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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 |
---|---|---|---|---|---|---|---|---|---|---|---|
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 |
DDE (4,4'-) | 14.2% | percent eggshell thinning compared to pre-1947 reference eggs | Female | Adult | 26 breeding attempts | 0.01-8.78 ppm, wet wt, in composite prey samples | 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 |
---|---|---|---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | negative correlation | correlation of heptachlor epoxide concentration in eggs and eggshell thickness | Female | Adult | 38 eggs | 0.10-1.10 ppm, wet wt, in eggs | TOX-REPRO - physiology | NR | environmental contamination | Toxicity Factor Datasets |
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 | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | eggshell thickness index = 1.799 - 0.243(log DDE) | linear regression of eggshell thickness index vs. log DDE concentration in eggs | Female | Adult | 295 eggs | range of mean concentrations in eggs: 0.58-15.19 ppm, wet wt | TOX-REPRO - physiology | NR | environmental contamination | Toxicity Factor Datasets |
MERCURY (elemental) | brood size = 0.848 - 0.635(log DDE) - 0.271(log Hg) | linear regression of brood size vs mercury and DDE concentrations in eggs | Female | Adult | 60 eggs | range of geometric mean concentrations in eggs: 0.21-1.27 ppm, dry wt | TOX-REPRO - reproductive success | NR | environmental contamination | Toxicity Factor Datasets |
DDE (4,4'-) | productivity = 1.412 - 0.724(log DDE) | linear regression of productivity (mean number of young raised per pair) vs. log DDE concentration in eggs | Both Male and Female | Adult | 14 pairs | range of mean concentrations in eggs: 0.58-15.19 ppm, wet wt | TOX-REPRO - reproductive success | NR | environmental contamination | Toxicity Factor Datasets |
DDE (4,4'-), HEPTACHLOR EPOXIDE | 15 ppm DDE, 0.7 ppm heptachlor epoxide | concentrations in eggs associated with population recovery | Both Male and Female | Both Adults and Juveniles | 550 eggs from 469 clutches | range of mean concentrations in eggs, ppm, wet wt: 0.58-15.19 (DDE); 0.01 - 0.77 (heptachlor epoxide) | TOX-POP - size effects | 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 | 11.4% | percent eggshell thinning compared to pre-DDT reference eggs | Female | Adult | Kola Peninsula | 8 nests | geom. mean concentrations in eggs, ppm, wet wt: 3.5 (DDE), 7.3 (PCBs), wet wt, in eggs (geometric 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
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 | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 16% | percent eggshell thinning compared to pre-1947 reference eggs | Female | Adult | South Australia | 13 eggs | 3.98 ppm, wet wt, in eggs | 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'-) | eggshell thickness index = 1.888 - 0.281(log DDE) | linear regression of eggshell thickness index and DDE content of eggs | Female | Adult | Tasmania, Victoria, South Australia | 137 eggs | 1.8-12.4 ppm, wet wt, in eggs (range of geometric means) | TOX-REPRO - physiology | NR | environmental contamination | Toxicity Factor Datasets |
DDE (4,4'-) | productivity = 1.79 - 0.04(DDE) | linear regression of productivity (number of young fledged per site) and DDE concentrations in eggs | Both Male and Female | Adult | Tasmania | 9 eggs | range of geometric means, ppm, wet wt: 2.0-6.1 (eggs); 0.06 - 1.78 (typical prey items) | TOX-REPRO - reproductive success | 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 | data correlating eggshell thinning and DDE concentrations in eggs | Female | Adult | Not Reported | NR | TOX-REPRO - physiology | NR | NR | 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'-) | no relation | linear regression of eggshell thickness and DDE concentration in eggs | Female | Adult | Victoria | 35 eggs | range of concentrations, ppm, wet wt: 2.30 to 82.00 (eggs); negligible to 0.74 (representative prey species) | 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'-) | no effect | eggshell thickness compared to pre-1947 reference eggs | Female | Adult | 2 eggs, 1 nest | 0.69-1.40 ppm, wet wt, in eggs | TOX-REPRO - physiology | NR | environmental contamination | Toxicity Factor Datasets |