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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 |
---|---|---|---|---|---|---|---|---|---|---|
DDT (4,4'-) | Decreased | Brain nucleus intercollicularis size | B | Adult | Okanagan Valley | See citation | NR | TOX-Non-Repro-Sublethal - organ/system effects | 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 |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | Soil: 53; earthworm: 73 | Bioaccessible fraction of Pb in soil vs. earthworms (modeled) | NR | Not Reported | See citation | See citation for model values | TOX-EXP IND - accumulation | Computer model | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
ACEPHATE | 23 d post application: 1.99 | Total plasma cholinesterase activity | Poinsett County and Wapanocca Nation Wildlife Refuge | 1 | 0.252 and 0.336 kg/ha | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Field-applied | Toxicity Factor Datasets | ||
DICROTOPHOS | 12 d post application: 1.99; 24 d: 1.17 | Total plasma cholinesterase activity | Poinsett County and Wapanocca Nation Wildlife Refuge | 12 d: 1; 24 d: 6 | 0.280 kg/ha | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Field-applied | Toxicity Factor Datasets | ||
MALATHION | 2 and 4 d post application: 1.46; 5 d: 1.17; 8 d: 1.99 | Total plasma cholinesterase activity | Poinsett County and Wapanocca Nation Wildlife Refuge | 2, 4, 8 d: 1; 5 d: 6 | 0.437 kg/ha | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Field-applied | Toxicity Factor Datasets | ||
ACEPHATE | 23 d post application: 0.31 | Total plasma acetylcholinesterase activity | Poinsett County and Wapanocca Nation Wildlife Refuge | 1 | 0.252 and 0.336 kg/ha | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Field-applied | Toxicity Factor Datasets | ||
DICROTOPHOS | 12 d post application: 0.31; 24 d: 0.26 | Total plasma acetylcholinesterase activity | Poinsett County and Wapanocca Nation Wildlife Refuge | 12 d: 1; 24 d: 6 | 0.280 kg/ha | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Field-applied | Toxicity Factor Datasets | ||
MALATHION | 2 and 4 d post application: 0.23; 5 d: 0.26; 8 d: 0.31 | Total plasma acetylcholinesterase activity | Poinsett County and Wapanocca Nation Wildlife Refuge | 2, 4, 8 d: 1; 5 d: 6 | 0.437 kg/ha | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Field-applied | Toxicity Factor Datasets | ||
ACEPHATE | With/without plasma cholinesterase reactivation: 69 g | Body mass | B | Not Reported | Poinsett County and Wapanocca Nation Wildlife Refuge | Reactivation: 1; no reactivation: 7 | See citation; other pesticides | TOX-Non-Repro-Sublethal - whole animal | Field-applied | Toxicity Factor Datasets |
ACEPHATE | Plasma cholinesterase reactivation: 2.0; no reactivation: 2.1 % | Body fat score | B | Not Reported | Poinsett County and Wapanocca Nation Wildlife Refuge | Reactivation: 1; no reactivation: 7 | See citation; other pesticides | TOX-Non-Repro-Sublethal - whole animal | Field-applied | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|
SELENIUM (elemental) | Reference: 3.17; mining: 4.48 mg/kg dw | Egg concentration | Soda Springs | Reference: 18; mining: 23 | 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 |
---|---|---|---|---|---|---|---|---|---|---|
DIMETHOATE | Control: 2708; treated: 2009 u/L | Blood serum cholinesterase activity | NR | Adult | Sherbrooke, Quebec | Control: 16; treated: 24 | 480 g/L | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Spray | Toxicity Factor Datasets |
DIMETHOATE | Control: 1712; treated: 1116 u/L | Blood serum cholinesterase activity | NR | Juvenile | Sherbrooke, Quebec | Control: 9; treated: 5 | 480 g/L | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Spray | Toxicity Factor Datasets |
DIMETHOATE | Control: 28.9; treated: 32.3 u/L | Brain serum cholinesterase activity | NR | Adult | Sherbrooke, Quebec | Control: 3; treated: 3 | 480 g/L | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Spray | Toxicity Factor Datasets |
DIMETHOATE | Treated: 9.5 | Brain serum cholinesterase activity | NR | Juvenile | Sherbrooke, Quebec | Treated: 1 | 480 g/L | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Spray | Toxicity Factor Datasets |
DIAZINON | Control: 2708; treated: 1403 u/L | Blood serum cholinesterase activity | NR | Adult | Sherbrooke, Quebec | Control: 16; treated: 21 | 500 g/L | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Spray | Toxicity Factor Datasets |
DIAZINON | Control: 1712; treated: 582 u/L | Blood serum cholinesterase activity | NR | Juvenile | Sherbrooke, Quebec | Control: 9; treated: 13 | 500 g/L | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Spray | Toxicity Factor Datasets |
DIAZINON | Control: 28.9; treated: 26.3 u/L | Brain serum cholinesterase activity | NR | Adult | Sherbrooke, Quebec | Control: 3; treated: 6 | 500 g/L | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Spray | Toxicity Factor Datasets |
DIAZINON | Treated: 7.5 | Brain serum cholinesterase activity | NR | Juvenile | Sherbrooke, Quebec | Treated: 2 | 500 g/L | TOX-Non-Repro-Sublethal - cellular/biochemical effects | Spray | Toxicity Factor Datasets |
DIMETHOATE | 18% | Egg mortality | B | Embryo | Sherbrooke, Quebec | 41 nests | 480 g/L | TOX-MORT - mortality in the field | Spray | Toxicity Factor Datasets |
DIAZINON | 31% | B | Embryo | Sherbrooke, Quebec | 24 nests | 500 g/L | TOX-MORT - mortality in the field | Spray | Toxicity Factor Datasets | |
DIMETHOATE | No effect except treatments up to d 3 (decreased) | Mean eggs laid | B | Embryo | Sherbrooke, Quebec | See citation | 480 g/L | TOX-REPRO - reproductive success | Spray | Toxicity Factor Datasets |
DIAZINON | Decreased | Mean eggs laid | B | Embryo | Sherbrooke, Quebec | See citation | 500 g/L | TOX-REPRO - reproductive success | Spray | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | 4.5, 3.5, 3.3 ug/g ww | Brain concentration | NR | Not Reported | 3 | NR | TOX-EXP IND - accumulation | Environmental contamination | Toxicity Factor Datasets |
OXYCHLORDANE | 4.9, 4.2, 4.2 ug/g ww | Brain concentration | NR | Not Reported | 3 | NR | TOX-EXP IND - accumulation | Environmental contamination | Toxicity Factor Datasets |
TRANS-NONACHLOR | 4.6, 2.8, 3.7 ug/g ww | Brain concentration | NR | Not Reported | 3 | NR | TOX-EXP IND - accumulation | Environmental contamination | Toxicity Factor Datasets |
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 |
---|---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | Kettle Creek (1993): 0.3; VBNWA (1993): ND; ANWA LH (1997): 1.6; UBC (1997): 4.2; EC Park (1997): 1.1; ANWA (1998): ND; TY Park (1998): ND; UBC (1998): 2.9; ST Park (1998): 0.05 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 |
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 |
Kettle Creek (1993): 0.2; VBNWA (1993): 0.9; ANWA LH (1997): ND; UBC (1997): ND; EC Park (1997): 2.1; ANWA (1998): ND; TY Park (1998): 1.4; UBC (1998): 2.0; 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 | |
CHLORDANE | Kettle Creek (1993): 2.3; VBNWA (1993): 3.9; ANWA LH (1997): 3.8; UBC (1997): 9.6; EC Park (1997): 4.8; ANWA (1998): 1.1; TY Park (1998): 0.5; UBC (1998): 15.6; ST Park (1998): 1.1 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 |
DDE (4,4'-) | Kettle Creek (1993): 4.9; VBNWA (1993): 46.7; ANWA LH (1997): 0.9; UBC (1997): 1.5; EC Park (1997): 3.2; ANWA (1998): 0.6; TY Park (1998): 1.9; UBC (1998): 0.6; ST Park (1998): 0.3 mg/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 |
DDD (4,4'-) | Kettle Creek (1993): 0.03; VBNWA (1993): 0.2; ANWA LH (1997): 0.003; UBC (1997): 0.01; EC Park (1997): 0.02; ANWA (1998): 0.01; TY Park (1998): 0.005; UBC (1998): 0.01; ST Park (1998): 0.005 mg/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 |
DDT (4,4'-) | Kettle Creek (1993): 0.3; VBNWA (1993): 1.5; ANWA LH (1997): 0.1; UBC (1997): 0.1; EC Park (1997): 0.2; ANWA (1998): 0.1; TY Park (1998): 0.08; UBC (1998): 0.1; ST Park (1998): 0.05 mg/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 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|---|
Body length | 93.74 | Total length | 0.46 | 85-101 | g | B | Adult | Old Fort Yuma, Imperial County, CA and Tuscon, Pima County, AZ | 62 | Exposure Factor Datasets |
Body length | 33.49 | Tail length | 1.02 | 28-41 | mm | B | Adult | Old Fort Yuma, Imperial County, CA and Tuscon, Pima County, AZ | 62 | Exposure Factor Datasets |
Body length | 13.31 | Hindfoot length | 0.68 | 3.5-15 | mm | B | Adult | Old Fort Yuma, Imperial County, CA and Tuscon, Pima County, AZ | 61 | Exposure Factor Datasets |
Body length | 29.31 | Ear length | 0.34 | 26-35 | mm | B | Adult | Old Fort Yuma, Imperial County, CA and Tuscon, Pima County, AZ | 48 | Exposure Factor Datasets |
Body length | 49.39 | Forearm length | 0.13 | 45.9-51.2 | mm | B | Adult | Old Fort Yuma, Imperial County, CA and Tuscon, Pima County, AZ | 62 | Exposure Factor Datasets |
Body length | 20.19 | Condylo-premexillary length | 0.25 | 19.6-22.1 | mm | B | Adult | Old Fort Yuma, Imperial County, CA and Tuscon, Pima County, AZ | 60 | Exposure Factor Datasets |