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添加复合吸附剂对土吸附菲和Cr (Ⅵ)的影响
摘要点击 1921  全文点击 749  投稿时间:2016-04-05  修订日期:2016-06-05
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中文关键词  修饰膨润土  生物炭  土  Cr(Ⅵ)    吸附量
英文关键词  modified bentonite  biochar  Lou soil  Cr(Ⅵ)  phenanthrene  adsorption amount
作者单位E-mail
李文斌 西北农林科技大学资源环境学院, 杨凌 712100 lwb062@163.com 
孟昭福 西北农林科技大学资源环境学院, 杨凌 712100
农业部西北植物营养与农业环境重点实验室, 杨凌 712100 
zfmeng@126.com 
吴琼 西北农林科技大学资源环境学院, 杨凌 712100  
许绍娥 西北农林科技大学资源环境学院, 杨凌 712100
Department of Biological and Agriculture Engineering, University of Arkansas, Fayetteville 72707, US 
 
刘泽 西北农林科技大学资源环境学院, 杨凌 712100  
中文摘要
      为了探究添加复合吸附剂对土吸附菲和Cr(Ⅵ)的影响,采用玉米秸秆生物炭和200% CEC十二烷基二甲基甜菜碱(BS-12)修饰膨润土(B200B)以质量比1:2、1:1和2:1组配为3种复合吸附剂(CS1:2、CS1:1和CS2:1),将其以不同添加量(2%、5%和10%)加入土,批处理法研究各土样对菲和Cr(Ⅵ)的等温吸附,并对比不同pH值和温度对吸附的影响.结果表明:①添加复合吸附剂的土(CS土)对Cr(Ⅵ)的吸附量是CK(土)的3.02~13.61倍,且等添加量下Cr(Ⅵ)吸附量表现为CS2:1 > CS1:1 > CS1:2 > CK.吸附为自发过程,表现为焓增(CS1:2除外)、熵增的特征.不同CS土对菲的吸附量为CK的3.87~13.00倍.2%和5%添加量下,菲的吸附量表现为CS1:2 > CS2:1 > CS1:1 > CK,而菲吸附量在10%添加量下为CS1:2 > CS1:1 > CS2:1 > CK.吸附表现为自发、焓减和熵增的特征.②10~30℃范围内,CK、CS1:1和CS2:1土对Cr(Ⅵ)的吸附量增加了5.84%、4.63%和8.22%,而CS1:2土对Cr(Ⅵ)的吸附量降低2.70%.CK对菲的吸附量从10~30℃增加1.69%,CS2:1、CS1:1和CS1:2土对菲的吸附量分别降低了10.55%、4.36%和12.81%.③pH值4~10,CK对Cr(Ⅵ)的吸附无显著变化,而各CS土对Cr(Ⅵ)的吸附量随pH值增大而降低.CK、CS1:2和CS1:1土对菲的吸附量在pH=4最大,而CS2:1土对菲的吸附量在pH=7最大.④复合吸附剂中B200B比例越高,CS土对菲的吸附越佳,而生物炭比例越高,CS土对Cr(Ⅵ)的吸附越好.
英文摘要
      To study the effect of the addition of compound adsorbent on the phenanthrene and Cr(Ⅵ) adsorption of Lou soil, biochar (made from corn stover) and B200B (Bentonite modified by BS-12, dodecyl dimethyl betaine with modified ratio of 200% CEC of Bentonite) were mixed at mass ratios of 1:2, 1:1 and 2:1 as the compound adsorbents (CS1:2, CS1:1 and CS2:1). Different amounts (2%, 5% and 10%) of these three compound adsorbents were added into Lou soil. Batch method was used to analyze the phenanthrene and Cr(Ⅵ) adsorption isotherms of different Lou samples, and compare the effect of environmental conditions such as pH value and temperature on the phenanthrene and Cr(Ⅵ) adsorption. The results indicated: ① Adsorption amounts of Cr(Ⅵ) on different Lou samples were 3.02 to 13.61 times higher than CK (original Lou soil). Under the same adding conditions (amount), Cr(Ⅵ) adsorption showed the order of CS2:1 Lou > CS1:1 Lou > CS1:2 Lou > CK. Cr(Ⅵ) adsorption was a spontaneous process with decreased enthalpy (except CS1:2) and increased entropy. Adsorption amounts of phenanthrene on different Lou samples were 3.87 to 13.00 times higher than CK. Phenanthrene adsorption presented the ranking of CS1:2 Lou > CS2:1 Lou > CS1:1 Lou > CK at the adding amounts of 2% and 5%, while showed the order of CS1:2 Lou > CS1:1 Lou > CS2:1 Lou > CK when 10% of the compound adsorbent was added. The adsorption was also a spontaneous process with decreased enthalpy and increased entropy. ② When the temperature was 10-30℃, the adsorption amount of Cr(Ⅵ) increased by 5.84%, 4.63% and 8.22% on CK, CS1:1 and CS2:1 Lou soils, and reduced by 2.70% on CS1:2 Lou soils. Adsorption amount of phenanthrene increased by 1.69% of CK and reduced by 10.55%, 4.36% and 12.81% of CS2:1, CS1:1 and CS1:2 Lou soils respectively. ③ When the pH was 4-10, the Cr(Ⅵ) adsorption had no significant change for CK, while those for CS1:2, CS1:1 and CS2:1 Lou soils all reduced. Phenanthrene adsorption of CK, CS1:2 and CS1:1 Lou soils was all highest at pH=4, and phenanthrene adsorption of CS2:1 Lou was highest at pH=7.④ The higher the ratio of B200B in compound adsorbent, the better the phenanthrene adsorption was. The higher the ratio of biochar in compound adsorbent, the better the Cr(Ⅵ) adsorption was.

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