BS-12改性不同磁性黏土矿物对苯酚的吸附
作者:
中图分类号:

X53

基金项目:

国家自然科学基金项目(41271244)资助


Adsorption of Phenol on BS-12-Modified Different Magnetic Clay Minerals
Author:
Fund Project:

The National Natural Science Foundation of China (General Program, Key Program, Major Research Plan)

  • 摘要
  • | |
  • 访问统计
  • |
  • 参考文献 [28]
  • |
  • 相似文献 [20]
  • | | |
  • 文章评论
    摘要:

    采用共沉淀法制备磁性海泡石(MST)、磁性沸石(MZT)和磁性凹凸棒石(MAT),并以两性表面活性剂十二烷基二甲基甜菜碱(BS-12)对其进行改性,以X射线衍射(XRD)对不同吸附剂材料进行表征分析,通过批处理法比较不同磁性黏土矿物经BS-12改性后对苯酚的吸附特征,同时考察温度、pH和离子强度对BS-12改性磁性黏土矿物吸附苯酚的影响。结果表明,三种黏土矿物原样和磁化样对苯酚的吸附能力分别呈NAT > NST > NZT、MAT > MST > MZT的大小顺序,磁化对凹凸棒石的苯酚吸附能力影响最大,这与Fe3O4在凹凸棒石上的覆盖度较高有关。经BS-12改性后,三种改性磁性黏土矿物对苯酚的吸附量均随改性比例的增大而增加,具有一致性;三种磁性黏土矿物中,BS-12改性对磁性海泡石的苯酚吸附能力提升最多,这与BS-12在磁性海泡石的改性率较高有关。温度和溶液初始pH的升高不利于BS-12改性磁化样对苯酚的吸附,但离子强度的增加对BS-12改性磁化样吸附苯酚具有促进作用。BS-12改性磁性黏土矿物对苯酚的吸附以疏水分配作用为主,吸附能力取决于有机碳含量。三种改性磁性黏土矿物中,BS-12改性磁性凹凸棒石上的有机碳含量最高,对苯酚的吸附能力最强,且吸附受温度、pH和离子强度的影响最小。

    Abstract:

    [Objective] Phenol is a common organic pollutant that comes along with wastewater discharged from chemical industries. Clay minerals are abundant in reserve and high in adsorptivity, and hence have good prospects in application as adsorbents. The technology of magnetization and amphoteric modification can keep clay minerals capable of adsorbing organic and heavy metal pollutants and separating solid from liquid as well, which is conducive to material recycling. However, so far little has been reported about researches on comparison between different types of magnetized and modified clay minerals in adsorption of phenols and its mechanism, which though has certain practical significance for the application of amphoteric modified magnetic clay minerals to treatment of organic wastewater pollution.[Method] Magnetic sepiolite (MST), magnetic zeolite (MZT) and magnetic attapulgite (MAT) were prepared using the co-precipitation method, and then modified separately with the amphoteric surfactant dodecyl dimethyl betaine (BS-12). X-ray diffraction (XRD) was performed to characterize these adsorption materials, and then batch method was adopted to compare the three BS-12 modified magnetic clay minerals in phenol adsorption characteristics, while effects of temperature, pH, ionic strength and modification degree on the clay minerals adsorbing phenol were also investigated.[Result] Results show that in terms of phenol adsorption capacity of the three natural clay minerals and the three magnetized clay minerals exhibited an order of NAT > NST > NZT, and MAT > MST > MZT, respectively, and magnetization had the highest effect on the phenol adsorption capacity of attapulgite, which is highly related to the high Fe3O4 coverage on attapulgite. Once modified with BS-12, the three modified magnetic clay minerals increased in phenol adsorption capacity with increasing modification degree, showing a consistent trend; Among the three magnetic clay minerals, magnetic sepiolite increased the most phenol adsorption capacity in response to the BS-12 modification, which is related to its higher BS-12 modification rate. The increase in temperature or pH was not conducive to phenol adsorption on the BS-12-modified magnetic clay minerals, but the increase in ionic strength did have some positive effect.[Conclusion] Phenol adsorption on BS-12-modified magnetic clay minerals is dominated by hydrophobic partitioning, and phenol adsorption capacity of the minerals depends on organic carbon content. Among the three BS-12 modified magnetic clay minerals, BS-12 modified magnetic attapulgite has the highest phenol adsorption capacity as it has the highest organic carbon content, and it capacity is rarely affected by temperature, pH and ionic strength.

    参考文献
    [1] Zhang Q R,Han Y,Wu L C. Influence of electrostatic field on the adsorption of phenol on single-walled carbon nanotubes:A study by molecular dynamics simulation[J]. Chemical Engineering Journal,2019,363:278-284.
    [2] Shao L S,Huang J H. Controllable synthesis of N-vinylimidazole-modified hyper-cross-linked resins and their efficient adsorption of p-nitrophenol and o-nitrophenol[J]. Journal of Colloid & Interface Science,2017,507:42-50.
    [3] El-Dib F I,Tawfik F M,Eshaq G,et al. Remediation of distilleries wastewater using chitosan immobilized Bentonite and Bentonite based organoclays[J]. International Journal of Biological Macromolecules,2016,86:750-755.
    [4] Liu Y S,Liu P,Su Z X,et al. Attapulgite-Fe3O4 magnetic nanoparticles via co-precipitation technique[J]. Applied Surface Science,2008,255(5):2020-2025.
    [5] Mesdaghinia A,Azari A,Nodehi R N,et al. Removal of phthalate esters(PAEs) by zeolite/Fe3O4:Investigation on the magnetic adsorption separation,catalytic degradation and toxicity bioassay[J]. Journal of Molecular Liquids,2017,233:378-390.
    [6] Yu T P,Dai Y Z,Wang W P,et al. Adsorption characteristic and mechanism of heavy metals onto magnetically modified sepiolite[J]. Environmental Chemistry,2013,32(8):1566-1570.[余铁萍,戴友芝,王未平,等. 磁性海泡石吸附水中重金属离子的特性及机理[J]. 环境化学,2013,32(8):1566-1570.]
    [7] Meng Z F,Zhang Y P,Wang G D. Sorption of heavy metal and organic pollutants on modified soils[J]. Pedosphere,2007,17(2):235-245.
    [8] Meng Z F,Zhang Y P,Zhang Z Q. Simultaneous adsorption of phenol and cadmium on amphoteric modified soil[J]. Journal of Hazardous Materials,2008,159(2/3):492-498.
    [9] Li T,Meng Z F,Zhang B. Adsorption of amphoteric modified bentonites to phenol and its thermodynamics[J]. Environmental Science,2012,33(5):1632-1638.[李婷,孟昭福,张斌. 两性修饰膨润土对苯酚的吸附及热力学特征[J]. 环境科学,2012,33(5):1632-1638.]
    [10] Bai J F,Meng Z F,Liu Y H,et al. Adsorption of phenol on amphoteric-cationic modified Lou soil[J]. China Environmental Science,2010,30(10):1389-1394.[白俊风,孟昭福,刘源辉,等. 两性-阳离子复配修饰塿土对苯酚的吸附[J]. 中国环境科学,2010,30(10):1389-1394.]
    [11] Ren S,Meng Z F,Liu W,et al. Characterization and adsorption performance of phenol on amphoteric modified magnetic bentonites[J]. Journal of Agro-Environment Science,2017,36(1):108-115.[任爽,孟昭福,刘伟,等. 两性修饰磁性膨润土的表征及其对苯酚的吸附[J]. 农业环境科学学报,2017,36(1):108-115.]
    [12] Wan D,Li W B,Wang G H,et al. Adsorption and heterogeneous degradation of rhodamine B on the surface of magnetic bentonite material[J]. Applied Surface Science,2015,349:988-996.
    [13] Liu C M,Wu P X,Zhu Y J,et al. Simultaneous adsorption of Cd2+ and BPA on amphoteric surfactant activated montmorillonite[J]. Chemosphere,2016,144:1026-1032.
    [14] Ren S,Meng Z F,Wang T,et al. Comparison of amphoteric-cationic and amphoteric-anionic modified magnetic bentonites:Characterization and sorption capacity of phenol[J]. Environmental Science,2018,39(1):187-194.[任爽,孟昭福,王腾,等. 阳(阴)离子复配修饰两性磁性膨润土的表面特征差异及对苯酚吸附的影响[J]. 环境科学,2018,39(1):187-194.]
    [15] Yu S M,Zhai L,Zhong S S,et al. Synthesis and structural characterization of magnetite/sepiolite composite and its sorptive properties for Co(Ⅱ) and Cd(Ⅱ)[J]. Journal of the Taiwan Institute of Chemical Engineers,2016,59:221-228.
    [16] Gaffer A,Al Kahlawy A A,Aman D. Magnetic zeolite-natural polymer composite for adsorption of chromium(VI)[J]. Egyptian Journal of Petroleum,2017,26(4):995-999.
    [17] Zou M F,Chen X Y,Lin X J,et al. Fabrication of magnetic carboxyl-functionalized attapulgite/calcium alginate beads for lead ion removal from aqueous solutions[J]. International Journal of Biological Macromolecules,2018,120:789-800.
    [18] Li W B,Meng Z F,Wu Q,et al. Modification mechanism of amphoteric modifier BS-12 on two different clays. Fresenius Environmental Bulletin,2016,25(10):3993-4003.
    [19] Meng Z F,Zhang Y P. Cd2+ adsorption of organic modified soils and its temperature effect[J]. Acta Pedologica Sinica,2005,42(2):238-246.[孟昭福,张一平. 有机修饰改性土对镉离子的吸附及温度效应[J]. 土壤学报,2005,42(2):238-246.]
    [20] Akyüz S,Akyüz T,Yakar A E. FT-IR spectroscopic investigation of adsorption of 3-aminopyridine on sepiolite and montmorillonite from Anatolia[J]. Journal of Molecular Structure,2001,565/566:487-491.
    [21] Yousef R I,El-Eswed B. The effect of pH on the adsorption of phenol and chlorophenols onto natural zeolite[J]. Colloids and Surfaces A:Physicochemical & Engineering Aspects,2009,334(1/2/3):92-99.
    [22] Huang J H,Wang X G,Jin Q Z,et al. Removal of phenol from aqueous solution by adsorption onto OTMAC-modified attapulgite[J]. Journal of Environmental Management,2007,84(2):229-236.
    [23] Wu P X. Clay mineral materials and environmental restoration[M]. Beijing:Chemical Industry Press,2004.[吴平霄. 黏土矿物材料与环境修复[M]. 北京:化学工业出版社,2004.]
    [24] Sawhney B L. Sorption of atrazine by Al- and Ca-saturated smectite[J]. Clays & Clay Minerals,1997,45(3):333-338.
    [25] Wu H H,Lin Y Y,Wu J Y,et al. Surface adsorption of iron oxide minerals for phenol and dissolved organic matter[J]. Earth Science Frontiers,2008,15(6):133-141.
    [26] Zhao Q,Burns S E. Molecular simulation of electro kinetics of montmorillonite surface coated with hexadecyltrimethylammonium cations[J]. Colloids and Surfaces A:Physicochemical and Engineering Aspects,2017,516:354-361.
    [27] Zhu L Z,Qi Q,Shen X Y,et al. Dynamic simulation of TEMIK residues and its movement in soil[J]. Environmental Pollution & Control,1994,(6):15-17.[朱利中,戚群,沈学优,等. 有机膨润土吸附苯胺的性能及其在水处理中的应用[J]. 环境污染与防治,1994,(6):15-17.]
    [28] Wei L,Zhu L,Qiu Y P. Effect of salting-out and ion-pairing on column transport of ionic liquids. Water Pollution and Treatment,2019,7(2):91-100.[魏丽,祝凌,邱宇平. 影响离子液体迁移的盐析和离子对效应. 水污染及处理,2019,7(2):91-100.]
    引证文献
    网友评论
    网友评论
    分享到微博
    发 布
引用本文

张梦飞,孟昭福,任爽,卜帅宾,王腾. BS-12改性不同磁性黏土矿物对苯酚的吸附[J].土壤学报,2021,58(3):712-721. DOI:10.11766/trxb201912220511 ZHANG Mengfei, MENG Zhaofu, REN Shuang, BU Shuaibin, WANG Teng. Adsorption of Phenol on BS-12-Modified Different Magnetic Clay Minerals[J]. Acta Pedologica Sinica,2021,58(3):712-721.

复制
分享
文章指标
  • 点击次数:792
  • 下载次数: 2370
  • HTML阅读次数: 1297
  • 引用次数: 0
历史
  • 收稿日期:2019-12-22
  • 最后修改日期:2020-03-08
  • 录用日期:2020-03-09
  • 在线发布日期: 2020-12-09
  • 出版日期: 2021-05-11
文章二维码