环境空气中微生物监测结果的影响因素研究

空气中微生物附着在雾霾颗粒物上,随呼吸进入人体危害健康,是多种疾病的致病因素,故而快速准确的监测出区域空气微生物的数量,对于后续采取防控措施具有积极意义.在国家没有出台相关监测技术标准的情况下,通过设置不同采样时间、培养时间,获取了不同实验条件下的监测结果,分析不同组别数据结果的差异性,得出细菌采样时间3~5 min,培养48h比较合适,霉菌采样时间3 min,培养72h即可的实验结论.这样既保证了采集到绝大部分微生物,同时能够尽快的得到空气中微生物菌落数量,对相关监测方法的进一步研究具有参考价值.     

板式生物滴滤塔高效净化硫化氢废气的研究

采用营养液分层喷淋、pH分别在线控制(pH 2.5、 4.5、 6.5)的板式生物滴滤塔(plate type-biotrickling filter, PTBTF)净化H₂S废气,考察PTBTF于挂膜启动及稳定运行阶段对H₂S的降解性能.结果表明,PTBTF系统在14 d内即完成挂膜,对浓度为188.6mg·m^-3的H₂S去除率达到100%;在进口浓度100～1000mg·m^-3、空床停留时间(EBRT)28～4 s的条件下,H₂S的去除率可达到99%以上;当H₂S去除率≥90%时, PTBTF系统的最大去除负荷随EBRT(3.3～6 s)的增加而增大,EBRT 6 s的最大去除负荷达到1019.0g·(m³·h)^-1;上、中、下3层填料对H₂S的去除负荷随进口H₂S负荷的波动呈显著变化;通过荧光染色观察填料上的细胞数,发现在挂膜阶段微生物数量增长明显,第125 d上层、中层和下层填料上的菌落数(以干填料计)分别达到了1.29×10⁷、 5.47×10⁸和1.07×10⁹个·g^-1;采用扫描电镜观察填料表面的生物膜,可见上填料层和下填料层的优势菌分别为杆菌和丝状菌;利用变性梯度凝胶电泳初步揭示了系统运行过程中生物群落的演替规律;通过对产物的分析,确定该PTBTF系统降解H₂S后主要产生SO^2-₄和单质硫.     

生物整治技术进展

综述了对于污染位点的难降解污染物和生物外源性污染物进行降解的原理与技术进展,生物整治的基本原理是对于具体的污染位点,应根据有利于污染物毒性降低和生物可利用性增加以微生物活性增加３个原则选择适当的治理措施,文中述及的原位和非原位生物整治技术包括：添加营养,接种外源降解菌,生物通气,土地处理,堆肥式处理,生物堆层和泥浆技术,还讨论了收集场地信息和评价治理效果的方法。     

微生物降解硝基芳香烃及其在环境保护中的应用

综述降解硝基芳烃的微生物类群,代谢途径,遗传操作及其在环境保护中的应用等方面的研究概况。     

高浓度油脂废水的微生物净化处理技术浅析

在简要介绍目前含有高浓度油脂废水的产生和排放现状之后,总结分析了最近几年来一些具有一定代表性的生物处理方法的研究成果,同时提出了今后油脂废水处理技术的一点建议。     

Dissimilatory reduction of FeIII (EDTA) with microorganisms in the system of nitric oxide removal from the flue gas by metal chelate absorption

In the system of nitric oxide removal from the flue gas by metal chelate absorption, it is an obstacle that ferrous absorbents are easily oxidized by oxygen in the flue gas to ferric counterparts, which are not capable of binding NO. By adding iron metal or electrochemical method, Fe^Ⅲ (EDTA) can be reduced to Fe^Ⅱ(EDTA).However, there are various drawbacks associated with these techniques. The dissimilatory reduction of Fe^Ⅲ(EDTA) with microorganisms in the system of nitric oxide removal by metal chelate absorption was investigated. Ammonium salt instead of nitrate was used as the nitrogen source, as nitrates inhibited the reduction of Fe^Ⅲ due to the competition between the two electron acceptors. Supplemental glucose and lactate stimulated the formation of Fe^Ⅱ more than ethanol as the carbon sources. The microorganisms cultured at 50~C were not very sensitive to the other experimental temperature, the reduction percentage of Fe^Ⅲ varied little with the temperature range of 30-50℃.Concentrated Na2 CO3 solution was added to adjust the solution pH to an optimal pH range of 6-7. The overall results revealed that the dissimilatory ferric reducing microorganisms present in the mix-culture are probably neutrophilic, moderately thermophiUc Fe^Ⅲ reducers.     

微生物对沉积物主要化学组分吸附重金属能力的影响

通过松花江水中微生物与铁、锰氧化物和腐殖酸形成的复合物质的比表面积及吸附Pb、Cd能力的分析,探讨微生物对沉积物中主要化学组分理化性质的影响及机理.结果表明:锰氧化物的比表面积大于铁氧化物和腐殖酸,与微生物结合后比表面积均不同程度增加. 固体物质的比表面积与吸附Pb和Cd的能力并不完全一致,与它们对重金属的吸附机制不同有关.复合物质的的吸附能力并不符合加和模型,微生物的存在掩盖了铁、锰氧化物和腐殖酸表面部分官能团,造成了复合物质的吸附量小于各组分的吸附量之和.     

Biodegradation kinetics of cymoxanil in aquatic system

A potential method to detoxify pesticides in aquatic system is using bioremediation. In this study, four microorganisms (Pseudomonas sp (EB11), Streptomyces sp. (EB12), Aspergillus niger (EB13) and Trichoderma viride (EB14) were isolated from cucumber leaves previously treated with cymoxanil using enrichment technique. These strains were evaluated for their potential to detoxify cymoxanil in aquatic system at the concentration level of 5×10^?4M. The effect of pH and temperature on the growth ability of the tested strains was also investigated by measuring the intracellular protein and mycelia dry weight for bacterial and fungal strains, respectively. Moreover, the remaining toxicity of cymoxanil after 28 days of incubation with tested strains was evaluated to confirm the complete removal of any toxic materials (cymoxanil and its metabolites). The results showed that the optimum pH for the growth of cymoxanil degrading strains (bacteria and fungi) was 7. A temperature of 30°C appears to be the optimum for the growth of either fungal or bacterial strains. Pseudomonas sp. (EB11) was the most effective strain in cymoxanil degradation followed Streptomyces sp (EB12), Trichoderma viride (EB14) and Aspergillus niger (EB13), with half-lives of 4.33, 9.5, 17.3 and 24.7 days, respectively. The degradation of cymoxanil by bacterial strains was much faster than fungal one. There is no remaining toxicity of cymoxanil detected in aqueous media previously treated with Pseudomonas sp. (EB11) for 28 days. The results suggest that bioremediation by Pseudomonas sp. (EB11) are promising for the detoxification of cymoxanil in aqueous media.     

秸秆还田配施化肥及微生物菌剂对水田土壤酶活性和微生物数量的影响

土壤微生物学特性是表征土壤质量的重要生物学指标。通过田间试验研究了秸秆还田配施不同配比化肥及微生物菌剂对水田土壤酶活性和微生物数量的影响。结果表明,与单施秸秆相比,秸秆还田配施N、P、K及微生物菌剂后,土壤过氧化氢酶、转化酶和尿酶活性分别提高了37.5%~68.8%、32.3%~61.5%和48.8%~102%,细菌和真菌数量分别提高了95.3%~174%、286%~351%,放线菌数量减少了34.5%~39.4%,差异显著。统计分析显示,土壤过氧化氢酶与尿酶活性之间及其酶活性与微生物数量之间关系密切。氨化细菌和硝化细菌数量主要控制土壤过氧化氢酶活性,真菌数量是转化酶活性的主要影响因素,而尿酶活性主要受细菌数量影响。秸秆还田配施微生物菌剂及平衡施肥可以促进酶活性的增强,使土壤微生物群落物种个体数增加更多,分布更为均匀。过量施用氮肥会抑制土壤酶活性和微生物的生长和繁殖。     

基于活性微生物特征的供水管壁生物膜生长特性

管网生物膜由各种活性微生物、微生物残体及有机无机杂质组成,管网生物膜的生长会导致机会致病菌寄居、管道腐蚀以及水质恶化等系列饮用水卫生问题.为研究供水管壁生物膜形成过程和附着生长活性微生物的分布特征,采用异养菌平板计数(HPC)、流式细胞术(FCM)和16S rRNA高通量测序对3种典型室内供水管材:聚氯乙烯(PVC)、无规共聚聚丙烯(PPR)、不锈钢(STS)内壁活性微生物的生长特性和群落多样性进行了分析.结果表明,PVC管壁生物量在第73 d最先达到峰值,3种管材内壁单位面积最大生物量、生物膜成熟时期生物量均呈现PVC PPR STS的规律. 3种管材表面活性细菌群落结构组成上,PVC管表面主要以硝化螺旋菌门为主,PPR和STS管以疣微菌门为主,其中STS管壁上生物膜物种丰富度最低、多样性最小,群落结构最简单. PVC和PPR管内壁表面相较STS管存在更多的蓝藻细菌和放线菌,在饮用水输配过程中更易引发饮用水嗅味问题.管材介质对管壁生物膜上微生物群落结构存在一定影响.