MgCl2改性的污水污泥源生物炭:用作水中除磷的吸附材料

Valber Georgio de Oliveira Duarte , Jader Alves Ferreira , Denise Eulálio , Guilherme Max Dias Ferreira , Vera Regina Leopoldo Constantino , Gustavo Franco de Castro , Jairo Tronto
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摘要

污水污泥(SS)是污水处理厂由于去除固体和液体废物而产生的。SS富含有机物,可能含有病原体和高浓度重金属,对环境构成重大挑战。在这方面,已加紧寻求有效和可持续的解决办法来处理这种废物。将SS转化为生物炭正在成为有效管理这种废物的有用解决方案。生物炭是一种由生物质热解获得的含碳物质,其孔隙率和比表面积取决于所使用的原料。本研究旨在以SS为生物质制备mgcl2改性生物炭,作为水介质中磷的吸附剂。采用x射线粉末衍射(XRD)、热重分析(TGA)、衰减全反射傅立叶变换红外光谱(ATR-FTIR)、扫描电镜- x射线能谱(SEM-EDS)、比表面积(BET)和零电荷点(PZC)对制备的SS进行了热解。对磷在生物炭上的动力学和平衡吸附研究进行了评估,其中将50.0 mg恒定质量的生物炭添加到25.0 mL的溶液中,其中P的浓度范围为0至350.0 mg∙L−1。溶液旋转48 h,并进行三次。用镁对生物炭进行改性是有效的。此外,动力学数据表明,拟二阶模型较好地拟合了实验数据。吸附机理是通过Mg2+离子在500℃热解材料表面化学沉淀P种或与阴离子Cl-等离子交换。P的吸附等温线符合Langmuir模型,48 h后的最大吸附量为176 mg·g⁻1。由SS制备的镁功能化生物炭具有从水介质中去除磷的高能力,这代表了将该材料用作磷肥的有希望的替代方案。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
Sewage sludge-derived biochar modified with MgCl2: Used as adsorbent material for phosphorus removal from aqueous medium
Sewage sludge (SS) is produced in wastewater treatment plants due to the removal of solid and liquid waste. SS is rich in organic matter and can contain pathogens and high levels of heavy metals, posing a significant environmental challenge. The search for effective and sustainable solutions to treat this waste has intensified in this context. Transforming SS into biochar is emerging as a useful solution for effectively managing this waste. Biochar is a carbonaceous material obtained from biomass pyrolysis, having porosity and specific surface area that vary depending on the raw material used. This study aimed to produce MgCl2-modified biochar using SS as biomass to be used as an adsorbent for P in an aqueous medium. SS containing or not MgCl2 incorporated was pyrolyzed at different temperatures and the obtained materials were characterized by X-ray powder diffraction (XRD), thermogravimetric analysis (TGA), attenuated total reflectance Fourier transform infrared spectroscopy (ATR-FTIR), scanning electron microscopy coupled with energy dispersive X-ray spectroscopy (SEM-EDS), specific surface area (BET) and point of zero charge (PZC). Kinetic and equilibrium adsorption studies of P on the biochar were evaluated, in which a 50.0 mg constant mass of biochar was added to 25.0 mL solutions containing P concentrations ranging from 0 to 350.0 mg∙L−1. The solutions were swirled for 48 h and was conducted in triplicate. The process of modifying the biochar with magnesium was effective. Additionally, the kinetic data showed that the pseudo-second-order model better fitted the experimental data. The adsorption mechanism occurs through the chemical precipitation of P species with Mg2+ ions or ionic exchange with anions such as Cl- on the surface of the material pyrolyzed at 500°C. The P adsorption isotherm followed the Langmuir model, with a maximum adsorption capacity of 176 mg·g⁻1 after 48 h. Magnesium-functionalized biochar produced from SS has a high capacity for P removal from an aqueous medium, which represents a promising alternative for applying this material as a P fertilizer.
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