夏尔希里地区土壤重金属特征及空间变异分析

以夏尔西里地区为研究区,对土壤中As、Zn、Hg、Pb等4种重金属的含量特征和空间分异特征进行研究,并采用单因子污染指数法、内罗梅综合污染指数法、克里格插值法对研究区土壤重金属污染状况和分布特征进行了分析,结果表明:研究区4种重金属含量为:ZnAsPbHg,Hg属于强变异性,其它3种重金属和有机质均属于中等变异强度;相关性分析结果显示:Zn和Pb呈现显著的正相关,As与Hg、Pb均表现出显著的负相关,有机质和Pb、As、Zn、Hg呈现出弱相关性;重金属含量空间分异特征整体表现为绿洲区荒漠区山地区;重金属污染评价结果为:Pb和Zn污染指数介于1~2之间,属于轻污染,Hg和As污染指数介于2~3之间,属于中度污染。     

海南省农产品产地土壤环境质量评价

采用单项质量指数与综合质量指数相结合的方法,对海南省农产品产地的土壤进行了重金属Cd、 Hg、 As、 Pb、 Cr、 Cu、 Zn和Ni含量的抽样调查分析与评价。结果表明,海南省农产品产地土壤重金属的平均含量均低于“HJ 332-2006”（食用农产品产地环境质量评价标准）规定的限值,土壤重金属的单项质量指数均≤0．7,综合质量指数为0．33,土壤环境质量均为1级,属于清洁水平,适宜发展无公害农产品。同时发现,部分产地的土壤中重金属含量有超标现象,海口有部分样品Cd、 Hg、 Cr、 Cu和Ni超标,三亚有部分样品Cd和Hg超标,儋州、澄迈均以Ni超标为主,琼海有部分样品Cr、 Cu和Ni超标。重金属含量之间多呈正相关关系,其中As与Pb、 As与Cu、 Cr与Zn、 Cu与Zn之间的相关性达到了极显著水平, Cd与Hg、 Pb、 Ni, Pb与Cu, Cr与Cu, Cu与Ni之间的相关性达到了显著水平。大部分监测点土壤中重金属含量均高于海南省水稻土自然背景值,表明在监测点土壤中产生了重金属累积。     

东莞市农田土壤和蔬菜重金属的含量特征分析

从东莞市采集118 个农田土壤样品和43 个蔬菜样品, 测试其中Cu、Zn、Ni、Cr、Pb、 Cd、As 和Hg 等8 种重金属元素的含量, 并结合GIS 制图和数据统计, 对农田土壤中重金属 的空间分布和来源、土壤和蔬菜中重金属的富集特征及其潜在风险进行了分析。结果表明, 农田土壤中Cu、Zn、Ni、Pb、Cd 和Hg 等元素含量均高于相应元素的广东省土壤背景值, 其中, Pb (65.38 mg kg^-1) 和Hg (0.24 mg kg^-1) 含量分别为其对应背景值的1.82 和2.82 倍。与我国《土壤环境质量标准》中II 级标准(pH < 6.5) 相比, 土壤中Cu、Ni、Cd 和Hg 含量样本超标率分别为3.4%、5.9%、1.7%和28%, 表现为以Hg 为主的多种重金属共同污染。土壤 中8 种重金属中Cu、Zn、Ni、Cr 和As 等元素主要来源于成土母质, Pb、Hg 和Cd 等元素主要与人类活动有关。空间分布上, Cu、Zn、Ni、Cr、Pb、As 和Hg 等7 种重金属含量呈现出西部高、东部低的特点, Cd 含量在西北部和东南部较高, 西南部较低。与《食品中污染物限量》(GB2762-2005) 等相关标准比较, 蔬菜中Ni、Pb 和As 含量的样本超标率分别为4.7%、16.3%和48.8%。蔬菜中重金属富集系数的顺序为: Cd > Zn > Cu > As > Ni > Hg > Cr > Pb。     

艾比湖流域农田土壤重金属的环境风险及化学形态研究

采集土壤样品,测定8种重金属（As、Cd、Cr、Cu、Hg、Ni、Pb、Zn）的总量及各形态含量,然后采用多种方法并结合土壤背景值进行分析。结果表明：艾比湖流域农田土壤中8种重金属的含量值均未超过国家土壤质量二级标准的限值, 8种重金属可以辨识为2个主成分,重金属Cd、Hg、Pb和Zn的较高风险区主要分布在研究区的中部,重金属As、Cr、Cu和Ni的较高风险区主要分布在研究区南部靠近荒漠、山地以及研究区边缘区域,重金属As、Cr和Ni均以残渣态为主,其他形态含量较低。农田土壤中重金属的生物毒性以Cb为最大,Pb和Hg次之。     

艾比湖流域农田土壤重金属的环境风险及化学形态研究北大核心CSCD

采集土壤样品,测定8种重金属(As、Cd、Cr、Cu、Hg、Ni、Pb、Zn)的总量及各形态含量,然后采用多种方法并结合土壤背景值进行分析。结果表明:艾比湖流域农田土壤中8种重金属的含量值均未超过国家土壤质量二级标准的限值,8种重金属可以辨识为2个主成分,重金属Cd、Hg、Pb和Zn的较高风险区主要分布在研究区的中部,重金属As、Cr、Cu和Ni的较高风险区主要分布在研究区南部靠近荒漠、山地以及研究区边缘区域,重金属As、Cr和Ni均以残渣态为主,其他形态含量较低。农田土壤中重金属的生物毒性以Cb为最大,Pb和Hg次之。     

黄河下游滩区开封段土壤重金属空间分异规律

对黄河下游滩区开封段及滩外土壤采样48个,按照土壤化学分析方法,对铅(Pb)、铬(Cr)、汞(Hg)、砷(As)和镉(Cd)5种重金属进行分析,采用单因子污染指数、普通克里格法和相关分析对研究区土壤重金属含量特征、污染状况和分布特征进行了计算。结果表明:①研究区土壤5种重金属Pb、Cr、Hg、As和Cd含量就平均值而言,Cr的平均含量最大,Pb、Hg的平均含量最小。Pb、Cr、Hg、As和Cd4种重金属元素的变异系数在0.13～0.28之间,属于中等变异强度,Hg变异系数较大,Hg的空间差异相对较大;②重金属元素Pb、Cr、Hg、As、Cd之间具有较强的线性关系,可能具有共同来源——水沙输入;③主要污染元素为Hg、As、Pb,其中Pb的污染为中度污染且范围较广,而As和汞Hg构成三级轻度污染。Cr和Cd在各村间变化不大,Cr,Cd没有构成污染,且Cd是全部清洁表现出污染没有积累;④土壤各重金属元素的空间分布特征在研究区内上下段之间分异明显,上段呈清洁状态,中段有少量污染,下段表现出明显富集的分布状态。     

上海市崇明岛农田土壤重金属的环境质量评价

通过对上海市崇明岛28个菜地土壤表层样品、65个稻田土壤表层样品及9个西瓜地土壤表层样品的分析测试,利用国家、行业和地方的相关标准评价了农田土壤重金属(Pb、Cd、Cr、As、Hg)的环境质量状况.研究发现:崇明岛农田土壤重金属的总体含量为Pb21.597 mg·kg-1、Cd 0.176 mg-kg-1、Cr 69.395 mg·kg-1、As 9.209 mg·kg-1、Hg O.128 mg·kg-1.与上海市土壤背景值相比,除Pb、Cr外,其余重金属平均含量均高于其背景值,Cd、As和Hg分别高出背景值33.O%、1.2%和26.3%.在GIS软件支持下,通过空间插值分析了研究区农田土壤重金属含量的空间分布特征,结果发现,农田土壤质量整体尚好,土壤生态率为1.26%,优良率为97.14%,合格率为1.47%,不合格率为0.12%.以背景值为标准,崇明岛农田土壤Pb、Cd、Cr、As、Hg的超标率分别为10.1%、85.7%、27.0%、55.4%、55.2%;3种土地利用类型中,菜地受重金属污染最为严重,这主要与菜地施用更多农药有关.崇明岛重金属的年沉降通量分别为Pb 7735.470 ug·m-2.a-1、Cd 208.432ug.m-2·a-1、As 2237.738 ug·m-2·a-1、Hg 52.783 ug·m-2·a-1,农作物秸秆焚烧处理是崇明岛大气重金属沉降的重要来源,大气沉降对崇明岛农田土壤重金属有较大的影响.     

大山包黑颈鹤国家级自然保护区湿地土壤重金属污染评价

2014年9~11月,在测定大山包黑颈鹤国家级自然保护区湿地土壤重金属含量的基础上,分析其重金属的来源;采用内梅罗综合污染指数法和潜在生态危害指数法,评价该区土壤重金属污染特征和潜在的生态危害。结果表明,研究区土壤中的Cu、Zn、Cr、Pb、Cd、Ni、As和Hg的平均质量比分别为159.73 mg/kg、133.35mg/kg、16.53 mg/kg、39.6 mg/kg、1.26 mg/kg、34.76 mg/kg、5.19 mg/kg和0.08 mg/kg;其中,Cd和Hg含量都高于云南省背景值,大多数采样点土壤中的As、Cu、Pb和Zn含量也高于云南省背景值,Cr和Ni含量低于云南省背景值;土壤重金属的污染程度由高到低依次为Cd、Cu、Zn、Pb、Ni、Hg、As和Cr污染,重金属的潜在生态危害由强至弱依次为Cd、Hg、Cu、As、Pb、Zn和Cr生态危害。退耕4 a的土壤综合污染程度和重金属的潜在生态危害指数最高,其次为自然土壤的,退耕10 a土壤的最低;研究区土壤潜在生态危害程度为中等至强等危害程度,土壤重金属污染严重,Cd是第一污染物。土壤退耕年限越长,土壤的污染程度和潜在生态危害越低。研究区湿地土壤重金属污染严重,可能会对黑颈鹤(Grus nigricollis)的取食和健康造成危害。     

施用不同畜禽粪便土壤剖面中重金属分布特征

针对不同粪便集中施用情况, 选取禹城市3 个畜禽养殖区, 通过采集不同旱地农田土壤剖面样品, 研究典型重金属元素随粪便施用程度的变化、土壤剖面中重金属垂直分布特征以及施用不同畜禽粪便土壤剖面中重金属分布的差异。结果发现,长期施用畜禽粪便土壤剖面中重金属Cu、Zn、Pb、Cr、As的含量要高于未施用畜禽粪便的对照土壤剖面, 其中Cu、Zn 超过对照组较大;偶尔施用畜禽粪便土壤剖面Cu、Zn、Pb、Cr、As 的含量低于长期施用畜禽粪便土壤剖面, 且与未施用畜禽粪便的对照土壤剖面相差不大。牛粪集中施用区土壤剖面中Cu、Pb、Cr、Cd、Ni 等重金属存在较为明显的淋溶下移性, Hg、As两元素存在较为明显的表层或亚表层聚集现象;猪粪集中施用区土壤剖面各重金属除Cr、Ni 外, 都显示出较为明显的表层或亚表层聚集现象;鸡粪集中施用区的土壤剖面Cu、Pb、Cd、Cr、Ni 存在一定的淋溶下移性, 而Zn、Hg、As等3 种元素存在显著表层亚表层聚集现象。长期施用不同畜禽粪便的不同土壤剖面Cr、Ni、Cd、Pb 等含量变化差异明显, 而As、Hg差异性不显著;施牛粪与施鸡粪剖面中的Zn, 施猪粪与施鸡粪剖面中的Cu差异也不显著。     

西溪湿地土壤重金属分布特征及其生态风险评价

测试和研究了杭州西溪湿地土壤中铜(Cu)、锌(Zn)、铅(Pb)、镉(Cd)、汞(Hg)、砷(As)和铬(Cr)的含量与分布特征,采用内梅罗综合污染指数和Hakanson潜在生态危害指数法对湿地土壤重金属污染环境质量和潜在生态风险进行了评价。结果表明,西溪湿地土壤表层7种重金属平均含量的质量比分别为36.8 mg/kg(Cu)、91.5 mg/kg(Zn)、39.2 mg/kg(Pb)、0.23 mg/kg(Cd)、0.19 mg/kg(Hg)、6.3 mg/kg(As)和64.9 mg/kg(Cr)。由于受各种人为作用的影响,与浙江省土壤背景值相比,Cu、Pb、Cd和Zn在湿地土壤中的积累较大,有3个采样点[菜地、芦苇(Phram ites austrlis)滩地和靠马路的居民区]土壤中的Cd含量超过《土壤环境质量标准》(GB15618-1995)标准值的二级标准(pH<6.5)。湿地土壤重金属污染环境质量和生态风险评价结果显示,内梅罗综合污染指数平均值为1.73,多种重金属潜在生态风险指数平均值为114.6,说明总体上西溪湿地土壤重金属污染及其潜在生态风险为轻微级。最后,讨论了西溪湿地公园土壤重金属的可能来源,对比了重金属污染评价中不同评价标准和评价方法的差异性。     

蔬菜重金属暴露接触对大宝山矿区及周边居民的健康风险

通过36个土壤样品,32个灌溉水及120个蔬菜样品的调查研究,结果表明,广东韶关翁源县大宝山及周边的四个地区土壤、灌溉水及蔬菜中重金属含量都表现为:上坝>下坝>蓑衣坑>何屋。下坝、蓑衣坑及何屋通过食用蔬菜日均Pb、Zn、Cd、Cu摄入量均未超过FAO/WHO人均日摄入可允许限量标准。但上坝居民通过蔬菜摄入Pb和Cd的DI分别为PTDI的1.40和1.35倍。靶标危害系数(Target hazard quotients)THQ研究结果表明,何屋和蓑衣坑的蔬菜中几种重金属的THQ值均小于1,说明蔬菜途径摄入重金属对其居民健康风险很低。上坝居民通过蔬菜摄入的Pb和Cd的THQ均大于1,蔬菜途径重金属暴露接触对上坝居民健康具有潜在风险。居住在污染河流横石河下游的上坝居民面临严重的重金属接触暴露风险,显著高于对太平河上游及下游居民的健康风险。     

东莞市农田土壤和蔬菜重金属含量分析(英文)

A total of 118 of agricultural soil and 43 of vegetable samples were collected from Dongguan City,Guangdong,China. The spatial distribution,sources,accumulation charac-teristics and potential risk of heavy metals in the agricultural soils and vegetables were de-picted in details by three different approaches,including total contents of eight metal ele-ments in soils and vegetables,GIS maps and multivariate analysis of heavy metals in soils in the study. The results show that there are higher accumulation of heavy metals such as Cu,Zn,Ni,Pb,Cd and Hg in agricultural soils,and the contents of Pb (65.38 mg kg-1) and Hg (0.24 mg kg-1) are 1.82 and 2.82 times of the background contents of the corresponding heavy metals in soils of Guangdong Province,respectively. There are about 3.4% of Cu,5.9% of Ni,1.7% of Cd and 28% of Hg in all collected soil samples from all investigated sites which have overran the contents for heavy metals of the China Environmental Quality Standard for Soils (GB15618-1995,Grade Ⅱ ). The pollution characteristics of multi-metals in soils are mainly reflected by Hg. There are different sources to eight metal elements in soils,Cu,Zn,Ni,Cr and As are predominantly derived from parent materials,and Pb,Hg and Cd are affected by anthropogenic activities. The spatial distribution shows that the Cu,Zn,Ni,Cr,Pb,As and Hg contents of agricultural soils are high in the west and low in the east,and Cd contents are high in the northwest,southeast and low in the southwest in Dongguan. The ratios of vegetable samples which Ni,Pb and As concentrations higher than the Maximum Levels of Con-taminants in Foods (GB2762-2005) are 4.7%,16.3% and 48.8%,respectively. The order of bio-concentration factors (BCF) of heavy metals in vegetables is Cd Zn Cu As Ni Hg Cr Pb. It is necessary to focus on potential risk of heavy metals for food safety and hu-man's health from agricultural soils and vegetables in Dongguan City,Guangdong Province.     

Heavy metal concentrations of agricultural soils and vegetables from Dongguan, Guangdong

A total of 118 of agricultural soil and 43 of vegetable samples were collected from Dongguan City, Guangdong, China. The spatial distribution, sources, accumulation characteristics and potential risk of heavy metals in the agricultural soils and vegetables were depicted in details by three different approaches, including total contents of eight metal elements in soils and vegetables, GIS maps and multivariate analysis of heavy metals in soils in the study. The results show that there are higher accumulation of heavy metals such as Cu, Zn, Ni, Pb, Cd and Hg in agricultural soils, and the contents of Pb (65.38 mg kg?1) and Hg (0.24 mg kg?1) are 1.82 and 2.82 times of the background contents of the corresponding heavy metals in soils of Guangdong Province, respectively. There are about 3.4% of Cu, 5.9% of Ni, 1.7% of Cd and 28% of Hg in all collected soil samples from all investigated sites which have overran the contents for heavy metals of the China Environmental Quality Standard for Soils (GB15618-1995, Grade Ⅱ). The pollution characteristics of multi-metals in soils are mainly reflected by Hg. There are different sources to eight metal elements in soils, Cu, Zn, Ni, Cr and As are predominantly derived from parent materials, and Pb, Hg and Cd are affected by anthropogenic activities. The spatial distribution shows that the Cu, Zn, Ni, Cr, Pb, As and Hg contents of agricultural soils are high in the west and low in the east, and Cd contents are high in the northwest, southeast and low in the southwest in Dongguan. The ratios of vegetable samples which Ni, Pb and As concentrations higher than the Maximum Levels of Contaminants in Foods (GB2762-2005) are 4.7%, 16.3% and 48.8%, respectively. The order of bio-concentration factors (BCF) of heavy metals in vegetables is Cd > Zn > Cu > As > Ni > Hg > Cr > Pb. It is necessary to focus on potential risk of heavy metals for food safety and human’s health from agricultural soils and vegetables in Dongguan City, Guangdong Province.     

Assessment on environmental quality of heavy metals in agricultural soils of Chongming Island, Shanghai City

The environmental quality of heavy metals (Pb, Cd, Cr, As, Hg) in agricultural surface soil of Chongming Island was assessed by national, local and professional standards based on a large scale investigation, in which 28 samples from vegetable plots, 65 samples from paddy fields and 9 samples from watermelon fields were collected from whole island area. Results showed that the average concentration of Pb, Cd, Cr, As and Hg was 21.6 mg·kg-1 , 0.176 mg·kg-1, 69.4 mg·kg-1, 9.209 mg·kg-1 and 0.128 mg·kg-1, respectively. Compared with the background value of Shanghai City soil, except for Pb and Cr, all the other heavy metals average concentrations in Chongming Island agricultural surface soil exceeded their corresponding natural-background values. The concentrations of Cd, As and Hg were 33.0%, 1.2% and 26.3% higher than the background value of Shanghai City, respectively. In addition, inverse distance interpolation (IDW) tool of GIS was also applied to study the spatial variation of heavy metals. The results indicated that most of agricultural soil quality was good, and the ratio of ecological, good soil, certified soil and disqualified soil were 1.26%, 97.1%, 1.47% and 0.12%, respectively. About 10.1%, 85.7%, 27.0%, 55.4% and 55.2% soil samples exceeded the Pb, Cd, Cr, As and Hg background value of Shanghai City, respectively. Among these three land use type soils, vegetable soil was most seriously polluted by heavy metals, which is probably related to the over-application of pesticides. The annual deposition fluxes of Pb, Cd, As and Hg were 7736 μg·m-2·a-1, 208 μg·m-2·a-1, 2238 μg·m-2·a-1 and 52.8 μg·m-2·a-1, respectively. Crop straw burning was the important source of heavy metals of atmospheric deposition, and atmospheric deposition contributed a lot to heavy metals in agricultural soil in Chongming Island.     

湘江中下游农田土壤和蔬菜的重金属污染

从湖南省湘江中下游衡阳-长沙段沿岸采集219 个农田土壤样品和48 个蔬菜样品, 测 试其中As、Cd、Cr、Cu、Ni、Pb、Zn 等7 种重金属元素的含量, 并结合GIS 作图与数据统 计, 对农田土壤中重金属空间分布、土壤和蔬菜中重金属富集特征以及其潜在风险进行分析。 结果表明, 农田土壤中As、Cd、Cu、Ni、Pb 和Zn 含量均大于湖南省相应土壤重金属含量背 景值, Cd (2.44 mg kg^-1)、Pb (65.00 mg kg^-1)、Zn (144.13 mg kg^-1) 含量分别超标7.97、3.69 和 1.63 倍。与我国《土壤环境质量标准》(GB15618-1995) 中II 级标准(pH 6.5~7.5) 比较, 土壤 As、Cd、Cu、Ni、Pb 和Zn 含量的超标率分别为13.2%、68.5%、2.7%、2.7%、8.7%和 15.1%, 表现为以Cd 为主的多种重金属混合污染。菜地土壤中As、Cd、Cu、Pb 和Zn 的含 量( 几何均值) 分别高于水稻土As、Cd、Cu、Pb 和Zn 含量。与《食品中污染物限量》 (GB2762-2005) 等标准比较, 蔬菜As、Cd、Ni、Pb 含量的样本超标率分别为95.8%、68.8%、 10.4%和95.8%; 蔬菜Cd、Pb、Zn 含量与相应土壤的Cd、Pb、Zn 含量存在极显著的相关性 (P < 0.01)。湘江中下游的农田土壤和蔬菜中重金属污染的潜在风险值得关注。     

Heavy metal pollution of soils and vegetables in the midstream and downstream of the Xiangjiang River, Hunan Province

A total of 219 agricultural soil and 48 vegetable samples were collected from the midstream and downstream of the Xiangjiang River (the Hengyang–Changsha section) in Hunan Province. The accumulation characteristics, spatial distribution and potential risk of heavy metals in the agricultural soils and vegetables were depicted. There are higher accu-mulations of heavy metals such as As, Cd, Cu, Ni, Pb and Zn in agricultural soils, and the contents of Cd (2.44 mg kg-1), Pb (65.00 mg kg-1) and Zn (144.13 mg kg-1) are 7.97, 3.69 and 1.63 times the corresponding background contents in soils of Hunan Province, respectively. 13.2% of As, 68.5% of Cd, 2.7% of Cu, 2.7% of Ni, 8.7% of Pb and 15.1% of Zn in soil sam-ples from the investigated sites exceeded the maximum allowable heavy metal contents in the China Environmental Quality Standard for Soils (GB15618-1995, Grade II). The pollution characteristics of multi-metals in soils are mainly due to Cd. The contents of As, Cd, Cu, Pb and Zn in vegetable soils are significantly higher than the contents in paddy soils. 95.8%, 68.8%, 10.4% and 95.8% of vegetable samples exceeded the Maximum Levels of Contami-nants in Foods (GB2762-2005) for As, Cd, Ni and Pb concentrations, respectively. There are significantly positive correlations between the concentrations of Cd, Pb and Zn in vegetables and the concentrations in the corresponding vegetable soils (p<0.01). It is very necessary to focus on the potential risk of heavy metals for food safety and human health in agricultural soils and vegetables in the midstream and downstream of the Xiangjiang River, Hunan Province of China.     

北京市小麦籽粒的重金属含量及其健康风险分析

为评价北京市小麦重金属含量及其健康风险,采集北京市现有小麦种植区土壤和小麦籽粒对应样品68份,分析其重金属含量,并估算消费导致重金属摄入量。结果表明:北京市麦地土壤重金属As、Cd、Cr、Cu、Ni、Pb和Zn的平均值分别为7.46、0.165、37.8、20.3、24.2、14.3和70.1mg/kg,处于比较清洁水平。这说明小麦种植这种土地利用方式并不会导致土壤重金属升高。小麦籽粒中重金属含量,除Cr与食品卫生标准限值没有显著性差异外,其他元素均显著低于相应标准限值。普通人群通过小麦制品消费,As、Cd、Cr、Cu、Ni、Pb和Zn的摄入量分别为0.005、0.004、0.136、0.994、0.041、0.024、4.75mg/人 · d。北京小麦种植的主要4个区中,顺义产小麦的Cr、Cu、Ni和Pb导致的重金属摄入量高于其他3个区,房山产小麦导致的重金属摄入量最低。对于普通人群而言,通过小麦和蔬菜摄入重金属没有明显风险。     

湘江中下游农田土壤和蔬菜的重金属污染

A total of 219 agricultural soil and 48 vegetable samples were collected from the midstream and downstream of the Xiangjiang River（the Hengyang-Changsha section）in Hunan Province.The accumulation characteristics,spatial distribution and potential risk of heavy metals in the agricultural soils and vegetables were depicted.There are higher accumulations of heavy metals such as As,Cd,Cu,Ni,Pb and Zn in agricultural soils,and the contents of Cd（2.44 mg kg^-1 ）,Pb（65.00 mg kg^-1 ）and Zn（144.13 mg kg^-1 ）are 7.97,3.69 and 1.63 times the corresponding background contents in soils of Hunan Province,respectively. 13.2%of As,68.5%of Cd,2.7%of Cu,2.7%of Ni,8.7%of Pb and 15.1%of Zn in soil samples from the investigated sites exceeded the maximum allowable heavy metal contents in the China Environmental Quality Standard for Soils（GB15618-1995,Grade Ⅱ）.The pollution characteristics of multi-metals in soils are mainly due to Cd.The contents of As,Cd,Cu,Pb and Zn in vegetable soils are significantly higher than the contents in paddy soils.95.8%, 68.8%,10.4%and 95.8%of vegetable samples exceeded the Maximum Levels of Contaminants in Foods（GB2762-2005）for As,Cd,Ni and Pb concentrations,respectively.There are significantly positive correlations between the concentrations of Cd,Pb and Zn in vegetables and the concentrations in the corresponding vegetable soils（p〈0.01）.It is very necessary to focus on the potential risk of heavy metals for food safety and human health in agricultural soils and vegetables in the midstream and downstream of the Xiangjiang River,Hunan Province of China.     

青海省湟水河西宁段重金属元素的污染和评价

湟水河是西宁市的重要河流。开展湟水河西宁段沉积物的重金属研究对西宁市的环境保护和生态建设具有重要意义。本次研究对湟水河西宁段表层泥质沉积和河水以及流域内的现代菜地表土和松树苗地表土的重金属含量进行了测定。同时,采用全新世以前的黄土、湟水河一级阶地的砂质沉积给出了西宁市自然状态下的重金属背景值。各类样品的重金属元素含量结果表明:1)自然状态下,Pb为29.5 mg/kg,As为15.6 mg/kg,Hg为0.01 mg/kg,Cd为0.18 mg/kg,Cr为31.1 mg/kg。2)河流表层泥质沉积的重金属含量平均值,Pb为45.2 mg/kg,As为7.8 mg/kg,Hg为0.02 mg/kg,Cd为0.48 mg/kg,Cr为48.8 mg/kg。3)总体上,河流表层泥质沉积、现代菜地表土和松树苗地表土的Cd、Pb、Hg、Cr均比自然状态下的背景值要高。4)湟水河西宁段已出现较明显的重金属污染,应控制Cd等重金属元素向河流中的排放。