Applicability of Gobiocypris rarus in Fish Embryo Acute Toxicity Test
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摘要: 为了验证我国本土鱼种稀有鮈鲫(Gobiocypris rarus)在鱼类胚胎急性毒性试验的适用性,评价其在鱼类替代试验中的应用潜力,选取3,4-二氯苯胺和五水硫酸铜,按照《OECD化学品测试准则No.236鱼类胚胎急性毒性试验》,分别开展6次稀有鮈鲫胚胎急性毒性试验,通过评价试验结果的重复性,验证稀有鮈鲫是否适用于鱼类胚胎急性毒性试验.结果表明:3,4-二氯苯胺和五水硫酸铜对稀有鮈鲫胚胎的96 h LC50(96 h半数致死浓度)平均值(x)分别为12.8和1.76 mg/L,标准差(s)分别为1.70和0.197 mg/L;变异系数(CV)分别为13.3%和11.2%,均小于30%;两种化学品6次试验的96 h LC50均在各自x±2s范围内.研究显示,稀有鮈鲫胚胎的形态特征、发育过程及孵化时间等生物学特征均与斑马鱼类似,3,4-二氯苯胺和五水硫酸铜这两种化学品的胚胎急性毒性试验结果具有良好的重复性,其敏感性也与成鱼类似.因此,稀有鮈鲫作为一种我国本土的标准试验鱼种,具有鱼类胚胎急性毒性试验的应用潜力.Abstract: The study is aimed to validate whether Chinese rare minnow (Gobiocypris rarus) is applicable for fish embryo acute toxicity test, and also to evaluate the possibility of using its embryo as an alternative to test fish in acute toxicity tests, which lay a foundation for producing the related national standard of chemical testing. According to OECD Guidelines for the Testing of Chemicals No.236:Fish Embryo Acute Toxicity Test, six independent embryo tests were performed using newly fertilized eggs of G. rarus that were exposed to two reference substances, i.e. 3, 4-dichloroaniline and copper sulfate pentahydrate, respectively. The repeatability of the test results was evaluated to validate whether G. rarus was applicable for fish embryo acute toxicity test. The mean estimates of the concentration causing 50% mortality (LC50, x) of G. rarus embryos for a period of 96 h were 12.8 mg/L for 3, 4-dichloroaniline and 1.76 mg/L for copper sulfate pentahydrate, with their corresponding standard deviations of 1.70 and 0.197 mg/L, respectively; and their coefficient of variation (CV) of LC50 values were 13.3% and 11.2%, which was less than 30%. The 96 h LC50 values of six runs for each chemical fallen into the range of (x±2s). The characteristics of G. rarus embryos regarding morphology, stages of development and hatch duration were quite similar to those of Danio rerio, and toxicity tests for two chemicals using G. rarus eggs presented a promising result, too. The sensitivity in G. rarus embryos' response to the two chemicals was comparable to that of adult fish. Therefore, the endemic fish species, G. rarus could serve as a candidate organism for fish embryo acute toxicity test.
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Key words:
- Gobiocypris rarus /
- embryo /
- acute toxicity /
- repeatability
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表 1 胚胎急性毒性试验死亡表征及观察现象[7]
Table 1. The indicators of lethality and four apical observations in fish embryo acute toxicity test[7]
死亡表征 观察现象 卵凝结 卵黄凝结的胚胎肉眼观察呈乳白色,在显微镜下呈黑色.可分别在24、48、72和96 h观察 体节未形成 在(26±1)℃下,正常发育的胚胎在24 h后会形成大约20节体节.体节发育正常的胚胎会有自主运动(来回收缩),自主运动的出现可表明胚胎体节发育成型.体节缺失可分别在24、48、72和96 h观察.如果暴露24 h后体节未形成,可归因于发育迟缓;如果48 h后仍未形成,可判定死亡 尾部未分离 正常发育的胚胎,在其身体后部伸长后可观察到尾部与卵黄囊分离的现象.尾部未分离可分别在24、48、72和96 h观察 失去心跳 在(26±1)℃下,正常发育的胚胎在48 h后会有心跳.心率不齐或有心跳但腹部无血流循环均不能判定胚胎死亡.判定胚胎无心跳,至少在放大80倍下观察持续1 min或以上.无心跳可分别在48、72和96 h观察 表 2 3, 4-二氯苯胺和五水硫酸铜对稀有鮈鲫胚胎的96 h LC50
Table 2. The 96 h LC50 values of 3, 4-dichloroaniline and copper(Ⅱ) sulfate pentahydrate in G. rarus embryo acute toxicity test
试验序号 96 h LC50/(mg/L) 3, 4-二氯苯胺 五水硫酸铜 D-1 14.6 2.07 D-2 12.9 1.91 D-3 10.4 1.73 D-4 12.0 1.57 D-5 14.8 1.60 D-6 11.9 1.65 表 3 3, 4-二氯苯胺和五水硫酸铜对稀有鮈鲫的FET和AFT试验结果与预测结果
Table 3. Both tested and predicted results of 3, 4-dichloroaniline and copper(Ⅱ) sulfate pentahydrate in FET and AFT for G. rarus mg/L
化学品 FET LC50试验值 AFT LC50预测值 AFT LC50试验值 3, 4-二氯苯胺 12.8 20.4 6.59 五水硫酸铜 1.76 2.79 1.29 -
[1] Organization for Economic Cooperation and Development.OECD guidelines for the testing of chemicals.Section 2: effects on biotic systems test No.203: fish, acute toxicity test[S].Paris, France: Organization for Economic Cooperation and Development, 1992. [2] International Standardization Organization.ISO 7346, water quality-determination of the acute lethal toxicity of substances to a freshwater fish (Brachydanio rerio Hamilton-Buchanan (Teleostei, Cyprinidae)): Part 1.static method.Part 2.semi-static method.Part 3.flow-through method[S].Geneva, Switzerland: International Standardization Organization, 1996. [3] Environmental Protection Agency.EPA ecological effects test guidelines, OPPTS 850.1075: fish acute toxicity test, freshwater and marine[S].Washington DC, United States: Environmental Protection Agency, 1996. [4] RUSSELL W M S, BURCH R L.The principles of humane experimental technique[M].London, Methuen:Universities Federation for Animal Welfare, 1959:238. [5] MICHELLE R E, SCOTT E B, THOMAS A B, et al.The fish embryo toxicity test as an animal alternative method in hazard and risk assessment and scientific research[J].Aquatic Toxicology, 2010, 97(2):79-87. http://www.wanfangdata.com.cn/details/detail.do?_type=perio&id=f1f92d6b5edb3b8a40feb5f9ff1a16dd [6] KRISTIN S.Proposal to improve vertebrate cell cultures to establish them as substitutes for the regulatory testing of chemicals and effluents using fish[J].Toxicology, 2006, 224:163-183. doi: 10.1016/j.tox.2006.04.042 [7] Organization for Economic Cooperation and Development.OECD guidelines for the testing of chemicals: Section 2.effects on biotic systems test No.236: fish embryo acute toxicity (FET) test[S].Paris, France: Organization for Economic Cooperation and Development, 2013. [8] Organization for Economic Cooperation and Development.OECD series on testing and assessment.No.157 validation report (Phase 1) for the zebrafish embryo toxicity test[R].Paris, France: Organization for Economic Cooperation and Development, 2011. [9] Organization for Economic Cooperation and Development.OECD series on testing and assessment.No.179 validation report (Phase 2) for the zebrafish embryo toxicity test[R].Paris, France: Organization for Economic Cooperation and Development, 2012. [10] 王佳佳, 徐超, 屠云杰, 等.斑马鱼及其胚胎在毒理学中的试验研究与应用进展[J].生态毒理学报, 2007, 2(2):123-135.WANG Jiajia, XU Chao, TU Yunjie, et al.Experimental research and application of Zebrafish and embryos in toxicology[J].Asian Journal of Ecotoxicology, 2007, 2(2):123-135. [11] HUANG Lixing, WANG Chonggang, ZHANG Youyu, et al.Benzo[a] pyrene exposure influences the cardiac development and the expression of cardiovascular relative genes in zebrafish (Danio rerio) embryos[J].Chemosphere, 2012, 87:369-375. doi: 10.1016/j.chemosphere.2011.12.026 [12] 朱琳, 史淑洁, 佟玉洁.应用斑马鱼胚胎致畸效应检测环境污染物毒性[J].环境与健康杂志, 2003, 20(2):122-124. doi: 10.3969/j.issn.1001-5914.2003.02.034ZHU Lin, SHI Shujie, TONG Yujie.Application of the teratogenic effects of embryo development in zebrafish to the determination of toxicity of environmental pollutants[J].Journal of Environment and Health, 2003, 20(2):122-124. doi: 10.3969/j.issn.1001-5914.2003.02.034 [13] Deutsches Institut für Normung.DIN 38415-6, German standard methods for the examination of water, waste water and sludge-subanimal testing (group T): Part 6.toxicity to fish.determination of the non-acute-poisonous effect of waste water to fish eggs by dilution limits (T6)[S].Berlin, Germany: Deutsches Institut für Normung, 2001. [14] International Standards Organization.ISO 15088, water quality-determination of the acute toxicity of waste water to zebrafish eggs (Danio rerio)[S].Geneva, Switzerland: International Standards Organization, 2007. [15] FRANCOIS B, RUBEN S, JANE M R, et al.OECD validation study to assess intra-and inter-laboratory reproducibility of the zebrafish embryo toxicity test for acute aquatic toxicity testing[J].Regulatory Toxicology and Pharmacology, 2014, 69:496-511. doi: 10.1016/j.yrtph.2014.05.018 [16] SCOTT E B, JANE M R, GREGORY J C.Use of fish embryo toxicity tests for the prediction of acute fish toxicity to chemicals[J].Environmental Toxicology and Chemistry, 2013, 32(8):1768-1783. doi: 10.1002/etc.v32.8 [17] LAMMER E, CARR G J, WENDLER K, et al.Is the fish embryo toxicity test (FET) with the zebrafish (Danio rerio) a potential alternative for the fish acute toxicity test?[J].Comparative Biochemistry and Physiology Part C, 2009, 149:196-209. [18] 曹文宣, 王剑伟.稀有鮈鲫:一种新的鱼类试验动物[J].试验动物科学与管理, 2003, 20(S1):96-99. http://d.old.wanfangdata.com.cn/Periodical/hjkxyj200204017CAO Wenxuan, WANG Jianwei.Rare minnoe:a new laboratory animal in China[J].Laboratory Animal Science and Management, 2003, 20(S1):96-99. http://d.old.wanfangdata.com.cn/Periodical/hjkxyj200204017 [19] 环境保护部化学品登记中心.化学品测试方法-生物系统效应卷, 203鱼类急性毒性试验[M].2版.北京:中国环境出版社, 2013:30-36. [20] 国家质量监督检验检疫总局, 中国国家标准化管理委员.GB/T 29763-2013化学品稀有鮈鲫急性毒性试验[S].北京: 中国标准出版社, 2013. [21] 王剑伟.稀有鮈鲫的繁殖生物学[J].水生生物学报, 1992, 16(2):165-174. doi: 10.3321/j.issn:1000-3207.1992.02.004WANG Jianwei.Reproductive biology of Gobiocypris rarus[J].Acta Hydrobiologica Sinica, 1992, 16(2):165-174. doi: 10.3321/j.issn:1000-3207.1992.02.004 [22] 王蕊, 殷浩文.斑马鱼胚胎发育中适宜的毒理学指标分析[J].环境与职业医学, 2004, 21(2):88-93. http://d.old.wanfangdata.com.cn/Periodical/ldyx200402016WANG Rui, YIN Haowen.Analysis on feasible toxicological endpoints in embryonic development of Brachydanio rerio[J].Journal of Environmental and Occupational Medicine, 2004, 21(2):88-93. http://d.old.wanfangdata.com.cn/Periodical/ldyx200402016 [23] 梁艺怀, 张京佶, 石利利, 等.稀有鮈鲫作为化学品生态毒性测试鱼类模式生物的标准化实践[J].生态毒理学报, 2017, 12(2):2-10. http://d.old.wanfangdata.com.cn/Periodical/cyyhj201702001LIANG Yihuai, ZHANG Jingji, SHI Lili, et al.Standardization of Gobiocypris rarus as fish model used in chemical ecotoxicity testing[J].Asian Journal of Ecotoxicology, 2017, 12(2):2-10. http://d.old.wanfangdata.com.cn/Periodical/cyyhj201702001 [24] 王剑伟, 曹文宣.中国本土鱼类模式生物稀有聚集研究应用的历史与现状[J].生态毒理学报, 2017, 12(2):20-33.WANG Jianwei, CAO Wenxuan.Gobiocypris rarus as a Chinese native model organism:history and current situation[J].Asian Journal of Ecotoxicology, 2017, 12(2):20-33. [25] 卢玲, 沈英娃.酚类、烷基苯类、硝基苯类化合物和环境水样对剑尾鱼和稀有鮈鲫的急性毒性[J].环境科学研究, 2002, 15(4):57-59. doi: 10.3321/j.issn:1001-6929.2002.04.017LU Ling, SHEN Yingwa.Acute toxicity of phenol, alkyl benzene, nitrobenzene and water sample to sword fish (Xiphophorus helleri) and rare minnow (Gobiocypris rarus)[J].Research of Environmental Sciences, 2002, 15(4):57-59. doi: 10.3321/j.issn:1001-6929.2002.04.017 [26] ZHU Bin, LIU Tianqiang, HU Xuegang, et al.Developmental toxicity of 3, 4-dichloroaniline on rare minnow (Gobiocypris rarus) embryos and larvae[J].Chemosphere, 2013, 90:1132-1139. doi: 10.1016/j.chemosphere.2012.09.021 [27] 常剑波, 王剑伟, 曹文宣.稀有鮈鲫胚胎发育研究[J].水生生物学报, 1995, 19(2):97-103. doi: 10.3321/j.issn:1000-3207.1995.02.001CHANG Jianbo, WANG Jianwei, CAO Wenxuan.The embryonic development of Gobiocypris rarus[J].Acta Hydrobiologica Sinica, 1995, 19(2):97-103. doi: 10.3321/j.issn:1000-3207.1995.02.001 [28] 李忻林, 董洪坪, 王婷, 等.温度对斑马鱼胚胎发育的影响[J].四川动物, 2014, 33(6):829-835. http://d.old.wanfangdata.com.cn/Periodical/scdw201406004LI Xinlin, DONG Hongping, WANG Ting, et al.Effect of temperature on embryonic development of zebrafish[J].Sichuan Journal of Zoology, 2014, 33(6):829-835. http://d.old.wanfangdata.com.cn/Periodical/scdw201406004 [29] KIRSTEN H, THOMAS B.Dechorionation as a tool to improve the fish embryo toxicity test (FET) with the zebrafish (Danio rerio)[J].Comparative Biochemistry and Physiology Part C, 2011, 153:91-98. http://www.wanfangdata.com.cn/details/detail.do?_type=perio&id=d57632fd73d30287c0d151a1739691d9 [30] Environmental Protection Agency.EPA 821-R-02-012, methods for measuring the acute toxicity of effluents and receiving waters to freshwater and marine organisms[R].5th ed.Washington DC, United States: Environmental Protection Agency, 2002. [31] MONICA L, WOFLGANG G, JURGEN M, et al.Comparison of testing acute toxicity on embryo of zebrafish, Brachydanio rerio and RTG-2 cytotoxicity as possible alternatives to the acute fish test[J].Chemosphere, 1995, 30(11):2087-2102. doi: 10.1016/0045-6535(95)00088-P [32] 张京佶, 殷浩文, 赵华清.稀有鮈鲫对重铬酸钾和3, 4-二氯苯胺急性毒性研究[J].中国实验动物学报, 2014, 22(2):57-61. doi: 10.3969/j.issn.1005-4847.2014.02.013ZHANG Jingji, YIN Haowen, ZHAO Huaqing, Acute toxicity of potassium bichromate and 3, 4-dichloroaniline in Chinese rare minnow (Gobiocypris rarus)[J].Acta Laboratorium Animals Scientia Sinica, 2014, 22(2):57-61. doi: 10.3969/j.issn.1005-4847.2014.02.013 [33] 国家环境保护局.HJ/T 154-2004新化学物质危害评估准则[S].北京: 中国环境科学出版社, 2004. -