持久性有机污染土壤的植物修复及其机理研究进展

随着人类对化学品的依赖程度越来越高,环境的有机污染状况也越来越严重.有机污染土壤的植物修复是指利用植物在生长过程中,吸收、降解、钝化有机污染物的一种原位处理污染土壤的方法,具有应用成本低、生态风险小、对环境副作用小等特点.本文综述了近年来国内外有机污染土壤的植物修复研究进展情况,重点介绍了多氯联苯、多环芳烃、农药和硝基芳香化合物等持久性有机污染物的植物修复,阐述了有机污染土壤植物修复的关键机制,并分析了该技术在实际工程应用中的局限性及应考虑的因素.最后,指出了今后该领域的重点研究方向.     

磷酸盐修复重金属污染土壤的研究进展

从研究方法、反应机理以及风险评价等方面综述了磷酸盐修复重金属污染土壤的研究进展,分析和讨论了其中存在的问题和不足,提出了今后加强研究的重点。目前磷酸盐修复重金属污染土壤时,使用的主要研究方法有化学形态提取法、化学平衡形态模型法和光谱及显微镜技术,各个方法都有其优缺点,应该结合使用并探索新方法。磷酸盐稳定重金属的作用机理主要有3个:磷酸盐诱导重金属吸附、磷酸盐和重金属生成沉淀或矿物和磷酸盐表面吸附重金属,但磷酸盐与重金属反应的机理十分复杂,人们尚不完全清楚,因此难以有效区分和评价诱导吸附机理和沉淀机理或其它固定机理,相应地对磷酸盐修复重金属的长期稳定性难以预测。磷酸盐修复重金属污染土壤时由于其较高的施用量可能会造成磷的积聚从而引发一些环境风险,如磷淋失造成水体富营养化,营养失衡造成作物必需的中量和微量元素缺乏以及土壤酸化等。所以应该谨慎选择磷肥种类和用量,最好是水溶性磷肥和难溶性磷肥配合、磷肥与石灰物质等配合施用。今后应着重研究磷酸盐与重金属相互作用的机理区分和评价;关注磷酸盐修复重金属污染土壤时存在的潜在风险,特别是加强植物长期不断吸收磷或其它环境条件变化致使土壤磷素持续减少过程中稳定的重金属溶解性和移动性的研究,磷酸盐修复重金属污染土壤的长期田间实践等。     

赤泥在重金属污染治理中的应用研究进展

尽管赤泥在重金属污染环境修复研究中的应用越来越受到重视,但赤泥给污染环境修复带来突破的同时也给环境带来风险.目前,在赤泥的重金属环境修复研究中,针对赤泥的修复效果和修复过程研究较多,而对赤泥的钝化机理研究不够深入,赤泥修复的环境安全风险评价才刚起步.本文对近年来国内外关于赤泥修复重金属污染的研究进行综述,并指出了赤泥在今后的重金属污染治理中应加强的方向:一是深入赤泥对重金属钝化机制的研究;二是探索有效的赤泥安全评价方法;三是联合赤泥修复和生物修复技术(植物和微生物)对重金属和有机物复合污染进行修复.     

重金属污染土壤原位化学固定修复研究进展

重金属污染土壤原位化学固定修复是通过添加不同外源物质固定土壤中重金属元素,达到降低重金属迁移性和生物有效性的一种重要方法.由于操作方便和效果快速,使其在污染土壤治理过程中有着不可代替的作用,尤其对于耕作土壤中的面源污染.许多具有俘获土壤中重金属离子能力的自然物质和工业副产品如磷矿石、泥炭土、石灰和有机肥等都可用在实地的固定修复中.采用实验室评价和实地应用评价,一方面可以评估这些固定物质在土壤中对重金属离子的固定效率;另一方面可以评估重金属的溶出、释放和生物毒性等生态风险.本文对原位修复过程中采用的不同固定物质的来源和分类进行了概述,对化学固定过程的机理进行了探讨,同时阐述了重金属污染土壤化学固定修复应用过程中的实验室评价和实地应用评价方法,分析了化学固定修复的局限性并提出了今后的发展方向.     

有机修复剂在重金属污染土壤修复中的应用

有机修复剂在重金属污染土壤修复中具有举足轻重的作用.本文结合国内外的研究成果和最新研究进展,从土壤重金属污染修复中有机修复剂应用的发展状况、应用机理、优缺点、影响因素以及成功实例等几个方面论述了国内外有机修复剂的研究现状,列举了几种应用较为广泛的有机修复剂(如氨基多羧基酸、有机酸、有机质、生物乳化剂等)的最新研究进展,总结了影响有机修复剂使用的主要因素,指出目前有机修复剂在实际应用中可能出现的问题,同时对今后的发展方向进行了展望.     

降低水稻镉吸收原位钝化修复技术及其作用机理

重金属镉原位钝化修复是指向土壤中施加一些活性钝化修复材料, 通过改变镉在土壤中的赋存状态, 降低土壤中镉的生物有效性。该文对重金属镉污染土壤原位钝化修复中不同来源的钝化剂进行了分类, 概述了它们各自对重金属镉污染土壤的作用机理及其钝化修复效果。全面分析了目前该领域存在的主要问题, 并对其发展前景进行了展望。     

微生物对砷的作用机理及利用真菌修复砷污染土壤的可行性

利用真菌修复砷污染土壤和水体具有很大的发展潜力,是环境科学领域研究的热点.环境中存在的砷虽然不能像有机污染物那样被微生物降解,但可以通过微生物对砷的氧化/还原、吸附/解吸、甲基化/去甲基化、沉淀/溶解等作用影响其生物有效性,从而达到降低环境中的砷毒害、修复砷污染环境的目的.本文阐述了微生物对砷的作用机理,综述了真菌对砷累积与挥发研究的最新进展,探讨了其在修复砷污染土壤方面的可行性,旨在为利用真菌来修复砷污染土壤提供理论依据.     

溶磷微生物在钝化和植物修复重金属污染土壤中的作用

钝化和植物修复是重金属污染土壤修复的重要技术手段,而溶磷微生物可进一步增强钝化和植物修复重金属污染土壤的作用。介绍了钝化和植物修复重金属污染土壤的基本原理,总结了溶磷微生物对土壤中难溶性磷酸盐的溶解、利用磷酸盐钝化修复重金属污染土壤、溶磷微生物对磷酸盐钝化修复的强化以及溶磷微生物强化植物修复重金属污染土壤的研究进展,探讨了溶磷微生物对重金属的抗性及其溶磷机理、溶磷微生物对磷酸盐钝化修复重金属污染土壤的强化作用机理以及溶磷微生物强化植物修复重金属污染土壤的作用机理。旨在为生物修复重金属污染土壤研究提供一定的理论依据和技术支撑。     

利用能源植物治理土壤重金属污染

随着工农业的发展,土壤重金属污染日益加剧,严重威胁着粮食生产和人类健康。植物修复因其成本低、环境友好以及可大规模原位修复等优点备受关注,成为近年来迅速发展的重金属污染土壤治理技术。在介绍国内外植物修复技术发展与应用现状的基础上,提倡大力发展能源植物修复重金属污染土地,并结合湖南重金属污染田间试验结果,重点对甜高粱(Sorghum bicolor(Linn.)Moench)用于重金属污染土壤修复的优势、可行性及提高修复效率的措施进行了深入分析与探讨。利用甜高粱治理土壤重金属污染,能将土壤修复与生物能源生产有机结合,使重金属从粮食链转入能源链,同时兼顾了生态和经济效益,具有广阔的应用前景。     

中国土壤重金属污染修复研究展望

文章通过对土壤重金属污染相关文献进行研究分析,从我国土壤重金属污染的现状、修复技术应用和研究前景等方面进行了系统综述,重点分析了我国土壤重金属污染修复技术的应用和研究前景。超富集植物修复是一种新兴的绿色生物技术,成本较低,易操作,是土壤污染治理的环境友好技术。微生物修复具有成本低、无二次污染、对环境影响小、效率高等特点,可在一定程度上带来经济效益和生态效益,是一种理想的绿色修复方法。并指出筛选和培育生物量大、适应性强、富集能力强、易栽培且具经济效益的超富集植物、利用大型真菌吸收和富集土壤重金属、组合运用多种修复技术、结合应用分子生物学技术和基因工程技术和加强土壤重金属污染修复效果的评价将是今后研究的重点和热点。     

玉米各器官积累Pb能力的品种间差异

为了研究不同玉米(Zea mays)品种及不同器官对Pb积累能力的差异,在土壤Pb含量为595.55 mg·kg^-1 的高Pb胁迫和含量为195.55 mg·kg^-1的低Pb胁迫(对照)条件下,采用盆栽试验结合火焰原子吸收等方法,测定了25个玉米品种各器官Pb的含量。结果表明:Pb胁迫下供试玉米品种各器官含Pb量表现为根>茎≌叶>籽实;与对照相比,根、茎、叶Pb含量均大幅度提高,籽实含量的提高幅度相对较小;Pb胁迫条件下,有近半数的供试玉米品种的籽实Pb含量超过了国家规定的卫生标准,显示了在受重金属污染农田生产的玉米产品存在着较高的受Pb污染的风险。有22个品种平均籽实生物量在较强Pb胁迫下有所下降,降幅为0.9%~38.7%,但平均降幅仅为12.6%,显示玉米在Pb胁迫下的减产不易察觉,从而增加了在受污染农田中玉米产品受Pb污染的风险。但研究也表明,在较高Pb胁迫下尚有52%的品种籽实Pb含量未超过国家卫生标准最高限量值,因此可以利用这些品种在受Pb污染农田中进行玉米生产,以降低Pb经玉米产品进入人类食物链的风险。研究结果还发现供试玉米品种各营养器官间Pb含量均呈极显著正相关,但营养器官与籽实Pb含量间无显著相关。其中在较强的胁迫条件下营养器官Pb含量特别高的品种No.1的籽实中Pb含量(0.19 mg·kg^-1)比较低,未超过国家卫生标准;品种No.2、No.3和品种No.6也有类似的特点。除上述品种以及品种No.4外,其余品种籽实Pb含量遵循与营养器官Pb含量成正比的一般规律。根中Pb含量特别高的品种No.1,籽实产量在Pb胁迫下略有下降,但下降幅度最小。胁迫条件下,品种No.1的营养器官Pb总量最高(51.69 mg·plant^-1),是对照的近12倍;籽实Pb含量符合国家标准的品种No.2,No.3和No.6的营养器官Pb总量也较高,在36~42 mg·plant^-1之间。由此可见,存在着在受Pb污染农田利用这些品种进行玉米生产同时修复受污染土壤的可能。     

Heavy metals fractionation and organic matter mineralisation in contaminated calcareous soil amended with organic materials

Degradation of organic matter (OM) from organic amendments used in the remediation of metal contaminated soils leads to changes in soil chemical properties shortly after their addition, which may affect the soil metal distribution. The effects of two differing organic amendments on OM mineralisation and fractionation of heavy metals in a contaminated soil were investigated in an incubation experiment. The treatments were: control unamended soil, soil amended with fresh cow manure, and soil amended with a compost having a high maturity degree. The soil used was characteristic of the mining area at La Unión (Murcia, Spain) with 28% CaCO(3) and sandy-loam texture (pH 7.7; 2602 mg kg(-1)Zn; 1572 mg kg(-1)Pb). Manure and compost C-mineralisation after 56 days (24% and 3.8%, respectively) were below values reported previously for uncontaminated soils. Both amendments favoured Zn and Pb fixation, particularly the manure. Mn solubility increased at the beginning of the experiment due to a pH effect, and only Cu solubility increased through organic matter chelation in both amended soils.     

基于同步辐射技术研究土壤铁氧化物固定重金属分子机制的进展

铁氧化物在土壤中广泛赋存,因其比表面积大,对重金属具有很强的吸附固定能力,深刻影响着土壤重金属的形态转化过程.因此,研究土壤铁氧化物对重金属的固定机制,对于深入理解重金属在土壤系统中的环境化学行为以及评估污染土壤重金属生物有效性具有重要意义.然而,采用传统的吸附模型和化学提取法研究土壤铁氧化物固定重金属的机制具有明显的局限性,无法从分子水平上阐明其固定机制.同步辐射技术在环境土壤学的应用显著推进了在分子水平上认识土壤铁氧化物吸附重金属及其受典型环境因子影响的分子机制.本文主要从同步辐射技术的发展历程、模拟系统和实际土壤系统中铁氧化物在多种因素影响下对重金属固定的分子机制等方面进行了综述,同时对同步辐射技术的未来发展趋势及其在该研究领域的应用进行了展望.     

微生物对植物修复重金属污染土壤的促进效果

以印度芥菜作为超富集植物,通过盆栽试验研究了巨大芽胞杆菌和胶质芽胞杆菌的混合微生物制剂、黑曲霉30177发酵液对植物修复Cd、Pb、Zn污染土壤的作用.结果表明：巨大芽胞杆菌和胶质芽胞杆菌的混合微生物制剂不仅可以促进超富集植物的生长,增强超富集植物对土壤Cd、Pb、Zn的吸收,而且大幅度提高了植物的修复效率,在添加外源可溶性Cd、Pb、Zn的污染土壤上,可分别使印度芥菜提取量(以植物干质量计)提高1.18、1.54和0.85倍,在添加底泥Cd、Pb、Zn污染的土壤上,可分别使印度芥菜提取量提高4.00、0.64和0.65倍,在底泥污染的土壤上的促进效果明显强于外源添加污染的土壤.黑曲霉30177发酵液能显著促进印度芥菜对土壤Cd、Pb、Zn的吸收,在添加外源可溶性Cd、Pb、Zn的污染土壤上,印度芥菜地上部Cd、Pb、Zn的吸收量分别比对照提高了88.82%、129.04%和16.80%;在添加底泥Cd、Pb、Zn污染的土壤上,可分别比对照提高78.95%、113.63%和33.85%;但它可导致印度芥菜生物量的大幅度降低,起不到提高植物修复提取量的效果.经反相高效液相色谱初步分析发现,胶质芽胞杆菌、巨大芽胞杆菌发酵液中含有草酸、柠檬酸等有机酸,有机酸对重金属有一定的溶解作用,从而提高了重金属的生物有效性.     

长白山不同海拔梯度森林土壤中性糖分布特征

2010年7月,采集长白山北坡5个典型植被带(阔叶红松林、明针叶林、暗针叶林、岳桦林和高山苔原)林下土壤,研究了不同海拔梯度下森林土壤的中性单糖分布、数量及其影响因素,并结合中性糖来源差异探讨土壤有机质的生物化学积累机制.结果表明: 在长白山不同海拔梯度下,森林土壤的中性糖差异显著,中性糖来源碳在土壤有机碳(SOC)中的相对含量为80.55～170.63 mg·g^-1,并且随海拔升高呈递增的趋势.采用多元线性拟合分析发现,生长季平均气温是影响土壤中性糖相对含量的主要因素,低温有助于中性糖的积累.土壤中(半乳糖+甘露糖)/(阿拉伯糖+木糖)为1.62～2.28,且随海拔升高呈增加趋势,说明土壤中微生物来源中性糖的贡献随海拔升高逐渐增加.微生物熵随海拔升高而降低,说明低温条件下微生物活性下降而对外源碳的利用效率提高,植物残体被微生物分解转化后,以微生物同化物的形式固存于土壤中,从而增加了微生物来源中性糖的比例.     

The Chemophytostabilisation Process of Heavy Metal Polluted Soil

Industrial areas are characterised by soil degradation processes that are related primarily to the deposition of heavy metals. Areas contaminated with metals are a serious source of risk due to secondary pollutant emissions and metal leaching and migration in the soil profile and into the groundwater. Consequently, the optimal solution for these areas is to apply methods of remediation that create conditions for the restoration of plant cover and ensure the protection of groundwater against pollution. Remediation activities that are applied to large-scale areas contaminated with heavy metals should mainly focus on decreasing the degree of metal mobility in the soil profile and metal bioavailability to levels that are not phytotoxic. Chemophytostabilisation is a process in which soil amendments and plants are used to immobilise metals. The main objective of this research was to investigate the effects of different doses of organic amendments (after aerobic sewage sludge digestion in the food industry) and inorganic amendments (lime, superphosphate, and potassium phosphate) on changes in the metals fractions in soils contaminated with Cd, Pb and Zn during phytostabilisation. In this study, the contaminated soil was amended with sewage sludge and inorganic amendments and seeded with grass (tall fescue) to increase the degree of immobilisation of the studied metals. The contaminated soil was collected from the area surrounding a zinc smelter in the Silesia region of Poland (pH 5.5, Cd 12 mg kg^-1, Pb 1100 mg kg^-1, Zn 700 mg kg^-1). A plant growth experiment was conducted in a growth chamber for 5 months. Before and after plant growth, soil subsamples were subjected to chemical and physical analyses. To determine the fractions of the elements, a sequential extraction method was used according to Zeien and Brümmer. Research confirmed that the most important impacts on the Zn, Cd and Pb fractions included the combined application of sewage sludge from the food industry and the addition of lime and potassium phosphate. Certain doses of inorganic additives decreased the easily exchangeable fraction from 50% to 1%. The addition of sewage sludge caused a decrease in fraction I for Cd and Pb. In combination with the use of inorganic additives, a mobile fraction was not detected and an easily mobilisable fraction was reduced by half. For certain combinations of metals, the concentrations were detected up to a few percent. The application of sewage sludge resulted in a slight decrease in a mobile (water soluble and easily exchangeable metals) fraction of Zn, but when inorganic additives were applied, this fraction was not detected. The highest degree of immobilisation of the tested heavy metals relative to the control was achieved when using both sewage sludge and inorganic additives at an experimentally determined dose. The sequential extraction results confirmed this result. In addition, the results proved that the use of the phytostabilisation process on contaminated soils should be supported.     

Growth of Jatropha curcas on heavy metal contaminated soil amended with industrial wastes and Azotobacter. A greenhouse study

The aims of the study were to evaluate the effect of organic wastes (biosludge and dairy sludge) and biofertilizer (Azotobacter chroococcum) on the planting conditions of Jatropha curcas in metal contaminated soils. Results showed that the plants survival rate in heavy metal contaminated soil increased with addition of amendments. Treatment T6 (heavy metal contaminated soils+dairy sludge+biofertilizer) observed to be the best treatment for growth (height and biomass) as compared with the treatment T5 (heavy metal contaminated soils+biosludge+biofertilizer). In addition, organic amendments provided nutrients such as carbon, N, P and K to support plant growth and reduced the metal toxicity to plant. The present study showed that metal contaminated lands/soils could be suitably remediated by adapting appropriate measures.     

Immobilization of Zinc and Cadmium in Polluted Soils by Polynuclear Al13 and Al-Montmorillonite

We investigated the suitability of two aluminum-based binding agents, polynuclear Al₁₃ and Al-coated montmorillonite (Al-mont-morillonite), for the immobilization of heavy metals in two contaminated agricultural soils: a loamy luvisol from an arable site in Rafz, Canton Zürich, Switzerland, and a sandy podsol from Szopienice, Upper Silesia, Poland. Both soils were polluted by lead, zinc, and cadmium: the soil from Szopienice by the emissions of a nearby zinc-lead smelter, and the soil from Rafz by sewage sludge applications. While the samples from Szopienice exhibited extremely high loads of these metals, the samples from Rafz were only moderately contaminated. The samples from both soils were slightly acidic. The Rafz soil contained 2.5% organic matter, that from Szopienice only 1.5%. Destruction of the organic matter in the Szopienice samples by H₂O₂ led to a significant release of Zn and Cd into solution. This indicated that organic matter is an important factor for the immobilization of heavy metals in this soil. The treatment of the Szopienice samples with 8?mmol Al₁₃ per kg dry soil resulted in a considerable mobilization of the two metals. As the pH of the samples did not decrease, this effect was presumably due to direct interactions between the applied aluminium and organic matter. After destruction of soil organic matter, the two binding agents exhibited an immobilizing effect on Zn, which, however, was weak compared with the binding of the metal by the organic matter prior to its destruction. In the case of the Rafz samples, metal mobilization was observed only for Al₁₃ if applied in high doses (4 and 8?mmol per kg soil), but not for Al-montmorillonite. In this soil, Al-montmorillonite as well as Al₁₃ at low doses (1.2?mmol per kg soil and less) decreased soluble zinc concentrations significantly. The mobilization of metals at high doses of the applied binding agents and the dependence of this effect on the type of soil show that care has to be taken with this remediation method and that the proper doses of applied binding agents can be crucial for the success of metal immobilization in polluted soils.