Species
Filter by Species
Filter by Toxicity Endpoint Type
Filter by Exposure Endpoint Type
Filter by Chemical
Filter by Location
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'-), DIELDRIN, HEPTACHLOR EPOXIDE, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | increased | occurence of wild birds dying diagnosed with organochlorine poisoning | Both Male and Female | Both Adults and Juveniles | 5 kestrels | 0.17-12.0 (DDE), 0.61-6.55 (PCBs), 0.08-5.17 (heptachlor epoxide), 1.97-5.15 (oxychlordane), 0.38-3.26 (trans-nonachlor), 0.75-3.70 (dieldrin) wet wt in brain | TOX-MORT - mortality in the field | NR | NR | Toxicity Factor Datasets |
Chemical | Endpoint Value | Toxicity Endpoint Type | Type |
---|---|---|---|
POLYCHLORINATED BIPHENYLS | review | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Toxicity Factor Datasets |
POLYCHLORINATED BIPHENYLS | review | TOX-MORT - toxicity benchmarks | 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'-), DDE (4,4'-), DDT (4,4'-) | review | concentrations of chemicals in eggs and diet associated with mortality and eggshell thinning (various raptor species) | Not Reported | Adult | Not Reported | NR | TOX-REPRO - physiology | NR | environmental contamination | Toxicity Factor Datasets |
DIELDRIN | review | concentrations in brain associated with mortality (various raptor species) | Not Reported | Not Reported | Not Reported | NR | TOX-MORT - dose-response data | NR | environmental contamination | Toxicity Factor Datasets |
DIELDRIN | review | concentrations in eggs associated with reduced productivity (various raptor species) | Not Reported | Not Reported | Not Reported | NR | TOX-REPRO - physiology | NR | environmental contamination | Toxicity Factor Datasets |
POLYCHLORINATED BIPHENYLS | review | concentrations in brain associated with mortality (various raptor species) | Not Reported | Not Reported | Not Reported | NR | TOX-MORT - dose-response data | NR | environmental contamination | Toxicity Factor Datasets |
POLYCHLORINATED BIPHENYLS | review | concentrations in eggs associated with reduced reproduction (various raptor species) | Not Reported | Adult | Not Reported | NR | TOX-REPRO - reproductive success | NR | environmental contamination | Toxicity Factor Datasets |
HEPTACHLOR EPOXIDE | review | concentrations in brain associated with mortality (various raptor species) | Not Reported | Not Reported | Not Reported | NR | TOX-MORT - dose-response data | NR | environmental contamination | Toxicity Factor Datasets |
OXYCHLORDANE | review | concentrations in brain associated with mortality (various raptor species) | Not Reported | Not Reported | Not Reported | NR | TOX-MORT - dose-response data | NR | environmental contamination | Toxicity Factor Datasets |
HEPTACHLOR EPOXIDE | review | concentrations in eggs associated with reduced reproduction (various raptor species) | Not Reported | Not Reported | Not Reported | NR | TOX-REPRO - reproductive success | NR | environmental contamination | Toxicity Factor Datasets |
HEXACHLOROBENZENE | review | concentrations in eggs associated with reduced reproduction (various raptor species) | Not Reported | Not Reported | Not Reported | NR | TOX-REPRO - reproductive success | NR | environmental contamination | Toxicity Factor Datasets |
MERCURY COMPOUNDS | review | concentrations in brain and liver associated with mortality (various avian species) | Not Reported | Not Reported | Not Reported | NR | TOX-MORT - dose-response data | NR | environmental contamination | Toxicity Factor Datasets |
MERCURY COMPOUNDS | review | concentrations in eggs associated with reduced reproduction (various avian species) | Not Reported | Not Reported | Not Reported | NR | TOX-REPRO - reproductive success | 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'-) | 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 |
DDE (4,4'-) | 21% decrease | eggshell thickness compared to pre-1940 museum specimens | Female | Adult | Ungava region, Quebec; islands of Northwest Territories | 21 eggs from 12 clutches | mean +/- SE concentrations, ppm: 253 +/- 160 (eggs); 334 +/- 95 (fat of adult females, lipid basis) | TOX-REPRO - physiology | 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'-), HEPTACHLOR EPOXIDE, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | 12.1% | percent eggshell thinning (as indicated by Ratcliffe Index) compared to pre-1947 eggs | Not Reported | Embryo | Mid-Atlantic coastal and urban breeding sites | 39 eggs | range of concentrations in eggs, ppm, wet wt : 2.5-18 (DDT and metabolites); 0.06-0.47 (heptachlor epoxide); 0.16-0.82 (oxychlordane); 2.1-19 (PCBs) | TOX-REPRO - physiology | 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'-), POLYCHLORINATED BIPHENYLS | 11% decrease | eggshell thickness compared to pre-1947 reference eggs | Female | Adult | eastern U.S. coast | 112 eggs | geometric mean concentrations in eggs (n=37), ppm, wet wt: 7.8 (DDE) and 8.9 (PCBs) | TOX-REPRO - physiology | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
AROCLOR 1248, AROCLOR 1254, AROCLOR 1260, DDE (4,4'-), DDT (4,4'-), MERCURY COMPOUNDS | no effect | eggshell thickness compared to pre-1947 reference eggs | Female | Adult | urban nest sites | 9 eggs | mean concentrations in 7 eggs, ppm, wet wt: 3.61 (DDE); 0.026 (DDT); 5.71 (Aroclor 1260); 0.446 (Aroclor 1248); 0.16 (Aroclor 1254); 0.163 (Hg) | TOX-REPRO - physiology | 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'-) | 13.1% and 13.6% decreases in tundrius and anatum ssp. | eggshell thickness compared to pre-1947 reference eggs | Female | Adult | 21 and 34 eggs for tundrius and anatum ssp. | 9.3-10.6 ppm DDE, wet wt, in eggs of tundrius and anatum ssp. | TOX-REPRO - physiology | 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'-) | review | eggshell thickness compared to that of pre-1945 eggs | Female | Adult | Not Reported | NR | TOX-REPRO - physiology | 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 |
---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | review | mortality in conjunction with pesticide use and residues in birds | Not Reported | Adult | Not Reported | NR | TOX-MORT - mortality in the field | 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'-) | 7.4-8.3% | percent eggshell thinning compared with pre-1946 reference eggs | Female | Adult | Amchitka | 3-7 eggs/year | 25.0-39.8 ppm, dry wt, in eggs (range of annual means) | TOX-REPRO - physiology | NR | environmental contamination | Toxicity Factor Datasets |
DDE (4,4'-) | 16.8-24.9% | percent eggshell thinning compared with pre-1946 reference eggs | Female | Adult | Colville, Yukon, Tanana Rivers | 3-11 eggs/year | 105.6-344.3 ppm, dry wt, in eggs (range of annual means) | TOX-REPRO - physiology | 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 |
DDE (4,4'-), MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | +2 to 16% | percent eggshell thinning compared to pre-1947 reference eggs | Female | Adult | Gulf of California | 5 eggs (from 5 nests) | range of residues in eggs, ppm, wet wt: 2.4-25.0 (DDE); 0.5-10.6 (PCBs); 0.2-4.2 (Hg) | TOX-REPRO - physiology | 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'-), 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 | 15% | percent eggshell thinning compared with pre-DDT reference eggs | Female | Adult | Rankin Inlet | 20 eggs | geometric mean (range) residues in eggs, ppm, wet wt: 8.31 (1.67-45.63; PCBs); 4.45 (0.76-28.05; DDE); 0.36 (0.05-1.80; dieldrin) | TOX-REPRO - physiology | NR | environmental contamination | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE | no effect | number of viable eggs or young versus "normal" nest success | Not Reported | Juvenile | Peace, Slave, and Mackenzie Rivers | 15 nests | mean residue concentrations in fat of nesting females (ppm, wet wt): 37.3 (DDT), 284 (DDE), 39.5 (DDD), 3.3 (dieldrin), 4.4 (heptachlor epoxide) | TOX-REPRO - reproductive success | NR | environmental contamination | Toxicity Factor Datasets |
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 |
---|---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, POLYCHLORINATED BIPHENYLS | 15.8% | mean eggshell thinning compared to "pre-pesticide" reference eggs | Female | Adult | Rankin Inlet | 78 eggs | geometric mean concentration in 52 eggs, ppm, wet wt: 7.59 (DDE); 8.74 (PCBs); 0.41 (dieldrin); 0.36 (heptachlor epoxide) | TOX-REPRO - physiology | NR | environmental contamination | Toxicity Factor Datasets |
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 |
DDE (4,4'-) | 7.5% decrease | eggshell thickness compared to "pre-pesticide" reference eggs | Female | Adult | Amchitka Island | 3-6 eggs/year | annual mean concentrations in eggs (range), ppm, wet wt: 1.89 (1.27-2.43) to 6.96 (3.28-13.37) | TOX-REPRO - physiology | 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'-) | 21.7% decrease (tundra population); 16.8% decrease (taiga population); 7.5% decrease (Aleutian population) | eggshell thickness compared to pre-1947 reference eggs | Female | Adult | Colville River (tundra); Yukon River (taiga); Amchitka Island (Aleutian) | 23 eggs (tundra pop.); 14 eggs (taiga pop.); 11 eggs (Aleutian pop.) | mean concentration in eggs, ppm, lipid basis: 889 (tundra); 673 (taiga); 167 (Aleutian) | TOX-REPRO - physiology | 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 |