重金属污染对土壤微生物生态的影响

土壤重金属污染面积大,波及范围广,是一个全球性的环境问题。重金属的大量积累会降低土壤中微生物的生物量和活性,甚至会影响微生物群落的结构和多样性。土壤微生物由于其高灵敏度和及时对环境因素作出变化而越来越多地被用作监控土壤质量的生物指标。现主要针对土壤中重金属污染在土壤微生物活性、生物量、微生物群落结构等方面的影响进行综述。结合现有研究因素综合考虑,对微生物生态学研究指标在重金属土壤修复领域进行展望,为重金属污染土壤研究提供更为全面的质量评价和有效指标。     

红壤矿区复垦土壤的微生物生态特征及其稳定性恢复研究Ⅱ．对土壤微生物生态特征和群落结构的影响

研究了浙江哩铺铜矿废弃地土壤微生物生态特征和群落结构．结果表明,与对照土壤相比矿区土壤微生物生态特征发生了明显的改变,微生物呼吸速率减弱,微生物生物量显著降低,微生物生理生态参数Cmic／Corg下降、qCO2值明显升高,重金属对土壤微生物生态特征有明显的影响．Bio1og结果显示,矿区土壤微生物的群落结构发生变异,对能源碳的消耗量和速度明显升高,改变了微生物利用碳源的种类,使微生物消耗更多的能源,以维持其正常的生命活动,利用效率降低,明显不如对照土壤．由此可见,微生物生态特征是表征矿区复垦土壤重金属污染的灵敏、有效和可靠的生物学指标．     

红壤矿区复垦土壤的微生物生态特征及其稳定性恢复研究Ⅱ.对土壤微生物生态特征和群落结构的影响

研究了浙江哩铺铜矿废弃地土壤微生物生态特征和群落结构.结果表明,与对照土壤相比矿区土壤微生物生态特征发生了明显的改变,微生物呼吸速率减弱,微生物生物量显著降低,微生物生理生态参数C_mic/C_org下降、qCO₂值明显升高,重金属对土壤微生物生态特征有明显的影响.Biolog结果显示,矿区土壤微生物的群落结构发生变异,对能源碳的消耗量和速度明显升高,改变了微生物利用碳源的种类,使微生物消耗更多的能源,以维持其正常的生命活动,利用效率降低,明显不如对照土壤.由此可见,微生物生态特征是表征矿区复垦土壤重金属污染的灵敏、有效和可靠的生物学指标.     

入侵植物对根际土壤微生物群落影响的研究进展

入侵植物根际土壤微生物是地下生态系统的重要组成部分。外来植物入侵到新的栖息地后能够促进其根际土壤微生物群落结构的演替、改变土壤理化性质, 强化微生物群落功能的发挥, 进而创造更适合外来植物生长的土壤微环境, 促进外来种的入侵进程。从外来入侵植物根际土壤微生物的研究方法、外来入侵植物对根际土壤微生物群落影响以及从地下生态学对外来植物入侵的影响等方面进行了综述。土壤微生物研究方法主要包括微生物计数法、微生物生理生化指标方法及分子技术 3 类; 入侵植物对根际土壤微生物的影响主要体现在对其生物量、多样性以及功能微生物菌群等方面。在今后的研究中, 应当注重对同一区域外来入侵植物和近缘本土种、及其伴生种的根际土壤微生物进行比较研究; 加强入侵植物根际微生物功能机理、环境因子与微生物间关联性的研究; 同时在研究方法上应注重传统方法与生物标记法及其与分子技术的结合。     

放射性污染对铀矿区土壤微生物群落结构的影响

为探究放射性及其伴生污染对铀矿区附近土壤微生物群落功能多样性的影响，采集退役铀矿冶周围不同辐射值的土壤为研究对象，通过测定其土壤理化性质、土壤可培养微生物计数及Biolog-ECO微孔板培养，分析土壤放射性污染程度及理化性质对土壤微生物群落功能多样性和数量的影响。结果表明，矿区放射性污染土壤中重金属含量普遍较高，尤其是铅已超出管控标准。随着辐射值的增加，土壤中可培养微生物数量显著下降，特别是放线菌和真菌的数量；微生物群落功能多样性指数、物种丰富度指数、优势度、均一性指数显著下降；对碳源利用也逐渐下降，尤其是对酚酸类和胺类碳源，利用率分别下降25.8%、29.7%。RDA分析发现放射性核素是该区域驱动土壤微生物群落代谢发生变化的主要因素。铀矿区放射性污染及伴随的重金属污染明显改变土壤微生物群落结构，抑制了土壤微生物群落的代谢活性，造成土壤微生物群落功能多样性下降。     

重金属对土壤微生物的生态效应

通过分析重金属对土壤微生物生化过程与数量、种群及群落的影响、影响重金属对土壤微生物毒性的因素、重金属对土壤微生物毒性的评价指标、微生物对重金属的耐性与适应性以及重金属毒性的差异 ,综合评述了重金属对土壤微生物的生态效应 .     

基于菌植互作的植物根际细菌钝化镉作用和机制研究进展

土壤重金属镉(Cd)污染严重危害农产品安全生产,植物根际细菌在钝化土壤Cd和帮助作物抵御Cd胁迫方面发挥重要作用。本文首先概括在修复Cd污染土壤中得到广泛应用的植物根际细菌种类,并从根际细菌直接吸附Cd、调整土壤理化特性、调控土壤微生物群落和其他作用4方面阐述了植物根际细菌对Cd的钝化作用,其次从菌植互作角度阐述植物根系分泌物与根际细菌群落相互影响对土壤Cd的钝化作用。最后展望重金属胁迫下植物根际钝化Cd核心菌群的构建,以在新兴学科与技术的快速发展中探明植物根系-微生物互作体系的分子机制,深入开展植物根际细菌钝化修复重金属污染土壤的理论研究和实践。     

重金属土壤微生物的生态效应

通过分析重金属对土壤微生物生化过程与数量、种群及群落的影响、影响重金属对土壤微生物毒性的因素、重对土壤微生物毒性的评价指标、微生物对重金属的耐性与适应性以及重金属毒性的差异,综合评述了重金属对土壤微生物生态效应。     

施硅对抑制植物吸收重金属镉的效应研究进展

施用化学改良剂是控制土壤重金属污染的有效手段。研究施硅对抑制植物吸收重金属镉的影响及其作用机制,对促进利用硅肥作为改良剂治理重金属污染土壤技术的发展有重要意义。近年来,以硅肥作改良剂对重金属污染的土壤进行治理的研究大量涌现。本文从施硅对抑制植物吸收镉及镉在植物体内的分布、迁移的影响;从植物细胞膜透性、抗氧化物酶系和抗氧化剂等新陈代谢或生理过程及硅-金属复合物的结构组成等方面对植物抗镉胁迫的生理生化效应及其抑制植物吸收重金属镉的机制进行综述,并对今后有待进一步研究的问题提出了建议。     

镍污染对土壤微生物的生态效应

镍是高等植物和某些微生物必需的微量营养元素之一,在它们的生命活动中起着重要作用;但浓度较高时,也是一种极毒元素。大量的研究表明,镍污染土壤中微生物的生长、代谢、群落结构和种群多样性会受到不同程度的影响;微生物在长期受重金属威迫的环境中形成其适应性。利用微生物形成的这种适应机制,采用微生物技术治理重金属污染的土壤是可能的。本文还对镍污染土壤的微生物评价指标体系、土壤环境容量、微生物技术开发和综合治理技术开发等的进一步研究作了展望。     

Characteristics and diversity of microbial communities in lead–zinc tailings under heavy metal stress in north-west China

High-throughput 16S rRNA and 18S rRNA sequencing were performed to study the changes of soil microbial diversity and community structure under different heavy metal pollution levels in Chengxian lead–zinc mining area, Gansu Province. In this study, we characterized the main physicochemical properties, multiple heavy metal pollution, and microbial community structure of the soil in the tailings. The results show that the soil near the tailings pond was alkaline, barren and the heavy metals were seriously polluted. The microbial diversity and richness of S1 and S2 sites were significantly lower than that of CK2 site (P < 0·05), indicating that the heavy metal pollution could change the physicochemical properties and microbial community structure in soil. Among 97 identified core operating taxa of fungal communities, Ascomycota, Teguta and Basidiomycota were dominant at the phylum level, while among 1523 identified core operating taxa of bacterial communities, Actinomycota was dominant at the phylum level. In addition, the redundancy analysis and Spearman correlation analysis showed that the physicochemical properties and the heavy metal concentration had significant effects on the composition and distribution of soil microbial community. The basic characteristics of soil physicochemical properties, multiple heavy metal pollution and microbial community structure in the tailings were revealed, hoping to provide a basis for ecological rehabilitation of tailings by revealing the variance rule of microbial community diversity in the future.     

Phospholipid Fatty Acid Composition and Heavy Metal Tolerance of Soil Microbial Communities along Two Heavy Metal-Polluted Gradients in Coniferous Forests

The effects of long-term heavy metal deposition on microbial community structure and the level of bacterial community tolerance were studied along two different gradients in Scandinavian coniferous forest soils. One was near the Harjavalta smelter in Finland, and one was at Ronnskar in Sweden. Phospholipid fatty acid (PLFA) analysis revealed a gradual change in soil microbial communities along both pollution gradients, and most of the individual PLFAs changed similarly to metal pollution at both sites. The relative quantities of the PLFAs br18:0, br17:0, i16:0, and i16:1 increased with increasing heavy metal concentration, while those of 20:4 and 18:2(omega)6, which is a predominant PLFA in many fungi, decreased. The fungal part of the microbial biomass was found to be more sensitive to heavy metals. This resulted in a decreased fungal/bacterial biomass ratio along the pollution gradient towards the smelters. The thymidine incorporation technique was used to study the heavy metal tolerance of the bacteria. The bacterial community at the Harjavalta smelter, exposed mainly to Cu deposition, exhibited an increased tolerance to Cu but not to Cd, Ni, and Zn. At the Ronnskar smelter the deposition consisting of a mixture of metals increased the bacterial community tolerance to all tested metals. Both the PLFA pattern and the bacterial community tolerance were affected at lower soil metal concentrations than were bacterial counts and bacterial activities. At Harjavalta the increased Cu tolerance of the bacteria and the change in the PLFA pattern of the microbial community were found at the same soil Cu concentrations. This indicated that the altered PLFA pattern was at least partly due to an altered, more metal-tolerant bacterial community. At Ronnskar, where the PLFA data varied more, a correlation between bacterial community tolerance and an altered PLFA pattern was found up to 10 to 15 km from the smelter. Farther away changes in the PLFA pattern could not be explained by an increased community tolerance to metals.     

Comparison of microbial and meiofaunal community analyses for determining impact of heavy metal contamination

The impact of long-term heavy metal contamination on soil communities was assessed by a number of methods. These included plate counts of culturable bacteria, community level physiological profiling (CLPP) by analysis of the utilization of multiple carbon sources in BIOLOG plates, community fatty acid methyl ester (C-FAME) profiling and dehydrogenase enzyme activity measurements. These approaches were complemented with microscopic assessments of the diversity of the nematode community. Samples from two sites with different histories of heavy-metal input were assessed. Major differences in microbial and meiofaunal parameters were observed both between and within the sites. There was a large degree of congruence between each of the microbiological approaches. In particular, one sample appeared to be distinguished by a reduction in culturable bacteria (especially pseudomonads), limited response to carbon sources in CLPP, and major differences in extracted fatty acid profiles. The use of multivariate analysis to examine the relationship between microbial and physicochemical measurements revealed that CLPP and plate counts were useful for determining the gross effect of metals on soil microbial communities, whereas proportions of metal-resistant bacteria and dehydrogenase activity differentiated between the two sites. Copper and zinc concentrations and pH all showed significant correlation with the microbial parameters. Nematode community structure was affected to a greater extent by soil pH than by metal content, but the within-site rankings were the same as those achieved for microbiological analyses. The use of these methods for field evaluation of the impact of industrial pollution may be possible provided care is taken when interpreting the data.     

分离自活性污泥的硫酸盐还原菌用于铅锌冶炼渣重金属污染修复

【背景】从活性污泥中分离出一类具有硫酸盐还原能力的菌株,探讨了其用于铅锌冶炼渣重金属污染修复的可行性。【目的】研究硫酸盐还原菌(Sulfate reducing bacteria)对铅锌冶炼渣中重金属的固化作用。【方法】将从活性污泥中分离出的硫酸盐还原菌接种到铅锌冶炼渣中进行修复,采用X射线衍射、Tessier、电感耦合等离子体发射光谱仪检测、高通量测序等方法进行实验。检测铅锌冶炼渣中矿物组成,以及修复过程中重金属化学形态、各金属离子浓度和微生物群落结构的变化。【结果】修复实验表明,体系中电位降低、pH值提高、各重金属稳定态增加、离子浓度降低且微生物群落结构变化显著,硫酸盐还原菌成为优势菌群。【结论】接种硫酸盐还原菌后铅锌冶炼渣中的重金属原位固化效果显著,从而降低生物可利用性,将恶性循环变为良性循环,所以硫酸盐还原菌可用作重金属污染修复的固化药剂。     

长期重金属胁迫对农田土壤微生物生物量、活性和种群的影响

调查了沈阳张士灌区长期污水灌溉造成的原位农田土壤重金属污染状况,从土壤微生物生物量、微生物活性和微生物种群数量的角度评价了长期重金属污染对农田土壤生态系统的影响.结果表明,张士灌区土壤存在严重的Cd污染,土壤Cd含量达1.75～3.89 mg·kg ^-1,部分区域还伴有Cu、Zn复合污染.在目前污染程度下,土壤微生物生物量碳(C_mic)、微生物商(qM)、土壤脱氢酶活性以及自生固氮菌数量随土壤重金属含量增加呈下降趋势,代谢商(qCO₂)随土壤重金属含量增加显著升高,而底物诱导呼吸强度(SIR)、纤维素酶活性以及细菌、放线菌和真菌数量无明显变化.相关性分析表明,土壤Cd含量变化是影响微生物参数变化的主要因素,在微生物参数中微生物商和代谢商对重金属污染最敏感.     

贵州省典型汞铊矿区周边农田土壤跳虫群落特征

大量的采矿活动导致矿区周边土壤重金属污染, 严重危害土壤生物安全。汞、铊等重金属元素毒性强, 相关污染的土壤生态风险鲜有研究。跳虫作为土壤环境变化指示生物, 能很好地反映土壤质量的健康状况。本研究以贵州省某汞铊矿区周边的农田土壤为研究对象, 按离矿区距离和作物类型设置4个采样区, 每个采样区种植2种作物, 每种作物农田设置3个样方。研究土壤跳虫群落结构和多样性及其影响因子。结果表明, 调查区内跳虫平均密度为12,000 ind./m²; 采样区距离矿区越近, 土壤重金属污染程度越大, 综合污染指数越高, 跳虫种数、密度、多样性和丰富度指数均呈先增加再降低的趋势; 环境因子分析表明重金属显著影响跳虫群落结构: Folsomides americanus、Isotomiella minor和Protaphorura encarpatus数量与汞、铊和砷含量呈负相关。高有机质含量能缓解重金属对土壤跳虫的影响, 但作物类型(玉米与薏仁)对土壤跳虫群落结构的影响无显著差异。本研究结果表明土壤有机质或能反向调节重金属污染对土壤跳虫群落的影响。     

重金属污染对土壤有机质积累的影响

采用田间采样分析与室内培养试验相结合的方法,研究了不同重金属污染土壤中有机质积累的差异及重金属污染强度对土壤有机质矿化动态变化的影响.结果表明：污染土壤中重金属的大量积累可减弱有机物质的矿化速率,增加土壤有机质的积累.土壤中颗粒态有机质及其占总有机碳的比例随重金属积累的增加而增加;而微生物生物量碳占总碳的比例却随土壤重金属污染水平的提高而下降.污染土壤中颗粒态有机质对重金属有显著的富集,这可能是影响土壤有机物质进一步矿化的原因之一.重金属污染可改变土壤有机质的矿化速率,影响土壤有机质的积累与分配.     

Sulfate-reducing bacteria Desulfobulbus sp. strain BH from a freshwater lake in Guizhou Province, China

Sulfate-reducing bacteria (SRB) from the anaerobic sediments of the freshwater Baihua Lake (Guizhou Province, China) at eutrophicated sites polluted with heavy metals, particularly with mercury, have been studied. SRB belonging to the genus Desulfobulbus prevailed. A detailed study of the dominating Desulfobulbus isolate designated as strain BH revealed its difference in regards to genetic, morphological, physiological, and biochemical characteristics from the other species of this genus. Strain BH utilized a wide range of organic substrates, demonstrated a high level of hydrogen sulfide production, and could be considered an important component of the microbial community in the polluted lake.