Chlordane components and metabolites in seven species of Arctic seabirds from the Northwater Polynya: relationships with stable isotopes of nitrogen and enantiomeric fractions of chiral components

被引:77
作者
Fisk, AT
Moisey, J
Hobson, KA
Karnovsky, NJ
Norstrom, RJ
机构
[1] Environm Canada, Natl Wildlife Res Ctr, Hull, PQ K1A 0H3, Canada
[2] Carleton Univ, Dept Chem, Ottawa, ON K1S 5B6, Canada
[3] Univ Saskatchewan, Dept Biol, Saskatoon, SK S7N 0W0, Canada
[4] Prairie & No Wildlife Res Ctr, CWS, Saskatoon, SK S7N 0X4, Canada
[5] Univ Calif Irvine, Dept Ecol & Evolutionary Biol, Irvine, CA 92697 USA
基金
美国国家科学基金会;
关键词
bioaccumulation; biotransformation; nitrogen-15; chiral compounds;
D O I
10.1016/S0269-7491(00)00153-6
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
The Northwater Polynya (NOW) is a large area of year-round open water found in the high Arctic between Ellesmere Island and Greenland, NOW has high biological productivity compared with other arctic marine areas, and supports large populations of several seabird species. Seven species of seabirds, dovekie (Alle alle, DOVE), thick-billed murre (Uria lomvia, TBMU), black guillemot (Cepphus grylle, BLGU), black-legged kittiwake (Rissa tridactyla, BLKI), ivory gull (Pagophila eburnea, IVGU), glaucous gull (Larus hyperboreus, GLGU) and northern fulmar (Fulmaris glacialis, NOFU) were collected in May and June 1998 to determine chlordane concentrations in liver and fat and to examine species differences, relationships with stable isotopes of nitrogen, and enantiomeric fractions (EFs) of chiral components. Sigma CHLOR concentrations varied over an order of magnitude among species, from a low of 176+/-19 ng/g (lipid corrected) in TMBU liver to a high of 3190+/-656 ng/g (lipid corrected) in NOFU liver. Lipid-corrected concentrations of chlordane did not vary between sex for any species or between fat and liver except for the DOVE, that had fat concentrations that were significantly greater than the liver. delta N-15 values described a significant percentage of the variability of concentrations for most chlordane components, although less than what has been reported for whole food chains. Slopes of delta N-15 versus concentration of chlordane components and Sigma CHLOR were similar with the exception of those which were metabolized (irans-chlordane) or formed through biotransformation (oxychlordane). The relative proportions of chlordane components in sea birds were related to phylogeny; the procellariid (NOFU) had the greatest percentage of oxychlordane (>70%), followed by the larids (BLKI, IVGU and GLGU; 40-50%) and the alcids (DOVE and BLGU; 10-20%). The exception was TBMU, an alcid, where oxychlordane made up > 40% of its chlordane. EFs of chiral components failed to predict concentration or trophic level, but did identify biotransformation differences between species and chlordane components. TBMU appeared to have a greater capacity to metabolize and eliminate chlordane, based on high proportions of oxychlordane, the highest EFs for oxychlordane and heptachlor epoxide, and a delta N-15-Sigma CHLOR value which was well below the relationships developed for all seabird species. (C) 2001 Elsevier Science Ltd. All rights reserved.
引用
收藏
页码:225 / 238
页数:14
相关论文
共 45 条
  • [1] [Anonymous], 1998, AMAP ASS REP ARCT PO
  • [2] Baird Pat Herron, 1994, Birds of North America, V92, P1
  • [3] Using enantiomers to trace pesticide emissions
    Bidleman, TF
    Falconer, RL
    [J]. ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1999, 33 (09) : 206A - 209A
  • [4] A STRUCTURE ACTIVITY RELATIONSHIP (SAR) APPROACH TOWARDS METABOLISM OF PCBS IN MARINE ANIMALS FROM DIFFERENT TROPHIC LEVELS
    BOON, JP
    EIJGENRAAM, F
    EVERAARTS, JM
    DUINKER, JC
    [J]. MARINE ENVIRONMENTAL RESEARCH, 1989, 27 (3-4) : 159 - 176
  • [5] BRANE BM, 1999, TECHNICAL REPORT SER, V326
  • [6] BRAUNE BM, 1989, ENVIRON TOXICOL CHEM, V8, P957, DOI [10.1897/1552-8618(1989)8[957:DOOCIH]2.0.CO
  • [7] 2, 10.1002/etc.5620081015]
  • [8] BRAUNE BM, 1994, ENV STUDIES, V72, P305
  • [9] BRAUNE BM, 1994, ENV STUDIES, V72, P312
  • [10] BROMAN D, 1992, ENVIRON TOXICOL CHEM, V11, P331