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Leaching of polycyclic aromatic hydrocarbons (PAHs) from sewage sludge-derived biochar

机译:从污水污泥衍生的生物炭浸出多环芳烃(PAHS)

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Polycyclic aromatic hydrocarbons (PAHs), a family of persistent organic pollutants with various negative health effects, are inherently formed during biochar pyrolysis. However, the knowledge regarding the leaching potentials and mechanisms of PAHs remains limited for biochar implementation to soil. In this study we evaluated the leaching behaviors of PAHs from sewage sludge-derived biochar pyrolyzed at different temperatures (300-700 degrees C) using the protocol of Synthetic Precipitation Leaching Procedure (SPLP) with deionized water. Leachate concentrations of sixteen U. S. Environmental Protection Agency PAHs increased with the increasing pyrolysis temperature, exhibiting an opposite pyrolytic temperature dependence with their concentrations in biochar. The total leachate PAH concentration peaked at 700 degrees C with 11.75 mu g/L, corresponding to 15.9% of total PAHs present in biochar. PAH leaching was associated with the release of hydrophobic organic compounds (HOCs) that created a mobile phase to facilitate the mobilization of PAHs into water. The enhanced release of calcium, aluminum, and barium from the biochars with pyrolysis temperature could also favor the leaching of biochar PAHs, due to the destruction of HOCs-(metal ions)-mineral linkages, which improved the release of HOCs and HOCs-bound PAHs; and because the extent of metal cross-linking in biochar is reduced, enabling better diffusion of PAHs through the inner matrix and thus accelerating their desorption.
机译:多环芳烃(PAHS)是一种具有各种阴性健康作用的持续有机污染物的家族,在生物淀粉过程中固有地形成。然而,关于浸出潜力和PAHS机制的知识仍然有限于土壤的生物炭。在这项研究中,我们使用与去离子水的合成沉淀浸出程序(SPLP)的方案,从不同温度(300-700摄氏度)的污水污泥衍生的生物炭中评估了PAHS的浸出行为。渗滤液浓度为16岁美国。环境保护局PAHS随着热解温度的增加而增加,表现出与其在生物炭中的浓度相反的热解温度依赖性。总渗滤液PAH浓度在700℃下达到11.75μg,11.75μg,对应于生物炭中存在的15.9%。 PAH浸出与产生流动相的疏水性有机化合物(HOC)的释放有关,以促进将PAHS迁入水中。由于Hocs-(金属离子) - mineral键的破坏,增强了来自热解温度的钙,铝和钡的增强释放来自生物脉冲温度的生物脉冲温度的爆发,这改善了Hocs和Hocs结合的释放PAHS;并且因为生物炭中的金属交联程度降低,因此能够更好地通过内基质扩散PAH,从而加速其解吸。

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