DIELDRIN
Mammals, Bats (Chiroptera), Little Brown Bat (Myotis lucifugus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DIELDRIN | Range: <0.03-0.93 µg/g ww | Brain concentration | NR | Not Reported | 5 | New Jersey Rabies Laboratory | Toxicity Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DIELDRIN | See citation Figure 1 | Body concentration | F | Both Adults and Juveniles | 47 | Patuxent Wildlife Research Center, Laurel | Toxicity Factor Datasets | USA |
DIELDRIN | Adult: 0.09, juvenile: 0.14 ppm | Guano concentration | Both Adults and Juveniles | 47 | Patuxent Wildlife Research Center, Laurel | 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 |
---|---|---|---|---|---|---|---|---|
DIELDRIN | 0.56, 0.30, 0.15 ug/g ww | Brain concentration | NR | Not Reported | 3 | Toxicity Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Sample Size | Location | Type |
---|---|---|---|---|---|
DIELDRIN | Kettle Creek (1993): 4.0; VBNWA (1993): 0.6; ANWA LH (1997): ND; UBC (1997): ND; EC Park (1997): ND; ANWA (1998): ND; TY Park (1998): ND; UBC (1998): ND; ST Park (1998): ND 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 |
---|---|---|---|---|---|---|---|---|
DIELDRIN | Penticton (1993): 53.9; Kelowna (1994): not detected; Penticton (1994): 44.8; Penticton (1995): 16.7; Naramata (1997): ND; Penticton (1997): ND; Naramata (1998): ND 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 |
---|---|---|---|---|---|---|---|---|
DIELDRIN | <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 |
---|---|---|---|---|---|---|---|---|
DIELDRIN | Naramata: 0.13; Cawston: 0.032; 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 | California Counties | Countries | Lab |
---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | Breeding: not detected | Unspecified tissue concentration | M | Not Reported | Breeding: 1, non-breeding: 5 | Toxicity Factor Datasets | USA | |||
DIELDRIN | Breeding: 0.12 ppm | Unspecified tissue concentration | F | Not Reported | Breeding: 5, non-breeding: 5 | Toxicity Factor Datasets | USA | |||
DIELDRIN | 0.54 µg/g ww | Feather concentration | NR | Both Adults and Juveniles | 45 | Rio Negro Province; rural site: Bariloche; ag site: Valle | Toxicity Factor Datasets | ARGENTINA | ||
DIELDRIN | 0.11 ppm ww | Egg concentration | Embryo | 2 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |||
DIELDRIN | Alaska: 29, California: 77.5 ng/g lw | Blood concentration | B | Juvenile | Alaska: 14, California: 6 | Alaksa: 3 sites in eastern AK, California: 3 sites between Santa Cruz and Monterey | Toxicity Factor Datasets | |||
DIELDRIN | 48.68 µg/g | Egg concentration | NR | Embryo | 5 | Green Bay | Toxicity Factor Datasets | USA | ||
DIELDRIN | See citation | Egg concentration | NR | Embryo | Varied by site | Multiple sites in Straight of Georgia | Toxicity Factor Datasets | CANADA | ||
DIELDRIN | 0.19 µg/kg ww | Egg concentrations | Embryo | 14 | Fern Ridge Reservoir | Toxicity Factor Datasets | USA | |||
DIELDRIN | 15.0 ng/g ww (5.443-39.6) | Egg concentration | 10 | Marsh Island | Toxicity Factor Datasets | USA | Laboratory | |||
DIELDRIN | Not detected | Plasma concentration | B | Juvenile | 13 | Bahía Magdalena | Toxicity Factor Datasets | MEXICO | ||
DIELDRIN | 5.42 ng/g ww (3.15-9.96) | Egg concentration | 33 | Marsh Island | Toxicity Factor Datasets | MEXICO | Laboratory | |||
DIELDRIN | 0.02 ppm ww | Egg concentration | Embryo | 2 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |||
DIELDRIN | 0.50 ng/g ww ± 0.4 | Egg concentration | Embryo | 8 | Colorado River Delta | Toxicity Factor Datasets | MEXICO | Laboratory | ||
DIELDRIN | MS-90: 0.0258, BI-82: 0.0926, BI-89: 0.0270, BI-90: 0.0661, WM-89: 0.0308 WM-90: 0.0204, WM-91: 0.00887, SW-91: 0.0275 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 | ||
DIELDRIN | 0.02 | Egg concentration | Embryo | 22 | South San Francisco Bay marshes | Toxicity Factor Datasets | USA | Laboratory | ||
DIELDRIN | 0.039 µg/g ww ± 0.035 | Liver concentration | NR | Hatchling | 4 | Hamilton Harbour, Western Lake Ontario | Toxicity Factor Datasets | CANADA | Laboratory | |
DIELDRIN | 0.03 µg/g ww ± 0.02 | Liver concentration | NR | Hatchling | 4 | Snake and Pigeon Islands, Eastern Lake Ontario | Toxicity Factor Datasets | CANADA | Laboratory | |
DIELDRIN | Not detected | Egg concentration | Embryo | 4 | Naval Air Base Coronado | Toxicity Factor Datasets | San Diego | USA | ||
DIELDRIN | Not detected | Egg concentration | Embryo | 5 | Tijuana Slough | Toxicity Factor Datasets | San Diego | USA | ||
DIELDRIN | 0.20 mg/kg | Egg concentration | Embryo | 60 | NJ, PA, DE, MD, VA | Toxicity Factor Datasets | USA | |||
DIELDRIN | 1982-1986: 0.07, 1990-1998: not detected, 2004-2006: not detected mg/kg | Plasma concentration | B | Adult | 1982-1986: 72, 1990-1998: 97, 2004-2006: 25 | Rankin Inlet, Nunavut | Toxicity Factor Datasets | CANADA | ||
DIELDRIN | 1982-1986: 0.07, 1990-1998: 0.01, 2004-2006: 0.01 mg/kg | Plasma concentration | F | Adult | 1982-1986: 54, 1990-1998: 66, 2004-2006: 16 | Rankin Inlet, Nunavut | Toxicity Factor Datasets | CANADA | ||
DIELDRIN | 1982-1986: 0.08, 1990-1998: <0.01, 2004-2006: <0.01 mg/kg | Plasma concentration | M | Adult | 1982-1986: 18, 1990-1998: 31, 2004-2006: 9 | Rankin Inlet, Nunavut | Toxicity Factor Datasets | CANADA | ||
DIELDRIN | Alaska: 28, California: 78.8 ng/g lw | Blood concentration | B | Pup | Alaska: 3, California: 5 | Alaksa: 3 sites in eastern AK, California: 3 sites between Santa Cruz and Monterey | Toxicity Factor Datasets | |||
DIELDRIN | 8.9 ± 2.9 ng/g | Accumulation in eggs from spiked nest material | NR | Embryo | 10 | Texas Tech University, Lubbock | Toxicity Factor Datasets | Lab | USA | Laboratory |
DIELDRIN | Alaska: 16, California: 36.3 ng/g lw | Blood concentration | F | Adult | Alaska: 38, California: 18 | Alaksa: 3 sites in eastern AK, California: 3 sites between Santa Cruz and Monterey | Toxicity Factor Datasets | |||
DIELDRIN | 13 ± 22 ng/g | Accumulation in eggs from spiked nest material | NR | Embryo | 10 | Texas Tech University, Lubbock | Toxicity Factor Datasets | Lab | USA | Laboratory |
DIELDRIN | Alaska: 15, California: 59.7 ng/g lw | Blood concentration | M | Adult | Alaska: 16, California: 11 | Alaksa: 3 sites in eastern AK, California: 3 sites between Santa Cruz and Monterey | Toxicity Factor Datasets | |||
DIELDRIN | 16.7 ng/g ww (9.26-56.8) | Egg concentration | 18 | Crab Bank | Toxicity Factor Datasets | USA | Laboratory | |||
DIELDRIN | Not detected | Plasma concentration | B | Juvenile | 39 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
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 |
---|---|---|---|---|---|---|---|---|
DIELDRIN | Not detected | Plasma concentration | Both Male and Female | Juvenile | 39 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
DIELDRIN | Not detected | 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 |
---|---|---|---|---|---|---|---|---|
DIELDRIN | 0.11 ppm ww | Egg concentration | Embryo | 2 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |
DIELDRIN | 0.02 ppm ww | Egg concentration | Embryo | 2 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |
DIELDRIN | MS-90: 0.0258, BI-82: 0.0926, BI-89: 0.0270, BI-90: 0.0661, WM-89: 0.0308 WM-90: 0.0204, WM-91: 0.00887, SW-91: 0.0275 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 |
Bullfrog (Lithobates catesbeianus formerly Rana catesbeiana)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 12.3 ug/l | NOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 29 d | Laboratory | |
DIELDRIN | 12.0 ug/g at 30.3 ug/l | whole body dieldrin concentration (ug/g, wet wt.) at the LC50 | Not Reported | Tadpole | Not Reported | Toxicity Factor Datasets | 29 d | Laboratory | |
DIELDRIN | 19.0 ug/g at 52.3 ug/l | whole body dieldrin concentration (ug/g, wet wt.) | Not Reported | Tadpole | Not Reported | Toxicity Factor Datasets | 29 d | Laboratory | |
DIELDRIN | 34.4 ug/l (95% CL: 31.1 - 38.1 ug/l) | LC50 | Not Reported | Embryo | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | embryo-larvae, 11d | Laboratory | |
DIELDRIN | 0.5 ug/g at 12.3 ug/l | whole body dieldrin concentration (ug/g, wet wt.) at the NOAEL | Not Reported | Tadpole | Not Reported | Toxicity Factor Datasets | 29 d | Laboratory | |
DIELDRIN | 25.1 ug/l | LOAEL, based on mortality but gross spinal deformities also observed | Not Reported | Embryo | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | embryo-larvae, 11d | Laboratory | |
DIELDRIN | 360 - 900 | range of bioconcentration factors; calculated by dividing the whole body tissue dieldrin concentration by water dieldrin concentration | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 29 d | Laboratory | |
DIELDRIN | 11.0 ug/l | NOAEL | Not Reported | Embryo | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | embryo-larvae, 11d | Laboratory | |
DIELDRIN | 36,000 - 90,000 | range of lipid bioconcentration factors; calculated by dividing the whole body bioconcentration values x 100 by percent lipid | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 29 d | Laboratory | |
DIELDRIN | 8.7 ug/l (95% CL: 7.8-9.7 ug/l) | LC50 | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 50 d | Laboratory | |
DIELDRIN | 11.2 ug/l | LOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 50 d | Laboratory | |
DIELDRIN | 4.0 ug/l | NOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 50 d | Laboratory |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|
DIELDRIN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
Great Horned Owl (Bubo virginianus)
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 |
---|---|---|---|---|---|---|---|
DIELDRIN | 0.07 +/- 0.03 ppm (uncontaminated site); 0.34 +/- 0.21 ppm (contaminated site) | mean (+/- SE) concentrations in plasma | Not Reported | Adult | 2 birds on contaminated sites; 5 birds on uncontaminated sites | Rocky Mountain Arsenal National Wildlife Refuge | Toxicity Factor Datasets |
DIELDRIN | 0.01 +/- 0.003 ppm (uncontaminated site); 0.22 +/- 0.03 ppm (contaminated site) | mean (+/- SE) concentrations in plasma | Not Reported | Juvenile | 6 birds on contaminated sites; 10 birds on uncontaminated sites | Rocky Mountain Arsenal National Wildlife Refuge | 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 |
Great Horned Owl (Bubo virginianus), Mourning Dove (Zenaida macroura)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
ALDRIN, DIELDRIN | 6.1 ppm (brain), 10.7 ppm (body remainder) dieldrin, wet wt | post-mortem concentrations | Not Reported | Not Reported | 1 bird | Toxicity Factor Datasets |
Mallard duck (Anas platyrhynchos)
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 |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | no effect | total body weight, compared to control | Not Reported | Juvenile | 4-6/dose | Toxicity Factor Datasets | 1 d | Laboratory | |
DIELDRIN | 9.7 ug/g lipid, 3.3 ug/g skin, 1.3 ug/g brain, 0.8 ug/g liver, 0.7 ug/g muscle at 2.6 ug/g food | mean of day 5, 7, 8 (approx. steady state) tissue concentrations | Not Reported | Juvenile | 6 | Toxicity Factor Datasets | 1 d | Laboratory | |
DIELDRIN | 42.5 ug/g lipid, 14.6 ug/g skin, 1.6 ug/g brain, 2.5 ug/g liver, 1.2 ug/g muscle at 26.2 ug/g food | mean of day 5, 7, 8 (approx. steady state) tissue concentrations | Not Reported | Juvenile | 6 | Toxicity Factor Datasets | 1 d | Laboratory | |
DIELDRIN | 80.7 ug/g lipid, 30.1 ug/g skin, 1.6 ug/g brain, 4.1 ug/g liver, 1.8 ug/g muscle at 49.3 ug/g food | mean of day 5, 7, 8 (approx. steady state) tissue concentrations | Not Reported | Juvenile | 6 | Toxicity Factor Datasets | 1 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 706 - 1,995 | steady state bioconcentration factor for lipid, calculated on a wet weight basis; range for 7 doses | Not Reported | Juvenile | 8-16/dose | Toxicity Factor Datasets | 1 d at initiation | Laboratory | |
DIELDRIN | 178 - 684 | steady state bioconcentration factor for skin, calculated on a wet weight basis; range for 7 doses | Not Reported | Juvenile | 8-16/dose | Toxicity Factor Datasets | 1 d at initiation | Laboratory | |
DIELDRIN | 49 - 163 | steady state bioconcentration factor for liver, calculated on a wet weight basis; range for 7 doses | Not Reported | Juvenile | 8-16/dose | Toxicity Factor Datasets | 1 d at initiation | Laboratory | |
DIELDRIN | 5.5 - 95 | steady state bioconcentration factor for muscle, calculated on a wet weight basis; range for 7 doses | Not Reported | Juvenile | 8-16/dose | Toxicity Factor Datasets | 1 d at initiation | Laboratory | |
DIELDRIN | 165 ug/g diet (100 - 224 ug/g, 95% CI) | 96 hr LC50 | Not Reported | Juvenile | 10/dose | Toxicity Factor Datasets | 1 - 25 d | Laboratory | |
DIELDRIN | 29.5 ug/g diet (14 - 28 ug/g, 95% CI) | 24-d LC50 | 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 |
---|---|---|---|---|---|---|---|
DDE (4,4'-), DIELDRIN, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | positive correlation | relationships between EROD activity and dieldrin concentrations | Female | Adult | 5 birds/timepoint (timepoints = 0,10,20,32,42,52,59,70,80,90,100 days) | Bloomington | Toxicity Factor Datasets |
DDE (4,4'-), DIELDRIN, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | positive correlation | relationship between BROD, PROD, and EROD activities and total PCB, oxychlordane, and TEQs concentrations | Female | Adult | 5 birds/timepoint (timepoints = 0,10,20,32,42,52,59,70,80,90,100 days) | Bloomington | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | decreased @ 10 ppm (serotonin only) and 30 ppm | Serotonin, norepinephrine, and dopamine levels versus controls | Both Male and Female | Juvenile | 3-6 per group | Toxicity Factor Datasets | 75 days | Laboratory | |
DIELDRIN | increased with all doses | brain, liver, and adipose dieldrin concentrations | Both Male and Female | Juvenile | 4-6 per group | Toxicity Factor Datasets | 75 days | Laboratory | |
DIELDRIN | no effect | bw versus controls | Both Male and Female | Juvenile | 9-25 per group | Toxicity Factor Datasets | 75 days | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DIELDRIN | no effect | fertility, hatchability and duckling weight | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory | |
DIELDRIN | no effect | hepatic microsomal enzyme activity (aniline hydroxylase and aminopyrine N-demethylase) | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory |
Peregrine Falcon (Falco peregrinus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
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 |
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 | Condition |
---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN | 48.0 (DDE), 3.35 (DDD), 1.02 (DDT), 1.45 (dieldrin) | mean concentrations of pesticides in eggs (ppm, dry weight) | Female | Adult | 2 eggs | Yukon River | Toxicity Factor Datasets | |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN | 622.0 (DDE), 25.4 (DDD), 25.3 (DDT), 6.20 (dieldrin) | mean concentrations of pesticides in fat (ppm, dry weight) | Both Male and Female | Adult | 4 birds | Yukon River | Toxicity Factor Datasets | breeding |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
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 |
Mourning Dove (Zenaida macroura)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DIELDRIN | 44-46 mg/kg | median lethal dosage | Not Reported | Not Reported | 20 birds | Toxicity Factor Datasets | Laboratory |
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 |
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 | |
DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS | 0.70 (0.20 SE) ppm (wet wt) | lead concentration in tibia | Female | Juvenile | 2 | Toxicity Factor Datasets | Laboratory | |
DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS | 232 (9 SE) ppm (wet wt) | DDE concentration in carcass | Female | Juvenile | 2 | Toxicity Factor Datasets | Laboratory |
Loggerhead Shrike (Lanius ludovicianus)
Chemical | Endpoint Value | Location | Type | Lab |
---|---|---|---|---|
DIELDRIN | review | Toxicity Factor Datasets | Laboratory |
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 |
Deer Mouse (Peromyscus maniculatus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DIELDRIN | increase | population size at contaminated vs reference sites | Both Male and Female | Both Adults and Juveniles | Not Reported | Rocky Mountain Arsenal National Wildlife Refuge | Toxicity Factor Datasets |
DIELDRIN | increase | % of female deer mice exhibiting signs of reproduction increased as dieldrin levels increased at contaminated vs control sites | Female | Adult | Not Reported | Rocky Mountain Arsenal National Wildlife Refuge | 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 |