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Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DDT (Technical Grade Mixture) | 0.78 ppm | mean DDT concentration in plasma of birds sampled 0-1.5 mi from sprayed area | Both Male and Female | Adult | La Grande-Enterprise (OR), Potlatch (ID) | 23 birds | 0.75 lb/ac application | TOX-EXP IND - accumulation | 1 yr | diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
CADMIUM CHLORIDE | increased @ 10, 50 ug/g diet | kidney Cu concentration versus controls | Male | Adult | 8 | 0, 10, or 50 ug Cd/g | TOX-EXP IND - accumulation | 42 days | Diet | Toxicity Factor Datasets |
CADMIUM CHLORIDE | increased @ 10, 50 ug/g diet | kidney Zn concentration versus controls | Male | Adult | 8 | 0, 10, or 50 ug Cd/g | TOX-EXP IND - accumulation | 42 days | Diet | Toxicity Factor Datasets |
CADMIUM CHLORIDE | increased @ 10, 50 ug/g diet | liver cadmium concentration versus controls | Male | Adult | 8 | 0, 10, or 50 ug Cd/g | TOX-EXP IND - accumulation | 42 days | Diet | Toxicity Factor Datasets |
CADMIUM CHLORIDE | no effect | liver Cu concentration versus controls | Male | Adult | 8 | 0, 10, or 50 ug Cd/g | TOX-EXP IND - accumulation | 42 days | Diet | Toxicity Factor Datasets |
CADMIUM CHLORIDE | no effect | liver Zn concentration versus controls | Male | Adult | 8 | 0, 10, or 50 ug Cd/g | TOX-EXP IND - accumulation | 42 days | Diet | Toxicity Factor Datasets |
CADMIUM CHLORIDE | increased @ 10, 50 ug/g diet | kidney Cd concentration versus controls | Male | Adult | 8 | 0, 10, or 50 ug Cd/g | TOX-EXP IND - accumulation | 42 days | Diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
LEAD ACETATE | increased | liver and kidney Pb concentrations versus controls | Male | Adult | 30 | 20 ppm x 1.6(week, after 1st week) | TOX-EXP IND - accumulation | 15 weeks | Diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | one shot: 180.4 (18.1), female; 5.0 (0.6), male two shot: 183.4 (21.2), female; 15.9 (4.1), male | mean (SE) lead residues in femur | Both Male and Female | Adult | 20 females, 10 males/group | 0, 1, 2 lead shot (206 mg avg wt) | TOX-EXP IND - accumulation | Single dose (one shot); repeated dose (two shot) | Gavage | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
RADIONUCLIDES | 160 +/- 162SE mrem/d; range = 7-982 mrem/d | whole animal dose estimated with implanted dosimeters | Not Reported | Not Reported | test reactor area, Idaho National Engineering Lab | 70 animals | Air: 10 - 2000 mroetgen/d | TOX-EXP IND - accumulation | NR | site contamination | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
LEAD COMPOUNDS | Bone; 52.10 +/- 33.81SD, Kidney; 8.46 +/- 3.03SE, Liver; 3.29 +/- 1.77SD, Brain; 0.84 +/- 0.25SE, Feces; 153.6+/- 103.5SD ppm (dry weight) | Mean concentrations in deer mice from roadside site (ppm, dry weight). Feces collected from nest box after 1 yr accumulation. Roadside tissue concentrations significantly different from control site. | Both Male and Female | Adult | Interstate 25, Denver (elev. 1884-2018 m) | 9 - 10 animals | mean surface soil; 73.0 +/- 19.9SD ppm, dry weight | TOX-EXP IND - accumulation | NR | multiple | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
CADMIUM COMPOUNDS, COPPER COMPOUNDS, ZINC COMPOUNDS | Diet:Soil; 128.0 (Cd), 1.31 (Cu), 1.87 (Zn). Liver:Soil; 35.3 (Cd), 0.17 (Cu), 1.25 (Zn). Liver:Diet; 0.27 (Cd), 0.12 (Cu), 0.66 (Zn). | Ratio of metal concentrations (ug/g dry weight) in diet:soil, liver:soil and liver:diet at an abandoned mine site. Diet concentrations measured from stomach contents. Soil based on acid extractable concentrations. Soil copper; liver cadmium, copper an | Both Male and Female | Adult | Blue Grouse Mountain Copper Mine, Honeymoon Bay, Vancouver Island, British Columbia | 6-9 soil or tissue samples/site | Soil: 0.21 +/- 0.006 SD (Cd), 315.0 +/- 3.15SD (Cu), 80.6 +/- 10.4SD (Zn) mg/kg dry weight | TOX-EXP IND - accumulation | NR | site contamination | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 5.8 ppm; range, 3.6-8.2 ppm (wet wt) | mean and range of concentration in carcass, wet wt | Both Male and Female | Adult | near cities | 4 bats | NR | TOX-EXP IND - accumulation | NR | NR | Toxicity Factor Datasets |
DDD (4,4'-) | 0.1 ppm; range, <0.1-0.3 ppm (wet wt) | mean and range of concentration in carcass, wet wt | Both Male and Female | Adult | near cities | 4 bats | NR | TOX-EXP IND - accumulation | NR | NR | Toxicity Factor Datasets |
DDT (4,4'-) | 1.8 ppm; range, 0.6-3.8 ppm (wet wt) | mean and range of concentration in carcass, wet wt | Both Male and Female | Adult | near cities | 4 bats | NR | TOX-EXP IND - accumulation | NR | NR | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), POLYCHLORINATED BIPHENYLS | 10.4 ppm DDE, 8 ppm est. PCBs, <0.1 ppm DDD, 0.2 ppm DDT | residues measured in live and dead eggs | Female | Adult | 11 colonies | <0.1-0.08 ppm DDE, <0.01-0.5 ppm est. PCBs, <0.01-0.04 ppm DDD, <0.01-0.01 ppm DDT in dietary fish | TOX-EXP IND - accumulation | parent diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 250 | Ratio of carcass concentration (4.6 ppm wet wt) to dietary concentration of PCBs | Not Reported | Adult | Lake Pointsett, Dry Lake | 10 carcasses | <0.05-0.11 PCBs, <0.05-0.11 mercury, 0.016-0.092 OC insecticides; ppm (wet wt) in fish | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 5.7 ppm wet wt PCBs | concentration in eggs | Female | Adult | Lake Pointsett, Dry Lake | 5 eggs | <0.05-0.11 PCBs, <0.05-0.11 mercury, 0.016-0.092 OC insecticides; ppm (wet wt) in fish | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 0.24 ppm wet wt PCBs | concentration in carcass | Not Reported | Juvenile | Lake Pointsett, Dry Lake | 5 birds | <0.05-0.11 PCBs, <0.05-0.11 mercury, 0.016-0.092 OC insecticides; ppm (wet wt) in fish | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 14 | Ratio of concentration in carcass (0.64 ppm wet wt mercury) to dietary concentration (fish) | Not Reported | Adult | Lake Pointsett, Dry Lake | 10 carcasses | <0.05-0.11 PCBs, <0.05-0.11 mercury, 0.016-0.092 OC insecticides; ppm (wet wt) in fish | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 0.29 ppm wet wt mercury | mean concentration in eggs | Female | Adult | Lake Pointsett, Dry Lake | 5 eggs | <0.05-0.11 PCBs, <0.05-0.11 mercury, 0.016-0.092 OC insecticides; ppm (wet wt) in fish | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 0.28 ppm wet wt mercury | concentration in liver | Not Reported | Nestling | Lake Pointsett, Dry Lake | 5 birds | <0.05-0.11 PCBs, <0.05-0.11 mercury, 0.016-0.092 OC insecticides; ppm (wet wt) in fish | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 7.98 ppm wet wt mercury | concentration in liver | Both Male and Female | Adult | Lake Pointsett, Dry Lake | 5 birds | <0.05-0.11 PCBs, <0.05-0.11 mercury, 0.016-0.092 OC insecticides; ppm (wet wt) in fish | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Range | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|---|
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 31.3 | mean biomagnification factor for eggs from forage fish | 11.7-56.8 | Female | Adult | 12 eggs/site x 5 sites | 5.8-24.4 pgTCDD equivalents/g fish, wet wt, (5 sites) | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 162.4 pg/g bw gained (wet wt) | pg TCDD equivalents accumulated per gram of body weight gained (from eggs to largest chicks) | Not Reported | Nestling | Green Bay, Lake Michigan | 20 chicks | 24.4 pg TCDD equivalents/g fish, wet wt | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 100.4 pg/g bw gained (wet wt) | pg TCDD equivalents accumulated per gram of body weight gained from egg to largest chick stage | Not Reported | Nestling | Beaver Islands, Lake Michigan | 20 chicks | 5.8 pg TCDD equivalents/g fish, wet wt | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 37.6 pg/g bw gained (wet wt) | pg TCDD equivalents accumulated per gram of body weight gained (from eggs to largest chicks) | Not Reported | Nestling | Thunder Bay, Lake Huron | 20 chicks | 18.1 pg TCDD equivalents/g fish, wet wt | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 28.3 pg/g bw gained (wet wt) | pg TCDD equivalents accumulated per gram of body weight gained (from eggs to largest chicks) | Not Reported | Nestling | North Channel, Lake Huron | 20 chicks | 7.6 pg TCDD equivalents/g fish, wet wt | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 47.5 pg/g bw gained (wet wt) | pg TCDD equivalents accumulated per gram of body weight gained (from eggs to largest chicks) | Not Reported | Nestling | St. Martin's Shoal, Lake Huron | 20 chicks | 11.1 pg TCDD equivalents/g fish, wet wt | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDT (4,4'-) | 13.3 ppm | mean residue concentration in brains of birds that survived | Male | Juvenile | 7 birds | 1,250-2,500 ppm diet | TOX-EXP IND - accumulation | 5 d | diet | Toxicity Factor Datasets |
DDD (4,4'-), DDT (4,4'-) | 19.0 ppm | mean residue concentration in brains of birds that survived | Female | Juvenile | 4 birds | 1,500-2,250 ppm diet | TOX-EXP IND - accumulation | 5 d | diet | Toxicity Factor Datasets |
DDD (4,4'-), DDT (4,4'-) | 42.9 ppm | mean residue concentration in brains of birds that died | Male | Juvenile | 7 birds | 1,250-2,500 ppm diet | TOX-EXP IND - accumulation | 5 d | diet | Toxicity Factor Datasets |
DDD (4,4'-), DDT (4,4'-) | 44.6 ppm | mean residue concentration in brains of birds that died | Female | Juvenile | 4 birds | 1,500-2,250 ppm diet | TOX-EXP IND - accumulation | 5 d | diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
CHLORDANE | 8,906 ppb, range; 4,954 - 15, 609 ppb | mean and range of total technical chlordane residues in newt carcasses (without liver and stomach) 14 days after application | Both Male and Female | Both Adults and Juveniles | 4 | aerial application; water residues, 4.6 ppb (day 7), 0.29 ppb (day 52), 0.009 ppb (day 421); sediment residues, 35 ppb (day 7), 34 ppb (day 52), 20 ppb (day 1014) | TOX-EXP IND - accumulation | 14 d | field application | Toxicity Factor Datasets |
CHLORDANE | 2,116 ppb, range; 1,354 - 3,783 ppb | mean and range of total technical chlordane residues in newt carcasses (without liver and stomach) 451 days after application | Both Male and Female | Both Adults and Juveniles | 6 | aerial application; water residues, 4.6 ppb (day 7), 0.29 ppb (day 52), 0.009 ppb (day 421); sediment residues, 35 ppb (day 7), 34 ppb (day 52), 20 ppb (day 1014) | TOX-EXP IND - accumulation | 451 d | field application | Toxicity Factor Datasets |
CHLORDANE | 176 ppb, range; 29 - 272 ppb | mean and range of total technical chlordane residues in newt carcasses (without liver and stomach) 1036 days after application | Both Male and Female | Both Adults and Juveniles | 8 | aerial application; water residues, 4.6 ppb (day 7), 0.29 ppb (day 52), 0.009 ppb (day 421); sediment residues, 35 ppb (day 7), 34 ppb (day 52), 20 ppb (day 1014) | TOX-EXP IND - accumulation | 1036 d | field application | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
CARBARYL | increased at 0.56 kg/ha (2, 8-9 d. post-spray) | whole carcass concentration of carbaryl | Not Reported | Not Reported | 8-9 birds/group | 0, 0.44, 0.56 kg/ha application | TOX-EXP IND - accumulation | 2, 8-9, 21-30 d. post-spray | field application | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
STRYCHNINE | 86 ug strychnine/0.3 g stomach content | maximal concentration of strychnine measured in stomachs of dead killdeer | Not Reported | Not Reported | 2 | 375 ug/g seed bait | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | 65.4-123.2 ug/g, dry wt | mean lead concentrations in femur (greater accumulation with mixed seed vs. pelleted diet) | Female | Adult | 12/group | 1#8 lead shot (70.0 +/- 0.5 mg) | TOX-EXP IND - accumulation | single | oral | Toxicity Factor Datasets |
LEAD (elemental) | 2.80-4.98 ug/g, dry wt | mean lead concentrations in liver (greater accumulation with mixed seed vs. pelleted diet) | Female | Adult | 12/group | 1#8 lead shot (70.0 +/- 0.5 mg) | TOX-EXP IND - accumulation | single | oral | Toxicity Factor Datasets |