饮水中的挥发性卤代烃研究

阐述了源水氯化消毒过程中产生挥发性卤代烃机理，通过模拟清毒处理，研究了各种环境条件下如活性氯浓度，ｐＨ值，时间等对卤代烃形成的影响，对氯仿挥发动力学做了初步探讨，同时对具有相同过程的游泳池中的卤代烃也作了含量调查。     

氯化消毒饮用水中强致突变物MX[3-氯-4-(二氯甲基)-5-羟基-2(5H)-呋喃酮]的形成

利用一系列XAD吸附树脂及大孔阴、阳离子交换树脂,将太湖水中溶解态有机物分离为溶解态富里酸类、腐殖酸类、憎水弱酸类、憎水碱类、憎水中性物类、亲水酸类、亲水碱类七种组分,分别对不同组分的有机物进行氯化处理后,用GC/MS选择离子峰面积法测定了产物中的MX[3-氯-4-（二氯甲基）-5-羟基-2（5H）-呋喃酮]。结果表明,太湖水体中的溶解态腐殖酸类可能是生成MX的重要前驱物。     

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).     

Formation potentials of typical disinfection byproducts and changes of genotoxicity for chlorinated tertiary effluent pretreated by ozone

The effects of ozonation on the formation potential of typical disinfection byproducts (DBPs) and the changes of genotoxicity during post chlorination of tertiary effluent from a sewage treatment plant were investigated. Ozonation enhanced the yields of all detected chlorine DBPs except CHCl3. At a chlorine dose of 5 mg/L, the three brominated THMs and five HAAs increased, while chloroform decreased with the increase of ozone dose from 0 to 10 mg/L (ozone dose in consumption base). At a chlorine dose of 10 ...     

Formation potentials of typical DBPs and changes of genotoxicity for chlorinated tertiary effluent pretreated by ozone

The effects of ozonation on the formation potential of typical disinfection byproducts (DBPs) and the changes of genotoxicity during post chlorination of tertiary effluent from a sewage treatment plant were investigated. Ozonation enhanced the yields of all detected chlorine DBPs except CHCl3. At a chlorine dose of 5 mg/L, the three brominated THMs and five HAAs increased, while chloroform decreased with the increase of ozone dose from 0 to 10 mg/L (ozone dose in consumption base). At a chlorine dose of 10 mg/L, the two mixed bromochloro species THMs and two dominant HAAs (DCAA and TCAA) firstly increased and then decreased with the increase of ozone dose, with the turning point approximately occurring at an ozone dose of 5 mg/L. The genotoxicity detected using umu test, on the other hand, was removed from 7 μg 4-NQO/L to a negligible level by ozonation under an ozone dose of 5 mg/L. Chlorination could further remove the genotoxicity to some extent. It was found that SUVA (UV absorbance divided by DOC concentration) might be used as an indicative parameter for monitoring the removal of genotoxicity during the oxidation.     

Cancer risk assessment from exposure to trihalomethanes in tap water and swimming pool water

We investigated the concentration of trihalomethanes （THMs） in tap water and swimming pool water in the area of the Nakhon Path- om Municipality during the period April 2005-March 2006. The concentrations of total THMs, chloroform, bromodichloromethane, dibromochloromethane and bromoform in tap water were 12.70-41.74, 6.72-29.19, 1.12-11.75, 0.63-3.55 and 0.08-3.40 μg/L, respectively, whereas those in swimming pool water were 26.15-65.09, 9.50-36.97, 8.90-18.01, 5.19-22.78 and ND-6.56 μg/L, respectively. It implied that the concentration of THMs in swimming pool water was higher than those in tap water, particularly, brominated-THMs. Both tap water and swimming pool water contained concentrations of total THMs below the standards of the World Health Organization （WHO）, European Union （EU） and the United States Environmental Protection Agency （USEPA） phase Ⅰ, but 1 out of 60 tap water samples and 60 out of 72 swimming pool water samples contained those over the Standard of the USEPA phase Ⅱ. From the two cases of cancer risk assessment including Case Ⅰ Non-Swimmer and Case Ⅱ Swimmer, assessment of cancer risk of nonswimmers from exposure to THMs at the highest and the average concentrations was 4.43×10^-5 and 2.19×10^-5, respectively, which can be classified as acceptable risk according to the Standard of USEPA. Assessment of cancer risk of swimmers from exposure to THMs at the highest and the average concentrations was 1.47×10^-3 and 7.99×10^-4, respectively, which can be classified as unacceptable risk and needs to be improved. Risk of THMs exposure from swimming was 93.9%-94.2% of the total risk. Cancer risk of THMs concluded from various routes in descending order was： skin exposure while swimming, gastro-intestinal exposure from tap water intake, and skin exposure to tap water and gastro-intestinal exposure while swimming. Cancer risk from skin exposure while swimming was 94.18% of the total cancer risk.     

Trihalomethane formation potential of organic fractions in secondary effluent

Organic matter is known to be the precursor of numerous chlorination by-products. Organic matter in the secondary e uent from the Wenchang Wastewater Treatment Plant (Harbin, China) was physically separated into the following fractions: particulate organic carbon (1.2–0.45 m), colloidal organic carbon (0.45–0.1 m), fine colloidal organic carbon (0.1–0.025 m), and dissolved organic carbon (DOC) (< 0.025 m). Moreover, < 0.45 m fraction was chemically separated into hydrophobic acid (HPO-A), hydrophobic neutral (HPO-N), transphilic acid (TPI-A), transphilic neutral (TPI-N), and hydrophilic fraction (HPI). The chlorine reactivity of these organic fractions obtained from both size and XAD fractionations were evaluated. The structural and chemical compositions of the HPO-A, HPO-N, TPI-A, and TPI-N isolates were characterized using elemental analysis (C, H, O, and N), Fourier transform infrared spectroscopy (FT-IR), and proton nuclear magnetic resonance spectroscopy (1H-NMR). Results showed that DOC was dominant in terms of total concentration and trihalomethane formation potential (THMFP), and there was no statistical di erence in both specific THMFP (STHMFP) and specific ultraviolet light absorbance among the 0.45, 0.1, and 0.025 m filtrates. HPO-A had the highest STHMFP compared to other chemical fractions. HPO-A, HPO-N, TPI-A, and TPI-N contained 3.02%–3.52% of nitrogen. The molar ratio of H/C increased in the order of HPO-A < HPO-N < TPI-A < TPI-N. The O/C ratio was relatively high for TPI-N as compared to those for the other fractions. 1H-NMR analysis of the four fractions indicated that the relative content of aromatic protons in HPO-A was significantly higher than those in the others. The ratio of aliphatic to aromatic protons increased in the order of HPO-A < HPO-N < TPI-A < TPI-N. FT-IR analysis of the four fractions showed that HPO-A had greater aromatic C==C content whereas HPO-N, TPI-A, and TPI-N had greater aliphatic C–H content. TPI-N contained more oxygen-containing functional groups than the other fractions.     

地下水氨氮污染及处理技术综述

综述了地下水中氨氮的污染现状,主要阐述了吸附和离子交换法、折点加氯法和生物脱氮法的原理和各自的优缺点,指出应将这些方法结合起来,开发高效、经济、稳定、操作简便的氨氮脱除技术。     

Effect of ferric and bromide ions on the formation and speciation of disinfection byproducts during chlorination

The e ects of ferric ion, pH, and bromide on the formation and distribution of disinfection byproducts (DBPs) during chlorination were studied. Two raw water samples from Huangpu River and Yangtze River, two typical drinking water sources of Shanghai, were used for the investigation. Compared with the samples from Huangpu River, the raw water samples from Yangtze River had lower content of total organic carbon (TOC) and ferric ions, but higher bromide concentrations. Under controlled chlorination conditions, four trihalomethanes (THMs), nine haloacetic acids (HAAs), total organic halogen (TOX) and its halogen species fractions, including total organic chlorine (TOCl) and total organic bromide (TOBr), were determined. The results showed that co-existent ferric and bromide ions significantly promoted the formation of total THMs and HAAs for both raw water samples. Higher concentration of bromide ions significantly changed the speciation of the formed THMs and HAAs. There was an obvious shift to brominated species, which might result in a more adverse influence on the safety of drinking water. The results also indicated that high levels of bromide ions in raw water samples produced higher percentages of unknown TOBr.     

水中利谷隆氯化降解动力学和消毒副产物生成特性

采用常用消毒剂次氯酸钠对含氮除草剂利谷隆开展了氯化降解实验研究,系统考察了加氯量、p H值、加Br-量以及温度对降解效果的影响,分析了氯化反应过程中消毒副产物生成特性.结果表明,次氯酸钠对利谷隆的氧化降解过程符合二级反应动力学;p H值对该降解反应影响较大,当p H值为7时反应速率最快,其中HOCl、OCl-与利谷隆的基元反应速率常数分别为4.84×102L·(mol·h)-1和3.80×102L·(mol·h)-1.在添加溴离子时,反应速率随着溴离子的加入逐渐减小.改变温度时,反应速率随着温度的增加而逐渐增大.利谷隆在氯化降解过程中可产生三氯甲烷、二氯乙腈、三氯硝基甲烷、卤代丙酮等多类型消毒副产物.在不同p H值和添加溴离子条件下,消毒副产物种类与浓度会出现显著差异.