G. TeklitAmabye, Tesfakiros Semere
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引用次数: 2

摘要

采用静态生物测定法测定林丹(Gammalin 20)对多色异鳃鳗幼鱼的急性毒性。鱼的平均重量为2.5 g,总长度为8.6 cm。实验单元设6组,每碗含10条鱼,水容量为20升。对甘麦素20、有机氯农药进行蒸馏,浓缩收集有效成分林丹,制备原液。准备了0.02、0.04、0.06、0.08和0.10 ml/L的分级浓度,每个碗中有10只鱼暴露在不同浓度的环境中,并进行了不引入毒物的对照实验。实验组重复了三次。每天对暴露的鱼进行观察,并立即将死亡鱼取出,记录暴露24和48小时内的死亡率。24、48小时的LC50均为0.06 ml/L。将得到的结果转化为概率分析,并将其与暴露24和48小时期间林丹的分级浓度绘制。24小时和48小时的R2分别为0.76和0.80,表明林丹与死亡率有较强的相关性。水质变化范围为pH: 7.80 ~ 8.46,温度:28.39 ~ 28.42℃,DO: 5.06 ~ 5.17 mg/L,电导率:462.00 ~ 482.00µS/cm, TDS: 231.00 ~ 241.00 mg/L。虽然水质参数随着林丹浓度的增加而增加,但它在最大允许水平内,对鱼没有任何影响,鱼的死亡是由于林丹的潜在毒性。建议Gammalin 20在水生环境中毒性和持久性很强,应大力劝阻使用。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Bioassay of Lindane (Gamalin 20) to Hetrobrancus bidorsalis Juveniles
The study was carried out to determine the acute toxicity of lindane (Gammalin 20) to Hetrobranchus bidorsalis juveniles using static bioassays. The mean weight and total length of the fish samples were 2.5 g and 8.6 cm respectively. Six groups of the experimental units were set up containing 10 fish individuals in each bowl with 20 litres water capacity. The Gammalin 20, organo chlorine pesticide was distillated and the active ingredient lindane was condensed and collected and the stock solution was prepared. Graded concentration of 0.02, 0.04, 0.06, 0.08 and 0.10 ml/L were prepared and the fish of 10 individuals in each of the bowls were exposed to the different concentration with a control experiment where the toxicant was not introduced. The experimental set was replicated three times. The exposed fish were observed daily and death ones were removed immediately and mortality was recorded for 24 and 48 hours exposure period. The LC50 was determined to be 0.06 ml/L for the 24 and 48 hours exposure period. The obtained result was transformed to probit analysis which was plotted against the graded concentration of lindane for the 24 and 48 hours exposure period. The R2 values of 0.76 and 0.80 were obtained for the 24 and 48 hours respectively indicating a strong relationship of lindane with mortality. The result of the water quality varied from pH: 7, 80-8.46, temperature: 28.39-28.42°C DO: 5.06-5.17 mg/L, Conductivity: 462.00-482.00 µS/cm and TDS: 231.00-241.00 mg/L. Although the water quality parameters increase with increase in the lindane concentration yet it was within the maximum permissible level and did not have any effect on the fish and the death of the fish was due to the toxic potential of lindane. It was recommended that Gammalin 20 is very toxic and persistent in the aquatic environment and it use should be greatly discouraged.
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