American Kestrel (Falco sparverius)
American Kestrel (Falco sparverius)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| LEAD COMPOUNDS | 7.84 ppm femur at 120 ppm; 16.60 ppm femur at 212 ppm; 18.44 ppm femur at 448 ppm | mean lead concentration in femur | Both Male and Female | Adult | 8-14/group | Toxicity Factor Datasets | 1-2 yr | Laboratory | |
| LEAD COMPOUNDS | no effect | packed cell volume, hemoglogin concentration, erythrocyte counts | Both Male and Female | Adult | 8-14/group | Toxicity Factor Datasets | 1-2 yr | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DIMETHYLMERCURY | no effect | eggshell thickness | Female | Adult | Not Reported | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DDE (4,4'-) | decrease | eggshell thickness | Female | Adult | 8/group | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-) | decrease | Calcium ATPase activity of shell gland | Female | Adult | 8/group | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-) | decrease | carbonic anhydrase activity of shell gland | Female | Adult | 8/group | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-) | no effect | calcium concentration in blood | Female | Adult | 8/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DDE (4,4'-) | decrease at all doses (15.1-29.2%) | eggshell thickness | Female | Adult | 2-5 pairs/dose | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|
| DDE (4,4'-) | 5.53 mg/kg egg (wet wt) | mean DDE concentration in eggs (pooled analyses) | Both Male and Female | Embryo | 10 eggs | N. Niagra Peninsula, Ontario | Toxicity Factor Datasets | CANADA |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| LEAD (elemental) | no effect | eggshell thickness | Female | Adult | 16 pairs/group | Toxicity Factor Datasets | Laboratory | |
| LEAD (elemental) | no effect | lead concentration in eggshell | Female | Adult | 16 pairs/group | Toxicity Factor Datasets | Laboratory | |
| LEAD (elemental) | 62.0 ppm tibia, 13.5 ppm humeri at 50 ppm | lead concentrations in bones | Female | Adult | 16 pairs/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| METHYLPARATHION | increased at 2, 3 mg/kg bw | abnormal posture, ataxia, paresis | Both Male and Female | Adult | 5/dose | Toxicity Factor Datasets | Laboratory | |
| METHYLPARATHION | increase at 3 mg/kg bw | mortality rate 2 hr post-dose | Both Male and Female | Adult | 5/dose | Toxicity Factor Datasets | Laboratory | |
| METHYLPARATHION | decrease at 2, 3 mg/kg bw | cloacal temperature | Both Male and Female | Adult | 5/dose | Toxicity Factor Datasets | Laboratory | |
| METHYLPARATHION | decrease at 2, 3 mg/kg bw | plasma cholinesterase activity 2 hr post-dose | Both Male and Female | Adult | 5/dose | Toxicity Factor Datasets | Laboratory | |
| METHYLPARATHION | decrease at 1, 2, 3 mg/kg bw | brain acetylcholinesterase activity 10 hr post-dose | Both Male and Female | Adult | 5/dose | Toxicity Factor Datasets | Laboratory | |
| METHYLPARATHION | increased at 2, 3 mg/kg bw | plasma glucose concentrations | Both Male and Female | Adult | 5/dose | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| ACEPHATE, DDE (4,4'-) | no effect | prey capturing behavior | Not Reported | Adult | 5-6/group | Toxicity Factor Datasets | Laboratory | |
| ACEPHATE, DDE (4,4'-) | decrease for both treatments | median serum cholinesterase activity 24 hr post-dose | Not Reported | Adult | 5-6/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS | 1.05 (0.05 SE) ppm (wet wt) | lead concentration in liver | Female | Juvenile | 2 | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS | 0.70 (0.20 SE) ppm (wet wt) | lead concentration in tibia | Female | Juvenile | 2 | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS | 232 (9 SE) ppm (wet wt) | DDE concentration in carcass | Female | Juvenile | 2 | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS | 10.4 (0.6 SE) ppm (wet wt) | DDE concentration in brain | Female | Juvenile | 2 | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS | decreased | bw (versus pre-study bw) | Female | Juvenile | 2 | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| LEAD (elemental) | 0.367 (0.129 SE) ppm at 49 mg/d | mean lead concentration (wet wt) in liver | Female | Adult | 3/group | Toxicity Factor Datasets | Laboratory | |
| LEAD (elemental) | 28.70 (2.6 SE) ppm at 49 mg/d | mean lead concentration (wet wt) in bone | Female | Adult | 3/group | Toxicity Factor Datasets | Laboratory | |
| LEAD COMPOUNDS | 0.357 (0.012 SE) ppm at 29.3 ppm | mean lead concentration (wet wt) in liver | Female | Adult | 3/group | Toxicity Factor Datasets | Laboratory | |
| LEAD COMPOUNDS | 7.63 (1.03 SE) ppm at 29.3 ppm | mean lead concentration (wet wt) in bone | Female | Adult | 3/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| CARBOFURAN | 3 | number of dead kestrels found on treated fields | Not Reported | Not Reported | 44 fields | Toxicity Factor Datasets | |
| CARBOFURAN | 1.7-7.4 ppm (wet wt) | carcass residues of kestrels found dead | Not Reported | Not Reported | 3 birds | Toxicity Factor Datasets |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DDE (4,4'-) | no effect | variance in kestrel response time to prey stimulus | Not Reported | Adult | 6 | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-) | 1.37 (0.10 SE) mg/kg | mean DDE concentration in blood (wet wt) | Not Reported | Adult | 6 | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DDE (4,4'-) | decrease at 10 ppm | mean eggshell thickness | Female | Adult | 8-10 | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-) | 0.71 (0.05 SE) ppm at 0 ppm, 32.4 (2.78 SE) ppm at 10 ppm |
mean residues in eggs | Female | Embryo | 9-10 | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DDE (4,4'-) | decrease at 3 ppm | mean eggshell thickness | Female | Adult | 18 | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| EPN | 4.0 mg/kg bw (3.1-5.1 95% CI) | LD50 | Both Male and Female | Adult | 5/group | Toxicity Factor Datasets | Laboratory | |
| FENTHION | 1.4 mg/kg bw | LD50 | Both Male and Female | Adult | 5/group | Toxicity Factor Datasets | Laboratory | |
| CARBOFURAN | 0.6 mg/kg bw (0.5-1.0 95% CI) | LD50 | Both Male and Female | Adult | 5/group | Toxicity Factor Datasets | Laboratory | |
| MONOCROTOPHOS | 1.5 mg/kg bw | LD50 | Both Male and Female | Adult | 5/group | Toxicity Factor Datasets | Laboratory | |
| EPN | 68% (10.0 SD) | mean brain cholinesterase depression (relative to control) in birds that died in 8 hrs post-dose | Both Male and Female | Adult | 12 | Toxicity Factor Datasets | Laboratory | |
| FENTHION | 88% (2.7 SD) | mean brain cholinesterase depression (relative to control) in birds that died in 8 hrs post-dose | Both Male and Female | Adult | 8 | Toxicity Factor Datasets | Laboratory | |
| CARBOFURAN | 83% (4.3 SD) | mean brain cholinesterase depression (relative to control) in birds that died in 8 hrs post-dose | Both Male and Female | Adult | 12 | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DDE (4,4'-) | 984.1-1438.6 ppm (dry wt) | brain residues in birds that died | Male | Adult | 2 | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-) | 232.9 ppm (dry wt) | mean brain residues in birds that survived | Male | Adult | 11 | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-) | 507-877.1 ppm (dry wt) | liver residues in birds that died | Male | Adult | 2 | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-) | 88.1 ppm (dry wt) | mean liver residues in birds that survived | Male | Adult | 11 | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| DDE (4,4'-) | 10% decrease | eggshell thickness change relative to control | Female | Adult | 34 eggs | Cayuga Lake Basin | Toxicity Factor Datasets |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| FENTHION | 100% | Male | Adult | 14 | Toxicity Factor Datasets | Laboratory | ||
| FENTHION | 77.9-92% | range of brain acetylcholinesterase inhibition (relative to control) in birds that died | Male | Adult | 14 | Toxicity Factor Datasets | Laboratory | |
| FENTHION | 96% | range of plasma cholinesterase inhibition (relative to control) in birds that died | Male | Adult | 14 | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| LEAD COMPOUNDS | 0.24 ug/g at study area, 0.087 ug/g at reference area |
mean lead concentration in blood (wet wt) | Both Male and Female | Nestling | 30 (study area) 22 (reference) |
Coeur D'Alene River | Toxicity Factor Datasets |
| LEAD COMPOUNDS | 0.46 ug/g at study area 0.25 ug/g at reference area |
mean lead concentration in blood (wet wt) | Both Male and Female | Adult | 3 (study area) 6 (reference) |
Coeur D'Alene River | Toxicity Factor Datasets |
| LEAD COMPOUNDS | decreased | red blood cell delta aminolevulinic acid dehydratase activity (relative to control) | Both Male and Female | Both Adults and Juveniles | 33 | Coeur D'Alene River | Toxicity Factor Datasets |
| LEAD COMPOUNDS | decreased | hematocrit | Both Male and Female | Juvenile | 30 | Coeur D'Alene River | Toxicity Factor Datasets |
| LEAD COMPOUNDS | decreased | hemoglobin (relative to control) | Both Male and Female | Both Adults and Juveniles | 33 | Coeur D'Alene River | Toxicity Factor Datasets |
| LEAD COMPOUNDS | 0.23 ug/g (wet wt) | mean lead concentration in liver | Both Male and Female | Juvenile | 30 | Coeur D'Alene River | Toxicity Factor Datasets |
| LEAD COMPOUNDS | no effect | number of young produced | Both Male and Female | Adult | 20 nests | Coeur D'Alene River | Toxicity Factor Datasets |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| DDT (Technical Grade Mixture) | 6.42 ppm | mean DDT concentration in eggs 0-0.8 mi from sprayed area | Both Male and Female | Embryo | 21 eggs | La Grande-Enterprise (OR), Potlatch (ID) | Toxicity Factor Datasets |
| DDT (Technical Grade Mixture) | 10.4% decrease | change in mean eggshell thickness (relative to control) 0-0.8 miles from sprayed area | Female | Adult | 21 eggs | La Grande-Enterprise (OR), Potlatch (ID) | Toxicity Factor Datasets |
| DDT (Technical Grade Mixture) | no effect | mean productivity (young produced) | Both Male and Female | Adult | 21 eggs | La Grande-Enterprise (OR), Potlatch (ID) | Toxicity Factor Datasets |
| DDT (Technical Grade Mixture) | 0.78 ppm | mean DDT concentration in plasma of birds sampled 0-1.5 mi from sprayed area | Both Male and Female | Adult | 23 birds | La Grande-Enterprise (OR), Potlatch (ID) | Toxicity Factor Datasets |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| FLUORIDE, SODIUM | 247.0 +/- 103.1 ppm @ 0 ppm; 6137.9 +/- 823.8 ppm @ 1120 ppm; 10,272.6 +/- 865.8 ppm @ 2240 ppm | mean fluoride content in the diaphyses of femurae | Both Male and Female | Juvenile | 9-10/group | Toxicity Factor Datasets | 7 d | Laboratory | |
| FLUORIDE, SODIUM | no effect | growth of body weight and skeletal components (skull, bill, tarsus, antebrachium, and manus) | Both Male and Female | Juvenile | 9-10/group | Toxicity Factor Datasets | 7 d | Laboratory | |
| FLUORIDE, SODIUM | increased at 1120, 2240 ppm | % bone ash | Both Male and Female | Juvenile | 9-10/group | Toxicity Factor Datasets | 7 d | Laboratory | |
| FLUORIDE, SODIUM | decreased at 2240 ppm | bonebreaking strength | Both Male and Female | Juvenile | 9-10/group | Toxicity Factor Datasets | 7 d | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| PCB 105 (2,3,3',4,4'-PENTACHLOROBIPHENYL), PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL), PCB 153 (2,2',4,4',5,5'-HEXACHLOROBIPHENYL) | increased with PCB 153 | aminopyrine N-demethylase and aldrin epoxidase activities in liver | Female | Adult | 5-6/group | Toxicity Factor Datasets | 1 yr | Laboratory | |
| PCB 105 (2,3,3',4,4'-PENTACHLOROBIPHENYL), PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL), PCB 153 (2,2',4,4',5,5'-HEXACHLOROBIPHENYL) | increased with PCB 105 | aminopyrine N-demethylase activity in liver | Female | Adult | 5-6/group | Toxicity Factor Datasets | 1 yr | Laboratory | |
| PCB 105 (2,3,3',4,4'-PENTACHLOROBIPHENYL), PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL), PCB 153 (2,2',4,4',5,5'-HEXACHLOROBIPHENYL) | increased with PCB 126 | 7-ethoxyresorufin O-deethylase and aldrin epoxidase activities in liver | Female | Adult | 5-6/group | Toxicity Factor Datasets | 1 yr | Laboratory | |
| PCB 105 (2,3,3',4,4'-PENTACHLOROBIPHENYL), PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL), PCB 153 (2,2',4,4',5,5'-HEXACHLOROBIPHENYL) | no effect | hepatic porphyrin levels | Female | Adult | 5-6/group | Toxicity Factor Datasets | 1 yr | Laboratory | |
| PCB 105 (2,3,3',4,4'-PENTACHLOROBIPHENYL), PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL), PCB 153 (2,2',4,4',5,5'-HEXACHLOROBIPHENYL) | no effect | liver weight | Female | Adult | 5-6/group | Toxicity Factor Datasets | 1 yr | Laboratory | |
| PCB 105 (2,3,3',4,4'-PENTACHLOROBIPHENYL), PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL), PCB 153 (2,2',4,4',5,5'-HEXACHLOROBIPHENYL) | 2.4 (control), 119.0 (PCB 153), 182.0 (PCB 105), 3.3 (PCB 126) mg/kg, wet weight | PCB concentrations in pooled adipose tissue | Female | Adult | 5-6/group | Toxicity Factor Datasets | 1 yr | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
|---|---|---|---|---|---|---|---|---|---|
| Clutch or Litter Size | 4 | average clutch size | eggs/clutch | Female | Adult | 42 | Sagehen Creek Field Station | Exposure Factor Datasets | Nevada, Sierra |
| Duration of Incubation or Gestation | d | Both Male and Female | Embryo | Not Reported | Sagehen Creek Field Station | Exposure Factor Datasets | Nevada, Sierra | ||
| Growth Rate | y = 7.77 + 7.44x | growth rate from day 3-16 | Female | Nestling | Not Reported | Sagehen Creek Field Station | Exposure Factor Datasets | Nevada, Sierra | |
| Hatching Success | 89.3 | % | Both Male and Female | Hatchling | 168 | Sagehen Creek Field Station | Exposure Factor Datasets | Nevada, Sierra |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|---|
| Age at Fledging, Metamorphosis, Weaning | 28.4 | mean nestling period | d | Both Male and Female | Fledgling | 29 chicks | Exposure Factor Datasets | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|---|
| Body Weight - Mean | 102.5 | g | Male | Adult | 88 | throughout USA | Exposure Factor Datasets | USA | |
| Time of Molt | July-October/November | period of molt | Both Male and Female | Adult | Not Reported | throughout USA | Exposure Factor Datasets | USA | |
| Survival/ Mortality | 57 | average annual mortality of banded individuals (over 6 years) | % | Both Male and Female | Both Adults and Juveniles | Not Reported | throughout USA | Exposure Factor Datasets | USA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|---|
| Food Ingestion Rate | 0.42 | mean caloric consumption per g body weight per day (wet weight basis) | kcal/g/day | Male | Adult | 2 | Exposure Factor Datasets | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
|---|---|---|---|---|---|---|---|---|
| Time of Migration or Dispersal | August (begin), October (peak), November (end) | time period of fall migration | Both Male and Female | Not Reported | 276 | Pt. Diablo, Marin Headlands | Exposure Factor Datasets | Marin |
| Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| Metabolic Rate | combined day and night oxygen consumption over one 24 hr period | ml oxygen/g/hr | Both Male and Female | Adult | 3 birds | Exposure Factor Datasets | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Error |
|---|---|---|---|---|---|---|---|---|---|---|
| Body Fat (total or %) | 6.01 | percent body fat calculated from total body electrical conductivity | % | Male | Adult | 12 | Cape May | Exposure Factor Datasets | migrating | 1.92 SE |
| Body Fat (total or %) | 8.51 | percent body fat calculated from total body electrical conductivity | % | Female | Adult | 13 | Cape May | Exposure Factor Datasets | migrating | 2.00 SE |
| Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition |
|---|---|---|---|---|---|---|---|---|
| Body Fat (total or %) | mean percent body fat as measured by fat extraction from April to September | % | Male | Adult | 14 | Cache county | Exposure Factor Datasets | premigratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error | Lab |
|---|---|---|---|---|---|---|---|---|---|---|
| Body Fat (total or %) | 2.46 | total body fat based on Soxhlet fat extraction | g | Both Male and Female | Adult | 21 | Exposure Factor Datasets | 0.25 SE | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
|---|---|---|---|---|---|---|---|---|
| Dietary Composition | insects (97%), isopod (5%), birds (27%), mammals (25%) | percent occurrence in sample pellets | Not Reported | Not Reported | Not Reported | agricultural lands | Exposure Factor Datasets | Tulare |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|---|
| Duration of Incubation or Gestation | 30.9 | incubation period | d | Both Male and Female | Embryo | 2 clutches (8 eggs) | Berks county | Exposure Factor Datasets |
| Survival/ Mortality | 78 | hatching success | % | Both Male and Female | Hatchling | 55 eggs (14 clutches) | Berks county | Exposure Factor Datasets |
| Clutch or Litter Size | 4.23 | eggs | Female | Adult | 13 clutches | Berks county | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
|---|---|---|---|---|---|---|---|---|---|---|
| Clutch or Litter Size | 4.59 | eggs/clutch | Female | Adult | 244 | Exposure Factor Datasets | 0.60 SD | |||
| Survival/ Mortality | 0.602 | mortality rate estimate for banded individuals | Both Male and Female | Both Adults and Juveniles | 118 | throughout USA and Canada | Exposure Factor Datasets | 0.035 SD | ||
| Survival/ Mortality | 0.465 | mortality rate of banded individuals, 1946-65 | Both Male and Female | Adult | 6,544 | throughout USA and Canada | Exposure Factor Datasets | CANADA, USA | 0.017 SD |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Lab |
|---|---|---|---|---|---|---|---|---|---|---|
| Time of Nesting | May 20 to Jul 20 | period from earliest egg laying date to date of latest brood departure | Both Male and Female | Adult | 11 nests | Jackson Hole | Exposure Factor Datasets | |||
| Territory Size | observed range of movement during nesting, based on observations of individual or pair movements | mi^2 | Not Reported | Adult | 11 birds | Jackson Hole | Exposure Factor Datasets | |||
| Dietary Composition | white-footed mice (6.0%), meadow mice (78.9%), shrews (1.3%), pocket gopher (1.0%), uinta ground squirrel (0.3%), sm-med sized birds (5.7%), insects (59.9%) | percent occurrence of prey items in pellets during nesting | % | Not Reported | Not Reported | 299 pellets from 8 nests | Jackson Hole | Exposure Factor Datasets | ||
| Food Ingestion Rate | averages of food amounts eaten per day | g | Both Male and Female | Not Reported | 3 birds | Exposure Factor Datasets | captive | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|---|
| Fledging or Weaning Rate | 49% | mean percent of successful nests per year | % | Both Male and Female | Adult | 259 nesting attempts | Berks and Lehigh counties | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|---|
| Clutch or Litter Size | 4.4 | mean clutch size (4 sample years) | eggs/clutch | Female | Adult | 7-23 nests/year | Lucas and Wayne Counties (40deg57'N, 93deg18'W) | Exposure Factor Datasets |