Oloffs P C, Albright L J, Szeto S Y
J Environ Sci Health B. 1978;13(1):47-58. doi: 10.1080/03601237809372076.
A fresh-water lake, free from detectable pesticide residues before this study, was treated with a commercial formulation of technical chlordane. Water and sediment samples were analysed for chlordane residues 7, 24, 52, 279. and 421 days after treatment. Residues moved rapidly from the water to the lake bottom, supporting earlier results of a laboratory study with other organochlorines. In water, alpha- and gamma-chlordane concentrations remained proportional to total chlordane concentrations, as determined by total-peak area measurements of gas-liquid chromatogrammes. But in bottom sediments, alpha- and gamma-chlordane were more persistent than other constituents of technical chlordane, supporting recent evidence that quantification of technical chlordane residues on the basis of gamma-chlordane quantification only (or that of alpha- and gamma-chlordane only), can lead to incorrect results and that this method, although simple and fast, should no longer be recommended.
一个在本研究之前未检测出农药残留的淡水湖,用工业氯丹的商业配方进行了处理。在处理后的第7天、24天、52天、279天和421天,对水和沉积物样本进行了氯丹残留分析。残留物质迅速从水中转移到湖底,这证实了早期对其他有机氯进行实验室研究的结果。在水中,通过气液色谱图的总峰面积测量确定,α-氯丹和γ-氯丹的浓度与总氯丹浓度保持比例关系。但在底部沉积物中,α-氯丹和γ-氯丹比工业氯丹的其他成分更持久,这证实了最近的证据,即仅基于γ-氯丹(或仅基于α-氯丹和γ-氯丹)的定量来量化工业氯丹残留可能会导致错误结果,并且这种方法虽然简单快捷,但不应再被推荐。