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虾壳粉对水溶液中阴、阳离子型染料的吸附

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吴琦, 戴凌青, 杨文叶, 葛柳钦, 夏枚生. 虾壳粉对水溶液中阴、阳离子型染料的吸附[J]. 环境工程学报, 2019, 13(3): 594-606. doi: 10.12030/j.cjee.201809141
引用本文: 吴琦, 戴凌青, 杨文叶, 葛柳钦, 夏枚生. 虾壳粉对水溶液中阴、阳离子型染料的吸附[J]. 环境工程学报, 2019, 13(3): 594-606. doi: 10.12030/j.cjee.201809141
shu
WU Qi, DAI Lingqing, YANG Wenye, GE Liuqin, XIA Meisheng. Adsorption of cationic and anionic dyes from aqueous solutions by shrimp shell powder[J]. Chinese Journal of Environmental Engineering, 2019, 13(3): 594-606. doi: 10.12030/j.cjee.201809141
Citation: WU Qi, DAI Lingqing, YANG Wenye, GE Liuqin, XIA Meisheng. Adsorption of cationic and anionic dyes from aqueous solutions by shrimp shell powder[J]. Chinese Journal of Environmental Engineering, 2019, 13(3): 594-606. doi: 10.12030/j.cjee.201809141
shu

虾壳粉对水溶液中阴、阳离子型染料的吸附

  • 1.

    浙江大学海洋学院，舟山 316021

  • 基金项目:

Adsorption of cationic and anionic dyes from aqueous solutions by shrimp shell powder

  • 1.

    Ocean College, Zhejiang University, Zhoushan 316021, China

  • Fund Project:

  • 摘要: 采用废弃虾壳制备吸附剂处理含刚果红或亚甲基蓝的溶液。考察了温度、吸附时间、初始浓度、吸附剂投加量和初始溶液pH对吸附效果的影响并构建了去除率预测模型，并对吸附等温线、吸附动力学和吸附热力学进行系统研究。结果表明：虾壳粉对刚果红和亚甲基蓝的吸附分别在24 h和4 h时达到平衡，平衡吸附量随吸附时间、初始浓度及吸附剂投加量的增加而增大；刚果红平衡吸附量随pH升高而增大，亚甲基蓝平衡吸附量几乎不随pH变化。在15 ℃下，吸附剂投加量为1 g·L-1，刚果红吸附的最优条件为接触时间24 h、pH=4，在该条件下，虾壳粉对刚果红的饱和吸附量为276.64 mg·g-1；亚甲基蓝吸附的最优条件为接触时间4 h、pH=12，在该条件下，虾壳粉对刚果红的饱和吸附量为1.44 mg·g-1；虾壳粉对2种染料的吸附过程以物理吸附为主，符合准二级动力学方程。虾壳粉对阴离子型染料的吸附效果较优，对阳离子型染料有一定吸附性能，是一种经济高效的染料废水吸附材料。
    Abstract: Shrimp shell-based bio-adsorbent was prepared and used to treat the simulated wastewater with congo red or methylene blue. The effects of temperature, adsorption time, initial dye concentration, adsorbent dosage and initial solution pH on adsorption efficiency were investigated, the prediction model for removal efficiency was subsequently built, and the adsorption isotherm, adsorption kinetics and adsorption thermodynamics were systematically studied. The results showed that the adsorption of congo red and methylene blue by shrimp shell powder reached equilibrium at 24 h and 4 h, respectively. The equilibrium adsorption capacity increased with increasing adsorption time, the initial dye concentration and adsorbent dosage. As pH increased, the equilibrium adsorption capacity of congo red increased, while the equilibrium adsorption capacity of methylene blue almost presented no change with pH. At 15 ℃, absorbent dose of 1 g·L-1, the optimum contact time of 24 h and pH=4, the saturated adsorption capacity of congo red by shrimp shell powder was 276.64 mg·g-1, while that of methylene blue was 1.44 mg·g-1 at pH=12. The adsorption of congo red and methylene blue onto shrimp shell was mainly considered as a physical adsorption process and could be described by a quasi-second-order model. Overall, shrimp shell-based bio-adsorbent exhibited an excellent removal efficiency for cation dye, while a slight removal one for anion dye. It is expected to be an economical and efficient material for wastewater treatment.
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  • [1] 林俊雄, 詹树林, 方明晖, 等. 三种吸附剂的改性与染料吸附特性比较研究[J]. 浙江大学学报(工学版), 2006, 40(12): 2031-2036.
    [2] 刘宝河, 孟冠华, 陶冬民, 等. 污泥吸附剂对3种染料吸附动力学的研究[J]. 环境工程学报, 2011, 5(1): 95-99.
    [3] 徐颖, 叶志隆, 叶欣, 等. 给水污泥对水中磷的吸附性能[J]. 环境工程学报, 2018, 12(3): 712-719.
    [4] 高国龙, 李登新, 孙利娜. 废布料活性炭吸附典型染料动力学研究[J]. 环境工程学报, 2011, 5(6): 1405-1408.
    [5] WANG S, BOYJOO Y, CHOUEIB A, et al. Removal of dyes from aqueous solution using fly ash and red mud[J]. Water Research, 2005, 39(1): 129-138.
    [6] BATZIAS F A, SIDIRAS D K. Dye adsorption by calcium chloride treated beech sawdust in batch and fixed-bed systems[J]. Journal of Hazardous Materials, 2004, 114(1/2/3): 167-174.
    [7] 王丰喜, 倪佩军, 刘张敏, 等. 硅质壳及硅藻土对亚甲基蓝吸附性能比较[J]. 环境工程学报, 2016, 10(4): 1693-1698.
    [8] AN H K, PARK B Y, KIM D S. Crab shell for the removal of heavy metals from aqueous solution[J]. Water Research, 2001, 35(15): 3551-3556.
    [9] VIJAYARAGHAVAN K, WINNIE H Y N, BALASUBRAMANIAN R. Biosorption characteristics of crab shell particles for the removal of manganese(II) and zinc(II) from aqueous solutions[J]. Desalination, 2011, 266(1): 195-200.
    [10] 魏燕芳, 邹哲凯. 废弃雪虾壳对染料的吸附行为[J]. 华侨大学学报(自然科学版), 2013, 34(5): 547-551.
    [11] GREGORIO C. Non-conventional low-cost adsorbents for dye removal: A review[J]. Bioresource Technology, 2006, 97(9): 1061-1085.
    [12] WU F C, TSENG R L, JUANG R S. Comparative adsorption of metal and dye on flake- and bead-types of chitosans prepared from fishery wastes[J]. Journal of Hazardous Materials, 2000, 73(1): 63-75.
    [13] KOUSHA M, TAVAKOLI S, DANESHVAR E, et al. Central composite design optimization of acid blue 25 dye biosorption using shrimp shell biomass[J]. Journal of Molecular Liquids, 2015, 207: 266-273.
    [14] DAI L, YAO Z, YANG W, et al. Crab shell: A potential high-efficiency and low-cost adsorbent for dye wastewater[J]. Fresenius Environmental Bulletin, 2017, 26(8): 4991-4998.
    [15] DOTTO G L, SANTOS J M, RODRIGUES I L, et al. Adsorption of methylene blue by ultrasonic surface modified chitin[J]. Journal of Colloid & Interface Science, 2015, 446(1): 133-140.
    [16] DOLTABADI M, ALIDADI H, DAVOUDI M. Comparative study of cationic and anionic dye removal from aqueous solutions using sawdust‐based adsorbent[J]. Environmental Progress & Sustainable Energy, 2016, 35(4): 1078-1090.
    [17] LANGMUIR I. The adsorption of gases on plane surfaces of glass, mica and platinum[J]. Journal of the American Chemical Society, 1918, 40(9): 1361-1403.
    [18] FREUNDLICH H. Ueber die adsorption in loesungen[J]. Zeitschrisft fur Physikalische Chemie, 1907, 57: 385-470.
    [19] REDLICH O, PETERSON D L. A useful adsorption isotherm[J]. Journal of Physical Chemistry, 1959, 63(6): 1024.
    [20] TOTH J. State equations of the solid gas interface layer[J]. Acta Chemica Academiae Hungaricae, 1971, 69: 311-317.
    [21] LAGERGREN S. About the theory of so-called adsorption of soluble substances[J]. Kungliga Svenska Vetenskapsakademiens Handlingar, 1898, 24(4): 1-39.
    [22] HO Y S, MCKAY G. Pseudo-second order model for sorption processes[J]. Process Biochemistry, 1999, 34(5): 451-465.
    [23] WEBER W J, MORRIS J C. Kinetics of adsorption on carbon from solution[J]. Asce Sanitary Engineering Division Journal, 1963, 89(1): 1-2.
    [24] 张跃冬. 半纤维素原料的预处理及酶解制备低聚木糖的研究[D]. 北京: 中国科学院大学, 2015.
    [25] 李婷. 配煤法制备柱状净水活性炭的研究[D]. 徐州: 中国矿业大学, 2015.
    [26] 姜鲁华, 杜芳林, 张瑞社, 等. 纳米碳酸钙制备过程中添加剂对产物的影响[J]. 青岛科技大学学报(自然科学版), 2002, 23(4): 17-19.
    [27] 蒋挺大. 甲壳素[M]. 北京: 化学工业出版社, 2003.
    [28] WANYONYI W C, ONYARI J M, SHIUNDU P M. Adsorption of congo red dye from aqueous solutions using roots of eichhornia crassipes: Kinetic and equilibrium studies[J]. Energy Procedia, 2014, 50: 862-869.
    [29] BEGUM H A, MONDAL A K, MUSLIM T. Adsorptiveremoval of reactive black 5 from aqueous solution using chitin prepared from shrimp shells[J]. Bangladesh Pharmaceutical Journal, 2012, 15(2): 145-152.
    [30] GUIBAL E, MILOT C, ROUSSY J. Influence of hydrolysis mechanisms on molybdate sorption isotherms using chitosan[J]. Separation Science & Technolog, 2007, 35(7): 1021-1038.
    [31] PRINCE J I C, SIVAKUMAR A, KAMIL M. Crab shell-treated custard apple shell for the removal of lead (II) and cadmium (II) from paint industry effluent: Kinetic. thermodynamics and equilibrium studies[J]. Research on Chemical Intermediates, 2015, 41(2): 609-622.
    [32] ZUNIGA-ZAMORA A, GARCIAMENCA J, CERVANTESGONZALEZ E. Removal of congo red from the aqueous phase by chitin and chitosan from waste shrimp[J]. Desalination & Water Treatment, 2015, 57(31): 1-12.
    [33] LIU M, XU J, CHENG B, et al. Synthesis and adsorption performance of Mg(OH)2 hexagonal nanosheet-graphene oxide composites[J]. Applied Surface Science, 2015, 332: 121-129.
    [34] RAVAL N P, SHAH P U, LADHA D G, et al. Comparative study of chitin and chitosan beads for the adsorption of hazardous anionic azo dye congo red from wastewater[J]. Desalination & Water Treatment, 2015, 57(20): 9247-9262.
    [35] FOROUGHI-DAHR M, ABOLGHASEMI H, ESMAIELI M, et al. Experimental study on the adsorptive behavior of congo red in cationic surfactant-modified tea waste[J]. Process Safety & Environmental Protection, 2015, 95: 226-236.
    [36] CHATTERJEE S, CHATTERJEE S, CHATTERJEE B P, et al. Adsorptive removal of congo red, a carcinogenic textile dye by chitosan hydrobeads: Binding mechanism, equilibrium and kinetics[J]. Colloids & Surfaces A: Physicochemical & Engineering Aspects, 2007, 299(1/2/3): 146-152.
    [37] NAMASIVAYAM C, MUNIASAMY N, GAYATRI K, et al. Removal of dyes from aqueous solutions by cellulosic waste orange peel[J]. Bioresource Technology, 1996, 57(1): 37-43.
    [38] VIMONSES V, LEI S M, BO J, et al. Adsorption of congo red by three Australian kaolins[J]. Applied Clay Science, 2009, 43(3): 465-472.
    [39] 王赛花, 牛红云, 蔡亚岐. 新型石墨烯磁性复合材料的制备及其对水中亚甲基蓝的吸附去除[J]. 分析测试学报, 2015, 34(2): 127-133.
    [40] DOTTO G L, SANTOS J M N, RODRIGUES I L, et al. Adsorption of methylene blue by ultrasonic surface modified chitin[J]. Journal of Colloid & Interface Science, 2015, 446: 133-140.
    [41] GHOSH D, BHATTACHARYYA K G. Adsorption of methylene blue on kaolinite[J]. Applied Clay Science, 2002, 20(6): 295-300.
    [42] RAO V V B, RAO S R M. Adsorption studies on treatment of textile dyeing industrial effluent by flyash[J]. Chemical Engineering Journal, 2006, 116(1): 77-84.
    [43] SUN S, WANG A. Adsorption kinetics of Cu(II) ions using N, O-carboxymethyl-chitosan[J]. Journal of Hazardous Materials, 2006, 131(1): 103-111.
    [44] PEREZ-MARIN A B, ZAPATA V M, ORTUNO J F, et al. Removal of cadmium from aqueous solutions by adsorption onto orange waste[J]. Journal of Hazardous Materials, 2007, 139(1): 122-131.
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  • 刊出日期:  2019-03-14
吴琦, 戴凌青, 杨文叶, 葛柳钦, 夏枚生. 虾壳粉对水溶液中阴、阳离子型染料的吸附[J]. 环境工程学报, 2019, 13(3): 594-606. doi: 10.12030/j.cjee.201809141
引用本文: 吴琦, 戴凌青, 杨文叶, 葛柳钦, 夏枚生. 虾壳粉对水溶液中阴、阳离子型染料的吸附[J]. 环境工程学报, 2019, 13(3): 594-606. doi: 10.12030/j.cjee.201809141
shu
WU Qi, DAI Lingqing, YANG Wenye, GE Liuqin, XIA Meisheng. Adsorption of cationic and anionic dyes from aqueous solutions by shrimp shell powder[J]. Chinese Journal of Environmental Engineering, 2019, 13(3): 594-606. doi: 10.12030/j.cjee.201809141
Citation: WU Qi, DAI Lingqing, YANG Wenye, GE Liuqin, XIA Meisheng. Adsorption of cationic and anionic dyes from aqueous solutions by shrimp shell powder[J]. Chinese Journal of Environmental Engineering, 2019, 13(3): 594-606. doi: 10.12030/j.cjee.201809141
shu

虾壳粉对水溶液中阴、阳离子型染料的吸附

  • 1. 浙江大学海洋学院，舟山 316021
基金项目:

摘要: 采用废弃虾壳制备吸附剂处理含刚果红或亚甲基蓝的溶液。考察了温度、吸附时间、初始浓度、吸附剂投加量和初始溶液pH对吸附效果的影响并构建了去除率预测模型，并对吸附等温线、吸附动力学和吸附热力学进行系统研究。结果表明：虾壳粉对刚果红和亚甲基蓝的吸附分别在24 h和4 h时达到平衡，平衡吸附量随吸附时间、初始浓度及吸附剂投加量的增加而增大；刚果红平衡吸附量随pH升高而增大，亚甲基蓝平衡吸附量几乎不随pH变化。在15 ℃下，吸附剂投加量为1 g·L-1，刚果红吸附的最优条件为接触时间24 h、pH=4，在该条件下，虾壳粉对刚果红的饱和吸附量为276.64 mg·g-1；亚甲基蓝吸附的最优条件为接触时间4 h、pH=12，在该条件下，虾壳粉对刚果红的饱和吸附量为1.44 mg·g-1；虾壳粉对2种染料的吸附过程以物理吸附为主，符合准二级动力学方程。虾壳粉对阴离子型染料的吸附效果较优，对阳离子型染料有一定吸附性能，是一种经济高效的染料废水吸附材料。

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