期刊文献+

固相萃取-羟基衍生化-气相色谱/质谱联用测定滇池水体中酚类内分泌干扰物 被引量:13

DETERMINATION OF PHENOLS IN SUFACE WATER OF DIANCHI LAKE BY SOLID EXTRACTION-HYDROXYL DERIVATIZATION-GC/MS
下载PDF
导出
摘要 采用PTA-OH为衍生化试剂,对酚类内分泌干扰物的衍生化条件进行了优化,并在优化条件下,利用固相萃取-羟基衍生化-气相色谱/质谱法检测了滇池水体中酚类内分泌干扰物的浓度.结果表明,目标物PTA-OH衍生化在乙酸乙酯中、20℃条件下衍生化5min可达到最佳衍生化效果,衍生化后酚类内分泌干扰物的GC/MS检测限达到0.1pg.μl-1,检测范围为20—1000pg.μl-1;滇池水体中的辛基酚的浓度为ND—56.5ng.l-1;枯烯基酚的浓度为23.5—48.5ng.l-1;壬基酚的浓度为13.6—141.6ng.l-1;双酚A的浓度为ND—4713.6ng.l-1.滇池水体中4种酚类内分泌干扰物普遍存在,其中双酚A的污染较严重. Phenyltrimethylammonium (PTA-OH) was used to derivatize phenolic endocrine disrupting chemicals (EDCs) and its derivatization conditions were tested. The optimized derivatization conditions were then used in a solid phase extraction-hydroxyl derivatization-GC/MS method for simultaneous determination of target phenols in surface water of Dianchi Lake. The results showed that the optimum derivatization conditions for derivatization with PTA-OH were ethyl acetate as solvent at 20℃ for 5min,and the instrumental detection limits for phenolic EDCs after derivatization was found to be 0.1pg·μl^-1 with a linear detection range from 20 to 1000pg·μl^-1. The concentrations of 4-tert-octylphenol (4-t-OP),4-cumylphenol (4-CP),4-nonylphenol (4-NP) and bisphenol A (BPA) in surface water of Dianchi Lake were ND—56.5ng·l^-1,23.5—48.5ng·l^-1,13.6—141.6ng·l^-1 and ND—4713.6ng·l^-1,respectively.This indicates the four phenolic EDCs are ubiquitously present in surface water of Dianchi Lake,among which BPA is dominant one.
出处 《环境化学》 CAS CSCD 北大核心 2010年第4期744-748,共5页 Environmental Chemistry
基金 国家自然科学基金(20767002) 云南省自然科学基金(2007B035M) 教育部留学回国人员科研启动基金(教外司留[2008]890号)
关键词 酚类 内分泌干扰物 衍生化 气相色谱-质谱 滇池 phenols endocrine disrupting chemicals derivatization gas chromatography-mass spectrometry (GC-MS) Dianchi Lake.
  • 相关文献

参考文献8

  • 1Nunez L, Turiel E, Tadeo J L, Determination of Nonylphenol and Nonylphenol Ethoxylates in Environmental Solid Samples by Ultrasonic- Assisted Extraction and High Performance Liquid Chromatography-Fluorescence Detection [ J ] . Journal of Chromatography A, 2007, 1146: 157--163.
  • 2Xiao Q W, Li Y Q, Ouyang H X et al. , High-Performance Liquid Chromatographic Analysis of Bisphenol A and 4-nonylphenol in Serum, Liver and Testis Tissues after Oral Administration to Rats and Its Application to Toxicokinetic Study [ J ] . Journal of Chromatography B,2006, 830:322--329.
  • 3Gatidou G, Thomaidis N S, Stasinakis A Set al. , Simultaneous Determination of the Endocrine Disrupting Compounds Nonylphenol, Nonylphenol Ethoxylates, Trielosan and Bisphenol A in Wastewater and Sewage Sludge by Gas Chromatography-Mass Spectrometry [ J ] . Journal of Chromatography A, 2007, 1138 [ J] : 32-41.
  • 4Zafra A, del Olmo M, Sauarz Bet al. , Gas Chromatographic-Mass Spectrometric Method for the Determination of Bisphenol A and Its Chlorinated Derivatives in Urban Wastewater [J] . Water Research, 2003, 37: 735--742.
  • 5陈荣圻.烷基酚聚氧乙烯醚的生态环保问题探讨[J].染料与染色,2003,40(5):290-292. 被引量:6
  • 6杜兵,张彭义,张祖麟,余刚.北京市某典型污水处理厂中内分泌干扰物的初步调查[J].环境科学,2004,25(1):114-116. 被引量:65
  • 7Fmmme H, Kuchler T, Otto T et al. , Occurrence of Phthalates and Bisphenol A and F in the Environment [ J] . Water Research, 2002, 36: 1429-1438.
  • 8Environment Canada, Health Canada, Editor, Canadian Environmental Protection Act, Priority Substances List Assessment Report. Bis (2-ethylhexyl) phthalate [ R ] . Canada, 1994.

二级参考文献13

  • 1Kavlock G, Daston P, et al. Research Needs for the Risk As sessment of Health and Environmental Effects of Endocrine Disruptors[J]. 1996,104(Sup. 4): 1 -26.
  • 2Japan Environment Agency. Stratic programs on environmental disruptors' 98. Reports[ R]. Tokyo, 1998.
  • 3European Commission DG ENV.Towards the establishment of a priority of substances for further evaluation of their role in en docrine disruption[ R ]. Reports, Netherlands, 2000.
  • 4Nasu M, Goto M, Kato HY, et al. Study on endocrine disrupting chemicals in wastewater treatment plants[J]. Water Science and Technology, 2001,43(2): 101 - 108.
  • 5Alcock R, Sweetman A, Jones KC. Assessment of Organic Con taminant Fate In Waste Water Treatment Plants I: Selected Compounds and Physicochemical Properties[ J ]. Chemosphere, 1999, 38 (10): 2247-2262.
  • 6Johnson AC, Sumpter JP. Removal of Endocrine disrupting Chemicals in Activated Sludge Treatment Works[J]. Environ. Sci. &Teehnol. ,2001,35(24) :4697-4703.
  • 7Perez S, Guillamon M, barcelo D. Quantitative analysis of poly cyclic aromatic hydrocarbons in sewage sludge from wastewater treatment plants[J ]. Journal of chromatography A, 2001,938: 57-65.
  • 8Hermann F, Thomas K,Thomas O, et al. Occurrence of Phtha lates and bisphenol A and F in the environment[J]. Water Re search, 2002,36:1429- 1438.
  • 9Cheng HF,Chen SY, Lin JG. Hazardous organic matters in mu nicipal sewage sludge in Taiwan[ J ]. Water Science and Technol ogy ,2001,44(10) :65-70.
  • 10Sekela M, Brewer R, Moyle G, et al. Occurrence of an environmental Estrogen (4-NonylPhenol)in sewage treatment plant effluent and the aquatic receiving environment [J ]. Water Sci ence and Technology, 1999,39 ( 10 ~ 11 ): 217 ~ 220.

共引文献69

同被引文献990

引证文献13

二级引证文献95

相关作者

内容加载中请稍等...

相关机构

内容加载中请稍等...

相关主题

内容加载中请稍等...

浏览历史

内容加载中请稍等...
;
使用帮助 返回顶部