicianus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | Chaetodipus arenarius (11.0), Chaetopidus baileyi (20.5), Peromyscus eva (15.0) | Species captured (mean weight, g) | Not reported | Baja California Sur | Exposure Factor Datasets | MEXICO |
Double-crested Cormorant (Phalacrocorax auritus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Striped mullet: 25.5, gulf menhaden: 17.6, hardhead catfish: 11.8, Sciaendiae: 15.7, unidentifiable fish: 5.9 | Frequency | % | Not Reported | 51 | Lavaca bay | Exposure Factor Datasets | USA |
Dietary Composition | Striped mullet: 28.5, hardhead catfish: 2.5, gulf toadfish: 46.4 Sciaendiae: 0, unidentifiable fish: 3.6 | Frequency | % | Not Reported | 28 | Laguna Madre | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Pre-goby: 10.15, Transition 10.25, Post-goby: 14.81 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Not Reported | Pre-goby: 17,681, Transition 1800, Post-goby: 4662 | Lilttle Galloo Island, Lake Ontario | Exposure Factor Datasets | CANADA |
Dietary Composition | See citation Table 4 | Percent species by number by different periods | % | NR | Not Reported | Pre-goby: 17,681, Transition 1800, Post-goby: 4662 | Lilttle Galloo Island, Lake Ontario | Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | 2006: >93% alewife, 2007: 86.5%; balance made up of round goby, rainbow smelt, pumpkinseed | Chick diet | % by mass | B | Adult | Tommy Thompson Park, Lake Ontario | Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Herring, shad: 0.6, Peamouth/Pikeminnow: 24.0, Sucker: 5.8, Smelt: 0.3, Salmonid: 45.5, Stickleback: 5.0, Sculpin: 8.0, Surfperch: 0.3, Flounder: 8.5, Other: 1.8 | Percent by mass from adult foregut and chick regurgitation samples | % | NR | Both Adults and Juveniles | 206 | Rice Island/Channel Markers | Exposure Factor Datasets | USA |
Dietary Composition | Herring, shad: 27.8, Peamouth/Pikeminnow: 0.7, Sucker: 4.7, Smelt: 7.6, Salmonid: 15.9, Stickleback: 2.1, Sculpin: 9.2, Surfperch: 7.3, Flounder: Pacific sand lance: 1.8, Flounder: 9.8 Other: 1.3 | Percent by mass from adult foregut and chick regurgitation samples | % | NR | Both Adults and Juveniles | 128 | East Sand Island | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | Cyprinid, Lepomis spp., rainbow smelt, rock bass, white perch, yellow perch | Percent by number before alewife eastablishment | % | Exposure Factor Datasets | USA | |
Dietary Composition | Alewife ,cyprinid, Lepomis spp., rainbow smelt, rock bass, white perch, yellow perch | Percent by number after alewife eastablishment | % | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation | Percent by number | % | Lake Oneida | Exposure Factor Datasets | USA |
Dietary Composition | See citation | Percent by number | % | Lake Oneida | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Age-Specific | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation | Percent composition and biomass | B | Adult | Exposure Factor Datasets | Leech Lake | USA | |
Dietary Composition | See citation | Percent composition and biomass | B | Chick | Exposure Factor Datasets | Leech Lake | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Pre-goby: 14.4, Transition 14.3, Post-goby: 20.1 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Adult | Pre-goby: 3100, Transition 2206, Post-goby: 1028 | Griswold Island | Exposure Factor Datasets | CANADA |
Dietary Composition | Pre-goby: 11.9, Transition 12.7, Post-goby: 16.7 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Adult | Pre-goby: 923, Transition 1631, Post-goby: 2035 | McNair Island | Exposure Factor Datasets | CANADA |
Dietary Composition | Pre-goby: 13.2, Transition 12.8, Post-goby: 17.0 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Adult | Pre-goby: 1187, Transition 518, Post-goby: 1404 | Strachan Island | Exposure Factor Datasets | CANADA |
Dietary Composition | See citation Table 4 | Percent species by number by different periods | % | NR | Not Reported | See citation | Three sites along St. Lawrence River | Exposure Factor Datasets | CANADA |
Great Horned Owl (Bubo virginianus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Townsend vole: 84.8, common muskrat: 1.0, rat species: 1.0, medium songbirds: 5.1, family anatidae: 5.1, order coleoptera: 3.0 | Percent by number in pellets/prey remains | % | NR | See citation | Alaskan National Wildlife Area | Exposure Factor Datasets | CANADA |
Dietary Composition | Townsend vole: 69.0, North American deer mouse: 11.2, rat species: 7.8, house mouse: 0.9, shrew-mole: 1.7, shrew species: 7.8, small songbirds: 0.9, American crow: 0.9 | Percent by number in pellets/prey remains | % | NR | See citation | Forest Richmond | Exposure Factor Datasets | CANADA |
Dietary Composition | Townsend vole: 97.5, rat species: 2.5 | Percent by number in pellets/prey remains | % | NR | See citation | Arthur Drive | Exposure Factor Datasets | CANADA |
Dietary Composition | Townsend vole: 70.3, North American deer mouse: 1.4, rat species: 1.4, shrew species: 9.5, American crow: 2.7, great blue heron: 1.4, barn owl: 10.8, order coleoptera: 2.7 | Percent by number in pellets/prey remains | % | NR | See citation | Terra Nova Park | Exposure Factor Datasets | CANADA |
Dietary Composition | Townsend vole: 37.3, rat species: 25.5, eastern cottontail: 23.5, coast mole: 5.9, medium songbirds: 2.0, small songbirds: 2.0, American crow: 2.0, family anatidae: 2.0 | Percent by number in pellets/prey remains | % | NR | See citation | Beach Groove Park | Exposure Factor Datasets | CANADA |
Dietary Composition | Townsend vole: 2.1, North American deer mouse: 21.3, rat species: 42.6, order lagomorpha: 2.1, eastern cottontail: 4.3, medium songbirds: 10.6, small songbirds: 6.4, American crow: 4.3, order coleoptera: 6.4 | Percent by number in pellets/prey remains | % | NR | See citation | Crescent Park | Exposure Factor Datasets | CANADA |
Dietary Composition | Townsend vole: 57.3, pacific jumping mouse: 1.3, rat species: 33.4, eastern cottontail: 2.7, medium songbirds: 1.3, American crow: 1.3, family anatidae: 1.3, order coleoptera: 1.3 | Percent by number in pellets/prey remains | % | NR | Central Surrey | Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Mammalia: 89.76, aves: 7.07 | Percent biomass in disturbed site | % | B | Not Reported | 1478 | US Army Dugway Proving Ground | Exposure Factor Datasets | USA |
Dietary Composition | Mammalia: 95.74, aves: 0.85 | Percent biomass in undisturbed site | % | B | Not Reported | 2448 | US Army Dugway Proving Ground | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Class aves: 13.8, class mammalia: 86.2, class crustacae: 0.0 | Percent biomass | % | NR | Not Reported | 285 | Fort Cluster | Exposure Factor Datasets | USA |
Dietary Composition | Class aves: 24.8, class mammalia: 75.2, class crustacae: 0.0 | Percent biomass | % | NR | Not Reported | 285 | Trowbridge | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Mammals: 34, birds: 38, amphibians: 8, reptiles: 2, fishes: <1, insects: 18 | Percent frequency | % | NR | Not Reported | 85 | Lami Biological Reserve | Exposure Factor Datasets | BRAZIL |
Burrowing Owl (Athene cunicularia)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation Figure 1 | Percent biomass/burrow | Exposure Factor Datasets | Santa Clara | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Baiomys taylori: 16, Reithrodontomys fulvescens: 11, Peromyscus: 7, Cryptotis parva: 6, Mus musculus: 6, Perognathus merriami: 3, Sigmodon hispidus: 1 |
Percent frequency of occurrence of mammalian species in pellets | % | NR | Not Reported | 182 | Southern Texas | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Aranedia: 31.5, Coloptera: 51.9, Dermaptera: 64.8, Isopoda: 3.7, Lepidoptera: 14.8, Orthoptera: 98.2, Rodentia: 3.7, Solipugida: 40.7 | Percent frequency of occurrence in stomach contents | % | NR | Not Reported | 53 | Calipatria State Prison | Exposure Factor Datasets | Imperial | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Invertebrates: 97, Vertebrates: 66 | Percent frequency of occurrence | % | NR | Not Reported | 426 | Nevada Test Site | Exposure Factor Datasets | USA |
Dietary Composition | Invertebrates: 95, Vertebrates: 67 | Percent frequency of occurrence | % | NR | Not Reported | 1631 | Nevada Test Site | Exposure Factor Datasets | USA |
Dietary Composition | Invertebrates: 100, Vertebrates: 34 | Percent frequency of occurrence | % | NR | Not Reported | 213 | Nevada Test Site | Exposure Factor Datasets | USA |
Dietary Composition | Invertebrates: 83, Vertebrates: 67 | Percent frequency of occurrence | % | NR | Not Reported | 186 | Nevada Test Site | Exposure Factor Datasets | USA |
Dietary Composition | Invertebrates: 99, Vertebrates: 79 | Percent frequency of occurrence | % | NR | Not Reported | 806 | Nevada Test Site | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Vertebrates: 362, Arthropods: 233.2 | Percent of total prey biomass | % | NR | Not Reported | 2 | Tall Grass Prairie National Preserve | Exposure Factor Datasets | USA |
Dietary Composition | See citation Figure 2 | Percent of total prey biomass at different breeding stages | % | NR | Not Reported | 2 | Tall Grass Prairie National Preserve | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Arachnida: 7, Crustacea: <1, Insecta: see citation, Reptilia: <1, Aves: <1, Mammalia: see citation, Other vertebrates: <1 | Percent count of prey items | % | NR | Not Reported | 182 | Southern coastal Texas | Exposure Factor Datasets | USA |
Dietary Composition | Arachnida: 1, Crustacea: <1, Insecta: see citation, Reptilia: 2, Aves: 9, Mammalia: see citation, Other vertebrates: 8 | Percent biomass of prey items | % | NR | Not Reported | 182 | Southern coastal Texas | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation Table 1 | Vertebrate prey types by land-cover type | M | Adult | 18 | Between Alberta and Saskatchewan | Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Mice: 57.0, Insects: 31.6, Petrels 32.9, Auklet: 2.5, Unknown bird: 10.1 | Percent frequency of occurrence | % | NR | Not Reported | 79 | Southeast Farallon Island | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Insecta: see citation, Arachnida: 8.3, Gastropoda: 1.7, Reptilia: 0, Aves: 0.7, Mammalia: 0.2 | Percent frequency of occurrence | % | NR | Not Reported | 29 | Rutland Ranch, rural habitat | Exposure Factor Datasets | USA |
Dietary Composition | Insecta: see citation, Arachnida: 9.1, Gastropoda: 0.8, Reptilia: 1.0, Aves: 2.9, Mammalia: 0.3 | Percent frequency of occurrence | % | NR | Not Reported | 55 | Marco Island, urban habitat | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Dietary Composition | Mammals: 20.9, Birds: 0.6, Reptiles: 1.3, Chelicerates: 25.3, Lycosidae: 1.2, Bothriuridae: 24.1, Insects: 51.9 | Percent frequency of occurrence | % | 589 | Protected Natural Area Penı´nsula Valde´ s, Chubut, Argentina | Exposure Factor Datasets | ARGENTINA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation Figures 1 & 2 | Mean proportion of prey in pellets | % | NR | Not Reported | 178 | South-eastern coast of Buenos Aires Province |
Exposure Factor Datasets | ARGENTINA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Rodentia: 27.8, Procellariiformes: 5.3, Charadriiformes: 0.1, Passeriformes: 0.2, Unknown bird: 0.7, Arachnida: 0.4, Orthoptera: 28.1, Dermaptera: 0.2, Coleoptera: 32.3, Lepidoptera: 3.8, Lithobiomorpha: 0.6, Peracarida/amphipoda: 0.3, Isopoda: 0.2, Unknown arthropod: 0.1 | Percent of total in pellets | % | NR | Not Reported | 679 | Southeast Farallon Island | Exposure Factor Datasets | San Francisco | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation Table 1 | Proporation of frequency of each taxon from pellets (temporal) | 35-110 | Somuncurá Plateau Protected Area | Exposure Factor Datasets | ARGENTINA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Dietary Composition | Rodentia: 74.9, Reptilia: 0.5, Anura: 3.9, Coleoptera: 12.2, Dermaptera: 0, Hymenoptera: 0.01, Ortoptera: 0.05, Aranea: 8.2, Scorpionida: 0.3, Gastropoda: 0 | % total biomass consumed | B | Not Reported | Inter-Andean Valley | Exposure Factor Datasets | ECUADOR |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Dietary Composition | Mammals: 71.0, Birds: 1.4, Reptiles: 2.8, Invertebrates: 24.8 | % total biomass consumed | B | Not Reported | Pampa del Tamarugal, Atacama Desert | Exposure Factor Datasets | CHILE |
Dietary Composition | Mammals: 13.3, Birds: 0.3, Reptiles: 9.1, Invertebrates: 77.4 | % frequency | B | Not Reported | Pampa del Tamarugal, Atacama Desert | Exposure Factor Datasets | CHILE |
Dietary Composition | Mammals: 25.5, Birds: 7.7, Reptiles: 2.6, Invertebrates: 64.2 | % total biomass consumed | B | Not Reported | Pampa del Tamarugal, Atacama Desert | Exposure Factor Datasets | CHILE |
Dietary Composition | Mammals: 2.2, Birds: 0.7, Reptiles: 3.9, Invertebrates: 93.1 | % frequency | B | Not Reported | Pampa del Tamarugal, Atacama Desert | Exposure Factor Datasets | CHILE |
Brown Pelican (Pelecanus occidentalis)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation Figure 3 | Proportion of anchovy:sardine | NR | Midriff Islands | Exposure Factor Datasets | MEXICO |
Dietary Composition | 0.83 | Percentage of diet that is anchovy+sardine | NR | Midriff Islands | Exposure Factor Datasets | MEXICO |
American Kestrel (Falco sparverius)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Vertebrates (29.1 %) Arthropods (70.9 %) | Frequency determined by pellet analysis | Frequency, % | Fledgling | 19 fledglings | Parque Luro Reserve | Exposure Factor Datasets | ARGENTINA |
Dietary Composition | Vertebrates (11.2 %) Arthropods (88.8 %) | Frequency determined by prey remains | Frequency, % | Fledgling | 19 fledglings | Parque Luro Reserve | Exposure Factor Datasets | ARGENTINA |
Coachella Valley Fringe-toed Lizard (Uma inornata)
Exposure Endpoint Type | Endpoint Value | Life Cycle Stage | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation | Not Reported | Thousand Palms Preserve | Exposure Factor Datasets | Riverside | USA |
Desert Tortoise (Gopherus agassizi)
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation Table 6 | B | Adult | 18 | Desert Tortoise Research Natural Area, eastern Kern County, California |
Exposure Factor Datasets | Kern | USA |
Dietary Composition | See citation Table 8 | B | Adult | 18 | Desert Tortoise Research Natural Area, eastern Kern County, California |
Exposure Factor Datasets | Kern | USA |