保山市主要蔬菜生产地土壤重金属含量分析及评价

对保山市几个蔬菜生产集中地的土壤进行了调查、采样及样品分析,分析元素为重金属镉、汞、砷、铅、铬。结果表明,保山市几个主要蔬菜生产地土壤重金属根据单项和综合污染指数法判断都属安全,土壤本身对蔬菜生产不会产生污染危害。     

萍乡市农用土壤重金属含量及其分布特征分析

以江西省萍乡地区农用土壤为研究对象,分析研究了萍乡市农用土壤中重金属的含量、分布特征。结果表明:萍乡地区农用土壤中重金属的平均含量均未超过国家土壤环境质量二级标准,但其中锌、镍、铬、铜、镉、砷、铅、锰、汞的含量均超过了江西省土壤重金属相应元素的背景值。从空间分布来看,在全市5个县区布置的29个测点中,有14个测点的重金属含量超标;其中上栗县有8个测点超标,明显多于其他县区,出现了不同的污染特征。     

四川省马边磷矿区水环境中典型重金属污染分析

马边磷矿区磷矿资源丰富,区内磷矿开采企业较多。在开采的过程中难免会对当地的河水造成一定的影响。为了进一步了解马边磷矿区的环境影响问题,本文通过对磷矿区采集的水体样品和同一地点的水系沉积物样品进行分析测试,共检测了Cd、As、Cu、Cr、Pb、Zn六种重金属元素的含量,采用潜在生态危害指数法对沉积物中的重金属污染程度进行了综合评价。结果如下:马边磷矿区河水中的重金属元素的浓度较低,6种重金属元素含量均低于国家标准(GB3838-2002)。水系沉积物中的重金属元素含量较高,其中:Cd、Pb、Zn分别为2. 06mg/kg、182. 39mg/kg、479. 13 mg/kg。与四川省土壤元素背景值相比:Cd元素超标25. 7倍,Pb元素超标5. 9倍,Zn元素超标5. 5倍,其余元素未超标。与马边地区1∶20万区域水系沉积物背景值相比:Cd元素超标3. 12倍,Pb元素超标3. 3倍,Zn元素超标2. 5倍,As元素超标1. 6倍,Cu、Cr元素含量在背景值以内。与“中国土壤元素背景值”相比:Cd元素超标29. 4倍,Pb元素超标7. 7倍,Zn元素超标7. 1倍。潜在生态危害指数法评价结果表明:Cd的生态危害指数最大,其次为Pb和As,其余Cu、Cr、Zn等元素属于轻微生态风险。     

杭州城区河道底泥重金属污染及潜在生态风险评价

对杭州城区34条河道45个点位河道底泥进行采样,分析了pH及汞、砷、铅、铬、镉、铜、锌、镍等重金属含量,并进行污染及潜在生态风险评价。结果表明,监测点位的底泥为中性偏碱性,重金属含量分布不均,且范围波动很大,部分河道底泥重金属中汞、铅、镉、铬、锌、镍等有不同程度的超标,少数河道镉、铬、锌污染严重;按《农用污泥中污染物控...     

某冶炼厂周边农田土壤重金属污染特性分析及评价

采用污染指数法对冶炼厂周边的土壤及稻谷进行重金属（Zn、D、Cu、Pb、Cd和As）污染评价，结果显示冶炼厂周边土壤中除重金属铅、铬和砷外，其他重金属都超过了土壤环境质量标准，六种重金属平均综合污染指数达到2．89；对于稻谷样本中重金属含量，锌和铬含量满足评价标准要求，铜、铅、镉和砷含量超标，其超标倍数范围分别为4．68～6．35、5．45～36．75、0．05～1．5和1．59—5．67。说明冶炼厂周边土壤及稻谷已受到重金属不同程度上的污染。而重金属污染的相关性分析表明冶炼厂周边的土壤中存在多种重金属不同程度、不同组合的复合污染类型，农田生态系统存在复合污染的趋势。     

基于GIS的耕地土壤重金属污染与农业功能定位研究——以山东省聊城市为例

按8km×8km的网格将聊城市耕地分为137个采样点，调查砷、镉、铬、铜、汞、镍、铅、锌等重金属的污染状况。采用国家土壤环境质量标准、农产品安全质量标准和绿色食品产地环境条件作为评价标准，采用单因子指数和综合指数为评价方法进行污染评价。研究表明，聊城市土壤污染强度依次为铜〉镍〉锌〉砷〉铬〉镉〉铅〉汞，但均未超标。以GIS为操作平台显示聊城市重金属空间分布状况，并对区域耕地进行了功能的定位。聊城市西南部土壤质量最优，适宜种植绿色食品；无公害蔬菜和安全粮食种植区在各县市均有不同程度的分布。     

水稻产区农业生态环境重金属状况研究与评价

分别采集土壤、灌溉水样品18个，对宁化县水稻产区农业生态环境监测点的镉、汞、砷、铅、铬和铜等重金属含量进行检测，采用单因子指数法对其结果进行分析和评价。结果表明，宁化县水稻产区的农业生态环境中6种重金属元素含量均在标准规定范围内，产区土壤、灌溉水质量均为一级，达到安全清洁水平。     

都江堰(内江)水系河床底泥重金属污染调查与评价

采集了都江堰水系9条河流23个河床底泥样品，对底泥中重金属铜、锌、铅、镉、汞、铬、砷进行了分析，在分析中使用标准土样对分析结果进行质量控制。对底泥污染程度进行了评价和研究。结果表明，都江堰水系9条河流河床底泥受到不同程度的重金属污染，城市上游河段基本清洁，城市或工业集中发展区河床底泥受到污染，其中，沙河和毗河下游底泥已受到中到重金属重度污染，府河下游河段受到重金属中度污染。     

某区域内矿区土壤重金属污染与生态风险评价

探究区域内矿区土壤重金属变化并对其进行污染评价,旨在为该区域环境保护及污染治理提供一定的理论依据,以期实现矿山地质环境保护与矿产资源开发并行的矿业绿色发展。以铅、锌、镉、砷含量为评价指标,结合《土壤环境质量标准》(GB 15618—2018),采用重金属单因子污染指数法与内梅罗综合污染指数法进行重金属污染评价,并对该区域矿区潜在生态风险作出评定。结果表明,A矿区土壤各重金属含量的变异系数为149.05%~211.42%,B矿区土壤各重金属含量变异系数为60.88%~118.58%;A矿区土壤重金属均出现超标现象,其中铅、锌和镉含量超标较为严重,超标率在72%以上,而砷含量超标现象则相对较轻,超标率为36.36%;B矿区土壤铅和锌含量均未出现超标,超标率为0,而砷和镉含量则出现不同程度的超标,其中砷含量超标率为92.31%,镉含量超标率为65.38%;两个矿区土壤各重金属含量均超背景值的现象,超背景值比例为42.31%~100.00%。A矿区土壤以铅、锌和镉污染为主,而B矿区土壤中砷和镉的污染较为严重。两个矿区土壤重金属综合污染指数均属重度污染,A矿区生态风险综合指数为很强生态风险危害,而B矿区为中等生态风险危害。     

广东徐闻县绿色食品（菠萝）基地土壤重金属状况研究与评价

对广东省徐闻县5个乡镇土壤样品中重金属（镉、汞、砷、铅、铬和铜）含量进行了检测,采用单因子指数法对其结果进行评价。结果表明,徐闻县绿色食品原料（菠萝）基地土壤中6种重金属元素含量均在标准规定范围内,5个乡镇的土壤环境质量均为一级,达到安全清洁水平。     

我国蔬菜和蔬菜种植土壤的重金属污染现状与一般规律

本文对我国部分城市农用土壤和蔬菜重金属污染现状进行了综述，重金属污染在蔬菜种植土壤和蔬菜中主要是以Pb、Cd、Hg为主，且工业城市和人口密度大的城市尤为突出。分析了植物吸附重金属的一般规律与影响因素。为防治重金属污染提供了理论依据。     

柴窝堡湖表层底泥重金属污染评价

研究了乌鲁木齐市柴窝堡湖表层底泥的重金属含量,并采用Hakanson潜在生态危害指数法对底泥中的重金属潜在生态风险进行评价。结果表明:底泥中Cu、Zn、Pb、Cd含量均超出乌鲁木齐市土壤背景值。除湖心区外,Cd在5个监测区域中的潜在生态危害均为中等;其它重金属在5个采样点的潜在生态危害均为轻微。各重金属间的相关性分析表明,Zn与Cu,Pb与Cd、Cu呈显著正相关,说明这4种元素污染源可能相同。柴窝堡湖表层底泥受到Cu、Zn、Pb、Cd污染,需采取相应措施防止重金属由底泥进入水相。     

河流底泥重金属污染及潜在生态风险评价——以湘江株洲段为例

通过对湘江株洲段6个监测断面左右两岸共32个底泥样品重金属Pb,Zn,Cd,As,Hg和Cr质量比进行分析研究,并进行潜在生态风险评价。结果表明：霞湾断面是重金属富集最严重的断面;Cd,Hg和As的含量均超过GB15618—1995三级标准和长沙-湘潭-株洲3市土壤背景值;重金属含量大部分分布特征为右岸高于左岸;从重金属污染的潜在生态风险看,湘江株洲段各监测断面潜在生态风险都很高;各重金属元素对生态风险影响程度从大到小的顺序为：Hg〉Cd〉As〉Pb〉Zn〉Cr。     

成都平原农用土壤重金属污染现状及防治对策

随着工业化进程的加快和农业生产中化肥和农药不合理施用使得农用土壤重金属污染风险逐渐增大。本文对成都平原农用土壤和农作物重金属污染现状进行了综述，发现农用土壤和蔬菜中重金属污染均以Pb、Cd和Hg三种元素为主。分析了重金属离子在土壤一植物系统中迁移的一般规律及其影响因子，分析了农用土壤重金属污染的主要原因，为预防和防治污染提供了一些建议。     

Health risk assessment due to heavy metal exposure from commonly consumed fish and vegetables

Contamination of heavy metals in fish and vegetables is regarded as a major crisis globally, with a large share in many developing countries. In Bogra District of Bangladesh, concentrations of six heavy metals, i.e., chromium (Cr), nickel (Ni), copper (Cu), arsenic (As), cadmium (Cd) and lead (Pb), were evaluated in the most consumed vegetables and fish species. The sampling was conducted during February–March 2012 and August–September 2013. The levels of metals varied between different fish and vegetable species. Elevated concentrations of As, Cd and Pb were observed in vegetable species (Solanum tuberosum, Allium cepa and Daucus carota), and fish species (Anabas testudineus and Heteropneustes fossilis) were higher than the FAO/WHO permissible limits, indicating these three metals might pose risk from the consumption of these vegetable and fish species. The higher concentration of heavy metals in these vegetable species might be due to the higher uptake from soil and sediment ingestion behavior in fish species. Multivariate principal component analysis (PCA) showed significant anthropogenic contributions of Cr, Ni, Cu and Pb in samples as the PCA axis scores were correlated with scores of anthropogenic activities. Target hazard quotients showed that the intakes of Cu, As and Pb through vegetables and fish were higher than the recommended health standards, indicated non-carcinogenic risk. Therefore, intakes of these elements via fish and vegetables for Bangladeshi people are a matter of concern.     

四川东部沱江茎瘤芥产地重金属特征及其富集规律研究

通过对四川省沱江乡榨菜种植区土壤和榨菜中重金属的分布特征进行调查分析。结果表明，菜头叶茎中（Zd、Cr、（Zu、Hg、As、Pb6种重金属元素的含量一般随着土壤中此6种重金属元素含量的增加而增多，但分析样品中也有部分样点表现出异样趋势，通过分析此异常主要是人为活动影响造成的。菜头叶茎中对此6种重金属元素均表现出较高富集性，其中尤以cd最为严重，富集系数高达12．14。     

钻井液环保性能评价与分析方法研究

通过对国内外与钻井液相关的环保标准、管理指南等规范性文件的调研,结合我国陆上油田清洁生产与环境保护的实际情况,提出将钻井液的环保性能评价项目分为生物毒性、生物降解性、重金属(总镉、总汞、总铅、总铬、总砷)、石油类和pH值等5类9项,并推荐了相应的评价分析方法。     

某钢铁企业周边土壤重金属污染状况调查与评价

通过对某钢铁企业周边土壤重金属(Cu、Pb、Cd、Ni、Hg、As)含量的调查与分析,采用重金属单项污染指数、超标倍数、污染分担率和内梅罗污染指数评价方法对土壤重金属污染状况进行评价。结果表明,该钢铁企业周边土壤主要污染物为镉,含量在1.06~2.41 mg/kg之间,超标0.8~3.0倍。通过对除尘灰中相应重金属含量分析,弄清了土壤中重金属来源。     

Total Contents and Sequential Extraction of Heavy Metals in Soils Irrigated with Wastewater,Akaki, Ethiopia

The Akaki River, laden with untreated wastes from domestic, industrial, and commercial sources, serves as a source of water for irrigating vegetable farms. The purpose of this study is to identify the impact of waste-water irrigation on the level of heavy metals and to predict their potential mobility and bioavailability. Zn and V had the highest, whereas Hg the lowest, concentrations observed in the soils. The average contents of As, Co, Cr, Cu, Ni, Zn, V, and Hg of both soils; and Pb and Se from Fluvisol surpassed the mean + 2 SD of the corresponding levels reported for their uncontaminated counterparts. Apparently, irrigation with waste water for the last few decades has contributed to the observed higher concentrations of the above elements in the study soils (Vertisol and Fluvisol) when compared to uncontaminated Vertisol and Fluvisol. On the other hand, Vertisol accommodated comparatively higher average levels of Cr, Cu, Ni, Zn, etc V, and Cd, whereas high contents of Pb and Se were observed in Fluvisol. Alternatively, comparable levels of Co and Hg were found in either soil. Except for Ni, Cr, and Cd in contaminated Vertisol, heavy metals in the soils were not significantly affected by the depth (0–20 and 30–50 cm). When the same element from the two soils was compared, the levels of Cr, Cu, Ni, Pb, Se, Zn, V, Cd at 0–20 cm; and Cr, Ni, Cu, Cd, and Zn at 30–50 cm were significantly different. Organic carbon (in both soils), CEC (Fluvisol), and clay (Vertisol) exhibited significant positive correspondences with the total heavy metal levels. Conversely, Se and Hg contents revealed perceptible associations with carbonate and pH. The exchangeable fraction was dominated by Hg and Cd, whereas the carbonate fraction was abounded with Cd, Pb, and Co. conversely, V and Pb displayed strong affinity to reducible fraction, where as Cr, Cu, Zn, and Ni dominated the oxidizable fraction. Cr, Hg, Se, and Zn (in both soils) showed preference to the residual fraction. Generally, a considerable proportion of the total levels of many of the heavy metals resided in non residual fractions. The enhanced lability is generally expected to follow the order: Cd > Co > Pb > Cu > Ni > Se > V and Pb > Cd > Co > Cu > Ni > Zn in Vertisol and Fluvisol, respectively. For the similar wastewater application, the soil variables influence the status and the distribution of the associated heavy metals among the different soil fractions in the study soils. Among heavy metals that presented relatively elevated levels and with potential mobility, Co, Cu, Ni (either soil), V (Vertisol), Pb, and Zn (Fluvisol) could pose health threat through their introduction into the food chain in the wastewater irrigated soils.