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首页> 外文期刊>Ozone: Science & Engineering: The Journal of the International Ozone Association >The Effect of Ozonation and Filtration on AOC (Assimilable Organic Carbon) Value of Water from Eutrophic Lake
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The Effect of Ozonation and Filtration on AOC (Assimilable Organic Carbon) Value of Water from Eutrophic Lake

机译:臭氧化和过滤对富营养化湖泊水的AOC(可同化有机碳)值的影响

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The effects of applying ozone into the source water of Cheng-Ching Lake Water Works (CCLWW) on the analysis of AOC (assimilable organic carbon) were compared in the laboratory and pilot-scale tests.CCLWW takes its raw water from an eutrophic lake.A pilot plant,established in CCLWW in southern Taiwan,was performed to improve the quality of water obtained by the former treatment processes.The direct application of ozone to the source water of CCLWW is called the pre-O_3 process.The post-O_3 process involves the treatment of effluent with ozone through a sand filter,following other treatments,including pre-O_3,coagulation and sedimentation.In a laboratory test,a 0.45 mu m membrane filter was used to replace the facility of filtration for a sand filter.AOC_(Total) comprises AOC_(P17) and AOC_(NOX),which were determined using the P.fluores-cens strain P17 and the Spirillum species strain NOX,respectively.During over 2 years' sampling in eutrophic lake,it revealed that AOC_(P17) contributed substantially to AOC_(total).However,the filtrate from the source water obtained by filtering through a 0.45 um membrane filter had an AOC_(Total) much lower than that of the source water,especially for the considerable decrease of AOC_(P17).Also,the AOC value in source water is increased with algae number but not with NPDOC (non-purgeable dissolved organic carbon).This result indicated that algae numbers existing in the eutrophic lake might affect the analysis of AOC.Following the pre-O_3 process at the pilot-scale plant,the AOC_(P17) was markedly lower than that of the source water,and AOC_(NOX) was slightly higher than that of the source water.However,when post-O_3 was added to the effluent from a sand filter at the pilot-scale plant,AOC_(NOX) exceeded that before post-O_3,while AOCP17 differed slightly from that before post-O_3.Apparently,this difference may be due to the algae number existing in the water samples.These results were verified by applying ozone to the source water,and to filtrate obtained by filtering through a 0.45 mu m membrane filter in a lab-scale test,respectively.
机译:在实验室和中试规模的试验中,比较了在正清湖自来水厂(CCLWW)的源水中添加臭氧对AOC(可吸收有机碳)分析的影响.CCLWW从富营养化的湖泊中提取其原水。在台湾南部的CCLWW中建立了一个试验工厂,以改善通过前处理过程获得的水的质量。将臭氧直接应用于CCLWW的原水称为O_3之前的过程.O_3之后的过程涉及通过沙滤器对臭氧进行处理,然后进行其他处理,包括O_3预处理,混凝和沉淀。在实验室测试中,使用0.45微米的膜式过滤器代替了沙滤器的过滤设施。 (总计)包括AOC_(P17)和AOC_(NOX),分别是通过荧光假单胞菌P17菌株和Spirillum菌种NOX确定的。在富营养化湖泊中经过2年的采样,发现AOC_(P17)和AOC_(NOX) P17)贡献了但是,通过0.45 um膜滤器过滤而得的原水滤液的AOC_(Total)大大低于原水的AOC_(Total),尤其是AOC_(P17)大大降低了。另外,源水中的AOC值随藻类数而增加,但不随NPDOC(不可净化的溶解有机碳)而增加。这表明富营养化湖泊中存在的藻类数可能会影响AOC的分析。遵循O_3之前的过程在中试规模的工厂中,AOC_(P17)显着低于原水,而AOC_(NOX)略高于原水。但是,当O_3后添加到中试规模工厂的沙滤器AOC_(NOX)超过了O_3之后的值,而AOCP17与O_3之后的值略有不同。显然,这种差异可能是由于水样中存在的藻类数量所致。通过将臭氧应用于水源进行了验证d分别通过在实验室规模的测试中通过0.45μm的膜过滤器过滤而获得的滤液。

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