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双子型复配增强两性膨润土吸附Cr(VI)的效应
引用本文:胡啸龙,孟昭福,王新欣,刘欣,孙秀贤,任爽,王腾,张凌恺,卜帅宾,张梦飞.双子型复配增强两性膨润土吸附Cr(VI)的效应[J].中国环境科学,2020,40(5):2087-2094.
作者姓名:胡啸龙  孟昭福  王新欣  刘欣  孙秀贤  任爽  王腾  张凌恺  卜帅宾  张梦飞
作者单位:1. 西北农林科技大学资源环境学院, 陕西 杨凌 712100; 2. 农业部西北植物营养与农业环境重点实验室, 陕西 杨凌 712100
基金项目:国家自然科学基金资助项目(41271244);陕西省重点研发计划项目(2017SF-385)
摘    要:在两性修饰剂十二烷基二甲基甜菜碱(BS)修饰膨润土的基础上,采用双子型阳离子修饰剂乙撑基双十四烷基二甲基氯化铵(EB)对其进行复配修饰,以批处理法研究了不同修饰比例、温度、pH值和离子强度条件下,BS+EB复配修饰膨润土对Cr(VI)的吸附规律和热力学特征,并通过吸附Cr(VI)前后BS+EB复配修饰膨润土的红外光谱和表面电荷探讨了其吸附机制.结果表明,与BS两性修饰膨润土比较,EB复配修饰显著增强了其对Cr(VI)的吸附能力,吸附量增加了2.02~27.25倍,30℃时吸附量呈现BS+150EB(BS和150%比例的EB复配修饰膨润土) > BS+100EB > BS+50EB > BS+25EB > BS > CK(膨润土)的趋势,对Cr(VI)的吸附量随EB修饰比例增加而上升.CK、BS修饰膨润土对Cr(VI)呈现自发、熵增和焓增的特征,而BS+EB复配修饰膨润土对Cr(VI)吸附量随着温度的升高而降低,呈现出增温负效应.随着pH值的升高、离子强度增加,各供试土样对Cr(VI)的吸附量逐渐降低.红外光谱和土壤表面电荷结果证实电荷引力是BS+EB复配修饰土吸附Cr(VI)的主要机制.

关 键 词:双子型表面活性剂  膨润土  复配修饰  吸附  Cr(VI)  
收稿时间:2019-10-16

Enhancing effect of gemini surfactant complex modification on Cr(VI) adsorption by amphoteric bentonite
HU Xiao-long,MENG Zhao-fu,WANG Xin-xin,Liu Xin,SUN Xiu-xian,REN Shuang,WANG Teng,ZHANG Ling-kai,BU Shuai-bin,ZHANG Meng-fei.Enhancing effect of gemini surfactant complex modification on Cr(VI) adsorption by amphoteric bentonite[J].China Environmental Science,2020,40(5):2087-2094.
Authors:HU Xiao-long  MENG Zhao-fu  WANG Xin-xin  Liu Xin  SUN Xiu-xian  REN Shuang  WANG Teng  ZHANG Ling-kai  BU Shuai-bin  ZHANG Meng-fei
Institution:1. College of Natural Resources and Environment, Northwest A & F University, Yangling 712100, China; 2. Key Laboratory of Plant Nutrition and Agro-environment in Northwest China, Ministry of Agriculture, Yangling 712100, China
Abstract:A series of amphoteric-cationic complex modified bentonites were prepared with amphoteric modifier dodecyldimethyl betaine(BS) and gemini cationic surfactant ethylene ditetradecyl dimethyl ammonium chloride(EB), Cr(VI) adsorption on BS+EB complex modified bentonite under different modification ratio, temperature, pH and ionic strength and its thermodynamic characteristics were studied by batch method, its adsorption mechanism was discussed by comparing surface charge and infrared spectrum of BS+EB complex modified bentonite before and after Cr(VI) adsorption. The results showed that EB complex modification significantly enhanced its adsorption capacity for Cr(VI), which was 2.02~27.25 times higher than that on BS amphoteric modified bentonite. The Cr(VI) adsorption increased with an increase of EB modification ratio at 30℃ and was ordered by BS+150EB(BS and 150% EB complex modified bentonite) > BS+100EB > BS+50EB > BS+25EB > BS > CK(bentonite). The Cr(VI) adsorption on both CK and BS modified bentonite was a spontaneous process with a characteristics of both enthalpy-increase and entropy-increase, except it on BS+EB complex modified bentonite decreased with an increase of temperature, showing a characteristics of negative temperature effect. With an increase of pH and ionic strength, the adsorption of Cr(VI) on each sample decreased gradually. The results of infrared spectra and soil surface charge confirmed that charge attraction was the main mechanism for Cr(VI) adsorption on BS+EB complex modified bentonite.
Keywords:gemini cationicsurfactant  bentonite  complex modification  adsorption  Cr (VI)  
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