期刊文献+

半透膜被动采样装置(SPMD)对水中典型酚类内分泌干扰物的富集研究

Enrichment of typical phenolic endocrine disruptors on semi-permeable membrane device (SPMD) from solution
下载PDF
导出
摘要 对3种典型酚类内分泌干扰物——双酚A(BPA)、辛基酚(OP)和壬基酚(NP)由水相到半透膜被动采样装置(SPMD)的富集动力学进行了实验室研究。研究发现,SPMD对OP和NP具有较好的富集效果,而对于BPA的富集能力较低。在4℃条件下,20 d内3种物质在水相和SPMD相间未达到分配平衡,而在15和25℃时,OP和NP可分别在3-15 d内达到分配平衡。将目标化合物的SPMD和水相分配平衡常数KSPMD实测值与经验计算值进行比较表明,二者之间存在较大偏差。改变水溶液pH值、碱度和硬度条件,观察其对目标化合物在SPMD相中的一日富集质量浓度ρs,1 d的影响。结果表明,在高pH值条件下,酚类目标污染物的离子化可导致其ρs,1 d的降低,而溶液碱度和硬度则对富集速率无显著影响。 This paper presents a laboratory experiment study on the enrichment dynamics of three typical phenolic endocrine disruptors,i.e.bisphenol A(BPA),4-tert-octylphenol(OP),and 4-nonylphenol(NP),on a semi-permeable membrane device(SPMD).It was found that OP and NP could be uptaken efficiently by SPMD,while the uptake efficiency of BPA was relatively low.Partition balance could not be reached for the three analytes at 4 ℃ during the 20 days period,but could for OP and NP at 15 or 25 ℃ in 3-15 days respectively The comparison between measured values and theoretical values of the lgKSPMD indicated the huge difference among them.The effects of water chemistry(pH,alkalinity,and hardness) on the 1 day uptake concentration of the three analytes by SPMD(ρs,1d) were also investigated.Results showed that ρs,1d of the three analytes all decreased significantly at high pH values,which might be explained by the ionization of analytes in water solution.However,the effects of water alkalinity and hardness on ρs,1d were unremarkable.
出处 《中国科技论文在线》 CAS 2009年第5期319-323,共5页
基金 国家自然科学基金项目(20807024) 高等学校博士学科点专向科研基金新教师基金(200800551051)
关键词 环境监测 半透膜被动采样装置 酚类内分泌干扰物 富集动力学 environmental monitoring SPMD phenolic endocrine disruptors enrichment dynamics
  • 相关文献

参考文献1

二级参考文献12

  • 1赵元慧,杨常岩,何艺兵,王连生.有机化合物生物富集因子快速测定方法[J].环境化学,1994,13(3):203-205. 被引量:2
  • 2HUCKINS J N, MANUWEERA G K, PETTY J D, et al.Lipid-containing semipermeable membrane devices for monitoring organic contaminants in water [J]. Environmental Science Technology,1993, 27(12): 2489-2496.
  • 3VRANA B, SCHUURMANN G. Calibrating the uptake kinetics of semipermeable membrane devices in water: Impact of hydrodynamics[J]. Environmental Science Technology, 2002, 36(2): 290-296.
  • 4HUCKINS J N, PETTY J D, ORAZIO C E, et al. Determination of uptake kinetics (sampling rates) by lipid-containing semipermeable membrane devices (SPMDs) for polycyclic aromatic hydrocarbons(PAHs) in water [J]. Environmental Science Technology 1999, 33(21):3918-3923.
  • 5HUCKINS J N, PETTY J D, PREST H F, et al. A guide for the use of semipermeable membrane devices (SPMDs) as samplers of waterborne hydrophobic organic contaminants [M]. CERC, U.S. Geological Survey, August 2000.
  • 6PREST H F, HUCKINS J N, PETTY J D, et al. A survey of recent results in passive sampling of water and air by semipermeable membrane devices [J]. Marine Pollution Bullein, 1995, 31 (4-12): 306-312.
  • 7KOT A, ZABIEGALA B, NAMIESNIK J. Passive sampling for long-term monitoring of organic pollutants in water [J]. Trends in Analytical Chemistry 2000, 19(7): 446-459.
  • 8HOFMANS H E. Numerical Modeling of the Exchange Kinetics of Semipermeable Membrane Devices [D]. AB Den Burg, The Netherlands: University of Utrecht, Netherlands Institute for Sea Research,1998.
  • 9SAYLES G. Biological fate of estrogenic compounds associated with sewage treatment: a review. U.S. EPA.
  • 10LITTEN S, MEAD B, HASSETT. Application of passive samplers(PISCES) to locating a source of PCBs on the Black River, New York[J]. Environmental Toxicology and Chemistry, 1993, 12(3): 639-647.

共引文献2

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