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Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
PENTACHLOROPHENOL | 22.2 +/- 5.5 ug/g lipid, 30.7 +/- 10.3 ug/g liver, 11.0 +/- 0 ug/g muscle, 4.0 +/- 1.4 ug/g brain at 961 ug/g diet | mean +/- SD tissue concentrations at the reported LOAEL (development) | Not Reported | Juvenile | 4-6 | 25.0, 54.2, 105.0, 233.2, 423.2, 961.0 ug/g diet | TOX-EXP IND - accumulation | 11 d | diet | Toxicity Factor Datasets |
PENTACHLOROPHENOL | 12.2 +/- 2.3 ug/g lipid, 20.7 +/- 3.7 ug/g liver, 3.3 +/- 1.6 ug/g muscle, 2.6 +/- 1.5 ug/g brain at 423.2 ug/g diet | mean +/- SD tissue concentrations at the reported NOAEL (development) | Not Reported | Juvenile | 6-8 | 25.0, 54.2, 105.0, 233.2, 423.2, 961.0 ug/g diet | TOX-EXP IND - accumulation | 11 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 |
---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 9.7 ug/g lipid, 3.3 ug/g skin, 1.3 ug/g brain, 0.8 ug/g liver, 0.7 ug/g muscle at 2.6 ug/g food | mean of day 5, 7, 8 (approx. steady state) tissue concentrations | Not Reported | Juvenile | 6 | <0.2, 2.6, 26.2, 49.3 ug/g diet | TOX-EXP IND - accumulation | 8 d | diet | Toxicity Factor Datasets |
DIELDRIN | 42.5 ug/g lipid, 14.6 ug/g skin, 1.6 ug/g brain, 2.5 ug/g liver, 1.2 ug/g muscle at 26.2 ug/g food | mean of day 5, 7, 8 (approx. steady state) tissue concentrations | Not Reported | Juvenile | 6 | <0.2, 2.6, 26.2, 49.3 ug/g diet | TOX-EXP IND - accumulation | 8 d | diet | Toxicity Factor Datasets |
DIELDRIN | 80.7 ug/g lipid, 30.1 ug/g skin, 1.6 ug/g brain, 4.1 ug/g liver, 1.8 ug/g muscle at 49.3 ug/g food | mean of day 5, 7, 8 (approx. steady state) tissue concentrations | Not Reported | Juvenile | 6 | <0.2, 2.6, 26.2, 49.3 ug/g diet | TOX-EXP IND - accumulation | 8 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 |
---|---|---|---|---|---|---|---|---|---|---|
METHYLMERCURY DICYANDIAMIDE | 0.51-0.54 ppm blood, 2.07-2.41 ppm kidney, 2.35-2.26 ppm liver, 0.74-0.97 ppm breast muscle, 0.47-0.51 ppm brain, 0.88 ppm eggs @ 0.5 ppm in diet | range of mean Hg (ppm wet-weight) concentrations in wild-strain males and females | Both Male and Female | Adult | 6-9 (9 breeding pairs/dose) | control and 0.5 mg Hg/kg diet (Hg as methylmercury dicyandiamide) | TOX-EXP IND - accumulation | 22 Dec. to 27 July, 1976; approx. 7 mo | 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 |
---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 10.6 +/- 2.2 ppm nasal gland, 16.1 +/- 5.1 ppm liver, 5.8 +/- 1.1 ppm kidney, 1.9 +/- 0.1 ppm brain @ 100 ppm diet | mean (+/- SE) DDE levels (ppm wet weight) | Both Male and Female | Juvenile | 4 | control or 100 ppm DDE | TOX-EXP IND - accumulation | 7 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 |
---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 1.23 +/- 0.12 ug/g wet weight | mean +/- SE p,p'-DDE concentration in shell gland mucosa | Female | Adult | Not Reported | control, 40 mg/kg dry weight diet | TOX-EXP IND - accumulation | 45 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 |
---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 38 ug/g wet weight egg (yolk + white), 1.20 ug/g wet weight egg shell gland mucosa @ 40 mg/kg | mean DDE concentrations | Female | Adult | 7-9 | control, 40 mg/kg dry weight | TOX-EXP IND - accumulation | 45 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 |
---|---|---|---|---|---|---|---|---|---|---|
BORIC ACID | 2 ug/g @ control; 4 ug/g @ 100 ppm; 5 ug/g @ 400 ppm; 51 ug/g @ 1600 ppm | boron accumulation in brain (geometric mean; ug/g dry weight) | Both Male and Female | Juvenile | 10 animals/pen; 3 pens/dose | control, 100, 400, 1600 ppm B as boric acid | TOX-EXP IND - accumulation | 10 wks | 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 |
---|---|---|---|---|---|---|---|---|---|---|
BORIC ACID | Egg; 3 ug/g @ 30 ppm, 13 ug/g @ 300 ppm, 49 ug/g @ 1000 ppm: Liver; 15 ug/g @ 300 ppm, 33 ug/g @ 1000 ppm: Brain; 14 ug/g @ 300 ppm, 41 ug/g @ 1000 ppm | boron concentrations in adult tissues (geometric mean; ug/g dry weight). | Both Male and Female | Adult | 10-20/dose | control, 30, 300, 1000 ppm B as boric acid (dry wt basis) | TOX-EXP IND - accumulation | 3 wks (pre-breeding) + breeding period to 21 d post-hatch | diet | Toxicity Factor Datasets |
BORIC ACID | Liver; 3 ug/g @ 30 ppm, 17 ug/g @ 300 ppm, 51 ug/g @ 1000 ppm: Brain; 4 ug/g @ 30 ppm, 19 ug/g @ 300 ppm, 66 ug/g @ 1000 ppm | boron concentrations in ducklings 21 d of age (geometric mean; ug/g dry weight). Concentrations at other doses were not detected. | Both Male and Female | Juvenile | 10-13/dose | control, 30, 300, 1000 ppm B as boric acid (dry wt basis) | TOX-EXP IND - accumulation | 3 wks (pre-breeding) + breeding period to 21 d post-hatch | 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 |
---|---|---|---|---|---|---|---|---|---|---|
ALUMINUM SULFATE | 3.59 ppm dry wt @ control, 5.16 ppm @ 0.1%, 15.52 ppm @ 0.05% | liver aluminum concentrations (ppm, dry wt) in ducklings | Not Reported | Juvenile | 8/dose | control, 0.1, 0.5% aluminum as Al2(SO4)3 | TOX-EXP IND - accumulation | 15 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 |
---|---|---|---|---|---|---|---|---|---|---|
SEWAGE SLUDGE | increase @ 20% Milorganite or Metrogro | liver cadmium concentrations; compared to controls | Male | Adult | 10/dose | control, 5%, 20% Milorganite or Metrogro | TOX-EXP IND - accumulation | 28 d (Milorganite); 57 d (Metrogro) | 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 |
---|---|---|---|---|---|---|---|---|---|---|
PHOSPHORUS (YELLOW OR WHITE) | positive correlation | P4 concentration in fat versus dose | Male | Adult | 4-5 birds/dose | 0, 1.0, 2.0, 3.4, 4.0, 6.5 mg/kg bw (pelletized) | TOX-EXP IND - accumulation | single | oral 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 12.7 +/- 8.7 ppm (wet wt), 253 +/- 160 ppm (lipid wt) | mean (+/-SE) DDE concentration in eggs | Female | Adult | Ungava region, Quebec; islands of Northwest Territories | 10 eggs | 334 +/- 95 ppm in fat (mean +/-SE; lipid basis) of adult females | TOX-EXP IND - accumulation | NR | environmental 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'-), MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 2.4-25.0 (DDE); 0.5-10.6 (PCBs); 0.2-4.2 (Hg) | residues in eggs (ppm, wet wt) | Female | Adult | Gulf of California | 5 eggs (from 5 nests) | range of residues in 8 prey species, whole body or muscle, ppm wet wt: 0.44-7.45 (DDE); 0.02-1.67 (PCBs); 0.3-3.15 (Hg) | TOX-EXP IND - accumulation | NR | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-), DIELDRIN, POLYCHLORINATED BIPHENYLS | 8.31 (1.67-45.63; PCBs); 4.45 (0.76-28.05; DDE); 0.36 (0.05-1.80; dieldrin) | geometric mean (range) residues in eggs, ppm, wet wt | Female | Adult | Rankin Inlet | 20 eggs | geometric mean residues in prey species, ppm, wet wt: non-detect. - 2.11(DDE); non-detect. - 6.88 (PCBs); 0 - 0.51 (dieldrin) | TOX-EXP IND - accumulation | NR | environmental contamination; diet | Toxicity Factor Datasets |
DDE (4,4'-), DIELDRIN, POLYCHLORINATED BIPHENYLS | 0.12 (0-2.59; PCBs); 0.06 (0-2.70; DDE); ND (0-0.06; dieldrin) | geometric mean residues (range) in plasma, ppm, wet wt of nestlings | Not Reported | Juvenile | Rankin Inlet | 79 nestlings | geometric mean residues in prey species, ppm, wet wt: non-detect. - 2.11(DDE); non-detect. - 6.88 (PCBs); 0 - 0.51 (dieldrin) | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
DDE (4,4'-), DIELDRIN, POLYCHLORINATED BIPHENYLS | males: 0.15 (0-3.27; PCBs); 0.31 (0.05-1.95; DDE); 0.03 (0-0.30; dieldrin) females: 0.87 (0-6.82; PCBs); 0.63 (0-4.23; DDE); 0.04 (0-0.37; dieldrin) | geometric mean residues (range) in plasma, ppm, wet wt of adult birds | Both Male and Female | Adult | Rankin Inlet | 26 males, 34 females | geometric mean residues in prey species, ppm, wet wt: non-detect. - 2.11(DDE); non-detect. - 6.88 (PCBs); 0 - 0.51 (dieldrin) | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
DDE (4,4'-), DIELDRIN, POLYCHLORINATED BIPHENYLS | liver: 1.58-59.45, PCBs; 0.99-18.84, DDE; 0.06-0.79, dieldrin breast: 0.35-57.30, PCBs; 0.30-16.95, DDE; 0-0.19, dieldrin | range of residues in liver and breast muscle (ppm, wet wt) of 22-31 day old nestlings found dead | Not Reported | Juvenile | Rankin Inlet | 7 birds | geometric mean residues in prey species, ppm, wet wt: non-detect. - 2.11(DDE); non-detect. - 6.88 (PCBs); 0 - 0.51 (dieldrin) | TOX-EXP IND - accumulation | NR | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, POLYCHLORINATED BIPHENYLS | log DDE in eggs = 0.9723 + 0.8506(log DDE in plasma); r = 0.66 | log-log relationship between DDE in plasma of female birds and DDE in eggs | Female | Adult | Rankin Inlet | 10 females | range of geometric mean concentrations in prey animals, ppm, wet wt: ND-4.22(DDE); ND-4.21 (PCBs); ND-0.19 (dieldrin); ND-1.73 (heptachlor epoxide) | TOX-EXP IND - accumulation | NR | environmental 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'-) | 1.89 (1.27-2.43) -6.96 (3.28-13.37) ppm, wet wt | annual mean (range) concentrations in eggs | Female | Adult | Amchitka Island | 3-6 eggs/year | whole body residues in prey species, ppm, wet wt: 0.006-1.884 | TOX-EXP IND - accumulation | NR | environmental 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE | 0.9-7.2 (DDT); 10.4-41.8 (DDE); 0.9-3.4 (DDD); 0.3-2.0 (dieldrin); 0.2-1.2 (heptachlor epoxide) | range of concentrations in eggs (ppm, wet wt) | Female | Adult | Peace, Slave, and Mackenzie Rivers | 7 eggs | mean (+/- SE) concentrations in fat of nesting females, ppm, wet wt: 37.3 +/- 12.2 (DDT), 284 +/- 62 (DDE), 39.5 +/- 11.2 (DDD), 3.3 +/- 1.3 (dieldrin), 4.4 +/- 2.6 (heptachlor epoxide) | TOX-EXP IND - accumulation | NR | environmental contamination | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE | 37.3 (DDT), 284 (DDE), 39.5 (DDD), 3.3 (dieldrin), 4.4 (heptachlor epoxide) | mean residue concentrations in fat (ppm, wet wt) | Female | Adult | Peace, Slave, and Mackenzie Rivers | 9 birds | mean (+/- SE) concentrations in 11 prey samples, ppm, wet wt: 0.13 +/- 0.18 (DDT), 0.66 +/- 0.67 (DDE), 0.11 +/- 0.16 (DDD), 0.01 +/- 0.02 (dieldrin), 0.05 +/- 0.04 (heptachlor epoxide) | TOX-EXP IND - accumulation | NR | environmental 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN | 48.0 (DDE), 3.35 (DDD), 1.02 (DDT), 1.45 (dieldrin) | mean concentrations of pesticides in eggs (ppm, dry weight) | Female | Adult | Yukon River | 2 eggs | range of mean concentrations in prey items, ppm dry wt: 0.32-6.02 (DDE), 0.07-0.17 (DDD), 0.09-0.19 (DDT), 0.00-0.11 (dieldrin) | TOX-EXP IND - accumulation | NR | environmental contamination | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN | 622.0 (DDE), 25.4 (DDD), 25.3 (DDT), 6.20 (dieldrin) | mean concentrations of pesticides in fat (ppm, dry weight) | Both Male and Female | Adult | Yukon River | 4 birds | range of mean concentrations in prey items, ppm dry wt: 0.32-6.02 (DDE), 0.07-0.17 (DDD), 0.09-0.19 (DDT), 0.00-0.11 (dieldrin) | TOX-EXP IND - accumulation | NR | environmental contamination | 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 |
---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 6.4-33 ppm, dry wt | range of concentrations in whole addled eggs | Female | Adult | 5 eggs from 3 clutches | 0.01-8.78 ppm, wet wt, in composite prey samples | TOX-EXP IND - accumulation | NR | environmental contamination | 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 |
---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 21:0.09 | ratio of average concentration of DDE in eggs to average concentration of DDE in prey items | Female | Adult | 12 prey species, pooled samples of 7-10 individuals | range of mean concentrations in prey species: 0.04-6.0 ppm, wet wt | TOX-EXP IND - accumulation | NR | environmental 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
MERCURY (elemental) | 2.80 - 10.60 ppm, dry wt (females) 3.70 - 8.95 ppm, dry wt (males) | range of concentrations measured in primary and rectrix feathers | Both Male and Female | Adult | Southern Sweden | 3 sample periods; 1-9 birds/sample period | < 0.1 to between 0.1 and 0.2 ppm, wet wt, in pectoral muscles of avian prey species | TOX-EXP IND - accumulation | NR | environmental contamination | Toxicity Factor Datasets |
MERCURY (elemental) | 6.90-29.50 ppm, dry wt (females) 12.10 ppm, dry wt (males) | concentrations measured in primary and rectrix feathers | Both Male and Female | Adult | Northern Sweden | 20 females, 1 male | < 0.1 to >0.4 ppm, wet wt, in pectoral muscles of avian prey species | TOX-EXP IND - accumulation | NR | environmental contamination | Toxicity Factor Datasets |
MERCURY (elemental) | 2.79 (3.10) ppm, dry wt | mean (SD) concentration measured in feathers | Not Reported | Juvenile | Southern Sweden | 3 nests | < 0.1 to between 0.1 and 0.2 ppm, wet wt, in pectoral muscles of avian prey species | TOX-EXP IND - accumulation | NR | environmental contamination | Toxicity Factor Datasets |
MERCURY (elemental) | 8.31(2.59) ppm, dry wt | mean (SD) concentration measured in feathers | Not Reported | Juvenile | Northern Sweden | 3 nests | < 0.1 to >0.4 ppm, wet wt, in pectoral muscles of avian prey species | TOX-EXP IND - accumulation | NR | environmental contamination | 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 |
---|---|---|---|---|---|---|---|---|---|---|
PENTACHLOROBENZENE | see citation | figures of feces and serum concentrations over time at the tested doses | Both Male and Female | Adult | 3/dose | 0, 65, 130, 260, 520 mg/animal | TOX-EXP IND - accumulation | single | oral via capsule | 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 |
---|---|---|---|---|---|---|---|---|---|---|
SELENOMETHIONINE | Y=1.132 + 0.801X (R^2 = 0.932) | relationship between Se concentrations in diet and blood | Both Male and Female | Adult | 9-10 pairs/group | 0,5,9 ppm, dry wt, in diet | TOX-EXP IND - accumulation | 77 d | diet | Toxicity Factor Datasets |
SELENIUM COMPOUNDS | 7.5 ppm Se, dry wt | maximum observed Se concentration in blood | Both Male and Female | Adult | 10 pairs/group | 8 ppm, dry wt, in contaminated prey species | TOX-EXP IND - accumulation | 77 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 |
---|---|---|---|---|---|---|---|---|---|---|
DICOFOL | non-detectable (@ 5 mg/kg), 560 ng/g (@ 20 mg/kg) | mean concentration of metabolite dichlorobenzophenone in eggs | Female | Adult | 10/group | 0,5,20 mg/kg bw | TOX-EXP IND - accumulation | daily, throughout breeding season | gavage | 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 |
---|---|---|---|---|---|---|---|---|---|---|
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | in ng/g, wet wt: 156 (@ 50 ng/g), 380 (@ 250 ng/g), 1098 (@1000 ng/g) | concentration in liver | Not Reported | Nestling | 9-11/group | 0,50,250,1000 g/ng bw | TOX-EXP IND - accumulation | 10 d | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 0.07 +/- 0.03 ppm (uncontaminated site); 0.34 +/- 0.21 ppm (contaminated site) | mean (+/- SE) concentrations in plasma | Not Reported | Adult | Rocky Mountain Arsenal National Wildlife Refuge | 2 birds on contaminated sites; 5 birds on uncontaminated sites | 0.18 ppm (uncontaminated), 1.15 ppm (contaminated) in soil within adult home ranges | TOX-EXP IND - accumulation | NR | habitat contamination | Toxicity Factor Datasets |
DIELDRIN | 0.01 +/- 0.003 ppm (uncontaminated site); 0.22 +/- 0.03 ppm (contaminated site) | mean (+/- SE) concentrations in plasma | Not Reported | Juvenile | Rocky Mountain Arsenal National Wildlife Refuge | 6 birds on contaminated sites; 10 birds on uncontaminated sites | 0.18 ppm (uncontaminated), 1.15 ppm (contaminated) in soil within adult home ranges | TOX-EXP IND - accumulation | NR | habitat contamination | Toxicity Factor Datasets |