新疆喀什市农田土壤重金属特征分析

目的对新疆喀什市农田土壤重金属特征进行分析,方法采用火焰原子分光光度计测定土壤中的重金属Cu、Zn、Pb、Cr、Cd、Ni。结果农田土壤在不同深度土层的重金属Cr、Cd、Cu、Ni、Pb、Zn含量分布规律均为0~20 cm土层20~40 cm土层40~60 cm土层,即在土壤表层聚集。结论棉田土壤的Cd、Cu、Ni、Pb、Zn的含量均高于小麦土壤,且Cd含量略高于土壤背景值。     

湖南长沙城市土壤地质环境综合评价

对长沙市土壤重金属Cu、Pb、Zn、Cd、Cr、Hg、As污染现状进行了调查与评价。结果表明,长沙市110个样本中总体Cd、Cr污染程度已经属于重污染,Zn、As属于中污染,Cu、Pb、Hg属于轻度污染;不同母岩类型土壤中泥盆纪砂页岩、新生代沉积物、花岗岩的重金属含量较高。     

湘潭市土壤重金属地球化学特征的统计分析

运用相关性分析、聚类分析、因子分析及直方图分析对湘潭市土壤重金属地球化学特征进行了研究。结果表明：（1）As、Cd、Cu、zn与pH值呈显著正相关;As与Cd、Cu、Ph、zn呈显著正相关;Cd与As、Cu、Pb呈显著正相关;Cu与As、Cd、Pb、Zn呈显著正相关;Pb与As、Cu、zn呈显著正相关;Zn与As、Cd、Cu、Pb呈显著正相关;Hg与其他重金属及pH值不具有显著相关关系。（2）本区重金属分为两类,即Cr、pH、As、Zn、Cu、Cd;Hg、Pb。（3）区内重金属存在3种主要元素组合即As—Cd—Cu—Pb—Zn—pH;Cr—Hg;Cd—pH;（4）区内重金属As、Cd、Cr、Cu、Hg、Zn服从正态分布。（5）通过前人对湘潭市土壤重金属进行生态地球化学评价可知,区内Cd、Hg属重污染,从统计分析结果来看,Cd随着本区pH值变化而变化,并与As、Cu、Pb相关性显著;而Hg与pH值及其它重金属之间没有必然联系。     

杭州不同功能区道路灰尘中污染物的分布和有效性

比较研究了杭州城市的工业区、商业区、居民区、公园和附近农村道路灰尘中重金属(Pb、Cu、Cd、Zn、Hg)、P和有机物的积累情况,测定了灰尘分散到水中后污染物在溶液、悬浮物和沉积物中的分配情况。结果表明,不同功能区城市灰尘中污染物含量有较大的变异:重金属一般以工业区和商业区为最高;P以居民区和商业区为最高,而有机物以公园和居民区最高;灰尘中污染物含量随粒径减小而增加。当灰尘分散至水中后,重金属等污染物大部分以沉积相形式存在,少量以溶解相和悬浮相存在;溶解态重金属的比例均较低,平均在0.5%以下,其中ρ(Hg)、ρ(Cd)>ρ(Zn)、ρ(Cu)>ρ(Pb)。而生物有效态(双酸提取)重金属占其总量的比例平均在12%~29%之间,由高到低顺序为Zn,Cd,Cu,Hg,Pb。     

长沙市公园土壤重金属调查与评价

根据对长沙市公园土壤的重金属含量测定结果,采用内梅罗综合污染指数对其进行了评价,并运用相关分析、聚类分析进行了统计分析。研究结果表明,岳麓山公园、烈士公园土壤重金属含量较低,月亮岛土壤重金属含量较高。通过内梅罗综合污染指数评价,认为岳麓山公园土壤属于安全级别,未发生重金属污染;烈士公园土壤中Cr、Hg、Cd属轻污染,其余重金属无污染;月亮岛中土壤重金属污染相对严重,其中Zn、Cd属重污染。通过相关分析表明,与pH值呈正相关的为Cr、Zn、Pb、As;聚类分析研究表明,在距离为20分为两大类Cr、Zn;Hg、Cd、Cu、As、Pb、pH。     

贵阳污灌区菜地土壤团聚体中有机碳和重金属的含量特征及相关性分析

以贵阳某污灌区菜地土壤为研究对象,分别采用微波消解-电感耦合等离子体质谱(ICP-MS)法和水合热重铬酸钾氧化分光光度法分析不同粒径土壤团聚体中重金属和有机碳的含量特征,并对有机碳和重金属的相关性进行分析。结果表明,以2mm粒径团聚体的含量为最高,约占75%。Cu、Zn、Cd和Pb在0.25～0.5mm粒径团聚体中含量最高,Cr在5～8mm粒径团聚体中含量最高,As在不同粒径团聚体中的含量变化不大,重金属含量随土层深度增大而减小。土壤重金属富集因子表现为CuPbCdZnCrAs,Cu、Zn、Cd和Pb在0.25～0.5mm粒径团聚体中分布因子最高,而在5～8mm粒径团聚体中重金属的质量负载因子最大。土壤有机碳含量随团聚体粒径的增大表现为先增大后减小,不同粒径团聚体中Cu、Cd、Pb和As含量与有机碳含量均呈显著正相关(p0.05)。污灌区菜地土壤Cr、As在5～8mm粒径团聚体中富集现象显著,Cu、Zn、Cd、Pb在0.25～0.5mm粒径团聚体中均表现出显著的富集特征。6种重金属在5～8mm粒径团聚体中的质量负载因子均为最高,表明6种重金属在5～8mm粒径团聚体中的贡献最大。     

丹-锡高速公路两侧土壤中重金属元素污染的测定与评价（英文）

论文对丹-锡高速公路两旁土壤中重金属Pb、Cd、Cr、Cu、Zn、Fe、Ni和Mn元素的含量进行了采样调查。分别用单项污染指数、内梅罗指数和地累积指数对土壤中重金属元素的污染状况进行了评价。结果表明:高速公路两旁栽种防护林对土壤重金属污染起到一定的防护作用。随着距路基中心距离的增加,土壤pH值变化范围不大,土壤略呈弱酸性,土壤中Pb、Zn、Mn、Cd和Cu的含量呈现下降的趋势,Fe、Cr、Ni的含量在距路基10~30m范围内略有增加。公路两侧土壤中Pb含量超过背景值,但没有引起污染,Zn、Cr和Cd含量处于轻度到中度污染。土壤中Pb、Cd、Zn、Fe和Cu来自于同一类污染源。     

冶炼厂烟囱降尘农田土壤重金属含量及潜在生态风险评价

摘要：为了研究冶炼厂下风向烟囱降尘对农田土壤重金属污染影响程度,以济源市某一冶炼厂工业烟囱下风向降尘覆盖农田土壤为研究对象,依次对距离该厂烟囱大约为750m-3000m的7个农田研究区（P1-P7）土壤中重金属（Hg、As、Pb、Cd、Cu、Zn、Ni、Cr、）含量进行污染状况分析,采用了单项潜在生态风险指数法和综合潜在生态风险指数法对冶炼厂下风向烟囱降尘土壤中重金属的潜在生态风险进行评价。结果表明：在3 km2研究区域范围内,距离冶炼厂越近土壤重金属含量越高,Pb、Cd为重度污染,超过了《土壤环境质量农用地土壤污染风险管控标准》（GB15618-2018）农用地土壤污染风险管制值的1.2倍,距离冶炼厂烟囱下风向P1区土壤中重金属As、Pb、Cd、Cu、Zn超过土壤环境质量农用地土壤风险筛选值,Cd 在浓度值均超过农用土壤污染风险管制值1.8倍,As元素平均浓度值超农用土壤污染风险管制值1.7倍,Pb、Cu和Zn污染较严重,Cd、Hg对综合指数（RI）贡献值较大分别为68.63和22.4。单项潜在生态风险指数评价结果显示Cd存在极严重的潜在生态风险,Pb、Cu存在较严重潜在生态风险,冶炼厂下风向土壤中综合潜在生态风险指数评价显示,冶炼厂下风向降尘土壤重金属具有较强的生态风险。     

某冶炼厂周边土壤重金属污染评价分析及源解析研究

有色金属矿产资源采选冶活动造成的土壤重金属污染已成为严重的环境问题。采用电感耦合等离子体质谱法和光谱法测定某冶炼厂周边不同区域内土壤中重金属Cu、Pb、Zn、As、Ni、Cr、Cd、Hg元素含量,采用Kriging空间插值方法对重金属空间分布特征进行分析,采用内梅罗指数法对其污染状况进行评价,采用多元统计分析对重金属元素的污染源进行分析。结果表明,研究区土壤采样点80%处于污染状态,且以重度污染为主,污染比较严重的区域受风向影响在冶炼厂的西部和南部方向,污染严重的重金属元素为Cu、Pb、Cd、Zn和As,土壤中各重金属元素的污染源除来自于冶炼厂外,Zn-Cd-PbCu-As、Ni-Cr、Hg分别还受到机动车辆排放、自然因素、燃煤及农药使用的影响。     

万宁小海表层沉积物中重金属物质的空间分布特征及生态风险分析

为了解万宁小海海域表层沉积物重金属污染状况,2020年5月在小海潟湖采集18个沉积物样品,采用电感耦合等离子体质谱法（ICP-MS）同时测定5种重金属含量,采用原子荧光光度计测定总汞和砷,并分析归纳出重金属分布特征。采用Hakanson的潜在生态风险指数法识别小海表层沉积物潜在生态风险程度,以及运用富集系数和地累积法进一步评价小海表层沉积物重金属的污染程度。结果表明：Cu、Pb、Zn、Cd、Cr、Hg和As含量平均值分别为7.26 mg/kg、27.08 mg/kg、75.06 mg/kg、0.16 mg/kg、38.43 mg/kg、0.054 mg/kg、4.66 mg/kg,均符合第一类海洋沉积物质量标准。7种元素的潜在生态风险程度依序为Hg＞Cd＞Pb＞As＞Cu＞Cr＞Zn,其中Hg和Cd为主要潜在生态危害因子,其综合潜在生态风险等级已达到中等级风险;富集系数评价和地质累积系数评价污染程度依次为：Cd＞Hg＞Pb＞Zn＞Cr＞As＞Cu;表层沉积物中TOC 含量与 Cu、Pb、Zn、Cd 和 Cr 含量具存在显著正相关,与粒度呈一定的负相关。     

黔产市售绿茶重金属的含量特征及健康风险评估

为研究黔产市售绿茶中重金属的含量分布特征及健康风险,以五个生产加工地的黔产市售绿茶为研究对象,分析其9种重金属(Pb、Cr、Cd、Hg、Cu、Zn、Mn、Ni和As)含量,利用美国环境保护署(USEPA)推荐的健康风险评价模型进行人体重金属的健康风险评价。结果表明,五种茶叶中Cr、Cd、Pb、Hg、Cu和As含量均低于国家限量标准。黔产市售绿茶的重金属浸出率大小次序为Zn>Mn>Hg>As>Cd>Pb>Cr>Cu>Ni。健康风险评价结果表明,五个产地的绿茶中重金属通过饮茶途径所产生的健康危害个人年风险大小次序为Cd>As>Mn>Ni>Cr>Hg>Pb>Zn>Cu,茶叶中重金属通过饮茶途径所产生的个人健康危害年风险总和为4.33×10-6~5.73×10-6 a-1,均低于USEPA和ICRP推荐的最大可接受风险水平,表明重金属引起的健康危害极小,其对暴露人群造成的健康危害可忽略不计,绿茶中重金属均处于安全范围内。     

Uptake,Translocation, and Bioaccumulation of Elements in Forest Nettle (Laportea alatipes)

Elements found in the edible parts of plants are considered to be the main source of nutrients for humans and animals. However, there is insufficient information on the relationship between heavy metal pollution in the growing soil of most edible plants. In this study, the distribution of elements in the edible forest nettle (Laportea alatipes) was evaluated as a function of geographical location. Forest land soils had higher concentrations of minor elements (Cu, Cr, Ni, and Zn) compared to soils from rural and suburban areas. Translocation factors for Cd and Pb showed effective translocation from the roots to the leaves; however, these heavy metals in leaves were still above South African maximum permissible levels for vegetables. Atmospheric depositions may play a significant role in higher Cd and Pb concentrations in the leaves. Bioaccumulation factors showed the plant to accumulate Cu, Mn, and Zn to meet physiological requirement levels. Geoaccumulation indices and enrichment factors showed no soil contamination or minimal enrichment by trace metals. Principal component analysis showed Co, Cr, Cu, Fe, Ni, Pb, and Zn in soil to originate from a common source which may be soil silicates and other minerals.     

A review of heavy metal contaminations in urban soils, urban road dusts and agricultural soils from China

This paper reviews quite a few heavy metal contamination related studies in several cities from China over the past 10 years. The concentrations, sources, contamination levels, sample collection and analytical tools of heavy metals in urban soils, urban road dusts and agricultural soils were widely compared and discussed in this study. The results indicate that nearly all the concentrations of Cr, Ni, Cu, Pb, Zn, As, Hg and Cd are higher than their background values of soil in China. Among the cities, the contamination levels of the heavy metals vary in a large range. The geoaccumulation index shows that the contamination of Cr, Ni, Cu, Pb, Zn and Cd is widespread in urban soils and urban road dusts of the cities. Generally, the contamination levels of Cu, Pb, Zn and Cd are higher than that of Ni and Cr. Agricultural soils are also significantly influenced by Cd, Hg and Pb derived from anthropogenic activities. The integrated pollution index (IPI) indicates that the urban soils and urban road dusts of the developed cities and the industrial cities have higher contamination levels of the heavy metals. The comparison of the IPIs of heavy metals in urban soils and urban road dusts of Shanghai, Hangzhou, Guangzhou and Hongkong reveals that the contamination levels of the metals in urban road dusts are higher than that in urban soils in the cities. Moreover, the main sources of the metals in urban soils, urban road dusts and agricultural soils are also different.     

成都市农业土壤重金属污染特征初步研究

对成都市农业土壤中七种重金属元素Pb、Hg、Cr、As、Cu、Zn和Cd进行了测定和研究,并进行了潜在生态风险评价。结果表明,成都市农业土壤重金属元素含量分别为:Pb 77.27mg/kg,Hg 0.31 mg/kg,Cr 59.50 mg/kg,As 11.27 mg/kg,Cu 42.52 mg/kg,Zn 227.00 mg/kg,Cd0.36 mg/kg;重金属潜在的生态危害因子表明,Hg和Cd达到中等生态危害程度,Pb、As、Cu、Zn、Cr达到轻微生态危害;多种重金属的生态系统的潜在生态风险指数(RI)表明,成都市农业土壤生态危害级别为中等生态危害。     

Certification of the contents of some heavy metals (Cd, Cu, Hg, Ni, Pb and Zn) in three types of soils

Summary The element contents of Cd, Cu, Hg, Ni, Pb and Zn of three types of soil were certified. The preparation, homogeneity and stability are reported. The certified contents as well as values for Co, Cr, Mn and Se and for the aqua regia soluble contents Cd, Cr, Cu, Mn, Ni, Pb and Zn are given.

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Zertifizierung von Schwermetallspuren (Cd, Cu, Hg, Ni, Pb und Zn) in drei Bodenproben

Zusammenfassung In drei verschiedenen Bodenproben wurden die Elementgehalte an Cd, Cu, Hg, Ni, Pb und Zn zertifiziert. Es wird berichtet über die Bereitung, Homogenität und Stabilität. Die zertifizierten Gehalte sowie der Gehalt an Cr, Co, Mn und Se und der Gehalt an königswasserlöslichem Cd, Cr, Cu, Mn, Ni, Pb und Zn werden angegeben.

     

用植物叶片中重金属元素含量指示大气污染的研究

通过对潮州市区交通繁忙路段和对照区 (红山森林公园 )不同植物叶片重金属元素 (Pb、Cd、Cu、Zn)的含量研究 ,探讨了重金属含量与城市大气污染之间的关系。结果表明 ,植物叶片中的重金属元素富积量和大气中污染指数正相关。植物叶片的重金属元素富积量可较好和客观地指示市区大气的重金属污染状况。该研究为城市规划和环境保护提供了科学依据     

Mineral constituents of edible parasol mushroom Macrolepiota procera (Scop. ex Fr.) Sing and soils beneath its fruiting bodies collected from a rural forest area

Concentrations and interrelationships of twenty elements were studied in parasol mushroom and in the top layer of soil (0–10 cm) from the area of Kiwity (Poland). K, P, Mg, Ca, and Zn were found to be the most abundant elements in the mushroom. Higher concentrations of Fe, Mn, Na, Ni occurred in stipes then in caps, while Cd, Cr, Cu, Hg, Rb dominated in caps. Ag, Al, and Ba concentrations in caps and stipes were similar. Parasol mushroom is efficient in up-take and separation of Ag, Cd, Cu, Hg, K (in caps, the bioconcentration factor is BCF ≥ 100), Na, P, Rb (50 < BCF < 100), and Mg, Zn (BCF > 10) in its fruiting bodies, while Al, Ba, Ca, Co, Cr, Fe, Mn, Sr, and Pb are eliminated (BCF < 1). Parasol mushroom from rural forest area in the north-eastern region of Poland is of hygienic concern for human health because of toxic mercury and cadmium content in the edible caps, which are also rich in essential Cu, Fe, and their K, Mn, and Zn content is also high.     

Assessment of the health of a river ecosystem due to the impact of pollution from industrial discharge using instrumental neutron activation analysis and inductively coupled plasma-mass spectrometry

Inductively coupled plasma-mass spectrometry (ICP-MS) and neutron activation analysis (NAA) were employed in the determination of heavy metal concentrations in water, plant and sediment samples to assess the extent of heavy metal pollution in a river system which is located within an industrial zone. Elemental concentrations of As, Pb, Hg, Cr, Cu, Cd, Ni and Zn were measured in the samples. Statistical analysis was performed on the data obtained to look for trends in the pollution pattern of these elements on the river system. The trend in concentrations of heavy metals pollution in water samples is in the order of Zn > Cu > Ni > Cr > As > Pb > Hg > Cd, whereas in plants the order is Zn > Cr > Cu > Pb > Ni > As > Hg > Cd and in sediments Zn > Cu > Pb > Ni > As > Hg.