非流体介质中多环芳烃污染的微生物固定化修复技术

非流体介质中多环芳烃(PAHs)污染的修复是目前环境工作者所面临的艰巨而紧迫的任务.由于非流体介质环境的特殊性,常规修复方法难以高效地发挥作用,传统微生物修复技术采用的游离微生物也存在许多弊端.而微生物固定化能大幅度地提高参加反应的微生物浓度,避免优势菌受土著菌的恶性竞争,增强微生物的耐环境冲击性.微生物固定化技术在一定程度上克服了传统工艺的不足,因而广泛应用于流体介质(废水等)和半流体介质(泥浆等)环境污染的修复.在概述固定化微生物技术的特点和分析国内外研究进展的基础上,指出将该技术应用于非流体介质中PAHs污染的原位修复领域的可行性,并论述了需要解决的关键科学问题,提出了利用微生物固定化技术修复非流体介质中PAHs污染的未来研究课题.     

固定化微生物技术在受污养殖水体和水华水域生物修复中的应用

固定化微生物技术作为一种新型的生物修复技术,具有高效、稳定、生物安全性较高等特点,已经广泛应用于各种污染水体的净化修复之中,也包括受污染日益严峻的近海养殖水体。综述从固定化微生物技术的出现和应用出发,对不同固定方法的优劣及其所擅长降解的污染物类型进行对比,对不同载体的特点进行分析,总结了固定化微生物技术在近海养殖水体污染修复的研究概况,并对当前该技术应用存在的问题进行分析和未来研究的方向进行展望。     

固定化微生物技术修复多氯联苯污染土壤的应用前景

多氯联苯(PCBs)是一类持久性有机污染物,生物危害性极大,流入环境后易被土壤颗粒吸附而长期蓄积在土壤中.运用生物技术修复PCBs污染土壤一直是国内外学者研究的热点.其中固定化微生物技术因其独特的优势而具备了较高的开发与应用价值.本文简要评述了当前PCBs污染土壤的主要修复技术,并通过分析固定化微生物技术的特点及其在有机污染土壤修复方面的研究进展,论述了运用该技术修复PCBs污染土壤的可行性以及所面临的关键科学问题.     

微生物固定化技术在水体修复中的研究进展

微生物固定化技术目前已被广泛应用于环境生态修复等领域，对此，文章围绕微生物固定化技术，基于前人的研究成果和目前微生物固定化技术的相关研究进展，及其在水体修复方面的应用展开了探讨，并提出了发展展望，期望能够为微生物固定化技术的发展应用提供有益参考。     

低温微生物修复石油烃类污染土壤研究进展

耐冷菌、嗜冷菌等低温微生物广泛存在于极地、高山以及高纬度等土壤环境中,是石油烃类污染物在低温条件下降解与转化的重要微生物资源.利用低温微生物的独特优势,石油污染土壤的低温生物修复技术的研究成为当前热点领域.本文系统综述了低温石油烃降解菌的分类及冷适机制,低温微生物对不同类型石油烃组分的降解特征和降解机理,低温环境中接种降解菌、添加营养物质和表面活性剂等强化技术在石油污染土壤中生物修复的应用.以及微生物分子生物学技术在低温微生物降解石油烃的研究现状,为拓展我国石油污染土壤生物修复技术提供参考.     

微生物厌氧呼吸与有机污染水体沉积物修复

水体沉积物有机污染是当前全球关注的重要环境问题。微生物具有呼吸和代谢多样性,能以多种污染物作为厌氧呼吸的电子供体或受体,与周围环境中的生物和非生物因素组成代谢网络耦合有机污染物降解转化,是有机污染水体沉积物修复的重要驱动者。本文重点综述了微生物厌氧呼吸、电子传递网络及其对有机污染水体沉积物的修复机制研究进展,并对有机污染水体沉积物微生物修复理论和技术研究的问题和挑战进行了探讨。     

微生物固定化技术在河流治理中的应用及研究进展

微生物在污染物去除中发挥着重要作用,但是河流自身条件会限制微生物持久有效的发挥净化功能,微生物固定化技术则可以改善这种状况,起到强化微生物处理效果的作用。分析了微生物直接用于受污染河流治理的限制因素,阐述了微生物固定化技术的高效作用机理和改进方法,并对当前该技术应用存在的问题进行分析和未来研究的方向进行展望,以期为固定化技术用于河流污染治理提供理论参考和技术借鉴。     

微生物降解硝基苯废水的研究进展

硝基苯是一种淡黄色,苦杏仁味的高毒物质,且难生物降解,广泛应用于化工、染料、制药等工业,具有稳定化学性质、高毒性和易在生物体内积累的优先污染物.硝基苯的大量排放对环境构成了严重威胁,对该污染物的处理一直是研究焦点.对硝基苯的降解方法主要有物理法、化学法和生物法,生物法费用低、不易造成二次污染,可以最大程度的降解污染物.微生物降解在硝基苯类化合物废水治理和污染环境修复方面具有明显优势,近年来人们己筛选出许多硝基苯高效降解菌.从降解菌的种类,降解途径,共代谢,固定化,基因工程,高盐条件下的降解等方面阐述了硝基苯生物降解的最新研究进展.     

微生物强化修复石油污染土壤的研究进展

微生物修复被认为是去除石油污染物和修复石油污染土壤的一种经济、高效且无二次污染的绿色清洁技术。受土壤环境条件和石油污染物性质等因素制约,土壤中土著石油降解微生物常存在数量不足、活性偏低、生长缓慢等问题,导致修复效果不佳、修复周期偏长。微生物强化修复技术可有效提高微生物降解效能,通过投加具有降解效能的功能菌株或菌剂、营养物质、表面活性剂、生长基质及固定化微生物等手段,可改善提升土著微生物对石油污染土壤的修复效果。文中梳理了已报道的石油降解微生物的种类,总结了微生物修复石油污染土壤的主要影响因素,阐述了微生物强化修复石油土壤的多种有效策略,提出了微生物强化修复石油污染的未来发展方向。     

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。     

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。     

微生物细胞表面呈现技术研究进展

微生物细胞表面工程是近年来发展起来的,它利用细胞表面展示技术使外源蛋白固定化于细胞表面,从而生产微生物细胞表面蛋白。微生物细胞表面工程可用于细胞催化剂、细胞吸附剂、活疫苗、生物传感器的开发等。微生物细胞表面工程具有广阔的应用前景,但是国内对这一领域的研究刚起步。在介绍细胞表面工程的基础上,对微生物细胞表面工程技术进展进行了综述,展望了对该技术的发展。     

微生物细胞表面工程研究进展*

微生物细胞表面工程是近年来发展起来的,它利用细胞表面展示技术使外源蛋白固定化于细胞表面,从而生产微生物细胞表面蛋白。微生物细胞表面工程可用于细胞催化剂、细胞吸附剂、活疫苗、生物传感器的开发等。微生物细胞表面工程具有广阔的应用前景,但是国内对这一领域的研究尚刚起步。在介绍了细胞表面工程的基础上,对微生物细胞表面工程技术进展进行了综述,并对该技术的发展给予展望。     

Calcium controls the assembly of the photosynthetic water-oxidizing complex: a cadmium(II) inorganic mutant of the Mn4Ca core

Perturbation of the catalytic inorganic core (Mn4Ca1OxCly) of the photosystem II-water-oxidizing complex (PSII-WOC) isolated from spinach is examined by substitution of Ca2+ with cadmium(II) during core assembly. Cd2+ inhibits the yield of reconstitution of O2-evolution activity, called photoactivation, starting from the free inorganic cofactors and the cofactor-depleted apo-WOC-PSII complex. Ca2+ affinity increases following photooxidation of the first Mn2+ to Mn3+ bound to the 'high-affinity' site. Ca2+ binding occurs in the dark and is the slowest overall step of photoactivation (IM1-->IM1* step). Cd2+ competitively blocks the binding of Ca2+ to its functional site with 10- to 30-fold higher affinity, but does not influence the binding of Mn2+ to its high-affinity site. By contrast, even 10-fold higher concentrations of Cd2+ have no effect on O2-evolution activity in intact PSII-WOC. Paradoxically, Cd2+ both inhibits photoactivation yield, while accelerating the rate of photoassembly of active centres 10-fold relative to Ca2+. Cd2+ increases the kinetic stability of the photooxidized Mn3+ assembly intermediate(s) by twofold (mean lifetime for dark decay). The rate data provide evidence that Cd2+ binding following photooxidation of the first Mn3+, IM1-->IM1*, causes three outcomes: (i) a longer intermediate lifetime that slows IM1 decay to IM0 by charge recombination, (ii) 10-fold higher probability of attaining the degrees of freedom (either or both cofactor and protein d.f.) needed to bind and photooxidize the remaining 3 Mn2+ that form the functional cluster, and (iii) increased lability of Cd2+ following Mn4 cluster assembly results in (re)exchange of Cd2+ by Ca2+ which restores active O2-evolving centres. Prior EPR spectroscopic data provide evidence for an oxo-bridged assembly intermediate, Mn3+(mu-O2(-))Ca2+, for IM1*. We postulate an analogous inhibited intermediate with Cd2+ replacing Ca2+.     

Characterization of airborne fungal levels after mold remediation

The overall objective of this project was to evaluate levels of airborne fungi present after a mold remediation project and determine the effectiveness of this remediation using airborne mold levels to determine the success of these projects. Andersen N6 (viable) and Air-O-Cell (non-viable) sampling techniques were utilized. Both test methodologies demonstrated that levels of mold in the successfully remediated portions of buildings were significantly different (p<0.05) from the levels found in non-complaint and outdoor samples from the same building, respectively. Conversely, levels in unsuccessful remediation projects were not significantly different (p>0.05) to non-complaint and outdoor samples. Both techniques showed high variability in the overall mold levels found between sites; however, the ratios of specific mold groups in each area tested, within the same site, were remarkably similar. The use of either viable or non-viable mold sampling techniques after mold remediation is essential for determining the success of such projects. This project demonstrates the relationship between mold levels and the success of a mold remediation projects, and will assist in the interpretation of data collected at the conclusion of a mold remediation project.     

Changing pattern of cytokeratin 7 and 20 expression from normal epithelium to intestinal metaplasia of the gastric mucosa and gastroesophageal junction

It is currently unclear whether intestinal metaplasia at the esophagogastric junction and in the distal esophagus represent a continuum of the same underlying disease process, i.e., gastroesophageal reflux, or constitute different entities with a different pathogenesis. Biopsies below the Z line might show specialized epithelium in some patients and the question is whether this is another form of short segment Barrett's esophagus or whether it is related to a generalized atrophic process of the stomach. Data from recent studies regarding the expression of cytokeratin CK7 and CK20 in intestinal metaplasia (IM) found at the gastroesophageal junction are conflicting. Prompted by these data we undertook the present study: a) to evaluate the expression of CK7 and CK20 in IM of the gastric cardia and to compare the findings with those in patients with Barrett's esophagus and IM of the gastric corpus and antrum mucosa; and b) to evaluate the immunophenotype of non-intestinalized cardiac mucosa and to compare it with that of normal gastric epithelium. We studied the expression of CK7 and CK20 on biopsy specimens from patients with long-segment Barrett's esophagus (n=17) and surgical resection and biopsy specimens of gastric cardia (n=15), corpus (n=14) and antrum (n=22) from patients with histological evidence of IM. Eighty-four biopsy specimens from 42 patients (antrum n=15, corpus n=20, cardia n=7) without evidence of IM were studied as a control group. We observed an immunophenotype characterised by diffuse moderate to strong CK7 staining on the surface and crypt epithelium combined with strong CK20 staining on the surface and superficial part of the crypts in 94.1% (16/17) of the cases with long-segment Barrett's esophagus, but in none of the 36 cases with IM in distal stomach (antrum and corpus). IM in the gastric cardia expressed the immunophenotype seen in IM of the gastric mucosa in 93.3% (14/15) of the cases. On the other hand, normal cardiac epithelium expressed patchy strong CK7 staining on the surface epithelium and on both, superficial and deep parts of the pits combined with patchy strong CK20 staining on the surface epithelium and superficial pits, a feature permitting distinction of the normal cardiac epithelium from those of the normal gastric antrum and corpus epithelium. We conclude that the expression of cytokeratins 7 and 20 can be used to distinguish the origin of IM of the gastroesophageal junction. The CK7/20 immunophenotype of IM in the gastric cardia closely resembles that of the IM in the gastric antrum and corpus and is different from IM in long-segment Barrett's esophagus. In contrast, the CK7/20 immunophenotype of the cardiac epithelium is different from that of the gastric antrum and corpus mucosa, suggesting that cardiac epithelium might not be a native normal gastric epithelium but one that is acquired as a consequence of longstanding inflammation. Changing pattern of CK7 and CK20 expression from normal to intestinalized epithelium suggests that IM arising from cardiac epithelium might have distinctive features.     

分子生物学方法在微生物多样性研究中的应用

微生物多样性是生物多样性的重要组成部分。由于微生物和大生物（动、植物）相比,存在着多种显著差异,因此其多样性,保护及利用也有所不同,尤其是研究方法亟待完善,提高。近年来,分子生物学方法广泛用于微生物多样性的研究并取得了一系列研究成果。本文从四个方面加以介绍：１）微生物总ＤＮＡ制备及其遗传多样性检测方法;２）１６ＳｒＲＮＡ基因序列研究;３）核酸杂交分析技术;４）ＤＮＡ动力学的研究。今后的发展趋势是加     

磁选育浸矿菌种新方法的研究--磁泳分离菌种

世界无处不有磁,磁场对整个世界产生着重大的影响。本文通过大量镜检工作,观察到从酸性矿坑水中初步分离培养得到的部分细菌对外加磁场均有微弱的趋磁性。基于菌种的这种特性,设计了磁泳装置用不同的磁场梯度分离细菌,磁泳分离的方法可以初步分离出近磁、远磁菌,这两个菌群的生理特性有着很大的差异,主要体现在其对亚铁氧化和对金属离子的浸出上,远磁菌亚铁氧化活性比近磁菌高将近50%,远磁菌对铜离子的浸出效果也比近磁菌好。近磁菌在强磁性矿物培养基中生长情况较好,而远磁菌在弱磁性矿物培养基中生长情况较好。而且,在近磁菌的纯培养菌体中分离到磁性颗粒。实验结果证明,采用磁泳用于分离体内含有磁性颗粒的细菌是可行并且有效的,这一分离技术和工艺的结合也将大大促进我国生物冶金的步伐。     

New insights into the Lpt machinery for lipopolysaccharide transport to the cell surface: LptA-LptC interaction and LptA stability as sensors of a properly assembled transenvelope complex

Lipopolysaccharide (LPS) is a major glycolipid present in the outer membrane (OM) of Gram-negative bacteria. The peculiar permeability barrier of the OM is due to the presence of LPS at the outer leaflet of this membrane that prevents many toxic compounds from entering the cell. In Escherichia coli LPS synthesized inside the cell is first translocated over the inner membrane (IM) by the essential MsbA flippase; then, seven essential Lpt proteins located in the IM (LptBCDF), in the periplasm (LptA), and in the OM (LptDE) are responsible for LPS transport across the periplasmic space and its assembly at the cell surface. The Lpt proteins constitute a transenvelope complex spanning IM and OM that appears to operate as a single device. We show here that in vivo LptA and LptC physically interact, forming a stable complex and, based on the analysis of loss-of-function mutations in LptC, we suggest that the C-terminal region of LptC is implicated in LptA binding. Moreover, we show that defects in Lpt components of either IM or OM result in LptA degradation; thus, LptA abundance in the cell appears to be a marker of properly bridged IM and OM. Collectively, our data support the recently proposed transenvelope model for LPS transport.