HEPTACHLOR EPOXIDE
Mammals, Bats (Chiroptera), Little Brown Bat (Myotis lucifugus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | Range: <0.02-3.70 µg/g ww | Brain concentration | NR | Not Reported | 5 | New Jersey Rabies Laboratory | Toxicity Factor Datasets | USA |
Birds, Terrestrial birds, Passeriformes, American Robin (Turdus migratorius)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | 4.5, 3.5, 3.3 ug/g ww | Brain concentration | NR | Not Reported | 3 | Toxicity Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Sample Size | Location | Type |
---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | Kettle Creek (1993): 0.3; VBNWA (1993): ND; ANWA LH (1997): 1.6; UBC (1997): 4.2; EC Park (1997): 1.1; ANWA (1998): ND; TY Park (1998): ND; UBC (1998): 2.9; ST Park (1998): 0.05 ug/kg | Egg concentration | Kettle Creek (1993): 4; VBNWA (1993): 2; ANWA LH (1997): 6; UBC (1997): 9; EC Park (1997): 1; ANWA (1998): 1; TY Park (1998): 2; UBC (1998): 5; ST Park (1998): 2 | Okanagan Valley | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | Penticton (1993): 1.5; Kelowna (1994): 0.4; Penticton (1994): 0.4; Penticton (1995): 0.4, Naramata (1997): 0.1; Penticton (1997): 0.1; Naramata (1998): 0.2 ug/kg | Egg concentration | B | Embryo | Penticton (1993): 23; Kelowna (1994): 1; Penticton (1994): 2; Penticton (1995): 13, Naramata (1997): 19; Penticton (1997): 12; Naramata (1998): 22 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | <0.01 ug/g ww | Egg concentration | B | Embryo | 18 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | Naramata: 0.010; Cawston: 0.007; Vaseaux: <0.0008 mg/kg ww | Egg concentration | B | Embryo | Naramata: 5; Cawston:5; Vaseaux: 2 | Okanagan Valley | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Lab |
---|---|---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | 2.99 µg/g ww | Feather concentration | NR | Both Adults and Juveniles | 45 | Rio Negro Province; rural site: Bariloche; ag site: Valle | Toxicity Factor Datasets | ARGENTINA | |
HEPTACHLOR EPOXIDE | 0.04 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | ||
HEPTACHLOR EPOXIDE | 0.005-7.88 ng/mL | Plasma concentration | B | Juvenile | 39 | Punta Abreojos | Toxicity Factor Datasets | MEXICO | |
HEPTACHLOR EPOXIDE | 9.28 µg/g | Egg concentration | NR | Embryo | 5 | Green Bay | Toxicity Factor Datasets | USA | |
HEPTACHLOR EPOXIDE | 0.13 µg/kg ww | Egg concentrations | Embryo | 14 | Fern Ridge Reservoir | Toxicity Factor Datasets | USA | ||
HEPTACHLOR EPOXIDE | 0.04 µg/g ww | Brain concentration | NR | Nestling | 4 | Lake Okeechobee | Toxicity Factor Datasets | USA | |
HEPTACHLOR EPOXIDE | Not detected | Brain concentration | NR | Nestling | 2 | Central Everglades | Toxicity Factor Datasets | USA | |
HEPTACHLOR EPOXIDE | Not detected | Brain concentration | NR | Nestling | 10 | Mangrove estuary, west coast of Everglades National Park | Toxicity Factor Datasets | USA | |
HEPTACHLOR EPOXIDE | 0.01 | Egg concentration | Embryo | 22 | South San Francisco Bay marshes | Toxicity Factor Datasets | USA | Laboratory | |
HEPTACHLOR EPOXIDE | 0.006 µg/g ww ± 0.002 | Liver concentration | NR | Hatchling | 4 | Hamilton Harbour, Western Lake Ontario | Toxicity Factor Datasets | CANADA | Laboratory |
HEPTACHLOR EPOXIDE | 0.008 µg/g ww ± 0.006 | Liver concentration | NR | Hatchling | 4 | Snake and Pigeon Islands, Eastern Lake Ontario | Toxicity Factor Datasets | CANADA | Laboratory |
HEPTACHLOR EPOXIDE | 0.10 mg/kg | Egg concentration | Embryo | 60 | NJ, PA, DE, MD, VA | Toxicity Factor Datasets | USA | ||
HEPTACHLOR EPOXIDE | 0.95 ng/g ww | Plasma concentration, geometric mean | NR | Nestling | 43 nests | Great Lake Basin | Toxicity Factor Datasets | CANADA | |
HEPTACHLOR EPOXIDE | 0.03 µg/g lw | Blubber concentration | B | Not Reported | 18 | Todos Santos Bay, Ensenada, Baja California | Toxicity Factor Datasets | MEXICO | |
HEPTACHLOR EPOXIDE | 1.844882 ng/mL | Plasma concentration | B | Juvenile | 13 | Bahía Magdalena | Toxicity Factor Datasets | MEXICO | |
HEPTACHLOR EPOXIDE | 0.03 ppm ww | Egg concentration | Embryo | 1 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | ||
HEPTACHLOR EPOXIDE | MS-90: 0.0160, BI-82: not detected, BI-89: 0.0170, BI-90: 0.0242, WM-89: 0.0151, WM-90: 0.0132, WM-91: 0.0146, SW-91: 0.0110 µg/g ww | Egg concentration | NR | Embryo | BI-82: 10, others: 5 | MS: Mallard Slough, Bair Island, WM: West Marin Island, SW: South Wilbur Flood Area | Toxicity Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
ALDRIN, DDT (Technical Grade Mixture), DIELDRIN, ENDRIN, HEPTACHLOR, HEPTACHLOR EPOXIDE, LINDANE | review | eggshell breakage, weight and thickness compared to 1950 measurements | Female | Adult | Not Reported | Toxicity Factor Datasets | UNITED KINGDOM |
Pacific Green Turtle (Chelonia mydas)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | 0.005-7.88 ng/mL | Plasma concentration | Both Male and Female | Juvenile | 39 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
HEPTACHLOR EPOXIDE | 1.844882 ng/mL | Plasma concentration | Both Male and Female | Juvenile | 13 | Bahía Magdalena | Toxicity Factor Datasets | MEXICO |
Snowy Egret (Egretta thula)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | 0.04 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
HEPTACHLOR EPOXIDE | 0.03 ppm ww | Egg concentration | Embryo | 1 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
HEPTACHLOR EPOXIDE | MS-90: 0.0160, BI-82: not detected, BI-89: 0.0170, BI-90: 0.0242, WM-89: 0.0151, WM-90: 0.0132, WM-91: 0.0146, SW-91: 0.0110 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 |
Peregrine Falcon (Falco peregrinus)
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 | 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 |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE | no effect | number of viable eggs or young versus "normal" nest success | Not Reported | Juvenile | 15 nests | Peace, Slave, and Mackenzie Rivers | Toxicity Factor Datasets | CANADA | |
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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | negative correlation | correlation of heptachlor epoxide concentration in eggs and eggshell thickness | Female | Adult | 38 eggs | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-), HEPTACHLOR EPOXIDE | 15 ppm DDE, 0.7 ppm heptachlor epoxide | concentrations in eggs associated with population recovery | Both Male and Female | Both Adults and Juveniles | 550 eggs from 469 clutches | Toxicity Factor Datasets | UNITED KINGDOM |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
HEPTACHLOR EPOXIDE | review | concentrations in brain associated with mortality (various raptor species) | Not Reported | Not Reported | Not Reported | Toxicity Factor Datasets | Laboratory | |
HEPTACHLOR EPOXIDE | review | concentrations in eggs associated with reduced reproduction (various raptor species) | Not Reported | Not Reported | Not Reported | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), HEPTACHLOR EPOXIDE, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | 12.1% | percent eggshell thinning (as indicated by Ratcliffe Index) compared to pre-1947 eggs | Not Reported | Embryo | 39 eggs | Mid-Atlantic coastal and urban breeding sites | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, POLYCHLORINATED BIPHENYLS | 15.8% | mean eggshell thinning compared to "pre-pesticide" reference eggs | Female | Adult | 78 eggs | Rankin Inlet | Toxicity Factor Datasets |
DDE (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, POLYCHLORINATED BIPHENYLS | log DDE in eggs = 0.9723 + 0.8506(log DDE in plasma); r = 0.66 | log-log relationship between DDE in plasma of female birds and DDE in eggs | Female | Adult | 10 females | Rankin Inlet | Toxicity Factor Datasets |
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 | no effect | eggshell thickness compared to pre-1946 museum speciments | Female | Adult | 3 eggs | south-central Montana | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
AROCLOR 1254, DDE (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, OXYCHLORDANE | 5% decrease | eggshell thickness index compared with reference eggs | Female | Adult | 18 eggs, 15 clutches | Butler, Delaware, Hamilton Counties | Toxicity Factor Datasets |
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 |
---|---|---|---|---|---|---|---|
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 | 13 owls | Toxicity Factor Datasets |
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 mortality as a result of organochlorine poisoning | Female | Adult | 1 owl | 6 km s. of Corvallis | Toxicity Factor Datasets |
Double-crested Cormorant (Phalacrocorax auritus)
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, HEXACHLOROBENZENE, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 95% | percent of eggs lost or broken before hatching in contaminated colonies | Not Reported | Embryo | 235 eggs | Lake Huron | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, HEXACHLOROBENZENE, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 23.9% thinner | eggshell thickness compared with pre-1947 eggshells in contaminated colonies | Not Reported | Embryo | 18 eggs | Lake Huron | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, HEXACHLOROBENZENE, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 2.4% | mean hatching success in contaminated colonies | Not Reported | Embryo | 331 eggs | Lake Huron | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, HEXACHLOROBENZENE, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 0.06-0.11 (1972); 0.3 (1973) | fledging success (young/nest) in contaminated colonies | Not Reported | Embryo | 42 (1973)-66 (1972) nests | Lake Huron | Toxicity Factor Datasets |
American Kestrel (Falco sparverius)
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 |