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污水处理厂污泥水溶解性有机物的光谱特性分析
摘要点击 2513  全文点击 1381  投稿时间:2015-10-27  修订日期:2015-11-27
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中文关键词  污泥水  三维荧光光谱  溶解性有机物  污水处理  傅里叶红外光谱
英文关键词  reject water  three-dimensional emission-excitation matrix  dissolved organic matters  wastewater treatment  Fourier transform infrared spectroscopy
作者单位E-mail
牛天浩 上海电力学院环境与化学工程学院, 上海 200090 blastcalf@126.com 
周振 上海电力学院环境与化学工程学院, 上海 200090 zhouzhen@shiep.edu.cn 
胡大龙 上海电力学院环境与化学工程学院, 上海 200090  
魏海娟 上海城投污水处理有限公司, 上海 201203  
李晶 上海城投污水处理有限公司, 上海 201203  
窦微笑 上海电力学院环境与化学工程学院, 上海 200090  
葛红花 上海电力学院环境与化学工程学院, 上海 200090  
中文摘要
      污泥水是污水处理厂污泥浓缩、稳定、脱水等环节产生的废水,具有污染物浓度高、成分复杂的特点.采用三维荧光光谱和红外光谱研究了污泥水中溶解性有机物(DOM)的光谱特性.污泥水荧光性DOM(FDOM)可利用平行因子分析划分为6个荧光组分,分别为类蛋白质组分C1(275/355 nm)、C4(235/350 nm)和C6(275/305 nm),及类腐殖酸组分C2(250,340/440 nm)、C3(320/380 nm)和C5(250/465 nm).重力浓缩和机械浓缩污泥水中COD与所有类腐殖酸组分均正显著相关(P<0.01),类蛋白质组分对其影响不大.离心脱水污泥水中组分C1、C4和C5含量明显上升.深度脱水污泥水中FDOM荧光峰位置和强度与其它污泥水存在显著差异,C3和C6分别较离心脱水污泥水升高15.63和7.30倍. 与浓缩污泥水相比,离心脱水污泥水中多糖和腐殖酸吸收峰增强,而深度脱水污泥水中蛋白质大量释放,金属离子会与腐殖酸和蛋白质络合引起DOM结构变化.
英文摘要
      Reject water generated from sludge thickening, dewatering and stabilization process contains high-content and complex dissolved organic matters (DOM). The spectral characteristics of DOM in the reject water were investigated by three-dimensional excitation-emission matrix and Fourier transform infrared spectroscopy. Fluorescent DOM (FDOM) from reject water were decomposed into six components by parallel factor analysis, the protein-like C1 (275/355 nm), C4 (235/350 nm) and C6 (275/305 nm) and the humic-like C2 (250, 340/440 nm), C3 (320/380 nm) and C5 (250/465 nm). Soluble COD in the sludge thickening reject water was positively correlated with all the three humic-like substances at P<0.01 level, and was insignificantly influenced by protein-like substances. The tryptophan-like C1, C4 and humic-like C5 increased in the centrifugal dewatering reject water (CDRW). FDOM in the advanced dewatering reject water (ADRW) were significantly different from those of other reject water in fluorescence peak locations and intensities, and humic-like C3 and tyrosine-like C6 in the DOM were 15.63 and 7.30 times higher than those in CDRW. Compared to sludge thickening reject water, infrared peaks related to polysaccharide and humic substances in CDRW were enhanced, and massive proteins were released into ADRW. DOM structures in ADRW were changed owing to the complexation between metals and both humic substances and proteins.

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