徐州矿区充填复垦场地作物重金属含量研究

为了了解矿区充填复垦土壤重金属污染状况和复垦场地主要作物的重金属含量情况,通过场地采样试验与室内检测相结合的方法,对不同作物不同部位的砷、镉、铬、汞、铅、铜和锌等重金属含量进行了测定,并进行了相关的分析和研究。结果表明:作物在生育阶段不同部位对不同元素的敏感性不同;复垦场地红豆幼苗受重金属的污染较轻,而小麦和水稻则较严重;复垦场地应改变耕作制度,种植红豆或者利用红豆充当先锋作物。     

Heavy metal uptake by wheat seedlings grown in fly ash-amended soils

A bioassay technique was used to investigate heavy metals uptake by wheat seedlings grown in fly ash-amended soils. No negative effect of fly ash on the growth of wheat seedlings was found. The addition of the fly ash generally decreased the heavy metal concentration in the wheat seedlings. The total accumulation largely depended on the soil characteristics. The variation in the soil pH induced by the fly ash treatment could be considered the most important parameter that influenced heavy metals uptake. In the soil with a higher increase of pH (2 units) total accumulation of heavy metals decreased with increasing fly ash addition. In the other soils where the pH variation was lower (0.4 units), total accumulation of some heavy metals increased. These obtained data provide useful information which is required before the agronomic use of fly ash can be recommended in Italian soils.     

Evaluation of Cocomposted Coal Fly Ash on Dynamics of Microbial Populations and Heavy Metal Uptake

Vicia faba, in a pot experiment with sandy and clayey soils under greenhouse conditions, was checked for growth response to different amendments with coal alkaline fly ash or cocomposted fly ash mixed with lignocellulosic residues. Soil microbial populations, pH and electrical conductivity as well as heavy metal uptake by plants were monitored. At rates of five and ten percent (on a dry matter basis) in both soils, neither fly ash alone nor cocomposted fly ash exerted any negative effect. Plant biomass production was not influenced in either clayey or sandy soil. Alkaline fly ash did not promote microbial growth when applied alone to the soils. However, cocomposted fly ash generally increased bacterial and actinomycetes counts in both soils. Fungi were not affected by ash. Due to the increase of soil pH by alkaline fly ash or cocomposted fly ash, plant uptake of heavy metals was depressed in the sandy soil. Heavy metal mobility did not cause change in the clayey soil where a high buffering capacity mitigated the effects of fly ash amendments.     

3种改良剂对油菜生物量及其吸收重金属的影响

通过连续三季盆栽试验研究粉煤灰、膨润土、腐殖酸提高油菜生物量,降低油菜Cd、Pb、Cu、Zn浓度的效果。结果表明,膨润土、腐殖酸、粉煤灰的施入提高油菜生物量的效果第二季好于第一、三季。仅考虑对生物量的影响,改良剂效果为膨润土>腐殖酸>粉煤灰。第二季膨润土降低油菜Cd浓度效果较好;第二季粉煤灰、第二季膨润土及第二、三季腐殖酸降低油菜Pb浓度效果较好,3种改良剂均有降低油菜中Pb浓度的效果;3种改良剂均未显著影响油菜中Cu浓度;第二季膨润土降低油菜Zn浓度效果较好。3种改良剂抑制土壤重金属进入油菜的效果不同,应用时可根据改良剂特点适时施入土壤,充分发挥改良剂吸附、固定重金属的作用。     

Remediation of Fly Ash Dumpsites Through Bioenergy Crop Plantation and Generation: A Review

Utilization of fly ash, a byproduct of coal combustion in thermal power plants, is a sustainable use of waste for power generation. Discarding fly ash as waste in landfills/ash ponds may not only be regarded as a loss of valuable land and essential nutrients, but also pose a significant health hazard due to fine air-borne particles and leaching of heavy metals. The presence of essential macro- and micronutrients and its porosity make fly ash an excellent soil amendment for plant growth as an organic nitrogen (N) and carbon (C) supplementation. As harmful heavy metals make fly ash unsafe for agronomy, bioenergy crop plantation and energy generation from different thermochemical conversions of the biomass would be an ideal method for coal fly ash utilization through which carbon-neutral fuel can be generated from fossil fuel, thus reducing climate change impact. This review summarizes the development of bioenergy plantation and silviculture at fly ash dumpsites with an integrated phyto-bio-rhizo-mycoremediation approach and assesses utilization of the valuable biomass for thermal energy, electricity, and biofuel generation with inclusion of a SWOT analysis (a strategic technique typically used to help identify the strength, weakness, opportunities, and threat). Bioenergy crop production through integrated phytomanagement can generate billions of dollars of wealth from waste and provides a sustainable solution for fly ash management, with environmental, economic, and social benefits.     

Enzyme Activities in a Sandy Soil Amended with Sewage Sludge and Coal Fly Ash

Previous studies showed that coal fly ash could stabilize sewage sludge by reducing metal availability, but fly ash may cause an adverse effect on soil microbial activities. Therefore, an experiment was performed to evaluate the effects of amendment of soil with anaerobically digested dewatered sewage sludge, stabilised with alkaline coal fly ash, on soil enzyme activity and the implications for soil nutrient cycling. Sewage sludge was amended with 0, 5, 10, 35 and 50% w/w of fly ash, and then the ash-sludge mixtures were incubated with a sandy soil at 1:1 (v/v). Dehydrogenase activity decreased with an increase in fly ash amendment level and the time of incubation. Soil receiving 5% ash-sludge amendment had a higher dehydrogenase activity than other treatments. Soil receiving 10% ash-sludge mixture had the highest urease activity and in general, urease activity decreased with increasing incubation time. Phosphatase activity was the highest at 5% ash-sludge mixture amended soil and no general trend was observed with time. Water-soluble Zn, Mn and Cu contents were suppressed by the addition of fly ash. The present experiment indicated that addition of 10% ash-sludge mixture should have a positive benefit on the activity of soil microorganisms, N and P nutrient cycling, and reduce the availability of heavy metals.     

粉煤灰对污染土壤中铜镉的稳定化

采用批衡量吸附和室内培养实验,考察了粉煤灰对Cu和Cd的吸附等温线及0.2%、0.5%、1%和2%用量的粉煤灰对土壤pH、有效态Cu和Cd、以及5种化学形态Cu和Cd分布的影响。结果表明:粉煤灰对Cu和Cd的吸附等温线均可以用Langmuir和Freundlich方程进行拟合,其对Cu的最大吸附量(9.90 mg/g)高于对Cd的最大吸附量(9.43 mg/g)。随着粉煤灰用量的增加,土壤pH显著增加,有效态Cu和Cd显著降低。同时,粉煤灰处理显著降低了离子交换态Cu和Cd含量,增加了铁锰氧化物结合态Cu和Cd含量,降低了Cu和Cd活性,使活性态Cu和Cd逐渐向潜在活性态和非活性态转化。其中培养60天后,2%处理的粉煤灰处理较对照pH提高了0.44个单位,离子交换态Cu和Cd分别降低了35.7%和35.9%。因此,粉煤灰能够有效吸附Cu和Cd,显著降低土壤有效态和离子交换态Cu和Cd的含量,在重金属稳定化修复应用中具有较好的应用前景。     

Co-disposal of Heavy Metals Containing Waste Water and Medical Waste Incinerator Fly Ash by Hydrothermal Process with Addition of Sodium Carbonate: A Case Study on Cu(II) Removal

Fly ash generated from medical waste incinerator and wastewater produced from electroplating plants contains various hazardous contaminants such as heavy metals and chlorinated organic compounds. The primary goal of this research was to investigate the feasibility of removing heavy metals from wastewater using medical waste incinerator fly ash as the treatment reagent with addition of small amount of sodium carbonate (Na₂CO₃) in a hydrothermal process. Copper (Cu) was used as the model heavy metal contaminant in the process. The results revealed that medical waste incinerator fly ash could effectively stabilize Cu(II) ion from wastewater, the crystal phase and simple substance formed during the treatment played a significant role in the fixation of heavy metals in wastewater and fly ash. The heavy metal leachability of treated ash was also measured after removal process. The co-disposal of Cu-containing wastewater and heavy metals-bearing medical waste incinerator fly ash by hydrothermal treatment with addition of a small amount of Na₂SO₃ was found promising as an effective way of removing Cu from wastewater. The reutilization feasibility of fly ash and the formation mechanism of copper-containing substances were also discussed in this paper.     

生物质电厂飞灰用作肥料的可行性评价

为了研究炉排燃烧生物质电厂飞灰在农林方面的应用价值和可能产生的环境影响,根据欧盟相关标准分析了2种飞灰(A、B)的基础特性(水分、灰分、总有机碳含量、p H值和电导率),并利用电感耦合等离子体光谱仪、质谱仪分析了飞灰中营养元素和有害元素的含量;参考中国固体废物浸出毒性浸出方法标准研究了营养元素和有害元素的浸出特性。结果表明,2种飞灰p H值均大于12,呈较强的碱性;并且二者不仅含有较高浓度的有机碳(A:18.39%;B:7.79%),还富含K、Ca、Mg、P等营养元素,其他主要有害元素的含量低于欧盟一些国家生物质灰农、林用和中国粉煤灰农用标准所规定上限值,这使得它们可以作为土壤改良剂或者辅料应用的农林方面。此外,除A飞灰中Cr的浸出率为1.274%外,其他有害元素的浸出率远小于1%,因而当它们应用在农林土壤时不至于造成污染。     

Coal Fly Ash and Phospho‐gypsum Mixture as an Amendment to Improve Rice Paddy Soil Fertility

Abstract

Rice is a plant that requires high levels of silica (Si). As a silicate (SiO₂) source to rice, coal fly ash (hereafter, fly ash), which has an alkaline pH and high available silicate and boron (B) contents, was mixed with phosphor‐gypsum (hereafter, gypsum, 50%, wt wt^?1), a by‐product from the production of phosphate fertilizer, to improve the fly ash limitation. Field experiments were carried out to evaluate the effect of the mixture on soil properties and rice (Oryza sativa) productivity in silt loam (SiL) and loamy sand (LS) soils to which 0 (FG 0), 20 (FG 20), 40 (FG 40), and 60 (FG 60) Mg ha^?1 were added. The mixture increased the amount of available silicate and exchangeable calcium (Ca) contents in the soils and the uptake of silicate by rice plant. The mixture did not result in accumulation of heavy metals in soil and an excessive uptake of heavy metals by the rice grain. The available boron content in soil increased with the mixture application levels up to 1.42 mg kg^?1 following the application of 60 Mg ha^?1 but did not show toxicity. The mixture increased significantly rice yield and showed the highest yields following the addition of 30–40 Mg ha^?1 in two soils. It is concluded that the fly ash and gypsum mixture could be a good source of inorganic soil amendments to restore the soil nutrient balance in rice paddy soil.     

Treatment of Acid Mine Drainage Using Fly Ash Zeolite

In this paper, two Indian fly ashes (from Talcher and Ramagundam) were converted into zeolites and both the raw fly ash and zeolite were used to treat two British acidic mine waters. The results demonstrate that fly ash zeolites are more effective than raw fly ash for treatment of acid mine drainage. Fly ash has been found effective for removal of Pb, but with increased dosing, caused release of Ba, Cr, Sr (both fly ashes) plus Zn, Ni (Talcher), or Fe (Ramagundam) into mine water. In contrast, increased dosing with fly ash zeolite removed 100% Pb, 98.9% Cd, 98.8% Zn, 85.6% Cu, 82.8% Fe, 48.3% Ni, and 44.8% Ba from mine water. Fly ash is amorphous in nature and many metals attached on the surface of the ash particles are easily leached off when ash comes in contact with acidic mine water. However, fly ash zeolite is crystalline in nature and due to its high cation exchange properties, most of the metals present in acid mine water are retained in surface sites.     

Reduction of Pb,Zn and Cd Availability from Tailings and Contaminated Soils by the Application of Lignite Fly Ash

The effectiveness of lignite fly ash for stabilization of Pb,Zn and Cd in tailings and contaminated soils was examined. Flyash was mixed with the contaminated soil or oxidic tailingssamples at various doses and pot experiments were performed.The effectiveness of stabilization was mainly evaluated by thestandard US EPA TCLP toxicity test. The 5-stage sequentialextraction procedure was also applied to determine the form ofcontaminants in the fly ash amended soil or tailings samples.Complementary EDTA extraction tests were also carried out. Thefly ash treatment resulted in the reduction of TCLP solubilityof Pb, Zn and Cd to below the respective regulatory limits at5 and 10% w/w fly ash addition rates in tailings and soil,respectively. Speciation of lead, in the treated soil andtailings samples indicated that there was a significanttransition of the heavy metals form from the exchangeable andcarbonate fractions to reducible and residual, suggesting thatthe potential mechanisms of heavy metals retention are, apartfrom increase of pH, sorption on the oxides and hydroxidessurfaces and binding with the hydrated fly ash compounds.     

Studies on the Phase Mineralogy and Leaching Characteristics of Coal Fly Ash

The phase mineralogy and leaching characteristics of some Indian coal fly ashes were studied to assess their safe disposal in abandoned coal mines. Since, fly ash contains a number of toxic trace elements, the leaching of fly ash was tested using strong acid/alkali solutions and distilled water under different conditions (solid-liquid ratio, leaching time, pH) in the temperature range of 30-100 °C. It was found that the concentration of various metals in leachates depends on their chemical nature, association with mineral phases of ash and follows the almost similar concentration profile to that of iron, especially in acidic medium. The distribution of toxic trace elements in fly ash and their leachability were found to depend on the amount of unburnt carbon and iron in fly ash. In alkaline medium, leaching of iron and toxic trace elements (except As) from fly ash was very negligible. Hence, alkali treatment of coal fly ash is desirable for its safe use in refilling of coal mines.     

污泥添加粉煤灰堆肥化对Cu、Zn、Pb形态的影响

污泥中重金属的危害是影响污泥土地利用的重要因素;污泥重金属危害不仅取决于总量,其形态分布更能反映重金属的迁移性以及生物有效性。实验以木屑为调节剂,粉煤灰作为钝化剂,研究污泥堆肥前后重金属Cu、Zn与Pb的形态分布变化。结果表明,堆肥对Cu有活化作用,而添加粉煤灰堆肥化能有效抑制这种活化,起到钝化作用,堆肥化使Pb向更稳定形态转化,添加粉煤灰堆肥化对Zn的钝化效果较好,当粉煤灰添加量为35%时,对Cu、Zn、Pb 3种重金属的易迁移态均具明显的钝化效果。     

粉煤灰施入砂姜黑土对麦田重金属元素分布影响的研究

采用盆栽试验方法 ,研究了粉煤灰施入砂姜黑土的改良效果及Cd、Cr、Pb、Hg和As等重金属元素在小麦各部位的积累与分布。结果表明 :粉煤灰施入砂姜黑土可以降低土壤容重、比重及土壤粘粒含量 ,增加孔隙和土壤渗透系数。被吸收的重金属元素主要分布在根系中 ,其次是叶片 ,在茎杆、叶鞘及籽粒中的分布极少。根系对Cd和As具有富集作用 ;籽粒中Cd、Cr、Pb、As随用灰量的增加而增加 ,Hg则减少 ,但在 3 6× 10 4kg/hm2 的用灰量范围内 ,5种重金属元素在籽粒及土壤中的含量均在安全标准之内     

不同复垦时间的粉煤灰充填复垦土壤重金属污染与评价

为了解粉煤灰充填复垦土壤重金属污染情况，通过实地试验与现场采样化验相结合的方法，对复垦时间不同的粉煤灰复垦土壤里砷(As)、镉(Cd)、铬(Cr)、汞(Hg)、铅(Pb)、铜(Cu)、硒(Se)、锌(Zn)、、镍(Ni)和氟(F)等重金属和微量元素含量的时空变异性进行了研究。结果发现：以土壤本底值作为评价标准时，粉煤灰充填复垦土壤整体处于受污染状态。其中，表层复垦土壤受到Cd、Se、Zn、F 4种元素污染较重；粉煤灰充填复垦土壤适合旱作，不适合用作水田；随着复垦时间的增加，表层复垦土壤的污染指数呈递增趋势。     

基于废弃物的潞安煤矿废弃地改良土壤基质配比研究

为解决潞安矿区煤矸石山、塌陷地生态修复缺土少肥问题,本研究将粉煤灰、污泥与垃圾堆肥以5%、10%、20%体积比例正交混合配制改良土壤基质进行盆栽试验,观测不同配比土壤的理化性质、养分及重金属含量、高羊茅与紫叶小檗生长状况,并用主成分–聚类分析法筛选最优配比。结果表明:添加垃圾堆肥可以提高土壤有效养分与有机质含量,对土壤理化性质改良有明显效果;添加污泥仅提升土壤有效磷含量;添加粉煤灰在降低土壤容重、增大总孔隙度与非毛管孔隙度上效果明显,但对土壤p H、阳离子交换量(CEC)与碱解氮的改良具有显著负效应。各废弃物改良基质的碱解氮、有效磷、速效钾、有机质等含量均较高,土壤重金属含量也处在安全范围,而土壤容重、非毛管孔隙、pH、电导率(EC)与CEC等指标性质较优的处理组为粉煤灰∶污泥∶垃圾堆肥∶土=5%∶20%∶20%∶55%、10%∶10%∶20%∶60%、20%∶5%∶20%∶55%3个处理。经过综合筛选,本研究基质最优混合配比为粉煤灰∶污泥∶垃圾堆肥∶土=5%∶20%∶20%∶55%,可作为当地矿区废弃地生态修复客土材料推荐方案。     

Effects of Fly Ash pH on the Uptake of Heavy Metals by Chicory

Chicory was cultivated in a pot experiment using two soils of different pH. Treatments were NPK, fly ash (pH 8) + NP and fly ash (pH 12) + NP, respectively. Another series of pots received heavy metals in soluble form additionally to the described treatments. It was observed that fly ash causes generally a decrease in Zn, Cd, Ni and Cu concentrations of chicory. The reduction occurs both for the metals naturally present in the soil and, to a greater extent, for those added as salts. This effect is more evident when fly ash at pH 12, rather than that at pH 8, was used. The increase of soil-pH through the fly ash addition is the major factor decreasing heavy metal availability. It was observed that potassium originating from fly ash is not available for crop uptake.     

Hazard identification of coal fly ash leachate using a battery of cyto-genotoxic and biochemical tests in Allium cepa

Leaching of heavy metals from coal fly ash dumpsites is an environmental threat often polluting both groundwater and surface water. This led to a detailed investigation on the cyto-genotoxicity and oxidative stress associated with the fly ash leachate (FL). Allium cepa L. bulbs were exposed to three concentrations of FL. Response to FL resulted in a reduction of root growth, inhibition of cell viability by up to 50%, and decrease in mitotic indices (control: 10.27; FA:water 1:4–4.52) with increased frequency of chromosome aberrations (5.7 fold) and bi-nucleate cells. Results of comet assay indicated that approximately sixfold increase in genotoxicity of FL was congruent with the endpoints of oxidative stress evaluated. The malondialdehyde content, superoxide dismutase, guaiacol peroxidase and glutathione-S-transferase activities were elevated in the treated plants in a dose dependent manner. The elemental analysis of FL showed the presence of heavy metals like cobalt (Co), chromium (Cr), copper (Cu), manganese (Mn), cadmium (Cd), nickel (Ni), lead (Pb) and zinc (Zn). The study demonstrated that FL can cause adverse effects to the plants. Therefore, the disposal of coal fly ash should be handled with caution and prevented from contaminating the surroundings.     

Geochemical Assessment of Environmental Effects of Ash from Yatagan (Mugla-Turkey) Thermal Power Plant

Yatagan Thermal Power Plant consumes low-quality ligniteproduced from the Yatagan Basin, located in the western part ofthe Aegean region nearby Mugla City. The basin is aligned in anorthwest-southeast direction. The dominant wind direction isalso northwest-southeast, which controls the boundary of thewaste at the disposal site. In this study, the concentration of30 volatile elements was analyzed in coal, bottom ash, fly ashand background soil. The study area was divided into grids. The size of the grids was 1 km² for the background soiland 50–100 m for the ash in the vicinity of the wastedisposal site. 15 fly and bottom ash, six coal and nine-background soil samples were analyzed according to a sequential technique using ICP-AES. The results reveal that heavy metal concentrations in the coal are below the world averages for coal whereas those of bottom ash and fly ash arewithin the world averages for the respective ashes, indicatingheavy metal enrichment. It is recommended that extra care shouldbe taken to prevent subsurface contamination in the study area.