入侵植物黄顶菊与3种牧草竞争效应研究

以入侵植物黄顶菊和多年生黑麦草、紫花苜蓿、高丹草3种牧草为试验材料,采用盆栽取代试验方法观察了不同密度及比例条件下4种植物的竞争表现,为黄顶菊生物替代提供理论依据.结果表明:(1)在3种牧草中,高丹草对黄顶菊株高控制效果最为明显,并以苗期效果最好,在低密度比例下对黄顶菊抑制率即可达60.00%;而多年生黑麦草和紫花苜蓿的控制效果较差,在低密度比例下对黄顶菊起不到抑制作用.(2)在高丹草低密度替代组合中,黄顶菊单株生物量、分枝数比对照均明显减少,抑制率分别可达91.40%和44.87%;而多年生黑麦草和紫花苜蓿各密度替代组合中,黄顶菊单株生物量、分枝数与对照相同或大于对照.(3)在各个生育时期,除高密度高丹草替代组合外,其他组合中黄顶菊的相对产量值均极显著小于1.0,生长受明显抑制;而在各替代密度下,多年生黑麦草、紫花苜蓿与黄顶菊竞争替代效果均不明显.研究发现,高丹草的替代效果明显优于多年生黑麦草和紫花苜蓿,可以作为生物替代的材料对黄顶菊进行替代控制,且在植株比为1∶3比例下即可实现理想控制效果.     

基于五室培养法的接菌紫花苜蓿受损根系模拟修复研究

本研究以紫花苜蓿为寄主植物,采用五室培养系统按照根系在土壤中分布的体积比例定量模拟根系损伤,初步探讨紫花苜蓿和菌根真菌共生体的协同修复作用及其生态效应。结果表明,在不同的试验设计中,接种菌根有效地缓解了根系损伤带来的不利影响,双侧接菌在植株生物量、菌根侵染效果以及收集到的矿质元素浓度等均高于单侧接菌和对照,土壤有效磷含量在伤根前后仍维持在10 mg/kg。接菌改善了紫花苜蓿根际微环境,在一定程度上减缓根系损伤对植物的负面影响,有利于采煤沉陷区地表植被的修复。     

不同品种(系)牧草镉修复能力综合评价

该研究选用3种高丹草、2种苏丹草、2种杂交狼尾草、一年生黑麦草和多年生黑麦草共9个牧草品系,采用盆栽试验,设置0(CK)、10(Cd10)、20 mg/kg(Cd20)镉胁迫处理,考察不同品系的生长指标、镉含量和富集指标,运用极差化法和主成分分析建立综合评价模型,通过计算各牧草在模型中的综合得分,筛选出最适宜实地修复的牧草,探究不同品种和不同品系牧草的镉修复能力差异,建立Cd污染土壤植物修复能力评价体系,发掘兼顾富集量和后处理的镉污染土壤植物修复资源。结果表明：(1)镉胁迫会不同程度降低牧草的株高和生物量,其中江苏苏丹草在Cd10和Cd20中的耐胁迫能力均较强;(2)在Cd10和Cd20处理下,一年生和多年生黑麦草均具有较高的地上部和地下部Cd含量,高丹草的3个品系在Cd含量和Cd积累量两方面存在较大差异;(3)在Cd10和Cd20处理下,高丹草和黑麦草的富集指标表现优异,且富集指标在高丹草品系间存在较大差异;(4)2个镉质量分数处理下综合评价得分最高的均是一年生黑麦草,其次为高丹草。研究表明,参试牧草对镉胁迫均有较强的耐受性,但耐受能力和富集能力在品系间存在明显差异,并以高丹草品系间差异最大;一年生黑麦草能耐受20 mg/kg以下镉胁迫,且生物量较小,对镉有较强的浓缩效应,可作为镉污染土壤实地修复的可靠材料;综合评价模型可作为镉污染修复植物资源筛选的可靠方法。     

有机磷生物修复研究进展

目前,有机磷的生物修复还主要是微生物修复。但是植物修复更具优越性,因其花费更少、对环境更安全。然而植物对生长条件的要求相对较高,修复效率较低,应用还非常有限。本文综述了有机磷微生物修复和植物修复的研究进展,总结了已知的有机磷降解酶及其生物来源。结果表明,植物材料的筛选、土壤与OPs作用机理的研究、植物耐受和消除OPs的基因组学研究、植物-微生物联合降解体系的建立以及降解酶的植物根系分泌系统的利用是提高有机磷植物修复效率的重要途径。     

重金属污染土壤植物修复中的微生物功能研究进展

综述了国内外在重金属污染土壤植物-微生物联合修复领域的研究报道,总结了近5年的研究实例。植物-微生物联合修复体系具有生物固定与生物去除土壤重金属的两种功能,根际微生物可以菌根、内生菌等方式与根系形成联合体,通过增强植物抗性和优化根际环境,促进根系发展,增强植物吸收和向上转运重金属的能力。建立植物-微生物联合修复体系,可充分发挥植物与微生物作用功能的优势,提高污染土壤的修复效率。增强植物修复体系中微生物功能的重点是深入研究根际微生物、根系和介质载体三者之间复合功能,结合污染土壤类型与植物群落配置的特点筛选扩繁高效菌种与菌群。     

植物修复石油烃污染土壤的机制

根据石油烃污染土壤植物修复的应用和研究现状,对近年来国内外植物修复机制进行阐述与探讨。植物首先通过根系直接吸收石油烃,并利用自身的新陈代谢或植物内生菌的协作将其去除。石油烃一旦被根系吸收,植物就会通过木质化作用将其储存在组织中,或通过植物挥发或植物降解将其转化成一些低毒的中间代谢产物或CO_2和H2O;而植物内生菌与植物降解、植物修复以及植物保护密切相关。其次,根际分泌物和根际微生物在石油烃污染土壤根际修复方面起到重要作用。根际是受根系活动影响的一个微生态区,因而可以认为根际修复是去除土壤中石油烃的主要方式。植物根系可以向根际释放一些分泌物和酶类。其中,酶可以直接作用于石油烃,对石油烃的降解起到关键的作用;而根际分泌物可以向根际微生物提供碳源、能源或共代谢物,使根际微生物数量和活性明显高于非根际,生物降解作用增强。今后可以从根际分泌物作用的微生态过程、功能基因的寻找和构建、厌氧氧化的过程和机制、植物内生菌的作用和应用,以及利用组学手段研究植物修复机制5个方面开展工作,以期望为未来植物修复工作提供重要的科学支持。     

一株毒死蜱降解细菌的分离鉴定及其在土壤修复中的应用

从蔬菜大棚土壤中分离到一株能以毒死蜱为唯一碳源和能源生长的菌株DSP3,该菌在含毒死蜱（100mg/L）的酵母膏和蛋白胨与同样毒死蜱含量而无酵母膏蛋白胨的无机盐培养基中,18d对毒死蜱的降解率分别为986%和762%;在土壤实验中20d对毒死蜱（100mg/kg）的降解率接近100%,加入DSP3菌在蔬菜大棚新鲜土壤中能有效促进毒死蜱在土壤中的降解。根据生理生化特征、16S rDNA序列分析、（G+C）mol%测定和DNA同源性分析,将菌株DSP3鉴定为粪产碱杆菌（Alcaligenes faecalis）。     

植物根系分泌物对土壤污染修复的作用及影响机理

生物修复是一种经济环保的土壤修复技术。根系分泌物是利用生物修复污染土壤过程中的关键物质,也是植物与土壤微生物进行物质交换和信息传递的重要载体,在植物响应污染物胁迫中扮演重要角色。研究植物根系分泌物对土壤污染修复的作用和影响机理,是深入理解植物和微生物环境适应机制的重要途径,对促进生物修复污染土壤有重要指导意义。从污染物胁迫对根系分泌物的影响、根系分泌物对土壤污染物环境行为的影响、根系分泌物在调控污染土壤中根际微生物群落结构和多样性中发挥的作用等几个方面综述了根系分泌物对土壤污染修复的影响及内在机制。研究结果表明,根系分泌物在降低重金属对植物的毒性、加速有机污染物降解等方面有非常重要的作用。根系分泌物对土壤微生物的丰度和多样性均有显著影响,其与根际微生物互作在土壤污染物的消减中发挥了重要的调控作用。在此基础上,提出了以往研究中的不足,并对污染物胁迫下根系分泌物未来研究的方向和趋势进行了展望。     

植物-微生物联合修复化学农药污染土壤的研究进展

化学农药的高毒性、生物积累性和扩散性极易对环境及人类健康造成危害,环境中化学农药的去除尤为重要。植物-微生物联合修复技术因其高效、环境友好和修复成本低等优点受到越来越多的关注,植物-微生物联合修复化学农药污染土壤是一种很有前景的方法。植物为根际和内生细菌提供养分,而细菌通过化学农药的降解和解毒来支持植物生长。本文综述了影响化学农药在植物体内吸收和转运的因素以及植物-微生物修复技术的原理,并讨论了植物与微生物在化学农药污染土壤修复中的协同效应,并对植物-微生物联合修复法在化学农药污染土壤修复中的应用前景进行了展望。     

石油烃污染土壤的生物修复

从中原油田污染土壤中通过实验室驯化培养分离到一组能以中原原油为碳源的快速生长的石油烃降解菌.用该组降解菌接种原油污染土壤,研究其原位生物联合修复实验,接种降解菌的各区分别种植大豆、施有机肥料、施有机肥料和锯末,与空白试样作对比.经过120d的联合修复,各区石油降解菌的总数(lgcfu/g)由接种时的5.25分别变为7.79、4.96、5.15、4.67.石油烃降解率分别达到89.4%、72.5%、76.7%、49.2%.表明分离的该组石油烃降解菌是一组高效降解菌且其与植物联合修复石油污染土壤能显著提高修复效果.     

Degradation of crude oil in the rhizosphere of Sorghum bicolor

Dissipation of petroleum contaminants in the rhizosphere is likely the result of enhanced microbial degradation. Plant roots may encourage rhizosphere microbial activity through exudation of nutrients and by providing channels for increased water flow and gas diffusion. Phytoremediation of crude oil in soil was examined in this study using carefully selected plant species monitored over specific plant growth stages. Four sorghum (Sorghum bicolor L.) genotypes with differing root characteristics and levels of exudation were established in a sandy loam soil contaminated with 2700 mg crude oil/kg soil. Soils were sampled at three stages of plant growth: five leaf, flowering, and maturity. All vegetated treatments were associated with higher remediation efficiency, resulting in significantly lower total petroleum hydrocarbon concentrations than unvegetated controls. A relationship between root exudation and bioremediation efficiency was not apparent for these genotypes, although the presence of all sorghum genotypes resulted in significant removal of crude oil from the impacted soil.     

Chlorpyrifos bioremediation in <Emphasis Type="Italic">Pennisetum</Emphasis> rhizosphere by a novel potential degrader <Emphasis Type="Italic">Stenotrophomonas maltophilia</Emphasis> MHF ENV20

Rhizoremediation is a specific type of phytoremediation involving both plants and their rhizosphere associated microbes. In the present study Pennisetum pedicellatum and rhizosphere associated degrading strains were evaluated for chlorpyrifos remediation. Time-course pot experiments were conducted in greenhouse with P. pedicellatum grown in soil amended with chlorpyrifos at the concentrations of 10, 25, 50, 75 and 100 mg/kg for 60 days. The half life of chlorpyrifos varied from 19.25 to 13.02 days in planted treatments. Residual concentrations of chlorpyrifos were negatively correlated with abundance of degrading microorganisms in rhizosphere. The isolated species of Bacillus, Rhodococcus and Stenotrophomonas were evaluated for their degrading potential in mineral medium. A novel isolated strain of potential degrader Stenotrophomonas maltophilia named as MHF ENV20 showed better survival and degradation at high concentration of chlorpyrifos. Degradation of chlorpyrifos by strain MHF ENV20, 100, 50 and 33.3% degradation within the time period of 48 h (h), 72 and 120 h at 50,100 and 150 mg/kg concentrations, further the gene encoding the organophosphorous hydrolase (mpd) was amplified using PCR amplification strategy and predesigned primers. Our findings indicate that rhizosphere remediation is effective bioremediation technique to remove chlorpyrifos residues from soil. P. pedicellatum itself, in addition to the rhizosphere bacterial consortium, seemed to play an important role in reducing chlorpyrifos level in soil. High chlorpyrifos tolerance and rhizospheric degradation capability of P. pedicellatum, makes this plant suitable for decontamination and remediation of contaminated sites. The ability to survive at higher concentration of chlorpyrifos and enhanced degrading potential due to presence of mpd gene make S. maltophilia MHF ENV20 an ideal candidate for its application in chlorpyrifos remediation.     

丛枝菌根对有机污染土壤的修复作用及机理

丛枝菌根(AM)是丛枝菌根真菌(AMF)与植物根系相互作用的互惠共生体,能改良土壤结构,增强植物抗性.自然界中已知的AMF有170多种,分布广泛,且可与大多数植物共生.利用AM修复有机污染土壤正成为一个崭新的研究方向.本文综述了AM对多环芳烃、酞酸脂、石油和农药等一些典型有机污染物污染土壤的修复作用.AM修复有机污染土壤的机理主要包括:AMF代谢有机污染物;AM分泌酶,降解污染物;AM影响根系分泌作用,并促进根际微生物对有机污染物的降解;AMF宿主植物吸收积累污染物.AM修复研究中,高效AMF的筛选、复合菌种效应、土壤老化、AM作用下植物对有机污染物的吸收积累等几方面仍有待于深入研究.     

Numerical Simulation of Plant–microbial Remediation for Petroleum-polluted Soil

This paper presents a numerical analysis of the migration and transformation mechanism of petroleum hydrocarbons (PHs) pollutants in soil. The mathematical model of the solute migration and plant–microbial remediation for PH polluted soil was established. The model was verified by field experimental data. Then, the software Hydrus-1D was employed to simulate the processes of diffusion, adsorption, desorption, microbial degradation, and plant adsorption of PHs in the soil–water system. The process of plant–microbial remediation for PH-contaminated soil was also simulated. The space-time change of PHs in soil was obtained, and the fate and remediation efficiency of PHs in soil were revealed in different remediation conditions. The results indicated that the Hydrus-1D model can adequately simulate the process of plant–microbial remediation. Plant–microbial remediation appears to be more efficient than the application of bacteria or Suaeda salsa. The majority of PH pollutants are degraded in the upper soil levels. For long-chain petro-alkane-contaminated soil, plant–microbial remediation is a more efficient method. A suitable moisture level in soil is important for improving the bioremediation effect of plant–microbial remediation technology.     

Studies on Biodegradation of Kerosene in Soil under Different Bioremediation Strategies

The effectiveness of bioremediation is often a function of the microbial population and how they can be enriched and maintained in an environment. Strategies for inexpensive in situ bioremediation of soil contaminated with petroleum hydrocarbons include stimulation of the indigenous microorganisms by introduction of nutrients (biostimulation) and/or through inoculation of an enriched mixed microbial culture into soil (bioaugmentation). To demonstrate the potential use of bioremediation in soil contaminated with kerosene, a laboratory study with the objective of evaluating and comparing the effects of bioattenuation, biostimulation, bioaugmentation, and combined biostimulation and bioaugmentation was performed. The present study dealt with the biodegradation of kerosene in soil under different bioremediation treatment strategies: bioattenuation, biostimulation, bioaugmentation, and combined biostimulation and bioaugmentation, respectively. Each treatment strategy contained 10% (w/w) kerosene in soil as a sole source of carbon and energy. After 5 weeks of remediation, the results revealed that bioattenuation, bioaugmentation, biostimulation, and combined biostimulation and bioaugmentation exhibited 44.1%, 67.8%, 83.1%, and 87.3% kerosene degradation, respectively. Also, the total hydrocarbon-degrading bacteria (THDB) count in all the treatments increased with time up till the second week after which it decreased. The highest bacterial growth was observed for combined biostimulation and bioaugmentation treatment strategy. A first-order kinetic model equation was fitted to the biodegradation data to further evaluate the rate of biodegradation and the results showed that the specific degradation rate constant (k) value was comparatively higher for combined biostimulation and bioaugmentation treatment strategy than the values for other treatments. Therefore, value of the kinetic parameter showed that the degree of effectiveness of these bioremediation strategies in the clean up of soil contaminated with kerosene is in the following order: bioattenuation < bioaugmentation < biostimulation < combined biostimulation and bioaugmentation. Conclusively, the present work has defined combined biostimulation and bioaugmentation treatment strategy requirements for kerosene oil degradation and thus opened an avenue for its remediation from contaminated soil.     

Comparative Mesocosm Study of Biostimulation Efficiency in Two Different Oil-Amended Sub-Antarctic Soils

Biological treatment has become increasingly popular as a remediation method for soils and groundwater contaminated with petroleum hydrocarbon, chlorinated solvents, and pesticides. Bioremediation has been considered for application in cold regions such as Arctic and sub-Arctic climates and Antarctica. Studies to date suggest that indigenous microbes suitable for bioremediation exist in soils in these regions. This paper reports on two case studies at the sub-Antarctic Kerguelen Island in which indigenous bacteria were found that were capable of mineralizing petroleum hydrocarbons in soil contaminated with crude oil and diesel fuel. All results demonstrate a serious influence of the soil properties on the biostimulation efficiency. Both temperature elevation and fertilizer addition have a more significant impact on the microbial assemblages in the mineral soil than in the organic one. Analysis of the hydrocarbons remaining at the end of the experiments confirmed the bacterial observations. Optimum temperature seems to be around 10 degrees C in organic soil, whereas it was higher in mineral soil. The benefit of adding nutrients was much stronger in mineral than in the organic soil. Overall, this study suggests that biostimulation treatments were driven by soil properties and that ex situ bioremediation for treatment of cold contaminated soils will allow greater control over soil temperature, a limiting factor in cold climates.     

酞酸酯污染农田土壤生物修复研究进展

酞酸酯是目前世界上产量最大、应用面积最广的人工合成有机物,作为塑化剂被广泛应用于塑料制品中。近年来发现酞酸酯是一类典型的环境内分泌干扰物。随着生活中塑料制品日益增多,尤其是农用薄膜和有机肥的大量使用,农田土壤中酞酸酯污染日益加剧,酞酸酯污染土壤的修复逐渐引起国内外学者的广泛关注。生物修复具有价格低廉、效果良好和环境友好等特点,尤其适合于大面积污染农田土壤修复。从植物修复、微生物修复、植物微生物联合修复和动物修复等方面综述了国内外酞酸酯污染土壤生物修复的研究现状,并从高效修复植物筛选及机理探讨、实际污染土壤的降解菌修复研究、高效降解菌群的构建和作用机制等方面对该领域的研究进行了展望,以期为酞酸酯污染土壤的修复研究提供借鉴并拓展新的思路。     

Effect of salinity on the bioremediation of petroleum hydrocarbons in a saline-alkaline soil

Aims: The aim of this paper is to check the effect of salinity on the bioremediation process of petroleum hydrocarbons in the saline‐alkaline soil. Methods and Results: In this study, soil salinity was adjusted to different levels by water leaching method and the bioremediation process was conducted for 28 days. Soil pH increased after leaching and decreased during bioremediation process. At initial time, moderate salinity enhanced the biodegradation and addition of microbial consortium was not effective in enhancing degradation rate of petroleum hydrocarbons. At day of 28 days, higher degradation rate was found in treatments with more leaching times with a maximum value of 42·36%. Dehydrogenase activity increased with the progress of bioremediation and positive correlation was found between dehydrogenase activity and degradation rate of petroleum hydrocarbons. Denaturing gradient gel electrophoresis analysis result showed decreased microbial community diversity with increased salt content. Conclusions: The result suggested that salinity had great impact on bioremediation, and leaching and addition of inoculated consortium were effective in enhancing biodegradation of petroleum hydrocarbons in the saline‐alkaline soil. Significance and Impact of the Study: The result of this study is important for understanding the bioremediation process of petroleum in contaminated soil. New remediation method of petroleum contaminated soil can be developed based on this study.