期刊文献+

固定化微生物吸附剂对Cr^(3+)的吸附特性研究 被引量:4

On the characteristics of the adsorption of Cr^(3+) by immobilized microorganism adsorbents
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摘要 从皮革铬鞣、复鞣污泥等处分离、纯化出4株菌株TP、XB、MY和TQ,采用海藻酸钠悬滴法并添加膨润土制成微生物固定化吸附剂,研究该吸附剂对低质量浓度Cr3+的吸附特性。结果表明,4种固定化颗粒对低质量浓度Cr3+有较好的吸附作用。实验室条件下,当吸附温度为30℃时,6 h后固定化吸附剂进入缓慢吸附和平衡吸附阶段。吸附等温曲线拟合研究表明,不同温度下吸附剂适合不同的等温模型。4种微生物吸附剂均与Lagrange拟二级动力学模型拟合最佳,且吸附量从高到低为TQ、TP、XB、MY。颗粒内扩散模型研究表明,20℃下XB和MY对Cr3+的吸附分为快速吸附和缓慢吸附阶段;30℃和40℃下固定化颗粒均呈现表面吸附—缓慢吸附—平衡吸附过程。热力学研究表明,吸附反应均属于自发进行的吸热过程,并且均是化学吸附。 This article is aimed to reduce the low concentrated Cr3 + in the environment by using new composite immobilized microorgan- ism adsorbents, that are, the 4 kinds of microorganism adsorbents (TP, XB, MY and TQ) isolated from the chrome-tanned leather building section and the activated sludge from the sewage. In this ar- ticle, we have adopted the sodium alginate pendant-drop method to produce the immobilized microorganism adsorbents added by bentonite in hoping to improve the adsorption efficiency. The results of our ex- periment and analysis show that the 4 immobilized microorganism ad- sorbents turn to be effective to adsorb the low concentrated Cr3 + in the l!quid phase. In laboratory conditions, the said results indicate that at 30 % the adsorption of Cr3 + by immobilized microorganism adsorbents has entered into the slow adsorption and equilibrium ad- sorption phases during the 6 h period and the mass concentration of Cr3+ in the residual solution after TP, XB, MY, TQ adsorbing turned to drop from 5 mg/L to 0.47 mg/L, 1.19 mg/L, 1.54 mg/L and 0.23 mg/L, respectively. In the process, the adsorption rate of all the immobilized microorganism adsorbents may have been over 70% . In our experiments, we have used 2 adsorption isotherm mod- els (Langmuir and Freundlich isotherm models) to fit the experimen- tal data. As a result, different kinds of adsorbents should be made suitable h)r the different models at the temperatures of 20 - 40 ℃ , thus showing it was easy to proceed with the adsorption process of Cr3+ by immobilized adsorbent particles. Besides, the kinetic study results were found in much better agreement with Lagrange pseudo- second-order model than with Lagrange pseudo-first-order model with the order of adsorption quantity being TQ 〉 TP 〉 XB 〉 MY based on the calculation results. What is more, the fitting of intraparticle diffu- sion model proves that the adsorption process of Cr3 + by XB and MY had been going on in 2 steps (fast and slow adsorption phases) in 20 ℃
出处 《安全与环境学报》 CAS CSCD 北大核心 2015年第2期178-183,共6页 Journal of Safety and Environment
关键词 环境科学技术基础学科 固定化 等温吸附模型 动力学 热力学 basic disciplines of environmental science and technolo-gy immobilization isothermal adsorption model kinet-ics thermodynamics
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参考文献16

  • 1汤克勇.铬的污染源及其危害[J].皮革科学与工程,1997,7(1):33-37. 被引量:44
  • 2MURPHY V, HUGHES H, MCLOUGHLIN P. Enhancement strategies for Cu(11), Cr(III) and Cr(VI) remediation by a variety of seaweed species[J]. Journal of Hazardous Materials, 2009, 166(1): 318-326. 被引量:1
  • 3BATISTAA A P S, ROM O L P C, ARGUELHO M L P M, et al. Biosorption of Cr(III) using in natura and chemically treated tropical peats[J]. Journal of Hazardous Materials, 2009, 163(2/3): 517-523. 被引量:1
  • 4严平,谢翼飞.重金属Cu^(2+)抗性菌的筛选与吸附性能研究[J].安全与环境学报,2012,12(3):39-41. 被引量:4
  • 5ZHAO Yan(赵妍), ZHANG Xiaoxia(张晓霞), XIE Xianxian(谢贤仙), et al. Studies on the effect of additives on the structures and properties of PVDF hollow fiber ultrafiltration membrane[J]. 水处理技术, 2011, 37(11): 105-109. 被引量:1
  • 6GEOFFREY M G. Bioremedial potential of microbial mechanisms of metal mobilization and immobilization[J]. Current Opinion in Biotechnology, 2000, 11(3): 38-42. 被引量:1
  • 7康春莉,高红杰,郭平,叶春翔,万婷婷.吸附铅、镉固定化细菌胞壁多糖小球包埋条件的优化选择[J].生态环境,2007,16(3):825-829. 被引量:7
  • 8SAFA A, ZER G, ADNAN . Adsorption of lead(11) ions onto 8-hydroxy quinoline-immobilized bentonite[J]. Journal of Hazardous Materials, 2009, 161(1): 499-509. 被引量:1
  • 9ATES S, MEHMETOGLU U. A new method for immobilization of β-galactosidase and its utilization in a plug flow reactor[J]. Process Biochemistry, 1997, 32(5): 433-436. 被引量:1
  • 10FIOL N, ESCUDERO C, VILLAESCUSA I. Chromium sorption and Cr(VI) reduction to Cr(III) by grape stalks and yohimbe bark[J]. Bioresource Technology, 2008, 99(11): 5030-5036. 被引量:1

二级参考文献25

  • 1朱雪强,韩宝平.重金属生物吸附研究进展[J].中国环保产业,2004(5):19-21. 被引量:18
  • 2王雅静,戴惠新.生物吸附法分离废水中重金属离子的研究进展[J].冶金分析,2006,26(1):40-45. 被引量:20
  • 3周东琴,魏德洲.沟戈登氏菌对重金属的生物吸附-浮选和解吸性能[J].环境科学,2006,27(5):960-964. 被引量:24
  • 4PRASHANTH S J,MULIMANI V H.Soymilk oligosaccharide hydrolysis by Aspergillus oryzae α-galactosidase immobilized in calcium alginate[J].Process Biochemistry,2005,40:1199-1205. 被引量:1
  • 5ATES S,MEHMETOGLU U.A new method for immobilization of β-galactosidase and its utilization in a plug flow reactor[J].Process Biochem,1997,32(5):433-436. 被引量:1
  • 6TEWARI N,VASUDEVAN P,GUHA B K.Study on biosorption of Cr(VI) by Mucor hiemalis[J].Biochemical Engineering Journal,2005,23:185-192. 被引量:1
  • 7KARTAL S N,IMAMURA Y.Removal of copper,chromium,and arsenic from CCA-treatedwood onto chitin and chitosan[J].Bioresource Technology,2005,96:389-392. 被引量:1
  • 8GUIBAUD G,COMTE S,BORDAS F,et al.Metal removal from single and multimetallic equimolar systems by extracellular polymers extracted from activated sludges as evaluated by SMDE polarography[J].Process Biochemistry,2005,40:661-668. 被引量:1
  • 9OZER A,OZER D.Comparative study of the biosorption of Pb(Ⅱ),Ni(Ⅱ) and Cr(VI) ions onto S.cerevisiae:determination of biosorption heats[J].Journal of Hazardous Materials B,2003,100:219-229. 被引量:1
  • 10Fumihisa Kobayashi,Rumiko Kofuji,Yuya Yamashita, etal.A novel treatment system of wastewater contaminated with copper by a moss[].Biomedical Engineering.2006 被引量:1

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