共查询到19条相似文献，搜索用时 140 毫秒
1.
为了解垃圾填埋场周边地下水环境污染状况,以长沙市固体废弃物处理场周边土壤、地下水及下游水库水质为研究对象,对研究区进行采样分析,采用单因子污染指数法和内梅罗污染综合指数法对该垃圾填埋场周边环境重金属含量特征进行分析与风险评价。结果表明：As、Cr（Ⅵ）、Ni、Pb、Zn、Cu重金属是填埋场周边环境中的主要污染物,区域采样点及下游水库中重金属含量均值低于地下水质量标准Ⅲ类,填埋场区污染状况良好;Cr（Ⅵ）含量在ZK1与R1样品中均高于地下水质量标准Ⅲ类,是填埋场周边地下水的主要风险污染物;ZK1~ZK4中土壤重金属元素以Pb、Cr（Ⅵ）富集为主,其达中度污染程度,应引起重视。 相似文献
2.
为了深入了解垃圾渗滤液对浅层地下水污染的机理,揭示不同龄期垃圾渗滤液在浅层地下水中多组分运移规律,文章以阜新市垃圾填埋场为研究对象,通过室内土柱对比实验,研究了不同龄期垃圾渗滤液在浅层地下水中多组分运移的机理和规律。结果表明不同龄期垃圾渗滤液在入渗过程中都会引起地下水不同程度的污染,且新鲜垃圾渗滤液较老龄垃圾渗滤液更易污染地下水,其污染机理主要为吸附、解析、溶解、沉淀和离子交换等水岩作用。研究结果为今后垃圾填埋场的治理和地下水的修复提供理论依据。 相似文献
3.
4.
5.
垃圾填埋是目前处理城市生活垃圾普遍使用的方式,由此产生的垃圾渗滤液成为主要的地下水污染源.本文以上海市某生活垃圾填埋场作为研究对象,研究垃圾填埋对地下水的影响.通过监测该场地垃圾填埋前后2年内场区及周边地下水水质的变化情况,以垃圾填埋前调查区的地下水样品分析结果为本底值,采用本底法对地下水水质进行评价来判定地下水是否受到垃圾渗滤液的影响.评价结果显示,对于本研究的水质动态监测阶段,调查区内的浅层地下水水质暂未受到垃圾渗滤液的影响,个别监测井水质发生较大变化是由于填埋场施工建设过程中,破坏了监测井井盖及挖穿了井边含水层顶层.随着整个垃圾填埋场运行时间的延长,防渗漏措施的有效性以及垃圾渗滤液对周边地下水的影响还需要进一步研究. 相似文献
6.
7.
依据实际调查数据,采用单因子污染指数分析法确定了生活垃圾填埋场地下水中主要污染物、污染程度和污染范围,并进行了土壤和地下水污染耦合性分析,研究结果表明：该生活垃圾填埋场地下水污染物主要为氨氮、总氮、高锰酸盐、锰、挥发酚和氟化物,其污染指数最大值分别为1 407.24、745.00、137.12、97.50、3.60和1.68,污染区总面积0.168 km2;填埋场下游沟谷纵向上,总氮、锰两项指标在土壤中的含量与地下水中浓度变化趋势一致;其污染途径主要为库区防渗层破损,渗滤液垂向沿基岩风化裂隙进入地下含水层,以连续渗漏的方式不断污染地下水,污染物在地下水径流作用下向拦挡坝下游不断迁移。 相似文献
8.
对于入河排污口设置,通常需对周边地下水、地表水水质、水量、水生态及第三者权益分析,而北方小型河流易发生断流,时常着重于分析对其地下水的影响.以农安县某垃圾填埋场为例,结合水文地质勘察结果,运用Visual MODFLOW软件,模拟预测该垃圾填埋场渗滤液中主要特征污染物COD及氨氮在通过富滨分干排放时对周边地下水污染物的迁移特征,分析对其周边地下水的影响.最终模拟预测结果显示,渗滤液对地下水的影响主要取决于污染因子的浓度、地下水径流的方向、水力梯度、含水层的渗透性和富水性等,其模拟因子COD的最大影响距离均不超过450 m,氨氮的最大影响距离均不超过500 m. 相似文献
9.
垃圾填埋技术是我国应用较广的垃圾处理技术,以某简易垃圾填埋场为例,查明研究区水文地质条件,通过计算得到垃圾渗漏液产生量及相关污染物浓度,选取合理预测参数,运用visual-modflow软件建立研究区地下水流场及地下水溶质运移模型,对研究区地下水相关污染因子进行预测,根据相关预测模型和参数,结果发现:该简易垃圾填埋场中氨氮污染距离可达536.4 m;高锰酸钾指数污染距离可达480.36 m,说明该简易垃圾填埋场渗滤液的泄漏已对下游一定区域的地下水环境造成了污染。 相似文献
10.
11.
This paper studies a landfill where there are three faults running through.As serious pollution has occurred to the geological environment,the landfill is to be closed up and renovated.The paper aims to explore the role of fracture structure in leachate pollution at the landfill.The research was carried out in several stages.First,mathematical models of the pre-renovation landfill with three faults running through and the landfill after renovation were established.And then,the boundary conditions and parameters of the two mathematical models were determined.The groundwater level of the landfills was simulated in order to modify the two mathematical models.As a result,a feasible mathematical model was achieved.Based on this model,a comparison was made of the COD concentration variations in the inside leachate and outside leachate between the two landfills. Accordingly,the impacts of the fracture structure on the pollution of leachate at the landfills could be identified.The study results show that while faults contribute to the migration of leachate,they also serve as a confluence of leachate,thus further deteriorating the environment.The COD concentrations of the inside leachate and the outside leacbate of the pre-renovation landfill are respectively 800 mg/L and 220 mg/L higher than those of the post.renovation landfill.Therefore,measures must be taken to handle the leachate seepage in areas where there are faults as well as the neighboring areas so as to get the environmental pollution under control. 相似文献
12.
This paper studies a landfill where there are three faults running through. As serious pollution has occurred to the geological environment, the landfill is to be closed up and renovated. The paper aims to explore the role of fracture structure in leachate pollution at the landfill. The research was carried out in several stages. First, mathematical models of the pre-renovation landfill with three faults running through and the landfill after renovation were established. And then, the boundary conditions and parameters of the two mathematical models were determined. The groundwater level of the landfills was simulated in order to modify the two mathematical models. As a result, a feasible mathematical model was achieved. Based on this model, a comparison was made of the COD concentration variations in the inside leachate and outside leachate between the two landfills. Accordingly, the impacts of the fracture structure on the pollution of leachate at the landfills could be identified. The study results show that while faults contribute to the migration of ieachate, they also serve as a confluence of leachate, thus further deteriorating the environment. The COD concentrations of the inside leachate and the outside leachate of the pre-renovation landfill are respectively 800 mg/L and 220 mg/L higher than those of the post-renovation landfill. Therefore, measures must be taken to handle the ieachate seepage in areas where there are faults as well as the neighboring areas so as to get the environmental pollution under control. 相似文献
13.
《Applied Geochemistry》2001,16(7-8):659-718
The literature has been critically reviewed in order to assess the attenuation processes governing contaminants in leachate affected aquifers. Attenuation here refers to dilution, sorption, ion exchange, precipitation, redox reactions and degradation processes. With respect to contaminants, focus is on dissolved organic matter, xenobiotic organic compounds, inorganic macrocomponents as anions and cations, and heavy metals. Laboratory as well as field investigations are included. This review is an up-date of an earlier comprehensive review. The review shows that most leachate contamination plumes are relatively narrow and do not in terms of width exceed the width of the landfill. The concept of redox zones being present in the plume has been confirmed by the reported composition of the leachate contaminated groundwater at several landfills and constitutes an important framework for understanding the behavior of the contaminants in the plume as the leachate migrates away from the landfill. Diverse microbial communities have been identified in leachate plumes and are believed to be responsible for the redox processes. Dissolved organic C in the leachate, although it appears to be only slowly degradable when the volatile organic acids are gone, apparently acts as substrate for the microbial redox processes. Several xenobiotic organic compounds have been found to be degradable in leachate contaminated groundwater, but degradation rates under anaerobic redox conditions have only been determined in a few cases. Apparently, observations in actual plumes indicate more extensive degradation than has been documented in the laboratory. The behavior of cations in leachate plumes is strongly influenced by exchange with the sediment, although the sediment often is very coarse and sandy. Ammonium seems to be subject to anaerobic oxidation, but the mechanisms are not yet understood. Heavy metals do not seem to constitute a significant pollution problem at landfills, partly because the heavy metal concentrations in the leachate often are low, and partly because of strong attenuation by sorption and precipitation. Although complexation of heavy metals with dissolved organic matter is significant, the heavy metals are in most cases still strongly attenuated in leachate-polluted aquifers. The information available on attenuation processes has increased dramatically during the last 15 a, but the number of well-documented full scale leachate plumes are still few and primarily from sandy aquifers. Thus, the diversity of attenuation processes in leachate plumes is probably not yet fully understood. Apparently, the attenuation processes in leachate plumes may for many contaminants provide significant natural remediation, limiting the effects of the leachate on the groundwater to an area usually not exceeding 1000 m from the landfill. 相似文献
14.
E. A. Rahim Bahaa-eldin I. Yusoff S. Abdul Rahim W. Y. Wan Zuhairi M. R. Abdul Ghani 《Environmental Earth Sciences》2011,63(5):1043-1055
This paper aims at determining of inorganic leachate contamination for a capped unsanitary landfill in the absence of hydrogeological data. The 2D geoelectrical resistivity imaging, soil physicochemical characterization, and surface water analysis were used to determine contamination load and extent of selective heavy metal contamination underneath the landfill. The positions of the contaminated subsoil and groundwater were successfully delineated in terms of low resistivity leachate plumes of <10 Ωm. Leachate migration towards the reach of Kelang River could be clearly identified from the resistivity results and elevated concentrations of Fe in the river downslope toe of the site. Concentration of Fe, Mn, Ca, Na, K, Mg, Cu, Cr, Co, Ni, Zn, and Pb was measured for the subsoil samples collected at the downslope (BKD), upslope (BKU), and the soil-waste interface (BKI), of the landfill. The concentration levels obtained for most of the analyzed heavy metals significantly exceed the normal range in typical municipal solid waste landfill sites. The measured heavy metal contamination load in the subsoil is in the following order Fe ? Mn > Zn > Pb > Cr > Cu. Taking into consideration poor physical and chemical characteristics of the local soil, these metals first seem to be attenuated naturally at near surface then remobilize unavoidably due to the soil acidic environment (pH 4.2-6.18) which in turn, may allow an easy washing of these metals in contact with the shallow groundwater table during the periodic fluctuation of the Kelang River. These heavy metals are believed to have originated from hazardous industrial waste that might have been illegally dumped at the site. 相似文献
15.
以江汉平原典型场区周边农田土壤为研究对象,分析了土壤重金属元素Cd、Pb、As、Hg的总量和赋存形态特征,选用修正单项污染指数法、潜在生态风险指数法、风险评估编码法(RAC)和次生相与原生相比值法(RSP)四种评价方法开展了土壤重金属的污染风险评价,并对评价结果进行了对比讨论。分析结果表明:（1）基于总量的两种方法对比,潜在生态风险指数法优于修正单项污染指数法。（2）基于形态的两种方法对比,RAC法的评价结果比RSP法更为合理。（3）基于总量和形态方法对比,潜在生态风险指数法和RAC法各有其优缺点,潜在生态风险指数法能直观反映重金属在土壤中的富集信息和环境危害性,而RAC法则可以利用形态来阐明重金属在土壤环境中的行为特性和生态活性。因此,在进行土壤重金属污染风险评价时,综合考虑重金属种类、累积程度、生物毒性和生物可利用性等参数指标,才能更加科学准确地评估重金属在土壤中的环境风险。综合上述评价结果,江汉平原典型场区周边农田土壤重金属元素Pb、As污染程度较低,对周边环境无影响;重金属元素Hg累积程度不高,但由于其具有较高的生物毒性,对周边环境存在潜在威胁;重金属元素Cd是研究区最主要的污染因子,对周边环境影响大,亟需采取相应措施减轻Cd带来的风险。 相似文献
16.
Testing the ability of bentonite-amended natural zeolite (clinoptinolite) to remove heavy metals from liquid waste 总被引：2，自引：0，他引：2
The design of environmentally sound liquid waste containment structures has become a crucial task in engineering applications
due to ever increasing groundwater contamination from such sites. Construction of such structures usually requires a bottom
liner of low hydraulic conductivity as part of the design. In order to reduce the hazards associated with liquid wastes including
landfill leachate, bentonite-amended natural zeolite is proposed as an alternative to conventional earthen liners. Among many
contaminants associated with liquid wastes, heavy metals are the most dangerous ones. This paper deals with determining the
ability of natural zeolite to remove heavy metals from aqueous waste. For this purpose, crushed natural zeolite (clinoptinolite)
is amended with commercial powdered bentonite to yield a soil mixture low in permeability and high in ion-exchange capacity.
Leachate from a conventional landfill is used as the percolation fluid. Concentrations of certain heavy metals in the effluent
fluid percolated through the bentonite-zeolite mixture are compared with that of initial leachate. The conclusion is reached
that certain metals are efficiently removed from the influent solution by the soil matrix whereas some ions do not show significant
reduction in concentration. This is attributed to high hydraulic conductivity of the bentonite-zeolite mixture. 相似文献
17.
采用土柱淋滤试验研究了不同填埋年限的垃圾渗滤液DOM在土壤中垂直迁移及其对土壤重金属Pb淋滤溶出的影响。结果表明,不同填埋年限(0.4~5.12 a)的垃圾渗滤液DOM在土壤中垂直向下的迁移速率存在差异,填埋时间短的垃圾渗滤液DOM在土壤中迁移性较强。与对照相比(不加渗滤液DOM),垃圾渗滤液处理对红壤中土壤重金属Pb的累积解吸率高74.25%;在潮土上高-38.79%,且垃圾填埋年限中期的渗滤液DOM对土壤重金属的溶出影响更显著,说明垃圾渗滤液DOM进入土壤环境对重金属的迁移有促进作用。 相似文献
18.
Magnetic properties and heavy metal content of landfill leachate sludge samples from two municipal solid waste disposal sites
near Bandung, West Java, Indonesia, and their correlation with heavy metals are studied in the present work. Leachate was
found to be sufficiently magnetic with mass-specific magnetic susceptibility that varies from 64.8 to 349.0 × 10−8 m3 kg−1. It is, however, less magnetic than the soils around the landfill sites. The magnetic minerals are predominantly pseudo-single
domain and multidomain magnetite. Leachate samples from the older but inactive disposal site, Jelekong, are found to be more
magnetic than that from Sarimukti, the younger and active site. The enhancement of leachate due to the soil-derived ferrimagnetic
particles is possibly the same for both Sarimukti and Jelekong. The fact that strong correlation between magnetic parameters
and heavy metals is observed in Jelekong but is absent in Sarimukti suggests that the use of magnetic measurement as a proxy
measurement for heavy metal content in leachate is plausible provided that the magnetic susceptibility exceeds certain threshold
value. Moreover, the accumulation of magnetic minerals and heavy metals in leachate might depend on the activity and the age
of landfill site. 相似文献
19.
垃圾填埋场渗滤液中的重金属与土体发生物理化学反应,可能导致土体微观结构的改变,重金属等有毒物质得以扩散、运移,威胁人体健康和周边环境。为探究重金属污染对黄土宏观持水性及微观结构的影响,采用轴平移技术测得铅污染黄土的土-水特征曲线。通过扫描电子显微镜（SEM）、压汞（MIP）、X射线衍射（XRD）和Zeta电位试验,阐明细观结构变化特征。结果表明：铅污染黄土的进气值随铅离子浓度的增加而减小,当铅污染浓度由0 mg/kg增加至2 000 mg/kg时,进气值从19.18 kPa下降至12.12 kPa;铅污染导致持水性能降低,渗透系数随铅离子浓度的增加而增加,饱和渗透系数从7.92×10–8 m/s增加到3.73×10–7 m/s;铅污染引起的物理化学反应及Zeta电位的降低导致絮凝结构形成,小孔隙占比减小,中孔隙占比增加;铅污染引起的微观结构演化与宏观持水性和渗透性具有良好的对应关系。该研究结果可为重金属污染场地非饱和渗流及溶质运移等问题的研究提供重要参数。 相似文献