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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 |
---|---|---|---|---|---|---|---|---|---|---|
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 | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|
Dietary Composition | Acridid, adult Coleoptera, Tettigoniid, larval Lepidoptera, Hymenoptera, Other, Hemipteran, spider | percent of arthropod taxa in the diet, listed in order of decreasing frequency | Not Reported | Adult | Arapaho Prairie | 95 birds | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Territory Size | 12,406.8 | average territory size in mated birds | m^2 | Male | Adult | Boulder | 17 birds | Exposure Factor Datasets |
Territory Size | 3,228.1 | average territory size of unmated birds | m^2 | Male | Adult | Boulder | 7 birds | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|
Dietary Composition | mourning dove | item found in stomach analysis | Not Reported | Not Reported | New Mexico State Hwy 26 | 1 bird | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Population Density | range of mean breeding bird densities on three grassland-sagebrush sites (over two years) | 2.0-3.5 | territories/16 ha | Both Male and Female | Adult | Wasatch National Forest | 3 sites | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 101.5 | mean body weight | 88.3-114.0 | g | Male | Adult | 8 birds | Exposure Factor Datasets |
Body Weight - Mean | 75.9 | mean body weight | 74.1-79.6 | g | Female | Adult | 3 birds | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|
Dietary Composition | Sturnella sp., Colaptes, sparrows, Lepus californicus, Sigmodon hispidus, Sylvilagus sp., Felis domesticus | species observed to be scavenged by meadowlarks | Not Reported | Adult | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Population Density | 0 to 12 (+/-15) | mean nest densities in untilled corn or soybean fields | nests/100 ha | Both Male and Female | Adult | Adair County | 8-9 fields | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Population Density | 4 (+/-4) | mean nest densities in strip cover along fields | nests/100 ha | Both Male and Female | Adult | Adair County | 35 fields | Exposure Factor Datasets |
Exposure Endpoint Type | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|
Body Weight - Mean | 25.15-25.68 | g | Male | Both Adults and Juveniles | Mandarte island | 11-37 birds | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | range of clutch sizes | 3-4 | eggs | Female | Adult | Sierra National Forest | 6 nests | Exposure Factor Datasets |
Hatching Success | range of hatching success | 1-2 | eggs/nest | Not Reported | Hatchling | Sierra National Forest | 6 nests | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Time of Nesting | May-August | inclusive of pairing through departure from nesting territory | Both Male and Female | Adult | Sierra National Forest | 15 birds | Exposure Factor Datasets | ||
Territory Size | range of territory sizes during the breeding season | 650-4131 | m^2 | Both Male and Female | Adult | Sierra National Forest | 15 birds | Exposure Factor Datasets | |
Hatching Success | 75% | hatching success among total eggs laid | Both Male and Female | Hatchling | Sierra National Forest | 8 nests | Exposure Factor Datasets | ||
Fledging or Weaning Rate | 50% | proportion of nestlings known or believed to have fledged | Both Male and Female | Fledgling | Sierra National Forest | 8 nests | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 3.68 | mean first clutch size | 0.1 SE | 3-5 | eggs | Female | Adult | Toledo, Wooster, OH | 31 nests | Exposure Factor Datasets |
Clutch or Litter Size | 3.14 | mean clutch size in renests | 0.1 SE | 2-4 | eggs | Female | Adult | Toledo, Wooster, OH | 29 nests | Exposure Factor Datasets |
Duration of Incubation or Gestation | 13.3 | 0.1 SE | d | Both Male and Female | Embryo | Toledo, Wooster, OH | 28 nests | Exposure Factor Datasets | ||
Age at Fledging, Metamorphosis, Weaning | 12.3 | 0.1 SE | 11-14 | d | Both Male and Female | Fledgling | Toledo, Wooster, OH | 82 chicks | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|---|
Survival/ Mortality | mortality of young birds based on number of eggs/season; in relation to high tides | 2.8-18.2 | % | Not Reported | Chick | San Pablo Marsh | 349 eggs | Exposure Factor Datasets | ||
Time of Mating/ Laying | late Feb/Mar-June | Not Reported | San Pablo Marsh | Exposure Factor Datasets | ||||||
Clutch or Litter Size | 3.2 | seasonal mean | 0.6 SD | eggs | Not Reported | San Pablo Marsh | 157 nests | Exposure Factor Datasets |