Lund SA, Fulton MH, Key PB
NOAA National Ocean Service, Center for Coastal Environmental Health and Biomolecular Research at Charleston, 219 Ft. Johnson Road, Charleston, SC, USA
Aquat Toxicol. 2000 Mar 1;48(2-3):127-134. doi: 10.1016/s0166-445x(99)00053-3.
Grass shrimp, Palaemonetes pugio, are common inhabitants of salt marshes along the Atlantic and Gulf coasts of North America. Grass shrimp embryos are brooded externally on the abdomen of adult females for about 2 weeks prior to hatching. In South Carolina, the spring spawning period for grass shrimp coincides with the period of peak pesticide application on crops grown along the South Carolina coast. Thus, grass shrimp of all developmental stages are at risk of exposure to pesticides present in nonpoint source agricultural runoff. Organophosphate (OP) insecticides are commonly applied agricultural chemicals which produce toxicity by inhibiting the nervous system enzyme, acetylcholinesterase (AChE). The purpose of this study was to examine the development of AChE activity in grass shrimp embryos and to assess their sensitivity to OP-induced AChE inhibition. Embryos were exposed for 24 h to either chlorpyrifos or malathion. All exposure concentrations were nominal and ranged from 0 to 2.00 µg l(-1) for chlorpyrifos and from 0 to 120.00 µg l(-1) for malathion. Quantifiable levels of AChE activity first appeared at Stage V of development and increased as embryonic development progressed. AChE inhibition by the OPs was assessed in Stage VI and Stage VII embryos. Both stages of embryos were more sensitive to chlorpyrifos than malathion. The 24-h Effective Concentration (EC(50)) values for chlorpyrifos were 0.49 µg l(-1) (95% C.I.=0.33-0.77 µg l(-1)) and 0.36 µg l(-1) (95% C.I.=0.33-0.38 µg l(-1)) for Stage VI and Stage VII embryos, respectively. In comparison, malathion 24-h EC(50) values were 55.53 µg l(-1) (95% C.I.=22.08-80.73 µg l(-1)) for Stage VI embryos and 29.93 µg l(-1) (95% C.I.=25.22-44.22 µg l(-1)) for Stage VII embryos. For both OPs, there were no significant differences in the EC(50) values calculated for Stage VI and Stage VII embryos; however, AChE inhibition was significantly (P</=0.05) greater in Stage VII embryos at the two highest exposure concentrations for each insecticide. A comparison of the results of these embryo tests with those found for adult and larval toxicity tests indicated that embryos were at least as sensitive to both the OPs as larval and adult grass shrimp. Embryo bioassays provide a number of important advantages over traditional laboratory toxicity tests including reduced laboratory space requirements, large numbers of embryos from a few ovigerous females, and small volumes of waste.
草虾(Palaemonetes pugio)是北美大西洋和墨西哥湾沿岸盐沼的常见居民。草虾胚胎在成年雌性腹部外孵化约2周后孵化。在南卡罗来纳州,草虾的春季产卵期与南卡罗来纳州海岸沿线作物上农药施用高峰期相吻合。因此,所有发育阶段的草虾都面临着接触非点源农业径流中农药的风险。有机磷(OP)杀虫剂是常用的农用化学品,通过抑制神经系统酶乙酰胆碱酯酶(AChE)产生毒性。本研究的目的是检测草虾胚胎中AChE活性的发育情况,并评估它们对OP诱导的AChE抑制的敏感性。将胚胎暴露于毒死蜱或马拉硫磷24小时。所有暴露浓度均为名义浓度,毒死蜱的浓度范围为0至2.00微克/升,马拉硫磷的浓度范围为0至120.00微克/升。可量化的AChE活性水平在发育的第五阶段首次出现,并随着胚胎发育的进行而增加。在第六和第七阶段的胚胎中评估了OP对AChE的抑制作用。两个阶段的胚胎对毒死蜱的敏感性均高于马拉硫磷。毒死蜱对第六阶段和第七阶段胚胎的24小时有效浓度(EC50)值分别为0.49微克/升(95%置信区间=0.33-0.77微克/升)和0.36微克/升(95%置信区间=0.33-0.38微克/升)。相比之下,马拉硫磷对第六阶段胚胎的24小时EC50值为55.53微克/升(95%置信区间=22.08-80.73微克/升),对第七阶段胚胎的24小时EC50值为29.93微克/升(95%置信区间=25.22-44.22微克/升)。对于两种OP,第六阶段和第七阶段胚胎计算出的EC50值没有显著差异;然而,在每种杀虫剂的两个最高暴露浓度下,第七阶段胚胎中的AChE抑制作用显著(P≤0.05)更大。将这些胚胎试验的结果与成年和幼虫毒性试验的结果进行比较表明,胚胎对两种OP的敏感性至少与幼虫和成年草虾一样。与传统的实验室毒性试验相比,胚胎生物测定具有许多重要优势,包括减少实验室空间需求、从少数抱卵雌性获得大量胚胎以及少量废物。