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使用低成本生物炭,一种绿色吸附剂,对水中铬的修复进行建模和评估。

Modeling and evaluation of chromium remediation from water using low cost bio-char, a green adsorbent.

机构信息

School of Environmental Sciences, Jawaharlal Nehru University, New Delhi 110067, India. dm

出版信息

J Hazard Mater. 2011 Apr 15;188(1-3):319-33. doi: 10.1016/j.jhazmat.2011.01.127. Epub 2011 Feb 4.

Abstract

Oak wood and oak bark chars were obtained from fast pyrolysis in an auger reactor at 400-450 °C. These chars were characterized and utilized for Cr(VI) remediation from water. Batch sorption studies were performed at different temperatures, pH values and solid to liquid ratios. Maximum chromium was removed at pH 2.0. A kinetic study yielded an optimum equilibrium time of 48 h with an adsorbent dose of 10 g/L. Sorption studies were conducted over a concentration range of 1-100mg/L. Cr(VI) removal increased with an increase in temperature (Q(Oak wood)(°): 25 °C = 3.03 mg/g; 35 °C = 4.08 mg/g; 45 °C = 4.93 mg/g and Q(Oakbark)(°): 25 °C = 4.62 mg/g; 35 °C = 7.43 mg/g; 45 °C = 7.51 mg/g). More chromium was removed with oak bark than oak wood. The char performances were evaluated using the Freundlich, Langmuir, Redlich-Peterson, Toth, Radke and Sips adsorption isotherm models. The Sips adsorption isotherm model best fits the experimental data [high regression (R(2)) coefficients]. The overall kinetic data was satisfactorily explained by a pseudo second order rate expression. Water penetrated into the char walls exposing Cr(VI) to additional adsorption sites that were not on the surfaces of dry char pores. It is remarkable that oak chars (S(BET): 1-3m(2)g(-1)) can remove similar amounts of Cr(VI) as activated carbon (S(BET): ∼ 1000 m(2)g(-1)). Thus, byproduct chars from bio-oil production might be used as inexpensive adsorbents for water purification. Char samples were successfully used for chromium remediation from contaminated surface water with dissolved interfering ions.

摘要

从在 400-450°C 的螺旋反应器中快速热解得到的橡木和橡木树皮炭被用于从水中修复六价铬。对这些炭进行了特性分析,并将其用于修复水中的六价铬。在不同温度、pH 值和固液比下进行了批量吸附研究。在 pH 值为 2.0 时,铬的去除率最高。动力学研究表明,在 10 g/L 的吸附剂剂量下,最佳平衡时间为 48 小时。吸附研究在 1-100mg/L 的浓度范围内进行。随着温度的升高,Cr(VI)的去除率增加(Q(Oak wood)(°):25°C = 3.03mg/g;35°C = 4.08mg/g;45°C = 4.93mg/g 和 Q(Oakbark)(°):25°C = 4.62mg/g;35°C = 7.43mg/g;45°C = 7.51mg/g)。橡木皮比橡木去除的铬更多。使用 Freundlich、Langmuir、Redlich-Peterson、Toth、Radke 和 Sips 吸附等温线模型评估了炭的性能。Sips 吸附等温线模型最适合实验数据[高回归(R(2))系数]。总体动力学数据可以通过拟二级速率表达式得到很好的解释。水渗透到炭壁中,使 Cr(VI)暴露于更多的吸附位,而这些吸附位不在干炭孔表面。值得注意的是,橡木炭(S(BET):1-3m(2)g(-1))可以去除与活性炭(S(BET):∼1000m(2)g(-1))相当数量的 Cr(VI)。因此,生物油生产中的副产物炭可能被用作廉价的水净化吸附剂。炭样品成功地用于从受污染的地表水去除溶解的干扰离子。

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