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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'-) | decreased compared with pre-1940 eggs | eggshell thickness index (Ratcliffe's Index) | Not Reported | Embryo | Bear River Migratory Bird Refuge | 93 eggs | 6.6 ppm DDE, 1.3 ppm DDD in eggs, wet wt | TOX-REPRO - physiology | NR | in ovo | 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'-) | 12.8 ppm DDE, 0.8 ppm DDD, wet wt | mean concentration in breast muscle | Not Reported | Adult | Bear River Migratory Bird Refuge | 24 birds | 0.01-0.02 ppm DDE in fish | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
DDE (4,4'-) | 61.5 ppm DDE, 5.2 ppm DDD, wet wt | mean concentration in visceral fat | Not Reported | Adult | Bear River Migratory Bird Refuge | 18 birds | 0.01-0.02 ppm DDE in fish | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
DDE (4,4'-) | 0.55 ppm DDE, 0.07 ppm DDD, wet wt | mean concentration in blood | Not Reported | Adult | Bear River Migratory Bird Refuge | 16 birds | 0.01-0.02 ppm DDE in fish | TOX-EXP IND - accumulation | NR | diet | Toxicity Factor Datasets |
DDE (4,4'-) | 6.6 ppm DDE, 1.3 ppm DDD, wet wt | mean concentration in whole eggs | Not Reported | Embryo | 40 eggs | 0.01-0.02 ppm DDE in fish | TOX-EXP IND - accumulation | NR | diet (parental) | 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'-), POLYCHLORINATED BIPHENYLS | no effect | eggshell thickness compared with pre-1947 measurements | Not Reported | Embryo | Tule Lake National Wildlife Refuge | 29 eggs | 1.4 ppm DDE, 0.18 ppm DDT+DDD, 2.21 ppm PCBs in eggs | TOX-REPRO - physiology | NR | in ovo | 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 COMPOUNDS | positive correlation | Hg concentration in brain correlation with P and K concentrations in blood | Not Reported | Adult | Clear Lake, Tule Lake, Eagle Lake | 11 birds | 0.13-0.28 ppm in brain, wet wt (location means) | TOX-Non-Repro-Sublethal - cellular/biochemical effects | NR | site contamination | Toxicity Factor Datasets |
MERCURY COMPOUNDS | 0.001 (Clear Lake), 0.16 (Tule Lake) | productivity (young to adult ratios) at study locations | Not Reported | Adult | Clear Lake, Tule Lake | 13 birds, Clear Lake; 5 birds, Tule Lake | 2.74 (0.89 SD) ppm, wet wt, in liver (Clear Lake); 1.22 (0.08 SD) ppm, wet wt, in liver (Tule Lake) | TOX-REPRO - reproductive success | NR | site contamination | Toxicity Factor Datasets |