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硫酸盐还原菌包埋固定化技术处理含铬废水 被引量:14

Treatment of chromium wastewater by immobilized sulfate-reducing bacteria-containing activated sludge
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摘要 分别以海藻酸钠和聚乙烯醇(PVA)为包埋剂,采用蠕动泵滴加,包埋固定经驯化后的硫酸盐还原菌(SRB)占优的活性污泥。以小球强度、传质性能、成球难易为指标定性确定包埋条件。评价海藻酸钙(CA)法、PVA法、PVA混合载体法包埋小球对含铬废水的处理效果。结果表明以Cr(VI)去除率为考核指标,PVA混合载体为最好的包埋方式,其最优条件是PVA质量浓度为9%、包泥量为1∶1,添加少量的海藻酸钠,SiO2,CaCO3和粉末活性炭(PAC)有利于颗粒球传质与耐用性能的提高。在连续化处理含铬废水的工艺中,进水COD质量浓度为500mg/L,SO24-为500mg/L,Cr(Ⅵ)为100mg/L,水力滞留时间为6h的条件下,Cr(Ⅵ)的去除率为99.68%,出水总Cr质量浓度为0.45mg/L,COD质量浓度为187mg/L,同时铬以沉淀的形式与颗粒球分离有利于铬的回收。 The immobilized sulfate reducing bacteria (SRB)-containing activated sludge beads were prepared using sodium alginate and polyvinyl alcohol (PVA) as entrapment agent. The optimal conditions were chosen in terms of the mechanical stability, mass transfer, and difficulty of form ing beads. In addition, the treatment of chromium-containing wastewater by immobilized beads was investigated. The results show that PVA is considered the best support according to the removal of chromium, the optimal conditions are 9% PVA, ratio of immobilized cells to entrapping agents of 1 : 1, and sodium alginate, SiO2, CaCO3 and powder active carbon (PAC) is added to improve the mass transfer and its durability, respectively. In the continuous experiments, the PVA mixed carrier process can effectively remove 100 mg/L Cr(Ⅵ) under the conditions of 500 mg/L sulfate, 500 mg/L chemical oxygen demand (COD) and 6 h hydraulic rest time (HRT). In drainage outlet, the removal rate of Cr(Ⅵ)gets to 99.68%, and the total Cr concentration and COD are 0.45 mg/L and 187 mg/L respectively. Chromium is separated from beads in the form of Cr(OH)3, which is beneficial to the recycle of chromium.
出处 《中南大学学报(自然科学版)》 EI CAS CSCD 北大核心 2005年第6期965-970,共6页 Journal of Central South University:Science and Technology
基金 湖南省科技计划重点资助项目(02CTY2003)
关键词 硫酸盐还原菌 包埋 海藻酸钠 聚乙烯醇 含铬废水 sulfate reducing bacteria immobilization sodium alginate PVA chromium-containing wastewater
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  • 1Ueki K,Ueki A.Removal of sulfate and heavy metal from acid mine water by anaerobic treatment with cattle waste:Effects of heavy metals on sulfate reduction[J].Environ Sci Health,1991,A26(8):1471-1489. 被引量:1
  • 2Dvorak D H,Hedin,R S.Treatment of metal-contaminated water using bacterial sulfate reduction:Results from pilot-scale reactor[J].Biotechnology and Bioengineering,1992,40(5):609-616. 被引量:1
  • 3Leenen E J,Dos Santos V,Grolle K,et al.Characteristics and selection criteria for support materials for cell immobilization in wastewater treatment[J].Wat Res,1996,30(12):2985-2996. 被引量:1
  • 4Wang D.Recent advances in immobilized cells[J].Biotechnology and Bioengineering,1991,38(4):261-269. 被引量:1
  • 5王建龙著..生物固定化技术与水污染控制[M].北京:科学出版社,2001:326.
  • 6WANG Jian-long.Biodegradation of plasticizer di-butyl phthalate (DBP) by immobilized microbial cells[J].Toxicological and Environmental Chemistry,2000,74(5):195-202. 被引量:1
  • 7Kawakami K,Tsuruda S,Miyag K.Immobilization of microbial cells in a mixed matrix of silicone polymer and calcium alginate gel.epoxidation of 1-ocetene by nocardia coralline B-276 in organic media[J].Biotechnology Progress,1990,5(6):357-361. 被引量:1
  • 8Abian O,Mateo C,Fernandez-Lorente G,et al.Stabilization of immobilized enzymes against water-soluble organic cosolvents and generation of hyperhydrophilic micro-environments surrounding enzyme molecules[J].Biocatalysis and Biotransformation,2001,19 (5):489-503. 被引量:1
  • 9Geoffrey W G,Geoffrey A C,Geoffrey M G.Accumulation of cobalt,zinc and manganese by the estuarine green microalgae Chlorella salina immobilized in alginate microbeads[J].Environ Sci Technol,1992,26(5):1764-1770. 被引量:1
  • 10Wong P K.Removal and recovery of Cu (Ⅱ) from industrial effluent by immobilized cells of Psedomonas Putida Ⅱ-11[J].Applied Microbiology Biotechnology,1993,39(9):127-131. 被引量:1

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