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Disinfection by-products and microbial contamination in the treatment of pool water with granular activated carbon

机译:用粒状活性炭处理池水中的消毒副产物和微生物污染

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摘要

For swimming pools, it is generally agreed that free chlorine levels have to be maintained to guarantee adequate disinfection. Recommended free chlorine levels can vary between 0.3 and 0.6 mg/L in Germany and up to 3 mg/L in other countries. Bathers introduce considerable amounts of organic matter, mainly in the form of such as urine and sweat, into the pool water. As a consequence, disinfection byproducts(DBPs) are formed. Regulations in Germany recommend levels of combined chlorine of less than 0.2 mg/L and levels of trihalomethanes (THMs) of less than 20 mu g/L Haloacetic acids (HAAs), haloacetonitriles (HANs), chloropicrin and chloral hydrate are also detected in considerable amounts. However, these compounds are not regulated yet. Swimming pool staff and swimmers, especially athletes, are primarily exposed to these byproducts by inhalation and/or dermal uptake. In Germany, new regulations for swimming pool water treatment generally require the use of activated carbon. In this project, three different types of granular activated carbon (GAC) (one standard GAC, two catalytic GACs) are compared for their long time behaviour in pool water treatment. In a pilot plant operated with real swimming pool water, production and removal of disinfection byproducts (THMs, HAAs, AOXs), of biodegradable substances (AOC), of bacteria (Pseudomonas aeruginosa, Legionella, coliforms, HPC) as well as the removal of chlorine and chloramines are monitored as function of GAC bed depth. Combined chlorine penetrates deeper in the filter bed than free chlorine does. However, both, free and combined chlorine removal efficiencies decrease over the time of filter operation. The decreases of removal efficiencies are also observed for parameters such as dissolved organic carbon, spectral absorption coefficient, adsorbable organic carbon and most of the disinfection byproducts. However, THMs, especially chloroform are produced in the filter bed. The GAC beds were contaminated microbially, especially with P. aeruginosa. The contamination was not removable by backwashing with chlorine concentrations up to 2 mg/l free chlorine.
机译:对于游泳池,普遍同意必须保持游离氯水平以保证充分消毒。推荐的游离氯含量在德国为0.3至0.6 mg / L,在其他国家则为3 mg / L。沐浴者将大量的有机物(主要以尿液和汗水等形式)引入游泳池水中。结果,形成了消毒副产物(DBP)。德国的法规建议合并氯的含量应低于0.2 mg / L,三卤甲烷(THM)含量应低于20μg / L卤代乙酸(HAAs),卤代乙腈(HANs),氯吡啶和水合氯醛含量也很高金额。但是,这些化合物尚未受到监管。游泳池工作人员和游泳者,尤其是运动员,主要通过吸入和/或皮肤吸收而暴露于这些副产物。在德国,游泳池水处理的新法规通常要求使用活性炭。在该项目中,比较了三种不同类型的颗粒活性炭(GAC)(一种标准GAC,两种催化GAC)在泳池水处理中的长时间行为。在使用实际游泳池水操作的中试工厂中,生产和去除消毒副产物(THM,HAA,AOX),可生物降解物质(AOC),细菌(铜绿假单胞菌,军团菌,大肠菌,HPC)以及去除氯和氯胺是根据GAC床深度进行监测的。结合的氯比游离氯更深地渗透到滤床中。但是,自由和联合去除氯的效率均会随着过滤器的运行时间而降低。对于诸如溶解的有机碳,光谱吸收系数,可吸附的有机碳和大多数消毒副产物之类的参数,还观察到去除效率的降低。但是,THM,特别是氯仿会在滤床上产生。 GAC床被微生物污染,尤其是铜绿假单胞菌。不能通过用浓度高达2 mg / l的游离氯进行反冲洗来清除污染物。

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