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1.
收集了研究区内2008年的历史数据和2018年采集的最新数据,共计278个样品,分析测试了土壤环境污染常提及的Cd、Hg、As、Pb、Cr、Cu、Ni、Zn共8类重金属元素,利用单因子指数评价法、内梅罗综合污染指数法以及土壤环境质量评估法评价研究区内西河和耒水2条河流周边的土壤环境质量类别,结合反距离空间插值法以及空间几何分析,直观地展示出研究区2008—2018年土壤重金属的时空变异特征。结果表明:采集的2期数据中除Cr外,Cd、Hg、As、Pb、Cu、Ni、Zn表层土壤重金属元素均存在点位超标的情况,说明该研究区中整体存在重金属污染;通过单因子指数评价可知,2期数据单因子指数平均值排前2位的均为Cd和Pb,Cr平均值最小,研究区内2期数据Cr超过98%点位均属于优先保护类点位,Cd、As、Pb均存在超过《土壤环境质量农用地土壤污染风险管控标准》(GB 15618-2018)管制值的点位;污染增强区主要分布于采矿及冶炼企业密度较大的西河中上游、耒水上游和耒水下游3个区。为防止今后土壤重金属污染进一步增强,建议对3个高值区采取恰当的管理措施。  相似文献   

2.
四川某金属制品厂周边土壤重金属分布特征及污染评价   总被引:1,自引:0,他引:1  
为考察四川某金属制品厂对周边土壤的重金属污染情况,对厂区周边不同方位、不同距离土壤进行取样,测定土样中Zn、Cr、Pb含量,应用单因子污染指数法和内梅罗综合指数法评价土壤环境质量,并运用Hakanson潜在生态危害指数法评估该区域土壤潜在生态风险。结果表明,厂区周边土壤Zn、Cr质量浓度平均值超过成都市土壤背景值,土样中Zn、Cr、Pb超标率分别为58.7%、94.1%、18.3%;0~10cm表层土样Zn质量浓度显著高于10~20cm亚表层土样,两土层Cr、Pb浓度没有显著差异;3种重金属在土壤中迁移能力为CrPbZn,风向不是影响土壤重金属分布的主要因素;研究区域土壤Zn、Cr处于轻度污染水平,总体处于中度污染水平;研究区3种重金属的潜在生态风险程度依次为PbCrZn,整体处于轻度综合潜在生态风险水平。  相似文献   

3.
广东省主要蔬菜产地土壤中重金属含量调查与评价   总被引:6,自引:1,他引:5  
调查了广东省20个市(县)52个主要蔬菜产地土壤重金属含量,并以<土壤环境质量标准>(GB 15618-1995)二级标准为评价标准,采用单项污染指数法和综合污染指数法对其进行评价.结果表明,156个蔬菜产地土壤样品中Cd、Hg、As和Cr的超标率分别为9.62%、3.85%、0.64%和0.64%,Pb未出现超标;有8个蔬菜产地土壤重金属处于轻污染,13个蔬菜产地土壤重金属处于警戒限,其余蔬菜产地土壤重金属均在安全范围内.蔬菜产地土壤Cd污染最为普遍和严重,其次是Hg和As,且Cd的变异系数为103.67%,预示蔬菜产地土壤可能受到Cd的点源污染.珠江三角洲地区蔬菜产地土壤重金属含量普遍高于其他地区,粤西和粤北地区个别蔬菜产地土壤重金属超标.  相似文献   

4.
为分析琼北火山岩地区土壤中重金属(As、Cd、Cr、Pb、Ni、Hg)的累积特征,采集旱地和水田的土壤表层样品,并对样品理化性质及重金属含量进行了分析,采用单因子污染指数法和内梅罗综合污染指数法对重金属污染状况进行了评价。结果表明,研究区旱地与水田土壤均呈强酸性-酸性,旱地土壤阳离子交换量(CEC)(4.66 cmol/kg)略大于水田土壤CEC(3.42 cmol/kg),表明旱地土壤保持养分的能力优于水田土壤。与海南土壤背景值比较,研究区旱地和水田土壤中Cd、Cr、Pb和Ni 4种重金属均有不同程度的累积,其中Cd累积程度较重。研究区旱地和水田土壤中Cr与Ni均具有较高的正相关关系,说明旱地和水田土壤中Cr与Ni可能同源,且受基性火山岩地质背景的影响较大。内梅罗综合污染指数评价结果表明,研究区旱地土壤重金属污染明显高于水田土壤,水田土壤重金属为轻度污染,而旱地土壤重金属已达到中度污染,尤其是Cr和Ni污染比较严重,应引起重视。  相似文献   

5.
典型农业活动区土壤重金属污染特征及生态风险评价   总被引:7,自引:0,他引:7  
联合野外采样和室内分析,以典型农田土壤为研究对象,分析土壤中重金属Cr、Ni、Cu、Zn、Cd、Pb、As和Hg的含量及污染特征,并采用单因子污染指数法、内梅罗污染指数法及潜在生态危害指数法,对农田土壤进行生态风险评价,同时利用主成分因子分析法,提取出3主因子,分析土壤重金属可能来源。结果表明,研究区农田土壤各重金属含量均高于背景值,表层污染程度高于底层;各重金属单因子污染指数对应污染等级均为清洁,内梅罗污染指数为0.46,污染等级为安全。潜在生态风险评估结果显示,研究区土壤重金属污染的潜在生态风险危害程度为中等,各重金属的潜在生态危害程度依次为CdHgAsCuPbNiCrZn。主成分因子分析显示,研究区土壤中Hg、As和Cr主要由工业污染源贡献,土壤中Cd、Pb的污染主要来源于不合理的农业生产活动和居民生活,Ni、Zn和Cu与自然成土过程密切相关。综合评价表明,尽管研究区农田土壤目前重金属污染情况较轻,未达到警戒水平,但由于城市化的发展及长期现代化农业耕作活动造成农田土壤重金属的富集,因此,增强农田土壤安全性生产管理、严控土壤污染源与推行标准农业生产是十分必要的。  相似文献   

6.
以盐城海岸带为研究区,分别采用地质累积指数法、内梅罗指数法和潜在生态危害指数法对土壤重金属污染进行风险评价,分析不同方法在评价同一研究区时结果的差异性。结果表明,研究区Cr、Ni、Zn、Cd质量浓度平均值超过盐城海岸带环境背景值。地质累积指数法显示研究区土壤重金属在中度污染到强污染;内梅罗指数法显示研究区土壤重金属为重度污染;潜在生态危害指数法显示研究区土壤重金属处于中度潜在生态危害程度。3种方法评价结果的严重程度为:内梅罗指数法地质累积指数法潜在生态危害指数法。3种评价方法均有一定缺陷与局限性,相对于单一方法的污染评价,采用多种方法评价土壤重金属污染可使评价结果更加客观。  相似文献   

7.
于贵阳花溪区蔬菜种植基地及零星菜地采集叶菜类、茎菜类和果菜类样品及对应土壤样品,测定土壤与蔬菜样品中Zn、Cd、Pb和Cu含量,分析土壤理化性质、土壤重金属全量、有效态含量与蔬菜中重金属含量之间的关系,通过污染指数和暴露风险健康评估指数分析城郊蔬菜中重金属污染状况以及摄入人群的健康风险。结果表明:部分菜地土壤样品Zn、Cu含量超出农用地土壤污染风险筛选值,超标率分别为8.82%、11.76%;蔬菜中重金属含量主要取决于土壤重金属有效态含量;研究区蔬菜均处于清洁水平,但有8.82%的蔬菜样品Pb处于Ⅱ级警戒值,且均为叶菜;Pb是叶菜类暴露健康风险的主要元素,而Cu是茎菜类与果菜类暴露健康风险的重要元素;蔬菜重金属对儿童和成人的危害指数均小于1.0,表明食用该地区的蔬菜不会对人体健康产生不良影响。  相似文献   

8.
采用实地采样与室内测试方法对宝鸡市长青镇冶炼厂周边居住区土壤重金属(Pb、Zn、Cd、Cr)的含量进行了测定分析,利用地质累积指数法和改进的综合污染指数法对其土壤环境质量进行了评价,应用美国环境保护署(USEPA)推荐的健康风险评价模型对研究区土壤重金属在3种暴露途径下的健康风险做出了初步评价,并用相关性分析法和聚类分析法对污染源进行了解析。结果表明,研究区域13个采样点表层土壤中重金属元素Pb、Zn、Cd和Cr的质量浓度分别为52.43~96.42、82.54~151.32、0.065~0.309、59.26~104.13mg/kg,平均值分别为67.55、107.20、0.120、75.23mg/kg,其值均高于陕西和中国的背景值,说明土壤受到不同程度污染;地质累积指数法进一步证实研究区域土壤已经受到4种重金属不同程度的污染,且处于中等污染及以内;而4种重金属的综合污染评价显示,除4号村庄、7号村庄处于中等污染外,其余均处于轻污染至中污染;研究区域中,4种重金属在3种暴露途径下对儿童的非致癌健康风险均大于成人,但对成人和儿童均不存在显著的非致癌健康影响和非致癌健康总风险,其风险顺序是经口摄入经皮肤接触经呼吸吸入;其次,Cd对成人和儿童经呼吸暴露途径均不存在致癌健康风险,而Cr对成人和儿童经呼吸暴露所致的致癌健康风险处于不可接受状态;另外,源解析结果显示,Pb和Zn具有相同的污染源,而Cd和Cr具有不同的污染源。  相似文献   

9.
矿业活动对土壤系统良性运转带来较大的环境负荷,矿区周边土壤重金属污染风险评估是土壤污染防治和资源可持续开发的关键。在应用单因子污染指数法、潜在生态风险指数法、风险评价编码法(RAC),并结合空间分析和冗余分析手段的基础上,对新疆某矿冶区周边土壤重金属生物有效性和生态风险进行了系统研究。结果表明:研究区土壤As、Cu、Mn和Cd超标率分别为88%、38%、49%和24%;土壤Mn、Zn、As和Cd弱酸可溶态高值区主要集中在尾砂库和收砷房的附近区域。单因子污染指数评价揭示As和Cu污染累积较为严重。潜在生态风险评价显示,As、Cd和Cu生态风险较高,Mn为低生态风险。风险编码法(RAC)评价结果进一步揭示Mn和Cd具有显著的土壤迁移风险。冗余分析结果显示,空间异质性是影响土壤重金属弱酸可溶态含量变异的主要因素。土壤pH和重金属弱酸可溶态是影响潜在生态风险指数(RI)的2个重要因素。综合风险评价手段与多尺度分析方法的联合应用有助于提高区域风险评价的准确性。  相似文献   

10.
雷州半岛土壤重金属分布特征及其污染评价   总被引:5,自引:1,他引:5  
在雷州半岛采集了106个土壤表层样品,分析了其中8种重金属元素(Cu、Pb、Zn、Cr、Ni、Cd、Hg和As)的全量.结果表明,雷州半岛土壤重金属污染由高到低排序为Ni>Cr>Hg>Cu>Zn>Cd>As>Pb,Zn、Cd、As和Pb质量浓度均没有超标,Hg和Cu质量浓度超标率亦不高,但Ni和Cr平均质量浓度达49.81、87.13 mg/kg,高于国内外其他对照区域,超标率分别为25.47%和24.53%;重金属元素在雷州半岛各土壤利用类型中分布规律不明显,按4种主要土壤利用类型受重金属污染程度大小排序为甘蔗地>果园土>水田>菜地;雷州半岛土壤综合污染指数总平均为0.970,土壤总体上尚清洁,重金属污染处于警戒水平;雷州半岛各区域中,徐闻、雷州两地土壤重金属质量浓度明显高于其他地区,其主要原因是徐闻、雷州两地成土母质主要为玄武岩,造成土壤Cr、Ni及其他重金属背景值较高.  相似文献   

11.
煤矿复垦区土壤重金属分布特征与质量评价   总被引:2,自引:0,他引:2  
为保证煤矿复垦区种植农作物的充填复垦土壤的生态安全,以淮南矿区煤矸石充填复垦地为研究对象,通过对研究区内Cd、Cr、Ni、Pb、Cu、Zn和Hg 7种重金属不同深度含量分析,总结其纵向分布特征,并将研究区土壤重金属含量与淮南市土壤背景值、《土壤环境质量标准》(GB 15618-1995)作比较,分析这7种重金属的污染程度.结果表明,这7种重金属都有不同程度的污染,其中土壤受Cd污染最严重,土壤中重金属垂直方向上无确定分布规律.总体而言,土壤重金属潜在生态风险属于强生态危害.从垂直方向来看,重金属潜在生态风险指数(RD随着深度的增加出现先下降后升高的趋势,其中40~60 cm深度的RI最大.重金属生态危害程度依次为Cd> Hg> Ni> Cu> Cr> Pb> Zn,其中Cd为矿区土壤中最主要的重金属污染生态风险因子.  相似文献   

12.
Areas contaminated with heavy metals can pose major risks to human health and ecological environments. The aims of this study are to assess human health risk and pollution index for heavy metals in agricultural soils irrigated by effluents of stabilization ponds in Birjand, Iran. The results revealed that the levels of Cr, Mn, Zn, Fe, Cu, Cd, and Pb were in range of 70.3–149.65, 355–570, 31.15–98.45, 23,925–29,140, 22.75–25.95, 0.17–6.51, and 8.5–23.5 mg/kg in topsoils, respectively. Total hazard index values from heavy metals through three exposure routes for adults and children were 9.13E−01 and 1.10, respectively, indicating that there was non-carcinogenic risk for children. The total risk of carcinogenic metals (Cr, Cd, and Pb) through the three exposure routes for adults and children was 1.06E−04 and 9.76E−04, respectively, which indicates that the metals in the soil will not induce carcinogenic risks to these age groups. Pollution levels of heavy metals in soil samples including enrichment factor (EF), contamination factor (CF), pollution load index (PLI), and geo-accumulation index (Igeo) showed heavy metal contamination of agricultural soils. The results of the present study provide basic information about heavy metal contamination control and human health risk assessment management in the study area.  相似文献   

13.
Urban soil is an important component of urban ecosystems. This study focuses on heavy metal contamination in soils of Wien (Austria) and results are compared to those for a few large European cities. We analysed the elemental contents of 96 samples of topsoil from urban, suburban and rural areas in Wien along a dynamic (floodplain forest) and a stable (oak–hornbeam forest) urbanization gradient. The following elements were quantified using ICP-OES technique: Al, As, Ba, Ca, Cd, Co, Cr, Cu, Fe, K, Mg, Mn, Pb, P, S and Zn. For heavy metals PI (pollution index) values were used to assess the level of pollution. The PI values indicated high level of pollution by Pb in the suburban and rural area of stable gradient and in the urban area of dynamic gradient; moderate level of pollution was indicated for Cd in the urban area of stable gradient. The level of pollution was moderate for Co in the suburban and rural area of the stable gradient, and for Cu in suburban area of stable gradient, and urban area of dynamic gradient. The pollution level of Zn was moderate in all areas. Urban soils, especially in urban parks and green areas may have a direct influence on human health. Thus, the elemental analysis of soil samples is one of the best ways to study the effects of urbanization. Our results indicated that the heavy metal contamination was higher in Wien than in a few large European cities.  相似文献   

14.
某矿区土壤和地下水重金属污染调查与评价   总被引:3,自引:0,他引:3  
为了解湘南某矿区土壤和地下水重金属污染状况,对该矿区东河流域附近重金属污染源进行了调查,同时,对地下水和土壤样品进行了采样分析,结果表明:(1)该矿区东河流域附近的主要污染源有18个,其中有色金属选厂、尾矿库、采矿场和冶炼厂是排放重金属较多的污染源;(2)20个采样点中土壤重金属Pb、Cd、Zn、As和Hg大部分超过国家土壤环境质量标准(GB15618-1995),综合污染指数P综〉1,该矿区主要的重金属污染元素为Cd、As和Hg,且土壤中Cd、Zn和As的含量两两之间存在着极显著的正线性相关关系;(3)重金属元素在土壤中的纵向迁移不明显,该矿区附近20个采样点的地下水并未受到污染,综合污染指数P综〈1。20个采样点地下水Pb、Cd、Zn、As、Hg浓度均能达到地下水质量标准(GB/T14848.9)中的Ⅲ类标准。  相似文献   

15.

Heavy metals are considered toxic to humans and ecosystems. In the present study, heavy metal concentration in soil was investigated using the single pollution index (PIi), the integrated Nemerow pollution index (PIN), and the geoaccumulation index (Igeo) to determine metal accumulation and its pollution status at the abandoned site of the Capital Iron and Steel Factory in Beijing and its surrounding area. Multivariate statistical (principal component analysis and correlation analysis), geostatistical analysis (ArcGIS tool), combined with stable Pb isotopic ratios, were applied to explore the characteristics of heavy metal pollution and the possible sources of pollutants. The results indicated that heavy metal elements show different degrees of accumulation in the study area, the observed trend of the enrichment factors, and the geoaccumulation index was Hg > Cd > Zn > Cr > Pb > Cu ≈ As > Ni. Hg, Cd, Zn, and Cr were the dominant elements that influenced soil quality in the study area. The Nemerow index method indicated that all of the heavy metals caused serious pollution except Ni. Multivariate statistical analysis indicated that Cd, Zn, Cu, and Pb show obvious correlation and have higher loads on the same principal component, suggesting that they had the same sources, which are related to industrial activities and vehicle emissions. The spatial distribution maps based on ordinary kriging showed that high concentrations of heavy metals were located in the local factory area and in the southeast-northwest part of the study region, corresponding with the predominant wind directions. Analyses of lead isotopes confirmed that Pb in the study soils is predominantly derived from three Pb sources: dust generated during steel production, coal combustion, and the natural background. Moreover, the ternary mixture model based on lead isotope analysis indicates that lead in the study soils originates mainly from anthropogenic sources, which contribute much more than the natural sources. Our study could not only reveal the overall situation of heavy metal contamination, but also identify the specific pollution sources.

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16.
According to the European Thematic Strategy for Soil Protection, the characterization of the content and source of heavy metals in soils are necessary to establish quality standards on a regional level that allow the detection of sampling sites affected by pollution. In relation to this, the surface horizons of 54 agricultural soils under vegetable crops in the Alicante province (Spain), a representative area of the European Mediterranean region, were sampled to determine the content of Cd, Co, Cr, Cu, Fe, Mn, Ni, Pb and Zn. Analytical determinations were performed by atomic absorption spectroscopy after microwave sample digestion in acid solution. Results indicated that heavy metal levels were similar to those reported by authors working on agricultural soils from other parts of the Mediterranean region, with the exception of Cu and Pb in some samples. Multivariate analysis (principal component analysis and cluster analysis) was performed to identify a common source for heavy metals. Moreover, soil properties were determined in order to characterize agricultural soils and to analyze relationships between heavy metal contents and soil properties. The content of Co, Cr, Fe, Mn, Ni and Zn were associated with parent rocks and corresponded to the first principal component called the lithogenic component. A significant correlation was found between lithogenic metals and some soil properties such as soil organic matter, clay content, and carbonates, indicating an important interaction among them. On the other hand, elements such as Cd, Cu and Pb were related to anthropic activities and comprised the second (Cu and Pb) and third principal components (Cd), designated the anthropogenic components. Generally, Cd, Cu and Pb showed a lower correlation with soil properties due to the fact that they remain in available forms in these agricultural soils. Taking into account these results and other achieved in other parts of the European Mediterranean region, it can be concluded that soil quality standards are highly needed to declare soils affected by human induced pollution. This is particularly relevant for anthropogenic metals (Cd, Cu and Pb, and in some areas also Zn). Further research in other agricultural areas of the region would improve the basis for proposing such soil quality standards.  相似文献   

17.
Soils enriched with heavy metals from vehicular emission present a significant exposure route of heavy metals to individuals using unpaved roads. This study assessed the extent of Cd, Cr, Co, Cu, Ni, Pb and Zn contamination of soils along unpaved roads in Cameroon, and the health risks presented by incidental ingestion and dermal contact with the soils using metal contamination factor (CF) pollution load index, hazard quotients (HQ) and chronic hazard index (CHI). CF values obtained (0.9–12.2) indicate moderate to high contamination levels. HQ values for Cr, Cd and Pb exceeded the reference doses. Moderate health hazard exists for road users in the areas with intense anthropogenic activities and high average daily traffic (ADT) volume according to CHI values (1–4) obtained. The economy and quality of life in cities with unpaved roads could be threatened by health challenges resulting from long-term exposure to heavy metal derived from high ADT volumes.  相似文献   

18.
Heavy metals in the surface soils from lands of six different use types in one of the world’s most densely populated regions, which is also a major global manufacturing base, were analyzed to assess the impact of urbanization and industrialization on soil pollution. A total of 227 surface soil samples were collected and analyzed for major heavy metals (As, Cd, Co, Cr, Cu, Fe, Hg, Mn, Ni, Pb, and Zn) by using microwave-assisted acid digestion and inductively coupled plasma–mass spectrometry (ICP-MS). Multivariate analysis combined with enrichment factors showed that surface soils from the region (>7.2?×?104 km2) had mean Cd, Cu, Zn, and As concentrations that were over two times higher than the background values, with Cd, Cu, and Zn clearly contributed by anthropogenic sources. Soil pollution by Pb was more widespread than the other heavy metals, which was contributed mostly by anthropogenic sources. The results also indicate that Mn, Co, Fe, Cr, and Ni in the surface soils were primarily derived from lithogenic sources, while Hg and As contents in the surface soils were controlled by both natural and anthropogenic sources. The pollution level and potential ecological risk of the surface soils both decreased in the order of: urban areas?>?waste disposal/treatment sites?~?industrial areas?>?agricultural lands?~?forest lands?>?water source protection areas. These results indicate the significant need for the development of pollution prevention and reduction strategies to reduce heavy metal pollution for regions undergoing fast industrialization and urbanization.  相似文献   

19.

The effect of industrial activities on trace metals in farmland of rapidly industrializing regions in developing countries has increasingly been a concern to the public. Here, soils were collected from 13 greenhouse vegetable production (GVP) farms or bases near industrial areas in the Yangtze River Delta of China to investigate the occurrence, speciation, and risks of Cr, Cu, Zn, Cd, Ni, and Pb in GVP soil. The results revealed that the main metal elements causing GVP soil pollution were Cd, Zn, Ni, and Cu, of which contamination levels were generally unpolluted to moderately polluted. Zinc pollution was mainly attributed to heavy fertilization, while Cd, Ni, and Cu pollution may be greatly ascribed to industrial effluents and coal combustion. Metal speciation studies showed that most of Cr, Ni, Cu, and Zn was present in residual fraction while more than half of Cd and Pb was present in non-residual fractions. Additionally, pollution of Cd, Cu, Ni, and Zn in GVP soil increased their corresponding mobile fractions. Risk assessment using potential ecological risk index and risk assessment code showed that Cd was the major risk contributor. Specifically, Cd generally posed moderate or considerable ecological risk as well as displayed medium or high mobility risk in GVP soil. Thus, great attention should be paid to the contribution of both industrial discharges and intensive farming to soil pollution by trace metals, especially Cd, because of its high mobility risk.

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