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垃圾填埋水溶性有机物组成、演化及络合重金属特征
引用本文:肖骁,何小松,席北斗,高如泰,李丹,张慧,崔东宇,袁志业.垃圾填埋水溶性有机物组成、演化及络合重金属特征[J].环境科学,2017,38(9):3705-3712.
作者姓名:肖骁  何小松  席北斗  高如泰  李丹  张慧  崔东宇  袁志业
作者单位:中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护地下水污染模拟与控制重点实验室, 北京 100012,中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护地下水污染模拟与控制重点实验室, 北京 100012,中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护地下水污染模拟与控制重点实验室, 北京 100012,中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护地下水污染模拟与控制重点实验室, 北京 100012,中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护地下水污染模拟与控制重点实验室, 北京 100012,中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护地下水污染模拟与控制重点实验室, 北京 100012,中国环境科学研究院环境基准与风险评估国家重点实验室, 北京 100012;中国环境科学研究院国家环境保护地下水污染模拟与控制重点实验室, 北京 100012,北京铮实环保工程有限公司, 北京 100076
基金项目:国家自然科学基金青年科学基金项目(51408573);国家水体污染控制与治理科技重大专项(2015ZX07103-007)
摘    要:采集不同填埋年限垃圾和渗滤液,提取制备水溶性有机物(DOM),采用紫外光谱、荧光光谱及1H-核磁共振,研究垃圾填埋DOM组成、演化及络合重金属特征.结果表明,填埋初期(5 a)DOM以脂肪族类物质为主,DOM中芳香族物质随填埋进行含量降低,苯环结构上的羰基、羧基和羟基等随填埋进行不断减少;填埋中后期(5 a)DOM以碳水化合物、有机胺等为主,随着填埋年限的延伸DOM中芳香性物质含量上升,苯环上羰基、羧基和羟基等官能团不断增加.填埋产生的渗滤液原液DOM中同时含有脂族类物质、碳水化合物、有机胺等,渗滤液经过厌氧-好氧和MBR处理后,碳水化合物和芳香族化合物含量相对增加,但小分子有机物和烷基链烃物质含量减少,脂肪链支链变短,分支增加.垃圾填埋DOM通过含氮和含氧官能团络合金属Zn从而影响其分布,而对其他金属的分布影响较小.

关 键 词:填埋垃圾  渗滤液  水溶性有机物  组成演化  光谱
收稿时间:2017/3/16 0:00:00
修稿时间:2017/4/11 0:00:00

Composition, Evolution, and Complexation of Dissolved Organic Matter with Heavy Metals in Landfills
XIAO Xiao,HE Xiao-song,XI Bei-dou,GAO Ru-tai,LI Dan,ZHANG Hui,CUI Dong-yu and YUAN Zhi-ye.Composition, Evolution, and Complexation of Dissolved Organic Matter with Heavy Metals in Landfills[J].Chinese Journal of Environmental Science,2017,38(9):3705-3712.
Authors:XIAO Xiao  HE Xiao-song  XI Bei-dou  GAO Ru-tai  LI Dan  ZHANG Hui  CUI Dong-yu and YUAN Zhi-ye
Institution:State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory of Simulation and Control of Groundwater Pollution, Chinese Research Academy of Environmental Science, Beijing 100012, China,State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory of Simulation and Control of Groundwater Pollution, Chinese Research Academy of Environmental Science, Beijing 100012, China,State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory of Simulation and Control of Groundwater Pollution, Chinese Research Academy of Environmental Science, Beijing 100012, China,State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory of Simulation and Control of Groundwater Pollution, Chinese Research Academy of Environmental Science, Beijing 100012, China,State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory of Simulation and Control of Groundwater Pollution, Chinese Research Academy of Environmental Science, Beijing 100012, China,State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory of Simulation and Control of Groundwater Pollution, Chinese Research Academy of Environmental Science, Beijing 100012, China,State Key Laboratory of Environmental Criteria and Risk Assessment, Chinese Research Academy of Environmental Sciences, Beijing 100012, China;State Environmental Protection Key Laboratory of Simulation and Control of Groundwater Pollution, Chinese Research Academy of Environmental Science, Beijing 100012, China and Beijing Zhengshi Environmental Engineering Co., Ltd., Beijing 100076, China
Abstract:Samples of wastes and leachates were collected from a landfill site and a leachate treatment planti.e., equalization basin, anaerobic zone, oxidation ditch, and membrane bioreactor (MBR) section]. Dissolved organic matter (DOM) was extracted from the wastes and leachates, and its composition, evolution, and complexation characteristics with heavy metals were studied using UV-Visible and fluorescence spectroscopy combined with1H nuclear magnetic resonance. The aliphatic compounds were found to be the main substances in DOM in the fresh landfill wastes (<5 a), and the relative content of aromatics and substituent groups, i.e., carbonyl, hydroxyl, and carboxyl functional groups, decreased during the initial process. On the other hand, carbohydrates and organic amines were observed to be the main substances in DOM obtained from the intermediate and old landfill wastes (>5 a), and the relative content of aromatics and substituent groups (carbonyl, hydroxyl, and carboxyl functional groups) increased persistently during the process of organic matter humification. The aliphatics, carbohydrates, and organic amines all existed in DOM from the equalization basin Carbohydrates and aromatic compounds increased rapidly after the anaerobic, aerobiotic, and membrane treatment. However, low molecular weight organic matter and alkyl chain substances decreased during the leachate treatment process and the side chain of the aliphatics was shortened despite the increase in its content. The distribution of zinc in the wastes and leachates was influenced by the complexation with the nitrogen-and oxygen-containing functional groups, whose effect on other metals was not obvious.
Keywords:municipal solid waste landfill  leachate  dissolved organic matter(DOM)  composition and evolution  spectra
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