Wan Michael T, Kuo Jen-ni, Pasternak John
Environmental Protection Branch, Environment Canada, Pacific and Yukon Region, 201-401 Burrard Street, Vancouver, BC, Canada.
J Environ Qual. 2005 Jun 7;34(4):1186-93. doi: 10.2134/jeq2004.0361. Print 2005 Jul-Aug.
Crop soils, ditch sediments, and water flowing from several farm areas to salmon tributary streams of the Fraser River in the Lower Fraser Valley (LFV) of British Columbia, Canada, were sampled in 2002-2003 to quantify for residues of an organochlorine cyclodiene pesticide, endosulfan (END = alpha-endosulfan + beta-endosulfan + endosulfan sulfate). Residues from historical use of other selected organochlorine pesticides, namely, cyclodienes (aldrin, alpha-chlordane, gamma-chlordane, dieldrin, endrin, endrin aldehyde, heptachlor, and heptachlor epoxide), hexachlorocyclohexanes [alpha-benzene-hexachloride (alpha-BHC), beta-BHC, delta-BHC, and gamma-BHC (lindane)], and DDT-related compounds (p,p-DDT, p,p-DDD, p,p-DDE, and methoxychlor) were also determined. Reference and background levels of these pesticides in ditches leading to fish streams were obtained from pristine watershed areas. Varying amounts of END residues were detected in soils (<0.02-5.60 mg kg(-1) dry wt.) and ditch sediments (<0.02-3.33 mg kg(-1) dry wt.) in mainly three of five farm areas sampled. Likewise, residues (excluding END) of other selected organochlorine compounds such as aldrin, BHC, chlordane, endrin, p,p-DDT, methoxychlor, and their respective major transformation products (endosulfan sulfate, dieldrin, endrin aldehyde, heptachlor, heptachlor epoxide, p,p-DDD, and p,p-DDE) were found in crop soils (<0.02-16.2 mg kg(-1) dry wt.) and sediments (<0.02-9.73 mg kg(-1) dry wt.). Most of these pesticides (END: <0.01-1.86 microg L(-1); other selected organochlorine pesticides: <0.0.1-1.50 microg L(-1)) were also found in ditch water leading to salmon streams in several farms. The END levels of crop soils from the same LFV study farms in 1994 and 2003 indicated an estimated decline of 22% to 1.35 mg kg(-1) dry wt. during that period. This reduction was probably due to the increasing use of alternate pesticides (e.g., organophosphorus compounds). Some possible biological implications of these pesticide residues on nontarget organisms in the LFV are discussed.
2002年至2003年期间,对加拿大不列颠哥伦比亚省低陆平原(LFV)弗雷泽河鲑鱼支流附近几个农场区域的农田土壤、沟渠沉积物以及从这些农场区域流入河流的水进行了采样,以量化有机氯环二烯类杀虫剂硫丹(END = α-硫丹 + β-硫丹 + 硫丹硫酸盐)的残留量。还测定了其他选定有机氯农药的历史使用残留量,即环二烯类(艾氏剂、α-氯丹、γ-氯丹、狄氏剂、异狄氏剂、异狄氏剂醛、七氯和七氯环氧化物)、六氯环己烷[α-六六六(α-BHC)、β-BHC、δ-BHC和γ-六六六(林丹)]以及滴滴涕相关化合物(p,p-DDT、p,p-DDD、p,p-DDE和甲氧滴滴涕)。从原始流域区域获取了通向鱼类溪流的沟渠中这些农药的参考水平和背景水平。在采样的五个农场区域中的三个区域,在土壤(<0.02 - 5.60 mg kg⁻¹干重)和沟渠沉积物(<0.02 - 3.33 mg kg⁻¹干重)中检测到了不同数量的硫丹残留。同样,在农田土壤(<0.02 - 16.2 mg kg⁻¹干重)和沉积物(<0.02 - 9.73 mg kg⁻¹干重)中发现了其他选定有机氯化合物如艾氏剂、六六六、氯丹、异狄氏剂、p,p-DDT、甲氧滴滴涕及其各自主要转化产物(硫丹硫酸盐、狄氏剂、异狄氏剂醛、七氯、七氯环氧化物、p,p-DDD和p,p-DDE)的残留。在几个农场通向鲑鱼溪流的沟渠水中也发现了这些农药中的大多数(硫丹:<0.01 - 1.86 μg L⁻¹;其他选定有机氯农药:<0.01 - 1.50 μg L⁻¹)。1994年和2003年来自同一低陆平原研究农场的农田土壤硫丹水平表明,在此期间估计下降了22%,降至1.35 mg kg⁻¹干重。这种减少可能是由于替代农药(如有机磷化合物)使用的增加。讨论了这些农药残留对低陆平原非靶标生物可能产生的一些生物学影响。