饮用水中蓝藻毒素污染研究进展

日趋严重的水体富营养化已成为全球性的环境问题，藻类及藻毒素给传统净水工艺带来了诸多不利影响，增加了水处理难度。对饮用水中蓝藻毒素去除技术进行了具体的论述，系统分析了各种技术的去除效果和局限性，并对藻毒素研究前景进行了展望。     

水处理工艺去除藻毒素的效果探讨

探讨了饮用水处理的各工艺过程对藻毒素的去除作用,并根据前期已进行的实验对各工艺的优化组合进行了讨论,认为以气浮代替沉淀,并附之以粉末活性炭吸附预处理可有效地去除藻毒素;对没有条件改造沉淀池的水厂可暂时采用预氯化和粉末活性炭吸附组合的工艺也可达到较好的效果;对生物预处理工艺进行适当的强化,可达到对有机物、藻类、藻毒素等物质的有效去除.     

饮用水中柱孢藻毒素与类毒素-A控制研究进展

柱孢藻毒素和类毒素-A是目前饮用水处理领域关注的两种新兴藻类分泌毒素。柱孢藻毒素分子结构稳定、沸点高、水中溶解度高,可引起严重的急性肝中毒,同时具有较强的细胞毒性与基因毒性。类毒素-A分子量小、结构简单、神经毒性极大,被称为"极速致死因子"。鉴于其广泛存在于蓝藻生长的水源水中,其浓度与微囊藻毒素相当,对饮用水安全构成较大威胁,为此对柱孢藻毒素与类毒素-A的结构特征、毒性、检测方法及控制方法进行了综述。两种溶解性藻毒素在饮用水常规处理中均难以有效去除,氯化消毒对柱孢藻毒素的降解具有较好的效果而难以氧化类毒素-A,臭氧氧化和高级氧化对两种藻毒素的去除具有一定的效果。如何强化净水工艺中柱孢藻毒素和类毒素-A的有效控制是目前该领域新的研究方向之一。     

包埋水华鱼腥藻和活性炭对污水中氮磷的净化

采用聚乙烯醇-海藻酸钠（PVA—SA）凝胶包埋水华鱼腥藻与活性炭混合物，对比水华鱼腥藻在包埋、吸附以及悬浮状态下对高浓度模拟废水中氨氮的去除效果，实验结果表明，水华鱼腥藻在包埋状态下对氨氮有更好的去除效果。通过正交实验研究SA、粉末活性炭（PAC）、水华鱼腥藻之间不同质量比的包埋混合物对去除污水中NH4＋-N、TP以及处理后废水中微囊藻毒素（MC）残留量的影响，结果表明，当PVA量为8％时，SA、PAC和藻含量分别在0．5％、0．5％和0．2％为NH4＋-N、TP的最佳去除组合，同时处理后污水中MC的含量也低于联合国标准1Iμg／L，避免了二次污染的同时为产毒素藻类的利用创造了条件。     

藻毒素处理技术研究进展

介绍了藻毒素的结构、性质及危害,总结了其物理、化学,物理化学和生物处理方法。对藻毒素的处理技术进行了展望。微囊藻毒素（MC）处理将是未来重要的研究领域。文章最后提出了几点努力方向。     

天然水华蓝藻中微囊藻毒素的提取和净化研究

利用天然水华蓝藻为原料，通过筛选、比较不同极性提取剂对微囊藻毒素的提取效果，80％甲醇溶液有较高的提取效率，而乙醇溶液可实现无毒提取，优化了提取方法。并通过调节溶液pH为藻胆蛋白等电点的方法去除共提取的大量藻胆蛋白，取得了很好的净化效果，为微囊藻毒素的分离和纯化研究提供了基础。     

浙江省蓝藻水华应急与预警监测

蓝藻水华污染可产生多种藻毒素,其中以微囊藻毒素的危害最为严重.通过对近年来国内外关于水体中微囊藻毒素检测技术的系统介绍以及优缺点分析,结合浙江省实情,提出了在浙江省开展蓝藻水华应急与预警监测的初步方案,以有效防范微囊藻毒素给水环境及人类健康带来的威胁.     

光反应器中UV/Fenton光降解湖水中微囊藻毒素的研究

在光催化反应器中,采用UV/Fenton光催化氧化技术,对湖水中微囊藻毒素的光催化降解过程中各影响因子分析表明:微囊藻毒素光催化氧化降解率受光照强度、氧化剂种类及浓度、溶液pH和不同光催化体系等多因素的影响.光促催化氧化体系对MC-LR藻毒素降解具有显著的作用,在紫外光与氧化剂的协同作用下,紫外光照强度越高,越易于促进MC-LR藻毒素快速降解,降解率可到达80%以上.     

微囊藻毒素的产生及其影响因子

介绍了光照、温度、营养元素、pH值等环境因子对微囊藻的生长及其毒素生成的影响.一定强度的光照促进毒素的合成,微囊藻生长在较低的温度或营养元素受限制时,生长速率下降,但毒素产率较高.微囊藻毒素的含量在藻的指数生长后期与稳定期达最大值,毒素产率则在指数生长初期达最大.不同环境因子可能通过不同途径影响毒素的产生,需进一步研究藻毒素的功能及合成途径.     

滇池铜绿微囊藻（Microcystis aeruginosa Kueitz）毒素及其在水体中的变化

本文研究了昆明市滇池富营养化所形成水华的主要蔬菜－铜绿微囊藻（Microcystis aeruginosa Kueitz)的毒素及其在水体的变化。经研究,滇池铜绿微囊藻的提取液有一个毒峰出现,用双波长紫外分光光度计测定,发现于240nm出现一个毒峰。用色质谱联用扫描得出,其分子离子峰为1040M／Z。用小白鼠注入藻类提取液进行试验,发现其肝脏肿大,并呈紫褐色。再将肝脏匀浆提取液用高压液相色谱测定,发现有毒峰出现。在不同季节、不同地点,采取湖水,经过滤后（去除藻类和碎屑）进行测定,结果得出：在藻类生长旺季及生长繁茂的地点,水体中藻毒素的含量较高。而在藻类生长淡季及分布较少的地点,水中藻毒素含量则较少。但总的看来,经过过滤后的湖水,其中藻毒素含量少。     

TiO2光催化技术处理饮用水微污染及杀灭微生物的研究

光催化处理饮用水微量污染物以及在饮用水消毒和杀菌方面的研究是近年来研究的热点.本文论述了 TiO2光催化处理饮用水中的微量卤代物、腐殖质、微生物代谢产物,以及杀灭细菌、真菌和病毒等微生物的研究进展.探讨了光催化杀灭微生物的作用机制,最后对该研究领域的发展方向提出建议和展望.     

Distribution of polycyclic aromatic hydrocarbons in surface water and sediment near a drinking water reservoir in Northeastern China

The levels of polycyclic aromatic hydrocarbons (PAHs) in the water and the sediment samples collected near the Mopanshan Reservoir—the most important drinking water resource of Harbin City in Northeast China—were examined. A total of 16 PAHs were concurrently identified and quantified in the three water bodies tested (Lalin River, Mangniu River, and Mopanshan Reservoir) and in the Mopanshan drinking water treatment plant during the high- and low water periods. The total PAH concentrations in the water and sediment samples ranged from 122.7 to 639.8 ng/L and from 89.1 to 749.0 ng/g dry weight, respectively. Similar spatial and temporal trends were also found for both samples. The lowest Σ₁₆PAH concentration of the Mopanshan Reservoir was obtained during the high water period; by contrast, the Lalin River had the highest concentration during the low water period. The PAH profiles resembling the three water bodies, with high percentages of low-molecular weight PAHs and dominated by two- to three-ring PAHs (78.4 to 89.0 %). Two of the molecular indices used reflected the possible PAH sources, indicating the main input from coal combustion, especially during the low water period. The conventional drinking water treatment operations resulted in a 20.7 to 67.0 % decrease in the different-ringed PAHs in the Mopanshan-treated drinking water. These findings indicate that human activities negatively affect the drinking water resource. Without the obvious removal of the PAHs in the waterworks, drinking water poses certain potential health risks to people.     

Minimization of the formation of disinfection by-products

The drinking water industry is required to minimize DBPs levels while ensuring adequate disinfection. In this study, efficient and appropriate treatment scheme for the reduction of disinfection by-product (DBPs) formation in drinking water containing natural organic matter has been established. This was carried out by the investigation of different treatment schemes consisting of enhanced coagulation, sedimentation, disinfection by using chlorine dioxide/ozone, filtration by sand filter, or granular activated carbon (GAC). Bench scale treatment schemes were applied on actual samples from different selected sites to identify the best conditions for the treatment of water. Samples were collected from effluent of each step in the treatment train in order to analyze pH, UV absorbance at 254 nm (UVA₂₅₄), specific UV absorbance at 254 nm (SUVA₂₅₄), dissolved organic carbon (DOC), haloacetic acids (HAAs) and trihalomethanes (THMs). The obtained results indicated that using pre-ozonation/enhanced coagulation/activated carbon filtration treatment train appears to be the most effective method for reducing DBPs precursors in drinking water treatment.     

Detection of mutagens in unconcentrated and concentrated drinking water supplies before and after treatment using a microscale fluctuation test

The aim of this work was to study three different concentration methods coupled with the microscale fluctuation test for routine screening of different drinking water supplies before and after treatment. Unconcentrated samples were also tested. The results showed the formation of direct-acting mutagens in drinking water from surface sources after chlorination.     

Effects of oxalic acid on the regrowth of heterotrophic bacteria in the distributed drinking water

Three laboratory-scale water pipe systems were set up to study the effects of adding oxalic acid on the bacterial regrowth and biofilm formation in the distributed drinking water. The results of water pipe experiment displayed that around 38% carbon in the oxalic acid could be converted to bacterial biomass. The maximum HPCs in biofilm were equal to 3.5x10(4), 3.38x10(5) and 2.8x10(6) CFUcm(-2) while the maximum HPCs of free bacteria were equal to 1.2x10(3), 2.54x10(3) and 3.78x10(4) CFUml(-1) for the blank and with addition of 10 and 50 micrograms OA eq-Cl(-1), respectively. These results imply that the addition of oxalic acid to distributed water has positive effect on the assimilable organic carbon content of drinking water and bacterial regrowth in water pipe. This effect is enhanced with addition of high-level oxalic acid. Batch tests were also conducted using water samples collected from a Taiwanese drinking water distribution system. The bacterial regrowth potentials (BRPs) of the blank were equal to 4.25x10(3), 1.46x10(4), 4.9x10(4) and 7.54x10(4) CFUml(-1) for water samples collected from treatment plant effluent, commercial area, mixed area, and residential area, respectively. These results show that the biological stability of distributed drinking water is the highest in treatment plant effluent, the moderate in the commercial area and mixed area, and the lowest in the residential area.     

The use of XAD-resins for the detection of mutagenic activity in water: II. Studies with drinking water

The combined XAD-4/8-Ames test procedure for concentrating and detecting trace amounts of organic mutagens, as already described for surface water, is shown to be suitable for drinking water as well. DMSO is as effective as acetone in eluting the adsorbed mutagens, and optimal recovery of overall mutagenic activity is observed at a flow rate of 2–4 bed volumes/min. The drinking water of 6 cities in The Netherlands, which prepare their drinking water from the rivers Rhine and Meuse, has been tested for mutagenic activity. Mutagenic activity could be demonstrated in 4 cities. Dose-related responses are observed with concentrates of as little as 500 ml of drinking water and the 4 cities clearly differ with regard to the type of mutations induced (TA 98 or TA 100) and the effect of metabolic activation. The absence of mutagenic activity in drinking water of 2 cities indicates that by a proper combination of treatment processes the organics which are responsible for the detected mutagenic activity in drinking water can be removed to a high degree.     

中国南方某城市自来水厂处理工艺对多环芳烃的去除效果研究

讨论了中国南方某城市自来水厂饮用水中的多环芳烃残留规律以及现有净水工艺对多环芳烃的去除效果。研究结果表明,该自来水厂饮用水中检出多环芳烃以2~4环芳烃为主,强致癌性高环数多环芳烃均在检出限以下,且多环芳烃总量未超出中国供水行业标准(2000年)的相关限值。各处理工艺段中,砂滤过程对多环芳烃的去除效果最好,相较于原水对多环芳烃总量的去除率可达64%。     

西北干旱地区农宅雨水转化为可饮水技术

雨水集流工程对于解决干旱地区人民生活用水问题起着重要作用,甘肃省兰州市榆中县北山地区处于严重缺水的地区,人畜的饮用水为雨水、雪水直接沉淀后的水窖水。经过对北山饮用水进行水质检测,发现水中浊度、锰含量、微生物数量均超过《生活饮用水卫生标准》(GB5749-2006)的规定值。通过对传统滤池进行改造并结合阳光消毒研制出了一种新型水处理器——阳光消毒-生物砂滤池(SBF)家庭水处理设备,通过生物砂滤池中微生物对雨水中污染物的氧化分解及河砂的过滤使水浊度及锰得到有效地去除,日光高温灭活和光氧化降解综合作用杀灭水中致病微生物。用SBF家庭水处理设备对雨水进行处理,水中浊度、锰含量、微生物数量均达到标准的规定值。     

Influence of seasonal climate differences on the pharmaceutical,hormone and personal care product removal efficiency of a drinking water treatment plant

The potential presence of pharmaceuticals, hormones and personal care products in drinking water supplies has raised concerned over the efficiency with which these substances are removed by water treatment processes. In this work, we analyzed samples of raw, unprocessed water collected in different periods and found them to contain higher levels of these contaminants in the colder periods (viz. 12–314 ng L⁻¹ in autumn and winter as compared to 8–127 ng L⁻¹ in spring and summer) as a result of their biodegradation being favoured by high temperatures and solar irradiance. We also assessed the efficiency with which these contaminants are removed from drinking water by a water treatment plant operating in south-eastern Spain. Preoxidation with potassium permanganate and chloramination with sodium hypochlorite in the presence of highly concentrated ammonia were found to be the treatment steps most markedly contributing to the removal of pharmaceuticals, hormones and personal care products from drinking water (especially in the warmer periods, where these contaminants were completely removed from the water). By contrast, water treated in the colder periods (autumn and winter) still contained small amounts of ibuprofen and carbamazepine (0.09–0.5 ng L⁻¹) which, however, accounted for less than 0.2% of their original concentrations in the water prior to treatment.