Frew John A, Grue Christian E
Washington Cooperative Fish and Wildlife Research Unit, School of Aquatic and Fishery Sciences, University of Washington, MS 355020, 1122 NE Boat St, Seattle, WA 98195, USA.
J Environ Monit. 2012 Mar;14(3):1024-34. doi: 10.1039/c2em10866f. Epub 2012 Feb 14.
The neonicotinoid insecticide imidacloprid (IMI) has been proposed as an alternative to carbaryl for controlling indigenous burrowing shrimp on commercial oyster beds in Willapa Bay and Grays Harbor, Washington. A focus of concern over the use of this insecticide in an aquatic environment is the potential for adverse effects from exposure to non-target species residing in the Bay, such as juvenile Chinook (Oncorhynchus tshawytscha) and cutthroat trout (O. clarki). Federal registration and State permiting approval for the use of IMI will require confirmation that the compound does not adversely impact these salmonids following field applications. This will necessitate an environmental monitoring program for evaluating exposure in salmonids following the treatment of beds. Quantification of IMI residues in tissue can be used for determining salmonid exposure to the insecticide. Refinement of an existing protocol using liquid-chromatography mass spectrometry (LC-MS) detection would provide the low limits of quantification, given the relatively small tissue sample sizes, necessary for determining exposure in individual fish. Such an approach would not be viable for the environmental monitoring effort in Willapa Bay and Grays Harbor due to the high costs associated with running multiple analyses, however. A new sample preparation protocol was developed for use with a commercially available enzyme-linked immunosorbent assay (ELISA) for the quantification of IMI, thereby providing a low-cost alternative to LC-MS for environmental monitoring in Willapa Bay and Grays Harbor. Extraction of the analyte from the salmonid brain tissue was achieved by Dounce homogenization in 4.0 mL of 20.0 mM Triton X-100, followed by a 6 h incubation at 50-55 °C. Centrifugal ultrafiltration and reversed phase solid phase extraction were used for sample cleanup. The limit of quantification for an average 77.0 mg whole brain sample was calculated at 18.2 μg kg(-1) (ppb) with an average recovery of 79%. This relatively low limit of quantification allows for the analysis of individual fish. Using controlled laboratory studies, a curvelinear relationship was found between the measured IMI residue concentrations in brain tissue and exposure concentrations in seawater. Additonally, a range of IMI brain residue concentrations was associated with an overt effect; illustrating the utility of the IMI tissue residue quantification approach for linking exposure with defined effects.
新烟碱类杀虫剂吡虫啉(IMI)已被提议作为西维因的替代品,用于控制华盛顿州威拉帕湾和格雷斯港商业牡蛎床上的本地穴居虾。在水生环境中使用这种杀虫剂引发的一个关注焦点是,接触海湾中存在的非目标物种(如奇努克鲑幼鱼(Oncorhynchus tshawytscha)和割喉鳟(O. clarki))可能产生的不利影响。联邦对IMI使用的注册和州许可批准将需要确认该化合物在田间施用后不会对这些鲑科鱼类产生不利影响。这将需要一个环境监测计划,以评估在处理牡蛎床后鲑科鱼类的接触情况。组织中IMI残留量的定量可用于确定鲑科鱼类对该杀虫剂的接触情况。鉴于确定单个鱼类接触情况所需的组织样本量相对较小,使用液相色谱质谱(LC-MS)检测对现有方案进行改进将提供低定量限。然而,由于进行多次分析的成本高昂,这种方法对于威拉帕湾和格雷斯港的环境监测工作不可行。开发了一种新的样品制备方案,用于与市售的酶联免疫吸附测定(ELISA)一起定量IMI,从而为威拉帕湾和格雷斯港的环境监测提供了一种低成本的LC-MS替代方法。通过在4.0 mL 20.0 mM Triton X-100中进行杜恩斯匀浆从鲑科鱼类脑组织中提取分析物,然后在50 - 55°C下孵育6小时。使用离心超滤和反相固相萃取进行样品净化。平均77.0 mg全脑样品的定量限计算为18.2 μg kg⁻¹(ppb),平均回收率为79%。这个相对较低的定量限允许对单个鱼类进行分析。通过对照实验室研究,发现脑组织中测得的IMI残留浓度与海水中的接触浓度之间存在曲线关系。此外,一系列IMI脑残留浓度与明显效应相关;说明了IMI组织残留量定量方法在将接触与明确效应联系起来方面的实用性。