Phalacrocorax auritus (Double-crested Cormorant)
Double-crested Cormorant (Phalacrocorax auritus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Population Density | See citation Table 1 | Adults/sq km | Adults/sq km | NR | Adult | North Channel, Lake Huron | Exposure Factor Datasets | CANADA |
Population Density | See citation Table 1 | Adults/sq km | Adults/sq km | NR | Adult | Georgian Bay, Lake Huron | Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|
Survival/ Mortality | See citation Figure 4 | Second-year birds | Adult | Great Lakes region | Exposure Factor Datasets | USA |
Survival/ Mortality | See citation Figure 5 | Hatch-year birds | Juvenile | Great Lakes region | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Survival/ Mortality | 0.696 | Survival, modeled average (Adult, at least 2 y) | Percent | Adult | Lake Michigan | Exposure Factor Datasets | USA |
Survival/ Mortality | 0.305 | Survival, modeled average (first year) | Percent | Juvenile | Lake Michigan | Exposure Factor Datasets | USA |
Survival/ Mortality | 0.774 | Survival, modeled average (Second/third year) | Percent | Juvenile | Lake Michigan | Exposure Factor Datasets | USA |
Survival/ Mortality | 0.633 | Survival, modeled average (Adult, at least 4 y) | Percent | Adult | Lake Michigan | Exposure Factor Datasets | USA |
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 | 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 | 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 |
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 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 2008: 1.79 ± 0.03, 2009: 1.96 ± 0.02 | Brood size | Number of hatchlings | NR | Hatchling | 2008: 493 nests, 2009: 559 nests | Northeast SD | Exposure Factor Datasets | USA |
Time of Hatching or Parturition | 2008: June 4, 2009: May 29 | Earliest hatch date | Hatchling | 2008: 493 nests, 2009: 559 nests | Northeast SD | Exposure Factor Datasets | USA | ||
Hatching Success | 2008: 49.5% [45.9-52.9 (95% CI)], 2009: 59.4% [55.8-63.1 (95% CI)] | Fledge success | Hatchling | 2008: 28, 2009: 25 | Northeast SD | 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 | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Home Range | 17490 sq km | sq km | B | Adult | 37 | Mississipi Alluvial Valley (AR, MS, LA) & Upper Coastal Plain (AL, MS) | Exposure Factor Datasets | Over-wintering populations | USA | 1986 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|
Population Density | See citation Figure 2 | Active nests/11,000 ha | Adult | Estero Bay Aquatic Preserve | Exposure Factor Datasets | Breeding | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|
Population Density | 1990: 3985, 1994: 9854, 1997: 8217, 2000: 12821, 2003: 11470 | Number of nests | Number of nests | Georgian Bay, Lake Huron | Exposure Factor Datasets | Breeding | CANADA |
Population Density | 1990: 4310, 1994: 7281, 1997: 8494, 2000: 12441, 2003: 11527 | Number of nests | Number of nests | North Channel, Lake Huron | Exposure Factor Datasets | Breeding | 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 | Location | Type | Countries |
---|---|---|---|---|---|
Population Density | See citation | Breeding pairs/location | Exposure Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries | Lab |
---|---|---|---|---|---|---|---|---|---|---|
DDT (4,4'-) | 14560 ng/g lw | Premature fetus concentration | B | Embryo | 9 | Coastal sites | Toxicity Factor Datasets | USA | ||
PCB | 1492 ng/g ww | Late-term fetus concentration | B | Embryo | 11 | Coastal sites | Toxicity Factor Datasets | USA | ||
DDT (4,4'-) | 4951 ng/g lw | Late-term fetus concentration | B | Embryo | 11 | Coastal sites | Toxicity Factor Datasets | USA | ||
PCB | 6831 ng/g lw | Late-term fetus concentration | B | Embryo | 11 | Coastal sites | Toxicity Factor Datasets | USA | ||
CEFTIOFUR CRYSTALLINE FREE ACID (EXCEDE) | 24.0 hr | Time to peak conc. | B | Not Reported | 12 | The Marine Mammal Center | Toxicity Factor Datasets | Marin | USA | |
CEFTIOFUR CRYSTALLINE FREE ACID (EXCEDE) | 60.8 hg | Terminal half-life | B | Not Reported | 12 | The Marine Mammal Center | Toxicity Factor Datasets | Marin | USA | |
VANADIUM (elemental) | San Pedro: 7.8, Roosevelt: 2.1, Alamo: 4.2 µg/g dw | Eggshell concentration | San Pedro: 2, Roosevelt: 2, Alamo: 1 | Toxicity Factor Datasets | ||||||
ZINC (elemental) | San Pedro: 43.2, Roosevelt: 43.3, Alamo: 57.9 µg/g dw | Eggshell concentration | San Pedro: 2, Roosevelt: 2, Alamo: 1 | Toxicity Factor Datasets | ||||||
MANGANESE COMPOUNDS | B850 site: 8.7, WOP vale site: 6.0 | Liver concentration | M | Yearling | 7 | Altamont hills | Toxicity Factor Datasets | San Joaquin | USA | |
CIPROFLAXACIN | 7.4 L/kg | Vol. distribution as function of bioavailability | NR | Not Reported | 20 | The Marine Mammal Center | Toxicity Factor Datasets | Marin | USA | |
CIPROFLAXACIN | 7.80 1/hr | Nonintravenous absorption rate | NR | Not Reported | 20 | The Marine Mammal Center | Toxicity Factor Datasets | Marin | USA | |
CIPROFLAXACIN | 0.22 1/hr | Elimination rate constant | NR | Not Reported | 20 | The Marine Mammal Center | Toxicity Factor Datasets | Marin | USA | |
CIPROFLAXACIN | 0.54 hr | Lag time | NR | Not Reported | 20 | The Marine Mammal Center | Toxicity Factor Datasets | Marin | USA | |
CIPROFLAXACIN | 1.67 mL/hr/kg | Total body clearance as function of bioavailability | NR | Not Reported | 20 | The Marine Mammal Center | Toxicity Factor Datasets | Marin | USA | |
CIPROFLAXACIN | 1.01 hr | Time to peak conc. | NR | Not Reported | 20 | The Marine Mammal Center | Toxicity Factor Datasets | Marin | USA | |
COPPER (elemental) | San Pedro: 3.1, Roosevelt: 1.6, Alamo: 5.7 µg/g dw | Eggshell concentration | San Pedro: 2, Roosevelt: 2, Alamo: 1 | Toxicity Factor Datasets | ||||||
MANGANESE COMPOUNDS | San Pedro: 3.8, Roosevelt: 3.1, Alamo: 6.1 µg/g dw | Eggshell concentration | San Pedro: 2, Roosevelt: 2, Alamo: 1 | Toxicity Factor Datasets | ||||||
NICKEL (elemental) | San Pedro: 1.4, Roosevelt: 8.4, Alamo: 12.8 µg/g dw | Eggshell concentration | San Pedro: 2, Roosevelt: 2, Alamo: 1 | Toxicity Factor Datasets | ||||||
SELENIUM (elemental) | San Pedro: <0.5, Roosevelt: 1.8, Alamo: 0.95 µg/g dw | Eggshell concentration | San Pedro: 2, Roosevelt: 2, Alamo: 1 | Toxicity Factor Datasets | ||||||
STRONTIUM | San Pedro: 459, Roosevelt: 188, Alamo: 201.3 µg/g dw | Eggshell concentration | San Pedro: 2, Roosevelt: 2, Alamo: 1 | Toxicity Factor Datasets | ||||||
LEAD (elemental) | San Pedro: <0.5, Roosevelt: 1.5, Alamo: <0.5 µg/g dw | Eggshell concentration | San Pedro: 2, Roosevelt: 2, Alamo: 1 | Toxicity Factor Datasets | ||||||
HEXACHLOROCYCLOHEXANE | 213 ng/g lw | Egg concentration | Embryo | 8 | Yellow River Delta | Toxicity Factor Datasets | CHINA | |||
PCB | 181 ng/g lw | Egg concentration | Embryo | 8 | Yellow River Delta | Toxicity Factor Datasets | CHINA | |||
PBDE MIXTURE | 54 ng/g lw | Egg concentration | Embryo | 8 | Yellow River Delta | Toxicity Factor Datasets | CHINA | |||
DECABROMODIPHENYL ETHANE (DBDPE) | 0.4 ng/g lw | Egg concentration | Embryo | 8 | Yellow River Delta | Toxicity Factor Datasets | CHINA | |||
PBDE MIXTURE | Aquatic: 1600, terrestrial: 430 ng/g lw | Egg concentration | Embryo | 13 | Central and coastal areas | Toxicity Factor Datasets | SPAIN | |||
DECABROMODIPHENYL ETHER (DBDPE) | 8.2 ng/g lw | Egg concentration | Embryo | 12 | Great Lakes Basin | Toxicity Factor Datasets | CANADA | |||
BIS(2,4,6-TRIBROMOPHENOXY)ETHANE (BTBPE) | 13 ng/g lw | Egg concentration | Embryo | 12 | Great Lakes Basin | Toxicity Factor Datasets | CANADA | |||
ZINC (elemental) | 5.83 mg/kg | Egg concentration | Embryo | 60 | NJ, PA, DE, MD, VA | Toxicity Factor Datasets | USA | |||
HEXACHLOROCYCLOHEXANE | 0.0035 mg/kg | Egg concentration | Embryo | 60 | NJ, PA, DE, MD, VA | Toxicity Factor Datasets | USA | |||
CIS-NONACHLOR | 0.026 mg/kg | Egg concentration | Embryo | 60 | NJ, PA, DE, MD, VA | Toxicity Factor Datasets | USA | |||
MERCURY (elemental) | 0.22 mg/kg | Egg concentration | Embryo | 60 | NJ, PA, DE, MD, VA | Toxicity Factor Datasets | USA | |||
SELENIUM (elemental) | 0.26 mg/kg | Egg concentration | Embryo | 60 | NJ, PA, DE, MD, VA | Toxicity Factor Datasets | USA | |||
HYDROXYLATED PCB (OH-PCB) | 8.77 ng/g ww | Plasma concentration, geometric mean | NR | Nestling | 36 nests | Great Lake Basin | Toxicity Factor Datasets | CANADA | ||
MIREX | Terrestrial: 733, aquatic: 330 ng/g lw | Egg concentration | Embryo | Terrestrial: 12, aquatic: 2 | Great Lakes Basin | Toxicity Factor Datasets | CANADA | |||
PBDE MIXTURE | Aquatic: 3300, terrestrial: 4200 ng/g lw | Egg concentration | Embryo | 12 | Great Lakes Basin | Toxicity Factor Datasets | CANADA | |||
PERFLUOROHEXASULFONATE (PFHxS) | 0.80 ng/g ww | Egg concentration | Embryo | 10 | Toxicity Factor Datasets | SWEDEN | ||||
PCB | 152 µg/g lw | Chick concentration | Chick | 7 | Toxicity Factor Datasets | USA | ||||
PCB | Review | Egg concentration | Embryo | See citation | North Rhine-Westphalia / Rhineland Palatinate | Toxicity Factor Datasets | GERMANY | |||
MANGANESE COMPOUNDS | 3730 ppb dw ± 1180 | Egg concentration | Embryo | 2 | Agassiz National Wildlife Refuge | Toxicity Factor Datasets | USA | |||
MANGANESE COMPOUNDS | San Pedro: 2.1, Roosevelt: 0.8, Alamo: 3.9 µg/g dw | Egg concentration | San Pedro: 5, Roosevelt: 2, Alamo: 1 | Toxicity Factor Datasets | ||||||
CHLOROPHACINONE | Broadcast: 85.5, spot: 89.0% | % reduction in population index | B | Not Reported | See citation | Bakersfield and King City | Toxicity Factor Datasets | USA | ||
TRAMADOL HYDRCHLORIDE | 1.40 L/hr/kg | Total body clearance as function of bioavailability | NR | Not Reported | 15 | The Marine Mammal Center | Toxicity Factor Datasets | Marin | USA | |
ZINC (elemental) | See citation Table 1 | Hair concentration | B | Pup | 199 | Gulf of California | Toxicity Factor Datasets | MEXICO | ||
PENTACHLOROPHENOL | 3.16 ng/g ww | Plasma concentration, geometric mean | NR | Nestling | 37 nests | Great Lake Basin | Toxicity Factor Datasets | CANADA | ||
DECHLORANE PLUS | Terrestrial: 38.4, aquatic: 27.7 ng/g lw | Egg concentration | Embryo | Terrestrial: 12, aquatic: 2 | Great Lakes Basin | Toxicity Factor Datasets | CANADA | |||
PBDE MIXTURE | 7.85 µg/g lw | Egg concentration | Embryo | 95 | Toxicity Factor Datasets | USA | ||||
PERFLUOROOCTANESULFONIC ACID (PFSA) | 83 ng/g ww | Egg concentration | Embryo | 10 | Toxicity Factor Datasets | SWEDEN | ||||
PBDE MIXTURE | 131 ng/g ww | Egg concentration | Embryo | 11 | MD, VA | Toxicity Factor Datasets | USA | |||
PCB | Review | Eggshell thickness | Embryo | See citation | North Rhine-Westphalia / Rhineland Palatinate | Toxicity Factor Datasets | GERMANY | |||
MERCURY (elemental) | 355 ppb dw ± 215 | Egg concentration | Embryo | 2 | Agassiz National Wildlife Refuge | Toxicity Factor Datasets | USA | |||
NICKEL (elemental) | San Pedro: 0.7, Roosevelt: <0.5, Alamo: <0.5 µg/g dw | Egg concentration | San Pedro: 5, Roosevelt: 2, Alamo: 1 | Toxicity Factor Datasets | ||||||
DIPHACINONE | Broadcast: 84.4, spot: 87.1% | % reduction in population index | B | Not Reported | See citation | Bakersfield and King City | Toxicity Factor Datasets | USA | ||
TRAMADOL HYDRCHLORIDE | 1.52 hr | Time to peak conc. | NR | Not Reported | 15 | The Marine Mammal Center | Toxicity Factor Datasets | Marin | USA | |
LEAD (elemental) | See citation Table 1 | Hair concentration | B | Pup | 199 | Gulf of California | Toxicity Factor Datasets | MEXICO | ||
DIELDRIN | 0.20 mg/kg | Egg concentration | Embryo | 60 | NJ, PA, DE, MD, VA | Toxicity Factor Datasets | USA | |||
DDE (4,4'-) | 2.70 ng/g ww | Plasma concentration, geometric mean | NR | Nestling | 38 nests | Great Lake Basin | Toxicity Factor Datasets | CANADA | ||
MIREX | Terrestrial: 13.5, aquatic: 29 ng/g lw | Egg concentration | Embryo | Terrestrial: 13, aquatic: 8 | Central and coastal areas | Toxicity Factor Datasets | SPAIN | |||
2,2',3,3',4,4',5,5',6,6'-DECABROMODIPHENYL ETHER (BDE-209) | 0.49 µg/g lw | Egg concentration | Embryo | 95 | Toxicity Factor Datasets | USA | ||||
PERFLUORODECANE SULFONATE (PFDS) | 0.66 ng/g ww | Egg concentration | Embryo | 10 | Toxicity Factor Datasets | SWEDEN | ||||
2,2',3,3',4,4',5,5',6,6'-DECABROMODIPHENYL ETHER (BDE-209) | 6.35 ng/g ww | Egg concentration | Embryo | 11 | MD, VA | Toxicity Factor Datasets | USA | |||
MERCURY (elemental) | Review | Egg concentration | Embryo | See citation | Toxicity Factor Datasets | GERMANY | ||||
SELENIUM (elemental) | 2420 ppb dw ± 74.5 | Egg concentration | Embryo | 2 | Agassiz National Wildlife Refuge | Toxicity Factor Datasets | USA | Laboratory | ||
SELENIUM (elemental) | San Pedro: 3.1, Roosevelt: 3.9, Alamo: 3.3 µg/g dw | Egg concentration | San Pedro: 5, Roosevelt: 2, Alamo: 1 | Toxicity Factor Datasets | ||||||
DIPHACINONE | Broadcast: 82.1, spot: 90.2% | % reduction in population index | B | Not Reported | See citation | Bakersfield and King City | Toxicity Factor Datasets | USA | ||
TRAMADOL HYDRCHLORIDE | 357.8 ng/mL | Peak concentration | NR | Not Reported | 15 | The Marine Mammal Center | Toxicity Factor Datasets | Marin | USA | |
SELENIUM (elemental) | See citation Table 1 | Hair concentration | B | Pup | 199 | Gulf of California | Toxicity Factor Datasets | MEXICO |