共查询到19条相似文献,搜索用时 109 毫秒
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生物反应器填埋场中水平沟回灌渗滤液非饱和-饱和渗流分析 总被引:3,自引:0,他引:3
水平沟回灌是生物反应器填埋场中渗滤液回灌的主要模式之一,为研究水平沟回灌时生物反应器填埋场中渗滤液的非饱和-饱和运移规律,垃圾体的饱和与非饱和区域采用不同水流控制方程,饱和区域的水流控制方程采用饱和Richards方程,对垃圾体非饱和区域,由质量守恒原理,以修正的Darcy定理为基础,结合Elagroudy等提出的垃圾体沉降模型,建立了考虑垃圾体沉降的非饱和渗滤液运移控制方程。基于建立的考虑沉降特性的二维非饱和-饱和水平沟回灌计算模型,研究了水平沟回灌时渗滤液在生物反应器填埋场中的运移规律,提出水平沟回灌系统的设计方法。 相似文献
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水分运移对填埋垃圾降解过程的影响模拟研究 总被引:1,自引:0,他引:1
模拟填埋实验对比研究了渗滤液定期排放、降雨入渗及渗滤液全量回灌对垃圾生物质降解过程的影响,探讨了生物气资源化填埋水分运移的调控措施.结果表明:渗滤液定期排放难以形成产甲烷菌适宜的Eh、pH及湿度条件,垃圾生物质降解表现为持续的水解产酸过程.降雨入渗对环境因子的调控作用微弱,且在入渗水持续冲刷下,CODCr累计净溶出量增加了67.8%.15±2℃下的渗滤液回灌使微生物代谢受到抑制,渗滤液累计产生量与CODCr累计净溶出量分别下降了70.9%与88.5%;反应温度升高至35±2℃,产甲烷菌适宜的环境条件快速形成,但也造成了NH4+-N的快速积累.减少地表水入渗量,合理控制渗滤液回灌温度,并在回灌前进行脱氮处理,可显著提高垃圾填埋处理的无害化与资源化水平. 相似文献
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垃圾堆体高度对渗滤液回灌处理的影响 总被引:14,自引:2,他引:14
通过模拟试验研究了垃圾填埋场渗滤液分别回灌到不同高度的垃圾柱之后,柱内的有机污染物降解变化规律。结果表明:回灌处理法对有机物有较好的处理效果,对回灌渗滤液中有机物的去除效果随垃圾堆体高度的增加而增加;单位矿化垃圾可承受的有机污染负荷有一限值,当在一定时间内因回灌而进入垃圾堆体中的有机污染负荷超过这一限值时,渗滤液回灌处理系统将遭到破坏且不易恢复。 相似文献
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考虑垃圾体沉降的生物反应器填埋场 渗滤液回灌运移规律 总被引:3,自引:0,他引:3
生物反应器填埋场在渗滤液的回灌过程中,垃圾体会产生较大的沉降变形,这主要是由于填埋体的自重和生物降解所致。由于沉降变形会导致生物反应器填埋场中垃圾体的孔隙比减小,孔隙比的减小会影响垃圾体的渗透系数和填埋场所能容纳的渗滤液量。为了研究考虑垃圾体沉降的生物反应器填埋场渗滤液回灌运移规律,根据质量守恒原理,以修正的Darcy定理为基础,结合Elagroudy等人提出的沉降模型,建立了考虑垃圾体沉降的生物反应器填埋场渗滤液回灌的计算模型,应用该模型研究了非饱和条件下渗滤液在生物反应器填埋场中的运移规律,分析了回灌强度、垃圾体初始孔隙比、初始含水率和组成成份等参数变化对垃圾体含水率和填埋场单位表面积回灌量的影响规律。 相似文献
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渗滤液回灌不仅能处理渗滤液、节约费用和保护环境,而且加速了填埋场稳定化,增加了产气率。以上海某填埋场四期工程为计算模型,本文考虑垃圾土沉降导致的成层性,运用SEEP/W有限元软件模拟渗滤液喷洒回灌。垃圾土在自重作用下会产生较大的沉降变形,导致垃圾土的孔隙率随深度变化,残余含水量、饱和含水量及饱和渗透系数也随之变化。在数值模拟中,以VGM(van-Genuchten-Mualem)函数描述垃圾土渗透系数与基质吸力关系,以流量边界模拟填埋场顶部、底部的渗滤液回灌和导排,分析了回灌过程中渗滤液的饱和-非饱和渗流情况,进而探讨了垃圾土成层性、回灌强度和排水流量对渗滤液运移规律的影响。 相似文献
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《Water research》1998,32(5):1383-1392
The characteristics of leachate from landfills vary according to site-specific conditions. Leachates from “old” landfills are often rich in ammonia nitrogen due to the hydrolysis and fermentation of the nitrogenous fractions of biodegradable substrates, with decreases in concentration mainly attributable to leachate washout. At landfills where leachate containment, collection and recirculation is practiced to accelerate decomposition of readily biodegradable organic constituents, leachate ammonia nitrogen concentrations may accumulate to higher levels than during conventional single pass leaching, thereby creating an ultimate leachate discharge challenge. Landfill leachate treatment options include complex and often costly sequences of external physical–chemical and biological processes for removal of high-strength organics and inorganics, including nitrogen. Therefore, this paper focuses on investigations with bioreactor landfill simulations to demonstrate the potential for in situ nitrogen removal in dedicated nitrification/denitrification zones. Using leachate recirculation, associated system modifications provided separate aerobic and anoxic zones for ammonia nitrogen transformations to nitrate and nitrogen gas, respectively. Results from the three simulated optional stages of methanogenesis, nitrification and denitrification indicated that nitrogen conversion and removal was dependent on the operational stage. Both separate and combined reactor operation with internal leachate recycle provided 95% nitrogen conversion. In contrast, combined reactor operation with single pass leaching provided a conversion efficiency per cycle ranging between 30–52% for nitrification and 16–25% for denitrification, thereby indicating the efficacy of using the landfill itself for attenuation of leachate ammonia nitrogen concentrations to levels acceptable for ultimate discharge. 相似文献
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为了研究城市生活垃圾降解与填埋场沉降关系问题,研制了一台垃圾降解压缩试验仪。该仪器具有温度控制、渗滤液回灌、加压、气体和液体收集等功能。5kg垃圾试样装入直径为190mm的土样室(试样初始高度为320mm),在150kPa压力下进行一维降解压缩试验。试验检验了温度、回灌、气压等因素对降解速率的影响程度。试验结果表明,温度是影响降解的主要因素,回灌能加快产气速率,在400kPa的气压下(绝对气压),降解仍能继续进行。在温度为41℃和回灌的条件下,6个月后降解已基本完成;气相色谱/质谱分析结果表明,气体组分主要为CH4、CO2和H2O。降解完成后,总的变形量为142mm,其中主压缩变形量为65mm,次压缩变形量为77mm。提出了在填埋场沉降计算时考虑气压影响的必要性。 相似文献
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从垃圾填埋场渗滤液中氨氮的特性及其对渗滤液生化处理的影响出发,结合渗滤液回灌探讨几种适于渗滤液中氨氮的脱除技术——调节pH值、氨吹脱、同步硝化反硝化、短程硝化反硝化、厌氧氨氧化,可供类似工程借鉴。 相似文献
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A cost effective and widely applied approach for landfill leachate disposal is to discharge it to a municipal wastewater treatment plant (WWTP). The recalcitrant nature of leachate organics and the impact on the downstream WWTPs were comprehensively investigated in this study. Size fractionation by ultrafiltration (UF) and microfiltration (MF) was employed in conjunction with various analyses (TOC, COD, nitrogen species and UV254 absorbance) on raw and biologically treated landfill leachates to provide insight into biological treatability. Overall, landfill leachate organics showed bio-refractory properties. Less than half of the organic matter, measured as total organic carbon (TOC), could be removed in the biological processes examined. Size distribution data showed that the <1 thousand Daltons (kDa) fraction is dominant in most untreated and treated landfill leachates, indicating difficulties for membrane treatment. Also, most removal occurred for the <1 kDa fraction in the biological processes, while the intermediate size fractions increased slightly. This may be caused by bio-flocculation and/or partial degradation of larger molecular weight fractions. Organic nitrogen was investigated in this study as one of the first explorations for landfill leachates. Organic nitrogen in landfill leachates was more bio-refractory than other organic matter. UV quenching by landfill leachates was also investigated since it interferes with the UV disinfection at WWTPs. The combination of activated carbon and activated sludge (PACT) showed some effectiveness for reducing UV quenching, indicating that carbon adsorption is a potential method for removal of UV quenching substances. Fourier transform Infrared (FT/IR) data showed that aromatic groups are responsible for the UV quenching phenomenon. 相似文献