DDT及其主要降解产物污染土壤的植物修复

用植草方法研究了受DDT及其主要降解产物污染土壤的植物修复试验，比较了10种草在不同污染浓度下对5种土壤的修复能力。研究表明，同一品种的草在不同土壤中对污染物的清除能力是不同的，不同品种的草在同一土壤中对污染物的清除能力也是不同的，在植物修复的过程中，通过草对有机污染物吸收的途径而去除土壤中污染物所作的贡献很小，植草3个月后，草对DDT及其主要降解产物的吸收与富集仅占原施药总量的0．13％－3．0％，而7．10％－71．94％的DDT及其主要降解产物从土壤中消失。     

有机氯农药六六六污染土壤的植物修复研究

我国20世纪六七十年代大量施用的有机氯农药,由于其性质极其稳定,在土壤至今仍有残留。植物修复有机农药污染土壤并不多见,但具有广阔的应用前景。此项研究对提高土壤环境质量、保证农产品的安全、实现农业可持续发展等有着重要的理论和现实意义。文章以多花黑麦草(Lolium multiforum Lan.)、紫花苜蓿(Medicago sativa L.)和籽粒苋(Amaranthus hypochondriacus L.)作为供试植物,在有机氯农药六六六(HCH)质量分数为1.09 mg.kg-1的污染土壤中种植3个月,研究了种植不同植物条件下土壤中HCH的消解情况。研究结果表明,与对照相比,种植植物大大提高了土壤中微生物数量和酶的活性,并且微生物的数量和酶的活性与土壤中HCH的消解密切相关。试验结束后,不同处理中HCH及其4种异构体的总含量降低幅度为43.87%~65.79%,其中种植紫花苜蓿和多花黑麦草的处理中HCH消解较快,对HCH污染土壤修复的效果较好。可见,植物修复技术是一种可行的环境友好的修复六六六污染土壤的技术。     

土壤中结合残留态农药的生态环境效应

土壤中农药结合残留态的形成，导致其活性暂时降低，但并未从土壤中消失，在特定的环境条件下又重新释放到环境中并表现出较高的生物有效性，从而威胁农产品质量安全与环境质量。文章论述了土壤中结合残留态农药的定义、形成过程及影响因素、老化和释放过程及机制。土壤中结合残留态农药主要通过吸附过程、化学反应及物理镶嵌等作用而形成，其形成过程受农药的结构和化学特性、土壤理化性质、环境条件和农艺措施的影响。老化是化合物和土壤组分紧密结合，减少被普通提取方法提取出来的数量，降低了化合物的生物有效性。同时老化的物质在土壤环境条件改变的情况下又重新释放到土壤溶液中或进行矿化，此过程可以通过物理一化学机制或生物化学作用而发生。重新释放到环境中的结合残留态农药又表现出较高的生物有效性，可能被植物、动物或微生物所吸收，并沿食物链富集和放大或进入水体污染水产品和造成水质恶化，从而威胁人体健康。文章还分析了土壤结合残留态农药可能带来的环境问题，提出了此问题今后研究的方向。     

土壤多环芳烃污染根际修复研究进展

多环芳烃(polycyclicaromatichydrocarbons,PAHs)是环境中普遍存在的具有代表性的一类重要持久性有机污染物,具“三致性”、难降解性,在土壤环境中不断积累,严重危害着土壤的生产和生态功能、农产品质量和人类健康。修复土壤多环芳烃污染已成为研究的焦点。根际修复是利用植物-微生物和根际环境降解有机污染物的复合生物修复技术,是目前最具潜力的土壤生物修复技术之一。对国内外学者近年来在土壤多环芳烃污染根际修复的效果、根际修复机理和根际修复的影响因素方面的研究进展作了较系统的综述,并分别分析了单作体系、混作体系、多进程根际修复系统和接种植物生长促进菌根际修复系统对土壤多环芳烃的修复效果。指出根际环境对PAHs的修复主要有3种机制:根系直接吸收和代谢PAHs;植物根系释放酶和分泌物去除PAHs,增加根际微生物数量,提高其活性,强化微生物群体降解PAHs。并讨论了影响根际修复PAHs的环境因素如植物、土壤类型、PAHs理化性质、菌根真菌以及表面活性剂等。植物-表面活性剂结合的根际修复技术、PAHs胁迫下根际的动态调节过程、运用分子生物学技术并结合植物根分泌物的特异性筛选高效修复植物以及植物富集的PAHs代谢产物进行跟踪与风险评价将成为未来研究的主流。     

不同有机物料对有机磷农药污染土壤酶活性及土壤微生物量的影响

农药污染严重影响了土壤的生态和食品的安全,为了解有机物料对农药污染土壤修复的影响,本文采用室内恒温恒湿培养的方法,研究了在有机磷农药污染的土壤中加入葡萄糖、堆肥、秸秆3种不同的有机物料对土壤微生物及土壤酶活性的影响,结果表明：有机磷农药对土壤微生物生物量碳和土壤的呼吸强度都有一定的影响,具体表现为前期（0～3 d）抑制,中期（3～40 d）为促进作用,后期（40 d以后）恢复稳定。加入有机物料后,显著提高了土壤的微生物生物量碳和土壤的呼吸强度,其中葡萄糖、堆肥、秸秆处理分别在第9、30、40天时的土壤的微生物生物量碳最高,在第9、30、50天时土壤的呼吸强度最高。有机磷农药对土壤过氧化氢酶和土壤脲酶影响表现为先抑制后激活,然后恢复的变化趋势。加入不同有机物料后,堆肥和秸秆对土壤过氧化氢酶和土壤脲酶都有促进作用,显著提高了其活性。堆肥处理的土壤过氧化氢酶、脲酶活性分别在0～20 d,20 d为最高,秸秆处理的土壤过氧化氢酶、脲酶活性都在40～50 d为最高。培养结束时（70 d）,秸秆、堆肥处理的土壤过氧化氢酶、脲酶活性要高于葡萄糖、空白处理。葡萄糖处理在前期（0～40 d）对过氧化氢酶、脲酶活性有一定的影响,到后期（40～70 d）同空白之间差异不大。研究结果表明有机物料的加入可以提高土壤微生物量和土壤的呼吸强度,提高土壤酶的活性,对于农药污染土壤的修复具有积极的作用。     

生物修复中有机污染物的生物可利用性

论述了土壤和地下水生物修复中有机污染物的生物可利用性。污染物的可利用性对生物修复速率和生物强化效率有重要影响。生物可利用性是指土壤和地下水中的微生物或其胞外酶对有机污染物的可接近性，它受土壤理化性质、污染物和微生物性质、污染接触时问等许多因素的综合影响。污染物的介质吸附、多相分配、老化和形成非水相基质，以及土壤微生物的吸附、过滤和沉降作用降低了污染物的可利用性。促进土壤中污染物和微生物的解吸附，增强非水相基质的溶解，加速土壤污染物与微生物之间的质量传递，可以增强污染物的可利用性和生物降解的速率。施用表面活性剂和电动力学方法可有效地增强污染物的生物可利用性。     

土壤原位修复技术研究与应用进展

土壤原位修复技术是指不经挖掘,直接在污染场地就地修复污染土壤的土壤修复技术,具有投资低,对周边环境影响小的特点,是土壤修复的研究热点。土壤原位修复技术主要有淋洗,气相抽提（SVE）,多相抽提（MPVE）,气相喷射（IAS）,生物降解,原位化学氧化（ISCO）,原位化学还原,污染物固定,植物修复等。淋洗法主要用于治理高渗透性土壤中的重金属和难挥发降解的有机物。土壤气相抽提和喷射技术适用于处理土壤中的易挥发污染物,并有常与加热技术,生物处理技术等联用,可以起到促进污染物挥发,增氧促分解的作用。多相抽提法主要用于治理存在大量非水相流体的污染场地,可将土壤中有机相污染物直接抽出。生物降解有生物好氧降解、生物厌氧降解、生物还原降解多种,降解方式由污染物种类和地质条件决定。化学方法可将污染物氧化或还原为低毒无毒物质,周期一般较短。固定污染物可以直接加入药剂反应生成沉淀,也可制造合适条件使微生物生成可沉淀重金属的离子。植物修复主要用于富集重金属,成本低廉,但富集了重金属的植物体的有效利用尚待进一步研究。土壤原位修复需要因地制宜,灵活结合工期、污染情况、地质条件、地面设施等,得出最经济实用的修复方法,并在辅助提高技术上展开更多研究,使原位修复技术更经济有效。     

污染土壤中菲的修复技术研究进展

菲是多环芳烃中的代表性物质,具有"三致"效应,而且菲的蒸汽压小,辛醇-水分配系数高,生物可利用性低,是一种持久性有机污染物。随着化石燃料的大量使用,受菲污染的土壤越来越多,研究菲的修复技术对污染土壤的再利用具有重要意义。结合目前国内外研究进展,综述了污染土壤中菲的修复方法,包括物理修复、化学修复和生物修复。针对各种修复方法,阐述了其原理、修复条件、实例应用和优缺点,重点论述了植物修复和微生物修复方法的降解机理和应用,分析了微生物性质,包括氧、营养物、温度、土壤理化性质、共存污染物等环境因素对生物降解的影响。由于溶解性的菲有较好的迁移转化能力,因此表面活性剂的助溶作用适用于各种修复方法,选择合适的表面活性剂可以提高修复效果。在各种修复技术中,物理修复是通过物理技术实现菲的解吸与富集,无污染,但是去除率低;化学修复是使用氧化剂将菲氧化分解成无毒易降解的小分子物质或通过添加化学淋洗剂增加菲的溶解性,提高迁移转化能力,用时短,但是引入其他试剂,容易造成二次污染;植物修复是通过植物的提取、降解和固定等过程实现菲的修复,尤其是植物的根际环境为微生物的生长提供有利的条件;微生物修复以菲可作为微生物生长的碳源为基础,在分解酶的作用下实现菲的降解,但是生物修复周期长,可利用的生物少,而且可能生成毒性更高的中间代谢产物。因此,寻找合适的修复物种,采用基因技术提高生物的修复能力或多法联用、取长补短可提高修复效率。最后,在共降解理论的基础上,结合重金属和有机污染物共存时,一种物质的存在对另一种物质的降解有促进作用,提出了协同降解的概念,寻求对多种污染物有协同降解或共降解作用的修复方法是今后发展的主要方向。     

根际环境与土壤污染的植物修复研究进展

土壤污染的植物修复通常与植物根际微生物紧密相关。根际微生物群落变化与土壤污染物在根际环境中的动态，可能是对土壤污染成功进行植物修复的基本过程。可见根际环境在土壤污染的植物修复中具有明显的重要作用。文章介绍了有关重金属在根际环境中的动态、有机污染物在根际环境中的降解转化、土壤重金属污染与土壤有机污染的植物修复研究进展。     

4种农药对土壤微生物的影响Ⅱ:氮素矿质化的变化

研究农药,氯氰菊酯、高效氯氰菊酯、多菌灵和丁硫克百威对山西省两种土壤氮素矿质化（ 氨化作用和硝化作用） 的影响．结果表明,添加低浓度（ ｗ ＝ １００ ｍｇ／ｋｇ） 的４ 种农药,对土壤氮素矿质化无显著影响． 高浓度（ ｗ ＝ １０００ ｍｇ／ｋｇ） 的菊酯类农药会抑制土壤中硝化细菌的活动,使土壤中氨的含量明显积累;添加高浓度多菌灵的土壤样品出现硝态氮积累的现象,这可能与其对微生物生长影响有关;添加高浓度丁硫克百威在一种土壤样品中使氨的含量有明显积累,但在另一种土壤样品中与对照基本相同．可见,农药对土壤氮素矿质化及微生物活性的影响,因农药品种的不同和浓度的不同而异,不同的土壤因微生物活性的差异而对农药污染的反应也不同     

A simple approach to modeling microbial biomass in the rhizosphere

Microorganisms make an important contribution to the degradation of contaminants in bioremediation as well as in phytoremediation. An accurate estimation of microbial concentrations in the soil would be valuable in predicting contaminant dissipation during various bioremediation processes. A simple modeling approach to quantify the microbial biomass in the rhizosphere was developed in this study. Experiments were conducted using field column lysimeters planted with Eastern gamagrass. The microbial biomass concentrations from the rhizosphere soil, bulk soil, and unplanted soil were monitored for six months using an incubation–fumigation method. The proposed model was applied to the field microbial biomass data and good correlation between simulated and experimental data was achieved. The results indicate that plants increase microbial concentrations in the soil by providing root exudates as growth substrates for microorganisms. Since plant roots are initially small and do not produce large quantities of exudates when first seeded, the addition of exogenous substrates may be needed to increase initial microbial concentrations at the start of phytoremediation projects.     

Microbial relationships in surface-mine revegetation

The establishment and interrelationships of microorganisms with soil and plant processes during reclamation are greatly influenced by the composition of the planting medium and vegetation practices. While in some instances the parent material may be used as the vegetation medium, the practice of topsoiling, particularly the direct haul method, may be beneficial in introducing microorganisms and improving the quality of the plant growth medium of spoils that are chemically or physically less desirable than the native soils. The influence of different vegetation types on soil development on surface mines may be a reflection of physioiogical differences that affect microbial development in the rhizosphere. Such differences include levels of carbohydrate translocated to the root system and/or released into the surrounding soil; the plant's effectiveness as a mycorrhizal host; and the rate of degradation of plant residues. It has become apparent that microbial interactions are an important part of plant and soil processes in reclamation. While some of the microorganisms important in plant growth and soil development can be introduced readily by management practices, the majority usually are disseminated by natural means and only gradually become a part of the microbial population. More research is needed on developing new methods or refining current procedures for early introduction of these microorganisms in reclamation practices.     

Microbial relationships in surface-mine revegetation

The establishment and interrelationships of microorganisms with soil and plant processes during reclamation are greatly influenced by the composition of the planting medium and vegetation practices. While in some instances the parent material may be used as the vegetation medium, the practice of topsoiling, particularly the direct haul method, may be beneficial in introducing microorganisms and improving the quality of the plant growth medium of spoils that are chemically or physically less desirable than the native soils. The influence of different vegetation types on soil development on surface mines may be a reflection of physioiogical differences that affect microbial development in the rhizosphere. Such differences include levels of carbohydrate translocated to the root system and/or released into the surrounding soil; the plant's effectiveness as a mycorrhizal host; and the rate of degradation of plant residues. It has become apparent that microbial interactions are an important part of plant and soil processes in reclamation. While some of the microorganisms important in plant growth and soil development can be introduced readily by management practices, the majority usually are disseminated by natural means and only gradually become a part of the microbial population. More research is needed on developing new methods or refining current procedures for early introduction of these microorganisms in reclamation practices.     

Effect of rhizosphere on soil microbial community and pyrene biodegradation

To access the influence of a vegetation on soil microorganisms toward organic pollutant biogegration, this study examined the rhizospheric effects of four plant species (sudan grass, white clover, alfalfa, and fescue) on the soil microbial community and in-situ pyrene (PYR) biodegradation. The results indicated that the spiked PYR levels in soils decreased substantially compared to the control soil without planting. With equal planted densities, the efficiencies of PYR degradation in rhizosphere with sudan grass, white clover, alfalfa and fescue were 34.0%, 28.4%, 27.7%, and 9.9%, respectively. However, on the basis of equal root biomass the efficiencies were in order of white clover >> alfalfa > sudan > fescue. The increased PYR biodegradation was attributed to the enhanced bacterial population and activity induced by plant roots in the rhizosphere. Soil microbial species and biomasses were elucidated in terms of microbial phospholipid ester-linked fatty acid (PLFA) biomarkers. The principal component analysis (PCA) revealed significant changes in PLFA pattern in planted and non-planted soils spiked with PYR. Total PLFAs in planted soils were all higher than those in non-planted soils. PLFA assemblages indicated that bacteria were the primary PYR degrading microorganisms, and that Gram-positive bacteria exhibited higher tolerance to PYR than Gram-negative bacteria did.     

Effects of microbial inoculations and surfactant levels on biologically- and chemically-assisted phytoremediation of lead-contaminated soil by maize (Zea Mays L.)

Assisted phytoremediation has been widely used for decontamination of potentially toxic elements contaminated soils. A greenhouse experiment was conducted to evaluate the effectiveness of different microbial inoculations and surfactant levels on the phytoremediation of a Pb-polluted calcareous soil by maize. The results showed that application of surfactant increased both root and shoot dry matter yields. Microbial inoculations, however, had no significant effect on the root or shoot dry matter yield. Mean Pb uptake in maize root or shoot increased only following the application of some surfactant levels. Inoculation with microorganisms significantly increased both mean Pb concentration and uptake in maize root but not in maize shoot. Application of 4?mmol surfactant kg?1 along with inoculation with Priformospora indica was effective in increasing Pb phytostabilisation potential. While the application of 2?mmol surfactant kg^?1 along with inoculation with Pseudomonas fluorescens was effective in increasing Pb phytoextraction potential. The fact that the values of translocation efficiencies were low in all treatments, demonstrated the low capability of maize for translocation of Pb from root to shoot. Inoculation with P. fluorescens was the most effective treatment in increasing metal micronutrient uptake. Microbial inoculation and surfactant levels enhanced Pb phytoremediation mostly through phytostabilisation of this metal by maize.     

Efficient phytoremediation of uranium mine tailings by tobacco

This investigation shows that tobacco plant roots and leaves accumulate 60?times more uranium than previously reported. Phytoremediation is a convenient technique to clean up polluted soils using herbaceous plants and trees. Increasing research aims to identify novel plant species that accumulate toxic metals. Tobacco plant (Nicotiana tabacum L.) is a promising cultivar for phytoremediation because tobacco is fast growing and easily propagated. Here, we study phytoremediation of uranium by two tobacco varieties Virginia and Burley, bred in natural conditions. Plants were grown on uranium mine tailings with an average uranium content of 15.3?mg?kg^?1. Each shoot sample was cross-sectioned into five uniform groups of leaves and stem segments. Results show a substantial variance in uranium uptake according to the section elderliness and origin of the plant parts. The highest concentrations of uranium values recorded in leaves of Burleys and Virginias nearest root shoot sections were 4.18 and 3.50?mg?kg^?1, respectively. These values are 60?times higher rates than those previously published for leaves of cultivars grown under similar conditions. Taking into account the level of soil contamination, the content of accumulated uranium demonstrates uranium hyperaccumulatory properties of tobacco plant and its potential utilization in phytoremediation of uranium-contaminated mediums.     

Introducing a new metal accumulator plant and the evaluation of its ability in removing heavy metals

A field study was conducted in a dried waste pool of a lead (Pb) mine in Arak (Iran) to find the accumulator plant(s) and to evaluate the amount of metal bioaccumulation in the root and shoot portion of the naturally growing vegetation. Concentrations of heavy metals were determined both in the soil and the plants that were grown in the dried waste pool. The concentrations of total Cu, Zn, Pb, and Ni in the waste pool were found to be higher than the natural soil and the toxic levels. The results showed that six dominant vegetations, namely, Centaurea virgata, Eleagnum angustifolia, Euphorbia macroclada, Gundelia tournefortii, Reseda lutea, and Scariola orientalis accumulated heavy metals. Based on the results, it was concluded that E. macroclada belonging to Euphorbiaceae is the best Pb accumulator and also a good accumulator for Zn, Cu, and Ni. The bioaccumulation ability of E. macroclada was evaluated in experimental pots. The study showed that the amount of heavy metals in polluted soils decreased several times during two years of phytoremediation. The accumulation of metal in the root, leaves, and shoot portions of E. macroclada varied significantly, but all the concentrations were within the toxic limits. Based on the obtained data, E. macroclada is an effective accumulator plant for soil detoxification and phytoremediation in critical conditions.     

About plant species potentially promising for phytoextraction of large amounts of toxic trace elements

There is no information yet about plant species capable of accumulating many different metals/metalloids. The plants feasible for phytoremediation aims must grow fast, have high biomass, deep roots, and should accumulate and tolerate a range of toxicants in their aerial parts. In our research, greenhouse and field experiments have been performed to investigate accumulation and tolerance of not well-studied trace elements such as Br, Eu, Sc, Th (and also U) in couch grass and wheat. We compared bioaccumulation abilities of the plants with those of some other plant species grown under the same conditions. Additionally, we tested the effects of inoculation of seeds with Cellulomonas bacteria on phytoextraction of the trace elements from contaminated soils. For determination of elements, we used neutron activation analysis and ICP-MS. It was found that couch grass and wheat can grow in heavily contaminated soils and accumulate different toxic trace elements to levels that exceed physiological requirements typical for most plant species. Infection of seeds with bacteria resulted in a significant increase in the uptake of various trace elements and their translocation to upper plant parts. The use of couch grass and/or wheat, either alone or in combination with microorganisms, is a promising way to phytoextract metals/metalloids from contaminated soils.

     

Effect of rhizosphere on soil microbial community and in-situ pyrene biodegradation

To access the influence of a vegetation on soil microorganisms toward organic pollutant biogegration, this study examined the rhizospheric effects of four plant species (sudan grass, white clover, alfalfa, and fescue) on the soil microbial community and in-situ pyrene (PYR) biodegradation. The results indicated that the spiked PYR levels in soils decreased substantially compared to the control soil without planting. With equal planted densities, the efficiencies of PYR degradation in rhizosphere with sudan grass, white clover, alfalfa and fescue were 34.0%, 28.4%, 27.7%, and 9.9%, respectively. However, on the basis of equal root biomass the efficiencies were in order of white clover >> alfalfa > sudan > fescue. The increased PYR biodegradation was attributed to the enhanced bacterial population and activity induced by plant roots in the rhizosphere. Soil microbial species and biomasses were elucidated in terms of microbial phospholipid ester-linked fatty acid (PLFA) biomarkers. The principal component analysis (PCA) revealed significant changes in PLFA pattern in planted and non-planted soils spiked with PYR. Total PLFAs in planted soils were all higher than those in non-planted soils. PLFA assemblages indicated that bacteria were the primary PYR degrading microorganisms, and that Gram-positive bacteria exhibited higher tolerance to PYR than Gram-negative bacteria did.