DIELDRIN

Mammals, Bats (Chiroptera), Little Brown Bat (Myotis lucifugus)

Citation:

Food chain aspects of chlordane poisoning in birds and bats.

Author(s)

Stansley, W., Roscoe, D.E., Hawthorne, E. and Meyer, R.

Issue

2

Volume

40
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

Citation:

Disposition of dietary dieldrin in the Little Brown Bat Myotis-Lucifugus and correlation of skin levels with body burden.

Author(s)

Clark Jr. D.R., Prouty, R.M.

Issue

2

Volume

33
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)

Citation:

Chlordane poisoning of birds in New Jersey, USA.

Author(s)

Stansley, W. and Roscoe, D.E.

Issue

9

Volume

18
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

Citation:
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

Citation:

The effects of environmental exposure to DDT on the brain of a songbird: changes in structures associated with mating and song.

Author(s)

Iwaniuk, A.N., Koperski, D.T., Cheng, K.M., Elliott, J.E., Smith, L.K., Wilson, L.K. and Wylie, D.R.

Issue

1

Volume

173
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

Citation:

An assessment of DDT and other chlorinated compounds and the reproductive success of American robins (Turdus migratorius) breeding in fruit orchards.

Author(s)

Gill, H., Wilson, L.K., Cheng, K.M. and Elliott, J.E.

Issue

1

Volume

12
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

Citation:

Organochlorines and reproductive success of birds in orchard and non-orchard areas of central British Columbia, Canada, 1990–91.

Author(s)

Elliott, J.E., Martin, P.A., Arnold, T.W. and Sinclair, P.H.

Issue

4

Volume

26
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

Citation:
Chemical	Endpoint Value	Endpoint Description	Sex	Life Cycle Stage	Sample Size	Location	Type	California Counties	Countries	Lab
DIELDRIN	Breeding: 0.12 ppm	Unspecified tissue concentration	F	Not Reported	Breeding: 5, non-breeding: 5		Toxicity Factor Datasets		USA
DIELDRIN	Breeding: not detected	Unspecified tissue concentration	M	Not Reported	Breeding: 1, 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	0.02	Egg concentration		Embryo	22	South San Francisco Bay marshes	Toxicity Factor Datasets		USA	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	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	Not detected	Egg concentration		Embryo	4	Naval Air Base Coronado	Toxicity Factor Datasets	San Diego	USA
DIELDRIN	0.039 µg/g ww ± 0.035	Liver concentration	NR	Hatchling	4	Hamilton Harbour, Western Lake Ontario	Toxicity Factor Datasets		CANADA	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	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	0.50 ng/g ww ± 0.4	Egg concentration		Embryo	8	Colorado River Delta	Toxicity Factor Datasets		MEXICO	Laboratory
DIELDRIN	0.02 ppm ww	Egg concentration		Embryo	2	Minidoka National Wildlife Refuge	Toxicity Factor Datasets		USA
DIELDRIN	Not detected	Egg concentration		Embryo	5	Tijuana Slough	Toxicity Factor Datasets	San Diego	USA
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	5.42 ng/g ww (3.15-9.96)	Egg concentration			33	Marsh Island	Toxicity Factor Datasets		MEXICO	Laboratory
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	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	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	0.20 mg/kg	Egg concentration		Embryo	60	NJ, PA, DE, MD, VA	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	Not detected	Plasma concentration	B	Juvenile	39	Punta Abreojos	Toxicity Factor Datasets		MEXICO
DIELDRIN	16.7 ng/g ww (9.26-56.8)	Egg concentration			18	Crab Bank	Toxicity Factor Datasets		USA	Laboratory
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	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

Snowy Egret (Egretta thula)

Citation:
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

Pacific Green Turtle (Chelonia mydas)

Citation:
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

Bullfrog (Lithobates catesbeianus formerly Rana catesbeiana)

Citation:

Teratogenesis, toxicity and bioaccumulation in frogs exposed to dieldrin

Author(s)

Schuytema, Gerald S., Alan V. Nebeker, William L. Griffis and Karsten N. Wilson

Pages

332-350

Year

Tuesday, January 1, 1991 - 12:00

Volume

21
Chemical	Endpoint Value	Endpoint Description	Sex	Life Cycle Stage	Sample Size	Type	Age-Specific	Lab
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	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	5.1 ug/g at 8.7 ug/l	whole body dieldrin concentration (ug/g, wet wt.) at the LC50	Not Reported	Tadpole	Not Reported	Toxicity Factor Datasets	50 d	Laboratory
DIELDRIN	6.0 ug/g at 11.2 ug/l	whole body dieldrin concentration (ug/g, wet wt.)	Not Reported	Tadpole	Not Reported	Toxicity Factor Datasets	50 d	Laboratory
DIELDRIN	360 - 540	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	50 d	Laboratory
DIELDRIN	36,000 - 54,000	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	50 d	Laboratory
DIELDRIN	30.3 ug/l (95% CL: 26.2 - 35.2 ug/l)	LC50	Not Reported	Tadpole	20 animals/replicate; 4 replicates/dose	Toxicity Factor Datasets	29 d	Laboratory
DIELDRIN	52.3 ug/l	LOAEL	Not Reported	Tadpole	20 animals/replicate; 4 replicates/dose	Toxicity Factor Datasets	29 d	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	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

American Kestrel (Falco sparverius)

Citation:

Accumulation of lead and organochlorine residues in captive American kestrels fed pine voles from apple orchards

Author(s)

Stendell, Rey C., W. Nelson Beyer and Robert A. Stehn

Pages

388-391

Year

Sunday, January 1, 1989 - 12:00

Issue

3

Volume

25
Chemical	Endpoint Value	Endpoint Description	Sex	Life Cycle Stage	Sample Size	Type	Lab
DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS	232 (9 SE) ppm (wet wt)	DDE concentration in carcass	Female	Juvenile	2	Toxicity Factor Datasets	Laboratory
DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS	10.4 (0.6 SE) ppm (wet wt)	DDE concentration in brain	Female	Juvenile	2	Toxicity Factor Datasets	Laboratory
DDE (4,4'-), DIELDRIN, LEAD COMPOUNDS	decreased	bw (versus pre-study bw)	Female	Juvenile	2	Toxicity Factor Datasets	Laboratory

Deer Mouse (Peromyscus maniculatus)

Citation:

Effects of dieldrin on homing and orientation in deer mice

Author(s)

Snyder, Ron L.

Pages

362-364

Year

Tuesday, January 1, 1974 - 12:00

Issue

2

Volume

38
Chemical	Endpoint Value	Endpoint Description	Sex	Life Cycle Stage	Sample Size	Location	Type
DIELDRIN	decrease at 5 mg/kg	homing orientation test, measured as time in maze pointing to capture site	Both Male and Female	Both Adults and Juveniles	15 animals/dose	NR	Toxicity Factor Datasets
DIELDRIN	decrease at 5 mg/kg	homing, measured as number recaptured at pre-exposure site	Both Male and Female	Both Adults and Juveniles	15 animals/dose	NR	Toxicity Factor Datasets

Brown Pelican (Pelecanus occidentalis)

Citation:

Chlorinated hydrocarbon residues in the diet and eggs of the Florida brown pelican

Author(s)

Thompson, Neal P., Patrick W. Rankin, Patricia E. Cowan, Lovett E. Williams, Jr. and Stephen A. Nesbitt

Pages

331-339

Year

Saturday, January 1, 1977 - 12:00

Issue

3

Volume

18
Chemical	Endpoint Value	Endpoint Description	Sex	Life Cycle Stage	Sample Size	Location	Type
AROCLOR 1254, DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN	0.896 ppm DDE, 0.256 ppm DDD, 0.166 ppm DDT, 0.208 dieldrin, 2.241 ppm PCB 1254	mean residues in eggs	Female	Adult	29 eggs	east coast	Toxicity Factor Datasets

California Clapper Rail (Rallus longirostris ssp. obsoletus)

Citation:

Trace element and organochlorine concentrations in California clapper rail (Rallus longirostris obsoletus) eggs

Author(s)

Lonzarich, David G., Thomas E. Harvey and Jean E. Takekawa

Pages

147-153

Year

Wednesday, January 1, 1992 - 12:00

Volume

23
Chemical	Endpoint Value	Endpoint Description	Sex	Life Cycle Stage	Sample Size	Location	Type
CHLORDANE, DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR, MERCURY (elemental), POLYCHLORINATED BIPHENYLS, SELENIUM (elemental)	no effect	eggshell thickness compared to those of museum eggs from 1907 and 1936	Female	Adult	29 eggs	North and South San Francisco Bay	Toxicity Factor Datasets

Great Horned Owl (Bubo virginianus)

Citation:

The nesting, reproductive performance, and chlorinated hydrocarbon residues in the red-tailed hawk and great horned owl in south-central Montana

Author(s)

Seidensticker, John C. and Harry V. Reynolds

Pages

408-418

Year

Friday, January 1, 1971 - 12:00

Issue

4

Volume

83
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

Citation:

Effects of pesticides on owls in North America

Author(s)

Blus, Lawrence J.

Pages

198-206

Year

Monday, January 1, 1996 - 12:00

Issue

4

Volume

30
Chemical	Endpoint Value	Endpoint Description	Sex	Life Cycle Stage	Location	Type	Countries
ALDRIN, BRODIFACOUM, CARBOFURAN, CHLORDANE, DIELDRIN, ENDRIN, FAMPHUR, FENTHION, PHORATE, STRYCHNINE	review	summaries of mortality due to organochlorine, anticholinesterase, anticoagulant, strychnine pesticides	Not Reported	Not Reported		Toxicity Factor Datasets	CANADA, USA

Citation:

Productivity and survival of great horned owls exposed to dieldrin

Author(s)

Frank, Rosemary A. and R. Scott Lutz

Pages

331-339

Year

Friday, January 1, 1999 - 12:00

Volume

101
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
DIELDRIN	negative correlation	relationship between residue in plasma and survival	Not Reported	Juvenile	6 birds (contaminated sites), 10 birds (uncontaminated sites)	Rocky Mountain Arsenal National Wildlife Refuge	Toxicity Factor Datasets
DIELDRIN	no effect	daily and interval survival estimates on uncontaminated versus contaminated sites	Not Reported	Juvenile	14 birds on contaminated sites; 41 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

Mallard duck (Anas platyrhynchos)

Citation:

Dieldrin and DDT effects on reproduction and some hepatic mixed-function oxidases in the mallard duck

Author(s)

Davison, K.L. and J.L. Sell

Pages

302-314

Year

Tuesday, January 1, 1974 - 12:00

Volume

2
Chemical	Endpoint Value	Endpoint Description	Sex	Life Cycle Stage	Sample Size	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
DIELDRIN	0.3 ug/g dry wt. @ 0 ppm; 0.9 - 5.0 @ 1 ppm; 4.1 - 40.1 @ 5ppm; 6.1 - 78.5 @ 10 ppm	dieldrin concentrations in egg dry matter ranging from 0-14 d to 330 - 343 d sampling periods at 4 dietary doses	Female	Adult	18/dose	Toxicity Factor Datasets	Laboratory

Citation:

Fecundity and progeny growth following subacute insecticide ingestion by the mallard

Author(s)

Muller, H.D. and D.C. Lockman

Pages

239-241

Year

Saturday, January 1, 1972 - 12:00

Volume

51
Chemical	Endpoint Value	Endpoint Description	Sex	Life Cycle Stage	Sample Size	Location	Type	Lab
DIELDRIN	decrease	average % hatchability, compared to controls	Both Male and Female	Adult	5 trios (2F, 1M)/dose		Toxicity Factor Datasets	Laboratory
DIELDRIN	no effect	progeny growth (average body weights) at hatch to 6 wks of age	Both Male and Female	Juvenile	5 trios (2F, 1M adults)/dose		Toxicity Factor Datasets	Laboratory

Citation:

Effects of aqueous and dietary exposure of dieldrin on survival, growth and bioconcentration in mallard ducklings

Author(s)

Nebeker, Alan V., William L. Griffis, Thomas W. Stutzman, Gerald S. Schuytema, Lori A. Carey and Susan M. Scherer

Pages

687-699

Year

Wednesday, January 1, 1992 - 12:00

Volume

11
Chemical	Endpoint Value	Endpoint Description	Sex	Life Cycle Stage	Sample Size	Type	Age-Specific	Lab
DIELDRIN	no effect	body weight at end of experiment	Not Reported	Juvenile	12/dose	Toxicity Factor Datasets	1 d at initiation	Laboratory
DIELDRIN	no effect	no mortality observed	Not Reported	Juvenile	12/dose	Toxicity Factor Datasets	1 d at initiation	Laboratory
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
DIELDRIN	16.4 ug/g diet	24-d LOAEL based on growth impairment	Not Reported	Juvenile	10/dose	Toxicity Factor Datasets	1 - 25 d	Laboratory
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

Citation:

DDT thins shells of eggs from mallard ducks maintained on ad libitum or controlled-feeding regimes

Author(s)

Davison, K.L. and J.L. Sell

Pages

222-232

Year

Tuesday, January 1, 1974 - 12:00

Volume

2
Chemical	Endpoint Value	Endpoint Description	Sex	Life Cycle Stage	Sample Size	Location	Type	Lab
DIELDRIN	6% decrease @ 10 ppm	eggshell thickness	Female	Adult	18/dose		Toxicity Factor Datasets	Laboratory

Citation:

Dieldrin and p,p'-DDT effects on some microsomal enzymes of livers of chickens and mallard ducks

Author(s)

Davison, Kenneth L. and Jerry L. Sell

Pages

1198-1205

Year

Saturday, January 1, 1972 - 12:00

Volume

20
Chemical	Endpoint Value	Endpoint Description	Sex	Life Cycle Stage	Sample Size	Location	Type	Age-Specific	Lab
DIELDRIN	increase @ 10-20 ug/g	estradiol metabolism and cytochrome P450 concentration	Female	Adult	4/dose/sampling time		Toxicity Factor Datasets	90 d at initiation	Laboratory
DIELDRIN	no effect	body or liver weight at end of experiment	Female	Adult	4/dose/sampling time		Toxicity Factor Datasets	90 d at initiation	Laboratory

Citation:

Subacute dietary toxicities of dicrotophos and dieldrin in time-replicated trials with young ring-necked pheasants and mallards

Author(s)

Hill, E.F.

Pages

105-120

Publisher

American Society for Testing and Materials

Year

Thursday, January 1, 1981 - 12:00
Chemical	Endpoint Value	Endpoint Description	Sex	Life Cycle Stage	Sample Size	Location	Type	Age-Specific	Lab
DIELDRIN	155.8 (coeff. of variation = 16.0%)	5 day dietary LC50	Not Reported	Juvenile	8-10/dose		Toxicity Factor Datasets	5 days	Laboratory
DIELDRIN	200.7 (coeff. of variation 22.3%)	5 day dietary LC50	Not Reported	Juvenile	8-10/dose		Toxicity Factor Datasets	5 days	Laboratory

Citation:

Organochlorine accumulation by sentinel mallards at the Winston-Thomas sewage treatment plant, Bloomington, Indiana

Author(s)

Custer, T.W., D.W. Sparks, S.A. Sobiech, R.K. Hines, and M.J. Melancon

Pages

163-169

Year

Monday, January 1, 1996 - 12:00

Volume

30
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

Citation:

Toxic, neurochemical and behavioral effects of dieldrin exposure in mallard ducks

Author(s)

Sharma, R.P., D.S. Winn and J.B. Low

Pages

43-53

Year

Thursday, January 1, 1976 - 12:00

Issue

1

Volume

5
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

Mourning Dove (Zenaida macroura)

Citation:

Acute toxicity of certain insecticides to the bobwhite quail and mourning dove

Author(s)

Dahlen, James H.,and Arnold O. Haugen

Pages

477-481

Year

Friday, January 1, 1954 - 12:00

Issue

4

Volume

18
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

Peregrine Falcon (Falco peregrinus)

Citation:

Chlorinated hydrocarbons in peregrines and their prey species from northern Canada

Author(s)

Enderson, James H. and Daniel D. Berger

Pages

149-153

Year

Monday, January 1, 1968 - 12:00

Issue

2

Volume

70
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

Citation:

Peregrines and pesticides in Alaska

Author(s)

Cade, Tom J., Clayton M. White, and John R. Haugh

Pages

170-178

Year

Monday, January 1, 1968 - 12:00

Issue

2

Volume

70
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

Double-crested Cormorant (Phalacrocorax auritus)

Citation:

Double-crested cormorants of the Great Lakes: egg-laying parameters, reproductive failure, and contaminant residues in eggs, Lake Huron 1972-1973.

Author(s)

Weseloh, D. Vaughn, Stanley M. Teeple, and Michael Gilbertson

Pages

427-436

Year

Saturday, January 1, 1983 - 12:00

Volume

61
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

Loggerhead Shrike (Lanius ludovicianus)

Citation:

Loggerhead Shrike (Lanius ludovicianus)

Author(s)

Yosef, Reuven

Pages

1-27

Publisher

The Academy of Natural Sciences and The American Ornithologists' Union

Year

Monday, January 1, 1996 - 12:00

Issue

231
Chemical	Endpoint Value	Location	Type	Lab
DIELDRIN	review		Toxicity Factor Datasets	Laboratory