Microwave‐enhanced Fe0/PDS system for treating refractory organic matter in biotreated landfill leachate effluent

化学 有机质 渗滤液 流出物 硫酸盐 零价铁 腐殖质 总有机碳 环境化学 吸附 无机化学 核化学 废物管理 有机化学 土壤水分 环境科学 工程类 土壤科学
作者
Feiyan Fang,Xi Luo,Qibin Li
出处
期刊:Water Environment Research [Wiley]
卷期号:97 (2)
标识
DOI:10.1002/wer.70040
摘要

Abstract The effluent produced from treating landfill leachate via biological methods still contains a large amount of refractory organic matter and needs to be further treated. In this study, we used a microwave‐enhanced zero‐valent iron/peroxydisulfate (MW/Fe 0 /PDS) system for the further treatment of biotreated landfill leachate effluent (BTLE). We investigated the efficiency and mechanism of removing refractory organic matter from BTLE. The results show that under the conditions of MW = 240 W, [PDS] 0 = 40 mM, [Fe 0 ] 0 = 10 mM, and t = 12 min, the MW/Fe 0 /PDS system best removed organic matter in the BTLE. The removal rates of UV absorbance at 254 nm, color number, and total organic carbon reached 76.94%, 93.50%, and 63.08%, respectively. The aromaticity, degree of humification, molecular weight, and degree of polymerization of the organic matter decreased significantly. The surface morphology and elemental valence analysis of Fe 0 before and after the reaction revealed that iron‐based oxides (i.e., Fe 2 O 3 , Fe 3 O 4 , FeOOH, and Fe (OH) 3 ) formed on the surface of Fe 0 . The refractory organic matter was removed by homogeneous and heterogeneous Fenton‐like reactions and the adsorption–precipitation of iron‐based colloids. The thermal and nonthermal effects of MW promoted direct PDS decomposition, accelerated the formation of Fe 2+ on the surface of Fe 0 , promoted the redox cycle of Fe 3+ /Fe 2+ , and generated more sulfate radicals (SO 4 •− ). Together, these effects improved the removal efficiency of refractory organic matter. The results of this study can serve as a theoretical basis for the use of the MW/Fe 0 /PDS system to treat refractory organic matter in BTLE. Practitioner Points A microwave‐enhanced Fe 0 /PDS system is effective for removing organic matter from landfill leachate. Colored and fluorescent organic matter in the landfill leachate was efficiently degraded. Heterogeneous and homogeneous effects Fenton reactions are involved in the system.
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