California
Snowy Egret (Egretta thula)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
OXYCHLORDANE | MS-90: 0.0355, BI-82: 0.109, BI-89: 0.0153, BI-90: 0.0549, WM-89: 0.0241, WM-90: 0.0306, WM-91: 0.0204, SW-91: 0.0167 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
ZINC (elemental) | BI-89: 53.6, WM-89: 57.8, WM-91: 51.5, SW-91: 52.3 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
HEPTACHLOR EPOXIDE | MS-90: 0.0160, BI-82: not detected, BI-89: 0.0170, BI-90: 0.0242, WM-89: 0.0151, WM-90: 0.0132, WM-91: 0.0146, SW-91: 0.0110 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
TRANS-NONACHLOR | MS-90: 0.0744, BI-82: 0.151, BI-89: 0.0290, BI-90: 0.166, WM-89: 0.0657, WM-90: 0.0677, WM-91: 0.0352, SW-91: 0.366 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
CIS-NONACHLOR | MS-90: 0.0233, BI-82: 0.103, BI-89: not detected, BI-90: 0.114, WM-91: not detected, SW-91: not detected µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DIELDRIN | MS-90: 0.0258, BI-82: 0.0926, BI-89: 0.0270, BI-90: 0.0661, WM-89: 0.0308 WM-90: 0.0204, WM-91: 0.00887, SW-91: 0.0275 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DDD (4,4'-) | MS-90:0.0222, BI-82: 0.246, BI-89: 0.0180, BI-90: 0.0473, WM-89: 0.0168, WM-90: 0.0098, SW-91: 0.0683 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DDT (4,4'-) | MS-90: 0.0122, BI-89: 0.0282, BI-90: 0.0506, WM-89: 0.0185, WM-90: 0.0236, SW-91: 0.0572 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
PCB | 2.49 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Mallard Slough | Toxicity Factor Datasets | USA |
BORON COMPOUNDS | BI-89: 0.408, WM-89: 0.395, WM-91: 0.859, SW-91: 1.29 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
PCB | 1982: 3.32, 1989: 1.23, 1990: 5.38 µg/g ww | Egg concentration | Not Reported | Embryo | 1982: 10, 1989: 5, 1990: 5 | Bair Island | Toxicity Factor Datasets | USA |
BARIUM (elemental) | BI-89: 0.259, WM-89: 0.351, SW-91: 0.823 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
PCB | 1989: 2.19, 1990: 0.792, 1991: 1.55 | Egg concentration | Not Reported | Embryo | 5 | W. Marin Island | Toxicity Factor Datasets | USA |
CHROMIUM (elemental) | BI-89: 0.849, WM-89: 0.813 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
PCB | 0.185 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | S. Wilbur Flood Area | Toxicity Factor Datasets | USA |
COPPER (elemental) | BI-89: 7.16, WM-89: 7.10, WM-91: 7.12, SW-91: 6.21 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DDE (4,4'-) | 0.925 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Mallard Slough | Toxicity Factor Datasets | USA |
IRON (elemental) | BI-89: 119.0, WM-89: 121.0, WM-91: 135.0, SW-91: 141.0 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DDE (4,4'-) | 1982: 2.04, 1989: 1.71, 1990: 1.88 µg/g ww | Egg concentration | Not Reported | Embryo | 1982: 10, 1989: 5, 1990: 5 | Bair Island | Toxicity Factor Datasets | USA |
MAGNESIUM COMPOUNDS | BI-89: 549, WM-89: 623, WM-91: 597, SW-91: 643 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DDE (4,4'-) | 1989: 1.86, 1990: 0.824, 1991: 1.17 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | W. Marin Island | Toxicity Factor Datasets | USA |
MANGANESE COMPOUNDS | BI-89: 2.43, WM-89: 3.07, WM-91: 4.54, SW-91: 2.43 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DDE (4,4'-) | 3.01 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | S. Wilbur Flood Area | Toxicity Factor Datasets | USA |
MOLYBDENUM | BI-89:0.778, WM-89: 0.884, WM-91: 0.617, SW-91: 0.616 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
?-BENZENEHEXACHLORIDE | MS-90: 0.0092, BI-89: 0.0168, BI-09: 0.0342, WM-89: not detected, WM-90: not detected, WM-91: 0.0264, SW-91: 0.0120 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
STRONTIUM | BI-89: 5.01, WM-89: 6.65, WM-91: 6.02, SW-91: 5.71 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
California Black Rail (Laterallus jamaicensis)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|
METHYLMERCURY | See citation Figures 3 & 4 | Blood concentration | Both Male and Female | Not Reported | 64 | Gambinini Marsh, Mid-Petaluma Marsh, Black John Slough | Toxicity Factor Datasets | Sonoma | USA |
METHYLMERCURY | See citation Figures 3 & 4 | Feather concentration | Not Reported | 127 | Gambinini Marsh, Mid-Petaluma Marsh, Black John Slough | Toxicity Factor Datasets | Sonoma | USA |
Pacific Green Turtle (Chelonia mydas)
Chemical | Endpoint Value | Endpoint Description | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|
COPPER (elemental) | Review | Blood concentration | San Diego Bay | Toxicity Factor Datasets | San Diego | USA |
LEAD (elemental) | Review | Blood concentration | San Diego Bay | Toxicity Factor Datasets | San Diego | USA |
Bullfrog (Lithobates catesbeianus formerly Rana catesbeiana)
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|
ENDOSULFAN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
CHLORDECONE (KEPONE) | no effect | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
DDT (Technical Grade Mixture) | increase at 1.0 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
CHLORDANE | no effect | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
CHLORDANE | increase at 0.5 lb/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
ENDRIN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
DIELDRIN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
ALDRIN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
TOXAPHENE (POLYCHLORINATED CAMPHENES) | increase at 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
LINDANE | increase at 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
HEPTACHLOR | increase at 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
Loggerhead Shrike (Lanius ludovicianus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-) | 293.43-820.93 ppm, lipid weight | concentrations of DDT, DDE, DDD (combined) in skin and brains, 2 years post-application | Not Reported | Not Reported | 2 birds | 3.2 km NE of Davis | Toxicity Factor Datasets | Yolo |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-) | see figure | figure showing concentration of DDT and metabolites in skin and brains before and after application | Not Reported | Not Reported | 27 birds (3-4/sampling time) | 3.2 km NE of Davis | Toxicity Factor Datasets | Yolo |
Southern Sea Otter (Enhydra lutris ssp. nereis)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-) | increase | otters that died from infectious diseases contained higher liver DDTs concentrations that those that died of trauma | Both Male and Female | Adult | 4-8 | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
TIN, BUTYL | increase | otters that died of infectious disease contained butyltin liver concentrations greater than those that died of trauma | Both Male and Female | Adult | 8-14 animals | Toxicity Factor Datasets |
Mallard duck (Anas platyrhynchos)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | higher in P8 than in T19 and TF, and in T19 than in TF | maximum likelihood estimate of 2-week Pb exposure rate | Both Male and Female | Both Adults and Juveniles | 50 birds/treatment | Sacramento National Wildlife Refuge; Willows, CA (39deg29'N, 122deg20'W) | Toxicity Factor Datasets | Sacramento |
LEAD (elemental) | higher in P8 than in T19 and TF, and in T19 than in TF | mortality rate (over 4 years) | Both Male and Female | Both Adults and Juveniles | 50 birds/treatment | Sacramento National Wildlife Refuge; Willows, CA (39deg29'N, 122deg20'W) | Toxicity Factor Datasets | Sacramento |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | California Counties | Lab |
---|---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | increased @ 2 #four shot | mortality versus controls | Both Male and Female | Adult | 12 (control); 16 (lab); 63 (field) | Sacramento National Wildlife Refuge | Toxicity Factor Datasets | 1 yr | Sacramento | Laboratory |
LEAD (elemental) | decreased @ 931,000 shot/acre or 2 #four pellets | spleen weight and total white blood cell counts versus controls | Both Male and Female | Adult | 12 (control); 16 (lab); 63 (field) | Sacramento National Wildlife Refuge | Toxicity Factor Datasets | 1 yr | Sacramento | Laboratory |
LEAD (elemental) | decreased @ 2 #four shot | spleen plaque forming cell counts, % packed cell volume versus controls | Both Male and Female | Adult | 16 (2 #four shot) 63 (field exposure) |
Sacramento National Wildlife Refuge | Toxicity Factor Datasets | 1 yr | Sacramento | Laboratory |
LEAD (elemental) | ppm wet wt: 1.40 (0.7), blood; 6.40 (4.92), liver; 38.64 (19.18), femur @ 2 #four shot | mean (2SE) lead concentrations in liver, femur and blood | Male | Adult | 31 birds | Sacramento National Wildlife Refuge | Toxicity Factor Datasets | 1 yr | Sacramento | |
LEAD (elemental) | ppm wet wt: 1.21 (0.78), blood; 2.32 (1.10), liver; 131.13 (90.94), femur @ 2 #four shot | mean (2SE) lead concentrations in liver, femur and blood | Female | Adult | 24 birds | Sacramento National Wildlife Refuge | Toxicity Factor Datasets | 1 yr | Sacramento |
California Sea Lion (Zalophus californianus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|
DDT (Technical Grade Mixture), POLYCHLORINATED BIPHENYLS | increase | incidence of premature parturtion associated with elevated DDT and PCB residues, compared to full term parturient group | Female | Adult | 4-6/group | San Miguel Island | Toxicity Factor Datasets | 6 - 15 yrs |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-), POLYCHLORINATED BIPHENYLS | increase | incidence of premature parturition associated with elevated DDT and PCB levels, compared to full term parturient group | Female | Adult | 10/group | San Miguel Island | Toxicity Factor Datasets | 6 - 14 yrs |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
BROMINE COMPOUNDS, CADMIUM COMPOUNDS, COPPER COMPOUNDS, IRON COMPOUNDS, MANGANESE COMPOUNDS, MERCURY COMPOUNDS, SELENIUM COMPOUNDS, SILVER COMPOUNDS, ZINC COMPOUNDS | increase | incidence of premature parturition correlated with different metal concentrations and ratios | Both Male and Female | Both Adults and Juveniles | 10/group | Toxicity Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Error |
---|---|---|---|---|---|---|---|---|---|---|
Growth Rate | 95.0 | daily weight gain during 1st mo of life | g/d | Female | Pup | 4 | San Nicolas Island | Exposure Factor Datasets | 5-30 d | 11.75 SE |
Deer Mouse (Peromyscus maniculatus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
CADMIUM COMPOUNDS, LEAD COMPOUNDS, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS, SELENIUM COMPOUNDS | no effect | incidence of liver and kidney histopathologies was not related to contaminant concentrations | Not Reported | Not Reported | 26 animals | salt marsh, San Pablo and San Francisco Bays | Toxicity Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Error |
---|---|---|---|---|---|---|---|---|---|---|
Metabolic Rate | 4.45 | field metabolic rate | ml CO2/g/h | Both Male and Female | Adult | 16 | White Mountain Research Station (elev., 1230 - 1830 m) | Exposure Factor Datasets | Inyo, Mono | 0.79 |
Merriam's Kangaroo Rat (Dipodomys merriami)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
HEXACHLOROETHANE | decrease | mean chromosomal abberrations per cell, compared to controls (not exposed to obscurant smoke) | Not Reported | Not Reported | 3-4/group | Goldstone, Fort Irwin | Toxicity Factor Datasets |
HEXACHLOROETHANE | no effect | sister chromatid exchange counts, compared to controls | Not Reported | Not Reported | 3-4/group | Goldstone, Fort Irwin | Toxicity Factor Datasets |
Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
Population Density | range of monthly density estimates over 2 yrs | #/ha | Not Reported | Not Reported | Not Reported | Indian Cove, Joshua Tree National Monument | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Error |
---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 36 | g | Male | Not Reported | NR (74 males and females total) | Owens Valley | Exposure Factor Datasets | Inyo | 0.22 SE |
Double-crested Cormorant (Phalacrocorax auritus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), POLYCHLORINATED BIPHENYLS | 28.8% decrease | mean thickness of eggshells collected in 1969 compared with pre-1946 museum specimens | Female | Adult | 17 eggs | Anacapa Island | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), POLYCHLORINATED BIPHENYLS | 38.3% decrease | mean thickness of eggshells collected in 1969 compared with pre-1946 museum specimens | Female | Adult | 23 eggs | Los Coronados Island | Toxicity Factor Datasets |
California Ground Squirrel (Spermophilus beecheyi)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
SODIUM MONOFLUOROACETATE | decrease @ 6.7 kg/ha | population size | Not Reported | Not Reported | 38.7-54.2 mean squirrel population size range | Exeter, Tulare | Toxicity Factor Datasets | Tulare |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
Age at Sexual Maturity | 1 | yr | Both Male and Female | Adult | Not Reported | University of California, Santa Cruz Campus [lat., 37^oN; long., 122^oW] | Exposure Factor Datasets | Santa Cruz |
Coyote (Canis latrans)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
SODIUM MONOFLUOROACETATE | increase @ 6.7 kg/ha | 5/6 radio-equipped coyotes were found dead during post-treatment period | Not Reported | Not Reported | 6 | Exeter, Tulare | Toxicity Factor Datasets | Tulare |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | mule deer (3%); small mammals (18%); birds (2%); reptiles (2%); insects (2%); fruits (82%); other (1%) | % frequency of food items in scats | % | Not Reported | Not Reported | 199 | Sierra National Forest (elev. 300 -3900 m) | Exposure Factor Datasets | Fresno |
Chemical | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|---|
STRYCHNINE | 2 | carcass count in 1 field (25m x 75m) | birds/field | Not Reported | Not Reported | 2 | Toxicity Factor Datasets | Yolo | |
STRYCHNINE | 86 ug strychnine/0.3 g stomach content | maximal concentration of strychnine measured in stomachs of dead killdeer | Not Reported | Not Reported | 2 | Toxicity Factor Datasets | Yolo |
Mourning Dove (Zenaida macroura)
Chemical | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|
TRICHLOROPHENOXYACETIC ACID (2,4,5-) | increased post-application from 1 to 4.1 birds per 40 ha | population density | Adult | 9 censuses pre- and post-spray | Truckee area | Toxicity Factor Datasets | Nevada |
California Brown Pelican (Pelecanus occidentalis ssp. californicus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-) | significantly decreased compared to pre-1943 samples | eggshell thickness (of intact or broken eggshells) | Female | Adult | 86 eggs | Anacapa Island and Isla Coronado Norte | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-) | increased compared to positive control (1969 data) | mean number of fledglings produced per nest in 1974 | Both Male and Female | Fledgling | 1286 nests | Anacapa Island and Isla Coronado Norte | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-) | non-detectable DDT plus TDE, 96.6 ppm DDE, lipid wet basis | concentration in egg contents | Female | Adult | 39 eggs | Anacapa Island and Isla Coronado Norte | Toxicity Factor Datasets |
Brown Pelican (Pelecanus occidentalis)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-) | 8 ug/g | critical threshold of DDE concentration in egg (wet wt basis) associated with 20% eggshell thinning | Both Male and Female | Embryo | 813 eggs | Toxicity Factor Datasets | |
DDE (4,4'-) | 3 ug/g | lowest level of DDE that would result in severely lowered reproductive success | Both Male and Female | Embryo | 156 eggs | Toxicity Factor Datasets |
Western Grebe (Aechmophorus occidentalis)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
MERCURY COMPOUNDS | positive correlation | Hg concentration in brain correlation with P and K concentrations in blood | Not Reported | Adult | 11 birds | Clear Lake, Tule Lake, Eagle Lake | Toxicity Factor Datasets | Lake, Lassen, Siskiyou |
MERCURY COMPOUNDS | 0.001 (Clear Lake), 0.16 (Tule Lake) | productivity (young to adult ratios) at study locations | Not Reported | Adult | 13 birds, Clear Lake; 5 birds, Tule Lake | Clear Lake, Tule Lake | Toxicity Factor Datasets | Lake, Siskiyou |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), POLYCHLORINATED BIPHENYLS | no effect | eggshell thickness compared with pre-1947 measurements | Not Reported | Embryo | 29 eggs | Tule Lake National Wildlife Refuge | Toxicity Factor Datasets |
Stephens' Kangaroo Rat (Dipodomys stephensi)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 67.26 | g | Both Male and Female | Adult | 14 | Bonsall and San Luis Rey | Exposure Factor Datasets | San Diego |
Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
Home Range | range of median maximum distance moved based on telemetry at 2 sites; 21 - 91 d observation | m | Female | Adult | 9 | Motte Rock Ecological Reserve [lat., 33^o53'N; long., 117^o6'W] and San Jacinto Wildlife Area [lat., 33^o51'N; long., 116^o54'W] | Exposure Factor Datasets | Riverside |
Western Meadowlark (Sturnella neglecta)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 4.00 | body weight of average adult | oz | Not Reported | Adult | Not Reported | Exposure Factor Datasets |
California Vole (Microtus californicus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | see citation | figure of seasonal changes in weight | g | Male | Adult | Not Reported | Sea Ranch | Exposure Factor Datasets | Sonoma |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
Time of Mating/ Laying | Oct. - Aug. | based on % scrotal males and performate females; overall range varied by location and year | Both Male and Female | Adult | Not Reported | Tilden Regional Park and Richmond Field Station | Exposure Factor Datasets |
Western Snowy Plover (Charadrius nivosus ssp. nivosus formerly Charadrius alexandrinus ssp. nivosus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
Survival/ Mortality | 0.643 | minimum annual survival rate of marked individuals | Not Reported | Juvenile | 14 birds | Point Reyes | Exposure Factor Datasets | Marin |
Killdeer (Charadrius vociferus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|---|
Population Density | 2.2 (fall), 1.8 (winter), 1.3 (spring) | mean population density | birds/ha | Not Reported | Not Reported | 10 seasons censused | Limantour Estero | Exposure Factor Datasets | Marin |
Great Horned Owl (Bubo virginianus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Neotoma fuscipes (7.9%), Thomomys bottae (20.7%), Mus musculus (25.0%), Microtus californicus (14.9%), Reithrodontomys megalotis (1.7%), Perognathus sp. (4.1%), Dipodomys agilis (4.3%), Peromyscus sp. (3.8%), Notiosorex crawfordi (0.3%), Sylvilagus sp. (0.8%), Sorex ornatus (0.1%), Scapanus latimanus (0.7%), Stenopelmatus sp (2.1%), Elgaria multicarinata (0.1%), unident. birds (4.3%) | percent of total number of specimens identified in pellets | Not Reported | Not Reported | 25 lbs of pellets | Univ. of Calif., Los Angeles campus | Exposure Factor Datasets | Los Angeles |
Pacific Treefrog (Pseudacris regilla formerly Hyla regilla)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
Time of Mating/ Laying | spring - summer | breeding | Both Male and Female | Adult | Not Reported | Angelo Coast Range Reserve [lat., 39^o44'N; long., 123^o39'W] | Exposure Factor Datasets | Mendocino |
San Clemente Loggerhead Shrike (Lanius ludovicianus ssp. mearnsi)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Survival/ Mortality | 45 | percent of fledglings that died before reaching independence from parents | % | Not Reported | Fledgling | 29 nests | San Clemente Island | Exposure Factor Datasets |
Little Pocket Mouse (Perognathus longimembris)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | see citation | monthly % volume of food items (detailed species-specific list) in feces | % | Both Male and Female | Not Reported | 3 - 26/mo | Irvine Ranch | Exposure Factor Datasets | Orange |
Song Sparrow (Melospiza melodia)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
Longevity | up to 7 | years | Both Male and Female | Adult | 6 animals (from 1000) | San Pablo Marsh; San Francisco Bay | Exposure Factor Datasets | Contra Costa |
Suisun Song Sparrow (Melospiza melodia ssp. maxillaris)
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|
Water Ingestion Rate | review | Not Reported | Not Reported | Not Reported | Suisun Bay | Exposure Factor Datasets |
Ensatina (Ensatina eschscholtzii)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|---|
Home Range | 32.8 | average distance moved between recaptures | ft | Male | Adult | 17 | Pinehurst Madrone Grove Park | Exposure Factor Datasets | Contra Costa |
San Pablo Song Sparrow (Melospiza melodia ssp. samuelis)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|---|
Population Density | 24.5; 15.4; 5.4 | depending on habitat type | nesting pairs/ha | Both Male and Female | Adult | 4 (nesting pair density) | Petaluma marsh | Exposure Factor Datasets | Sonoma |
California Red-legged Frog (Rana draytonii formerly Rana aurora ssp. draytonii)
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|
Time of Fledging or Metamorphosis | July - Sept. | Both Male and Female | Tadpole | Not Reported | Exposure Factor Datasets |
Western Pond Turtle (Actinemys marmorata formerly Clemmys marmorata)
Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
Population Density | range in density estimates at 2 locations | #/ha | Both Male and Female | Both Adults and Juveniles | Not Reported | Trinity River | Exposure Factor Datasets | Trinity |
Sea Otter (Enhydra lutris)
Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
Body Weight - Mean | Individual data available in Table 2 | kg | Male | Juvenile | 33 | Central coast | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Error |
---|---|---|---|---|---|---|---|---|---|
Home Range | 0.8 | km^2 | Male | Adult | 3 | Santa Cruz to San Luis Obispo | Exposure Factor Datasets | Residents | 0.8 SD |
Deer Mouse (Peromyscus maniculatus ssp. gambelii)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Error |
---|---|---|---|---|---|---|---|---|---|---|
Food Ingestion Rate | 0.14 | mean dry stomach content mass | g | Male | Juvenile | 69 | Tule Lake National Wildlife Refuge (1230 m) | Exposure Factor Datasets | Siskiyou | 0.01 SE |
American Kestrel (Falco sparverius)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
Fledging or Weaning Rate | 3.7 | fledged/successful nest | Both Male and Female | Fledgling | 30 nests | Great Basin (1260-2340 m) | Exposure Factor Datasets | Lassen |