Zhonghua yu fang yi xue za zhi [Chinese journal of preventive medicine] · 2010
[Determination of several herbicides, fungicides and estrogens in water from various treatment processes of different water plants in Shanghai by solid phase extraction-gas chromatography/mass spectrometry].
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Zheng Wei-wei, Wang Xia, Tian Da-jun, Wei Xiao, Chen Xin, Zhang Hao, Zhou Ying, Liu Li, Guo Shuai, Jiang Song-hui, Qu Wei-dong
Аннотация
OBJECTIVE: To establish the solid phase extraction-gas chromatography/mass spectrometry (GC/MS) method for qualitative and quantitative determination of several herbicides, fungicides and estrogens in drinking water.
METHODS: Duplicate 1 L water samples were collected from various treatment processes of different water plants. Target pollutants were extracted by XAD-2 resin from water samples and were eluted by 30% acetone-methanol. GC/MS was employed for qualitative and quantitative analysis of target pollutants.
RESULTS: The linear ranges of standard curves of 6 target compounds including atrazine, alachlor, 4-cumyphenol, thiabendazole, β-estradiol and ethylestradiol were 0.1 - 10 µg/ml and the R(2) values were 0.9915 - 0.9995. The detection limits, the recovery rates, and the relative standard deviation (RSD) were separately 0.01 - 0.40 µg/L, 74.0% - 112.0% and 2.3% - 14.8%. Atrazine (0.11 - 0.13 µg/L), 4-cumyphenol (0.20 - 0.35 µg/L), thiabendazole (0.92 - 1.46 µg/L), β-estradiol (1.02 - 1.32 µg/L) and ethylestradiol (0.96 - 1.66 µg/L)were all detected in raw water, post-coagulation water, post-sedimentation water and finished water using Huangpu River as water source. Alachlor was not detected in any water samples in Huangpu River. The 6 target compounds were not detected in any water samples from the water plants using Yangtse River as water source.
CONCLUSION: The methods with high sensitivity and satisfying selectivity are suitable to simultaneously qualitative and quantitative determination of target pollutants in drinking water. Concentrations of above-mentioned pollutants in drinking water coming from Huangpu River are obviously higher than in drinking water coming from Yangtze River. Thiabendazole, β-estradiol and ethylestradiol at the level of µg/L exist in drinking water coming from Huangpu River and more attention should be paid to surveillance of future.
METHODS: Duplicate 1 L water samples were collected from various treatment processes of different water plants. Target pollutants were extracted by XAD-2 resin from water samples and were eluted by 30% acetone-methanol. GC/MS was employed for qualitative and quantitative analysis of target pollutants.
RESULTS: The linear ranges of standard curves of 6 target compounds including atrazine, alachlor, 4-cumyphenol, thiabendazole, β-estradiol and ethylestradiol were 0.1 - 10 µg/ml and the R(2) values were 0.9915 - 0.9995. The detection limits, the recovery rates, and the relative standard deviation (RSD) were separately 0.01 - 0.40 µg/L, 74.0% - 112.0% and 2.3% - 14.8%. Atrazine (0.11 - 0.13 µg/L), 4-cumyphenol (0.20 - 0.35 µg/L), thiabendazole (0.92 - 1.46 µg/L), β-estradiol (1.02 - 1.32 µg/L) and ethylestradiol (0.96 - 1.66 µg/L)were all detected in raw water, post-coagulation water, post-sedimentation water and finished water using Huangpu River as water source. Alachlor was not detected in any water samples in Huangpu River. The 6 target compounds were not detected in any water samples from the water plants using Yangtse River as water source.
CONCLUSION: The methods with high sensitivity and satisfying selectivity are suitable to simultaneously qualitative and quantitative determination of target pollutants in drinking water. Concentrations of above-mentioned pollutants in drinking water coming from Huangpu River are obviously higher than in drinking water coming from Yangtze River. Thiabendazole, β-estradiol and ethylestradiol at the level of µg/L exist in drinking water coming from Huangpu River and more attention should be paid to surveillance of future.