Birds
Snowy Egret (Egretta thula)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
MERCURY COMPOUNDS | 2002: 12.8, 2003: 15.2, 2004: 13.0 g | Liver weight | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
MERCURY COMPOUNDS | 2002: 20.45, 2003: 36.38 µg/g ww | Feather concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
DDD (4,4'-) | MS-90:0.0222, BI-82: 0.246, BI-89: 0.0180, BI-90: 0.0473, WM-89: 0.0168, WM-90: 0.0098, SW-91: 0.0683 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
METHYLMERCURY | Review, see citation Figure 2 | Egg concentration | Embryo | Not reported | Toxicity Factor Datasets | USA | ||
DDD (2,4'-) | 0.12 ppm ww | Egg concentration | Embryo | 4 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
METHYLMERCURY | 0.15 µg/g [0.05-0.31 (95% CI)] | Embryonic LD50 | Embryo | 63 | Patuxent Wildlife Research Center | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 423, reference: 422 g | Body weight | Both Adults and Juveniles | LCRS: 6, Reference: 5 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | Lahontan Reservoir: 3.55, Humboldt River: 3.59 g | Kidney weight | Not Reported | Nestling | 7 | Lahontan Reservoir: contaminated site; Humbodlt River: reference site | Toxicity Factor Datasets | USA |
MERCURY COMPOUNDS | 2002: 6.66, 2003: 8.50 µg/g ww | Feather concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
DDT (4,4'-) | MS-90: 0.0122, BI-89: 0.0282, BI-90: 0.0506, WM-89: 0.0185, WM-90: 0.0236, SW-91: 0.0572 µg/g ww | Egg concentration | Not Reported | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
METHYLMERCURY | Review, see ciation Figure 3 | Feather concentration | Not Reported | Not reported | Toxicity Factor Datasets | USA | ||
DDT (2,4'-) | 0.46 ppm ww | Egg concentration | Embryo | 6 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 1997: 0.60, 1998: 1.20 µg/g ww | Stomach concentration | Both Adults and Juveniles | 1997: 4, 1998: 6 | Lahontan Reservoir | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 13.73, reference: 12.44 g | Liver weight | Both Adults and Juveniles | LCRS: 6, Reference: 5 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 0.170, 2003: 0.646, 2004: 0.262 g | Spleen weight | Not Reported | Nestling | 2002: 2, 2003: 7, 2004: 5 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
PCB | 2.49 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Mallard Slough | Toxicity Factor Datasets | USA |
BORON COMPOUNDS | BI-89: 0.408, WM-89: 0.395, WM-91: 0.859, SW-91: 1.29 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DDE (2,4'-) | 4.8 ppm ww | Egg concentration | Embryo | 9 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
DIELDRIN | 0.02 ppm ww | Egg concentration | Embryo | 2 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
METHYLMERCURY | 1997: 0.53, 1998: 1.12 µg/g ww | Stomach concentration | Both Adults and Juveniles | 1997: 4, 1998: 6 | Lahontan Reservoir | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 4.78, reference: 4.56 g | Kidney weight | Both Adults and Juveniles | LCRS: 6, Reference: 5 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 0.170, 2003: 0.646, 2004: 0.626 g | Spleen weight | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
PCB | 1982: 3.32, 1989: 1.23, 1990: 5.38 µg/g ww | Egg concentration | Not Reported | Embryo | 1982: 10, 1989: 5, 1990: 5 | Bair Island | Toxicity Factor Datasets | USA |
BARIUM (elemental) | BI-89: 0.259, WM-89: 0.351, SW-91: 0.823 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DDD (2,4'-) | 0.16 ppm ww | Egg concentration | Embryo | 6 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
HEPTACHLOR EPOXIDE | 0.03 ppm ww | Egg concentration | Embryo | 1 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 1997: 0.31, 1998: 0.61 µg/g ww | Stomach concentration | Both Adults and Juveniles | 5 | Carson Lake | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 0.28, reference: 0.50 g | Spleen weight | Both Adults and Juveniles | LCRS: 6, Reference: 5 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 2.41, 2003: 2.04, 2004: 1.66 g | Brain weight | Not Reported | Nestling | 2002: 2, 2003: 7, 2004: 5 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
PCB | 1989: 2.19, 1990: 0.792, 1991: 1.55 | Egg concentration | Not Reported | Embryo | 5 | W. Marin Island | Toxicity Factor Datasets | USA |
CHROMIUM (elemental) | BI-89: 0.849, WM-89: 0.813 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DDT (2,4'-) | 0.47 ppm ww | Egg concentration | Embryo | 6 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
OXYCHLORDANE | 0.02 ppm ww | Egg concentration | Embryo | 1 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
METHYLMERCURY | 1997: 0.28, 1998: 0.43 µg/g ww | Stomach concentration | Both Adults and Juveniles | 5 | Carson Lake | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 2.92, reference: 3.30 g | Brain weight | Both Adults and Juveniles | LCRS: 6, Reference: 5 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 2.34, 2003: 2.36, 2004: 2.32 g | Brain weight | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
PCB | 0.185 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | S. Wilbur Flood Area | Toxicity Factor Datasets | USA |
COPPER (elemental) | BI-89: 7.16, WM-89: 7.10, WM-91: 7.12, SW-91: 6.21 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
DIELDRIN | 0.11 ppm ww | Egg concentration | Embryo | 2 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
CIS-CHLORDANE | 0.03 ppm ww | Egg concentration | Embryo | 1 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 43.65, reference site: 7.92 µg/g ww | Liver concentration | Adult | LCRS: 6, reference: 5 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 38.0, reference: 43.0 | Hematocrit | Both Adults and Juveniles | LCRS: 6, Reference: 5 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 2.70, 2003: 3.06, 2004: 2.40 µg/g ww | Liver concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
DDE (4,4'-) | 0.925 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Mallard Slough | Toxicity Factor Datasets | USA |
IRON (elemental) | BI-89: 119.0, WM-89: 121.0, WM-91: 135.0, SW-91: 141.0 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
HEPTACHLOR EPOXIDE | 0.04 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
CIS-NONACHLOR | Not detected | Egg concentration | Embryo | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | ||
MERCURY COMPOUNDS | LCRS: 43.65, reference site: 7.92 µg/g ww | Liver concentration | Nestling | LCRS: 6, reference: 7 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | See citation Table 7 | Histopathology | Both Adults and Juveniles | LCRS: 5, Reference: 6 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | 2002: 0.82, 2003: 0.86, 2004: 0.76 µg/g ww | Liver concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
DDE (4,4'-) | 1982: 2.04, 1989: 1.71, 1990: 1.88 µg/g ww | Egg concentration | Not Reported | Embryo | 1982: 10, 1989: 5, 1990: 5 | Bair Island | Toxicity Factor Datasets | USA |
MAGNESIUM COMPOUNDS | BI-89: 549, WM-89: 623, WM-91: 597, SW-91: 643 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
OXYCHLORDANE | 0.04 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
ENDRIN | Not detected | Egg concentration | Embryo | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | ||
MERCURY COMPOUNDS | LCRS: 11.12, reference site: 3.13 µg/g ww | Kidney concentration | Adult | LCRS: 6, reference: 3 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | See citation Table 3 | Egg concentration | Embryo | See citation | Lahontan Reservoir & Humboldt River | Toxicity Factor Datasets | USA | |
METHYLMERCURY | 2002: 2.35, 2003: 2.63, 2004: 2.01 µg/g ww | Liver concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Lahontan Reservoir | Toxicity Factor Datasets | USA |
DDE (4,4'-) | 1989: 1.86, 1990: 0.824, 1991: 1.17 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | W. Marin Island | Toxicity Factor Datasets | USA |
MANGANESE COMPOUNDS | BI-89: 2.43, WM-89: 3.07, WM-91: 4.54, SW-91: 2.43 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
CIS-CHLORDANE | 0.01 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
TOXAPHENE (POLYCHLORINATED CAMPHENES) | 0.04 ppm ww | Egg concentration | Embryo | 1 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | LCRS: 2.74, reference site: 0.40 µg/g ww | Kidney concentration | Nestling | LCRS: 6, reference: 7 | LCRS: Carson Lake & Lahontan Reservoir; Reference site: Ruby Lake & Humboldt River | Toxicity Factor Datasets | USA | |
MERCURY COMPOUNDS | See citation Table 4 | Blood concentration | Both Adults and Juveniles | See citation | Lahontan Reservoir & Humboldt River | Toxicity Factor Datasets | USA | |
METHYLMERCURY | 2002: 0.68, 2003: 0.74, 2004: 0.59 µg/g ww | Liver concentration | Not Reported | Nestling | 2002: 9, 2003: 7, 2004: 5 | Humboldt River | Toxicity Factor Datasets | USA |
DDE (4,4'-) | 3.01 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | S. Wilbur Flood Area | Toxicity Factor Datasets | USA |
MOLYBDENUM | BI-89:0.778, WM-89: 0.884, WM-91: 0.617, SW-91: 0.616 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
California Black Rail (Laterallus jamaicensis)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|
METHYLMERCURY | See citation Figures 3 & 4 | Blood concentration | Both Male and Female | Not Reported | 64 | Gambinini Marsh, Mid-Petaluma Marsh, Black John Slough | Toxicity Factor Datasets | Sonoma | USA |
METHYLMERCURY | See citation Figures 3 & 4 | Feather concentration | Not Reported | 127 | Gambinini Marsh, Mid-Petaluma Marsh, Black John Slough | Toxicity Factor Datasets | Sonoma | USA |
Burrowing Owl (Athene cunicularia formerly Speotyto cunicularia)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
STRYCHNINE | no effect | number of young produced per nest attempt | Both Male and Female | Juvenile | 27 pr | Saskatchewan | Toxicity Factor Datasets | CANADA |
Great Horned Owl (Bubo virginianus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, MIREX, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | increased | mortality due to pesticide exposure based on history, ante-mortem signs, and gross pathology | Not Reported | Not Reported | 8 owls | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DIELDRIN | no effect | productivity in contaminated versus uncontaminated sites | Both Male and Female | Adult | 3-4 nests on contaminated sites; 5-9 nests on uncontaminated sites | Rocky Mountain Arsenal National Wildlife Refuge | Toxicity Factor Datasets |
Song Sparrow (Melospiza melodia)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
FONOFOS, TERBUFOS | no effect | survival of banded individuals, pre- versus post-application, up to 50 days post-application | Both Male and Female | Adult | 88 males, 44 females (treatment); 69 males, 27 females (control) | southwestern Ontario | Toxicity Factor Datasets | CANADA |
Western Grebe (Aechmophorus occidentalis)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|---|
MERCURY COMPOUNDS | 0.001 (Clear Lake), 0.16 (Tule Lake) | productivity (young to adult ratios) at study locations | Not Reported | Adult | 13 birds, Clear Lake; 5 birds, Tule Lake | Clear Lake, Tule Lake | Toxicity Factor Datasets | Lake, Siskiyou |
Double-crested Cormorant (Phalacrocorax auritus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | increased at 1606 ng/kg | total hepatic cytochrome P450 content | Not Reported | Hatchling | 5-12 eggs/dose | Saskatchewan, British Columbia, Lake Ontario | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
CADMIUM (elemental), MERCURY (elemental) | no correlation | correlation of mean metallothionein concentration (13.2-24.4 ug/g tissue) and metal concentrations in kidneys | Not Reported | Both Adults and Juveniles | 24 birds | Heron Is., Manawagonish Is., Ile aux pommes | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 47.5 pg/g bw gained (wet wt) | pg TCDD equivalents accumulated per gram of body weight gained (from eggs to largest chicks) | Not Reported | Nestling | 20 chicks | St. Martin's Shoal, Lake Huron | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | increased @ all doses | hepatic EROD activity in treated embryos versus controls | Not Reported | Embryo | 83-86 eggs/treatment | Lake Winnipegosis, Manitoba | Toxicity Factor Datasets | Laboratory |
Mallard duck (Anas platyrhynchos)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
MEXACARBATE | 3.0 mg/kg | LD50 | Both Male and Female | Not Reported | 12 | Toxicity Factor Datasets | 3 - 5 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD ACETATE | decreased | ALAD enzyme activity versus controls | Male | Adult | 10 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDT (Technical Grade Mixture) | no effect | fertility, hatchability and duckling weight | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
RADIONUCLIDES | see citation | table of mean concentrations of 6 radionuclides (238Pu, 239Pu, 241Am, 242Cm, 244Cm, 90Sr) in 6 mallard tissue types | Not Reported | Adult | 7-15 | leaching ponds, Test Reactor Area, Idaho National Engineering Laboratory | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1242 | decrease @ 150 ppm | body weight at 6, 8 and 12 wks of treatment | Female | Adult | 12 pairs/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DICOFOL | increase @ 100 ug/g | incidence of cracked and soft shelled eggs | Female | Adult | 4-8/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CRUDE OILS | decrease | plasma prolactin levels during oviposition, early incubation and post-natal care | Female | Adult | 5-12/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 |
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 |
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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIAZINON | 74 (day 3), 79 (day 8) lb/acre LC50 | 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 |
---|---|---|---|---|---|---|---|---|---|
PARATHION | 4/36 | mortality incidence by 20 hrs post-dose | Not Reported | Juvenile | 36/dose | Toxicity Factor Datasets | 14 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEPTOPHOS | decreased @ all doses | activity of brain and plasma cholinesterase, and brain neurotoxic esterase compared with controls | Female | Juvenile | 6/group | Toxicity Factor Datasets | 20 wks | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254, DDE (4,4'-) | no effect | food consumption rate (181 g/d) compared to control (173 g/d) | Female | Adult | 10/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | no effect | egg weight, length or breadth, compared to control | Female | Adult | 21-25/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | California Counties | Lab |
---|---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | decreased @ 2 #four shot | spleen plaque forming cell counts, % packed cell volume versus controls | Both Male and Female | Adult | 16 (2 #four shot) 63 (field exposure) |
Sacramento National Wildlife Refuge | Toxicity Factor Datasets | 1 yr | Sacramento | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
EPN | decreased @ 36 (cholineserase only), 108 ug/g | plasma alkaline phosphatase, aspartate aminotransferase, cholinesterase activities, and uric acid | Not Reported | Embryo | 12/group | Toxicity Factor Datasets | 72 hr of incubation (time of treatment) | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | lead only: 3.53 (+/- 1.43); lead-iron: 1.42 (+/- 0.65) ppm, wet wt | lead concentration in kidneys (mean +/- SE) | 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 |
---|---|---|---|---|---|---|---|---|---|
LEAD NITRATE | decreased @ 25 ppm/3 wks, 5 ppm/12 wks | delta-aminolevulinic acid dehydratase activity in blood versus controls | Male | Adult | 20/dose; 5/dose x time group | Toxicity Factor Datasets | 1 yr | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 78.2 (carcass); 61.6 (egg); 4.1 (brain) ppm, wet wt | DDE residues in whole carcass, egg contents, and brain | Female | Adult | 10/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CADMIUM CHLORIDE | 0.03 (@ 0 ppm), 0.02 (@ 2 ppm), 0.72 (@ 20 ppm) 8.47 (@ 200 ppm) ppm, wet wt | mean Cd concentrations in testes (ppm, wet wt) by 90 days | 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 | increased to 61% @ 1000 (LL), 100% @ 5000 (LL) | mortality versus controls | Not Reported | Juvenile | 12-14/group | Toxicity Factor Datasets | 1 d | Laboratory |