藏中矿区重金属污染对土壤微生物学特性的影响

土壤微生物对土壤重金属污染反应敏感,是探讨矿区土壤重金属污染生态效应的有效指标之一。通过野外调查与采样和室内分析,研究了藏中矿区重金属污染对土壤蔗糖酶、脲酶、脱氢酶和酸性磷酸酶活性、微生物生物量C（MBC）、N（MBN）和P（MBP）、土壤基础呼吸、代谢商（qCO2）及可矿化N的影响。研究表明,矿区土壤重金属Cu、Zn、Pb、Cd全量和有效含量均高于对照土壤;随着矿区土壤重金属含量增加,土壤酶活性、微生物量C、N和P、可矿化N均逐渐降低,土壤基础呼吸和qCO2则逐渐升高;土壤重金属与土壤蔗糖酶活性、脲酶活性、脱氢酶活性、酸性磷酸酶活性、MBC、MBN、土壤基础呼吸、qCO2及可矿化N具有显著的线性相关;脱氢酶活性对土壤重金属污染最为敏感,表明脱氢酶活性可作为藏中矿区土壤环境质量变化的有效指标。     

采煤沉陷区土壤重金属含量对土壤酶活性的影响

为探明煤矿沉陷区土壤受重金属污染情况,探讨重金属含量对酶活性的影响,以焦作韩王煤矿沉陷区为例,通过野外调查与采样和室内分析,研究煤矿沉陷区土壤中重金属累积特性与土壤酶活性的变化。结果表明:研究区土壤中重金属Cu、Zn、As、Mo、Hg、Pb、Cd等含量均高于对照小区的含量,且有明显的空间异质性;沉陷区各种酶活性大都低于对照点,其在空间分布上受重金属的影响,重金属Co、Ni对大多数酶有促进作用,As、Mo则对酶活性有抑制作用,重金属对酶活性的影响取决于重金属的类型与含量;在研究区,蔗糖酶对重金属污染较为敏感,表明蔗糖酶可作为评估煤矿沉陷区土壤环境质量变化的有效指标。     

Lysosomal Fragility in Earthworms (Eisenia Veneta) Exposed to Heavy Metal Contaminated Soils from Two Abandoned Pyrite Ore Mines in Southern Norway

In this study we have investigated the toxicity of soils from thetwo abandoned pyrite mines Ertelien and Konnerud in the southernpart of Norway. Soil samples were collected close to the pitheadof the mines, and earthworms were exposed to different concentrations of the contaminated mine soil mixed with commercial plant soil for a period of 14 days. Life-cycle responses such as growth and survival, as well as the biomarkerresponse lysosomal fragility were measured. The body burdens ofthe four heavy metals Cu, Cd, Zn and Pb were detected in the worms, and the body concentration of the metals generally increased with increasing heavy metal concentration in the soil.The growth and mortality of the earthworms were not influenced when exposed to any of the mine soil concentrations used. The lysosomal fragility of the earthworm coelomocytes measured by the neutral red retention time (NRR-time) was found to be markedly reduced in all the exposed earthworms. This assay seemsto be a sensitive and dose dependent endpoint for the toxicity assessment of heavy metal mixtures in pyrite mine soils.     

金属矿山水土流失防治中植物措施的特殊作用

金属矿山在开采过程中对矿区及周围的生态环境造成了较为严重的重金属污染.因此,在金属矿区开展重金属污染治理对于减轻重金属危害、确保农作物安全生产、保障人民健康,具有长远而重大的意义.笔者就植物措施在金属矿山水土流失防治中的特殊作用作一简要概括,对金属矿山植物措施防治水土流失的现状、植物修复技术的特点、超富集植物的筛选方法及筛选成果、影响植物措施在金属矿山水土流失防治中发挥特殊作用的因素等作了介绍,以期能为金属矿山的生态环境治理提供参考.     

新疆准东煤田土壤重金属来源分析及风险评价

为研究准东矿区土壤重金属来源及生态风险,分析了阜康市至准东矿区中间的3个缓冲区共27个土壤样方的As,Hg,Pb,Cr,Cu,Zn元素重金属含量状况,并利用因子分析、污染指数法、地累积指数法和潜在生态风险指数法对各缓冲区土壤重金属进行了污染来源及风险分析。结果表明:除Cr的总体平均值高于新疆土壤背景值外,其余重金属含量均低于背景值。基于土壤重金属空间分布图显示,除Cu,Hg含量高值分布于C区域土壤外,其余重金属高值均出现在准东矿区(A区域)附近土壤,3个区域各重金属所占比例基本一致,距离矿区越远,变异系数呈减少趋势;污染源分析可知,准东矿区89.3%的Hg来源于煤炭燃烧,40.1%的Pb来源于交通运输,19.65%的As来源于大气降尘,Cu和Cr的主要来源为煤尘,其贡献率分别为60.23%和81.57%,其中29.7%的Cu来源于土壤母质,75.1%的Zn来源于土壤母质;基于污染指数法、地累积指数法和潜在生态危害指数法对不同缓冲区土壤污染风险进行了评价,得出土壤整体呈轻度-中度污染水平,距离矿区越远重金属污染状况越轻。As,Hg,Pb和Cr元素生态风险均呈现缓冲区区域A区域B区域C的趋势,距离矿区越远,生态风险越低。潜在生态风险指数与重金属单因子生态风险的大小顺序一致。     

Response of microbial characteristics to heavy metal pollution of mining soils in central Tibet,China

Soil microbial activity plays a crucial role in soil microbiological processes, which can be used as a useful indicator to determine the ecological effects of heavy metal pollution on soils. The objective was to determine the effects of heavy metal pollution on mining soils at the Lawu mine of central Tibet, China on soil enzyme activities (sucrase, urease and acid phosphatase), microbial biomass C, N and P (MBC, MBN, and MBP), basal respiration, metabolic quotients, and N mineralization. Sixteen soil samples around the mine were sampled, and one soil sample, 2 km from the mine center, was taken as the control. Compared to the control, mining soils were polluted by heavy metals, Cu, Zn, Pb and Cd, resulting in decreases of sucrase activities, urease activities, acid phosphatase activities, MBC, MBN, MBP, and N mineralization, and increases of basal respiration and qCO₂. Multivariate analysis (cluster analysis [CA], principle component analysis [PCA] and canonical correlation analysis [CCA]) indicated nine microbial variables were only reduced to one principal component explaining 72% of the original variances, and MBC (R² = 0.93) had the highest positive loadings on the principal component. Mining soils polluted by heavy metals were perfectly clustered into four groups, which were highly distinguished by MBC. There were significant canonical correlations between soil heavy metals and microbial indexes on two canonical variates (R1 = 0.99, p < 0.001; R2 = 0.97, p < 0.01), which further demonstrated significant correlations between soil heavy metal contents and microbial characteristics. Hence, our results suggested that MBC may be used a sensitive indicator for assessing changes in soil environmental quality in metal mine of central Tibet.     

Comparisons of metal accumulation and excretion kinetics in earthworms (Eisenia fetida) exposed to contaminated field and laboratory soils

The uptake and excretion kinetics of cadmium, copper, lead and zinc were studied for Eisenia fetida exposed to mixtures of these metals in field and OECD artificial soil. Body burdens in worms exposed to all contaminated soils increased over the duration of the experiment. Highest accumulation rates were for worms exposed to the most polluted soils. Pronounced differences were found in the uptake and excretion patterns for essential and non-essential elements (particularly in field soils). For cadmium and lead (non-essential), an equilibrium plateau was not reached during the uptake study and slow excretion was found on transfer of worms to clean soil. For copper and zinc (essential), fast initial uptake was followed by equilibrium after only a few days exposure. Rapid excretion was found after transfer to clean soil, with half-lives of less than 1 day for both metals. A previous study of the effects of metals on worms exposed in OECD and field soils had indicated a higher toxicity in the artificial medium. Thus, in the present study, it was anticipated that greater toxicity would be reflected by increased body burdens for worms in OECD soil. This was, however, not the case. Explanations are given that might account for the fact that the greater toxicity in OECD soil is not invariably accompanied by higher metal burdens. These include the presence of high concentrations of very toxic and highly available ions in laboratory tests and potential differences in the importance of soluble and total metal concentration for determining toxicity and body burdens.     

Heavy metals and soil microbes

The discovery in the early 1980s that soil microorganisms, and in particular the symbiotic bacteria Rhizobium, were highly sensitive to heavy metals initiated a new line of research. This has given us important insights into a range of topics: ecotoxicology, bioavailability of heavy metals, the role of soil biodiversity, and the existence of ‘keystone’ organisms. Concurrently, and particularly in Europe, the research led to new approaches to the protection of soils from pollution that take into account the many effects on soil microorganisms. To date these key findings have largely been ignored in the USA, although our results caused considerable controversy there. In the past decade there have been many advances in the ecotoxicological assessment of metals and their effects on soil organisms but major gaps in knowledge and theory remain with regard to how microorganisms are exposed and respond to metals in soils. In this brief review we emphasise the need for long-term experiments and basic research to forge this understanding and improve environmental protection policies.     

Untersuchungen über die toxische Wirkung der in Siedlungsabfällen häufigen Schwermetalle auf die Bodenmikroflora

The toxic effects of heavy metals, commonly found in urban wastes on the soil microflora In several series the influence of soluble salts of Cd, Cr, Zn, Cu, Ni and Hg in various concentrations was tested on the development of bacteria and fungi in cultural studies and in soil model systems. In addition the changes in microbial biomass, in the activity of oxidoreductases and hydrolases, and in nitrification were measured in five soils. Comparison of the results of bacteria-plate-counts in the presence of heavy metals in agar-media and in soils demonstrated that all tested elements have a more toxic effect on isolated soil microorganisms under culture conditions than when tested after heavy metal application to soils. Beside Hg, eucaryotic soil fungi proved to be 10 – 50 fold more resistant to heavy metals in vitro as well as in situ. For calculating the effect of heavy metals on soil microbial activity soil enzymatic methods are not reliable and can be used only to some extent, because some cellfree encymes in the soil are activated or inactivated immediately by heavy metals. In long-term experiments, the microbial biomass and nitrification in soil is not significantly influenced by the elements Cd, Cu and Ni in the concentration range of the tolerable limit content. In contrast, Cr, Zn and Hg reduced these microbiological properties more or less distinctly.     

Treatment of Acid Mine Drainage by Sulphate-reducing Bacteria Using Low Cost Matrices

This paper reports a laboratory-scale investigation concerning the use of sulphate-reducing bacteria (SRB) in a semi-continuous process, where column packed-bed type bioreactors were used for the treatment of acid mine drainage (AMD). The use of different materials as solid matrices was tested and the performance of the bioremediation processes was discussed in terms of sulphate and metals removal and acid neutralization. The behaviour of a reactor filled with acidic soil from a mining area and organic wastes was compared with other three reactors where coarse sand, glass spheres and cereal straw were used as packaging materials. Batch experiments showed the presence and growth of SRB from the acidic soil in different pH conditions and the effect of the absence or presence of several added carbon sources: lactate, ethanol and lactose. The data showed that it is possible to grow SRB using the acidic soil as source of inocula, in the absence and in the presence of the carbon sources tested, since the pH of the media was previously increased to values of 5 or higher. When acidic soil from the mining area and organic wastes were utilised as column matrices, it is possible to remove the metals and to neutralise the acidity of AMD, although an inefficient sulphate removal was observed. When coarse sand or glass spheres were utilised, efficient metals sulphate removal were achieved. However, the incapacity of both systems to generate enough alkalinity does not allow maintaining their good performances in terms of iron removal and sulphate reduction. As a result, the incorporation of materials with neutralizing and buffer capacity to the matrix is recommended. Due to its low density, cereal straw was not suitable to obtain an anaerobic environment inside the column for SRB activity.     

Heavy metal contamination of soils in a mining area in South Africa and its impact on some biotic systems

In soils, animals and plants from selected sites in the Rustenburg mining area, a part of the South African ore belt, the heavy metal burden was examined. These sites belong to different soil types and are characterized by different land-use (agriculture, grassland). The heavy metal contamination of the soil samples is relatively high and is dominated by chromium and nickel, metals, which are extracted in the mine near the sampling sites. These high heavy metal concentrations had no clear inhibitory influence on micro-organisms or the enzyme activity of soils. It appears that the high clay content of the soils may counteract the influence of heavy metals. On the other hand, tolerant microbial populations may have been established. In addition, the investigated culture plants there was no correlation between the heavy metal content of the soils and the concentrations in roots and shoots. The dangerous, potential contamination of organs in humans seems to be modest, with the exception of tobacco leaves. The heavy metal content of tissues in the examined animals reflect the environmental habitat in situ with no obvious influence on the health of the animals.     

C and N mineralization and microbial biomass in heavy-metal contaminated soil

Heavy metals such as arsenic (As), lead (Pb), copper (Cu) and zinc (Zn) can be found in large concentrations in mine spills in Mexico. Interest in contamination by these heavy metals has increased recently as they can change the functioning of soil ecosystems qualitatively and quantitatively. They disturb the activities of soil fauna and contaminate drinking water in large parts of the world, which severely affects human health. Little, however, is known how heavy metals might affect the biological functioning of a soil. Soil was sampled from eight locations along a gradient of heavy-metal contamination with distance from a mine in San Luis Potosí (Mexico) active since about 1800 AD. Microbial biomass was determined with the original chloroform fumigation incubation (CFI) as well as extraction (CFE) techniques and the substrate induced respiration (SIR) technique while C and N mineralization were measured. Total concentrations of As in the top 0–10 cm soil layer ranged from 8 to 22992 mg kg^–1, from 31 to 1845 mg kg^–1 for Pb, from 27 to 1620 mg kg^–1 for Cu and from 81 to 4218 mg kg^–1 for Zn. There was a significant negative correlation (P < 0.0001) between microbial biomass, soil organic carbon, total N and C mineralization and the heavy metal content of the soil. The microbial biomass C to organic C ratio, which varied from 0.4 to 1.9%, specific respiratory activity (qCO₂), and oxidation of NO₂^– were not affected by heavy metals. It was found that long-term contamination of soil with heavy metals had an adverse effect on the amount of soil microorganisms as evidenced by a marked decrease in microbial biomass C, but not some of their characteristics. According to principal components analysis (PCA), the correlation matrix showed three distinct factors explaining 71% of the variance. A first factor including heavy metals (As, Pb, Cu and Zn) with a negative loading and total N, organic C, soil microbial biomass with a positive loading characterized the soil organic matter and contamination status. Loam and sand combined for the second factor characterizing the textural classification while the third factor was loaded by CEC and clay content.     

聚丙烯酸盐对长期重金属污染的矿区土壤的修复研究（Ⅱ）——对土壤微生物数量和土壤酶活性的影响

采用盆栽试验方法研究了聚丙烯酸盐对SDomingos金矿区重金属污染土壤的修复作用。在《聚丙烯酸盐对长期重金属污染土壤的修复研究（I）》^[30]（以下简称研究I）中聚丙烯酸盐的应用显著提高了土壤持水能力和土壤的pH,同时土壤中水溶性重金属的含量也比对照显著降低,从而使果园草Orchardgrass（Dactylis glomerata L．cv．Amba）的生物量得到显著增加。为更全面地说明聚丙烯酸盐在该重金属污染土壤修复上的作用,进一步探讨了聚丙烯酸盐对重金属污染土壤微生物属性的影响。结果表明,土壤细菌数量随聚丙烯酸盐水平的增加而增加,不同处理之间差异显著（P≤0．05）;与对照相比,聚丙烯酸盐处理的真菌数量显著增加（P≤0．05）,但随着聚丙烯酸盐水平的增加而显著降低（P≤0．05）,这可能是由于0．4％和0．6％的聚丙烯酸盐处理土壤pH显著提高所导致的。因此使用微生物数量评价土壤质量时,细菌比真菌表现更突出。使用聚丙烯酸盐修复的土壤脱氢酶、磷酸酶、蔗糖酶、蛋白酶和纤维素酶的活性均比对照显著增加（P≤0．05）,而脲酶活性的下降则可能是由于聚丙烯酸盐带来大量的铵态氮产生的抑制作用所致。综合研究I中的结果,聚丙烯酸盐不仅可以改善重金属污染土壤的理化性状而且对于土壤微生物属性也有显著的改善作用。从果园草生物量来看,0．4％聚丙烯酸盐的用量对该污染土壤的修复具有实践应用价值。     

土壤质量生物学指标研究进展

本文对近年土壤微生物、土壤酶活性和土壤动物等土壤质量生物学指标研究成果进行了综合评述。土壤微生物是土壤有机组分和生态系统中最活跃的部分,被认为是最敏感的土壤质量生物学指标:微生物生物量代表参与调控土壤中能量和养分循环及有机物质转化所对应微生物的数量,但须结合多样性研究以弥补其无法反映土壤微生物组成和区系变化的缺陷;微生物群落组成和多样性动态反映土壤中生物类群的多变性和土壤质量在微生物数量和功能上的差异;土壤微生物活性体现在土壤微生物商、微生物呼吸和代谢商等方面,应考虑生物量大小与微生物种群活性间的相关关系以反映微生物种群内的差异。土壤酶活性具有极高时效性,在较短时间内就能反映出土壤质量的变化。土壤动物通常以种类的组成和数量,土壤动物区系的相对丰度、多样性或活性作为评价土壤生物质量的敏感指标。与土壤理化指标相比,土壤生物学指标更能对土壤质量的变化做出灵敏迅速的响应,因而被广泛地用于评价土壤质量。     

Riboflavin content in the coelomocytes of contrasting earthworm species is differentially affected by edaphic variables including organic matter and metal content

The riboflavin content in extruded coelomocyte lysates derived from Dendrodrilus rubidus may serve as a sensitive bioindicator of soil metal pollution: the vitamin (B2) content has previously been found to be high in worms from unpolluted soil but low in worms inhabiting Zn/Pb mine soils, aerially deposited Ni-contaminated soil, and in worms experimentally transferred from clean soil to the metalliferous field soils. The aim of the present work was to extend these observations by comparing the number and riboflavin composition of coelomocytes retrieved from three lumbricid species (Allolobophora chlorotica, Dendrobaena veneta, Eisenia andrei) after 4-week exposures to an unpolluted commercial soil, two geochemically contrasting unpolluted field soils, and two different Zn/Pb/Cd-polluted soils from the Bukowno district in South Poland. Whilst eco-physiologically contrasting, these three earthworm species share the trait of possessing relatively high numbers of eleocytes, a category of immune-competent coelomocyte rich in autofluorescent riboflavin. Spectroflurometric analysis indicated that coelomocyte riboflavin content in worms maintained in strongly metalliferous soils or in unpolluted sandy-clay and loamy-sand soils was increased in coleomocytes from epigeic D. veneta and E. andrei species, whilst was decreased in endogeic A. chlorotica. In conclusion, the riboflavin content of earthworm coelomocytes is affected in species-specific ways by edaphic variables, including organic matter and metal pollution.     

Microbial use of lignite compared to recent plant litter as substrates in reclaimed coal mine soils

In the Lusatian mining district, rehabilitated mine soils contain substantial amounts of lignite in addition to recent carbon derived from plant litter. The aim of this study was to examine the importance of the two organic matter types as substrates for soil microbial biomass in mine soils containing organic matter with a contrasting degree of humification. Samples were taken from the lignite-containing overburden material, from a mine soil under 14-year-old black pine (Pinus nigra) and from a mine soil under 37-year-old red oak (Quercus rubra). Overburden material was ameliorated with alkaline ash and incubated in an identical manner as the 14-year-old and 37-year-old mine soils for 16 months. Carbon mineralisation was monitored throughout. After 0, 3, 6, 12 and 16 months, samples were removed and analysed for chemical parameters and for microbial biomass. In addition, ¹⁴C activity measurements in bulk soil and microbial biomass were used to estimate their lignite content.Despite the high content of organic carbon in lignite-rich overburden material, low contents of microbial biomass were recorded. Ash-amelioration led to high pH values in the overburden material, resulting in high concentrations of dissolved organic carbon most likely derived from lignite. Development of the microbial community was subsequently stimulated by presence of an easily available carbon source. In older mine soils, larger amounts of microbial biomass are most likely related to the presence of recent organic matter. Radiocarbon analysis of the microbial biomass extracted from the 14-year-old mine soil indicated higher lignite carbon contribution than recorded for microbial biomass of the 37-year-old mine soil. The highest concentration of lignite C present in microbial biomass as indicated by the C_mic/C_org ratio was, however, observed in the ameliorated overburden material. Therefore, we conclude that the importance of lignite as a carbon source for micro-organisms decreases when recent organic matter is present in the older stages of mine soil development.     

The impact of antibiotics (benzylpenicillin,and nystatin) on the biological properties of ordinary chernozems

In recent years, the input of antibiotics into soils has sharply increased. We studied the impact antibiotics (benzylpenicillin, pharmasin, and nystatin) at different concentrations (100 and 600 mg/kg) on population densities of microorganisms and enzymatic activity of ordinary chernozems in model experiments. The applied doses of antibiotics had definite suppressing effects on population densities of microorganisms (up to 30–70% of the control) and on the soil enzymatic activity (20–70% of the control). Correlation analysis showed close correlation between the concentrations of antibiotics and the population densities of soil microorganisms (r = ?0.68–0.86). Amylolytic bacteria had the highest resistance to the antibiotics, whereas ammonifying bacteria had the lowest resistance. Among the studied enzymes belonging to oxidoreductases and hydrolases, catalase and phosphatase had the highest and the lowest resistance to the antibiotics, respectively. The effect of antibiotics on the biological properties of the chernozem lasted for a long time. The studied parameters were not completely recovered in 120 days.     

Emerging resistant microbiota from an acidic soil exposed to toxicity of Cr, Cd and Pb is mainly influenced by the bioavailability of these metals

Purpose

The effect of pollutants in soil microorganisms is an important issue in order to understand their toxic effects in the environment, as well as for developing adequate bioremediation strategies. In this sense, the main objective of this study was to assess the involvement of the indigenous microbiota of an acidic forest Mediterranean soil by artificial pollution with heavy metals, and to detect and isolate resistant microorganisms that could be useful for bioremediation.

Materials and methods

Samples from a previously unpolluted acidic forest soil were amended with Cr(VI), Cd(II) or Pb(II) at total amounts ranging from 0.1 to 5,000 mg?kg^?1. These soil microcosms were incubated under controlled laboratory conditions for 28 days. Soluble fractions of metals were determined from aqueous extracts. Both activity and composition of the microbial community were assessed, respectively, by respirometric assays and molecular analysis (polymerase chain reaction denaturing gradient gel electrophoresis). The isolation of metal-resistant microorganisms was attempted by culture plating from microcosms incubated with high concentrations of metals. Isolated strains were tested in cultures with minimal medium to check for their metal resistance and their capacity to reduce the presence of toxic Cr(VI).

Results and discussion

A decrease in the soil respirometric activity and changes in the microbial community composition were detected from 10/100 mg?kg^?1 Cr and 1,000 mg?kg^?1 Cd and Pb. Presumably resistant bacterial and fungal populations developed in most of these polluted microcosms; however, the microbiota was severely impaired at the highest additions of Cr. Even though Cr was the most damaging metal in soil microcosms, if the soluble fractions of metals are considered instead of their total added amounts, the comparison among their toxic effects suggests a similar potential toxicity of Cr and Pb. Isolated multiresistant microorganisms were related mainly to Actinobacteria, Firmicutes and Ascomycota. Some of them showed the capacity to reduce Cr(VI) concentrations between 54 % and 70 % of the initial value. These strains were affiliated to several species of Streptomyces and Bacillus.

Conclusions

The combination of respirometric assays with molecular methods has been useful to assess the effect of metals on the soil microbial community, which can greatly be explained by their differential bioavailability. Cultivation-dependent and -independent approaches have proved the presence and development of multiresistant microorganisms in a previously unpolluted soil. Due to their properties, some of the isolated strains are potentially useful for soil bioremediation.     

超积累植物东南景天根际土壤酶活性研究

通过野外调查和盆栽试验研究了超积累植物东南景天根际土壤酶活性变化及其与重金属有效态的关系。研究结果表明,在矿山土壤、重度污染土壤和轻度污染土壤上,种植超积累生态型东南景天后,根际土壤有效态Zn分别比非根际减少了14.3%,7.9%和47.4%,有效态Cd分别比非根际减少25.1%,21.9%和20%。在铅锌矿区,东南景天生长地段土壤蔗糖酶、酸性磷酸酶、脱氢酶活性高于其它植物生长地段。在矿山土壤和重度污染土壤中,超积累生态型东南景天根际土壤酶活性明显高于非根际土壤,同时也高于非超积累生态型根际土壤。Pb、Zn、Cd、Cu4种重金属对东南景天根际土壤脲酶、蔗糖酶、脱氢酶活性均有抑制作用,而Pb对磷酸酶有一定的刺激作用。东南景天根际土壤脱氢酶、酸性磷酸酶活性与重金属有效态含量呈极显著相关。     

宿州市矿区与耕地土壤重金属含量及其潜在生态风险评价

以调查宿州市矿区与耕地土壤的重金属污染状况数据为基础,按照有关标准和方法,对宿州市矿区与耕地土壤重金属潜在生态风险进行了评价,结果表明:宿州市矿区土壤重金属含量均值除Pb外,其它都大于耕地,且Hg、Cr含量远远超过耕地;从单因子污染指数看,矿区土壤重金属污染主要是Hg、Cr的污染,而耕地整体状况良好;从内梅罗综合污染指数的均值来看,矿区土壤全部被污染,耕地仅有6%中度污染,8%轻度污染;从潜在生态风险指数来看,矿区土壤属于中等风险等级,耕地属于低风险等级,各重金属元素对矿区土壤潜在生态风险贡献大小顺序为:矿区土壤Hg>Cd>As>Cr>Cu>Zn>Pb,Hg潜在生态风险最大。