Application of magnetite-activated persulfate oxidation for the degradation of PAHs in contaminated soils

过硫酸盐 化学 环境化学 土壤水分 萃取(化学) 降级(电信) 环境修复 土壤污染 过硫酸钠 磁铁矿 污染 污染物 核化学 色谱法 有机化学 环境科学 催化作用 土壤科学 生物 冶金 材料科学 电信 计算机科学 生态学
作者
Muhammad Usman,Pierre Faure,Christian Ruby,Khalil Hanna
出处
期刊:Chemosphere [Elsevier]
卷期号:87 (3): 234-240 被引量:152
标识
DOI:10.1016/j.chemosphere.2012.01.001
摘要

In this study, feasibility of magnetite-activated persulfate oxidation (AP) was evaluated for the degradation of polycyclic aromatic hydrocarbons (PAHs) in batch slurry system. Persulfate oxidation activated with soluble Fe(II) (FP) or without activation (SP) was also tested. Kinetic oxidation of PAHs was tracked in spiked sand and in aged PAH contaminated soils at circumneutral pH. Quartz sand was spiked with: (i) single model pollutant (fluorenone) and (ii) organic extract isolated from two PAH contaminated soils (H and NM sampled from ancient coking plants) and was subjected to oxidation. Oxidation was also performed on real H and NM soils with and without an extraction pretreatment. Results indicate that oxidation of fluorenone resulted in its complete degradation by AP while abatement was very low (<20%) by SP or FP. In soil extracts spiked on sand, significant degradation of 16 PAHs was observed by AP (70-80%) in 1 week as compared to only 15% by SP or FP systems. But no PAH abatement was observed in real soils whatever the treatment used (AP, FP or SP). Then soils were subjected to an extraction pretreatment but without isolation of organic extract from soil. Oxidation of this pretreated soil showed significant abatement of PAHs by AP. On the other hand, very low degradation was achieved by FP or SP. Selective degradation of PAHs was observed by AP with lower degradation efficiency towards high molecular weight PAHs. Analyses revealed that no by-products were formed during oxidation. The results of this study demonstrate that magnetite can activate persulfate at circumneutral pH for an effective degradation of PAHs in soils. However, availability of PAHs and soil matrix were found to be the most critical factors for degradation efficiency.
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