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首页> 外文期刊>The Science of the Total Environment >Impacts of carbonization temperature on the Pb(II) adsorption by wheat straw-derived biochar and related mechanism
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Impacts of carbonization temperature on the Pb(II) adsorption by wheat straw-derived biochar and related mechanism

机译:碳化温度对麦秸生物炭吸附Pb(II)的影响及机理

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摘要

To determine the quantitative correlations between physicochemical characteristics and Pb(ll) adsorption amounts of biochar fractions, we prepared wheat straw-derived biochar under various carbonization temperatures (300-900 degrees C). The different fractions of the wheat straw-derived biochar, water-soluble material (WM), acid-soluble material (AM), and organic material (OM), were acquired. The ash content, ultimate analysis, pH, ion strength (IS),cation exchange capacity(CEC),and acidic functional groups(AFG) were characterized. The Pb(II) adsorption amounts of different biochars and their fractions were determined. The results revealed that the proportions of biochar fractions (WM, AM, and OM) varied with various carbonization temperatures. The maximum Pb(II) adsorption amount of wheat straw-derived biochar (q(Total)) was 157.95 +/- 0.13 mg/g obtained at 800 degrees C, and the quantitative correlations between Pb(II) adsorption amount (q) and carbonization temperature (T) can be elaborated by q(Total) = 170.72-336.62exp(-0.0035T) (R-2 = 0.97), q(WM) 106.18-390.10exp (-0.0046T) (R-2 = 0.98), q(AM) = 496.16-477.74exp(-0.0001T) (R-2 = 0.79), and q(OM) = 1.80 + 34.69exp (-0.0038T) (R-2 = 0.85). For rate of contribution (RC) for Pb(II) adsorption, when T < 400 degrees C, the order was AM (60.72 +/- 733%) > OM (23.41 +/- 7.33%) > WM (15.87 +/- 0.30%); however, when T >= 400 degrees C, the order was WM (52.31 +/- 0.85% - 67.65 +/- 2.99%) > AM (29.65 +/- 0.46% - 35.77 +/- 0.12%) > OM (2.30 +/- 0.47% - 12.02 +/- 2.43%). Moreover, q(WM) and q(AM) exhibited significant positive linear correlations with ash (q(WM) = 9.92Ash - 123.65, and q(AM) = 2.13Ash - 0.49), q(Total) was predominantly affected by ash content (q(Total) = 10.97 Ash - 95.49). The EDX, XRD, and FTIR analysis results further clarified that ion exchange and precipitation were the main adsorption mechanisms for Pb(II) adsorption by wheat straw-derived biochar. (C) 2019 Elsevier B.V. All rights reserved.
机译:为了确定理化特性与生物炭馏分的Pb(II)吸附量之间的定量相关性,我们在各种碳化温度(300-900摄氏度)下制备了麦杆衍生的生物炭。获得了麦秸衍生的生物炭,水溶性材料(WM),酸溶性材料(AM)和有机材料(OM)的不同部分。表征了灰分,最终分析,pH,离子强度(IS),阳离子交换容量(CEC)和酸性官能团(AFG)。确定了不同生物炭及其部分的Pb(II)吸附量。结果表明,生物炭馏分(WM,AM和OM)的比例随碳化温度的不同而变化。麦秸来源生物炭的最大Pb(II)吸附量(q(总计))为800.C下获得的157.95 +/- 0.13 mg / g,Pb(II)吸附量(q)和碳化温度(T)可以通过q(总计)= 170.72-336.62exp(-0.0035T)(R-2 = 0.97),q(WM)106.18-390.10exp(-0.0046T)(R-2 = 0.98)来阐述),q(AM)= 496.16-477.74exp(-0.0001T)(R-2 = 0.79)和q(OM)= 1.80 + 34.69exp(-0.0038T)(R-2 = 0.85)。对于Pb(II)吸附的贡献率(RC),当T <400摄氏度时,顺序为AM(60.72 +/- 733%)> OM(23.41 +/- 7.33%)> WM(15.87 +/-) 0.30%);但是,当T> = 400摄氏度时,顺序为WM(52.31 +/- 0.85%-67.65 +/- 2.99%)> AM(29.65 +/- 0.46%-35.77 +/- 0.12%)> OM(2.30 +/- 0.47%-12.02 +/- 2.43%)。此外,q(WM)和q(AM)与灰分呈显着正线性相关(q(WM)= 9.92Ash-123.65,q(AM)= 2.13Ash-0.49),q(Total)主要受灰分影响含量(q(总计)= 10.97灰分-95.49)。 EDX,XRD和FTIR分析结果进一步阐明,离子交换和沉淀是麦草衍生生物炭对Pb(II)吸附的主要吸附机理。 (C)2019 Elsevier B.V.保留所有权利。

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