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1.
A grass(Italian rye grass)experiment with complete desing of three factos(Hg,grass and exposure)and two levels(with and withou the factor tested)was carried out in Goeteborg,Sweden from May to September,1995,toward understanding the effect of mercury deposition on plant Hg content and its distribution.It has been found that besides the two general pathways of Hg absorption,i.e.root uptake and foliar absorption,mercury deposition can aslo signifcantly incease Hg content and total load in grass.Such effects seem to be confined only within the above-ground parts of grass plant.Estimate has been made to make clear of the contributions of different pathways to Hg Content and total Hg load in the upper part of grass.Results showed that the contribution of Hg deposition accounted for 27%-32%,of Hg content in the above-ground parts of grass plant without adding Hg to the soil.decreasing with the increase of soil and/or air Hg concentrations.The increment of Hg load in the upper part of grass plant caused by Hg deposition during an interval of two weeks varied between 0.01-0.07μg pt^-1,contributing to 17%-48% of the total Hg load in grass plant exposed.  相似文献   

2.
In acid precipitation area of Chongqing suburb the average of Hg in soil rose from 0.158mg/kg in 1984 to 0.20mg/kg in 1989,and Hg content of crops grown on these soils increased too.Both soil and vegetable Hg came mainly from power plant emission.which caused Hg and acid precipitiation pollution in environment and the Hg pollution of water,crops and milk in the area.  相似文献   

3.
As one of the most toxic heavy metals with persistence, bioaccumulation, and toxicity in environment, mercury and its envi- ronmental problems have caused a global concern. To fully understand the behavior and fate of mercury (Hg)(Ⅱ) in forest soils, a series of batch experiments were conducted to determine the adsorption and desorption characteristics of Hg(Ⅱ) by three dark brown forest soils from Mount Taishan, Laoshan Mountain, and Fanggan Village in Shandong Province, China. The adsorption solution was prepared using 0.1 mol L-1 NaNO3 as background electrolyte, with Hg(Ⅱ) at rising concentration gradients of 0.0, 2.0, 4.0, 6.0, 8.0, and 10.0 mg L-1 . Fourier transform infrared (FTIR) spectroscopy was adopted to characterize the soil samples and soil-Hg complexes. It was found that Hg(Ⅱ) adsorption isotherms could be well fitted with both Langmuir and Freundlich equations. The soil from Mount Taishan had the largest potential Hg(Ⅱ) adsorption capacity, though with less adsorptive intensity. The percentages of Hg(Ⅱ) desorbed from all soil samples were less than 0.6%, which suggested that all the soils studied had a high binding strength for Hg(Ⅱ). The soil from Mount Taishan had a higher Hg(Ⅱ) desorption capacity than the other soils, which indicated that the Hg(Ⅱ) deposited on the topsoil of Mount Taishan from atmosphere may easily discharge to surface water through runoff. Results of the FTIR spectroscopy showed that the three soils contained the same functional groups. The relative absorbencies of soil-Hg complexes changed significantly compared with those of the soil samples and the adsorption of Hg(Ⅱ) mainly acted on the O-H, C-O, and C=O groups of the soils.  相似文献   

4.
Hg vertial transference in soil-water system was studied by analyzing Hg vertical ditribution in soil column after adding Hg and one of the two leacheates,deionzied water or acid rain,into soil column.The results indicated that Hg was hardly transferable in puple soil.About 86%-88% of the total soil Hg was distributed in the top layer (0-2cm) and to Hg was detected in the leakage when the purple soil column was leached by deionized water and simulated acid rain.But Hg was more movalbe in yellow soil with only about 20%-22% of the total soil Hg distributed in the top layer (0-2cm),and about 17%-25% washed out from the soil column by deionized water and simulted acid rain,Incremant in soil bulk density colud reduce Hg leaching,thus the more the Hg kept in soil,the less the Hg leached into underground water,Deionized water and acid rain almost played the same role in leaching Hg.Bentioint was most effecient in preventing Hg from vertcal transferring in the soil coulumn.  相似文献   

5.
土-水体系中Hg的垂直迁移   总被引:1,自引:0,他引:1  
Hg vertical transference in soil-water system w as studied by analyzing Hg vertical distribution in soil column after adding Hg and one of the two leacheates, deionized water or acid rain, into soil column. The results indicated that Hg was hardly transferable in purple soil. About 86% ~ 88% of the total soil Hg was distributed in the top layer (0~2 cm) and no Hg was detected in the leakage when the purple soil column was leached by deionized water and simulated acid rain. But Hg was more movable in yellow soil with only about 20%~22% of the total soil Hg distributed in the top layer (0~2 cm), and about 17%~25% washed out from the soil column by deionized water and simulated acid rain. Increment in soil bulk density could reduce Hg leaching, thus the more the Hg kept in soil, the less the Hg leached into underground water. Deionized water and acid rain almost played the same role in leaching Hg. Bentonite was most efficient in preventing Hg from vertical transferring in the soil column.  相似文献   

6.
利用生物活性污染物剥离技术修复Hg污染的工业土壤   总被引:1,自引:0,他引:1  
The method to remove bioavailable amounts of heavy metals from a contaminated soil by using plants is defined as bioavailable contaminant stripping (BCS) and could safely be applied if the soil’s long-term ability to replenish the bioavailable pool is known. The aim of this study was to evaluate the ability of three common plant species selected, Brassica juncea, Poa annua, and Helianthus annus, to remove bioavailable amounts of mercury (Hg) from a contaminated industrial soil containing 15.1 mg kg-1 Hg. Trials were carried out under greenhouse conditions using pots (mesocosms). According to the precautionary principle, we modified the BCS remediation approach by adding a new step, in which mercury bioavailability was increased by the addition of a strong mobilizing agent, ammonium thiosulphate, (NH 4 ) 2 S 2 O 3 , to obtain an estimate of the likely long-term bioavailable Hg pool. The modified BCS remediation approach was called enhanced bioavailable contaminant stripping (EBCS). After one growth cycle, nearly all the bioavailable mercury (95.7%) was removed and the metal remaining in the soil was considered inert since it was neither extractable by (NH 4 ) 2 S 2 O 3 nor taken up by plants during a second growth cycle. The results demonstrated that EBCS appeared promising since it removed the most dangerous metal forms while substantially shortening the cleanup time.  相似文献   

7.
Soil remediation is an important part of the restoration process of degraded terrestrial ecosystems. Due to its unique properties, biochar is being used widely as an effective soil modifier in agricultural systems, but research is still rare on biochar application in grassland ecosystems, especially in degraded alpine grasslands. In this study, we conducted a plot experiment to investigate the effect of biochar application on soil physicochemical properties and microorganisms at the 0–20 cm soil depth of a degraded alpine grassland in Qinghai-Tibet Plateau, China. The experiment consisted of four corn straw biochar application levels (0%, 0.5%, 1% and 2%, with the percentage representing the ratio of biochar weight to the dry weight of soil in the surface 20 cm soil layer). When the biochar addition increased from 0% to 2%, total nitrogen, total organic carbon and available phosphorus in the 0–10 cm soil layer increased by 41%, 55% and 45%, respectively, in the second year after biochar addition. Meanwhile, soil electrical conductivity decreased, and soil water content increased. Total microbial, fungal and bacterial biomasses in the 0–10 cm soil layer increased from 9.15 to 12.68, 0.91 to 1.34, and 3.85 to 4.55 μg g-1, respectively. The relative biomasses of saprophytic fungi and methanotrophic bacteria decreased, while the relative biomasses of ectomycorrhizal fungi and arbuscular mycorrhizal fungi increased. These results indicate that biochar has a great potential in improving microbial activity and soil fertility in soil remediation of the degraded alpine grassland.  相似文献   

8.
重金属迁移与土壤性质的关系   总被引:6,自引:1,他引:5  
Cu, Zn, Pb and Hg runoff from yellow limestone soil and purple soils and the relationships between the mobility of the heavy metals and the soil characteristics were studied in laboratory using a rainfall simulator. The results showed that the concentrations of soluble Zn in surface runoff were significantly negatively correlated with the contents of < 0.002 mm particles and CEC of the soils, indicating that Zn was mostly adsorbed by clays in the soils. The contents of Cu and Hg in surface runoff were positively related to their contents in the soils. The amounts of Cu, Zn, Pb and Hg removed by surface runoff were influenced by the amounts of soil and water losses and their contents in the soils, and were closely related to the contents of soil particles 1~0.02 mm in size.  相似文献   

9.
In nutrient-limited alpine meadows,nitrogen(N) mineralization is prior to soil microbial immobilization;therefore,increased mineral N supply would be most likely immobilized by soil microbes due to nutrient shortage in alpine soils.In addition,low temperature in alpine meadows might be one of the primary factors limiting soil organic matter decomposition and thus N mineralization.A laboratory incubation experiment was performed using an alpine meadow soil from the Tibetan Plateau.Two levels of NH4NO3(N) or glucose(C) were added,with a blank without addition of C or N as the control,before incubation at 5,15,or 25 ℃ for 28 d.CO2 efflux was measured during the 28-d incubation,and the mineral N was measured at the beginning and end of the incubation,in order to test two hypotheses:1) net N mineralization is negatively correlated with CO2 efflux for the control and 2) the external labile N or C supply will shift the negative correlation to positive.The results showed a negative correlation between CO2 efflux and net N immobilization in the control.External inorganic N supply did not change the negative correlation.The external labile C supply shifted the linear correlation from negative to positive under the low C addition level.However,under the high C level,no correlation was found.These suggested that the correlation of CO2 efflux to net N mineralization strongly depend on soil labile C and C:N ratio regardless of temperatures.Further research should focus on the effects of the types and the amount of litter components on interactions of C and N during soil organic matter decomposition.  相似文献   

10.
土壤硼的电化学特征及解吸动力学   总被引:2,自引:0,他引:2  
Effects of humus fractions (fulvic acid,brown humic acid and grey humic acid) on the leachability and transferring activity of five types of mineral-bound Hg were investigated.Under the acid leaching condition;fulvic acid could promote leachability and vertical transference of all the mineral-bound Hg.Brown humicacid could retard the leaching and trasferring processes of CaCO30-Hg,Fe2O3-Hg,MnO2-Hg and kaolinite Hg but not bentonite-Hg.Grey humic acid could greatly enhance residing ability of the mineral-bound Hg in the soil colum and restrain them from vertical transferring.The effect of humus on leachability and transferring activity on the mineral-bound Hg was closely related to its ability to convert the mineral-bound Hg into orgainc-bound form and the transferbility of the latter in the soil column.The characteristics of the mineral-bound Hg in speciation were the internal factors that determined the extent and rate of the influence of the humus.  相似文献   

11.
In the early 1980's the Amazon region in the North of Brazil was the scene of the most intense gold rush in the history of Brazil. Metallic mercury (Hg) in gold mining activities is used to amalgamate particulate gold. The other sources of Hg emissions in Amazonian are tailing deposits and biomass burning of tropical forests and savannas. Total Hg concentrations in the urban area of Alta Floresta ranged from 20 to 5800 ng/m3. Indoor total Hg concentration in gold shops ranged from 250 to 40600 ng/m3. Particulate Hg accounts for 5 to 20% of total Hg in Alta Floresta. Through Factor and cluster analysis it was obtained a pattern of relationships between total Hg, fine and coarse mode particulate Hg, Pt, Pb, Ag and several other trace elements associated with the amalgamation process. A clear correlation was also observed with the fine mode biomass burning aerosol and coarse mode soil dust.  相似文献   

12.
To obtain the basic information on human exposure to mercury (Hg) due to gold mining activities in Amazon, total mercury (T-Hg) and methylmercury (MeI Ig) were determined for human hair, blood and/or urine samples collected from populations living in gold mining area and fishing villages upstream of the Tapajos River basin. Abnormally high levels of T-Hg were observed in hair and blood from all fishing villages investigated and more than 90% of T-Hg was in the form of MeHg in both samples, whereas in goldrnining area the value were much lower and the %MeHg values varied widely (20–100%) with individuals even in blood samples. Urine from gold shop workers contained Hg mostly in inorganic form at 165μg/g creatinine on the average, with the range of 20 to 450μg/g creatinine. A good correlation between Hg in hair and blood was found in fishing villages and the ratios of hair Hg to blood Hg were very close to 250, generally established for MeHg. T-Hg and inorganic Hg levels in urine from gold shop workers were also significantly correlated with inorganic Hg in blood.  相似文献   

13.
The distribution of mercury species was determined in soil from a site with Hg contamination. Mercury contamination was primarily confined to the top 40 cm of soil, and the concentration of total Hg ranged from 0.5 to 3000 µg Hg g?1. Of total Hg present, we determined that 91% was inorganic, 0.01% organic (as methyl Hg), and 6% elemental Hg. Furthermore, of total inorganic Hg present, 85% was in the insoluble mercuric sulfide form. Thus, of total Hg present in soil at this contaminated site, 91% was in the relatively insoluble HgS and Hg0 forms.  相似文献   

14.

Purpose

Vines (Vitis vinifera, L.) are a very important agricultural resource for Spain in general and for the Castilla-La Mancha region in particular, providing important productions of wines. Grapes and raisins are used for direct consumption too. In this work, we study analytical constraints regarding metallic trace elements uptake, focusing on Hg, from vines growing in the Almadén mercury mining district, the world's largest producer of this element, inactive nowadays.

Materials and methods

The study started with the analysis of these metals in soils and sets of vines leaves from seven sites located at different distances from the Almadén Hg mine. The samples of soils were dried at ambient temperature for 1 week. They were then sifted (<2 mm) and were stored for subsequent analysis. The leaves were dried and the leaf blade and petiole were separated. About 2 g of each sample were hand milled and analyzed using the same fluorescence spectrometer. Total mercury in soils and vine leaves were determined using a Lumex RA-915+ device, an atomic absorption spectrometer with a pyrolysis unit (RP-91c).

Results and discussion

Results show significant correlations between soil and leaves contents for total and organic mercury (R?=?0.934 and 0.984, respectively). Hg contents range in soil from 2,376 to 0.04 mg/kg in non-polluted places. For the organic fraction, the range varies between 197.49 and 3.15 mg/kg. Total Hg contents measured in leaves were from 5.14 mg/kg (close to dump zone of the mine) to 0.03 mg/kg in the proximity of Carrión de Calatrava, located some 100 km away from Almadén. Mercury reaches maximum in the proximity of known sources of the element: the mining and/or metallurgical areas of Almadén and Almadenejos.

Conclusions

Soils from the study area contain normal contents in trace metals, and these are conditioned by the local geology or urban locations of the area. Trace metals contents in leaves do not show a relationship with soil contents, possibly due to the low bioavailability of these elements in the soils investigated. Mercury is, as expected for this area, an exception to this trend, with very high concentrations that reach maximum values in the proximity of the known sources of the element: the proximity of mining and/or metallurgical areas in Almadén and Almadenejos.  相似文献   

15.
A pot experiment with 38 commonly cultivated rice cultivars from the Yangtze River Delta was conducted in a greenhouse to study the effect of mercury (Hg) contamination of a paddy soil (4.7 mg Hg [kg soil]–1) on crop growth and Hg accumulation in the grains. Mercury contamination differentially affected growth, grain yield, and Hg accumulation in brown rice of the tested cultivars. The average Hg concentration in the grains was significantly higher (p < 0.01) when plants were grown in the Hg‐contaminated compared to the control soil. Averaged over cultivars, the Hg concentration in brown rice exceeded the maximum permissible limit of 20 μg Hg kg–1. Increasing Hg concentrations were associated with grain‐yield declines up to 70%. This yield decline was mainly due to a reduction in the number of panicles. Japonica cultivars tended to be generally less affected by Hg than indica cultivars. The two japonica cultivars Jiahua and Chunjiang 026 showed both low Hg concentrations and no Hg‐induced grain‐yield reduction. These cultivars may be preferred candidates for cultivation in Hg‐contaminated soils or for studies on possible Hg‐exclusion mechanisms.  相似文献   

16.
李家飞  刘鸿雁  陈竹  饶程  姜畅  李政道 《土壤》2020,52(1):160-166
为揭示不同污染区重金属汞在土壤中的存在形态及分布特征,选取万山汞矿区、大龙燃煤电厂区为研究区域,以无污染区花溪区为对照,选择优化的Tessier连续化学浸提法进行汞的形态分析。结果表明:万山汞矿区与大龙燃煤电厂的土壤总汞平均值分别为22.7 mg/kg和0.648 mg/kg,均超过我国土壤环境质量二级标准(0.5 mg/kg),无污染对照区土壤总汞平均为0.179 mg/kg。在水平方向上,万山汞矿区靠近污染源的土壤汞含量相对较高,随着距离的增加而下降;大龙燃煤电厂区土壤汞在距燃煤电厂2.5 km范围内呈现先减小后增大的趋势。汞矿区土壤汞主要以残渣态(66.6%)为主,其次为有机结合态(30.0%);燃煤电厂则主要以有机结合态(75.7%)为主,其次为残渣态(17.46%);无污染区主要以残渣态(59.1%)为主,其次为有机结合态(28.9%)。内梅罗污染综合指数显示,万山汞矿区的土壤污染指数为107,为重度污染,这与污染源强度大有关,2004—2017年,总汞含量呈下降趋势;大龙燃煤电厂土壤污染指数为1.57,为轻度污染,同时土壤汞以有机结合态为主,潜在生物有效性相对较高,有一定的环境生态风险。  相似文献   

17.
In a polluted site in Germany not only metallic, ionic and MeHg could be detected, but also organomercurials such as methyl- ethyl- and phenyl-mercury. In addition sometimes other organomercurials could be separated but up to now not identified. Extraction of the organomercurials from soil and percolating water was performed by dithizone, differentiation and detection by High-Performance-Liquid-Chromatography and atomic fluorescence detection, respectively. Differentiation between gaseous organic and gaseous elemental mercury was done by adsorption on Carbotrap® and gold filters, thermal desorption and detection by atomic fluorescence The behaviour of 8 organomercurials in soil is described. For this a lysimeter of a new design was filled with polluted soil. The top layer of the soil was spiked with 8 organomercurials. The percolating water and the air above the soil, were analyzed. Different layers of the soil were also investigated after the experiment. By synthetic rain the movement of Hg species is low: the compounds stay in the first centimeters. Ethoxyethylmercury+, tolylmercury+, and nitromersol were not detected in the percocolate. Concentrations of phenylmercury+ and hydroxymercurybenzoicacid decreased. Methoxymethylmercury+ increased. In the head of the lysimeter, volatile Hg(0) concentration increased during 150 hours by a factor of 5, while volatile organic mercury decreased during this time by a factor of 10. The organomercurial-content in soil decreased.A transformation of organic to inorganic Hg is therefore presumed.  相似文献   

18.
The total Hg content in soil and in the epiphytic lichen Parmelia sulcata was determined in a former cinnabar mining area on Mt. Amiata. Metal concentrations in soil and in lichen are significantly related and decrease at increasing distances from the zone most affected by minespoil and by air which is still vented from mine shafts. On the basis of these results and of Al analysis, it seems likely that anomalous Hg content in Mt. Amiata lichens is mainly due to the out-gassing of volatile Hg from soil, from vegetation and, in the most heavily polluted zone, to the air from mine shafts.  相似文献   

19.
Brian E. Davies 《Geoderma》1976,16(3):183-192
Mercury was determined in 51 soil samples from historic base metal mining areas of England and Wales, together with cadmium, copper, lead, zinc, pH and organic content. Background mercury was calculated as 0.093 ppm whence 51% of the samples were judged to be contaminated. A very strong statistical correlation between mercury and lead and weaker but significant correlations between mercury and copper and zinc were found. Highest levels of mercury (maximum, 1.78 ppm Hg) and other metals occurred in soils derived from the floodplain of a river which was at one time badly polluted by mine waste. In a profile pit near a lead mine in the west of England both mercury and lead were enriched in surface horizons. It is concluded that land contaminated by heavy metals, especially lead, in the historic metal mining areas of England and Wales is also likely to be contaminated by mercury.  相似文献   

20.
Samples of six common plant species collected in the old mining areas near Prince George, British Columbia (Canada) and Mount Amiata, Tuscany (Italy) show remarkable similarities in the variation of plant/soil Hg concentration ratio with soil Hg content irrespective of species or other biological differences. In contrast, plants sampled in the geothermally active areas of New Zealand, Hawaii and around Mount St. Helens exhibit more individuality in the concentration ratio to soil Hg relationship, but the relationships are distinctly different from the mine site specimens. This distinction is particularly evident when the same species of Equisetum and Plantago taken from these two different areas are compared. These and other data support the hypothesis that specific local environmental factors strongly influence the accumulation of Hg in plants even when the immediate soil concentrations are the same. Our findings show that some plants contain concentrations of total Hg as high as 5500 to 14000 μg kg?1 (dw).  相似文献   

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