首页> 外文会议>1997 water quality technology conference (WQTC 1997) >EVALUATION OF TEMPERATURE AND SYSTEM CONDITIONS ON DBP FORMATION IN SURFACE WATER USING THE RAPID BENCH SCALE MEMBRANE TEST FOR ICR TREATMENT STUDIES
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EVALUATION OF TEMPERATURE AND SYSTEM CONDITIONS ON DBP FORMATION IN SURFACE WATER USING THE RAPID BENCH SCALE MEMBRANE TEST FOR ICR TREATMENT STUDIES

机译:利用快速弯管规模膜试验对地表水中DBP形成的温度和系统条件进行评估

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The Information Collection Rule (ICR) was published in the Federal Registerrnon May 14, 1996, and will require some public water supplies to conduct DBPrn(Disinfection By-Product) precursor removal studies (i.e. treatment studies)rnbeginning in May 1998 (1). The objective of these treatment studies is tornprovide the EPA with cost and performance data using either membranernprocesses or granular activated carbon (GAC) in order to meet the Stage 2rnDBP maximum contaminant levels (MCLs) for the sum of the fourrntrihalomethanes (THMs) at 40 ug/L and the sum of the five haloacetic acidsrn(HHA5) at 30 ug/L. The Rapid Bench Scale Membrane Test (RBSMT) will bernrequired for utilities with treated water total organic carbon (TOC) above 6-8rnmg/L.rnThe ICR Manual for Bench-and-Pilot Scale Treatment Studies states that therntreatment study feed water collected for the RBSMT must be representativernof the source under investigation. A volume of 90 to 110 gallons of waterrnmust be collected for the test. The initial chemistry water quality parametersrnthat must be taken into account in order to assess pretreatment of therninfluent water to the RBSMT are listed in Table 2. Since many of thesernanalytes are in EPA methods that require immediate cooling of the sample torn4℃, sample transportation in a temperature-controlled environment wouldrnbe necessary. The result is increased cost and additional problems withrnmonitoring and maintaining a constant temperature during transport of arnlarge volume of water.rnIt is unclear in the ICR Manual whether the SDS procedure is required forrnthe RBSMT or if UFC can be used or modified to provide constant chlorinationrnconditions to allow for the assessment of DBP breakthrough patterns in arnPWS. If SDS conditions are required it will be difficult for laboratories tornperform because SDS conditions change over time and if several bench-scalernsamples from different utilities are being evaluated simultaneously, each willrnrequire a specific incubation temperature, incubation time, pH, and finalrnchlorine residual.rnThe two issues under study in this paper are 1) the effects of samplerntransportation temperature on the integrity of source water used in thernRBSMT treatment studies and 2) a comparison between the DBPs formedrnunder actual plant conditions (simulated distribution system conditions-SDS)rnand those formed under the standard UFC (uniform formation conditions).rnA representative surface water sample was chosen for the studies. For the
机译:信息收集规则(ICR)于1996年5月14日在《联邦登记册》上发布,从1998年5月开始将需要一些公共供水来进行DBPrn(消毒副产物)前体去除研究(即治疗研究)(1)。这些处理研究的目的是使用膜工艺或颗粒活性炭(GAC)向EPA提供成本和性能数据,以使40 ug的三卤代甲烷(THM)的总和达到第2阶段DBP最大污染物水平(MCL)。 / L和30 ug / L下的五种卤代乙酸(HHA5)的总和。对于经过处理的水总有机碳(TOC)高于6-8rnmg / L的公用事业,将需要快速台秤膜测试(RBSMT)。 RBSMT必须代表被调查来源。必须收集90至110加仑的水进行测试。表2列出了为评估RBSMT的流入水的预处理而必须考虑的初始化学水质量参数rn。由于许多分析物均采用EPA方法,需要立即冷却样品至4℃,因此在温度受控的环境将是必要的。结果是成本增加,并且在运输大量水的过程中存在监测和保持恒温的附加问题。在ICR手册中尚不清楚RBSMT是否需要SDS程序,或者是否可以使用或修改UFC以提供恒定的氯化条件,允许评估arnPWS中的DBP突破模式。如果需要SDS条件,由于SDS条件会随着时间变化而变化,并且由于要同时评估来自不同公用事业的多个台式样品,每个实验室都将需要特定的孵育温度,孵育时间,pH值和最终的氯残留量,这将使实验室变得难以运作。本文研究的问题是1)样品运输温度对RBSMT处理研究中使用的水源完整性的影响,以及2)在实际工厂条件下(模拟分配系统条件-SDS)和在实际工厂条件下形成的DBP之间的比较。标准UFC(均匀地层条件)。rn研究选择了代表性的地表水样品。为了

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