Falconiformes
Peregrine Falcon (Falco peregrinus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Fledging or Weaning Rate | 1998: 1.4, 1999: 2.91, 2000: 2.54, 2001: 2.48, 2002: 2.48, 2003: 2.75 | Mean number fledglings/breeding pair | Mean number fledglings/breeding pair | Fledgling | 1998: 11, 1999: 12, 2000: 13, 2001: 22, 2002: 29, 2003: 34 | Biskaia | Exposure Factor Datasets | SPAIN |
Fledging or Weaning Rate | 1998: 2, 1999: 2.91, 2000: 2.5, 2001: 2.89, 2002: 2.71, 2003: 3.21 | Mean number fledglings/successful breeding pair | Mean number fledglings/successful breeding pair | Fledgling | 1998: 11, 1999: 12, 2000: 13, 2001: 22, 2002: 29, 2003: 34 | Biskaia | Exposure Factor Datasets | SPAIN |
Fledging or Weaning Rate | 1998: 1.27, 1999: 2.67, 2000: 2.31, 2001: 2.36, 2002: 1.96, 2003: 2.41 | Mean number fledglings/territorial pair | Mean number fledglings/territorial pair | Fledgling | 1998: 11, 1999: 12, 2000: 13, 2001: 22, 2002: 29, 2003: 34 | Biskaia | Exposure Factor Datasets | SPAIN |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Dietary Composition | See citation Figure 4 | Identifiable prey | Adult | Urban: 10, nonurban: 11 nests | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation Figure 2 | Identifiable prey | Coastal: 30, urban: 31 | Coastal vs. urban populations | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|---|---|
Time of Mating/ Laying | Tritriva: June, Tsimanampetsotsa: July | Courtship initiation | Adult | 3 | Exposure Factor Datasets | Breeding | MADAGASCAR | ||
Time of Mating/ Laying | Tritriva: July, Tsimanampetsotsa: August | Egg laying | Adult | 3 nests | Exposure Factor Datasets | Breeding | MADAGASCAR | ||
Time of Fledging or Metamorphosis | 42 | Days posthatch | d | Fledgling | Tsimanampetsotsa | Exposure Factor Datasets | MADAGASCAR | ||
Clutch or Litter Size | 3-Feb | Number of eggs | Embryo | 2 nests | Tsimanampetsotsa | Exposure Factor Datasets | MADAGASCAR |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation Figure 2 | Seasonal changes in diet | 486 prey remains | Warsaw buildings | Exposure Factor Datasets | POLAND |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Population Density | 1.16 | Pairs/100 sq km | Pairs/100 sq km | B | Adult | 249 | Central-eastern Italian Alps | Exposure Factor Datasets | Breeding | ITALY |
Time of Mating/ Laying | 43170 | B | Adult | 249 | Central-eastern Italian Alps | Exposure Factor Datasets | Breeding | ITALY | ||
Dietary Composition | Turdus pilaris: 8.34, Turdus merula: 4.82, Columba livia: 12.27, Garrulus gladnarius: 6.87, Stumus vulgaris: 2.75, Corvus corone cornix: 19.50, other Columbidae: 12.48, Other Turdidae: 4.39, Other birds: 28.58 | Percent by mass from pellets/prey remains | % | B | Adult | 249 | Central-eastern Italian Alps | Exposure Factor Datasets | Breeding | ITALY |
Population Density | Review | Pairs/100 sq km | Pairs/100 sq km | B | Adult | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Turdus migratorius: 11, Leucophaeus pipixcan: 8, Sialia currucoides: 6, Phalaropus fulicarius: 6, Colaptes auratus: 5, Phalaropus tricolor: 5, other Scolophacidae spp.: 7, Icteridae spp.: 7, other picidae spp.: 6, Fringillidae spp.: 5, other birds: 32, other animals: 3 | Percent frequency of prey remains | % | B | Nestling | 9 eyries | Yellowstone National Park | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Units | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | Synthliboramphus antiquus, Streptopelia orientalis, S. qumizusume, Zoothera dauma, Swimhow's Storm-Petrel, Larus crassirostris, Japanese Murrelet, Pitta nympha, Otus sunia, Otus semitroques, Asio otus, Caprimulgus indicus | NA | 393 pellets | Exposure Factor Datasets | SOUTH KOREA (REPUBLIC OF KOREA)+M10 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Body Weight - Mean | See citation Table 6 | Egg metrics | Embryo | See citation | Exposure Factor Datasets | GERMANY |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Hatching Success | See citation Table 1 | Hatched eggs from succesful clutches | Number of eggs hatched | Embryo | 93 | NJ, PA, DE, MD, VA | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | See citation Table 1 | Chicks/breeding pair | Average number chicks/year | NR | Chick | 820 nests | Exposure Factor Datasets | SPAIN | |
Population Density | 9 | Breeding pairs/1,500 sq km | Breeding pairs/1,500 sq km | B | Adult | 820 nests | Exposure Factor Datasets | SPAIN | |
Dietary Composition | See citation Table 2 | Prey types | % prey mass | B | Adult | Exposure Factor Datasets | SPAIN |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
AROCLOR 1248, AROCLOR 1254, AROCLOR 1260, DDE (4,4'-), DDT (4,4'-), MERCURY COMPOUNDS | no effect | eggshell thickness compared to pre-1947 reference eggs | Female | Adult | 9 eggs | urban nest sites | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-) | 1.89 (1.27-2.43) -6.96 (3.28-13.37) ppm, wet wt | annual mean (range) concentrations in eggs | Female | Adult | 3-6 eggs/year | Amchitka Island | Toxicity Factor Datasets |
DDE (4,4'-) | 7.5% decrease | eggshell thickness compared to "pre-pesticide" reference eggs | Female | Adult | 3-6 eggs/year | Amchitka Island | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
MERCURY (elemental) | 6.90-29.50 ppm, dry wt (females) 12.10 ppm, dry wt (males) |
concentrations measured in primary and rectrix feathers | Both Male and Female | Adult | 20 females, 1 male | Northern Sweden | Toxicity Factor Datasets | SWEDEN |
MERCURY (elemental) | 2.79 (3.10) ppm, dry wt | mean (SD) concentration measured in feathers | Not Reported | Juvenile | 3 nests | Southern Sweden | Toxicity Factor Datasets | SWEDEN |
MERCURY (elemental) | 8.31(2.59) ppm, dry wt | mean (SD) concentration measured in feathers | Not Reported | Juvenile | 3 nests | Northern Sweden | Toxicity Factor Datasets | SWEDEN |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-) | review | concentrations of chemicals in eggs and diet associated with mortality and eggshell thinning (various raptor species) | Not Reported | Adult | Not Reported | Toxicity Factor Datasets | Laboratory | |
DIELDRIN | review | concentrations in brain associated with mortality (various raptor species) | Not Reported | Not Reported | Not Reported | Toxicity Factor Datasets | Laboratory | |
DIELDRIN | review | concentrations in eggs associated with reduced productivity (various raptor species) | Not Reported | Not Reported | Not Reported | Toxicity Factor Datasets | Laboratory | |
POLYCHLORINATED BIPHENYLS | review | concentrations in brain associated with mortality (various raptor species) | Not Reported | Not Reported | Not Reported | Toxicity Factor Datasets | Laboratory | |
POLYCHLORINATED BIPHENYLS | review | concentrations in eggs associated with reduced reproduction (various raptor species) | Not Reported | Adult | Not Reported | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-) | 13.1% and 13.6% decreases in tundrius and anatum ssp. | eggshell thickness compared to pre-1947 reference eggs | Female | Adult | 21 and 34 eggs for tundrius and anatum ssp. | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | review | eggshell thickness compared to that of pre-1945 eggs | Female | Adult | Not Reported | Toxicity Factor Datasets | GLOBAL |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-) | 21.7% decrease (tundra population); 16.8% decrease (taiga population); 7.5% decrease (Aleutian population) | eggshell thickness compared to pre-1947 reference eggs | Female | Adult | 23 eggs (tundra pop.); 14 eggs (taiga pop.); 11 eggs (Aleutian pop.) | Colville River (tundra); Yukon River (taiga); Amchitka Island (Aleutian) | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DIELDRIN | review | mortality in conjunction with pesticide use and residues in birds | Not Reported | Adult | Not Reported | Toxicity Factor Datasets | CANADA, UNITED KINGDOM, USA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE | 0.9-7.2 (DDT); 10.4-41.8 (DDE); 0.9-3.4 (DDD); 0.3-2.0 (dieldrin); 0.2-1.2 (heptachlor epoxide) | range of concentrations in eggs (ppm, wet wt) | Female | Adult | 7 eggs | Peace, Slave, and Mackenzie Rivers | Toxicity Factor Datasets | CANADA | |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE | 37.3 (DDT), 284 (DDE), 39.5 (DDD), 3.3 (dieldrin), 4.4 (heptachlor epoxide) | mean residue concentrations in fat (ppm, wet wt) | Female | Adult | 9 birds | Peace, Slave, and Mackenzie Rivers | Toxicity Factor Datasets | nesting | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 16% | percent eggshell thinning compared to pre-1947 reference eggs | Female | Adult | 13 eggs | South Australia | Toxicity Factor Datasets | AUSTRALIA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-) | 7.4-8.3% | percent eggshell thinning compared with pre-1946 reference eggs | Female | Adult | 3-7 eggs/year | Amchitka | Toxicity Factor Datasets |
DDE (4,4'-) | 16.8-24.9% | percent eggshell thinning compared with pre-1946 reference eggs | Female | Adult | 3-11 eggs/year | Colville, Yukon, Tanana Rivers | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | eggshell thickness index = 1.888 - 0.281(log DDE) | linear regression of eggshell thickness index and DDE content of eggs | Female | Adult | 137 eggs | Tasmania, Victoria, South Australia | Toxicity Factor Datasets | AUSTRALIA |
American Kestrel (Falco sparverius)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Vertebrates (29.1 %) Arthropods (70.9 %) | Frequency determined by pellet analysis | Frequency, % | Fledgling | 19 fledglings | Parque Luro Reserve | Exposure Factor Datasets | ARGENTINA | |
Dietary Composition | Vertebrates (11.2 %) Arthropods (88.8 %) | Frequency determined by prey remains | Frequency, % | Fledgling | 19 fledglings | Parque Luro Reserve | Exposure Factor Datasets | ARGENTINA | |
Time of Mating/ Laying | Late October-late December | Adult | 6 nests | Parque Luro Reserve | Exposure Factor Datasets | ARGENTINA | |||
Clutch or Litter Size | 4.3 | eggs | Embryo | 6 nests | Parque Luro Reserve | Exposure Factor Datasets | ARGENTINA | 0.3 | |
Hatching Success | 0.73 | Embryo | 26 eggs | Parque Luro Reserve | Exposure Factor Datasets | ARGENTINA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | 48% decrease at 625 mg/kg bw 27% decrease at 125 mg/kg bw 12% decrease at 25 mg/kg bw |
red blood cell hemoglobin content | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | decrease at all doses (45-59%) | red blood cell delta aminolevulinic acid dehydratase | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | 30% decrease at 625 mg/kg bw 25% decrease at 125 mg/kg bw |
plasma creatine phosphokinase | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | decrease at 125, 625 mg/kg bw (47-57%) | brain delta aminolevulinic acid dehydratase activity | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | decrease at 125, 625 mg/kg bw (71-79%) | kidney delta aminolevulinic acid dehydratase activity | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory |
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 |
---|---|---|---|---|---|---|---|---|
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 |
---|---|---|---|---|---|---|---|---|
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 |
---|---|---|---|---|---|---|---|---|
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 | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
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 | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1262, POLYCHLORINATED DIBENZO-P-DIOXINS | increased @ 0.5, 5 ppm | in vitro microsomal breakdown of oestradiol | Both Male and Female | Adult | 4/group | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254, POLYCHLORINATED DIBENZO-P-DIOXINS | increased @ 5 ppm | amount of liver cytoplasmic RNA | Both Male and Female | Adult | 4/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
PARAQUAT | 86% of control @ 25 mg/kg, 74% of control @ 60 mg/kg | body weight by 10 days of dosing | Not Reported | Juvenile | 11/group | Toxicity Factor Datasets | Laboratory | |
PARAQUAT | 11% @ 25 mg/kg, 25% @ 60 mg/kg | percent increase over controls in brain to body weight ratio | Not Reported | Juvenile | 11/group | Toxicity Factor Datasets | Laboratory | |
PARAQUAT | 14% @ 25 mg/kg, 18% @ 60 mg/kg | percent increase over controls in liver to body weight ratio | Not Reported | Juvenile | 11/group | Toxicity Factor Datasets | Laboratory | |
PARAQUAT | 51% @ 60 mg/kg | percent increase over controls in kidney to body weight ratio | Not Reported | Juvenile | 11/group | Toxicity Factor Datasets | Laboratory | |
PARAQUAT | no effect | percent increase over controls in lung to body weight ratio | Not Reported | Juvenile | 11/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DICOFOL | decreased 5.45% (@ 5 mg/kg), 10.98% (@ 20 mg/kg) | eggshell thickness compared to controls | Female | Adult | 10/group | Toxicity Factor Datasets | Laboratory | |
DICOFOL | non-detectable (@ 5 mg/kg), 560 ng/g (@ 20 mg/kg) | mean concentration of metabolite dichlorobenzophenone in eggs | Female | Adult | 10/group | Toxicity Factor Datasets | Laboratory | |
DICOFOL | increased @ 5 and 20 mg/kg | incidence of abnormal embyronic gonads | Both Male and Female | Embryo | 10/group | Toxicity Factor Datasets | Laboratory | |
DICOFOL | increased @ 5 mg/kg | numbers of chicks or eggs lost (destroyed) by breeding male and female offspring of dicofol-treated females versus controls | Female | Adult | 10/group | Toxicity Factor Datasets | Laboratory | |
DICOFOL | no effect | eggshell thickness for breeding female offspring of dicofol-treated females versus controls | Female | Adult | 10/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | increased @ 2.3, 23, 233 ng/g | incidence of malformations or edema, and EROD activity versus controls | Not Reported | Hatchling | 24-26/treatment group | Toxicity Factor Datasets | hatchling | Laboratory | |
PCB 77 (3,3',4,4'-TETRACHLOROBIPHENYL) | reduced @ 100, 1000 ng/g | percent hatching success, percent pipped versus controls | Not Reported | Hatchling | 24-26/treatment group | Toxicity Factor Datasets | hatchling | Laboratory | |
PCB 77 (3,3',4,4'-TETRACHLOROBIPHENYL) | reduced @ 1000 ng/g | humerus length versus controls | Not Reported | Hatchling | 24-26/treatment group | Toxicity Factor Datasets | hatchling | Laboratory | |
PCB 77 (3,3',4,4'-TETRACHLOROBIPHENYL) | increased @ 100, 1000 ng/g | incidence of malformations or edema, and EROD activity versus controls | Not Reported | Hatchling | 24-26/treatment group | Toxicity Factor Datasets | hatchling | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SELENOMETHIONINE | reduced @ 12 ppm Se | ratio of # fertile eggs to total # eggs laid versus 6 ppm Se group | Both Male and Female | Adult | 15 pairs/treatment group; 10 control pairs | Toxicity Factor Datasets | Laboratory | |
SELENOMETHIONINE | no effect | incidence of embryo deformities versus controls | Both Male and Female | Adult | 15 pairs/treatment group; 10 control pairs | Toxicity Factor Datasets | Laboratory | |
SELENOMETHIONINE | no effect | chick mass and size at hatch, and chick survival to fledging versus controls | Both Male and Female | Adult, Juvenile | 15 pairs/treatment group; 10 control pairs | 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 |
---|---|---|---|---|---|---|---|---|
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 |
---|---|---|---|---|---|---|---|---|
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 | 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 |
Chemical | Endpoint Value | Location | Type |
---|---|---|---|
POLYCHLORINATED BIPHENYLS | review | Toxicity Factor Datasets |
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 |
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 |
---|---|---|---|---|---|---|---|
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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
CYANIDE, SODIUM | 4.0 mg/kg bw | LD50 | 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 |
---|---|---|---|---|---|---|---|---|
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 |
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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1248 | 18.5 ug/g (5.1SD), PCBs; 0.10 ug/g (0.03 SD), dieldrin;1.02 ug/g (0.39 SD), DDE @ 3.0 ug/g | mean carcass concentrations, wet wt | Both Male and Female | Adult | 8 pairs/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 weight (as percent of body weight) versus controls | Female | Adult | 4/treatment group | Toxicity Factor Datasets | Laboratory |