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臭氧/改性粘土/生物炭工艺处理富营养化水体 被引量:2

Combined Process of Ozonation,Modified Clay and Biological Activated Carbon for Treating Eutrophic Water
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摘要 针对富营养化水体的水质特征,构建了臭氧预氧化/改性粘土/臭氧一生物活性炭组合工艺,并用于处理常州科教城的景观河水。结果表明,在进水流量为50L/h、预氧化的臭氧投量为1.2mg/L、改性粘土投量为1.2g/L、臭氧一生物活性炭段的臭氧投量为2mg/L的条件下,当进水浊度为29~38NTU、CODM。为6~9mg/L、TN为3.47~3.60mg/L、TP为0.21~0.25mg/L、藻类为(3~10)×10。个/L时,该工艺对浊度、CODM。、TN、TP和藻类的去除率分别为97.5%、77.7%、81.9%、95.4%和99.2%,出水水质达到了《地表水环境质量标准》(GB3838--2002)的I类或Ⅱ类标准。 Aimed at the characteristics of eutrophic water, the combined process of ozonation, modified clay, ozone/biological activated carbon was built and used to treat the landscape river water in Changzhou Science and Education City. The results show that under the conditions of 50 L/h influent flow rate, 1.2 mg/L ozone dosage in ozonation pretreatment, 1.2 g/L modified clay dosage and 2 mg/L ozone dosage in ozone/biological activated carbon process, the removal rates of turbidity, CODMn, TN, TP and algae are 97.5% , 77.7% , 81.9% , 95.4% and 99.2% respectively when the influent turbidity, CODMn, TN, TP and algae are 29 to 38 NTU, 6 to 9 mg/L, 3.47 to 3.60 mg/L, 0.21 to 0.25 mg/L and (3 to 10) × 10^8 ind./L respectively. The effluent quality meets the I or 11 criteria specified in the Environmental Quality Standards for Surface Water ( GB 3838 - 2002 ).
出处 《中国给水排水》 CAS CSCD 北大核心 2010年第19期87-89,共3页 China Water & Wastewater
基金 国家水体污染控制与治理科技重大专项(2008ZX07421-002)
关键词 臭氧 改性粘土 生物活性炭 富营养化水体 ozone modified clay biological activated carbon eutrophic water
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