Column silylation method for determining endocrine disruptors from environmental water samples by solid phase micro-extraction

被引:57
作者
Helaleh, MIH [1 ]
Fujii, S
Korenaga, T
机构
[1] Univ Tokushima, Fac Integrated Arts & Sci, Tokushima 7708502, Japan
[2] Univ Tokushima, Grad Sch Ecosyst Engn, Tokushima 7708502, Japan
基金
日本学术振兴会;
关键词
phenols; poly(acrylate); derivatization; water samples; GC-MS;
D O I
10.1016/S0039-9140(01)00386-1
中图分类号
O65 [分析化学];
学科分类号
070302 ; 081704 ;
摘要
In solid phase micro-extraction (SPME), the analyte is partitioned between the coating and the sample and then desorption of the concentrated analyte is followed by GC-MS, where the analytes are thermally desorbed and subsequently separated on the column and quantified by the detector. The SPME method preserves all the advantages, such as simplicity, low cost, on site sampling and does not require solvents. Poly(acrylate) coating fibers have been developed for the extraction of phenols (such as 4-tert-butylphenol, 2,4-dichlorophenol, 4-n-pentylphenol, 4-n-hexylphenol, 4-tert-octylphenol, 4-n-heptylphenol, 4-n-nonylphenol, 4-n-octylphenol, pentachlorophenol and bisphenol A) in different water samples. The precision of the HS-SPME method ranges from 3-12% RSDs, depending on the compounds analyzed. More accurate results were obtained by HS-SPME with acidification and salting out, where the fiber is located above the liquid sample. The extraction period was 60 min, followed by desorption for 5 min at 300 degreesC. After the analytes were completely desorbed, 1 mul of bis(trimethylsilyl)trifluoroacetamide (BSTFA) was injected by ordinary GC-MS injection. The trimethylsilylate peaks were improved significantly compared with free phenol peaks. The addition of salt (saturated sodium chloride) and acidification by hydrochloric acid (pH 2.0) were found to be very important for enhancing the partitioning of the polar phenols into the polymer coating and preventing ionization of the analytes. The method is capable of limits of detection of subparts per billion of the total phenols extracted from environmental water samples. (C) 2001 Elsevier Science B.V. All rights reserved.
引用
收藏
页码:1039 / 1047
页数:9
相关论文
共 12 条
[1]  
ARTHUR CL, 1992, ANAL CHEM, V64, P1968
[2]   OPTIMIZATION OF SOLID-PHASE MICROEXTRACTION CONDITIONS FOR DETERMINATION OF PHENOLS [J].
BUCHHOLZ, KD ;
PAWLISZYN, J .
ANALYTICAL CHEMISTRY, 1994, 66 (01) :160-167
[3]   Quantitative determination of phenols in mainstream smoke with solid-phase microextraction-gas chromatography-selected ion monitoring mass spectrometry [J].
Clark, TJ ;
Bunch, JE .
JOURNAL OF CHROMATOGRAPHIC SCIENCE, 1996, 34 (06) :272-275
[4]   OCCURRENCE OF LOW-CHLORINATED AND HIGH-CHLORINATED PHENOLS IN MUNICIPAL SEWAGE BEFORE AND AFTER PASSING THROUGH BIOLOGICAL TREATMENT PLANTS [J].
FOLKE, J ;
LUND, U .
JOURNAL OF CHROMATOGRAPHY, 1983, 279 (NOV) :189-198
[5]  
Fresenius W., 1988, WATER ANAL PRACTICAL
[6]  
MUSSMANN P, 1992, WASSER, V79, P145
[7]   RAPID-DETERMINATION OF POLYAROMATIC HYDROCARBONS AND POLYCHLORINATED-BIPHENYLS IN WATER USING SOLID-PHASE MICROEXTRACTION AND GCMS [J].
POTTER, DW ;
PAWLISZYN, J .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 1994, 28 (02) :298-305
[8]  
ROWE WD, 1983, EVALUATION METHODS E
[9]  
YUJI T, 1999, BUNSEKI KAGAKU, V48, P589
[10]   HEADSPACE SOLID-PHASE MICROEXTRACTION [J].
ZHANG, ZY ;
PAWLISZYN, J .
ANALYTICAL CHEMISTRY, 1993, 65 (14) :1843-1852