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为探究拟除虫菊酯类农药对埋栖贝类的毒性作用,本文研究了甲氰菊酯、溴氰菊酯和氯氰菊酯对毛蚶(Scapharca subcrenata)幼贝和成贝的急性毒性效应及其物种敏感度分布。研究表明,甲氰菊酯、溴氰菊酯和氯氰菊酯对毛蚶幼贝的96 h半致死浓度(LC50)值分别为286.5、23.4和17.9 ng·mL-1,对成贝的96 h LC50值分别为3 931.9、709.5和737.7 ng·mL-1,说明相较成贝毛蚶幼贝对3种拟除虫菊酯类农药更敏感。多物种毒性数据比对发现,贝类对3种菊酯的敏感性低于已报道的鱼类和甲壳类,物种敏感度分布模型分析表明,基于保护95%水生生物种类的甲氰菊酯、溴氰菊酯和氯氰菊酯毒性阈值分别为0.20、0.01和0.02 ng·mL-1。研究结果可为我国近海环境中3种拟除虫菊酯类农药使用中的生态风险评估提供理论依据。
Abstract:The acute toxicity and species sensitivity distribution(SSD) of three synthetic pyrethroid insecticides(SPIs) including fenpropathrin, deltamethrin and cypermethrin on juveniles and adults of Scapharca subcrenata were studied. The results indicated that the 96 h halflethal concentration(LC50) of fenpropathrin, deltamethrin and cypermethrin was 286.5, 23.3 and 17.9 ng·mL-1 for juveniles, respectively, and the 96 h LC50 values for its adults was 3 931.9, 709.5 and 737.7 ng·mL-1, respectively. Juveniles were more sensitive to the tested SPIs than adults. Based on the SSD models, the toxicity thresholds of fenpropathrin, deltamethrin and cypermethrin for 95% protection of aquatic organisms was 0.20, 0.01 and 0.02 ng·mL-1, respectively. Ours results provided the basic data for ecological risk assessment of SPIs in coastal environment.
[1] 骆爱兰,余向阳,张存政,等.拟除虫菊酯类农药残留分析研究进展[J].江苏农业学报,2004,20(2):120-129.Luo A,Yu X,Zhang C,et al.Research progress of residue analysis for pyrethroids[J].Jiangsu J of Agr Sci,2004,20(2):120-129.
[2] 高钰一,沈美芳,宋红波,等.气相色谱法测定水产品中7种拟除虫菊酯的残留量[J].水产学报,2009,33(1):133-138.Gao Y,Shen M,Song H,et al.Determination of 7 pyrethroids residues in aquatic product by gas chromatography[J].Journal of Fisheries of China,2009,33(1):132-138.
[3] 赵李娜,赖子尼,李秀丽,等.珠江河口沉积物中拟除虫菊酯类农药污染及毒性评价[J].生态环境学报,2013,22(8):1408-1413.Zhao L,Lai Z,Li X,et al.Contamination and toxicity evaluation of pyrethroids in sediments of the Pearl River Estuary[J].Ecology and Environmental Sciences,2013,22(8):1408-1413.
[4] Tang W,Wang D,Wang J,et al.Pyrethroid pesticide residues in the global environment:An overview[J].Chemosphere,2018,191:990-1007.
[5] Zhong G,Tang J,Xie Z,et al.Selected current-use pesticides(CUPs) in coastal and offshore sediments of Bohai and Yellow Seas[J].Environ Sci Pollut Res,2015,22:1653-1661.
[6] 季芯羽,叶泰,袁敏,等.菊酯类农药代谢物分子印迹荧光传感器的制备及应用[J].分析测试学报,2019,38(12):1487-1492.Ji X Y,Ye T,Yuan M,et al.Preparation and application of a molecularly imprinted fluorescence sensor for pyrethroid pesticide metabolite[J].Journal of Instrumental Analysis,2019,38(12):1487-1492.
[7] Goedkoop W,Peterson M.The fate,distribution,and toxicity of Lindane in tests with Chironomus riparius:Effects of bioturbation and sediment organic matter content[J].Environmental Toxicology and Chemistry,2003,22:67-76.
[8] 陈波宇,郑斯瑞,牛希成,等.物种敏感度分布及其在生态毒理学中的应用[J].生态毒理报,2010,5(4):491-497.Chen Y,Zheng S,Niu X,et al.Species sensitivity distribution and its application in ecotoxicology[J].Ecology and Environmental Sciences,2010,5(4):491-497.
[9] Goldberg E D.The mussel watch concept[J].Environmental Monitoring and Assessment,1986,7(1):91-103.
[10] Jin J E,Ahn C B,Je J Y.Purification and characterization of antioxidant peptides from enzymatically hydrolyzed ark shell(Scapharca subcrenata)[J].Process Biochemistry,2018,72:170-176.
[11] Raimodno S,Vivian D N,Delos C,et al.Protectiveness of species sensitivity distribution hazard concentrations for acute toxicity used in endangered species risk assessment[J].Environmental Toxicology and Chemistry,2008,27(12):2599-2607.
[12] 国家环境保护总局.HJ/T153—2004新化学物质危害评估导则[S].北京:中华人民共和国环境保护部,2004.State Environmental Protection Administration.HJ/T153—2004 New Chemical Hazard Assessment Guidelines[S].Beijing:Ministry of Ecology and Environment of the People's Republic of China,2004.
[13] Sayeed I,Parvez S,Pandey S,et al.Oxidative stress biomarkers of exposure to deltamethrin in freshwater fish,Channa punctatus Bloch[J].Ecotoxicology and Environmental Safety,2003,56:295-301.
[14] 彭芳,王茜,王兰.溴氰菊酯对多刺裸腹溞急性毒性及解毒代谢的影响[J].水生生物学报,2013,37(3):530-534.Peng F,Wang X,Wang L.Effect of deltamethrin on acute toxicity and detoxification metabolism in water flea,Moina macrocopa[J].Acta Hydrobiologica Sinica,2013,37(3):530-534.
[15] 谭晓珍,吴垠,李韬,等.氯氰菊酯和氰戊菊酯对栉孔扇贝的急性毒性[J].大连水产学院学报,2005,20(3):203-207.Tan X Zh,Wu Y,Li T,et al.Acute toxicity of cypermethrin and fenvalerate to scallop(Chlamys farreri)[J].Journal of Dalian Fisheries University,2005,20(3):203-207.
[16] Singh P B,Singh V.Cypermethrin induced histological changes in gonadotrophic cells,liver,gonads,plasma levels of estradiol-17b and 11-ketotestosterone,and sperm motility in Heteropneustes fossilis(Bloch)[J].Chemosphere,2008,72(3):422-431.
[17] 赵玉琴,李丽娜,李建华.常见拟除虫菊酯和有机磷农药对鱼类的急性及其联合毒性研究[J].环境污染与防治,2008,11:53-57.Zhao Y Q,Li L N,Li J H.Study of acute and joint toxicity of common pyrethroid and organophosphate pesticides to fish[J].Environmental Pollution & Control,2008,11:53-57.
[18] 陈坚,胡一箫,许丰瑞,等.氨氮和硫化物对文蛤幼体及成体的急性毒性试验[J].现代农业科技,2010,3:324-325+331.Chen J,Hu Y X,Xu F R,et al.Acute toxicity experiments of ammonia-N and sulfide to the juveniles and adults of Meretrix meretrix[J].Modern Agricultural Science and Technology,2010,3:324-325+331.
[19] 徐瑞祥,陈亚华.应用物种敏感性分布评估有机磷农药对淡水生物的急性生态风险[J].湖泊科学,2012,24(6):811-821.Xu R,Chen Y.Assessing acute ecological risks of organophosphorus pesticides to freshwater organisms by species sensitivity distributions[J].J Lake Sci,2012,24(6):811-821.
基本信息:
DOI:10.16441/j.cnki.hdxb.20210007
中图分类号:X171.5
引用信息:
[1]孙策,苗晶晶,李莉,等.三种拟除虫菊酯对毛蚶的急性毒性效应及其物种敏感度分布研究[J],2021,51(12):133-140.DOI:10.16441/j.cnki.hdxb.20210007.
基金信息:
国家重点研究发展计划项目(2019YFD0901704);; 山东省现代农业产业技术体系建设专项资金项目(SDAIT-14-04)资助~~
2021-01-10
2021
2021-03-27
2021-06-18
2021
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