Literature DB >> 8781073

Residues of organochlorines in mallards and blue-winged teal collected in Colombia and Wisconsin, 1984-1989.

J E Botero1, M W Meyer, S S Hurley, D H Rusch.   

Abstract

We compared the seasonal concentrations of 12 organochlorine (OC) compounds in samples of breast muscle, associated skin, and subcutaneous fat of blue-winged teal (Anas discors) collected in Ciénaga Grande de Santa Marta, Colombia (1987-1988), and of mallards (Anas platyrhynchos) and blue-winged teal collected in Wisconsin (1984-1989). Although these species have similar feeding habits and overlapping breeding distributions, their winter ranges differ markedly. Most blue-winged teal winter in the Neotropics, whereas most mallards remain in the temperate regions of North America. A seasonal comparison of OC exposure in these species may help determine the geographic origins of contamination. All examined OCs were found to be below concentrations known to affect reproduction in waterfowl. DDE was most often detected in blue-winged teal and PCBs, in mallards. DDE exposure may have predominantly occurred outside of Wisconsin. The DDE concentration in blue-winged teal samples collected in Wisconsin in the spring (GM=0.406 microg/g) were greater (P<0.001) than in the fall (GM=0. 033 microg/g) and greater than the concentrations in mallard samples from the spring (GM=0.058 microg/g; P<0.001). Ciénaga Grande, however, was not a source of DDE contamination. The DDE concentrations in blue-winged teal samples from Ciénaga Grande did not differ between the spring (GM=0.037 microg/g) and the fall (GM=0. 039 microg/g) and were lower (P<0.001) than the concentration in blue-winged teal samples from Wisconsin in the spring. In contrast, PCB contamination seemed to have occurred in Wisconsin and affected mostly mallards. PCBs were not detected in the samples from Colombia and were detected in only five (8.3%) of the blue-winged teal samples from Wisconsin (GM=0.025 microg/g), however, those compounds were detected in 47% of the mallard samples collected in Wisconsin (GM=0.272 microg/g). DDE and PCB concentrations were greater (P=0.0) in mallard samples collected from wetlands adjacent to Lake Michigan than in samples from inland wetlands.

Entities:  

Mesh:

Substances:

Year:  1996        PMID: 8781073     DOI: 10.1007/bf00212370

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


  6 in total

1.  Seasonal and geographical variation of organochlorine residues in birds from northwest Mexico.

Authors:  M A Mora; D W Anderson
Journal:  Arch Environ Contam Toxicol       Date:  1991-11       Impact factor: 2.804

2.  Wildlife in some areas of New Mexico and Texas accumulate elevated DDE residues, 1983.

Authors:  D H White; A J Krynitsky
Journal:  Arch Environ Contam Toxicol       Date:  1986-02       Impact factor: 2.804

3.  Persistence of DDT and metabolites in wildlife from Washington State orchards.

Authors:  L J Blus; C J Henny; C J Stafford; R A Grove
Journal:  Arch Environ Contam Toxicol       Date:  1987-07       Impact factor: 2.804

4.  DDE in birds: lethal residues and loss rates.

Authors:  W H Stickel; L F Stickel; R A Dyrland; D L Hughes
Journal:  Arch Environ Contam Toxicol       Date:  1984-01       Impact factor: 2.804

5.  Microcontaminants and reproductive impairment of the Forster's tern on Green Bay, Lake Michigan--1983.

Authors:  T J Kubiak; H J Harris; L M Smith; T R Schwartz; D L Stalling; J A Trick; L Sileo; D E Docherty; T C Erdman
Journal:  Arch Environ Contam Toxicol       Date:  1989-09       Impact factor: 2.804

6.  Productivity, diet, and environmental contaminants in bald eagles nesting near the Wisconsin shoreline of Lake Superior.

Authors:  K D Kozie; R K Anderson
Journal:  Arch Environ Contam Toxicol       Date:  1991-01       Impact factor: 2.804

  6 in total

北京卡尤迪生物科技股份有限公司 © 2022-2023.