Y. Tsvetnenko
{"title":"Derivation of Australian tropical marine water quality criteria for the protection of aquatic life from adverse effects of petroleum hydrocarbons","authors":"Y. Tsvetnenko","doi":"10.1002/(SICI)1098-2256(1998)13:4<273::AID-TOX1>3.0.CO;2-4","DOIUrl":null,"url":null,"abstract":"The use of data on the water concentration of total petroleum hydrocarbons (TPH) in hazard evaluation for marine biota is hindered by the lack of justified water quality criteria for TPH. Using ecotoxicology data for marine organisms and U.S. EPA guidelines (1985, 1994), numerical criteria for TPH were derived. Acute and chronic toxicity data for marine organisms exposed to water-soluble fractions of oil products were obtained from published materials and the author's investigations. Out of 310 data reviewed and sorted, 82 data for the test temperatures of 20–32°C were selected and analyzed. The genus mean acute values (GMAV) were calculated for 15 animal genera belonging to the phyla Chordata, Arthropoda, Mollusca, Annelida. Plant values were obtained for six species of the algae classes Diatom, Chlorophyta and Dinophyta. The GMAVs ranged from 0.2 to 13.1 mg/L TPH. The considerable variability of data was attributed to differences in toxicity test designs. The EC50 values were adjusted by taking into account the fact that average test concentrations drop during courses of static-renewal and static toxicity tests. These adjustments resulted in a GMAV range of 0.2–5.2 mg/L with acceptable intergeneric variability. The final acute value derived as the fifth percentile of the set of 15 GMAVs for animals was in the range of 0.168–0.198 mg/L for the triangular, logistic, and normal distribution models. The advisory water quality criterion (AWQC) derived from these values was 0.007 mg/L. According to the criterion definition, to protect warm water marine organisms from unacceptable effects, an ambient concentration of TPH must not exceed AWQC of 0.007 mg/L. © 1998 John Wiley & Sons, Inc. Environ Toxicol Water Qual 13: 273–284, 1998","PeriodicalId":11824,"journal":{"name":"Environmental Toxicology & Water Quality","volume":"14 1","pages":"273-284"},"PeriodicalIF":0.0000,"publicationDate":"1998-01-01","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"","citationCount":"7","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Environmental Toxicology & Water Quality","FirstCategoryId":"1085","ListUrlMain":"https://doi.org/10.1002/(SICI)1098-2256(1998)13:4<273::AID-TOX1>3.0.CO;2-4","RegionNum":0,"RegionCategory":null,"ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"","JCRName":"","Score":null,"Total":0}
引用次数: 7
澳大利亚热带海洋水质标准的推导,以保护水生生物免受石油碳氢化合物的不利影响
总石油烃(TPH)水浓度数据在海洋生物群危害评价中的应用受到缺乏合理的TPH水质标准的阻碍。利用海洋生物的生态毒理学数据和美国环境保护署指南(1985,1994),导出了TPH的数值标准。海洋生物暴露于石油产品水溶性组分的急性和慢性毒性数据来自已发表的资料和作者的调查。在审查和整理的310个数据中,选择并分析了82个测试温度为20-32°C的数据。计算了脊索动物门、节肢动物门、软体动物门、环节动物门15个动物属的平均急性值(GMAV)。获得了硅藻、绿藻和藻门6种藻类的植物价值。GMAVs范围为0.2 ~ 13.1 mg/L TPH。数据的相当大的可变性归因于毒性试验设计的差异。考虑到静态更新和静态毒性试验过程中平均试验浓度下降的事实,对EC50值进行了调整。这些调整导致GMAV范围为0.2-5.2 mg/L,属间可变性可接受。在三角分布、logistic分布和正态分布模型中,15种动物GMAVs的第5个百分位数的最终急性值在0.168-0.198 mg/L之间。由此得出的建议水质标准(AWQC)为0.007 mg/L。根据标准定义,为了保护温水海洋生物免受不可接受的影响,环境TPH浓度不得超过AWQC的0.007 mg/L。©1998 John Wiley & Sons, Inc环境科学与技术,1998 (3):387 - 398
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