磷酸改性生物炭-LDHs(Mg-Al-NO3)复合材料对双酚A的吸附

叶益辰, 孙雨晴, 萨仁格日乐, 施乐乐, 张珍, 王涛, 刘永红. 磷酸改性生物炭-LDHs(Mg-Al-NO3)复合材料对双酚A的吸附[J]. 环境化学, 2020, (1): 61-70. doi: 10.7524/j.issn.0254-6108.2019020206
引用本文: 叶益辰, 孙雨晴, 萨仁格日乐, 施乐乐, 张珍, 王涛, 刘永红. 磷酸改性生物炭-LDHs(Mg-Al-NO3)复合材料对双酚A的吸附[J]. 环境化学, 2020, (1): 61-70. doi: 10.7524/j.issn.0254-6108.2019020206
YE Yichen, SUN Yuqing, SAREN Gerile, SHI Lele, ZHANG Zhen, WANG Tao, LIU Yonghong. Adsorption of bisphenol a by phosphoric acid modified biochar-LDHs(Mg-Al-NO3) composite[J]. Environmental Chemistry, 2020, (1): 61-70. doi: 10.7524/j.issn.0254-6108.2019020206
Citation: YE Yichen, SUN Yuqing, SAREN Gerile, SHI Lele, ZHANG Zhen, WANG Tao, LIU Yonghong. Adsorption of bisphenol a by phosphoric acid modified biochar-LDHs(Mg-Al-NO3) composite[J]. Environmental Chemistry, 2020, (1): 61-70. doi: 10.7524/j.issn.0254-6108.2019020206

磷酸改性生物炭-LDHs(Mg-Al-NO3)复合材料对双酚A的吸附

    通讯作者: 刘永红, E-mail: liuyh913@mail.hzau.edu.cn
  • 基金项目:

    中央高校基本科研业务费专项资金(2662017JC023)和国家重点研发计划(2016YFD0800800)资助.

Adsorption of bisphenol a by phosphoric acid modified biochar-LDHs(Mg-Al-NO3) composite

    Corresponding author: LIU Yonghong, liuyh913@mail.hzau.edu.cn
  • Fund Project: Supported by the Fundamental Research Funds for the Central Universities(2662017JC023) and the National Key R&D Program of China(2016YFD0800800).
  • 摘要: 本研究选取油菜秸秆为原料,在600℃下热解得到生物炭和磷酸改性生物炭,并用共沉淀法制备3种改性生物炭-LDHs (Mg-Al-NO3)复合材料.采用批量吸附法研究不同pH、吸附时间和不同生物炭/LDHs配比条件下复合材料对双酚A的吸附特性,借助XRD、FTIR和BET等测试手段探究了复合材料吸附双酚A的机制.结果表明,改性生物炭-LDHs (Mg-Al-NO3)复合材料吸附双酚A的吸附平衡时间为4 h,符合准二级动力学方程(R2>0.99);复合材料对双酚A的吸附效果稍逊于改性生物炭,改性生物炭在复合材料中所占比重越大,吸附效果越好.当pH值在5.0—9.0范围内变化时,改性生物炭-LDHs (Mg-Al-NO3)复合材料对双酚A的吸附量呈下降趋势,且在pH=9.0时达到最小值.等温吸附模型数据表明,复合材料用Freundlich等温吸附模型效果更好.通过XRD、BET、FTIR测试研究发现,由于LDHs占据了生物炭表面的活性位点,致使生物炭与双酚A之间的相互作用减弱,降低了复合物的吸附能力.本研究结果初步阐释了改性生物炭-LDHs (Mg-Al-NO3)复合材料吸附双酚A的机理,为生物炭-LDHs复合材料处理水体中有机污染物的应用提供了借鉴和参考.
  • 加载中
  • [1] FITZGERALD R E, WILKS M.F. Bisphenol A-Why an adverse outcome pathway framework needs to be applied[J]. Toxicology Letters, 2014, 230(2):368-374.
    [2] 郭丽敏. 关于双酚A奶瓶欧盟遭禁的探讨[J]. 塑料制剂, 2011(2):7-9. GUO L M. Discussion on the ban on bisphenol A milk bottles[J]. Plastic preparation, 2011

    (2):7-9(in Chinese).

    [3] KUCH H M, BALLSCHMITER K. Determination of endocrine disrupting phenolic compounds and estrogens in surface and drinking water by HRGC-(NCI)-MS in the pictogram per liter range[J]. Environmental Science and Technology, 2001, 35(15):3201-3206.
    [4] WARDLE D A, NILSSON M C, ZACKRISSON O. Fire-derived charcoal causes loss of forest Humus[J]. Science, 2008, 320(5876):629-629.
    [5] NGUYEN B T, LEHMANN J, HOCKADAY W C, et al. Temperature sensitivity of black carbon decomposition and oxidation[J]. Environmental Science and Technology, 2010, 44:3324-3331.
    [6] HALE S E, HANLEY K, LEHMANN J, et al. Effects of chemical, biological, and physical aging as well as soil addition on the sorption of pyrene to activated carbon and biochar[J]. Environmental Science and Technology, 2011, 45:10445-10453.
    [7] BRUUN S, JENSEN E S, JENSEN L S. Microbial mineralization and assimilation of black carbon, dependency on degree of thermal alteration[J]. Organic Geochemistry, 2008, 39:839-845.
    [8] 郎印海, 刘伟, 王慧. 生物炭对水中五氯酚的吸附性能研究[J]. 中国环境科学, 2014,34(8):2017-2023.

    LANG Y H, LIU W, WANG H. Adsorption efficiencies of pentachlorophenol from aqueous solution onto biochars[J]. China Environmental Science, 2014,34(8):2017-2023(in Chinese).

    [9] 王林, 徐应明, 梁学峰,等. 生物炭和鸡粪对镉低积累油菜吸收镉的影响[J]. 中国环境科学, 2014,34(11):2851-2858.

    WANG L, XU Y M, LIANG X F, et al. Effects of biochar and chicken manure on cadmium uptake in pakchoi cultivars with low cadmium accumulation[J]. China Environmental Science, 2014,34(11):2851-2858(in Chinese).

    [10] 李广坡, 林伟鑫, 杨美玉,等. 生物炭对水溶液中肉桂酸的吸附机制研究[J]. 环境化学,2018,37(6):1245-1252.

    LI G P, LIN W X, YANG M Y, et al. Sorption mechanism of cinnamic acid to biochar in aqueous solution[J]. Environmental Chemistry, 2018, 37(6):1245-1252(in Chinese).

    [11] MUNHERJEE A, ZIMMERMAN A.R, HARRIS W. Surface chemistry variations among a series of laboratory-produced biochars[J]. Geoderma, 2011, 163(3):247-255.
    [12] 吴文卫, 周丹丹. 生物炭老化及其对重金属吸附的影响机制[J]. 农业环境科学学报, 2019, 38(1):7-13.

    WU W W, ZHOU D D. Influence of biochar aging on its physicochemical properties and adsorption of heavymetals[J]. Journal of Agro-Environment Science, 2019, 38(1):7-13(in Chinese).

    [13] ZHOU N, CHEN H, XI J. Biochars with excellent Pb(Ⅱ) adsorption property produced from fresh and dehydrated banana peels via hydrothermal carbonization.[J]. Bioresource Technology, 2017, 232:204-210.
    [14] PENG H B, GAO P. CHU G, et al. Enhanced adsorption of Cu(Ⅱ) and Cd(Ⅱ) by phosphoric acid-modified biochars[J]. Environmental Pollution, 2017, 229:846-853.
    [15] LI H B, DONG X L, EVANDRO B, et al. Mechanisms of metal sorption by biochars:Biochar characteristics and modifications.[J]. Chemosphere, 2017, 178:466-478.
    [16] CONSTANTION V R L, PINNAVAIA T J. Basic properties of Mg2+1-x Al3+x layered double hydroxides intercalated by carbonate, hydroxide, chloride, and sulfate anions[J]. Inorganic Chemistry, 1995, 34:883-892.
    [17] TAN X F, LIU S B, LIU Y G. One-pot synthesis of carbon supported calcined-Mg/Al layered double hydroxides for antibiotic removal by slow pyrolysis of biomass waste[J]. Scientific Reports, 2016, doi:10.1038/srep39691
    [18] 王震宇, 刘国成, MONICA XING. 不同热解温度生物炭对Cd(Ⅱ)的吸附特性[J]. 环境科学, 2014, 35(12):4735-4744.

    WANG Z Y, LIU G C, MONICA X. Different pyrolysis temperatures biochar adsorption properties for Cd (Ⅱ)[J]. Environmental Science, 2014, 35(12):4735-4744(in Chinese).

    [19] 钟晓晓, 王涛, 原文丽,等. 生物炭的制备、改性及其环境效应研究进展[J].湖南师范大学自然科学学报, 2017, 40(5):44-50.

    ZHONG X X, WANG T, YUAN W L, et al. Progresses of preparation, modification and environmental behavior of biochar[J]. Journal of Natural Science of Hunan Normal University, 2017, 40(5):44-50(in Chinese).

    [20] 钟晓晓, 王涛, 王凯,等. 磷酸和热解温度对生物炭结构和性质的影响[J].湖南师范大学自然科学学报, 2018, 41(1):48-53.

    ZHONG X X, WANG T, WANG K, et al. Impacts of phosphorus acid concentration and pyrolysis temperature on structure and property of biochar[J]. Journal of Natural Science of Hunan Normal University, 2018, 41(1):48-53(in Chinese).

    [21] 张鑫慧, 张甘霖, 杨金玲. 典型热带土壤时间序列的电荷零点变化特征及其土壤发生意义[J].土壤, 2014, 46(2):347-354.

    ZHANG X H, ZHANG G L, YANG J L. The characteristics and significance of zero-point change of charge in typical tropical soil time series[J]. Soils, 2014, 46(2):347-354(in Chinese).

    [22] 王俊超, 郑凯琪, 俞筱妍,等. 垫料生物炭对Cd2+的吸附性能[J].环境工程学报, 2016, 10(11):6655-6661.

    WANG J C, ZHENG K Q, YU X Y, et al. Adsorption properties of Cd2+ by bedding materials derived-biochar[J]. Chinese Journal of Environmental Engineering, 2016, 10(11):6655-6661(in Chinese).

    [23] AMIT B, IOANNIS A, Adsorptive removal of bisphenol A (BPA) from aqueous solution:A review[J]. Chemosphere, 2017, 168:885-902.
    [24] 李健. 类水滑石(LDHs)结构的合成及吸附、光催化、腐蚀性能研究[D]. 青岛:山东科技大学,2017. LI J. Prepation and adsorption, photocatalysis and corrosion of LDHs materials structure[D]. Qingdao:Shandong University of Science and Technology, 2017(in Chinese).
    [25] 牛红梅, 徐莉. 镁铝水滑石及其插层组装化合物的合成与表征[J]. 西安科技大学学报, 2010, 30(6):731-733.

    NIU H M, XU L. Synthesis and characterization of magnesia-aluminum hydrotalcite and its intercalated assembly compounds[J]. Journal of XI'AN University of Science and Technology, 2010, 30(6):731-733(in Chinese).

    [26] 程春艳, 赵洪晨, 赵双双,等.Mg-Al层状双金属氢氧化物的合成及表征[J].科技视界,2018(19):70-71. CHENG C Y, ZHAO H C, ZHAO S S, et al. Synthesis and characterization of mg-al layered double hydroxides[J]. Science and Technology Vision, 2018

    (19):70-71(in Chinese).

    [27] 王璐, 赵保卫, 马锋锋,等. 马铃薯秸秆生物炭对黄土吸附Cd(Ⅱ)的影响[J]. 环境化学, 2016, 35(7):1422-1430.

    WANG L, ZHAO B W, MA F F, et al. Effects of biochar derived from potato straw on adsorption of Cd(Ⅱ) onto loess[J]. Environmental Chemistry, 2016, 35(7):1422-1430(in Chinese).

    [28] PETROVIC J T, STOJANVIC M D, MILOKOVIC J V, et al. Alkali modified hydrochar of grapepomace as a perspective adsorbent of Pb2+ from aqueous solution[J]. Journal of Environmental Management, 2016, 182:292-300.
    [29] 王彤彤, 马江波, 曲东,等. 两种木材生物炭对铜离子的吸附特性及其机制[J]. 环境科学, 2017, 38(5):2161-2171.

    WANG T T, MA J B, QU D, et al. Adsorption characteristics and mechanism of copper ions on two kinds of wood biochar[J]. Environmental Science,2017, 38(5):2161-2171(in Chinese).

    [30] 朱银涛, 李业东, 王明玉,等. 玉米秸秆碱化处理制备的生物炭吸附锌的特性研究[J]. 农业环境科学学报, 2018, 37(1):179-185.

    ZHU Y T, LI Y D, WANG M Y, et al. Adsorption characteristics of biochar prepared by corn stalk alkalization on zinc[J]. Journal of Agro-Environment Science, 2018, 37(1):179-185(in Chinese).

    [31] ZHAO Y F, ZHANG B, ZHANG X, et al. Preparation of highly orderedcubic NaA zeolite from halloysite mineral for adsorption of ammonium ions[J]. Journal of Hazardous Materials, 2010, 178(1-3):658-664.
    [32] SUN L, CHEN D, WAN S, et al. Performance, kinetics, and equilibrium of methylene blue adsorption on biochar derived from eucalyptus saw dust modified with citric, tartaric, and acetic acids[J]. Bioresource Technology, 2015, 198:300-308.
    [33] 徐楠楠, 林大松, 徐应明,等. 玉米秸秆生物炭对Cd2+的吸附特性及影响因素[J]. 农业环境科学学报. 2014, 33(5):958-964.

    XU N N, LIN D S, XU Y M, et al. Adsorption characteristics and influencing factors of Cd2+ on corn straw biochar[J]. Journal of Agro-Environment Science, 2014, 33(5):958-964(in Chinese).

    [34] 吴鸿伟, 陈萌, 黄贤金,等. 改性生物炭对水体中头孢噻肟的吸附机制[J]. 中国环境科学, 2018, 38(7):2527-2534.

    WU H W, CHEN M, HUANG X J, et al. Preparation of modified biochar for adsorption of cefotaxime in solution[J].China Environmental Science, 2018,38(7):2527-2534(in Chinese).

  • 加载中
计量
  • 文章访问数:  1574
  • HTML全文浏览数:  1574
  • PDF下载数:  74
  • 施引文献:  0
出版历程
  • 收稿日期:  2019-02-02
  • 刊出日期:  2020-01-01

磷酸改性生物炭-LDHs(Mg-Al-NO3)复合材料对双酚A的吸附

基金项目:

中央高校基本科研业务费专项资金(2662017JC023)和国家重点研发计划(2016YFD0800800)资助.

摘要: 本研究选取油菜秸秆为原料,在600℃下热解得到生物炭和磷酸改性生物炭,并用共沉淀法制备3种改性生物炭-LDHs (Mg-Al-NO3)复合材料.采用批量吸附法研究不同pH、吸附时间和不同生物炭/LDHs配比条件下复合材料对双酚A的吸附特性,借助XRD、FTIR和BET等测试手段探究了复合材料吸附双酚A的机制.结果表明,改性生物炭-LDHs (Mg-Al-NO3)复合材料吸附双酚A的吸附平衡时间为4 h,符合准二级动力学方程(R2>0.99);复合材料对双酚A的吸附效果稍逊于改性生物炭,改性生物炭在复合材料中所占比重越大,吸附效果越好.当pH值在5.0—9.0范围内变化时,改性生物炭-LDHs (Mg-Al-NO3)复合材料对双酚A的吸附量呈下降趋势,且在pH=9.0时达到最小值.等温吸附模型数据表明,复合材料用Freundlich等温吸附模型效果更好.通过XRD、BET、FTIR测试研究发现,由于LDHs占据了生物炭表面的活性位点,致使生物炭与双酚A之间的相互作用减弱,降低了复合物的吸附能力.本研究结果初步阐释了改性生物炭-LDHs (Mg-Al-NO3)复合材料吸附双酚A的机理,为生物炭-LDHs复合材料处理水体中有机污染物的应用提供了借鉴和参考.

English Abstract

参考文献 (34)

目录

/

返回文章
返回