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| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Technique | Type |
|---|---|---|---|---|---|---|---|---|---|---|
| MIREX | Naramata: 0.003; Cawston: 0.003; Vaseaux: 0.003 mg/kg ww | Egg concentration | B | Embryo | Okanagan Valley | Naramata: 5; Cawston:5; Vaseaux: 2 | NR | TOX-EXP IND - accumulation | Environmental contamination | Toxicity Factor Datasets |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Technique | Type |
|---|---|---|---|---|---|---|---|---|---|---|
| MIREX | <0.01 ug/g ww | Egg concentration | B | Embryo | Okanagan Valley | 18 | NR | TOX-EXP IND - accumulation | 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 |
|---|---|---|---|---|---|---|---|---|---|---|
| MIREX | 40.3% decrease @ 8 ppm | sperm concentration | Male | Adult | 5-10/group | 0 and 8 ppm, wet weight (=2.3-2.5 mg/kg bw/d) | TOX-REPRO - physiology | 62 and 69 d (2 study periods) | diet | Toxicity Factor Datasets |
| MIREX | no effect | sperm motility | Male | Adult | 5-10/group | 0 and 8 ppm, wet weight (=2.3-2.5 mg/kg bw/d) | TOX-REPRO - physiology | 62 and 69 d (2 study periods) | diet | Toxicity Factor Datasets |
| AROCLOR 1254, MIREX | 73.3% increase @ 8ppm mirex + 33 ppm Aroclor | semen volume | Male | Adult | 5-10/group | 0 and 8 ppm mirex + 33 ppm Aroclor, wet weight | TOX-REPRO - physiology | 62 and 69 d (2 study periods) | diet | Toxicity Factor Datasets |
| AROCLOR 1254, MIREX | 20.3% decrease @ 8 ppm mirex + 33 ppm Aroclor | sperm concentration | Male | Adult | 5-10/group | 0 and 8 ppm mirex + 33 ppm Aroclor, wet weight | TOX-REPRO - physiology | 62 and 69 d (2 study periods) | diet | Toxicity Factor Datasets |
| AROCLOR 1254, MIREX | no effect | sperm motility | Male | Adult | 5-10/group | 0 and 8 ppm mirex + 33 ppm Aroclor, wet weight | TOX-REPRO - physiology | 62 and 69 d (2 study periods) | 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'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, MIREX, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | increased | mortality due to pesticide exposure based on history, ante-mortem signs, and gross pathology | Not Reported | Not Reported | 8 owls | 13-96 (DDE), 0.01-0.65 (DDD), 0.03-0.17 (DDT, 2.83-71.0 (PCBs), 0.50-9.89 (dieldrin), 0.012-0.27 (HCB), 0.02-1.99 (Mirex), 0.12-7.74 (heptachlor epoxide), 0.98-8.68 (oxychlordane), 0.50-2.29 (trans-nonachlor), ppm wet wt, in brain | TOX-MORT - mortality in the field | NR | NR | Toxicity Factor Datasets |
| Chemical | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Technique | Type |
|---|---|---|---|---|---|---|---|---|
| MIREX | Not detected | Egg concentration | Embryo | Blackfoot Reservoir | NR | TOX-EXP IND - accumulation | Environmental contamination | Toxicity Factor Datasets |
| MIREX | Not detected | Egg concentration | Embryo | Minidoka National Wildlife Refuge | NR | TOX-EXP IND - accumulation | Environmental contamination | Toxicity Factor Datasets |