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污水中短长链全氟羧酸检测方法的开发
摘要点击 2192  全文点击 1301  投稿时间:2008-10-09  修订日期:2009-02-22
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中文关键词  全氟羧酸  弱阴离子交换柱  固相萃取  高效液相色谱-串联质谱仪  污水
英文关键词  perfluorocarboxylates(PFCAs)  weak anion exchange cartridge  solid phase extraction(SPE)  high performance liquid chromatography-tandem mass spectrometry  sewages
作者单位
李飞 同济大学环境科学与工程学院污染控制与资源化研究国家重点实验室上海200092 
张超杰  
曲燕  
陈晶  
周琪  
颜湘波  
马金星  
中文摘要
      开发了弱阴离子交换柱固相萃取+高效液相色谱-负电喷雾-串联质联法[WAX-SPE+HPLC-ESI(-)-MS/MS]检测污水中碳链长度在2~14内的全氟羧酸(PFCAs).采用弱阴离子交换(WAX)柱进行固相萃取时,将污水水样用甲酸酸化至pH=3.0,并使用2%甲酸溶液作净化溶剂、1%氢氧化铵甲醇溶液作洗脱溶剂,则可使短长链PFCAs(C2~C14)均具有较高的回收率,并克服了反相固相萃取柱对短链PFCAs(C2~C5)回收率低的缺点.为了验证方法的有效性,对上海市市政污水处理厂A和B的进水进行检测,结果表明各种PFCAs的回收率分别在56%~121%和54%~120%的范围内,相对标准偏差(RSD)分别小于11%和14%,方法检出限和定量限分别在0.2~1.0 ng/L和1.0~5.0 ng/L的范围内,这充分证明了该方法的可靠性.此外,在处理厂A和B内含量最高的PFCAs均为全氟辛酸(分别为743 ng/L和837 ng/L),其次为三氟乙酸(分别为139 ng/L和489 ng/L).
英文摘要
      A method using weak anion exchange cartridge for solid phase extraction before high performance liquid chromatography-negative electronspray ionization-tandem mass spectrometry [WAX-SPE+HPLC-ESI(-)-MS/MS] detection has been developed to measure C2-C14 perfluorocarboxylates (PFCAs) in sewages. When the weak anion exchange (WAX) cartridges were used for solid phase extraction (SPE), the better recoveries of short- and long-chain PFCAs (C2-C14) were achieved as the sewage samples were acidified to pH=3.0 by formic acid, 2% formic acid was used for washing solvent and 1% ammonium hydroxide in methanol was used for elution solvent. The WAX cartridges used for SPE overcame the disadvantages of reverse phase solid phase extraction cartridges, i.e. the recoveries of short-chain PFCAs (C2-C5) were very low. The validity of this method was demonstrated by determination of short- and long-chain PFCAs (C2-C14) in influent of municipal wastewater treatment plant A and B in Shanghai, China. The results indicate that the recoveries of all PFCAs in influent of plant A and B are 56%-121% and 54%-120%, respectively; the recovery relative standard deviations (RSD) of plant A and B are <11% and <14%, respectively; and the method detection limits (MDL) and method quantitation limits (MQL) are 0.2-1.0 ng/L and 1.0-5.0 ng/L, respectively. In addition, the perfluorooctanoate (743 ng/L and 837 ng/L, respectively) and trifluoroacetic acid (139 ng/L and 489 ng/L, respectively) are the most and the second most PFCAs found in both plant A and B.

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