American Robin (Turdus migratorius)
Birds, Terrestrial birds, Passeriformes, American Robin (Turdus migratorius)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DIMETHOATE | Control: 28.9; treated: 32.3 u/L | Brain serum cholinesterase activity | NR | Adult | Control: 3; treated: 3 | Sherbrooke, Quebec | Toxicity Factor Datasets | CANADA |
DIMETHOATE | Treated: 9.5 | Brain serum cholinesterase activity | NR | Juvenile | Treated: 1 | Sherbrooke, Quebec | Toxicity Factor Datasets | CANADA |
DIAZINON | Control: 2708; treated: 1403 u/L | Blood serum cholinesterase activity | NR | Adult | Control: 16; treated: 21 | Sherbrooke, Quebec | Toxicity Factor Datasets | CANADA |
DIAZINON | Control: 1712; treated: 582 u/L | Blood serum cholinesterase activity | NR | Juvenile | Control: 9; treated: 13 | Sherbrooke, Quebec | Toxicity Factor Datasets | CANADA |
DIAZINON | Control: 28.9; treated: 26.3 u/L | Brain serum cholinesterase activity | NR | Adult | Control: 3; treated: 6 | Sherbrooke, Quebec | Toxicity Factor Datasets | CANADA |
DIAZINON | Treated: 7.5 | Brain serum cholinesterase activity | NR | Juvenile | Treated: 2 | Sherbrooke, Quebec | Toxicity Factor Datasets | CANADA |
DIMETHOATE | 18% | Egg mortality | B | Embryo | 41 nests | Sherbrooke, Quebec | Toxicity Factor Datasets | CANADA |
DIAZINON | 31% | B | Embryo | 24 nests | Sherbrooke, Quebec | Toxicity Factor Datasets | CANADA | |
DIMETHOATE | No effect except treatments up to d 3 (decreased) | Mean eggs laid | B | Embryo | See citation | Sherbrooke, Quebec | Toxicity Factor Datasets | CANADA |
DIAZINON | Decreased | Mean eggs laid | B | Embryo | See citation | Sherbrooke, Quebec | Toxicity Factor Datasets | CANADA |
DIMETHOATE | Control: 2708; treated: 2009 u/L | Blood serum cholinesterase activity | NR | Adult | Control: 16; treated: 24 | Sherbrooke, Quebec | Toxicity Factor Datasets | CANADA |
DIMETHOATE | Control: 1712; treated: 1116 u/L | Blood serum cholinesterase activity | NR | Juvenile | Control: 9; treated: 5 | Sherbrooke, Quebec | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sample Size | Location | Type |
---|---|---|---|---|---|
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 | 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 | Okanagan Valley | 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 | 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 | Okanagan Valley | 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 | 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 | Okanagan Valley | 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 | 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 | Okanagan Valley | 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 | 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 | Okanagan Valley | Toxicity Factor Datasets |
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 | 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 | Okanagan Valley | 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 | 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 | Okanagan Valley | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | Soil: 53; earthworm: 73 | Bioaccessible fraction of Pb in soil vs. earthworms (modeled) | NR | Not Reported | See citation | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
ACEPHATE | 23 d post application: 1.99 | Total plasma cholinesterase activity | 1 | Poinsett County and Wapanocca Nation Wildlife Refuge | Toxicity Factor Datasets | USA | ||
DICROTOPHOS | 12 d post application: 1.99; 24 d: 1.17 | Total plasma cholinesterase activity | 12 d: 1; 24 d: 6 | Poinsett County and Wapanocca Nation Wildlife Refuge | Toxicity Factor Datasets | USA | ||
MALATHION | 2 and 4 d post application: 1.46; 5 d: 1.17; 8 d: 1.99 | Total plasma cholinesterase activity | 2, 4, 8 d: 1; 5 d: 6 | Poinsett County and Wapanocca Nation Wildlife Refuge | Toxicity Factor Datasets | USA | ||
ACEPHATE | 23 d post application: 0.31 | Total plasma acetylcholinesterase activity | 1 | Poinsett County and Wapanocca Nation Wildlife Refuge | Toxicity Factor Datasets | USA | ||
DICROTOPHOS | 12 d post application: 0.31; 24 d: 0.26 | Total plasma acetylcholinesterase activity | 12 d: 1; 24 d: 6 | Poinsett County and Wapanocca Nation Wildlife Refuge | Toxicity Factor Datasets | USA | ||
MALATHION | 2 and 4 d post application: 0.23; 5 d: 0.26; 8 d: 0.31 | Total plasma acetylcholinesterase activity | 2, 4, 8 d: 1; 5 d: 6 | Poinsett County and Wapanocca Nation Wildlife Refuge | Toxicity Factor Datasets | USA | ||
ACEPHATE | With/without plasma cholinesterase reactivation: 69 g | Body mass | B | Not Reported | Reactivation: 1; no reactivation: 7 | Poinsett County and Wapanocca Nation Wildlife Refuge | Toxicity Factor Datasets | USA |
ACEPHATE | Plasma cholinesterase reactivation: 2.0; no reactivation: 2.1 % | Body fat score | B | Not Reported | Reactivation: 1; no reactivation: 7 | Poinsett County and Wapanocca Nation Wildlife Refuge | Toxicity Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | 4.5, 3.5, 3.3 ug/g ww | Brain concentration | NR | Not Reported | 3 | Toxicity Factor Datasets | USA | |
OXYCHLORDANE | 4.9, 4.2, 4.2 ug/g ww | Brain concentration | NR | Not Reported | 3 | Toxicity Factor Datasets | USA | |
TRANS-NONACHLOR | 4.6, 2.8, 3.7 ug/g ww | Brain concentration | NR | Not Reported | 3 | Toxicity Factor Datasets | USA | |
DIELDRIN | 0.56, 0.30, 0.15 ug/g ww | Brain concentration | NR | Not Reported | 3 | Toxicity Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
SELENIUM (elemental) | Reference: 3.17; mining: 4.48 mg/kg dw | Egg concentration | Reference: 18; mining: 23 | Soda Springs | Toxicity Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
ORGANOCHLORINES | Orchard/sprayed: 88.0; non-orchard/non-sprayed: 92.0 % | Hatching rate | B | Embryo | Orchard/sprayed: 93; non-orchard/non-sprayed: 25 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
ORGANOCHLORINES | Orchard/sprayed: 2.34; non-orchard/non-sprayed: 1.96 hatchlings/nest | Brood size | B | Nestling | Orchard/sprayed: 93; non-orchard/non-sprayed: 23 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
ORGANOCHLORINES | Orchard/sprayed: 78.9; non-orchard/non-sprayed: 68.4 % fledged/brood | Fledge rate | B | Fledgling | Orchard/sprayed: 90; non-orchard/non-sprayed: 42 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
PCB | Orchard/sprayed (1997): 0.1266; non-orchard/non-sprayed (1997): 0.1311; orchard/sprayed (1998): 0.1281; non-orchard/non-sprayed (1998): 0.1288 | Eggshell thickness | B | Embryo | Orchard/sprayed (1997): 60; non-orchard/non-sprayed (1997): 19; orchard/sprayed (1998): 45; non-orchard/non-sprayed (1998): 28 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
HEPTACHLOR EPOXIDE | Penticton (1993): 1.5; Kelowna (1994): 0.4; Penticton (1994): 0.4; Penticton (1995): 0.4, Naramata (1997): 0.1; Penticton (1997): 0.1; Naramata (1998): 0.2 ug/kg | Egg concentration | B | Embryo | Penticton (1993): 23; Kelowna (1994): 1; Penticton (1994): 2; Penticton (1995): 13, Naramata (1997): 19; Penticton (1997): 12; Naramata (1998): 22 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
ORGANOCHLORINES | Orchard/sprayed (1997): 0.1266; non-orchard/non-sprayed (1997): 0.1311; orchard/sprayed (1998): 0.1281; non-orchard/non-sprayed (1998): 0.1288 | Eggshell thickness | B | Embryo | Orchard/sprayed (1997): 60; non-orchard/non-sprayed (1997): 19; orchard/sprayed (1998): 45; non-orchard/non-sprayed (1998): 28 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
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 | Penticton (1993): 23; Kelowna (1994): 1; Penticton (1994): 2; Penticton (1995): 13, Naramata (1997): 19; Penticton (1997): 12; Naramata (1998): 22 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
Penticton (1993): 22.5; Kelowna (1994): 26.2; Penticton (1994): 38.5; Penticton (1995): 31.4, Naramata (1997): 6.1; Penticton (1997): 0.3; Naramata (1998): 7.1 ug/kg | Egg concentration | B | Embryo | Penticton (1993): 23; Kelowna (1994): 1; Penticton (1994): 2; Penticton (1995): 13, Naramata (1997): 19; Penticton (1997): 12; Naramata (1998): 22 | Okanagan Valley | Toxicity Factor Datasets | CANADA | |
CHLORDANE | Penticton (1993): 13.3; Kelowna (1994): 17.3; Penticton (1994): 6.5; Penticton (1995): 10.5, Naramata (1997):1.6; Penticton (1997): 0.8; Naramata (1998): 1.6 ug/kg | Egg concentration | B | Embryo | Penticton (1993): 23; Kelowna (1994): 1; Penticton (1994): 2; Penticton (1995): 13, Naramata (1997): 19; Penticton (1997): 12; Naramata (1998): 22 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
DDE (4,4'-) | Penticton (1993): 55.8; Kelowna (1994): 17.4; Penticton (1994): 62.0; Penticton (1995): 60.3, Naramata (1997): 46.1; Penticton (1997): 26.7; Naramata (1998): 22.7 mg/kg | Egg concentration | B | Embryo | Penticton (1993): 23; Kelowna (1994): 1; Penticton (1994): 2; Penticton (1995): 13, Naramata (1997): 19; Penticton (1997): 12; Naramata (1998): 22 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
DDD (4,4'-) | Penticton (1993): 0.5; Kelowna (1994): 0.2; Penticton (1994): 0.2; Penticton (1995): 0.2, Naramata (1997): 0.7; Penticton (1997): 0.1; Naramata (1998): 0.2 mg/kg | Egg concentration | B | Embryo | Penticton (1993): 23; Kelowna (1994): 1; Penticton (1994): 2; Penticton (1995): 13, Naramata (1997): 19; Penticton (1997): 12; Naramata (1998): 22 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
DDT (4,4'-) | Penticton (1993): 6.5; Kelowna (1994): 3.4; Penticton (1994): 11.2; Penticton (1995): 3.4, Naramata (1997): 11.5; Penticton (1997): 5.9; Naramata (1998): 3.4 mg/kg | Egg concentration | B | Embryo | Penticton (1993): 23; Kelowna (1994): 1; Penticton (1994): 2; Penticton (1995): 13, Naramata (1997): 19; Penticton (1997): 12; Naramata (1998): 22 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
PCB | Orchard/sprayed: 3.61; non-orchard/non-sprayed: 3.10 eggs/clutch | Clutch size | B | Embryo | Orchard/sprayed: 150; non-orchard/non-sprayed: 42 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
PCB | Orchard/sprayed: 88.0; non-orchard/non-sprayed: 92.0 % | Hatching rate | B | Embryo | Orchard/sprayed: 93; non-orchard/non-sprayed: 25 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
PCB | Orchard/sprayed: 2.34; non-orchard/non-sprayed: 1.96 hatchlings/nest | Brood size | B | Nestling | Orchard/sprayed: 93; non-orchard/non-sprayed: 23 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
PCB | Orchard/sprayed: 78.9; non-orchard/non-sprayed: 68.4 % fledged/brood | Fledge rate | B | Fledgling | Orchard/sprayed: 90; non-orchard/non-sprayed: 42 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
ORGANOCHLORINES | Orchard/sprayed: 3.61; non-orchard/non-sprayed: 3.10 eggs/clutch | Clutch size | B | Embryo | Orchard/sprayed: 150; non-orchard/non-sprayed: 42 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
OCTACHLOROSTYRENE | <0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
DDD (2,4'-) | 0.008 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
HEPTACHLOR EPOXIDE | <0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
DDT (4,4'-) | Decreased | Brain size | B | Adult | See citation | Okanagan Valley | Toxicity Factor Datasets | CANADA |
OXYCHLORDANE | <0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
DDT (4,4'-) | Decreased | Brain RA and HVC size | B | Adult | See citation | Okanagan Valley | Toxicity Factor Datasets | CANADA |
CHLORDANE | <0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
DDT (4,4'-) | Decreased | Brain nucleus intercollicularis size | B | Adult | See citation | Okanagan Valley | Toxicity Factor Datasets | CANADA |
CHLORDANE | <0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
TRANS-NONACHLOR | 0.002 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
CIS-NONACHLOR | 0.003 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
DIELDRIN | <0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
PHOTOMIREX | <0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
<0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA | |
MIREX | <0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
<0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA | |
0.050 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA | |
PENTACHLOROBENZENE | <0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
DDT (4,4'-) | 11.530 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
<0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA | |
DDT (2,4'-) | 0.069 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
<0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA | |
DDE (4,4'-) | 55.775 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
<0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA | |
DDE (2,4'-) | 0.006 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
HEXACHLOROBENZENE | <0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
DDD (4,4'-) | 1.048 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
AZINPHOS-METHYL (GUTHION) | Sprayed: 3.08; control: 2.77 young hatched/nest | Brood size | B | Hatchling | Sprayed: 38; control: 13 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
AZINPHOS-METHYL (GUTHION) | Sprayed: 57.9; control: 61.5 % | Fledging success | B | Hatchling | Sprayed: 38; control: 13 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
AZINPHOS-METHYL (GUTHION) | Sprayed: 3.42; control: 3.15 eggs/clutch | Clutch size | B | Embryo | Sprayed: 38; control: 13 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
AZINPHOS-METHYL (GUTHION) | Sprayed: 90; 87.9 % | Hatching rate | B | Embryo | Sprayed: 38; control: 13 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
LEAD (elemental) | High: 3.64; moderate: 2.32; reference: 0.24 mg/kg dw | Blood concentration | High: 33; moderate: 12; reference: 6 | Coeur d'Alene River Basin | Toxicity Factor Datasets | USA |
LEAD (elemental) | High: 11.7; moderate: 2.90; reference: 0.37 mg/kg dw | Liver concentration | High: 6; moderate: 2; reference: 4 | Coeur d'Alene River Basin | Toxicity Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
PCB | 2.2-3.2 fledgling per nest | Fledgling success | B | Fledgling | NR | Housatonic River | Toxicity Factor Datasets | USA |
PCB | 26% | Mayfield nest success | B | Fledgling | NR | Housatonic River | Toxicity Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
MANGANESE COMPOUNDS | Mining district: 5.3; reference: 6.6 mg/kg dw | Liver concentration | Not reported | See citation | Toxicity Factor Datasets | USA |
NICKEL (elemental) | Mining district: 2.3; reference: 0.62 mg/kg dw | Liver concentration | Not reported | See citation | Toxicity Factor Datasets | USA |
SELENIUM (elemental) | Mining district: 1.9; reference: 3.4 mg/kg dw | Liver concentration | Not reported | See citation | Toxicity Factor Datasets | USA |
STRONTIUM | Mining district: <0.05; reference: 0.18 mg/kg dw | Liver concentration | Not reported | See citation | Toxicity Factor Datasets | USA |
VANADIUM (elemental) | Mining district: 0.36; reference: 0.27 mg/kg dw | Liver concentration | Not reported | See citation | Toxicity Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
CADMIUM (elemental) | Mining district: 52.8; reference: 28.4 mg/kg dw | Kidney concentration | NR | Not Reported | Mining district: 6; reference: 7 | Mining: southeast MO | Toxicity Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | Naramata: 103; Cawston: 67.7; Vaseaux: 1.53 mg/kg ww | Egg concentration | B | Embryo | Naramata: 5; Cawston:5; Vaseaux: 2 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
DDD (4,4'-) | Naramata: 2.96; Cawston: 1.87; Vaseaux: 0.001 mg/kg ww | Egg concentration | B | Embryo | Naramata: 5; Cawston:5; Vaseaux: 2 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
MIREX | Naramata: 0.003; Cawston: 0.003; Vaseaux: 0.003 mg/kg ww | Egg concentration | B | Embryo | Naramata: 5; Cawston:5; Vaseaux: 2 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
Naramata: <0.0012; Cawston: <0.0012; Vaseaux: <0.0012 mg/kg ww | Egg concentration | B | Embryo | Naramata: 5; Cawston:5; Vaseaux: 2 | Okanagan Valley | Toxicity Factor Datasets | CANADA | |
Naramata: <0.0014; Cawston: <0.0014; Vaseaux: <0.0014 mg/kg ww | Egg concentration | B | Embryo | Naramata: 5; Cawston:5; Vaseaux: 2 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DIAZINON | Treated: 993; control: 585 U/L | Plasma cholinesterase activity | F | Adult | Treated: 6; control: 6 | Laval, Quebec | Toxicity Factor Datasets | CANADA |
DIAZINON | Treated: 28.7; control: 27.6 U/g | Brain cholinesterase activity | F | Adult | Treated: 5; control: 6 | Laval, Quebec | Toxicity Factor Datasets | CANADA |
ACEPHATE | Treated: 795; control: 585 U/L | Plasma cholinesterase activity | F | Adult | Treated: 3; control: 6 | Laval, Quebec | Toxicity Factor Datasets | CANADA |
ACEPHATE | Treated: 26.3; control: 27.6 U/g | Brain cholinesterase activity | F | Adult | Treated: 3; control: 6 | Laval, Quebec | Toxicity Factor Datasets | CANADA |