American Kestrel (Falco sparverius)
American Kestrel (Falco sparverius)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DICOFOL | increased @ 5 mg/kg bw | incidence of abnormal gonads in male offspring of dicofol-treated females versus controls | Male | Adult | 10/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254, PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL), PCB 153 (2,2',4,4',5,5'-HEXACHLOROBIPHENYL), PCB 77 (3,3',4,4'-TETRACHLOROBIPHENYL) | increased with PCB 77 | liver ethoxyresorufin-O-deethylase activity versus controls | Female | Adult | 4/treatment group | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254, PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL), PCB 153 (2,2',4,4',5,5'-HEXACHLOROBIPHENYL), PCB 77 (3,3',4,4'-TETRACHLOROBIPHENYL) | decreased with PCB 153 | liver ethoxyresorufin-O-deethylase activity versus controls | Female | Adult | 4/treatment group | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254, PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL), PCB 153 (2,2',4,4',5,5'-HEXACHLOROBIPHENYL), PCB 77 (3,3',4,4'-TETRACHLOROBIPHENYL) | increased with PCB 126 | liver ethoxyresorufin-O-deethylase activity versus controls | Female | Adult | 4/treatment group | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | increased after 4 or 12 weeks | aminopyrine N-demethylase and aldrin epoxidase activities versus controls | Female | Adult | 4/treatment group | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | decreased after 4 weeks | liver ethoxyresorufin-O-deethylase activity versus controls | Female | Adult | 4/treatment group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | 40% at 625 mg/kg bw | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory | ||
LEAD (elemental) | decrease at 125, 625 mg/kg bw | body weight at end of dosing relative to control | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | decrease at 125, 625 mg/kg bw | growth rate relative to control | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | increase at all doses 1.4, 3.5, 5.5 ppm at 25, 125, 625 mg/kg bw, respectively |
liver lead concentration | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | increase at 125, 625 mg/kg bw 7.2, 15.5 ppm at 125, 625 mg/kg bw, respectively |
kidney lead concentrations | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
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'-), 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 |
---|---|---|---|---|---|---|---|---|
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 |
---|---|---|---|---|---|---|---|
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 | 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) | 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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1248 | 5.60 ug/g (1.15 SD), PCBs; 0.15 ug/g (0.05 SD), dieldrin; 0.15 ug/g (0.07 SD), DDE @ 3.0 ug/g | mean egg concentrations, wet wt | Female | Adult | 8 pairs/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | increased | occurence of wild birds dying diagnosed with organochlorine poisoning | Both Male and Female | Both Adults and Juveniles | 5 kestrels | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DICOFOL | increased | incidence of abnormal behavior in adult offspring of treated females | Both Male and Female | Adult | 10 pairs/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 | Lab |
---|---|---|---|---|---|---|---|---|
CRUDE OILS | decreased @ 3.0% | body weight | Both Male and Female | Juvenile | 16/group | Toxicity Factor Datasets | Laboratory | |
CRUDE OILS | increased @ 3.0% | food consumption | Both Male and Female | Juvenile | 16/group | Toxicity Factor Datasets | Laboratory | |
CRUDE OILS | decreased @ 3.0% | hemoglobin | Both Male and Female | Juvenile | 16/group | Toxicity Factor Datasets | Laboratory | |
CRUDE OILS | no effect | various hematological measurements (packed cell volume, erythrocyte counts, plasma uric acid, plasma alanine aminotransferase) | Both Male and Female | Juvenile | 16/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Location | Type |
---|---|---|---|
POLYCHLORINATED BIPHENYLS | review | Toxicity Factor Datasets | |
POLYCHLORINATED BIPHENYLS | review | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | decreased @ 250, 1000 ng/g bw | body and organ growth versus controls | Not Reported | Nestling | 9-11/group | Toxicity Factor Datasets | Day 1-Day 10 | Laboratory | |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | increased @ 50,250,1000 ng/g bw | incidence and severity of lesions in liver, spleen, bursa, thyroid versus controls | Not Reported | Nestling | 9-11/group | Toxicity Factor Datasets | Day 1-Day 10 | Laboratory | |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | increased | plasma enzyme activities indicative of hepatotoxicity versus controls | Not Reported | Nestling | 9-11/group | Toxicity Factor Datasets | Day 1-Day 10 | Laboratory | |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | no effect | hematocrit and hemoglobin values versus controls | Not Reported | Nestling | 9-11/group | Toxicity Factor Datasets | Day 1-Day 10 | Laboratory | |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | increased @ 50,250,1000 ng/g bw | hepatic monooxygenase activities versus controls | Not Reported | Nestling | 9-11/group | Toxicity Factor Datasets | Day 1-Day 10 | Laboratory | |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | in ng/g, wet wt: 156 (@ 50 ng/g), 380 (@ 250 ng/g), 1098 (@1000 ng/g) | concentration in liver | Not Reported | Nestling | 9-11/group | Toxicity Factor Datasets | Day 1-Day 10 | 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 |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | 21.5-22.6% decrease @ 33 ppm | sperm concentration | Male | Adult | 10/group | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | no effect | sperm motility | Male | Adult | 10/group | Toxicity Factor Datasets | Laboratory | |
MIREX | 40.3% decrease @ 8 ppm | sperm concentration | Male | Adult | 5-10/group | Toxicity Factor Datasets | Laboratory | |
MIREX | no effect | sperm motility | Male | Adult | 5-10/group | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254, MIREX | 73.3% increase @ 8ppm mirex + 33 ppm Aroclor | semen volume | Male | Adult | 5-10/group | Toxicity Factor Datasets | Laboratory |
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 |
---|---|---|---|---|---|---|---|---|
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 | Lab |
---|---|---|---|---|---|---|---|---|
FENTHION | increased @ all doses | mortality versus controls | Both Male and Female | Adult | 8 | Toxicity Factor Datasets | Laboratory | |
CARBOFURAN | increased at 63.4, 126.8, 253.6 ppm | mortality versus controls | Both Male and Female | Adult | 8 | Toxicity Factor Datasets | Laboratory | |
FENTHION | decreased to 10% of control levels | brain cholinesterase activity of birds that died | Both Male and Female | Adult | 8 | Toxicity Factor Datasets | Laboratory | |
CARBOFURAN | decreased to 35% of controls | brain cholinesterase activity in birds that died | Both Male and Female | Adult | 8 | Toxicity Factor Datasets | Laboratory |
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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SELENOMETHIONINE | blood Se concentration = 1.307 + 0.852(diet Se concentration) | relation between Se concentrations in blood (dry wt) and diet (dry wt) | Male | Adult | 40 birds | Toxicity Factor Datasets | Laboratory | |
SELENOMETHIONINE | egg Se concentration = 1.307 + 0.852(diet Se concentration) | relation between Se concentrations in egg (dry wt) and diet (dry wt) | Female | Adult | 53 eggs | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | decrease at 10, 50 ppm | mean blood delta aminolevulinic acid dehydratase | Both Male and Female | Adult | 16 pairs/dose | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | no effect | mean packed cell volume and red blood cell hemoglobin | Both Male and Female | Adult | 16 pairs/dose | 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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DICOFOL | 8.11 (fat), 0.28 (liver) ug/g @ 0.3 mg/kg bw/d | sum of geometric mean tissue concentrations (wet wt) of dicofol and metabolites (dichlorobenzophenone, mono-dechlorinated dicofol, dichlorobenzhydrol, DDE) | Female | Adult | 2-4/group | Toxicity Factor Datasets | Laboratory | |
DICOFOL | 82.36 (fat), 4.93 (liver), 1.15 (brain), 0.84 (oviduct) ug/g @ 3.0 mg/kg bw/d | sum of geometric mean tissue concentrations (wet wt) of dicofol and metabolites (dichlorobenzophenone, mono-dechlorinated dicofol, dichlorobenzhydrol, DDE) | Female | Adult | 2-4/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|
PARATHION | 25% at 4.6 ppm | Not Reported | Adult | 4/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 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Error |
---|---|---|---|---|---|---|---|---|---|---|
Territory Size | 31.6 | ha | Female | Adult | 5 | Hollister Basin (elev. 48-210 m) | Exposure Factor Datasets | San Benito, Santa Clara | 10.7 SD | |
Territory Size | 13.1 | ha | Male | Adult | 5 | Hollister Basin (elev. 48-210 m) | Exposure Factor Datasets | San Benito, Santa Clara | 2.0 SD | |
Dietary Composition | invertebrates (173.8), reptiles (23.0), birds (481.0), mammals (609.5) | amount of prey taken by prey weight | g | Female | Adult | 5 | Hollister Basin (elev. 48-210 m) | Exposure Factor Datasets | San Benito, Santa Clara | |
Dietary Composition | invertebrates (157.5), reptiles (0), birds (272.4), mammals (221.8) | amount of prey taken by prey weight | g | Male | Adult | 5 | Hollister Basin (elev. 48-210 m) | Exposure Factor Datasets | San Benito, Santa Clara |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 119.8 | mean body weight measured over 4 years | g | Female | Both Adults and Juveniles | 111 | coastal southern CA | Exposure Factor Datasets | 0.9 SE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Home Range | 1.5 | mean maximum diameter of winter home ranges | mi | Not Reported | Not Reported | 3 birds | agricultural lands | Exposure Factor Datasets |
Home Range | 1.4 | mean maximum diameter of breeding home ranges | mi | Not Reported | Not Reported | 4 birds | agricultural lands | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Survival/ Mortality | 12.6 | average length of survival of banded individuals | mo | Both Male and Female | Both Adults and Juveniles | 1,017 | throughout USA | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|---|
Hatching Success | 79 | mean hatchability measured over 4 years | % | Both Male and Female | Hatchling | 157 boxes | Great Basin (elev. 1260-2340 m) | Exposure Factor Datasets | Lassen |
Age at Fledging, Metamorphosis, Weaning | d | Both Male and Female | Fledgling | 112 | Great Basin (elev. 1260-2340 m) | Exposure Factor Datasets | Lassen | ||
Clutch or Litter Size | 4.3 | eggs/clutch | Female | Adult | 38 clutches | Great Basin (1260-2340 m) | Exposure Factor Datasets | Lassen | |
Fledging or Weaning Rate | 3.7 | fledged/successful nest | Both Male and Female | Fledgling | 30 nests | Great Basin (1260-2340 m) | Exposure Factor Datasets | Lassen |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 4.4 | eggs/clutch | Female | Adult | 10 nests | Jackson Hole | Exposure Factor Datasets | |
Hatching Success | 2 | percent of eggs that failed to hatch | % | Not Reported | Nestling | 10 nests | Jackson Hole | Exposure Factor Datasets |
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 | |
Time of Hatching or Parturition | Jun 20-Jun 22 | dates of earliest and latest hatching | Not Reported | Nestling | 11 nests | Jackson Hole | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Error |
---|---|---|---|---|---|---|---|---|---|---|
Population Density | 34 | average density | kestrels/100 mi | Both Male and Female | Both Adults and Juveniles | 135 obs. | coastal and coast range areas | Exposure Factor Datasets | Colusa, Humboldt, Lake, Mendocino, Yolo | +/- 11 95% CI |
Population Density | 115 | average density | individuals/100 mi | Both Male and Female | Both Adults and Juveniles | 205 obs. | agricultural lands | Exposure Factor Datasets | Colusa, Humboldt, Lake, Mendocino, Yolo | +/- 25 95% CI |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Lab |
---|---|---|---|---|---|---|---|---|---|---|
Duration of Incubation or Gestation | 28.4 | mean incubation period in captivity | d | Both Male and Female | Embryo | 5 | Exposure Factor Datasets | Breeding | Laboratory | |
Clutch or Litter Size | 3.66 | mean clutch size in captivity | eggs | Female | Adult | 5 | Exposure Factor Datasets | Breeding | Laboratory |
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 | California Counties | Condition |
---|---|---|---|---|---|---|---|---|---|---|
Population Density | 23 | individuals per 96 km2 | Both Male and Female | Adult | 23 | agricultural lands (lat, 38 deg 32'N; long., 121 deg 47'W) | Exposure Factor Datasets | Yolo | Breeding | |
Foraging Distance | distance foraged from nest | km | Female | Adult | 4 | agricultural lands (lat, 38 deg 32'N; long., 121 deg 47'W) | Exposure Factor Datasets | Yolo | Breeding |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
Longevity | 12 | yr | Not Reported | Adult | 1 | 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 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|---|
Surface Area | 7.15 x 10E-3 | dorsal surface area | m^2 | Not Reported | Adult | Not Reported | Exposure Factor Datasets | Laboratory |
Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | body weight at hatch | g | Both Male and Female | Hatchling | Not Reported | 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 | Condition |
---|---|---|---|---|---|---|---|---|---|
Territory Size | 1.4 | average diameter of territories | km | Both Male and Female | Adult | 16 | southcentral area, agricultural lands | Exposure Factor Datasets | wintering |