牛粪源生物炭对水中甲基紫的吸附动力学和热力学

尹丽, 邹海燕, 费陶, 肖小雨, 张慧, 何仲视. 牛粪源生物炭对水中甲基紫的吸附动力学和热力学[J]. 环境化学, 2017, 36(12): 2650-2657. doi: 10.7524/j.issn.0254-6108.2017051704
引用本文: 尹丽, 邹海燕, 费陶, 肖小雨, 张慧, 何仲视. 牛粪源生物炭对水中甲基紫的吸附动力学和热力学[J]. 环境化学, 2017, 36(12): 2650-2657. doi: 10.7524/j.issn.0254-6108.2017051704
YIN Li, ZOU Haiyan, FEI Tao, XIAO Xiaoyu, ZHANG Hui, HE Zhongshi. Thermodynamics and kinetics of sorption of methyl violet on cow-manure-derived biochar in an aqueous solution[J]. Environmental Chemistry, 2017, 36(12): 2650-2657. doi: 10.7524/j.issn.0254-6108.2017051704
Citation: YIN Li, ZOU Haiyan, FEI Tao, XIAO Xiaoyu, ZHANG Hui, HE Zhongshi. Thermodynamics and kinetics of sorption of methyl violet on cow-manure-derived biochar in an aqueous solution[J]. Environmental Chemistry, 2017, 36(12): 2650-2657. doi: 10.7524/j.issn.0254-6108.2017051704

牛粪源生物炭对水中甲基紫的吸附动力学和热力学

  • 基金项目:

    国家自然科学基金(41661095),江西省自然科学基金(20151BAB214005,20171BAB203025),江西省教育厅科技项目(GJJ160751)和江西省教育厅落地计划(KJLD14065)资助.

Thermodynamics and kinetics of sorption of methyl violet on cow-manure-derived biochar in an aqueous solution

  • Fund Project: Supported by the National Natural Science Foundation of China (41661095), Project of Natural Science Foundation of Jiangxi Province (20151BAB214005, 20171BAB203025), the Educational Commission of Jiangxi Province(GJJ160751) and the Landing Project of the Jiangxi Education Department (KJLD14065).
  • 摘要: 600 ℃缺氧热解制得牛粪源生物炭(CBC),采用SEM、FTIR和XRD等分析手段对生物炭理化性质进行表征,并通过静态平衡吸附法研究了CBC对甲基紫的吸附动力学及热力学过程.结果表明,甲基紫的吸附量随着其初始浓度的增加而增大,初始浓度由10 mg·L-1增加到40 mg·L-1,平衡吸附量由5 mg·g-1提高到30 mg·g-1,吸附过程先快后慢,60 min后吸附达到平衡;甲基紫的吸附量还随溶液pH的增加而增大,随温度的升高而增大;用准一级动力学方程、准二级动力学方程、Langmuir 吸附等温方程、Freundlich吸附等温方程对试验数据进行拟合,结果表明,准二级动力学模型更准确地反映其吸附动力学过程,Freundlich等温方程与实验数据拟合度更好,即甲基紫在CBC上的吸附以化学吸附为主;吸附热力学参数ΔG°S°>0、ΔH°>0,表明甲基紫在CBC上的吸附是自发进行的吸热过程.
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  • [1] LIU R, ZHANG B, MEI D, et al. Adsorption of methyl violet from aqueous solution by halloysite nanotubes[J]. Desalination, 2011, 268(1/3):111-116.
    [2] ADEYEMO A A, ADEOYE I O, BELLO O S. Adsorption of dyes using different types of clay:A review[J]. Applied Water Science, 2017, 7(2):1-26.
    [3] HU L X, XU D D, ZOU L P, et al. Heterogeneous fenton oxidation of refractory dye rhodamine B in aqueous solution with mesoporous Fe/SBA-15[J]. Acta Physico-Chimica Sinica, 2015, 31(4):771-782.
    [4] 阳海, 魏宏庆, 胡乐天, 等. 单偶氮染料AY17的光催化降解动力学及机制[J]. 环境科学, 2016, 37(8):3086-3093.

    YANG H, WEI H Q, HU L T, et al. Photocatalytic degradation kinetics and mechanism of monoazo dye acid yellow 17 by UV/TiO2 in aqueous solution[J]. Environmental Science, 2016, 37(8):3086-3093(in Chinese).

    [5] XU R K, XIAO S C, YUAN J H, et al. Adsorption of methyl violet from aqueous solutions by the biochars derived from crop residues[J]. Bioresource Technology, 2011, 102(22):10293-10298.
    [6] AZIZIAN S, HAERIFAR M, BASHIRI H. Adsorption of methyl violet onto granular activated carbon:Equilibrium, kinetics and modeling[J]. Chemical Engineering Journal, 2008, 146(1):36-41.
    [7] KEYHANIAN F, SHARIATI S, FARAJI M, et al. Magnetite nanoparticles with surface modification for removal of methyl violet from aqueous solutions[J]. Arabian Journal of Chemistry, 2016, 9:S348-S354.
    [8] SEWU D D, BOAKYE P, WOO S H. Highly efficient adsorption of cationic dye by biochar produced with korean cabbage waste[J]. Bioresource Technology, 2017, 224:206-213.
    [9] QIU Y, XIAO X, CHENG H, et al. Influence of environmental factors on pesticide adsorption by black carbon:pH and model dissolved organic matter[J]. Environmental Science & Technology, 2009, 43(13):4973-4978.
    [10] KUSMIERZ M, OLESZCZUK P, KRASKA P, et al. Persistence of polycyclic aromatic hydrocarbons (PAHs) in biochar-amended soil[J]. Chemosphere, 2016, 146:272-279.
    [11] ZHENG H, WANG Z, ZHAO J, et al. Sorption of antibiotic sulfamethoxazole varies with biochars produced at different temperatures[J]. Environmental Pollution, 2013, 181:60-67.
    [12] JIA M, WANG F, BIAN Y, et al. Effects of pH and metal ions on oxytetracycline sorption to maize-straw-derived biochar[J]. Bioresource Technology, 2013, 136(3):87-93.
    [13] QIU Y, ZHENG Z, ZHOU Z, et al. Effectiveness and mechanisms of dye adsorption on a straw-based biochar[J]. Bioresource Technology, 2009, 100(21):5348-5351.
    [14] CHUN Y, SHENG G, CHIOU C T, et al. Compositions and sorptive properties of crop residue-derived chars[J]. Environmental Science & Technology, 2004, 38(17):4649-4655.
    [15] XIAO X, SHENG GD, QIU Y. Improved understanding of tributyltin sorption on natural and biochar-amended sediments[J]. Environmental Toxicology & Chemistry, 2011, 30(12):2682-2687.
    [16] 季雪琴, 吕黎, 陈芬, 等. 秸秆生物炭对有机染料的吸附作用及机制[J]. 环境科学学报, 2016, 36(5):1648-1654.

    JI X Q, LU L, CHEN F, et al. Sorption properties and mechanisms of organic dyes by straw biochar[J]. Acta Scientiae Circumstantiae, 2016, 36(5):1648-1654(in Chinese).

    [17] KIM Y, BAE J, PARK H, et al. Adsorption dynamics of methyl violet onto granulated mesoporous carbon:Facile synthesis and adsorption kinetics[J]. Water Research, 2016, 101:187-194.
    [18] MORADI S, AZIZIAN S. Preparation of nanostructured carbon covered sand for removal of methyl violet from water[J]. Journal of Molecular Liquids, 2016, 219:909-913.
    [19] HAMEED B H, DAUD F B M. Adsorption studies of basic dye on activated carbon derived from agricultural waste:Hevea brasiliensis seed coat[J]. Chemical Engineering Journal, 2008, 139(1):48-55.
    [20] 施超, 冯景伟, 彭书传,等. 活性炭纤维对水中罗丹明B的吸附性能[J]. 环境化学, 2013,32(3):394-401.

    SHI C, FENG J W, PENG S C, et al. Adsorption propreties of Rhodamine B by activater carbon fiber in aqueous solutions[J]. Environmental Chemistry, 2013, 32(3):394-401(in Chinese).

    [21] ZHANG Z Y, XU X C.Wrapping carbon nanotubes with poly (sodium 4-styrenesulfonate) for enhanced adsorption of methylene blue and its mechanism[J]. Chemical Engineering Journal, 2014, 256(6):85-92.
    [22] AI L, ZHANG C, CHEN Z. Removal of methylene blue from aqueous solution by a solvothermal-synthesized graphene/magnetite composite[J]. Journal of Hazardous Materials, 2011, 192(3):1515-1524.
    [23] 李颖, 岳钦艳, 高宝玉, 等. 活性炭纤维对活性染料的吸附动力学研究[J]. 环境科学, 2007, 28(11):2637-2641.

    LI Y, YUE Q Y, GAO B Y, et al. Adsorption kinetics of reactive dyes on activated carbon fiber[J]. Environmental Science,,2007, 28(11):2637-2641(in Chinese).

    [24] MALL ID, SRIVASTAVA VC, AGARWAL N K. Removal of orange-g and methyl violet dyes by adsorption onto bagasse fly ash-kinetic study and equilibrium isotherm analyses[J]. Dyes & Pigments, 2006, 69(3):210-223.
    [25] PlLAZINSKI W, RUDZINSKI W, PLAZINSKA A. Theoretical models of sorption kinetics including a surface reaction mechanism:A review[J]. Advances in Colloid & Interface Science, 2009, 152(1-2):2-13.
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出版历程
  • 收稿日期:  2017-05-17
  • 刊出日期:  2017-12-15
尹丽, 邹海燕, 费陶, 肖小雨, 张慧, 何仲视. 牛粪源生物炭对水中甲基紫的吸附动力学和热力学[J]. 环境化学, 2017, 36(12): 2650-2657. doi: 10.7524/j.issn.0254-6108.2017051704
引用本文: 尹丽, 邹海燕, 费陶, 肖小雨, 张慧, 何仲视. 牛粪源生物炭对水中甲基紫的吸附动力学和热力学[J]. 环境化学, 2017, 36(12): 2650-2657. doi: 10.7524/j.issn.0254-6108.2017051704
YIN Li, ZOU Haiyan, FEI Tao, XIAO Xiaoyu, ZHANG Hui, HE Zhongshi. Thermodynamics and kinetics of sorption of methyl violet on cow-manure-derived biochar in an aqueous solution[J]. Environmental Chemistry, 2017, 36(12): 2650-2657. doi: 10.7524/j.issn.0254-6108.2017051704
Citation: YIN Li, ZOU Haiyan, FEI Tao, XIAO Xiaoyu, ZHANG Hui, HE Zhongshi. Thermodynamics and kinetics of sorption of methyl violet on cow-manure-derived biochar in an aqueous solution[J]. Environmental Chemistry, 2017, 36(12): 2650-2657. doi: 10.7524/j.issn.0254-6108.2017051704

牛粪源生物炭对水中甲基紫的吸附动力学和热力学

  • 1.  井冈山大学生命科学学院, 江西省生态环境与资源重点实验室, 吉安, 343009;
  • 2.  同济大学环境科学与工程学院, 污染控制与资源化研究国家重点实验室, 上海, 200092;
  • 3.  上海申丰地质新技术应用研究所有限公司, 上海, 201702;
  • 4.  广西威尔森环保科技开发有限公司, 南宁, 530022
基金项目:

国家自然科学基金(41661095),江西省自然科学基金(20151BAB214005,20171BAB203025),江西省教育厅科技项目(GJJ160751)和江西省教育厅落地计划(KJLD14065)资助.

摘要: 600 ℃缺氧热解制得牛粪源生物炭(CBC),采用SEM、FTIR和XRD等分析手段对生物炭理化性质进行表征,并通过静态平衡吸附法研究了CBC对甲基紫的吸附动力学及热力学过程.结果表明,甲基紫的吸附量随着其初始浓度的增加而增大,初始浓度由10 mg·L-1增加到40 mg·L-1,平衡吸附量由5 mg·g-1提高到30 mg·g-1,吸附过程先快后慢,60 min后吸附达到平衡;甲基紫的吸附量还随溶液pH的增加而增大,随温度的升高而增大;用准一级动力学方程、准二级动力学方程、Langmuir 吸附等温方程、Freundlich吸附等温方程对试验数据进行拟合,结果表明,准二级动力学模型更准确地反映其吸附动力学过程,Freundlich等温方程与实验数据拟合度更好,即甲基紫在CBC上的吸附以化学吸附为主;吸附热力学参数ΔG°S°>0、ΔH°>0,表明甲基紫在CBC上的吸附是自发进行的吸热过程.

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