固相反硝化技术同时去除地下水中的硝酸盐与农药进展

概述了固相反硝化技术及其特点,综述了固相反硝化技术在去除地下水中硝酸盐与农药的研究现状,分析了反应机理及当前研究中存在的问题,并在此基础上对固相反硝化的未来核心研究方向进行了展望。     

短程硝化活性污泥微生物群落结构及羟胺代谢对短程硝化的影响

活性污泥法随着技术的成熟,已应用在高氨氮污水/废水处理中,通过不断发展衍生出的很多新型工艺也成为研究热点,短程硝化反应作为代表已逐渐体现出优越性。短程硝化能达到高效净化污水的目的,其反应中的代谢产物羟胺也和微生物类群及反应产物之间有着至关重要的影响。反应器中活性污泥的微生物群落结构和动态密切相关,探究微生物群落结构能帮助生物强化、优化参数,提高脱氮效率。本文主要总结了近年来有关短程硝化/半短程硝化活性污泥微生物群落组成与结构及其与反应器处理效率之间的关系,以及羟胺代谢对短程硝化的影响等方面的研究进展,这些研究加深了对微生物群落结构和污水处理工艺之间的认识,但充分发掘生物信息、提高工艺效能之路仍然充满挑战,还需利用氮平衡方法、Real-time PCR法等多种生物技术手段对短程硝化进行全方位研究,为实践提供坚实的理论基础。     

浓香型白酒大曲微生物群落结构研究进展

大曲通常作为发酵剂用于酿造传统中国白酒,其提供各类微生物菌系和酶系启动白酒发酵,影响白酒风味和独特风格。近年来,对大曲微生物群落结构的研究成为研究热点,研究人员对大曲微生物群落结构、基因功能和功能微生物等进行了广泛而深入的研究,对大曲微生物组成、变迁规律和功能的认识逐渐清晰。本文综述了浓香型大曲微生物群落结构分析方法、主要微生物组成、重要功能微生物和微生物溯源,为研究大曲微生物群落结构、优化大曲生产工艺和改善白酒品质提供一定的理论依据。     

纳木错湖水体固碳微生物数量、群落结构及其驱动因子

湖泊是微生物固碳的主要生态系统之一,但青藏高原湖泊水体固碳微生物群落的研究还罕见报道。以纳木错为例,采用定量PCR和克隆文库方法,研究湖水中cbbL ID基因丰度和固碳微生物群落组成,并分析其与环境参数的关系。结果显示:纳木错湖水中存在较高丰度的cbbL ID类型固碳微生物,从表层到底层呈增加趋势,T2点底层达到最高值(6.37×10~8拷贝L~(-1)湖水)。cbbL ID类型固碳微生物共分四个类群,即不等鞭毛类(Stramenopiles),定鞭藻纲(Haptophyceae),蓝藻(Cyanobacteria)和隐藻门(Cryptophyta)。其中占主要的是Stramenopiles和Haptophyceae。Stramenopiles类群的多样性较高(含7个纲,13个科),其他类群只有1个科。相关性分析表明Stramenopiles和Haptophyceae出现频率存在显著的负相关关系(P0.01)。湖水深度和pH与湖水cbbL ID基因丰度显著相关(P0.05,P0.01)。叶绿素含量与Stramenopiles和Haptophyceae出现频率显著相关(P0.01)。     

口腔微生物群落结构分析方法的研究进展

牙菌斑是口腔常见感染性疾病——龋病和牙周病的始动因子,主要由微生物构成。在口腔中发现的700余个种属或种系型的细菌中,有50%左右未获得培养。基于分子生物学的方法在口腔微生态和感染性疾病的病因研究中已经成为不可或缺的技术。近年来,以16S rRNA基因为基础建立的分子生物学技术正逐步广泛用于微生物群落的分析,跨越了传统的微生物培养,直接对不同生态系,包括人类口腔的微生物组成进行了研究。本文主要介绍16s rRNA基因的分子分析技术,以及它们在口腔微生物群落结构分析研究中的应用,另外还简要介绍了一些尚未应用于口腔的新技术。     

氢自养微生物的驯化及其反硝化特性研究北大核心

【目的】本研究筛选出弱酸性环境下利用无机碳源进行高效脱氮的氢自养微生物,探究不同无机碳源对体系反硝化能力的影响,以及长期驯化过程中反应器内水质参数、微生物群落结构和脱氮周期变化规律。【方法】氢自养微生物的驯化采用一种成本低廉、气密性优良、可计算氢气利用率的序批式反应器,通过及时向装置内补充氢气、无机碳源、营养液和硝酸盐对微生物进行连续驯化。【结果】驯化的微生物利用NaHCO_(3)和CO_(2)作为混合无机碳源对硝酸盐的脱氮效果要优于单一使用NaHCO_(3);在环境温度为20℃,pH为6.3-7.0,硝态氮初始投加量为15 mg-N/L时,NO_(3)--N最高反应速率为1.374 mg-N/(L·h),氢气最高利用率为43.4%,脱氮周期为16 h,且脱氮过程中无亚硝酸盐积累;驯化得到的微生物主要为嗜酸菌属(Acidovorax),占比达84.4%。【结论】利用本研究的装置和驯化方法对土著微生物进行脱氮驯化是可行且高效的,可筛选出在弱酸性环境下利用无机碳源进行反硝化的氢自养微生物,为地下水中硝酸盐污染的生物修复提供理论依据,也为后续进一步研究弱酸性环境下氢自养微生物同时脱氮固铀奠定基础。     

油藏微生物群落结构解析

微生物采油(Microbial enhanced oil recovery,MEOR)以其费用低廉、无环境污染、施工简单、应用范围广等优点得到学者以及油田开发者的认同。油藏中的微生物类型多样且功能各异,可促进原油的开采,大幅度提高油气资源的利用率。因此分析油藏中微生物的类型和组成,了解土     

林冠受损对小坑林场土壤固碳微生物群落结构的影响

【目的】以典型南亚热带常绿阔叶林小坑林场土壤为研究对象,模拟2008年冰雪灾害对森林造成的损伤设置实验,分析不同林冠开度和凋落物输入量对土壤固碳微生物群落结构的影响。【方法】试验设置对照(CN)、损伤处理+移除处理枝叶(TR)、损伤处理+保留处理枝叶(TD)、未处理+添加处理枝叶(UD)4个处理,受损处理一年后,采用MiSeq高通量测序技术对土壤固碳微生物的功能基因cbbL进行测序分析。【结果】通过生物信息学及统计学分析表明,森林林冠损伤后林冠开度和凋落物输入量增加,导致土壤固碳微生物种群数量降低,多样性增加,群落结构也受到影响,亚硝化螺菌属(Nitrosospira)明显增加,成为优势种群,而原来的优势菌群慢生根瘤菌属(Bradyrhizobium)明显减少。主成分分析(PCA)表明,与对照相比,其他3个样地的土壤固碳微生物结构均发生明显改变。【结论】模拟林冠损伤处理一年后,凋落物的大量骤然输入和林冠开度增大提高了土壤固碳微生物群落多样性,但降低了其种群数量,影响了土壤固碳微生物群落结构,这为进一步的研究提供了依据。     

生物膜法强化净化氨氮污染水体及其微生物群落解析

【目的】比较不同营养条件及挂膜方式下生物膜法对氨氮污染水体的净化效果及其功能微生物群落结构。【方法】设置空白(Blank)、自然成膜(Raw)、预附脱氮菌强化挂膜(PCC)3组生物膜反应器,利用末端限制性片段长度多态性(T-RFLP)技术和非度量多维标度(NMDS)分析方法对生物膜反应器转化氨氮过程中微生物群落结构及其演替过程进行动态解析。【结果】在C/N=1:1时,除PCC在起始阶段短暂具有较高的氨氮脱除效率外,Blank、Raw和PCC最终均表现出较低的氨氮转化效率(10%-20%)。改变C/N=2:1后,Raw和PCC对人工合成污水中NH4+-N的转化率均提高至95%以上,而且Raw与PCC的群落结构在C/N=2:1时具有较高的相似性,优势菌群主要为γ-变形菌纲(Gammaproteobacteria)、放线菌纲(Actinobacteria)和硝化螺菌纲(Nitrospira)。【结论】C/N是影响生物膜反应器氨氮去除效果及驱动生物膜反应器中细菌群落结构发生改变的重要因子。     

海水养殖尾水处理系统中微生物群落对水处理阶段的响应

为了阐明南美白对虾高位池养殖尾水处理系统中不同水处理阶段微生物群落演替机制, 利用16S rRNA基因高通量测序技术分析了水体和生物膜的微生物群落结构。结果显示, 在水处理系统中主要是变形菌门(Proteobacteria)、浮霉菌门(Planctomycetes)、拟杆菌门(Bacteroidetes)、蓝细菌门(Cyanobacteria)、放线菌门(Actinobacteria)及酸杆菌门(Acidobacteria), 平均占细菌总OTU的88.61%。生物膜中生物多样性指数普遍高于水样, 与水体的共有菌为320种, 载体不同是造成群落结构差异的主要原因, 黏土陶粒和北美海蓬子(Salicornia bigelovii)根系是硝化作用的主要反应场所。在属水平上筛选出160种微生物, 主要属于变形菌门、拟杆菌门、浮霉菌门、蓝细菌门、厚壁菌门(Firmicutes)及放线菌门, 它们能够较好地区分菌群的来源及水处理的反应阶段。研究揭示了不同水处理阶段以及不同生物填料中微生物动态变化情况, 为今后的海水养殖尾水处理提供理论依据和技术参考。     

污染土壤微生物群落结构分子鉴定技术研究进展

土壤微生物群落结构多样性检测是土壤修复、监测、评估时的一个重要参数。由于绝大多数微生物在实验室条件下是不可培养,因而早期依赖于微生物培养的检测结果代表性不强。20世纪90年代以来,不依赖于微生物培养的分子生物学方法是研究微生物群落结构的重要手段。该文对近年来土壤污染微生物群落结构研究所采用的主要分子生物学方法按照其原理进行了比较、分析、总结。根据不同技术的灵敏度、优缺点分析了其适用范围。指出了目前技术中存在的一些共性问题和缺陷并展望了土壤修复领域分子生物学技术的发展趋势。     

Microbial Community Analysis and Effects of Fe(II)/Mn(II) Ratio on Denitrification in the Mixotrophic Biological Reactor

In this study, the denitrification performance of the mixotrophic biological reactor was investigated under varying Fe(II)/Mn(II) molar ratio conditions. Results indicate that the optimal nitrate removal ratio occurred at an Fe(II)/Mn(II) molar ratio of 9:1, pH of 7, with an HRT of 10?h. When the reactor was performing under optimal conditions, the nitrate removal reached 100.00% at a rate of 0.116?mmol·L^?1·h^?1. The proportion of oxidized Fe(II) and Mn(II) reached 99.29% and 21.88%, respectively. High-throughput sequencing results show that Pseudomonas was the dominant species in the mixotrophic biological reactor. Furthermore, the relative abundance of Pseudomonas and denitrification performance was significantly influenced by variation in the Fe(II)/Mn(II) molar ratio.     

Risk Assessment,Microbial Communities,and Pollution-Induced Community Tolerance

Until recently, parameters from microorganisms were generally not included in risk assessment at a comparable level to animals and plants. However, the major part of global biomass, biodiversity, and ecosystem processes is present in the microbial world and microbiological techniques applicable to risk assessment are becoming available. Two microbial indicators are described based on the usage of multiwell plates with different substrates and a redox indicator for monitoring mineralisation. With both techniques autochthonous microbial communities are analysed. Producing functional fingerprints of the microbial community gives insights into the composition of different functions. This is equivalent to observations of ecological abundance and species composition. When lack of reference sites or reference data renders risk assessment difficult, measurement of the pollution-induced community tolerance (PICT) can provide useful information.     

生物造粒流化床微生物落结构及其动态变化

为了研究生物造粒流化床污水处理反应器颗粒污泥中微生物群落结构及其动态变化,分别从生物造粒流化床10、60、110cm处取颗粒污泥,通过细胞裂解直接提取颗粒污泥细菌基因组DNA。以细菌和古细菌16S rRNA基因通用引物530F/1490R,对活性污泥中提取的细菌基因组DNA进行PCR扩增,长约1kb的PCR扩增产物纯化后经变性梯度凝胶电泳(DGGE)分离,获得微生物群落的DNA特征指纹图谱。结果显示,生物造粒流化床反应器颗粒污泥中的微生物群落非常丰富,在10cm处微生物的种属达到23种,60cm处为21种,110cm处为20种;生物造粒流化床不同高度都有一些各自的特有种属和共有种属,反应器不同高度的微生物群落演替不明显,微生物群落相似性为83.1%,群落结构较为稳定。     

Microbial Community Structure and Carbon-Utilization Diversity in a Mine Tailings Revegetation Study

Restoration of metals‐contaminated environments requires a functional microbial community for successful plant community establishment, soil development, and biogeochemical cycling. Our research measured microbial community structure and carbon‐utilization diversity in treatment plots from a mine waste revegetation project near Butte, Montana. Treatments included two controls (raw tailings) either (1) with or (2) without tilling, (3) shallow‐tilled lime addition, (4) deep‐tilled lime addition, (5) lime slurry injection, (6) topsoil addition, and (7) an undisturbed area near the tailings. Microbial community structural differences were assayed by plate counts of heterotrophic bacteria, actinomycetes, fungi, and bacterial endospores, and quantification of arbuscular mycorrhizae colonization. Metabolic diversity differences were assessed by carbon‐utilization profiles generated with Biolog microtiter plates. Heterotrophic bacteria counts were significantly higher in the limed and topsoil treatment plots than the control plots, and the actinomycete and fungal counts increased in the tilled control plot as well. Endospore counts were significantly higher in the topsoil addition and the undisturbed plots than the other treatment plots. Carbon‐utilization activity was very low in untreated plots, intermediate in lime‐treated plots, and very high in topsoil and undisturbed plots. Arbuscular mycorrhizae (AM) colonization levels of two grass species showed low levels of colonization on control, shallow‐limed, and lime slurry‐injected plots, and high levels on the deep‐limed and topsoil‐addition plots. Plant and soil system components increased across the treatment plots, but individual components responded differently to changing environmental conditions.     

Microbial Community Structure and Denitrification in a Wetland Mitigation Bank

Wetland mitigation is implemented to replace ecosystem functions provided by wetlands; however, restoration efforts frequently fail to establish equivalent levels of ecosystem services. Delivery of microbially mediated ecosystem functions, such as denitrification, is influenced by both the structure and activity of the microbial community. The objective of this study was to compare the relationship between soil and vegetation factors and microbial community structure and function in restored and reference wetlands within a mitigation bank. Microbial community composition was assessed using terminal restriction fragment length polymorphism targeting the 16S rRNA gene (total bacteria) and the nosZ gene (denitrifiers). Comparisons of microbial function were based on potential denitrification rates. Bacterial community structures differed significantly between restored and reference wetlands; denitrifier community assemblages were similar among reference sites but highly variable among restored sites throughout the mitigation bank. Potential denitrification was highest in the reference wetland sites. These data demonstrate that wetland restoration efforts in this mitigation bank have not successfully restored denitrification and that differences in potential denitrification rates may be due to distinct microbial assemblages observed in restored and reference (natural) wetlands. Further, we have identified gradients in soil moisture and soil fertility that were associated with differences in microbial community structure. Microbial function was influenced by bacterial community composition and soil fertility. Identifying soil factors that are primary ecological drivers of soil bacterial communities, especially denitrifying populations, can potentially aid the development of predictive models for restoration of biogeochemical transformations and enhance the success of wetland restoration efforts.Wetlands provide more ecosystem services (e.g., flood control, water purification, nutrient cycling, and habitat for wildlife) per hectare than any other ecosystem (16). Riparian wetlands, in particular, are sites of intense biogeochemical activity and play an important role in improving water quality, recycling nutrients, and detoxifying chemicals (41). Changing patterns of land use over the last century have resulted in the loss of over half of the wetlands in the contiguous United States (17) and about 60% of wetlands in the Midwestern United States (82). The loss of ecosystem services through conversion of wetlands to alternative (primarily agricultural) land uses exacerbates nutrient pollution and eutrophication of downstream ecosystems (57). Declines in wetland acreage have continued despite a federal policy goal of no-net-loss of wetland acreage and function adopted in 1990 (7, 55). Wetland mitigation projects provide compensation for impacted wetlands and aim to replace the critical functions provided by wetlands. Despite decades of wetland mitigation, however, restoration efforts frequently fail to reestablish desired levels of ecosystem services. Restoration outcomes remain uncertain, and more information is necessary in order to improve monitoring and assessment of wetland development (13, 18, 50, 80).One approach to wetland compensation is through mitigation banks. These sites are areas that are restored, established, enhanced, or preserved for replacement of wetlands that will be affected by future land use change. Mitigation banks are considered “third-party” compensatory mitigation, where the permittee (e.g., developer planning to destroy a wetland) is responsible for purchasing wetland credits in acreage, but the wetland bank is established and managed by another party (24). Wetland mitigation banks have unique characteristics that distinguish them from smaller individual restoration projects (7, 69, 81). Due to their size, wetland mitigation banks are especially heterogeneous and may have a great deal of within-site variability in hydrology and nutrient status, making it challenging to implement a single restoration design. Thus, wetland mitigation banks require intense management and monitoring for improved success (7, 69, 81).Restoration efforts such as mitigation banks aim to replace chemical, physical, and biological ecosystem functions of wetlands that have been lost through anthropogenic disturbance (24). Monitoring of wetland mitigation sites has largely focused on measures of macro-scale community structure (e.g., vegetation surveys) (52) along with measures of hydrology and soil type (24). Measurement of vegetation is a common proxy for wetland performance but does not provide an accurate assessment of wetland function (6, 52). Quantitative assessment is achievable, however, for ecosystem services such as water quality improvement through nitrate removal, where well-characterized microbial mechanisms underlie denitrification processes.The link between microbial community structure and function in a restoration context is a topic of current interest (33). Relating microbial community composition and dynamics to chemical, physical, and biological variables can help to reveal important ecological drivers of microbial communities and their activities (26, 35, 42). Conserved bacterial functional genes related to specific biogeochemical transformations allow evaluation of the community structure of microbial populations directly involved in these processes (49, 60, 63, 77, 79). Assessing the diversity of microorganisms that are specifically involved in denitrification is possible through amplification of the nosZ gene, which encodes the catalytic subunit of nitrous oxide reductase, the enzyme responsible for the final step of denitrification (60, 63, 66). Phylogenetically diverse microorganisms can carry out denitrification though the majority of previously described denitrifiers belong to subphyla within the Proteobacteria (53, 56, 60, 61). Denitrification is a facultative process that occurs only under anaerobic conditions (53, 75). Complete denitrification to N₂ is more prevalent in anaerobic, saturated wetland ecosystems (14, 76), and incomplete denitrification to N₂O is the less desirable, more common endpoint of denitrification under more aerobic, drier conditions (14, 62). While the environmental factors (e.g., oxygen, carbon, nitrate, and pH) that influence bulk denitrification rates have been well characterized (31, 72), the influence of these factors on the composition of denitrifier communities, particularly in a restoration context, is unclear. Understanding the relationship between the microbial populations responsible for nitrogen transformations and easily measured environmental parameters (e.g., soil chemical and physical measures) could lead to assessment metrics that are linked directly to ecosystem functions such as denitrification and bridge the current gap in functional assessment methods (36, 60, 70).The objectives of this study were (i) to compare the microbial and plant community composition in restored wetlands to the composition in adjacent reference floodplain forest wetlands; (ii) to assess the relationship between microbial community composition (based on terminal restriction fragment length polymorphism [T-RFLP]) and potential denitrification activity throughout the mitigation bank; and (iii) to examine soil factors correlated with microbial community composition using both phylogenetic and functional gene markers. As soil environmental conditions affect microbial community structure and activity, we expected that sites where wetland hydrology and soil chemistry have been successfully restored would harbor microbial assemblages that are similar in composition and denitrification function to those observed in reference wetlands within this mitigation bank.     

Long-Term Explosive Contamination in Soil: Effects on Soil Microbial Community and Bioremediation

Explosive contamination in soil is a great concern for environmental health. Following 50 years of munitions manufacturing and loading, soils from two different sites contained ≥ 6,435 mg 2,4,6-trinitrotoluene (TNT), 2,933 mg hexahydro-1,3,5-trinitro-1,3,5-triazine (RDX) and 2,135 mg octahydrol-1,3,5,7-tetranitro-1,3,5,7-tetrazocine (HMX) kg^{? 1} soil. Extractable nitrate-N was as high as 315 and ammonium-N reached 150 mg N kg^{? 1} soil. Water leachates in the highly contaminated soils showed near saturation levels of TNT and RDX, suggesting great risk to water quality. The long-term contamination resulted in undetectable fungal populations and as low as 180 bacterial colony forming units (CFU) g^–1 soil. In the most severely contaminated soil, dehydrogenase activity was undetectable and microbial biomass carbon was very low (< 3.4 mg C _mic kg^–1 soil). The diminished biological activity was a consequence of long-term contamination because short-term (14 d) contamination of TNT at up to 5000 mg TNT kg^–1 soil did not cause a decline in the culturable bacterial population. Natural attenuation may not be a feasible remediation strategy in soils with long-term contamination by high concentrations of explosives.     

复合微生物菌剂在剩余污泥堆肥中的作用研究

应用复合微生物菌剂对剩余污泥进行堆肥试验,较系统地研究了复合微生物菌剂在剩余污泥堆肥系统中的作用。结果表明:接种复合微生物菌剂进行剩余污泥堆肥,与对照组相比,不但能够提高堆肥温度,而且高温持续时间长,堆肥反应速率加快,腐熟时间缩短,当接种量为7%(体积比)时,腐熟时间比对照组提前了12 d。     

Identification of the Microbial Community Structure and Potential Mechanism of Environmental Adaptation in Contaminated Environments

Purpose: To assess the bacterial community structure and the possible mechanism underlying the environmental adaption in contaminated habitats.Methods: The 60-mer oligonucleotide multibacterial microarray (GSE38004) was downloaded from the Gene Expression Omnibus database. The changes in the abundance of bacterial populations and genes in contaminated habitats were assessed based on the gene expression profiles. Then the potential function of the genes and their involved pathways were predicted by a bioinformatics approach.Results: A total of 25 bacterial populations had different abundance between contaminated habitats and uncontaminated area, of which Sphingobium herbicidovorans (S. herbicidovorans) and Pseudomonas pavonaceae (P. pavonaceae) involved in 23 populations were determined to have higher abundance in contaminated areas. Additionally, 184 genes involved in anaerobic respiration and cellular respiration were detected to have potential bioremediation. The genes of MDH (Mannitol-1-phosphate/altronate dehydrogenases) and fadE (acyl-CoA dehydrogenase) may play key roles in the mechanism of metabolic adaption.Conclusions: S. herbicidovorans and P. pavonaceae were the predominant bacterial groups in contaminated sites for the various metabolic potential and antibiotic resistances. The significant genes (MDH, fadE) and pathways (citrate cycle, pyruvate metabolism, fatty acid metabolism) played key roles in the adaptive response of microorganisms in contaminated environment.