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不同温度生物炭对可变电荷土壤吸附Pb(II)的影响

[Effects of different temperatures biochar on adsorption of Pb(II) on variable charge soils].

作者信息

Jiang Tian-Yu, Jiang Jun, Xu Ren-Kou, Zhou Li-Xiang, Wang Shi-Mei

机构信息

College of Resources and Environmental Science, Nanjing Agricultural University, Nanjing 210095, China.

出版信息

Huan Jing Ke Xue. 2013 Apr;34(4):1598-604.

Abstract

Effects of incorporation of the biochars generated from rice straw and peanut straw at different temperatures on soil pH and Pb(II) adsorption were investigated with two variable charge soils. The soil pH increased by 1.04-3.00 units, and the increase in soil pH increased with the rise of pyrolysis temperature of the biochar. Results from adsorption isotherm experiments indicated that the incorporation of the biochar enhanced the adsorption of Pb(II) by two soils. The adsorption of Pb(II) was increased by 12.6% -57.6%, when the initial concentration of Pb(II) is 2 mmol x L(-1). The adsorption also increased with rising pH. Freundlich and Langmuir equations can be used to fit the adsorption isotherms of Pb(II), but the Freundlich equation fitted the adsorption data better, the r-values are above 0.94. Soils incorporated with peanut straw char have a greater adsorption capacity for Pb(II) than these incorporated with rice straw char as predicted by the parameters of k and Q(m) in Freundlich and Langmuir equations, respectively. The biochars generated at 400 degrees C have a greater enhancement on Pb(II) adsorption by soils than 300 degrees C and 500 degrees C. Desorption results showed that the desorption of Pb(II) for the treatments with biochar added was greater than that for the control, but the amount of desorbed Pb(II) was much lower than that of adsorbed Pb(II). These results suggested that the enhanced adsorption of Pb(II) by incorporation of the biochars involved at least two mechanisms: electrostatic adsorption and non-electrostatic adsorption.

摘要

研究了在两种可变电荷土壤中,不同温度下稻草和花生壳生物炭的掺入对土壤pH值和Pb(II)吸附的影响。土壤pH值增加了1.04 - 3.00个单位,且土壤pH值的增加随着生物炭热解温度的升高而增加。吸附等温线实验结果表明,生物炭的掺入增强了两种土壤对Pb(II)的吸附。当Pb(II)的初始浓度为2 mmol·L(-1)时,Pb(II)的吸附量增加了12.6% - 57.6%。吸附量也随着pH值的升高而增加。Freundlich和Langmuir方程可用于拟合Pb(II)的吸附等温线,但Freundlich方程对吸附数据的拟合效果更好,r值均在0.94以上。分别根据Freundlich和Langmuir方程中的k和Q(m)参数预测,掺入花生壳生物炭的土壤对Pb(II)的吸附能力比掺入稻草生物炭的土壤更强。400℃下生成的生物炭对土壤吸附Pb(II)的增强作用比300℃和500℃下生成的生物炭更大。解吸结果表明,添加生物炭处理的Pb(II)解吸量大于对照处理,但解吸的Pb(II)量远低于吸附的Pb(II)量。这些结果表明,生物炭掺入增强Pb(II)吸附至少涉及两种机制:静电吸附和非静电吸附。

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