McKinney Melissa A, De Guise Sylvain, Martineau Daniel, Béland Pierre, Lebeuf Michel, Letcher Robert J
Great Lakes Institute for Environmental Research, University of Windsor, Windsor, Ontario N9B 3P4, Canada.
Environ Toxicol Chem. 2006 May;25(5):1246-57. doi: 10.1897/05-284r.1.
Contaminants described as organochlorines (OCs; e.g., polychlorinated biphenyls [PCBs]) are present in tissues of marine mammals, including beluga whales (Delphinapterus leucas), but the complexity of contaminant exposure often is not fully known. The PCBs, OC pesticides, polybrominated diphenyl ether (PBDE) flame retardants, methylsulfonyl (MeSO2)- and hydroxy (OH)-PCB metabolites, and OH-PBDEs and methoxylated (MeO)-PBDEs were determined in the liver of beluga whales from two Canadian populations: the St. Lawrence Estuary (SLB; n=6), and western Hudson Bay in the Canadian Arctic (CAB; n=11). The sigmaPCB, sigmaDDT, and sigmaPBDE concentrations were higher (p < 0.05) in SLB versus CAB. Of 18 detectable OH-PCBs in SLB (mainly 4-OH-CB107, 4-OH-CB112, and 4'-OH-CB120), only 4'-OH-CB120 was found in CAB. The sigmaOH-PCB concentrations were less than 0.2% of the sigmaPCBs in both populations but were higher (p < 0.05) in SLB (65 +/- 22 ng/g lipid wt) than in CAB (3.1 +/- 0.5 ng/g lipid wt). The sigmaMeSO2-PCB concentrations were higher in SLB (3801 +/- 1322 ng/g lipid wt) relative to CAB (77 +/- 23 ng/g lipid wt) and were 11 and 4%, respectively, of the sigmaPCB concentrations. Of the 15 OH-PBDEs, only two congeners were detectable, but not quantifiable (notably 2'-OH-BDE 68 and 6-OH-BDE 47), in animals from both populations. Of the 15 MeO-PBDEs, 4'-MeO-BDE 17 and 6-MeO-BDE 47 in the SLB (n=2) and 2'-MeO-BDE 68 and 6-MeO-BDE 47 in the CAB (n=2) had concentrations from 20 to 100 ng/g lipid weight. The OH-PBDEs and MeO-PBDEs most likely are of natural origin and accumulated in beluga whales, whereas the OH-PCBs and MeSO2-PCBs are metabolites derived from accumulated PCBs. Canadian beluga whale liver contains previously unidentified organohalogen contaminants and metabolites and, thus, a complexity of contaminant exposure that may be impacting the health of Canadian beluga whale populations.
被描述为有机氯(OCs;例如多氯联苯[PCBs])的污染物存在于海洋哺乳动物的组织中,包括白鲸(白鲸属),但污染物暴露的复杂性往往并不完全清楚。对来自加拿大两个种群的白鲸肝脏中的多氯联苯、有机氯农药、多溴二苯醚(PBDE)阻燃剂、甲基磺酰基(MeSO2)和羟基(OH)多氯联苯代谢物以及羟基多溴二苯醚和甲氧基化(MeO)多溴二苯醚进行了测定:圣劳伦斯河口(SLB;n = 6)和加拿大北极地区的哈德逊湾西部(CAB;n = 11)。与CAB相比,SLB中的总多氯联苯、总滴滴涕和总多溴二苯醚浓度更高(p < 0.05)。在SLB中可检测到的18种羟基多氯联苯(主要是4-OH-CB107、4-OH-CB112和4'-OH-CB120)中,CAB中仅发现了4'-OH-CB120。两个种群中总羟基多氯联苯浓度均不到总多氯联苯浓度的0.2%,但SLB(65±22 ng/g脂质重量)中的浓度高于CAB(3.1±0.5 ng/g脂质重量)(p < 0.05)。相对于CAB(77±23 ng/g脂质重量),SLB中的总甲基磺酰基多氯联苯浓度更高(3801±1322 ng/g脂质重量),分别占总多氯联苯浓度的11%和4%。在15种羟基多溴二苯醚中,两个种群的动物中仅检测到两种同系物,但无法定量(特别是2'-OH-BDE 68和6-OH-BDE 47)。在15种甲氧基化多溴二苯醚中,SLB(n = 2)中的4'-MeO-BDE 17和6-MeO-BDE 47以及CAB(n = 二)中的2'-MeO-BDE 68和6-MeO-BDE 47的浓度为20至100 ng/g脂质重量。羟基多溴二苯醚和甲氧基化多溴二苯醚很可能源于天然并在白鲸体内蓄积,而羟基多氯联苯和甲基磺酰基多氯联苯是多氯联苯蓄积产生的代谢物。加拿大白鲸肝脏含有此前未识别的有机卤素污染物和代谢物,因此存在污染物暴露的复杂性,这可能正在影响加拿大白鲸种群的健康。