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苯乙烯系双腈胺螯合树脂对水相中As(Ⅴ)的吸附性能研究 被引量:1

Adsorption of As(Ⅴ) from aqueous solution onto a novel chelating resin containing cyanoguanidine moiety based on polystyrene
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摘要 将PS-DCDA树脂用于水相中As(Ⅴ)的吸附净化处理,探讨了溶液的pH值、初始As(Ⅴ)质量浓度、接触时间、温度、NaCl、竞争性阴离子等因素对吸附性能的影响,并研究了其对As(Ⅴ)的吸附等温线、动力学和热力学。结果表明,NaCl和竞争性阴离子(Cl-、SO24-、CO23-、NO3-、HPO24-等)明显地抑制了PS-DCDA树脂对As(Ⅴ)的吸附。PS-DCDA树脂对As(Ⅴ)的吸附符合Langmuir等温式,准二级吸附动力学方程能够很好地描述As(Ⅴ)在树脂上的吸附动力学行为。粒子内扩散方程表明,表面吸附和内部扩散参与到As(Ⅴ)的吸附过程当中。PS-DCDA树脂对As(Ⅴ)的热力学参数表明,PS-DCDA树脂对As(Ⅴ)的吸附是自发的、吸热的过程。已吸附As(Ⅴ)的PS-DCDA树脂可以用0.1 mol/L NaOH有效解吸,解吸后的树脂对As(Ⅴ)仍具有较高的吸附量。 The paper is to introduce its research on the adsorption of As(Ⅴ) from aqueous solution onto a novel chelating resin containing cyanoguanidine moiety based on polystyrene a novel chelating resin(PS-DCDA) containing cyanoguanidine moiety.For this purpose,first of all,it has prepared As(Ⅴ) from the aqueous solutions.And then we have investigated and analyzed various factors affecting the adsorption behavior,such as solution pH,initial As(Ⅴ) concentration,contact time,solution temperature,the NaCl and competitive anions.Through our experiments,we have found the adsorption of As(Ⅴ) was highly dependent on the solution pH while the maximum As(Ⅴ) adsorption rate could reach around pH=3.0.At the same time,the equilibrium data of As(Ⅴ) were analyzed by using Langmuir and Freundlich isotherm models.Through experiments,it has been found that the adsorption data of As(Ⅴ) can best be described by the Langmuir isotherm model with the maximum monolayer adsorption capacities of 42.01 mg/g,45.06 mg/g and 52.17 mg/g at 20 ℃,30 ℃ and 40 ℃,respectively.We have also found that the thermodynamic parameters such as enthalpy(ΔH),Gibbs free energy(ΔG) and entropy (ΔS) changes were detected and the results of the experiment show that the adsorption of As(Ⅴ) onto PS-DCDA resin proves to be feasible and endothermic in nature.The kinetic data have also been evaluated based on the pseudo-second order and intraparticle diffusion models,indicating that the adsorption kinetics of As(Ⅴ) was found to follow the pseudo-second order kinetic model.At the same time,the intraparticle diffusion model reveals that the adsorption of As(Ⅴ) on PS-DCDA resin is mainly governed by the surface adsorption and particle diffusion. Moreover,the increase of the concentration(0.01-1.0 mol/L) of NaCl in As(Ⅴ) solution can significantly reduce As(Ⅴ) adsorption on PS-DCDA resins.The competitive adsorption studies also confirm that the presence of Cl-,SO2-4,CO2-3,NO-3,HPO2-4 tends to highly inhibit the adsorption of As(Ⅴ) due to the competitive effect.And,finally,the As(Ⅴ) adsorbed in the experimental process could be efficiently desorbed with 0.1 mol/L NaOH solution.After five cycles of adsorption-desorption operations,it would be possible to increase the re-adsorption capacities to be as high as 75.69% of initial adsorption value.All the above results indicate that PS-DCDA resin was an eco-friendly,efficient and reusable adsorbent for removing As(Ⅴ) from the aqueous solution due to its simple preparation,high adsorption,quick and high adsorption rate,besides the effective regeneration and perfect reusability.
出处 《安全与环境学报》 CAS CSCD 北大核心 2012年第1期61-66,共6页 Journal of Safety and Environment
基金 国家水体污染控制与治理科技重大专项(2009ZX07212-001-04)
关键词 环境工程学 As(Ⅴ) PS-DCDA树脂 吸附 解吸 environmental engineering As(Ⅴ) PS-DCDA resin adsorption desorption
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  • 1XIA Y, LIU J. An overview on chronic arsenism via drinking water in PR China[J]. Toxicology, 2004, 198(1/2/3): 25-29.
  • 2SMITH A H, HOPENHAYN-RICH C, BATES M N, et al. Cancer risks from arsenic in drinking water[J]. Environmental Health Perspectives, 1992, 97(7): 259-267.
  • 3ZHENG Y M, ZOU S W, NADEESHANI N K G, et al. Adsorptive removal of arsenic from aqueous solution by a PVDF/zirconia blend flat sheet membrone[J]. Journal of Membrance Science, 2011, 374(1/2): 1-11.
  • 4WANG J W, BEJAN D, BUNCE N J. Removal of arsenic from synthetic acid mine drainage by electrochemical pH adjustment and coprecipitation with iron hydroxide[J]. Environmental Science Technology, 2003, 37(19): 4500-4506.
  • 5NGUYEN C M, BANG S, CHO J, et al. Performance and mechanism of arsenic removal from water by a nanofiltration membrane[J]. Desalination, 2009, 245(1/2/3): 82-94.
  • 6KIM J, BENJAMIN M M. Modeling a novel ion exchange process for arsenic and nitrate removal[J]. Water Research, 2004, 38(8): 2053-2062.
  • 7JANG M, CHEN W, CANNON F S. Preloading hydrous ferric oxide into granular activated carbon for arsenic removal[J]. Environmental Science Technology, 2008, 42(9): 3369-3374.
  • 8RAMESH A, HASEGAWA H, MAKI T, et al. Adsorption of inorganic and organic arsenic from aqueous solutions by polymeric Al/Fe modified montmorillonite[J]. Separation and Purification Technology, 2007, 56(1): 90-100.
  • 9DONG L, ZININ P V, COWEN J P, et al. Iron coated pottery granules for arsenic removal from drinking water[J]. Journal of Hazardous Materials, 2009, 168(2/3): 626-632.
  • 10ZHU H, JIA Y, WU X, et al. Removal of arsenic from water by supported nano zero-valent iron on activated carbon[J]. Journal of Hazardous Materials, 2009, 172(2/3): 1591-1596.

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共引文献34

同被引文献26

  • 1梁慧锋,马子川,张杰,胡章记.新生态二氧化锰对水中三价砷去除作用的研究[J].环境污染与防治,2005,27(3):168-171. 被引量:31
  • 2吴丰昌,万国江,蔡玉蓉.沉积物-水界面的生物地球化学作用[J].地球科学进展,1996,11(2):191-197. 被引量:96
  • 3孙红福,赵峰华,李文生,李荣杰,葛祥坤.煤矿酸性矿井水及其沉积物的地球化学性质[J].中国矿业大学学报,2007,36(2):221-226. 被引量:13
  • 4WANG Jincui(王金翠), SUN Jichao(孙继朝), JING Jihong(荆继红), et al. Relationship of arsenic contamination and ecological environment. 中国人口资源与环境, 2011, 21(3): 540-542.
  • 5CHUTIA P, KATO S, KOJIMA T, et al. Arsenic adsorption from aqueous solution on synthetic zeolites[J]. Journal of Hazardous Materials, 2009, 162(1): 440-447.
  • 6FERRECCIIO C, GONZALEZ C, MILOSAVJLEVIC V, et al. Lung cancer and arsenic concentrations in drinking water in Chile[J]. Epidemiology, 2000, 11(6): 673-679.
  • 7NG J, GOMEZ-CAMINERO A, HOWE P, et al. Arsenic and arsenic compounds[M]. Geneva: World Health Organization, 2001.
  • 8CONCA J L,WRIGHT J. An apatite II permeable reactive barrier to remediate groundwater containing Zn, Pb and Cd[J]. Applied Geochemistry, 2006, 21(12): 2188-2200.
  • 9PULS R W, BLOWES D W,GILLHAM R W. Long-term performance monitoring for a permeable reactive barrier at the U.S. Coast Guard Support Center, Elizabeth City, North Carolina[J]. Journal of Hazardous Materials, 1999, 68(1/2): 109-124.
  • 10KAMOLPORWIJIT W, LIANG L, WEST O R, et al. Preferential flow path development and its influence on long-term PRB performance: column study[J]. Journal of Contaminant Hydrology, 2003, 66(3/4): 161-178.

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