Barry M J, Logan D C, Ahokas J T, Holdway D A
Key Centre for Applied and Nutritional Toxicology, RMIT-University, Melbourne, Victoria, Australia.
Ecotoxicol Environ Saf. 1995 Dec;32(3):273-9. doi: 10.1006/eesa.1995.1114.
The effects of algal concentration (Selanastrum capricornatum) on the toxicity of the organochlorine pesticide endosulfan and the synthetic pyrethroid esfenvalerate to Daphnia carinata was investigated. The study progressed through four stages: (1) A dose-response experiment on the effects of endosulfan and esfenvalerate on the survival, growth, and reproduction of D. carinata at a single nonlimiting food level. (2) An experiment to investigate the effects of five different food concentrations on survival, growth, and reproduction of D. carinata at sublethal concentrations of endosulfan and esfenvalerate compared with nonexposed controls. (3) An experiment to investigate the effects of route of exposure (water, food-borne, or water+food-borne exposure) on the toxicity of endosulfan to D. carinata. (4) An experiment to investigate the effects of algal concentration on persistence of endosulfan in the water column and on the relative toxicity of the alpha and beta isomers and of endosulfan sulfate to D. carinata. In the first experiment all daphnids exposed to 500 ng/liter esfenvalerate died within 3 days. There was a significant effect of esfenvalerate on reproduction at 50 ng/liter by the second brood. Endosulfan did not cause significant mortality to daphnids but brood size was reduced at 320 micrograms/liter. In the second experiment the toxicity of esfenvalerate increased significantly with decreasing food concentration. In contrast, the toxicity of endosulfan to D. carinata was greatest at the higher food concentrations. Direct water-borne exposure to endosulfan was the most toxic route of exposure and the presence of algae decreased toxicity of this pesticide. The total amount of endosulfan (alpha + beta + endosulfan sulfate) persisting in the water column after 24 hr was greater at high food levels, suggesting that this may be one mechanism for increased toxicity at high food concentrations. The 48-hr LC50s of technical endosulfan, endosulfan sulfate, alpha-endosulfan, beta-endosulfan, and a 50:50 mixture of alpha, and beta endosulfan were 478, 756, 249, 205, and 234 micrograms/liter, respectively.
研究了藻类浓度(羊角月牙藻)对有机氯农药硫丹及拟除虫菊酯农药乙氰菊酯对隆线溞毒性的影响。该研究分四个阶段进行:(1)在单一非限制性食物水平下,进行硫丹和乙氰菊酯对隆线溞存活、生长和繁殖影响的剂量反应实验。(2)与未暴露对照组相比,研究在硫丹和乙氰菊酯亚致死浓度下,五种不同食物浓度对隆线溞存活、生长和繁殖的影响。(3)研究暴露途径(水体、食物携带或水体 + 食物携带暴露)对硫丹对隆线溞毒性的影响。(4)研究藻类浓度对硫丹在水柱中持久性以及硫丹α和β异构体及硫丹硫酸酯对隆线溞相对毒性的影响。在第一个实验中,所有暴露于500纳克/升乙氰菊酯的溞在3天内死亡。到第二代时,50纳克/升的乙氰菊酯对繁殖有显著影响(效果)。硫丹未导致溞显著死亡,但在320微克/升时窝卵数减少。在第二个实验中,乙氰菊酯的毒性随食物浓度降低而显著增加。相反,硫丹对隆线溞的毒性在较高食物浓度时最大。直接水体暴露于硫丹是最具毒性的暴露途径,藻类的存在降低了该农药的毒性。在高食物水平下,24小时后水柱中残留的硫丹总量(α + β + 硫丹硫酸酯)更大,这表明这可能是高食物浓度下毒性增加的一种机制。工业用硫丹、硫丹硫酸酯、α - 硫丹﹑β - 硫丹以及α和β硫丹50:50混合物的48小时半数致死浓度分别为478、756、249、205和234微克/升。