Laboratory
American Kestrel (Falco sparverius)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
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 |
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 | 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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254, MIREX | no effect | sperm motility | Male | Adult | 5-10/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
PARAQUAT | 22% @ 10 mg/kg, 18% @ 25 mg/kg, 44% @ 60 mg/kg | percent mortality | Not Reported | Juvenile | 11/group | Toxicity Factor Datasets | Laboratory | |
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 |
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 | 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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254, 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 |
Mallard duck (Anas platyrhynchos)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CADMIUM CHLORIDE | increased @ 10, 50 ug/g diet | kidney Zn concentration versus controls | Male | Adult | 8 | Toxicity Factor Datasets | 32 weeks | Laboratory | |
CADMIUM CHLORIDE | no effect | BW versus controls | Male | Adult | 8 | Toxicity Factor Datasets | 32 weeks | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD ACETATE | increased | liver and kidney Pb concentrations versus controls | Male | Adult | 30 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DIELDRIN | no effect | egg production, eggshell thickness and fertility, compared to control | Both Male and Female | Adult | 5 trios (2F, 1M)/dose | Toxicity Factor Datasets | Laboratory | |
DIELDRIN | decrease | average % hatchability, compared to controls | Both Male and Female | Adult | 5 trios (2F, 1M)/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SELENIUM COMPOUNDS, SELENOMETHIONINE | no effect | egg fertility, egg weight, eggshell thickness, and mean interval between laying of eggs versus controls | Both Male and Female | Adult | 15 pairs/treatment group, 10 pairs/control group | Toxicity Factor Datasets | Laboratory | |
SELENIUM COMPOUNDS, SELENOMETHIONINE | reduced with seleno-L-methionine or seleno-D,L-methionine | hatchability versus controls | Both Male and Female | Both Adults and Juveniles | 15 pairs/treatment group, 10 pairs/control group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1242 | 8.9% decrease @ 150 ppm | eggshell thickness, compared to control | Female | Adult | 12 pairs/dose | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1242 | 105.0 (7.7 SE) mg Aroclor 1260/kg egg @ 150 ppm | PCB concentration in eggs (PCB resembled Aroclor 1260 profile most closely) | Female | Adult | 12 pairs/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 0.3 ug/g | 24-d NOAEL based on growth impairment | Not Reported | Juvenile | 10/dose | Toxicity Factor Datasets | 1 - 25 d | Laboratory | |
DIELDRIN | see citation | figures of tissue dieldrin concentrations at different exposure times and doses | Not Reported | Juvenile | 10/dose | Toxicity Factor Datasets | 1 - 25 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CRUDE OILS | no effect | clutch size | Female | Adult | 17 pairs/dose | Toxicity Factor Datasets | 10 mo | Laboratory | |
CRUDE OILS | decrease | % hatchability (53% @ 3ml/100g vs 71% in controls) | Female | Adult | 17 pairs/dose | Toxicity Factor Datasets | 10 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | no effect | behavior of offspring; latency in response to approach a maternal call and distance travelled from a frightening stimulus | Female | Adult | 4 adults/dose; 141-175 offspring/dose | Toxicity Factor Datasets | 10 mo | Laboratory | |
DDE (4,4'-) | 0.021 - 0.028 ppm wet wt @ 0 ppm; 5.8 (0.32 SE; range 4.28-7.23) ppm wet wt @ 3 ppm | mean and range of DDE egg concentrations | Female | Adult | 8 eggs/dose | Toxicity Factor Datasets | 10 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 200.7 (coeff. of variation 22.3%) | 5 day dietary LC50 | Not Reported | Juvenile | 8-10/dose | Toxicity Factor Datasets | 5 days | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
PARATHION | 9% @ 1 mg/L | brain acetylcholinesterase activity compared with controls | Not Reported | Juvenile | 6/dose | Toxicity Factor Datasets | 2 weeks old | Laboratory | |
FENTHION | 67% @ 2.2 mg/L | percent mortality | Not Reported | Juvenile | 6/dose | Toxicity Factor Datasets | 2 weeks old | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DDT (4,4'-) | decreased @ all doses | body weight gain by 8 days compared with controls | Both Male and Female | Juvenile | 10/dose | Toxicity Factor Datasets | 7 d | Laboratory | |
DDT (4,4'-) | 1550 ppm | 5 day dietary LC50 | Both Male and Female | Juvenile | 10/dose | Toxicity Factor Datasets | 7 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
MALATHION | 49.5 lb/acre | LC50, exposed on day 3 or 8 of incubation | Not Reported | Embryo | 30/group | Toxicity Factor Datasets | Day 3 or 8 of incubation | Laboratory | |
DIAZINON | 9.7 (day 3), 11.1 (day 8) lb/acre | LC50, exposed on day 3 or 8 of incubation | Not Reported | Embryo | 30/group | Toxicity Factor Datasets | Day 3 or 8 of incubation | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEPTOPHOS | 5/5 @ 260 ppm | incidence of ataxia | Both Male and Female | Juvenile | 3-5/group | Toxicity Factor Datasets | 14 d | Laboratory | |
LEPTOPHOS | 4/5 @ 260 ppm | incidence of CNS lesions | Both Male and Female | Juvenile | 3-5/group | Toxicity Factor Datasets | 14 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
CRUDE OILS | 53% increase | plasma triiodothryonine concentration | Not Reported | Adult | 5/dose | Toxicity Factor Datasets | Laboratory | |
CRUDE OILS | 56% increase | hepatic cytochrome P450 content | Not Reported | Adult | 5/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254, DDE (4,4'-) | see citation | figure of # eggs/female/wk over time | Female | Adult | 10/dose | Toxicity Factor Datasets | Laboratory | |
DDE (4,4'-) | 373 (95% CL; 152-574) ppm lipid basis @ 40 ppm diet | DDE residue concentrations in eggs | Female | Adult | 12 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CRUDE OILS | decrease @ 0.25 - 5% | distance retreated from a frightening stimulus; impaired avoidance behavior | Both Male and Female | Juvenile | 10/dose | Toxicity Factor Datasets | 0-6 d post-hatch | Laboratory | |
CRUDE OILS | increase @ 2.5 - 5% | incidence of liver hypertrophy and splenic atropy | Both Male and Female | Juvenile | 10/dose | Toxicity Factor Datasets | 0-8 wks post-hatch | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | increased | erythrocyte protoporphyrin concentrations versus controls | Male | Adult | 20/treatment group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | no effect | body weight and hematocrit versus controls | Male | Juvenile | 20/treatment group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD NITRATE | no effect (3 or 8 d) | open field behavior scores versus controls | Not Reported | Juvenile | 26-28/group | Toxicity Factor Datasets | 9 d | Laboratory | |
LEAD NITRATE | decreased @ 5 ppm (8 d exposure) | mean percentage weight gain versus controls | Not Reported | Juvenile | 26-28/group | Toxicity Factor Datasets | 9 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | no effect | incidence of lead poisoning tissue lesions versus controls | Both Male and Female | Adult | control=2 F, 4 M; treatment=6 M-F pairs/group | Toxicity Factor Datasets | 6 mos | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
FUEL OILS | decreased @ 2% emulsion, incubation day 8 exposure | embryo survival through day 18 of incubation versus controls | Not Reported | Embryo | 30 eggs/group | Toxicity Factor Datasets | 3 or 8 days of incubation (time of treatment) | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DICHLOROPHENOXY-ACETIC ACID (2,4-) | decreased @ 1500 mg/kg bw | post-dose eggshell thickness versus pre-dose thickness | Female | Adult | 5/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CADMIUM CHLORIDE | increased @ 200 ppm | incidence of testes alterations (atrophy, decreased spermatogenesis) versus controls | Male | Adult | 5 birds | Toxicity Factor Datasets | first year | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
ALUMINUM SULFATE | decreased @ 1000 ppm Al (LH, LL), 5000 ppm Al (NN) | body weight growth versus controls | Not Reported | Juvenile | 12-14/group | Toxicity Factor Datasets | 1 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
NICKEL SULFATE | increased @ 800, 1200 ppm | incidence of clinical signs and mortality | Both Male and Female | Juvenile | 36 birds/dose | Toxicity Factor Datasets | 14 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
SALINE WATER | increased @ 67,000 umhos/cm (100%), 35,000 umhos/cm (100%), 21,500 umhos/cm (78%), and 20,000 umhos/cm (60%) | mortality versus controls | Not Reported | Juvenile | 10 birds/group | Toxicity Factor Datasets | 2 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
METHYLMERCURY CHLORIDE | decreased | hatchability versus controls | Not Reported | Juvenile | 29 pairs | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
SELENOMETHIONINE | decreased @ 20, 40 ppm | hepatic protein concentrations versus controls | Not Reported | Juvenile | 40 birds/group | Toxicity Factor Datasets | day old | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CADMIUM CHLORIDE | decreased @ 450 ppm | liver aldolase activity, plasma triiodothyronine levels | Not Reported | Adult | 12 birds/group | Toxicity Factor Datasets | 1 yr | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BORIC ACID, SELENOMETHIONINE | decreased @ 15 ppm Se | body, liver, and spleen weight; tarsus length versus controls | Not Reported | Juvenile | 15 birds/group | Toxicity Factor Datasets | day old | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
SODIUM MONOFLUOROACETATE | 9.78 (6.31-15.2), 3.71 (2.50-5.48), 3.71, 4.81 (2.57-8.99) | LD50's determined at ages 36 hr, 7 d, 30 d, and 6 mos, respectively (95% CI in parenth.) | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 36 hr, 7 d, 30 d, or 6 mos | Laboratory | |
ENDOSULFAN | 34.4 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 6 mos | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CRUDE OILS | decreased @ 1, 5 uL/egg | bill length of both sexes | Both Male and Female | Hatchling | 65 eggs/group | Toxicity Factor Datasets | 3 days | Laboratory | |
CRUDE OILS | decreased to 65% @ 1 uL/egg); 9% @ 5 uL/egg | embryo survival to 18 days | Both Male and Female | Embryo | 65 eggs/group | Toxicity Factor Datasets | 3 days | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | no effect | nasal gland and kidney Na-K-ATPase activity, following exposure to 100% seawater | Both Male and Female | Juvenile | 4-5 | Toxicity Factor Datasets | 3-5 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CRUDE OILS | decrease @ 0.5, 1, 3% | plasma corticosterone concentration, compared to control | Male | Juvenile | Not Reported | Toxicity Factor Datasets | 18 wks | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
BORIC ACID | Liver; 3 ug/g @ 30 ppm, 17 ug/g @ 300 ppm, 51 ug/g @ 1000 ppm: Brain; 4 ug/g @ 30 ppm, 19 ug/g @ 300 ppm, 66 ug/g @ 1000 ppm | boron concentrations in ducklings 21 d of age (geometric mean; ug/g dry weight). Concentrations at other doses were not detected. | Both Male and Female | Juvenile | 10-13/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
FUEL OILS | decrease @ 5, 10, 20, 50 ul | 30-d % hatching success | Not Reported | Embryo | 50/dose | Toxicity Factor Datasets | 8d of incubation | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
TRIMETHYLTIN CHLORIDE | increase @ 5 ppm | cephalic tumor incidence | Not Reported | Juvenile | 5/dose | Toxicity Factor Datasets | 3-4 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
PHOSPHORUS (YELLOW OR WHITE) | 6.96 mg/kg bw (2.66-8.96 95% CI) | 24 hour median lethal dose | Female | Adult | 6 birds/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | decreased @ 20, 100, 250, 500 mg/kg bw | plasma triiodothyronine concentrations versus controls | Male | Adult | 6-12/dose | Toxicity Factor Datasets | 1-2 yr | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
EMAMECTIN BENZOATE | 570 ppm diet, 391-915 (95% CI) | dietary LC50 | Both Male and Female | Juvenile | 10/dose | Toxicity Factor Datasets | 10 days | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BORIC ACID, SELENOMETHIONINE | no effect | onset of egg laying, eggshell thickness, frequency of embryo deformities versus controls | Both Male and Female | Both Adults and Juveniles | 14 pairs/treatment | Toxicity Factor Datasets | 1 yr | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD COMPOUNDS | increased @ 414, 828 ug/g | occurrence of intranuclear inclusion bodies in kidneys versus controls | Male | Adult | 10/ Pb treatment; 20/control treatment | Toxicity Factor Datasets | approx. 5 mo | Laboratory | |
LEAD COMPOUNDS | increased @ 869 and 954 ug/g | incidence of renal tubular intranuclear inclusion bodies versus corn or complete diet controls | Male | Adult | 5/ Pb treatment;3/control treatments | Toxicity Factor Datasets | approx. 7 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | decreased @ 10 ppm Hg, 10 ppm Hg + 10 ppm Se | hatchability versus controls | Both Male and Female | Both Adults and Juveniles | 12/group | Toxicity Factor Datasets | 18 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BISMUTH COMPOUNDS, IRON COMPOUNDS | no effect | mortality versus controls | Both Male and Female | Adult | 20 males, 20 females per group | Toxicity Factor Datasets | 6-8 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | 213(27.1) ppm, kidney; 91(4.55) ppm, liver; 9.8(3.22) ppm, ovary; 3.49(0.61) ppm, testis | mean(SE) wet wt concentrations of Pb in Pb-dosed birds | Both Male and Female | Adult | 18 pairs/group (control, Fe, Bi); 6 pairs/Pb group | Toxicity Factor Datasets | 6-8 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CYANOFENPHOS | decreased @ 2.0, 4.0 mg/kg/d | bw versus controls | Both Male and Female | Juvenile | 10 | laboratory | Toxicity Factor Datasets | 1 week | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | increased @ 10, 30 ppm | liver DNA content versus controls | Male | Both Adults and Juveniles | 5-15 per group | Toxicity Factor Datasets | 75 days | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | one shot: 180.4 (18.1), female; 5.0 (0.6), male two shot: 183.4 (21.2), female; 15.9 (4.1), male |
mean (SE) lead residues in femur | Both Male and Female | Adult | 20 females, 10 males/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CHLORPYRIFOS | decreased | body weight compared to controls | Both Male and Female | Adult | 24 pairs/dose | Toxicity Factor Datasets | 7 and 11 months old | Laboratory |
Deer Mouse (Peromyscus maniculatus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIBENZ[A]ANTHRACENE (1,2,5,6-) | 0.048 mg/kg/d | ED50 for immunosuppression, measured as suppression of plaque forming cell response | Male | Juvenile | Not Reported | Toxicity Factor Datasets | 7 - 8 wk | Laboratory | |
DIBENZ[A]ANTHRACENE (1,2,5,6-) | 0.85 mg/kg/d | ED50 for ethoxyresorufin-O-dealkylase (EROD) activity | Male | Juvenile | Not Reported | Toxicity Factor Datasets | 7 - 8 wk | Laboratory |
Clapper Rail (Rallus longirostris)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDT (4,4'-) | 44.6 ppm | mean residue concentration in brains of birds that died | Female | Juvenile | 4 birds | Toxicity Factor Datasets | Laboratory |
Merriam's Kangaroo Rat (Dipodomys merriami)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
METHYLPARATHION | no effect | discrimination between seeds and beads | Both Male and Female | Adult | 22 animals | Toxicity Factor Datasets | Laboratory | |
METHYLPARATHION | 18-19 % decrease | brain cholinesterase activity, compared to control | Both Male and Female | Adult | 2 animals | Toxicity Factor Datasets | Laboratory |
Mourning Dove (Zenaida macroura)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | light lesions present | histological exam of acid-fast intranuclear inclusions of cells of kidney proximal convoluted tubules | Not Reported | Not Reported | 2 | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | 639.43 and 345.95 ug/g, dry wt | lead concentration in kidneys of treated birds | Not Reported | Not Reported | 2 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Lab |
---|---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | decreased at 40 ppm | courtship behavior score (intensity) | Both Male and Female | Adult | 8/group | Toxicity Factor Datasets | breeding | Laboratory | |
AROCLOR 1254 | decreased at 10, 40 ppm | number of pairs nesting | Both Male and Female | Adult | 8/group | Toxicity Factor Datasets | breeding | Laboratory |
Loggerhead Shrike (Lanius ludovicianus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | increased at 1 mg/kg | latency to formation of natural prey killing behaviors | Not Reported | Juvenile | 10-11/dose | collected in San Diego County, CA | Toxicity Factor Datasets | 1 day post-hatch (begin) | Laboratory |
DIELDRIN | increased at 1, 2, 4, 8 mg/kg/d | rate of mortality compared with controls | Not Reported | Juvenile | 10-11/dose | collected in San Diego County, CA | Toxicity Factor Datasets | 1 day post-hatch (begin) | Laboratory |
Coyote (Canis latrans)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
PENTACHLOROBENZENE | see citation | figures of feces and serum concentrations over time at the tested doses | Both Male and Female | Adult | 3/dose | Toxicity Factor Datasets | 2 - 12 yrs | Laboratory |
Pacific Treefrog (Pseudacris regilla formerly Hyla regilla)
Chemical | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|---|
NITRATE, SODIUM | 111.0 | LOAEL for body weight and length | mg NO3-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | Laboratory |
Double-crested Cormorant (Phalacrocorax auritus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | decreased @ 349 ug/kg egg | spleen weights in treated embryos versus controls | Not Reported | Embryo | 83-86 eggs/treatment | Lake Winnipegosis, Manitoba | Toxicity Factor Datasets | Laboratory |
Bullfrog (Lithobates catesbeianus formerly Rana catesbeiana)
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|
TRICLOPYR | increase at 2.4 and 4.8 mg/l | Not Reported | Tadpole | 10 animals/replicate; 3 replicates/dose | Toxicity Factor Datasets | 1-2 d after hatching | Laboratory |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|
SULFURIC ACID | significant increase at pH 3.5 and 4.0 | Not Reported | Tadpole | 120 animals/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 11.0 ug/l | NOAEL | Not Reported | Embryo | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | embryo-larvae, 11d | Laboratory | |
DIELDRIN | 12.3 ug/l | NOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 29 d | Laboratory |
Desert Kit Fox (Vulpes macrotis ssp. arsipus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
ZINC PHOSPHIDE | 93 mg/kg bw (95% CI; 62-140 mg/kg) | LD50 | Not Reported | Adult | 2 animals/dose | Toxicity Factor Datasets | Laboratory |