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Chemical | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 0.19 µg/kg ww | Egg concentrations | Embryo | Fern Ridge Reservoir | 14 | 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 |
---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 48.68 µg/g | Egg concentration | NR | Embryo | Green Bay | 5 | NR | TOX-EXP IND - accumulation | Environmental contamination | Toxicity Factor Datasets |
DIELDRIN | See citation | Egg concentration | NR | Embryo | Multiple sites in Straight of Georgia | Varied by site | 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 | Type |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | Alaska: 29, California: 77.5 ng/g lw | Blood concentration | B | Juvenile | Alaksa: 3 sites in eastern AK, California: 3 sites between Santa Cruz and Monterey | Alaska: 14, California: 6 | NR | TOX-EXP IND - accumulation | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 0.11 ppm ww | Egg concentration | Embryo | Blackfoot Reservoir | 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 |
---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 0.54 µg/g ww | Feather concentration | NR | Both Adults and Juveniles | Rio Negro Province; rural site: Bariloche; ag site: Valle | 45 | NR | TOX-EXP IND - accumulation | Environmental contamination | Toxicity Factor Datasets |
DIELDRIN | Breeding: not detected | Unspecified tissue concentration | M | Not Reported | Breeding: 1, non-breeding: 5 | NR | TOX-EXP IND - accumulation | Environmental contamination | Toxicity Factor Datasets | |
DIELDRIN | Breeding: 0.12 ppm | Unspecified tissue concentration | F | Not Reported | Breeding: 5, non-breeding: 5 | 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 |
---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | Naramata: 0.13; Cawston: 0.032; Vaseaux: <0.0008 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 |
---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | Penticton (1993): 53.9; Kelowna (1994): not detected; Penticton (1994): 44.8; Penticton (1995): 16.7; Naramata (1997): ND; Penticton (1997): ND; Naramata (1998): ND ug/kg | Egg concentration | B | Embryo | Okanagan Valley | Penticton (1993): 23; Kelowna (1994): 1; Penticton (1994): 2; Penticton (1995): 13, Naramata (1997): 19; Penticton (1997): 12; Naramata (1998): 22 | 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 |
---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | <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 Technique | Type |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 0.56, 0.30, 0.15 ug/g ww | Brain concentration | NR | Not Reported | 3 | NR | TOX-EXP IND - accumulation | Environmental contamination | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|
DIELDRIN | Kettle Creek (1993): 4.0; VBNWA (1993): 0.6; ANWA LH (1997): ND; UBC (1997): ND; EC Park (1997): ND; ANWA (1998): ND; TY Park (1998): ND; UBC (1998): ND; ST Park (1998): ND ug/kg | Egg concentration | Okanagan Valley | Kettle Creek (1993): 4; VBNWA (1993): 2; ANWA LH (1997): 6; UBC (1997): 9; EC Park (1997): 1; ANWA (1998): 1; TY Park (1998): 2; UBC (1998): 5; ST Park (1998): 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 |
---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | Range: <0.03-0.93 µg/g ww | Brain concentration | NR | Not Reported | New Jersey Rabies Laboratory | 5 | 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 Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | See citation Figure 1 | Body concentration | F | Both Adults and Juveniles | Patuxent Wildlife Research Center, Laurel | 47 | Mealworm feed: 1.34 ppm dw | TOX-EXP IND - accumulation | 52 d | Dietary | Toxicity Factor Datasets |
DIELDRIN | Adult: 0.09, juvenile: 0.14 ppm | Guano concentration | Both Adults and Juveniles | Patuxent Wildlife Research Center, Laurel | 47 | Mealworm feed: 1.34 ppm dw | TOX-EXP IND - accumulation | 52 d | Dietary | Toxicity Factor Datasets |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | ponds, southern San Joaquin Valley | 10 animals/dose | 0.1, 0.5 lbs/acre | TOX-MORT - mortality in the field | single application | waterborne | 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 | 34.4 ug/l (95% CL: 31.1 - 38.1 ug/l) | LC50 | Not Reported | Embryo | 20 animals/replicate; 4 replicates/dose | 0, 0.8, 2.0, 4.9, 11.0, 25.4, 64.8, 154.8 ug/l | TOX-MORT - toxicity benchmarks | 21 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 25.1 ug/l | LOAEL, based on mortality but gross spinal deformities also observed | Not Reported | Embryo | 20 animals/replicate; 4 replicates/dose | 0, 0.8, 2.0, 4.9, 11.0, 25.4, 64.8, 154.8 ug/l | TOX-MORT - toxicity benchmarks | 21 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 11.0 ug/l | NOAEL | Not Reported | Embryo | 20 animals/replicate; 4 replicates/dose | 0, 0.8, 2.0, 4.9, 11.0, 25.4, 64.8, 154.8 ug/l | TOX-MORT - toxicity benchmarks | 21 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 8.7 ug/l (95% CL: 7.8-9.7 ug/l) | LC50 | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l | TOX-MORT - toxicity benchmarks | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 11.2 ug/l | LOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l | TOX-MORT - toxicity benchmarks | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 4.0 ug/l | NOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l | TOX-MORT - toxicity benchmarks | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 5.1 ug/g at 8.7 ug/l | whole body dieldrin concentration (ug/g, wet wt.) at the LC50 | Not Reported | Tadpole | Not Reported | 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l | TOX-EXP IND - accumulation | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 6.0 ug/g at 11.2 ug/l | whole body dieldrin concentration (ug/g, wet wt.) | Not Reported | Tadpole | Not Reported | 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l | TOX-EXP IND - accumulation | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 2.0 ug/g at 4.0 ug/l | whole body dieldrin concentration (ug/g, wet wt.) | Not Reported | Tadpole | Not Reported | 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l | TOX-EXP IND - accumulation | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 360 - 540 | range of bioconcentration factors; calculated by dividing the whole body tissue dieldrin concentration by water dieldrin concentration | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l | TOX-EXP IND - accumulation | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 36,000 - 54,000 | range of lipid bioconcentration factors; calculated by dividing the whole body bioconcentration values x 100 by percent lipid | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l | TOX-EXP IND - accumulation | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 30.3 ug/l (95% CL: 26.2 - 35.2 ug/l) | LC50 | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l | TOX-MORT - toxicity benchmarks | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 52.3 ug/l | LOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l | TOX-MORT - toxicity benchmarks | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 12.3 ug/l | NOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l | TOX-MORT - toxicity benchmarks | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 12.0 ug/g at 30.3 ug/l | whole body dieldrin concentration (ug/g, wet wt.) at the LC50 | Not Reported | Tadpole | Not Reported | 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l | TOX-EXP IND - accumulation | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 19.0 ug/g at 52.3 ug/l | whole body dieldrin concentration (ug/g, wet wt.) | Not Reported | Tadpole | Not Reported | 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l | TOX-EXP IND - accumulation | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 0.5 ug/g at 12.3 ug/l | whole body dieldrin concentration (ug/g, wet wt.) at the NOAEL | Not Reported | Tadpole | Not Reported | 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l | TOX-EXP IND - accumulation | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 360 - 900 | range of bioconcentration factors; calculated by dividing the whole body tissue dieldrin concentration by water dieldrin concentration | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l | TOX-EXP IND - accumulation | 4 d | waterborne | Toxicity Factor Datasets |
DIELDRIN | 36,000 - 90,000 | range of lipid bioconcentration factors; calculated by dividing the whole body bioconcentration values x 100 by percent lipid | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l | TOX-EXP IND - accumulation | 4 d | waterborne | 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'-), DIELDRIN, LEAD COMPOUNDS | 1.05 (0.05 SE) ppm (wet wt) | lead concentration in liver | Female | Juvenile | 2 | 38 lead, 48 DDE, 1.2 dieldrin ppm (wet wt) in voles | TOX-EXP IND - accumulation | 60 d | diet | Toxicity Factor Datasets |
DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS | 0.70 (0.20 SE) ppm (wet wt) | lead concentration in tibia | Female | Juvenile | 2 | 38 lead, 48 DDE, 1.2 dieldrin ppm (wet wt) in voles | TOX-EXP IND - accumulation | 60 d | diet | Toxicity Factor Datasets |
DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS | 232 (9 SE) ppm (wet wt) | DDE concentration in carcass | Female | Juvenile | 2 | 38 lead, 48 DDE, 1.2 dieldrin ppm (wet wt) in voles | TOX-EXP IND - accumulation | 60 d | diet | Toxicity Factor Datasets |
DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS | 10.4 (0.6 SE) ppm (wet wt) | DDE concentration in brain | Female | Juvenile | 2 | 38 lead, 48 DDE, 1.2 dieldrin ppm (wet wt) in voles | TOX-EXP IND - accumulation | 60 d | diet | Toxicity Factor Datasets |