1. 陕西理工大学化学与环境科学学院,陕西,汉中,723001
2. 陕西秦巴山区生物资源综合开发协同创新中心,陕西,汉中,723001
3. 西北农林科技大学水土保持研究所,陕西 杨凌,712100
4. 中科院水利部水土保持研究所,陕西 杨凌,712100
纸质出版:2017
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宋凤敏, 张兴昌, 葛红光. 黄褐土与水稻田沙土对Mn(Ⅱ)和Ni(Ⅱ)的吸附[J]. 水土保持学报, 2017,31(1):265-271.
SONG Fengmin1, 2, ZHANG Xingchang3, et al. Adsorption Characteristics of Mn (Ⅱ) and Ni (Ⅱ) in Browns Soil and Rice Paddies Sand[J]. 2017, 31(1): 265-271.
宋凤敏, 张兴昌, 葛红光. 黄褐土与水稻田沙土对Mn(Ⅱ)和Ni(Ⅱ)的吸附[J]. 水土保持学报, 2017,31(1):265-271. DOI: 10.13870/j.cnki.stbcxb.2017.01.044.
SONG Fengmin1, 2, ZHANG Xingchang3, et al. Adsorption Characteristics of Mn (Ⅱ) and Ni (Ⅱ) in Browns Soil and Rice Paddies Sand[J]. 2017, 31(1): 265-271. DOI: 10.13870/j.cnki.stbcxb.2017.01.044.
为探明陕南矿区典型土壤(黄褐土和水稻田沙土)对Mn(Ⅱ)和Ni(Ⅱ)的吸附特性,采用振荡平衡法研究黄褐土与水稻田沙土对Mn(Ⅱ)和Ni(Ⅱ)的等温吸附过程,并用数学模型模拟其吸附动力学过程,结合红外光谱(FTIR)分析,探讨2种土壤吸附Mn(Ⅱ)和Ni(Ⅱ)的机理及其影响因素。结果表明:Mn(Ⅱ)和Ni(Ⅱ)在2种土壤中的吸附均在120 min达到平衡,黄褐土对于Mn(Ⅱ)和Ni(Ⅱ)的吸附能力远远高于水稻田沙土,黄褐土对Mn(Ⅱ)和Ni(Ⅱ)最大吸附量分别为2.12,1.19 mg/g,沙土对Mn(Ⅱ)和Ni(Ⅱ)最大吸附量达到1.32,0.78 mg/g;准一级动力学模型、双常数模型和内扩散模拟模型适合于表征Mn(Ⅱ)和Ni(Ⅱ)的吸附动力学特征,黄褐土吸附动力学特性的模型吻合度高于水稻田沙土;Langmuir吸附等温方程可较好地模拟Ni(Ⅱ)在2种土壤中的等温吸附过程,Freundlich吸附等温方程可很好模拟Mn(Ⅱ)黄褐土吸附等温过程;在研究pH范围内,Mn(Ⅱ)的吸附率随pH的增加变化不大,Ni(Ⅱ)的吸附率均随pH的增加而增加,土壤pH对重金属离子解吸影响较大,酸性条件下有利于重金属离子解吸;通过土壤基本理化性质与吸附参数相关分析,结合吸附前后土壤的红外光谱分析,说明土壤有机质含量对重金属Mn(Ⅱ)和Ni(Ⅱ)的吸附起重要作用,有机物所含官能团对重金属起到一定的化学吸附作用。
In order to find out the adsorption characteristics of Mn (Ⅱ) and Ni (Ⅱ) in typical soil (browns soil and rice paddies sand ) in mining area of southern Shaanxi
and to provide certain theoretical basis for prevention and control pollution of manganese in the mining area
in this paper the adsorption behavior of Mn (Ⅱ) and Ni(Ⅱ) in typical soil was studied by using vibration batch equilibrium techniques
coupled with dynamics and thermodynamic absorption models and infrared spectroscopic (FTIR) analysis
it aimed to determine the mechanism and affecting factors of Mn (Ⅱ) and Ni (Ⅱ) absorption by the soil. The results showed that the absorptions of Mn (Ⅱ) and Ni (Ⅱ) by the two types soil achieved equilibrium within 120 min
the adsorption capacity of the metal on browns soil was much higher than the rice paddies sand
the maximum adsorption capacity of Mn (Ⅱ) and Ni (Ⅱ) on browns soil determined to be 2.12 mg/g and 1.19 mg/g,whereas on rice paddies sand reached 1.32 mg/g and 0.78 mg/g respectively. The adsorption kinetics process of Mn (Ⅱ) and Ni (Ⅱ) in the two kinds of soil could be well interpreted by three isotherm models (i.e.
pseudo-first-order kinetic
bi-constant and intra-particle diffusion models)
the alignment with the models for the browns soil of adsorption dynamics were higher than for the rice paddies sand. In two kinds of soil the adsorption isotherm of Mn (Ⅱ) and Ni (Ⅱ)
Freundlich equation was superior to the Langmuir adsorption isotherm equation. Within the pH range in the study
pH value had little influence on the adsorption efficiency of Mn (Ⅱ) from aqueous solution
but had some influence on Ni (Ⅱ)
whereas the desorption of the two kinds metal was affected by pH value
and metal could be desorbed from soil only when the pH value of solution was less than 3. The relation of basic physical and chemical properties of soil
adsorption parameters and FTIR analysis demonstrated that soil organic matter played an important role in adsorption of Mn (Ⅱ) and Ni (Ⅱ).
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