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Turdus migratorius (American robin)

Citation:

Monitoring exposure of passerines to acephate, dicrotophos, and malathion using cholinesterase reactivation.

Author(s)
Maul, J.D. and Farris, J.L.
Issue
4
Volume
73
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Technique Type
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
Citation:

Selenium levels in bird eggs and effects on avian reproduction.

Author(s)
Ratti, J.T., Moser, A.M., Garton, E.O. and Miller, R.
Issue
2
Volume
70
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
Citation:

Effects of insecticide use on breeding birds in Christmas tree plantations in Quebec.

Author(s)
Rondeau, G. and Desgranges, J.L.
Issue
5
Volume
4
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
Citation:

Chlordane poisoning of birds in New Jersey, USA.

Author(s)
Stansley, W. and Roscoe, D.E.
Issue
9
Volume
18
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
Citation:
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

Falco sparverius

Citation:

Differential habitat use by sexes of American kestrels wintering in northern California

Author(s)
Koplin, James R.
Pages
39-42
Year
Issue
2
Volume
7
Exposure Endpoint Type Endpoint Value Endpoint Description Error Units Sex Life Cycle Stage Location Sample Size Type
Population Density 115 average density +/- 25 95% CI individuals/100 mi Both Male and Female Both Adults and Juveniles agricultural lands 205 obs. Exposure Factor Datasets
Citation:

Longevity in a captive sparrow hawk

Author(s)
Kuyt, E.
Pages
197
Year
Volume
30
Exposure Endpoint Type Endpoint Value Units Sex Life Cycle Stage Sample Size Type
Longevity 12 yr Not Reported Adult 1 Exposure Factor Datasets
Citation:

Behavior and ecology of the American Kestrel in the Sierra Nevada of California

Author(s)
Balgooyen, Thomas G.
Year
Volume
103
Exposure Endpoint Type Endpoint Value Endpoint Description Range Units Sex Life Cycle Stage Location Sample Size Type
Body Weight - Mean body weight at hatch 10-12 g Both Male and Female Hatchling Sagehen Creek Field Station Not Reported Exposure Factor Datasets
Age at Fledging, Metamorphosis, Weaning 29-31 d Both Male and Female Fledgling Sagehen Creek Field Station Not Reported Exposure Factor Datasets
Clutch or Litter Size 4 average clutch size eggs/clutch Female Adult Sagehen Creek Field Station 42 Exposure Factor Datasets
Duration of Incubation or Gestation 29-31 d Both Male and Female Embryo Sagehen Creek Field Station Not Reported Exposure Factor Datasets
Home Range 109.4 average home range - breeding ha Both Male and Female Adult Sagehen Creek Field Station 32 Exposure Factor Datasets
Time of Mating/ Laying late May - June entire laying period Female Adult Sagehen Creek Field Station Not Reported Exposure Factor Datasets
Time of Molt May - September Both Male and Female Adult Sagehen Creek Field Station Not Reported Exposure Factor Datasets
Fledging or Weaning Rate 98 of chicks that hatched % Both Male and Female Fledgling Sagehen Creek Field Station 150 Exposure Factor Datasets
Growth Rate y = 8.89 + 7.33x growth rate from day 3-16 Male Nestling Sagehen Creek Field Station Not Reported Exposure Factor Datasets
Growth Rate y = 7.77 + 7.44x growth rate from day 3-16 Female Nestling Sagehen Creek Field Station Not Reported Exposure Factor Datasets
Hatching Success 89.3 % Both Male and Female Hatchling Sagehen Creek Field Station 168 Exposure Factor Datasets
Dietary Composition insects (31.7%), reptiles (26.0%), birds (16.6%), mammals (25.7%) percent of prey by prey weight Both Male and Female Adult Sagehen Creek Field Station Not Reported Exposure Factor Datasets
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