中国环境科学
中國環境科學
중국배경과학
CHINA ENVIRONMENTAL SCIENCE
2014年
3期
672-680
,共9页
严清%张怡昕%高旭%訾成方%甘秀梅%彭绪亚%郭劲松
嚴清%張怡昕%高旭%訾成方%甘秀梅%彭緒亞%郭勁鬆
엄청%장이흔%고욱%자성방%감수매%팽서아%곽경송
医药活性物质%风险评估%去除效果%质量平衡分析%污水处理厂
醫藥活性物質%風險評估%去除效果%質量平衡分析%汙水處理廠
의약활성물질%풍험평고%거제효과%질량평형분석%오수처리엄
pharmaceutically active compound%risk assessment%removal efficiency%mass balance calculation%municipalwastewater treatment plant
采用固相萃取、高效液相色谱/串联质谱法(污泥样品先采用超声波萃取预处理方法提取)检测分析了包括磺胺类、喹诺酮类、大环类酯类抗生素、心血管类、止痛剂类等8类医药活性物质在重庆某污水厂中的含量水平及其行为归趋.采用 EC/PNEC 综合评价体系评估环境中目标医药活性物质的生态风险,利用质量平衡分析的方法分析了其在水相及污泥相中的分布.结果表明,目标物质在水相中均可检出,其检出浓度在ng/L~μg/L,在污泥样品中可检测出18种目标物质,其浓度在ng/g (干重,下同).仅仅1.1%的目标物质被污泥吸附去除.污水处理厂初级处理及氯化消毒阶段对目标物质无明显去除效果,目标物质的去除主要发生在生物处理阶段,生物的降解或转化作用是目标物质的主要去除机制.EC/PNEC 分析表明,磺胺嘧啶、磺胺甲恶唑、氧氟沙星与脱水红霉素在污水处理厂出水及其污泥中综合评价因子均大于1,它们的存在可能对环境产生不同程度的危害.本研究结果表明,污水处理厂并不能完全去除水相中微量的医药物质,为防止排放导致的潜在生态风险,出水及污泥中活性医药物质需采取措施进行进一步的处理.
採用固相萃取、高效液相色譜/串聯質譜法(汙泥樣品先採用超聲波萃取預處理方法提取)檢測分析瞭包括磺胺類、喹諾酮類、大環類酯類抗生素、心血管類、止痛劑類等8類醫藥活性物質在重慶某汙水廠中的含量水平及其行為歸趨.採用 EC/PNEC 綜閤評價體繫評估環境中目標醫藥活性物質的生態風險,利用質量平衡分析的方法分析瞭其在水相及汙泥相中的分佈.結果錶明,目標物質在水相中均可檢齣,其檢齣濃度在ng/L~μg/L,在汙泥樣品中可檢測齣18種目標物質,其濃度在ng/g (榦重,下同).僅僅1.1%的目標物質被汙泥吸附去除.汙水處理廠初級處理及氯化消毒階段對目標物質無明顯去除效果,目標物質的去除主要髮生在生物處理階段,生物的降解或轉化作用是目標物質的主要去除機製.EC/PNEC 分析錶明,磺胺嘧啶、磺胺甲噁唑、氧氟沙星與脫水紅黴素在汙水處理廠齣水及其汙泥中綜閤評價因子均大于1,它們的存在可能對環境產生不同程度的危害.本研究結果錶明,汙水處理廠併不能完全去除水相中微量的醫藥物質,為防止排放導緻的潛在生態風險,齣水及汙泥中活性醫藥物質需採取措施進行進一步的處理.
채용고상췌취、고효액상색보/천련질보법(오니양품선채용초성파췌취예처리방법제취)검측분석료포괄광알류、규낙동류、대배류지류항생소、심혈관류、지통제류등8류의약활성물질재중경모오수엄중적함량수평급기행위귀추.채용 EC/PNEC 종합평개체계평고배경중목표의약활성물질적생태풍험,이용질량평형분석적방법분석료기재수상급오니상중적분포.결과표명,목표물질재수상중균가검출,기검출농도재ng/L~μg/L,재오니양품중가검측출18충목표물질,기농도재ng/g (간중,하동).부부1.1%적목표물질피오니흡부거제.오수처리엄초급처리급록화소독계단대목표물질무명현거제효과,목표물질적거제주요발생재생물처리계단,생물적강해혹전화작용시목표물질적주요거제궤제.EC/PNEC 분석표명,광알밀정、광알갑악서、양불사성여탈수홍매소재오수처리엄출수급기오니중종합평개인자균대우1,타문적존재가능대배경산생불동정도적위해.본연구결과표명,오수처리엄병불능완전거제수상중미량적의약물질,위방지배방도치적잠재생태풍험,출수급오니중활성의약물질수채취조시진행진일보적처리.
The occurrence and fate of eight therapeutic groups, including antibiotics, analgesics, antiepileptics, antilipidemics, antihypersensitives, were studied at a municipal wastewater treatment plant in Chongqing. PhACs were detected using high performance liquid chromatography/tandem mass spectrometry after solid-phase extraction, and the sludge samples were extracted by ultrasonic-assisted extraction before solid-phase extraction. The distribution of PhACs in water and sludge phase was calculated by mass balance analysis. Risk quotients, expressed as the ratios of environmental concentrations and the predicted no-effect concentrations, were used to analyze the ecotoxicological assessment of the target PhACs in the environment. Results showed that all the target pharmaceutically active compounds (PhACs) were present in wastewater, in concentrations ranging from low ng/L to a few μg/L.Among the target PhACs, 18were detected in the sludge samples and most PhACs were found at low ng/g dry weight levels. Only about 1.1%of the total mass load of the studied PhACs was removed by sorption of sludge. The removal of PhACs was insignificant in primary and disinfection processes and was mainly achieved during the secondary treatment. The aqueous removals for the selected PhACs were mainly attributed to the biodegradation processes. Risk quotients were higher than unity for sulfadiazine, sulfamethoxazole, ofloxacinand erythromycin-H2O, in effluent and sludge samples, indicating a significant ecotoxicological risk to human health. Therefore, further removal of PhACs in effluent and sludge is required before their discharge and application to prevent their introduction into the environment.