Species

Filter by Species

Filter by Toxicity Endpoint Type

Filter by Exposure Endpoint Type

Filter by Chemical

Filter by Location

Displaying 1881 - 1920 of 9478 datapoints
Export to CSV

Turdus migratorius (American robin)

Citation:

Impact of insecticides on the American robin (Turdus migratorius) in a suburban environment.

Author(s)
Décarie, R., DesGranges, J.L., Lépine, C. and Morneau, F.
Issue
3
Volume
80
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Technique Type
ACEPHATE Treated: 795; control: 585 U/L Plasma cholinesterase activity F Adult Laval, Quebec Treated: 3; control: 6 2.2 kg/ha TOX-Non-Repro-Sublethal - cellular/biochemical effects Treatment of nest-containing trees Toxicity Factor Datasets
ACEPHATE Treated: 26.3; control: 27.6 U/g Brain cholinesterase activity F Adult Laval, Quebec Treated: 3; control: 6 2.2 kg/ha TOX-Non-Repro-Sublethal - cellular/biochemical effects Treatment of nest-containing trees Toxicity Factor Datasets
DIAZINON Treated: 2.3; control: 3.1 Mean productivity total nests Laval, Quebec Treated: 11; control: 57 2.2 kg/ha TOX-REPRO - reproductive success Treatment of nest-containing trees Toxicity Factor Datasets
DIAZINON Treated: NR (first clutch) and 2.0 (second); control: 3.2 (first) and 2.6 (second) Mean productivity by clutch order Laval, Quebec Treated: NR (first clutch) and 8 (second); control: 46 (first) and 11 (second) 2.2 kg/ha TOX-REPRO - reproductive success Treatment of nest-containing trees Toxicity Factor Datasets
ACEPHATE Treated: 3.6; control: 3.1 Mean productivity total nests Laval, Quebec Treated: 20; control: 57 2.2 kg/ha TOX-REPRO - reproductive success Treatment of nest-containing trees Toxicity Factor Datasets
ACEPHATE Treated: 3.4 (first clutch) and NR (second); control: 3.2 (first) and 2.6 (second) Mean productivity by clutch order Laval, Quebec Treated: 17 (first clutch) and NR (second); control: 46 (first) and 11 (second) 2.2 kg/ha TOX-REPRO - reproductive success Treatment of nest-containing trees Toxicity Factor Datasets
DIAZINON Treated: 11; control: 13.1 Number feeding flights B Adult Laval, Quebec 56 2.2 kg/ha TOX-REPRO - behavior Treatment of nest-containing trees Toxicity Factor Datasets
DIAZINON Treated: 4.3; control: 5.7 Number of feeding flights F Adult Laval, Quebec 56 2.2 kg/ha TOX-REPRO - behavior Treatment of nest-containing trees Toxicity Factor Datasets
DIAZINON Treated: 60.3; control: 38.4 Total minutes sitting on nestlings NR Adult Laval, Quebec 56 2.2 kg/ha TOX-REPRO - behavior Treatment of nest-containing trees Toxicity Factor Datasets
ACEPHATE Treated: 12.5; control: 13.1 Number feeding flights B Adult Laval, Quebec 56 2.2 kg/ha TOX-REPRO - behavior Treatment of nest-containing trees Toxicity Factor Datasets
ACEPHATE Treated: 5.6; control: 5.7 Number of feeding flights F Adult Laval, Quebec 56 2.2 kg/ha TOX-REPRO - behavior Treatment of nest-containing trees Toxicity Factor Datasets
ACEPHATE Treated: 23.0; control: 38.4 Total minutes sitting on nestlings NR Adult Laval, Quebec 56 2.2 kg/ha TOX-REPRO - behavior Treatment of nest-containing trees Toxicity Factor Datasets
Citation:

Organochlorines and reproductive success of birds in orchard and non-orchard areas of central British Columbia, Canada, 1990–91.

Author(s)
Elliott, J.E., Martin, P.A., Arnold, T.W. and Sinclair, P.H.
Issue
4
Volume
26
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Technique Type
DDT (4,4'-) Naramata: 26.3; Cawston: 10.6; Vaseaux: 0.08 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
DDE (4,4'-) Naramata: 103; Cawston: 67.7; Vaseaux: 1.53 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
DDD (4,4'-) Naramata: 2.96; Cawston: 1.87; Vaseaux: 0.001 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
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
Naramata: <0.0012; Cawston: <0.0012; Vaseaux: <0.0012 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
Naramata: <0.0014; Cawston: <0.0014; Vaseaux: <0.0014 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
TRANS-NONACHLOR Naramata: 0.039; Cawston: 0.035; 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
OXYCHLORDANE Naramata: 0.016; Cawston: 0.016; Vaseaux: <0.0006 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
HEPTACHLOR EPOXIDE Naramata: 0.010; Cawston: 0.007; 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
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
HEXACHLOROBENZENE Naramata: 0.001; Cawston: 0.001; Vaseaux: 0.002 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
ORGANOCHLORINES Conventional orchard: 3.6; organic: 3.6 Clutch size B Embryo Okanagan Valley Conventional: 13; organic: 4 NR TOX-REPRO - reproductive success Environmental contamination Toxicity Factor Datasets
ORGANOCHLORINES Conventional orchard: 0.59; organic: 0.57 Nest success B Embryo Okanagan Valley Conventional: 22; organic: 5 NR TOX-REPRO - reproductive success Environmental contamination Toxicity Factor Datasets
ORGANOCHLORINES Conventional orchard: 0.59; organic: 0.73 Hatching success B Embryo Okanagan Valley Conventional: 22; organic: 5 NR TOX-REPRO - reproductive success Environmental contamination Toxicity Factor Datasets
ORGANOCHLORINES Conventional orchard: 0.87; organic: 0.91 Fledging success B Embryo Okanagan Valley Conventional: 18; organic: 5 NR TOX-REPRO - reproductive success Environmental contamination Toxicity Factor Datasets
Citation:

Effects of azinphos-methyl on American robins breeding in fruit orchards.

Author(s)
Gill, H., Wilson, L.K., Cheng, K.M., Trudeau, S. and Elliott, J.E.
Issue
6
Volume
65
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Technique Type
AZINPHOS-METHYL (GUTHION) See Figure 2 Plasma cholinesterase activity NR Okanagan Valley 1.4 kg Guthion 50% sprayed 2-4/yr TOX-Non-Repro-Sublethal - cellular/biochemical effects Treatment of nest-containing trees Toxicity Factor Datasets
AZINPHOS-METHYL (GUTHION) See Figure 2 Brain cholinesterase activity NR Okanagan Valley 1.4 kg Guthion 50% sprayed 2-4/yr TOX-Non-Repro-Sublethal - cellular/biochemical effects Treatment of nest-containing trees Toxicity Factor Datasets
AZINPHOS-METHYL (GUTHION) Sprayed: 3.42; control: 3.15 eggs/clutch Clutch size B Embryo Okanagan Valley Sprayed: 38; control: 13 1.4 kg Guthion 50% sprayed 2-4/yr TOX-REPRO - reproductive success Treatment of nest-containing trees Toxicity Factor Datasets
AZINPHOS-METHYL (GUTHION) Sprayed: 90; 87.9 % Hatching rate B Embryo Okanagan Valley Sprayed: 38; control: 13 1.4 kg Guthion 50% sprayed 2-4/yr TOX-REPRO - reproductive success Treatment of nest-containing trees Toxicity Factor Datasets
AZINPHOS-METHYL (GUTHION) Sprayed: 3.08; control: 2.77 young hatched/nest Brood size B Hatchling Okanagan Valley Sprayed: 38; control: 13 1.4 kg Guthion 50% sprayed 2-4/yr TOX-REPRO - reproductive success Treatment of nest-containing trees Toxicity Factor Datasets
AZINPHOS-METHYL (GUTHION) Sprayed: 57.9; control: 61.5 % Fledging success B Hatchling Okanagan Valley Sprayed: 38; control: 13 1.4 kg Guthion 50% sprayed 2-4/yr TOX-REPRO - reproductive success Treatment of nest-containing trees Toxicity Factor Datasets
Citation:

An assessment of DDT and other chlorinated compounds and the reproductive success of American robins (Turdus migratorius) breeding in fruit orchards.

Author(s)
Gill, H., Wilson, L.K., Cheng, K.M. and Elliott, J.E.
Issue
1
Volume
12
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Technique Type
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 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
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
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 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
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 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
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 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
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 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
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 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
Download CSV

Comment

Please let us know if the information on this page is helpful for you. Enter your comment and leave your email address if you would like to receive a response. Thank you!
OEHHA is subject to the California Public Records Act and other laws that require the release of certain information upon request. If you provide comments, please be aware that your name, address and e-mail may be available to third parties. In addition, all public comments will be posted on our web site upon the close of the comment period.
OEHHA California Office of Environmental Health Hazard Assessment