Literature DB >> 7726645

Dietary exposure of mink to carp from Saginaw Bay, Michigan. 1. Effects on reproduction and survival, and the potential risks to wild mink populations.

S N Heaton1, S J Bursian, J P Giesy, D E Tillitt, J A Render, P D Jones, D A Verbrugge, T J Kubiak, R J Aulerich.   

Abstract

Carp (Cyprinus carpio) collected from Saginaw Bay, Michigan, containing 8.4 mg total polychlorinated biphenyls (PCBs)/kg and 194 ng of 2,3,7,8-tetrachloro-dibenzo-p-dioxin equivalents (TEQs)/kg, were substituted for marine fish at levels of 0, 10, 20, or 40% in the diets of adult ranch mink (Mustela vison). The diets, containing 0.015, 0.72, 1.53, and 2.56 mg PCBs/kg diet, or 1.03, 19.41, 40.02, and 80.76 ng TEQs/kg diet, respectively, were fed to mink prior to and throughout the reproductive period to evaluate the effects of a naturally-contaminated prey species on their survival and reproductive performance. The total quantities of PCBs ingested by the mink fed 0, 10, 20, or 40% carp over the 85-day treatment period were 0.34, 13.2, 25.3, and 32.3 mg PCBs/mink. respectively. The corresponding quantities of TEQs ingested by the mink over the same treatment period were 23, 356, 661, and 1,019 ng TEQs/mink, respectively. Consumption of feed by mink was inversely proportional to the PCB and TEQ content of the diet. The diet containing Saginaw Bay carp caused impaired reproduction and/or reduced survival of the kits. Compared to controls, body weights of kits at birth were significantly reduced in the 20 and 40% carp groups, and kit body weights and survival in the 10 and 20% carp groups were significantly reduced at three and six weeks of age. The females fed 40% carp whelped the fewest number of kits, all of which were stillborn or died within 24 hours. Lowest observable adverse effect levels (LOAEL) of 0.134 mg PCBs/kg body weight/day or 3.6 ng TEQs/kg body weight/day for adult female mink were determined. The potential effects of exposure of wild mink to contaminated Great Lakes fish were assessed by calculating "maximum allowable daily intakes" and "hazard indices" based on total concentrations of PCB residues in several species of Great Lakes fish and mink toxicity data derived from the study.

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Year:  1995        PMID: 7726645     DOI: 10.1007/bf00213111

Source DB:  PubMed          Journal:  Arch Environ Contam Toxicol        ISSN: 0090-4341            Impact factor:   2.804


  36 in total

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Authors:  D J Hoffman; B A Rattner; L Sileo; D Docherty; T J Kubiak
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3.  Effects of feeding coho salmon and other Great Lakes fish on mink reproduction.

Authors:  R J Aulerich; R K Ringer; H L Seagran; W G Youatt
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4.  Determination of polychlorinated biphenyls in plant tissue.

Authors:  T R Schwartz; R G Lehmann
Journal:  Bull Environ Contam Toxicol       Date:  1982-06       Impact factor: 2.151

5.  In utero PCB/PCDF exposure: relation of developmental delay to dysmorphology and dose.

Authors:  M L Yu; C C Hsu; B C Gladen; W J Rogan
Journal:  Neurotoxicol Teratol       Date:  1991 Mar-Apr       Impact factor: 3.763

6.  Transfer of 2,4,5,2',4',5'-hexachlorobiphenyl and 2,2-bis-(p-chlorophenyl),1,1,1-trichloroethane (p,p'-DDT) from maternal to newborn and suckling rats.

Authors:  M Ando
Journal:  Arch Toxicol       Date:  1978-12-28       Impact factor: 5.153

7.  Feeding Great Lakes fish to mink: effects on mink and accumulation and elimination of PCBS by mink.

Authors:  T C Hornshaw; R J Aulerich; H E Johnson
Journal:  J Toxicol Environ Health       Date:  1983 Apr-Jun

8.  Toxicological manifestations of 2,4,5,2',4',5'-, 2,3,6,2',3',6'-, and 3,4,5,3',4',5'-hexachlorobiphenyl and Aroclor 1254 in mink.

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Journal:  J Toxicol Environ Health       Date:  1985

9.  Polychlorinated biphenyls (Aroclors 1016 and 1242): effects on survival and reproduction in mink and ferrets.

Authors:  M R Bleavins; R J Aulerich; R K Ringer
Journal:  Arch Environ Contam Toxicol       Date:  1980       Impact factor: 2.804

10.  Toxic interaction of specific polychlorinated biphenyls and 2,3,7,8-tetrachlorodibenzo-p-dioxin: increased incidence of cleft palate in mice.

Authors:  L S Birnbaum; H Weber; M W Harris; J C Lamb; J D McKinney
Journal:  Toxicol Appl Pharmacol       Date:  1985-02       Impact factor: 4.219

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Authors:  C M Arnett; J V Parales; J D Haddock
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2.  Organochlorine contaminants in wild mink from the lower Great Lakes basin, Canada, 1998-2006.

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Journal:  Environ Monit Assess       Date:  2017-08-19       Impact factor: 2.513

3.  Effects of dietary exposure to fumonisins from Fusarium moniliforme culture material (M-1325) on the reproductive performance of female mink.

Authors:  D C Powell; S J Bursian; C R Bush; J A Render; G E Rottinghaus; R J Aulerich
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4.  Twenty-five years after "Wingspread"- Environmental endocrine disruptors (EDCs) and human health.

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5.  Concentrations and profiles of polychlorinated biphenyls, -dibenzo-p-dioxins and -dibenzofurans in livers of mink from South Carolina and Louisiana, U.S.A.

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6.  Contaminants in fishes from Great Lakes-influenced sections and above dams of three Michigan rivers. II: Implications for health of mink.

Authors:  J P Giesy; D A Verbrugge; R A Othout; W W Bowerman; M A Mora; P D Jones; J L Newsted; C Vandervoort; S N Heaton; R J Aulerich
Journal:  Arch Environ Contam Toxicol       Date:  1994-08       Impact factor: 2.804

7.  Dietary exposure of mink to carp from Saginaw Bay, Michigan: 2. Hematology and liver pathology.

Authors:  S N Heaton; S J Bursian; J P Giesy; D E Tillitt; J A Render; P D Jones; D A Verbrugge; T J Kubiak; R J Aulerich
Journal:  Arch Environ Contam Toxicol       Date:  1995-10       Impact factor: 2.804

8.  Environmental contaminants in male river otters from Oregon and Washington, USA, 1994-1999.

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9.  Effects of Chinese domestic polychlorinated biphenyls (PCBs) on gonadal differentiation in Xenopus laevis.

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10.  Environmental contaminants in freshwater fish and their risk to piscivorous wildlife based on a national monitoring program.

Authors:  Jo Ellen Hinck; Christopher J Schmitt; Kimberly A Chojnacki; Donald E Tillitt
Journal:  Environ Monit Assess       Date:  2008-07-02       Impact factor: 3.307

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