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羊角月牙藻在制药废水毒性评价中的应用
引用本文:杜丽娜,曹 宇,穆玉峰,余若祯,许秋瑾,高俊发,左剑恶.羊角月牙藻在制药废水毒性评价中的应用[J].环境科学研究,2014,27(12):1525-1531.
作者姓名:杜丽娜  曹 宇  穆玉峰  余若祯  许秋瑾  高俊发  左剑恶
作者单位:1.中国环境科学研究院, 环境基准与风险评估国家重点实验室, 北京 100012
基金项目:国家水体污染控制与治理科技重大专项(2012ZX07501-003,4ZX07510-001,9ZX07529-006)
摘    要:以羊角月牙藻(FACHB-271 Selenastrum capricornutum)作为测试生物,分别采用EC50(半数抑制浓度)、TUa(急性毒性单位)和LID(最低无效应稀释度)指标对某制药厂污水处理站4个工艺节点和总出水排放口的水样进行急性毒性效应评价. 结果表明:地下调节池(工艺节点①)水样EC50为15.12%±3.82%,TUa为6.6,LID为16,为极毒/中毒废水;地上调节池(工艺节点②)水样EC50为15.81%±1.04%,TUa为6.3,LID为16,为极毒/中毒废水;中间沉淀池(工艺节点③)水样EC50为62.12%±3.83%,TUa为1.6,LID为8,为中毒/低毒废水;二级沉淀池(工艺节点④)水样EC50为89.10%±1.43%,TUa为1.1,LID为4,为低毒废水;总出水排放口水样EC50>100%,TUa<1,LID为1,为无毒或微毒废水. 经过各污水处理工艺节点后,制药废水对羊角月牙藻的急性毒性逐级减弱,并且毒性指标与ρ(CODCr)具有较好的线性关系. 研究还发现,采用毒性指标LID表征该制药废水的生物毒性,对废水样品的毒性分辨能力更强. 

关 键 词:制药废水    藻类    急性毒性    评价
收稿时间:2014/5/13 0:00:00
修稿时间:2014/9/2 0:00:00

Application of Selenastrum capricornutum in a Pharmaceutical Wastewater Toxicity Assessment
DU Li-n,CAO Yu,MU Yu-feng,YU Ruo-zhen,XU Qiu-jin,GAO Jun-fa and ZUO Jian-e.Application of Selenastrum capricornutum in a Pharmaceutical Wastewater Toxicity Assessment[J].Research of Environmental Sciences,2014,27(12):1525-1531.
Authors:DU Li-n  CAO Yu  MU Yu-feng  YU Ruo-zhen  XU Qiu-jin  GAO Jun-fa and ZUO Jian-e
Institution:1.State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China2.School of Environment, Chang'an University, Xi'an 710061, China3.School of Environment, Tsinghua University, Beijing 100084, China
Abstract:A green algae species (Selenastrum capricornutum, FACHB-271) was applied to study the acute toxicity of wastewater from a pharmaceutical manufacturer. Wastewater samples were collected from four treatment process nodes and the effluent of a pharmaceutical wastewater treatment. The acute toxic effects were evaluated by the level of EC50 (concentration for 50% of maximal effect), TUa (acute toxic unit) and LID (lowest ineffective dilution). The samples from the underground and ground regulating pool were extremely/moderately toxic. Underground (process node 1):EC50=15.12%±3.82%, TUa=6.6, LID=16; Ground (process node 2):EC50=15.81%±1.04%, TUa=6.3, LID=16); the primary setting pool wastewater (process node 3), EC50=62.12%±3.83%, TUa=1.6, LID=8, was moderately/low toxic; the secondary setting pool wastewater (process node 4), EC50=89.10%±1.43%, TUa=1.1, LID=4, was low toxic; the effluent sample, EC50 > 100%, TUa<1.0, LID=1, was not/slightly toxic. The results showed that the toxicity of wastewater samples was reduced gradually after each treatment, and a linear relationship was found between toxicity index and ln ρ(CODCr). In addition, the index, LID, can represent the toxic levels of wastewater samples more clearly. 
Keywords:pharmaceutical wastewater  algae  acute toxicity  assessment
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