周闰, 杨丽, 吴宇伉, 徐志飞, 孟元华, 丁新良, 陈晓峰. 无锡市不同生活饮用水中两类消毒副产物三卤甲烷及卤乙酰胺的浓度比较[J]. 环境与职业医学, 2023, 40(4): 456-461. DOI: 10.11836/JEOM22350
引用本文: 周闰, 杨丽, 吴宇伉, 徐志飞, 孟元华, 丁新良, 陈晓峰. 无锡市不同生活饮用水中两类消毒副产物三卤甲烷及卤乙酰胺的浓度比较[J]. 环境与职业医学, 2023, 40(4): 456-461. DOI: 10.11836/JEOM22350
ZHOU Run, YANG Li, WU Yukang, XU Zhifei, MENG Yuanhua, DING Xinliang, CHEN Xiaofeng. Trihalomethanes and haloacetamides as disinfection by-products in different types of drinking water of Wuxi[J]. Journal of Environmental and Occupational Medicine, 2023, 40(4): 456-461. DOI: 10.11836/JEOM22350
Citation: ZHOU Run, YANG Li, WU Yukang, XU Zhifei, MENG Yuanhua, DING Xinliang, CHEN Xiaofeng. Trihalomethanes and haloacetamides as disinfection by-products in different types of drinking water of Wuxi[J]. Journal of Environmental and Occupational Medicine, 2023, 40(4): 456-461. DOI: 10.11836/JEOM22350

无锡市不同生活饮用水中两类消毒副产物三卤甲烷及卤乙酰胺的浓度比较

Trihalomethanes and haloacetamides as disinfection by-products in different types of drinking water of Wuxi

  • 摘要: 背景

    无锡地区水源多样,消毒及处理工艺不同,形成的生活饮用水中消毒副产物(DBPs)含量不同,可能造成的健康风险也不同。

    目的

    了解无锡地区生活饮用水中三卤甲烷(THMs)和卤乙酰胺(HAcAms)两类消毒副产物的水平,并分析比较在不同水源、不同水期、不同消毒方式和不同净水工艺下的差异,为保障饮水安全提供技术支撑。

    方法

    以无锡市12家集中供水单位的出厂水及对应的近、中、远端末梢水为研究对象,于2019年12月及2020年7月采集水样检测THMs和HAcAms。采用建立的吹扫捕集-气相色谱质谱法测定水样中三氯甲烷(TCM)、二氯一溴甲烷(BDCM)、一氯二溴甲烷(DBCM)及三溴甲烷(TBM)共4种THMs的质量浓度(后简称浓度),固相萃取-气相色谱质谱法测定二氯乙酰胺(DCAcAm)、三氯乙酰胺(TCAcAm)、一氯一溴乙酰胺(BCAcAm)、二溴乙酰胺(DBAcAm)、二氯一溴乙酰胺(BDCAcAm)、二溴一氯乙酰胺(DBCAcAm)、三溴乙酰胺(TBAcAm)共7种HAcAms浓度。分析比较长江/太湖/水库3种不同水源类型、丰/枯水期、液氯/次氯酸钠2种消毒方式以及常规处理和常规+深度处理2种工艺的不同生活饮用水中THMs和HAcAms两类DBPs浓度。

    结果

    共采集无锡市生活饮用水水样96份。其中4种THMs检出率为100%,其浓度均未超过GB 5749—2022《生活饮用水卫生标准》标准限值,总浓度在1.027~40.225 μg·L−1之间,MP25P75)为24.782(17.784,30.932)μg·L−1;4种THMs浓度高低顺序为:TCM > BDCM > DBCM > TBM。7种HAcAms共检出5种,总浓度范围为0.137~3.288 μg·L−1MP25P75)为0.808(0.482,1.704)μg·L−1;以DCAcAm检出的浓度最高,最高浓度为2.448 μg·L−1,其次为BCAcAm,而TCAcAm、DBCAcAm未检出。以太湖33.353(26.649,36.217)μg·L−1和长江27.448(24.312,31.393)μg·L−1为水源的生活饮用水中THMs总浓度的MP25P75)高于以水库为水源的浓度16.359(2.305,21.553)μg·L−1P<0.05);而以太湖为水源的生活饮用水中HAcAms总浓度的MP25P75)为0.616(0.363,0.718)μg·L−1,低于以长江0.967(0.355,2.283)μg·L−1和水库1.071(0.686,1.828)μg·L−1为水源的浓度(P<0.05)。丰水期、枯水期之间以及不同消毒方式下水样中的THMs和HAcAms总浓度差异无统计学意义(P>0.05);运用臭氧-活性炭、膜工艺深度处理工艺的水厂水中THMs和HAcAms总浓度的MP25P75)为20.565(3.316,27.185)μg·L−1、0.623(0.452,1.286)μg·L−1,低于常规处理工艺的28.740(23.431,35.085)μg·L−1和0.934(0.490,2.116)μg·L−1P<0.05)。

    结论

    无锡地区生活饮用水中THMs和HAcAms浓度整体处于较低水平。受控的THMs含量均符合国家标准要求,未受控的HAcAms作为新兴消毒副产物,检出的浓度达μg·L−1级别。水源类型不同,两类DBPs的生成浓度存在差异;经深度处理工艺的水样产生的THMs和HAcAms浓度低于常规处理工艺下的水样。

     

    Abstract: Background

    The concentrations of disinfection by-products (DBPs) are varied by different water sources, disinfectants, or treatment processes in Wuxi, and the associated health risks are also different.

    Objective

    To understand the levels of trihalomethanes (THMs) and haloacetamides (HAcAms) in drinking water in Wuxi, and their variations by water sources, seasons, disinfectants or treatment processes, aiming to provide technical support for ensuring the safety of drinking water.

    Methods

    In dry period (December 2019) and wet period (July 2020), the finished water and tap water (from the beginning, middle, and end of the drinking water distribution network) from 12 centralized water treatment plants in Wuxi were collected to detect the concentrations of THMs and HAcAms in water samples. A purge and trap-gas chromatography-mass spectrometry method was applied to detect trichloromethane (TCM), bromodichloromethane (BDCM), dibromochloromethane (DBCM), and tribromomethane (TBM), and a solid-phase extraction-gas chromatography-mass spectrometry method to detect dichloroacetamide (DCAcAm), trichloroacetamide (TCAcAm), bromochloroacetamide (BCAcAm), dibromoacetamide (DBAcAm), bromodichloroacetamide (BDCAcAm), dibromochloroacetamide (DBCAcAm), and tribromoacetamide (TBAcAm). Analyses and comparisons were made on the concentrations of THMs and HAcAms in drinking water by water sources (the Yangtze River/the Taihu Lake/reservoir), wet/dry seasons, disinfection methods (liquid chlorine/sodium hypochlorite), and treatment processes (conventional treatment/conventional+advanced treatment).

    Results

    A total of 96 drinking water samples were collected in Wuxi. THMs were positive in all the water samples (100%), with concentration ranging from 1.027 to 40.225 μg·L−1 and the M (P25, P75) concentration being 24.782 (17.784, 30.932) μg·L−1. None of the 4 THMs exceeded the standard limit of the Standards for drinking water quality (GB 5749-2022 ), and the order of the 4 THMs concentrations from high to low was TCM > BDCM > DBCM > TBM. Five of the 7 HAcAms were detected, the total concentration ranged from 0.137 to 3.288 μg·L−1, and the M (P25, P75) was 0.808 (0.482, 1.704) μg·L−1. The DCAcAm concentration was the highest (2.448 μg·L−1), followed by BCAcAm, while TCAcAm and DBCAcAm were not detected. The M (P25, P75) of the total concentration of THMs in the drinking water from the Taihu Lake was 33.353 (26.649, 36.217) μg·L−1, that of the Yangtze River was 27.448 (24.312, 31.393) μg·L−1, and both were higher than the level of the reservoir 16.359 (2.305, 21.553) μg·L−1 (P<0.05), while the M (P25, P75) of the total concentration of HAcAms in the drinking water from the Taihu Lake was 0.616 (0.363, 0.718) μg·L−1, which was lower than those of the Yangtze River 0.967 (0.355, 2.283) μg·L−1 and the reservoir 1.071 (0.686, 1.828) μg·L−1 (P<0.05). There were no statistically significant differences in the total concentrations of THMs and HAcAms between wet season and dry season, or between different disinfection methods (P>0.05). The M (P25, P75) concentrations of THMs and HAcAms in drinking water after advanced treatment process involving ozone, activated carbon, and membrane were 20.565 (3.316, 27.185) μg·L−1 and 0.623 (0.452, 1.286) μg·L−1 respectively, and were lower than the corresponding values after conventional treatment process, 28.740 (23.431, 35.085) μg·L−1 and 0.934 (0.490, 2.116) μg·L−1 respectively (P<0.05).

    Conclusion

    The concentrations of THMs and HAcAms in drinking water in Wuxi are generally at a low level. The levels of controlled THMs meet the requirements of national standards, and the levels of uncontrolled HAcAms as new DBPs are up to μg·L−1. The concentrations of the two kinds of DBPs in drinking water vary by water sources. The concentrations of THMs and HAcAms produced by the advanced treatment process are lower than that by the conventional treatment process.

     

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