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有机改性蒙脱土对萘的吸附机制和影响因子
摘要点击 1383  全文点击 646  投稿时间:2020-03-26  修订日期:2020-05-05
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中文关键词  多环芳烃(PAHs)  耗散型石英晶体微天平(QCM-D)  吸附  有机改性蒙脱土  多环芳烃-重金属复合污染  
英文关键词  polycyclic aromatic hydrocarbons (PAHs)  dissipative quartz crystal microbalance (QCM-D)  adsorption  organo-clay particles  compound contamination of PAHs & heavy metals  naphthalene
作者单位E-mail
侯静雯 苏州科技大学环境科学与工程学院, 苏州 215009
中国科学院南京土壤研究所, 南京 210018 
kinow79524@163.com 
施维林 苏州科技大学环境科学与工程学院, 苏州 215009 weilin-shi@163.com 
高娟 中国科学院南京土壤研究所, 南京 210018 juangao@issas.ac.cn 
中文摘要
      我国场地土壤中多环芳烃(PAHs)污染或PAHs-重金属复合污染是常见的污染类型,对公众健康与环境构成巨大威胁.本研究利用耗散型石英晶体微天平(QCM-D)技术和批量吸附实验,探究实验室制备的2种有机改性黏土对萘的吸附机制,以及萘与Cu2+共存时黏土颗粒吸附情况.结果表明,25℃时,十六烷基三甲基溴化铵改性蒙脱土(CTAB-SMF)的吸附等温线符合Freundlich模型(R2>0.92,n>1),说明其对萘的吸附位点具有多样性,在较高萘平衡浓度(ce=1 mmol ·L-1)下吸附分配系数Kd为SMF的13.4倍;3-巯基丙基三甲氧基硅烷改性蒙脱土(TMSP-SMF)的吸附等温线符合Langmuir模型(R2>0.96),在较高萘平衡浓度(ce=1 mmol ·L-1)下吸附分配系数Kd为SMF的1.14倍.说明2种有机改性黏土对萘的吸附效果优于SMF颗粒.3种黏土颗粒对萘的吸附焓在-30~-10 kJ ·mol-1之间,均为自发物理吸附.溶液离子强度升高抑制了SMF吸附萘,但对改性黏土吸附萘无显著影响.萘平衡浓度较低(ce=0.1 mmol ·L-1)时,Cu2+的存在使TMSP-SMF对萘的吸附效果增加了3倍;同时萘能促进2种改性黏土对Cu2+的吸附.本研究通过原位在线QCM-D检测了黏土对萘的吸附机制,结果与批量吸附实验结果一致:CTAB-SMF对萘的吸附位点主要为黏土层间的改性剂基团,TMSP-SMF则位于黏土颗粒表面的改性剂基团.本项研究结果显示,QCM-D技术是一种有效的原位在线表征黏土膜吸附有机污染物的方法,2种有机改性的黏土颗粒可作为应用于PAHs或PAHs-重金属复合污染场地的修复材料.
英文摘要
      There are many sites contaminated by polycyclic aromatic hydrocarbons (PAHs) or combined PAHs-heavy metal in China, which pose serious health-risks to local people and environments. Dissipative quartz crystal microbalance (QCM-D) was applied to investigate the adsorption of naphthalene to two organic-modified smectite clays (cetyltrimethyl ammonium bromide modified montmorillonite, CTAB-SMF, and 3-mercapto propyl trimethoxy silane modified montmorillonite, TMSP-SMF) and original SMF, together with batch adsorption experiments. The results, based on in-situ online QCM-D experiments, showed that the adsorption sites of CTAB-SMF on naphthalene were mainly CTAB grouped between the interlayers of clay particles, while TMSP-SMF's were TMSP grouped on the surfaces of clay particles. The isotherms of naphthalene adsorption to CTAB-SMF fitted well (R2>0.92) with the Freundlich model, while the adsorption isotherms to TMSP-SMF and SMF fitted well with the Langmuir model (R2>0.96). The parameters of CTAB-SMF (n>1) indicated that the adsorption sites of naphthalene to CTAB-SMF were heterogeneous and the adsorption increases at higher equilibrium concentration. The adsorption capacity qmax of TMSP-SMF is significantly greater than that of SMF (P<0.05). Based on the calculation, the value of ΔHobs for these three clays (CTAB-SMF, TMSP-SMF, and SMF) were within the range of -30 to -10 kJ·mol-1, which indicated that it was a spontaneous exothermic physical process. The solution ionic strength could decrease the adsorption of naphthalene to SMF, but had limited effects on naphthalene adsorption to the two organo-modified clay particles. The existence of Cu2+ in the solution could enhance naphthalene adsorption to the three particles, and naphthalene could improve Cu2+ adsorption to these two modified clays. The results of this study show that QCM-D is a useful technique to indicate the changes of clay film during the process of adsorption, and the two organo-modified clay particles have the potential to be remediation materials to remediate PAHs or PAHs-heavy metal-contaminated sites.

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