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微波热解生物炭和水热炭对 Pb(II)的吸附取决于原料类型和生产温度。

Lead(II) adsorption on microwave-pyrolyzed biochars and hydrochars depends on feedstock type and production temperature.

机构信息

Department of Renewable Resources, University of Alberta, Edmonton, Alberta T6G 2E3, Canada; Land Reclamation International Graduate School, University of Alberta, Edmonton, Alberta T6G 2E3, Canada.

Department of Renewable Resources, University of Alberta, Edmonton, Alberta T6G 2E3, Canada; Land Reclamation International Graduate School, University of Alberta, Edmonton, Alberta T6G 2E3, Canada.

出版信息

J Hazard Mater. 2021 Jun 15;412:125255. doi: 10.1016/j.jhazmat.2021.125255. Epub 2021 Jan 29.

Abstract

Adsorption of lead(II) using carbon-rich chars is an environmentally sustainable approach to remediate lead(II) pollution in industrial wastewater. We studied mechanisms for lead(II) adsorption from synthetic wastewater by biochars produced by microwave-assisted pyrolysis and hydrochars by hydrothermal carbonization at three temperatures using four feedstocks. Lead(II) adsorption was highest (165 mg g) for canola straw biochar produced at 500 °C. Except for chars derived from sawdust, biochars outperformed hydrochars for lead(II) adsorption due to changes in solution pH driven by char pH. As char production temperature increased, lead(II) adsorption decreased in hydrochar mainly due to interaction with aromatic carbon but increased in biochar due to precipitation as hydrocerussite and lead oxide phosphate. Lead(II) adsorption also occurred via surface complexation and cation-ᴨ interaction, as the data fitted well to Freundlich, Langmuir and Temkin models, and the pseudo-first and pseudo-second order kinetic models, depending on feedstock type and production temperature. More than 80% of lead(II) adsorption occurred in the first 3 h for both types of chars; with a few exceptions, adsorption continued for almost 24 h. We conclude that production method, production temperature and feedstock type are crucial factors to consider in designing chars as adsorbents for removing lead(II) from wastewater.

摘要

使用富含碳的炭吸附铅(II)是一种环境可持续的方法,可用于修复工业废水中的铅(II)污染。我们研究了通过微波辅助热解和水热碳化在三种温度下使用四种原料生产的生物炭和水热炭从合成废水中吸附铅(II)的机理。在 500°C 下生产的油菜秸秆生物炭对铅(II)的吸附最高(165mg/g)。除了木屑衍生的炭以外,由于溶液 pH 受炭 pH 驱动的变化,生物炭对铅(II)的吸附优于水热炭。随着炭生产温度的升高,水热炭中铅(II)的吸附减少主要是由于与芳族碳的相互作用,但生物炭中铅(II)的吸附增加是由于氢羟磷铅矿和氧化铅的沉淀。铅(II)的吸附还通过表面络合和阳离子-π 相互作用发生,因为数据很好地符合 Freundlich、Langmuir 和 Temkin 模型以及拟一级和拟二级动力学模型,这取决于原料类型和生产温度。对于这两种类型的炭,超过 80%的铅(II)吸附在 3 小时内发生;除了少数例外,吸附几乎持续了 24 小时。我们得出的结论是,生产方法、生产温度和原料类型是设计用于从废水中去除铅(II)的炭作为吸附剂的关键因素。

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