贵阳花溪区石灰土林地土壤重金属含量特征及其污染评价

选取贵阳市花溪区典型石灰土林地土壤作为研究对象,分析了林地石灰岩和土壤中7种重金属(Cu、Zn、Mn、Cd、Ni、Pb、Co)的含量特征,以贵州省土壤背景值和全国石灰(岩)土类背景值为评价标准进行林地土壤重金属污染评价和潜在生态风险评价.结果表明:林地石灰岩以Pb的平均含量(40.21mg·kg-1)最高,Zn的(5.78 mg·kg-1)最低,7种重金属平均含量高低顺序为:Pb＞Ni＞Mn＞Co＞Cu＞Cd＞Zn;林地土壤中以Mn的平均含量(451.16 mg·kg-1以上)最高,Cd的(2.87mg·kg-1以下)最低,7种重金属含量的变异系数在8.57%～63.10%之间,Zn的平均含量明显低于贵州省土壤背景值和全国石灰(岩)土类背景值,Cu、Mn、Cd、Pb、Ni、Co的平均含量高于或接近于贵州省土壤背景值和全国石灰(岩)土类背景值.Cu、Zn、Mn、Ni、Co,Ni与Pb,Cd与Pb,Cd与Co来源相同的可能性较大,而Cd与Cu、Ni,Pb与Mn、Cu、Co的来源不同;石灰土偏碱性,富含Ca、Mg元素,有利于重金属Cd、Pb的累积.单因子污染指数和多因子综合指数(内梅罗指数法)与Hakanson潜在生态危害指数的评价结果一致,林地土壤重金属综合污染指数在3.67以上,达到重污染程度,以Cd的污染指数(4.94以上)最高,污染程度最为严重,其次是Pb(1.82以上),Zn、Mn污染程度最低,林地土壤重金属潜在生态危害指数(RI)为173.75以上,为中度生态危害程度,产生最大生态危害的是Cd,其次是Pb、Ni、Co、Cu,危害程度最小的是Mn、Zn,在相同的成土母岩和人为活动影响下,无林地土壤重金属的综合污染指数和潜在生态危害指数均明显高于有林地.     

山东省部分水岸带土壤重金属含量及污染评价

为了解山东省水岸带土壤重金属的含量特征和污染状况,于2010年9月—10月采集了39个水岸带土壤样品,分析了土壤中Cr、Co、Ni、Cu、Zn、Cd、Pb和Hg的含量以及土壤的pH值、粒度和有机质,采用单因子指数法、综合指数法和潜在生态危害指数法对水岸带土壤重金属污染进行了评价,并利用相关分析和聚类分析对其来源进行了初步的解析。结果表明：水岸带土壤的pH值为5.67—8.66,主要呈碱性;有机质的平均含量为9.39 g/kg,土壤粒度主要以砂粒和粉粒为主,其平均体积百分比分别为50.33%和38.48%,平均粒径为89.69 μm;Cr、Co、Ni、Cu、Zn、Cd、Pb和Hg的平均含量为53.03 mg/kg、10.33 mg/kg、24.96 mg/kg、18.38 mg/kg、56.13 mg/kg、0.142 mg/kg、22.48 mg/kg和0.020 mg/kg。各水岸带土壤重金属的含量均符合《土壤环境质量标准》（GB15618-1995）二级标准。以山东省土壤元素背景值为评价标准,水岸带土壤重金属总体表现为轻度污染和轻微生态风险,其中Cd和Hg是主要的污染因子,其对潜在生态危害指数的平均贡献率分别为46.8% 和33.6%。洙赵新河、廖河、门楼水库和东平湖水岸带土壤重金属污染及潜在生态危害明显高于其他水源地。源解析的结果表明：水岸带土壤重金属的含量受自然源和人为源的双重影响,人为源主要包括地表径流、工业废气、垃圾和交通运输等。     

Heavy metal pollution in aquatic ecosystems and its phytoremediation using wetland plants: an ecosustainable approach

This review addresses the global problem of heavymetal pollution originating from increased industrialization and urbanization and its amelioration by using wetland plants both in a microcosm as well as natural/field condition. Heavymetal contamination in aquatic ecosystems due to discharge of industrial effluents may pose a serious threat to human health. Alkaline precipitation, ion exchange columns, electrochemical removal, filtration, and membrane technologies are the currently available technologies for heavy metal removal. These conventional technologies are not economical and may produce adverse impacts on aquatic ecosystems. Phytoremediation of metals is a cost-effective "green" technology based on the use of specially selected metal-accumulating plants to remove toxic metals from soils and water. Wetland plants are important tools for heavy metal removal. The Ramsar convention, one of the earlier modern global conservation treaties, was adopted at Ramsar, Iran, in 1971 and became effective in 1975. This convention emphasized the wise use of wetlands and their resources. This review mentions salient features of wetland ecosystems, their vegetation component, and the pros and cons involved in heavy metal removal. Wetland plants are preferred over other bio-agents due to their low cost, frequent abundance in aquatic ecosystems, and easy handling. The extensive rhizosphere of wetland plants provides an enriched culture zone for the microbes involved in degradation. The wetland sediment zone provides reducing conditions that are conducive to the metal removal pathway. Constructed wetlands proved to be effective for the abatement of heavymetal pollution from acid mine drainage; landfill leachate; thermal power; and municipal, agricultural, refinery, and chlor-alkali effluent. the physicochemical properties of wetlands provide many positive attributes for remediating heavy metals. Typha, Phragmites, Eichhornia, Azolla, Lemna, and other aquatic macrophytes are some of the potent wetland plants for heavy metal removal. Biomass disposal problem and seasonal growth of aquatic macrophytes are some limitations in the transfer of phytoremediation technology from the laboratory to the field. However, the disposed biomass of macrophytes may be used for various fruitful applications. An ecosustainable model has been developed through the author's various works, which may ameliorate some of the limitations. The creation of more areas for phytoremediation may also aid in wetlands conservation. Genetic engineering and biodiversity prospecting of endangered wetland plants are important future prospects in this regard.     

桂北典型锰矿区周边土壤重金属污染状况及主要植物富集特征

为探究桂北某典型锰矿尾库区周边土壤和农作物重金属污染状况,筛选适合该地区污染土壤修复的植物材料,该研究在矿区周边采集了9种农作物和23种主要植物及其根际土壤,并测定了Cd、Mn、Cr、Pb和Zn 5种重金属含量,采用单因子污染指数法和综合污染指数法评价了矿区农田土壤、农作物中重金属的生态风险,通过计算植物对重金属的富集和转运系数评估其应用潜力。结果表明:(1)研究区土壤Cd、Mn污染最为严重,单因子污染指数分别为18.53、147.09,达到重度污染级别。(2)研究区花生和小白菜等作物可食用部位中的Cd、Cr、Pb含量均超过食品国家安全标准(GB 2762—2017)中的阈值,具有较高健康风险。(3)23种主要植物中青葙、鬼针草、一点红、蜈蚣草等对多种重金属转运系数大于1,具备富集型植物特征; 一把伞南星、蓖麻、千里光等根部重金属含量较高,转运系数较低,具备根部囤积型植物特征; 响铃豆、筒轴茅、苣荬菜等富集的重金属含量相对较低,且在重金属污染土壤中能健康生长,具备规避型植物特征。该研究结果表明,研究区土壤存在较严重的Cd/Mn复合污染,青葙等植物用于修复该复合污染土壤极具应用潜力。     

Heavy metal pollution assessment and soil property evolution under a natural ecological restoration process in a manganese wasteland in China

The space-for-time method was used to track changes in heavy metals (HMs), selected physicochemical properties and soil enzyme activities at different restoration ages, that is 5, 10, and 25 years (named R5, R10, and R25, respectively) and in a natural forest (NF, age > 100 years, as the control) in the Daxin manganese (Mn) wastelands in China. The results showed that the HM concentrations decreased over time, with Mn exhibiting the highest concentration, followed by zinc, copper, and cadmium; all the studied sites exhibited heavy pollution levels based on the Nemerow multifactor index, with a very high potential ecological risk (RI) level in R5, moderate RI in R10 and R25, and low RI in NF; generally speaking, the soil physicochemical properties improved, with the exceptions of the available phosphorus (AP) and calcium (Ca) levels; the soil enzymes generally exhibited the highest activities in R25, while the activity of catalase showed a significant (p < 0.05) decrease over time; both the HM concentrations and physicochemical properties showed significant correlations with soil enzyme activities; redundancy analysis showed that soil pH and HM species should be given more attention in R5 for vegetation recovery; and the HM concentrations, soil moisture content, and ammonium nitrogen, total nitrogen, potassium, and magnesium levels might be the limiting factors for plant colonization in early restoration periods, while the AP, total phosphorus, and Ca levels might be the limiting factors in later restoration periods. The obtained results will provide guidance for the restoration of abandoned Mn-polluted areas.     

Heavy metal surveys in sediments of five important Cuban bays

This paper presents data obtained between 1983 and 1989 on concentration of heavy metals in sediments of five Cuban bays having different physical and geographical characteristics and differing degrees of anthropogenic activities. Data are normalized with respect to Al, Fe, and organic content and processed through statistical techniques of multivariate analysis. The degree of heavy metal pollution among the harbors decreases in the following order: Havana, Santiago de Cuba, Cienfuegos Matanzas, Cárdenas     

广西锰矿恢复区食用农作物重金属污染评价

对广西平乐、荔浦两锰矿恢复区种植的食用农作物进行了调查和重金属含量分析.结果表明:两锰矿区农作物Zn、Pb、Cr、Cu和Cd的含量范围分别在1.18~20.46、0.52~16.16、0.33~6.62、0.01~6.24和0.01~2.76mg.kg-1之间.其中,豆类作物中的重金属含量最高,其次是薯类.单因子污染指数评价表明,农作物基本未受Zn、Cu污染,但受Pb、Cd和Cr污染严重,以Pb污染最重,受污染率达100%,Cr和Cd受污染率分别为96.9%和75.0%;从综合污染指数来看,农作物受污染率达100%,其中,重、中、轻污染分别占87.5%、9.4%和3.1%.表明在锰矿废弃地直接种植食用农作物存在较大风险,应重新考虑其恢复利用模式.     

重金属复合污染对大豆生长的影响及其综合评价研究

通过正交试验设计研究了溶液培养条件下Ｃｄ、Ｐｈ、Ｃｕ、Ｚｎ、Ａｓ复合污染对大豆幼苗生长的影响．结果表明,复合污染条件下,各元素在根中的积累顺序为ＡＳ＞Ｐｂ＞Ｃｕ＞Ｃｄ＞Ｚｎ,茎叶中为Ｃｄ＞Ｃｕ＞Ｚｎ＞Ａｓ＞Ｐｈ,其交互作用类型决定于元素的投加浓度及其与共存元素的比例,而对其生长发育,ＡＳ和ＣＵ是主要的毒害元素,并指出相对离子强度是复合污染综合效应指示与控制的又一有效指标．     

不同重金属污染水平下生物结皮及下层土壤细菌群落的差异性分析

为了探究生物结皮及下层土壤细菌群落多样性及结构在不同重金属污染水平下的差异及其影响因素,以宁夏东部工矿区和封育草地内广泛分布的两类生物结皮为研究对象,采用高通量测序技术,分析结皮层(A层)和结皮下层(B层)土壤细菌群落结构和多样性差异。采用相关分析、冗余分析探讨两个生境生物结皮各层次细菌群落与土壤环境因子的关系。结果表明：(1)相较于封育区,工矿区2类生物结皮对源自大气降尘的重金属元素具有更显著的表层富集作用,并表现出显著的种间差异：苔藓结皮>藻结皮。污染负荷指数评价结果显示：工矿区生物结皮各层次重金属污染程度更高,且均表现为A层污染程度高于B层。(2)两个生境的优势细菌门组成基本一致,均为放线菌门、变形菌门、酸杆菌门。受生物结皮类型、重金属污染程度的影响,细菌群落结构差异显著,主要表现为：工矿区藻结皮A、B层的α多样性指数均大于封育区,而苔藓结皮A、B层的细菌多样性指数高于封育区,丰富度指数低于封育区。主坐标分析结果显示,不同生境的生物结皮细菌群落结构差异明显,而同一生境的生物结皮细菌群落结构相似。重金属As、Pb、土壤黏粒含量和pH是影响生物结皮细菌群落结构的主要土壤环境因子...     

Heavy metals in Lake George, Uganda, with relation to metal concentrations in tissues of common fish species

The northern end of Lake George, Uganda, and its associated wetlands receive localized metal pollution from a former copper mine and tailings left after metal extraction. The aim of this study was to determine (i) whether the heavy metals are a threat to the biology of the major commercial fish species and (ii) whether consumption of the fish threatens human health. Concentrations of copper, zinc, cobalt and nickel in detrital sediments, plankton, and five fish species from sites in Lake George, the Kazinga Channel and Lake Edward (which are inter-connected) were determined using atomic absorption spectroscopy. The detrital sediments of Hamukungu Bay, Lake George, had average concentrations (g/g dry weight) of 96.3 zinc, 270.4 copper, 57.4 cobalt and 42.8 nickel. There were no significant differences between the Hamukungu Bay and the North Lake George site of Bushatu: both receive inflows from the mining activities. Concentrations of copper and zinc were significantly higher than background values from unpolluted freshwater ecosystems. Plankton samples showed a metal concentration gradient consistent with a gradient from the source of pollution in northern Lake George, along the Kazinga Channel to Lake Edward. The liver tissues of fish had markedly higher concentrations of copper and zinc than flesh. Concentrations of cobalt and nickel were relatively low. The highest mean concentrations of metals in liver tissue occurred in Oreochromis leucostictus (189.0 g/g Cu) and Bagrus docmac (187.5 g/g Zn) whilst the lowest occurred in Oreochromis niloticus (15.3 g/g and 78.2 g/g dry weight copper and zinc, respectively). However, O. niloticus contained the highest concentrations of cobalt (11.2 g/g) and nickel (3.8 g/g). Liver Somatic Indices (LSI) of the fish species from the different sites indicated a reduction of LSI in those fish from the most contaminated zones of northern Lake George compared with all other sites. This suggests there could be anatomical and physiological abnormalities linked to the heavy metal pollution. The flesh had only low concentrations of metals; well within international guidelines for consumption. A person would have to consume 9 kg of fresh flesh of Clarias sp. and 65 kg of O. leucostictus daily to exceed the WHO recommended intake for copper, and even more for other metals. This implies that currently metal pollution in Lake George presents an ecological rather than a human health concern.     

不同起源秋茄林湿地沉积物重金属污染与健康风险评价

秋茄(Kandelia obovata)林生态系统的重金属污染是滨海湿地研究的重要组成.为探究闽东不同起源秋茄林湿地的健康风险与重金属污染的状况,运用污染负荷指数法和人体健康风险评价法分析闽东不同起源秋茄林湿地表层沉积物重金属的含量特征并评估其健康风险.结果表明:(1)秋茄天然林湿地表层沉积物重金属平均含量排序为Zn(...     

Effect of an artificial metal pollution on nematode assemblage of a calcareous loamy chernozem soil

Heavy metal pollution in soils constitutes an acute problem threatening various groups of living organisms. Nematode samples were taken in the framework of a complex food-chain experiment which is being carried out after artificially contaminating a part of an agrobiotope. The 13 heavy metals and microelements involved in the study are the following: Al, As, Ba, Cd, Cr, Cu, Hg, Mo, Ni, Pb, Se, Sr, and Zn. Parallel plots receiving maximum concentrations equal to approx. 270 ppm were sampled twice during a complete vegetation period of winter wheat. Nematode abundance and richness as well as Maturity Index data revealed that Se and Cr had significantly negative effects on assemblages, while Zn appeared to have a generally positive influence on these parameters. Impacts by the other elements are less obvious or quite neutral (like that of Al). Favorable soil conditions and time elapsed (over 5 years) since the contamination, both resulting in a decrease of available element concentrations, may account for the not very pronounced effects. This revised version was published online in June 2006 with corrections to the Cover Date.     

环境重金属污染物的生物有效性

利用生态系统研究了白银有色金属冶炼矿区周围环境中重金属的分布及生物有效性。结果表明 ,工厂在冶炼过程中已造成 Pb、Cd、Cu、Zn对周围环境不同程度的污染 ,其含量与距工厂的距离呈负相关 ;重金属在各种生物体内均有不同程度的吸收和累积 ,其吸收累积量随重金属和生物种类的不同而有差异 ;土壤的污染 ,使农作物和牧草中 Pb、Cd含量超过动物的最大耐受量和中毒的临界值 ;动物研究发现 ,肾脏、骨骼和肝脏是机体内重金属蓄积的主要器官。因此 ,放牧动物可作为环境重金属污染状况的标识 ,对评价重金属环境污染对当地人群的危害也有重要意义     

河岸带土壤重金属元素的污染及危害评价

测定了金水河流域河岸带土壤部分重金属的全量和土壤水溶液的离子含量,运用污染指数和生态风险评价法对流域内土壤重金属进行评价.不同土地利用类型中,漫滩V、Cr含量最高(130.89、363.29 mg·kg-1),草地Ni、Pb、Ti、Mn、Zn、Cu含量最高(32.52、24.61、4378.09、1289.62、91.44、29.71 mg·kg-1).这主要是因为草地、漫滩能够有效吸附和沉积重金属,同时人类活动明显增加重金属生态危害.金水河流域河岸带土壤Cr、Pb、Zn均超过土壤环境质量标准(GB 15618-1995).与此同时,河漫滩白浆化棕壤和钙质粗骨土碳酸钙含量高,对Pb、Zn有较强的吸附和固定作用,能够有效吸附和沉积重金属;河漫滩人类干扰较重,造成其重金属含量较高.评价结果表明,流域河岸带内重金属环境污染达到中、重度污染,生态危害等级为轻微到中等级别.提高土壤腐殖质含量是减轻污染危害及增强土壤自净能力的重要措施.     

Vanadium as a tracer of oil pollution in the sediments of Kuwait

Vanadium is important as an indicator of oil pollution since oil is one of the main contributors of vanadium to the environment and because most crude oils contain relatively high concentrations of vanadium (30.6 ± 14.3 mg kg^–1 were measured in nine different Kuwait crudes). If oil has settled to the bottom and biodegradation has taken place, it is obvious that enrichment of vanadium in the sediment may be observed.More than 200 sampling sites were selected in the coastal zone of Kuwait and sediment samples were analyzed for grain size distribution, CaC0₃ content, heavy metals and TOC. The analytical results were normalized by taking into account the natural background levels of vanadium in different sediment fractions.After evaluation of the results, vanadium enrichments of as much as 10 to 77 mg kg^–1 were found at 15 sampling locations and of 1 to 10 mg kg^–1 at many others. The areas of vanadium enrichment in the sediments were located 3–5 km from the shoreline in the areas of wastewater discharges, near oil loading piers and in the shipping channels. There was no correlation between vanadium and TOC indicating that biodegradation of oils had taken place. However, high TOC values in the sediments were determined in the near shore sediments around the outlets.     

The response of macroinvertebrate production to a pollution gradient in a headwater stream

1. This study quantified patterns of macroinvertebrate secondary production and stored benthic organic matter along a gradient of pollution and habitat channelisation over a 3‐km reach of Goosefare Brook, a first‐order stream in southern Maine (U.S.A.). 2. Whole‐community invertebrate production decreased from 26.4 g ash‐free dry mass (AFDM) m⁻² year⁻¹ at the reference station to 1.1 g AFDM m⁻² year⁻¹ at stations with the greatest levels of pollution. Production decreased along the pollution gradient for most taxa, although decreases were partly offset by production increases in tolerant taxa. Biomass turnover rates (P/B) were less affected by the stresses than was production. 3. Differences in functional characteristics of the community were evident at stations with channelised habitat, but overall production declined in a linear pattern that mirrored the pollution gradient. Stored organic matter showed a decline along the gradient, but was also lower at channelised stations. Populations of taxa with documented pollution tolerance were more likely to maintain or increase production and P/B. 4. Decreasing biomass because of decreasing stored organic matter and lethal effects of pollutants resulted in shifts in the pathways of energy flow observed at stations exposed to moderate physical or chemical stress, to the loss of most taxa and an extreme (96%) decrease in production at the stations receiving the highest levels of metal pollution. 5. The shifting prominence of different taxa along a continuum of stress in Goosefare Brook shows that describing the nature of an impairment in a functional context requires consideration of chemical stressors, habitat alterations and food resources.     

Heavy metal pollution negatively correlates with anuran species richness and distribution in south‐eastern Australia

Heavy metal pollution has likely played an important role in global biodiversity decline, but there remains a paucity of information concerning the effects of metals on amphibian diversity. This study assessed anuran species richness and distribution in relation to sediment metal content and water chemistry in wetlands located along the Merri Creek corridor in Victoria, south‐eastern Australia. Anurans were present in 60% (21/35) of study sites, with a total of six species detected: the eastern common froglet (Crinia signifera), the eastern sign‐bearing froglet (Crinia parinsignifera), the southern brown tree frog (Litoria ewingii), the growling grass frog (Litoria raniformis), the eastern banjo frog (Limnodynastes dumerilii) and the spotted marsh frog (Limnodynastes tasmaniensis). Mean species richness was 1.77 ± 0.32 per site, and species richness ranged from zero to six species per site. Across sites, species richness correlated negatively with sediment concentrations of six heavy metals: copper, nickel, lead, zinc, cadmium and mercury. Species richness also correlated negatively with wetland water electrical conductivity (a proxy for salinity) and concentrations of orthophosphate. Distributions of the three most commonly observed frog species (C. signifera, L. tasmaniensis and L. ewingii) were significantly negatively associated with the total level of metal contamination at individual sites. The study is the first to provide evidence for an association between metal contamination and anuran species richness and distribution in the southern hemisphere, adding to a small but growing body of evidence that heavy metal pollution has contributed to global amphibian decline.     

重金属污染生态学研究现状与展望

重金属污染生态学的研究迄今已有近 5 0 a的历史 ,在土壤重金属元素背景值和环境标准的制定、重金属在环境中的迁移转化、重金属污染治理、元素分析测定方法和规范、对生物体的毒性及生物体的响应等方面取得了很多研究成果 ,出版了很多专著。在对重金属污染生态学研究进行简要回顾的基础上 ,以重金属在生物体内的行为特征 (吸收、迁移、富集、毒害、解毒和抗性等 )为主线 ,从微观和宏观水平 ,系统综述了目前该领域的研究现状 ,分析了尚存在的一些问题 ,最后从生物对重金属污染适应的分子机理、治理方法和技术的创新性、复合污染下环境标准制定的科学化以及重金属污染条件下全球生物进化的趋势预测等方面作了研究展望     

Heavy metal intracellular balance and relationship with metallothionein induction in the liver of carp after contamination by silver,cadmium and mercury following or not pretreatment by zinc

Determination of metal levels (copper, zinc, cadmium, silver and mercury) in soluble and insoluble fractions of liver homogenates has been performed after 7 days exposure of carps (Cyprinus carpio) to moderate concentrations of cadmium, silver and mercury in water. Metallothionein (MT) levels have been quantified by a polarographic method before and after the contamination and a subsequent decontamination phase (7 days). The influence of pretreatment by zinc (7 days) has also been evaluated. MT level variations have been interpreted as having regard to inter-related flows of metal between subcellular fractions. Special interest has been focused on heat-stable compound (HSC)-bound heavy metal flows within the cytosol, taking in account that MT is the major component of these ligands. Our data showed differences between the ability of metals to bind cytosolic ligands and HSCs, and their respective potency for MT induction in liver. Regardless of pretreatment, mercury gave the highest increase of liver MT, but the MT level decreased during the decontamination step, especially after pretreatment by zinc. Cadmium and silver gave similar increases, but a significant difference with the control appeared only after the decontamination step with cadmium, while 1 week of contamintion was enough for silver. However, silver binding with MT was achieved only by the end of the decontamination step, while cadmium depicted the highest ratio for HSC-bound toxic metals after the contamination. Our experimental conditions gave the following order of potency for MT induction in liver: mercury silver > cadmium > zinc. Results are discussed comparatively with data obtained with carp gills.     

春玉米与生姜间作不同种植方式农田生态效应研究

春玉米与生姜间作不同种植方式农田生态效应研究姚向高王爱玲（河南农业大学农学院,郑州４５０００２）ＳｔｕｄｙｏｆｔｈｅＥｃｏｌｏｇｉｃａｌＥｆｃｃｔｓｏｆＤｉｆｅｒｅｎｔＴｒｅａｔｍｅｎｔｏｆＩｎｔｅｒｃｒｏｐｐｉｎｇｏｆＳｐｒｉｎｇＭａｉｚｅａｎｄ...