我国地表水中典型DBPs的暴露水平及生态风险

氯消毒过程中可能生成有毒有害的副产物,会对水生态系统和环境健康产生直接和间接的次生危害.三卤甲烷（THMs）和卤乙酸（HAAs）是地表水中检出率最高的消毒副产物（DBPs）,其毒性效应受到广泛关注.本文检索整理了三氯甲烷（TCM）、三溴甲烷（TBM）、二氯乙酸（DCAA）和三氯乙酸（TCAA）在我国地表水暴露浓度和对水生生物的毒性效应浓度,了解我国重点流域地表水环境中TCM、TBM、DCAA和TCAA的浓度水平,分别利用急、慢性毒性数据推导预测无效应浓度（PNEC）,并使用风险商（RQ）和概率生态风险评价法（PERA）对我国重点流域水环境中TCM、TBM、DCAA和TCAA进行多层次生态风险评估.结果表明,我国地表水环境中TCM、TBM、DCAA和TCAA暴露浓度范围为n.d.~51μg/L.以致死和生长、繁殖等为测试终点的急、慢性毒性数据,构建物种敏感度分布（SSD）曲线,推导出TCM、TBM、DCAA和TCAA的PNEC值分别为0.586,0.857,0和44.880mg/L;0.006,0.064,0.956和0.012mg/L.基于急、慢性毒性数据计算出的RQ小于1.我国重点流域中TCM和TCAA对1%的水生生物造成生长、繁殖等慢性毒性影响的概率分别为78.86%和20.61%,存在潜在的生态风险.     

5种颗粒活性炭对水中卤乙酸的等温吸附试验

通过等温吸附实验,考察了5种不同类颗粒活性炭(GAC)对消毒副产物卤乙酸(HAAs)中致癌风险较高的二氯乙酸、三氯乙酸的吸附行为.结果表明:二氯乙酸、三氯乙酸的吸附行为符合Langmuir等温式;进口活性炭A对二氯乙酸饱和吸附量是3种国产活性炭的4.4～5.7倍,是另一种进口活性炭B的3.8倍;对三氯乙酸的饱和吸附量是3种国产活性炭的4.0～5.4倍,是另一种进口活性炭B的2.6倍.针对进口活性炭A开展的进一步研究结果表明,二氯乙酸、三氯乙酸2组分的相对吸附量与2组分的相对浓度成正比关系,二氯乙酸吸附容量变化对平衡浓度的敏感程度不如三氯乙酸.     

评价饮水DBPs致HepG2细胞损伤的2种试验方法

应用结晶紫染色法细胞毒性试验和胞质分裂阻滞法微核试验(CBMNT)评价饮水消毒副产物(DBPs)的HepG2细胞毒性和遗传毒性,探讨该2种试验方法纳入饮水安全性评价体系的可行性.根据遗传毒性和致癌性选用了5种DBPs,分别对HepG2细胞进行染毒,结果表明,5种DBPs的细胞毒性大小排序为3-氯-4-二氯甲基-5-羟基-2(5氢)-呋喃酮(MX)>二氯乙腈>二溴乙酸>二氯乙酸>三氯乙酸,其细胞毒性潜力(%C?值)分别为89.74,283.81,1217.02,5066.81,9335.38μmol/L,该5种DBPs在一定浓度下均可致HepG2细胞微核率显著增加,表现出明显的遗传毒性,其遗传损伤能力排序与细胞毒性大小相同.可考虑将这两种实验方法纳入到饮水安全性评价体系中.     

北京市饮用水中溴酸盐、卤代乙酸及高氯酸盐研究

调查了北京市饮用水厂源水及出厂水中消毒副产物溴酸盐、卤代乙酸及典型污染物高氯酸盐的污染现状,研究了其来源及环境影响因素.结果表明,北京市饮用水中基本不含溴酸盐;含有5种卤代乙酸和高氯酸盐.饮用水加氯消毒是产生卤代乙酸的主要原因.在所调查水厂出厂水中卤代乙酸的平均浓度为42.1～149.5μg/L;其中含氯卤代乙酸占总量的90%以上.5种卤代乙酸的含量顺序为三氯乙酸>二氯乙酸>氯溴乙酸>二溴乙酸>一溴二氯乙酸.饮用水中卤代乙酸受季节影响较大,9月份浓度最高,4月份浓度最低.高氯酸盐主要存在于以地下水为源水的水厂中,受地下水污染影响较大.各水厂出厂水中高氯酸盐含量为0.1～6.8μg/L.饮用水中高氯酸盐在11月份含量最高,7月份含量最低.     

煮沸对氯、氯胺模拟消毒饮用水中六大类DBPs的去除规律研究

以陆生来源有机物为原料制备了模拟氯、氯胺消毒饮用水,系统研究了煮沸对六大类46种消毒副产物（disinfection by-products, DBPs）的去除规律.结果显示,相比氯消毒,氯胺消毒可有效减少三卤甲烷（THMs）、卤乙酸（HAAs）、卤乙醛（HALs）、卤代硝基甲烷（HNMs）、卤乙腈（HANs）等DBPs的生成,但会提高碘代DBPs (I-DBPs)、卤乙酰胺（HAcAms）的生成.煮沸对于绝大多数DBPs （除了二卤乙酸）有良好的去除效果,并发现如下规律：(1)就单种DBP而言,消毒方式对煮沸去除DBPs并无显著影响;(2)在同类型的DBPs中,取代程度高的DBPs普遍比取代程度低的DBPs容易去除;(3)取代程度相同的同类型DBPs,煮沸后DBPs去除率大部分遵循I-DBPs> Br-DBPs> Cl-DBPs的规律;(4)少部分DBPs （如Cl/Br-THMs、二卤乙腈）,煮沸去除率表现出沸点或亨利常数依赖性.总体来看,DBPs去除率排序为THMs≈HANs≈HALs≈HNMs> HAcAms>>HAAs.此外,煮沸后各类DBPs的...     

长三角部分水源水氯化消毒后卤乙酸形成的多元回归模型研究

以长三角比较有代表性的3处水源(太湖、钱塘江、金兰水库)为实验对象,研究不同消毒条件下9种卤乙酸(haloacetic acids,HAAs)的形成及其影响因素,并通过建立多元回归模型来评估水源水氯化后HAAs的形成.结果表明:HAAs的形成水平依次为太湖钱塘江金兰水库,且均以二卤乙酸(dihaloacetic acid,DHAA)、三卤乙酸(trihaloacetic acid,THAA)为主.二氯乙酸(dichloroacetic acid,DCAA)、总二卤乙酸(ΣDHAA)、HAA5(USEPA规定的5种HAAs)、HAA9(9种HAA的简称)的回归模型具有良好的预测潜力,准确率达83.3%~94.4%,而三氯乙酸(trichloroacetic acid,TCAA)、一溴二氯乙酸(bromodichloroacetic acid,BDCAA)、ΣTHAA(总三卤乙酸)模型的预测准确率较低,只有47.2%~61.1%.根据偏相关系数分析,影响DCAA、ΣDHAA、HAA5的关键的因子是溶解性有机碳;影响TCAA、ΣTHAA、HAA9的关键的因子是投氯量;影响BDCAA形成的最关键因子是溴离子.     

模拟泳池水中氯化消毒副产物的生成规律

以模拟泳池水为研究对象,研究不同的氯化时间、氯投加量、pH值、反应温度条件对泳池水在氯化消毒过程中生成消毒副产物（DBPs）的影响.研究结果表明：延长氯化反应时间,二氯乙酸（DCAA）、三氯乙酸（TCAA）和三氯甲烷（TCM）的浓度不断升高,二氯乙腈（DCAN）、三氯硝基甲烷（TCNM）和1,1,1-三氯丙酮（1,1,1-TCP）的浓度则先升高再降低.DBPs浓度在氯化反应的前24h增幅较大,48h后趋于平缓;随着氯投加量的增加,DCAA、TCAA、TCM、TCNM和1,1,1-TCP浓度一直呈上升趋势,而DCAN浓度则先升高再降低.在氯投加量为2mg/L时,DBPs的浓度较低;在pH值从6升高到8的过程中,DCAA、TCAA、DCAN和1,1,1-TCP浓度先升高再降低,TCM和TCNM浓度则一直升高.pH值在6~7范围内可有效控制DBPs的形成;随着反应温度的升高,DCAA、TCAA、TCM和TCNM浓度持续升高,DCAN和1,1,1-TCP则逐渐降低.综上所述,应合理调节泳池水的氯化消毒条件,在保证舒适度的同时有效控制DBPs的生成.     

饮用水中典型微生物消毒过程中消毒副产物的生成规律

以饮用水中典型微生物--大肠杆菌（Escherichia coli）为试验对象,研究pH值、氯化时间、氯投量及细菌浓度对大肠杆菌在氯化消毒过程中生成消毒副产物（DBPs）的影响,并分析何种氯化条件下,DBPs控制效果最佳.研究表明：随氯投量增加,二氯乙腈（DCAN）呈先上升后下降趋势;随氯化时间延长,三氯丙酮（1,1,1-TCP）和DCAN先增加后减少;在pH值从5升高到9时,1,1,1-DCP、三氯硝基甲烷（TCNM）、二氯乙酸（DCAA）和三氯乙酸（TCAA）持续降低;细菌污染水源事件在近年常有报道,当水源水中细菌浓度增加时,饮用水中三氯甲烷（TCM）、TCNM、DCAA和TCAA浓度增加,但DCAN、三氯乙腈（TCAN）、二氯丙酮（1,1-DCP）和1,1,1-TCP不一定增加.为了达到低毒性的目的,氯投量浓度不宜太高,同时控制氯化时间为6h和pH>8.     

海水淡化低温多效蒸馏工艺(LT-MED)沿程溴代消毒副产物的生成

研究了海水淡化低温多效蒸馏(LT-MED)工艺沿程水质和溴代消毒副产物(Br-DBPs)变化特征.LT-MED工艺进水海水的Br-浓度和比紫外吸收值(SUVA)分别为54.6 mg·L~(-1)和1.7 L·(mg·m)-1,其荧光特征有机物主要有色氨酸类芳香族蛋白质、富里酸类有机物和溶解性微生物代谢产物.进水海水经Na Cl O消毒后,DBPs的种类和浓度显著增加,且增加的主要为Br-DBPs,三溴甲烷(CHBr3)占总三卤甲烷(THMs)的100%;一溴乙酸(C2H3Br O2)和二溴乙酸(C2H2Br2O2)分别占总卤乙酸(HAAs)的31.9%和68.1%;四溴苯酚(C6H5Br O)占总卤代酚(HPs)的100%.LT-MED海水淡化产品水中THMs、HAAs和HPs均未检出,但是其浓水中的THMs、HAAs和HPs浓度分别为56.9、35.0和0.1μg·L~(-1).     

长距离供水系统中消毒副产物分布特征及二次加氯的影响

供水管网覆盖区域大,导致出厂消毒剂量不足以维持管网末梢余氯量,需进行途中二次投氯.以H市供水管网为目标,通过均匀布点采样分析,考察二次加氯消毒型管网中消毒副产物(disinfection by-products,DBPs)的分布特征.结果表明,管网中检出DBPs包括三氯甲烷(TCM)、一溴二氯甲烷(BDCM)、二溴一氯甲烷(DBCM)、三溴甲烷(TBM)、二氯乙酸(DCAA)、三氯乙酸(TCAA)、二氯乙腈(DCAN)、溴氯乙腈(BCAN)和三氯硝基甲烷(TCNM)等,所检水样中DBPs浓度均低于《生活饮用水卫生标准》(GB 5749-2006)规定的标准限值.二次加氯前检出质量浓度(以平均值±偏差表示)分别为:(8.08±3.34)、(9.77±2.91)、(7.38±4.82)、(2.65±2.02)、(2.95±3.26)、(6.02±6.06)、(3.13±2.48)、(1.61±2.05)和(0.15±0.10)μg·L~(-1).二次加氯后检出质量浓度分别为:(10.30±4.55)、(11.73±3.60)、(8.23±5.22)、(2.95±2.45)、(3.29±3.60)、(8.15±7.58)、(3.31±2.61)、(1.33±2.04)和(0.12±0.06)μg·L~(-1).二次加氯后DBPs含量相较于出厂水至二次加氯点呈明显上升趋势,三卤甲烷(THMs)和卤乙酸(HAAs)分别比前段管网含量升高6.32%～26.60%和5.32%～42.71%.此外,原水水质和季节变化对DBPs的形成有一定影响,夏季DBPs的水平普遍高于春季或秋季.出厂水及管网水DBPs生成势分析表明,H市供水系统中DBPs可能存在超标风险,后续需考虑进一步优化处理工艺以保障供水水质.     

Determination of haloacetic acids in hospital e uent after chlorination by ion chromatography

The ion chromatography combined solid phase extraction （SPE） method was developed for the analysis of low concentration haloacetic acids （HAAs）, a class of disinfection by-products formed from chlorination of hospital wastewater. The monitored HAAs included monochloroacetic acid, monobromoacetic acid, dichloroacetic acid, dibromoacetic acid and trichloroacetic acid. The method employed a sodium hydroxide eluent at a flow rate of 0.8 ml/min, electrolytically generated gradients, and suppressed conductivity detection. To analyze the HAAs in real hospital wastewater samples, C18 pretreatment cartridge was utilized to reduce samples＇ turbidity. Preconcentration with SPE and matrix elimination with treatment cartridges were investigated and found to be able to obtain acceptable detection limits. Linearity, repeatability and detection limits of the above method were evaluated. The detection limits of monobromoacetic acid and dibromoacetic acid were 2.61 μg/L and 1.30 μg/L, respectively, and the other three acids are ranging from 0.48 to 0.82μg/L under 25-fold preconcentration. When the above optimization procedure was applied to three hospital wastewater samples with different treatment processes in Tianjin, it was found that the dichloroacetic acid was the major compound, and the growth ratios of the HAAs after disinfection by sodium hypochlorite were 91.28%, 63.61% and 79.50%, respectively.     

Determination of haloacetic acids concentrations in hospital effluent after chlorination by ion chromatography

The ion chromatography combined solid phase extraction (SPE) method was developed for the analysis of low concentration haloacetic acids(HAAs),a calss of disinfection by-products formed as a result of chlorination of hospital wastewater. The monitored HAAs included monochloroacetic acid, monobromoacetic acid, dichloroacetic acid, dibromoacetic acid and trichloroacetic acid. The method employed a sodium hydroxide eluent at a flow rate of 0.8 ml/min, electrolytically generated gradients, and suppressed conductivity detection. To analyze the HAAs in real hospital wastewater samples, C18 pretreatment cartridge was utilized to reduce samples' turbidity. Preconcentration with SPE and matrix elimination with treatment cartridges were investigated and were found to be able to obtain acceptable detection limits. Linearity, repeatability and detection limits of the above method were evaluated. The detection limits of monobromoacetic acid and dibromoacetic acid were 2.61 μg/L and 1.30 μg/L respectively, and the other three are ranging from 0.48 to 0.82 μg/L under 25-fold preconcentration. When the above optimization procedure was applied to three hospital wastewater samples with different treatment processes in Tianjin, it was found that the dichloroacetic acid is the major compound, and the growth ratios of the HAAs after disinfection by sodium hypochlorite were 91.28%, 63.61% and 79.50%, respectively.     

Disinfection byproducts in chlorinated or brominated swimming pools and spas: Role of brominated DBPs and association with mutagenicity

Although the health benefits of swimming are well-documented, health effects such as asthma and bladder cancer are linked to disinfection by-products (DBPs) in pool water. DBPs are formed from the reaction of disinfectants such as chlorine (Cl) or bromine (Br) with organics in the water. Our previous study (Daiber et al., Environ. Sci. Technol. 50, 6652; 2016) found correlations between the concentrations of classes of DBPs and the mutagenic potencies of waters from chlorinated or brominated swimming pools and spas. We extended this study by identifying significantly different concentrations of 21 individual DBPs in brominated or chlorinated pool and spa waters as well as identifying which DBPs and additional DBP classes were most associated with the mutagenicity of these waters. Using data from our previous study, we found that among 21 DBPs analyzed in 21 pool and spa waters, the concentration of bromoacetic acid was significantly higher in Br-waters versus Cl-waters, whereas the concentration of trichloroacetic acid was significantly higher in Cl-waters. Five Br-DBPs (tribromomethane, dibromochloroacetic acid, dibromoacetonitrile, bromoacetic acid, and tribromoacetic acid) had significantly higher concentrations in Br-spa versus Cl-spa waters. Cl-pools had significantly higher concentrations of Cl-DBPs (trichloroacetaldehyde, trichloromethane, dichloroacetic acid, and chloroacetic acid), whereas Br-pools had significantly higher concentrations of Br-DBPs (tribromomethane, dibromoacetic acid, dibromoacetonitrile, and tribromoacetic acid). The concentrations of the sum of all 4 trihalomethanes, all 11 Br-DBPs, and all 5 nitrogen-containing DBPs were each significantly higher in brominated than in chlorinated pools and spas. The 8 Br-DBPs were the only DBPs whose individual concentrations were significantly correlated with the mutagenic potencies of the pool and spa waters. These results, along with those from our earlier study, highlight the importance of Br-DBPs in the mutagenicity of these recreational waters.     

海水淡化超滤-反渗透工艺沿程溴代消毒副产物变化规律

研究了海水淡化超滤-反渗透(UF-RO)工艺沿程有机物和溴代消毒副产物(Br-DBPs)变化特征.该海水中含有较高浓度的Br-(45.6~50.9 mg·L-1)和较多的芳香类化合物[比紫外吸收值SUVA为3.6~6.0 L·(mg·m)-1];色氨酸类芳香族蛋白质、富里酸类有机物和溶解性微生物代谢产物是海水中主要的荧光特征有机物.UF-RO工艺进水海水经Na Cl O消毒后,DBPs的种类和浓度显著增加,且增加的主要为Br-DBPs,其中三溴甲烷(CHBr3)占总三卤甲烷(THMs)的70.48%~91.50%,二溴乙酸(Br2CHCO2H)占总卤乙酸(HAAs)的81.14%~100%,二溴乙腈(C2HBr2N)占总卤乙腈(HANs)的83.77%~87.45%.UF膜对THMs、HAAs和HANs的去除率分别为36.63%~40.39%、73.83%~95.38%和100%.RO膜可以完全去除HAAs,但是对THMs不能完全去除.进水海水的抗雌激素活性为0.35~0.44 mg·L-1,氯消毒后增加了32%~69%.海水淡化UF-RO系统生成的DBPs和其他生物毒性物质最终被截留到了UF浓水和RO浓水中.     

Formation of regulated and unregulated disinfection byproducts during chlorination and chloramination: Roles of dissolved organic matter type, bromide, and iodide

Algal blooms and wastewater effluents can introduce algal organic matter (AOM) and effluent organic matter (EfOM) into surface waters, respectively. In this study, the impact of bromide and iodide on the formation of halogenated disinfection byproducts (DBPs) during chlorination and chloramination from various types of dissolved organic matter (DOM, e.g., natural organic matter (NOM), AOM, and EfOM) were investigated based on the data collected from literature. In general, higher formation of trihalomethanes (THMs) and haloacetic acids (HAAs) was observed in NOM than AOM and EfOM, indicating high reactivities of phenolic moieties with both chlorine and monochloramine. The formation of haloacetaldehydes (HALs), haloacetonitriles (HANs) and haloacetamides (HAMs) was much lower than THMs and HAAs. Increasing initial bromide concentrations increased the formation of THMs, HAAs, HANs, and HAMs, but not HALs. Bromine substitution factor (BSF) values of DBPs formed in chlorination decreased as specific ultraviolet absorbance (SUVA) increased. AOM favored the formation of iodinated THMs (I-THMs) during chloramination using preformed chloramines and chlorination-chloramination processes. Increasing prechlorination time can reduce the I-THM concentrations because of the conversion of iodide to iodate, but this increased the formation of chlorinated and brominated DBPs. In an analogous way, iodine substitution factor (ISF) values of I-THMs formed in chloramination decreased as SUVA values of DOM increased. Compared to chlorination, the formation of noniodinated DBPs is low in chloramination.     

芳香类有机物生成氯化消毒副产物特性及其与化学结构的关系

选择与腐殖酸有相似芳香结构的有机物进行氯化试验,测定其卤乙酸及三卤甲烷生成量,研究前体物化学结构与氯化消毒副产物生成特性的关系.结果表明:①主要卤乙酸生成活性排序为:对羟基苯甲酸>4-氨基苯乙酮>邻苯二酚>间苯二酚;主要三卤甲烷生成活性排序为:间苯二酚>4-氨基苯乙酮>2-羟基-4-氨基甲苯>对羟基苯甲酸.②卤乙酸的前期氯化反应速度排序为:间苯二酚>4-氨基苯乙酮>对羟基苯甲酸>邻苯二酚;三卤甲烷的前期氯化反应速度排序为:对羟基苯甲酸>2-羟基-4-氨基甲苯>间苯二酚>4-氨基苯乙酮.③对位或邻位取代基结构物质以生成卤乙酸为主;间位取代基结构物质以生成三卤甲烷为主.④苯环上羟基官能团生成消毒副产物的活性最高,酮基官能团次之;氨基官能团主要起到与其它活性官能团形成对位、邻位或间位结构的辅助作用;醛基和羧基官能团为惰性官能团;甲基官能团的作用有待深入考察.     

膜生物反应器处理城市污水的后续次氯酸钠消毒研究

针对膜生物反应器（membrane bioreactor,MBR）处理城市污水的后续次氯酸钠消毒,分别开展了不同氯的投加剂量对指示微生物（总大肠菌群和粪大肠菌群）的灭活效果、消毒副产物（disinfection by-products,DBPs）生成量以及消毒后出水发光菌急性毒性研究.结果表明,在工程应用中MBR处理工...