好氧反硝化菌Achromobacter sp.L16的脱氮特性

在垃圾渗滤液中分离出一株异养硝化-好氧反硝化菌L16,经过形态观察和16S rDNA基因序列分析鉴定为Achromobacter sp.,L16对氨氮和硝酸盐氮的去除率分别为61.94%和98.40%。对菌株好氧反硝化和异养硝化培养条件进行优化结果表明:L16在以硝酸盐为氮源、柠檬酸钠为碳源、C/N为20、培养温度为30℃、培养转速为150 r/min条件下硝酸盐氮去除率为99.74%,总氮去除率58.90%。L16在以氨氮为氮源、柠檬酸钠为碳源、C/N为20、培养温度为30℃、培养转速为200 r/min条件下氨氮去除率提高到93.41%,总氮去除率86.33%。优化后L16具有高效的异养硝化-好氧反硝化能力,可将氮素大部分转化为气体和菌体胞内氮,具有潜在的实际废水应用价值。     

基于响应面法对一株好氧反硝化菌脱氮效能优化

【目的】水体富营养化是当今我国水环境面临的重大水域环境问题,氮素超标排放是主要的引发因素之一。好氧反硝化菌构建同步硝化反硝化工艺比传统脱氮工艺优势更大。获得高效的好氧反硝化菌株并通过生长因子优化使脱氮效率达到最高。【方法】经过序批式生物反应器(Sequencing batch reactor,SBR)的定向驯化,筛选获得高效好氧反硝化菌株,采用响应面法优化好氧反硝化过程影响总氮去除效率的关键因子(碳氮、溶解氧、pH、温度)。【结果】从运行稳定的SBR反应器中定向筛选高效好氧反硝化菌株Pseudomonas T13,采用响应面法对碳氮比、pH和溶解氧关键因子综合优化获得在18 h内最高硝酸盐去除率95%,总氮去除率90%。该菌株的高效反硝化效果的适宜温度范围为25?30 °C;最适pH为中性偏碱;适宜的COD/NO3?-N为4:1以上;最佳溶解氧浓度在2.5 mg/L。【结论】从长期稳定运行的SBR反应器中筛选获得一株高效好氧反硝化菌Pseudomonas T13,硝酸盐还原酶比例占脱氮酶基因的30%以上,通过运行条件优化获得硝氮去除率达到90%以上,对强化废水脱氮工艺具有良好应用价值。     

垃圾渗滤液中好氧反硝化菌的筛选及其反硝化条件优化

从江苏省常州市某垃圾渗滤液处理厂的纯氧曝气池中提取活性污泥,筛选获得1株高效好氧反硝化菌CZ1。根据菌株形态、生理生化特性进行初步鉴定,并结合该菌株的16S rDNA基因序列分析,判定该菌株为蜡样芽胞杆菌(Bacillus cereus)。研究了菌株的好氧反硝化特性,结果表明,以硝酸钾为唯一氮源,CZ1在24h内对硝酸盐氮的去除率达到97.69%。同时考察了碳源种类、C/N、温度、初始pH以及溶解氧对该菌株好氧反硝化能力的影响,通过单因素实验获得其最佳好氧反硝化条件:温度35℃,丁二酸钠为唯一碳源,C/N为6,初始pH值为7.0~7.5,转速为160 r/min。     

好氧反硝化细菌SY-D-22的分离、优化及脱氮机理

【背景】在处理含硝酸盐氮的废水中,常见微生物不能同时高效去除硝酸盐氮和总氮,导致处理废水时往往使用多种微生物复合菌剂或者使用复杂的工艺。【目的】高效、安全地去除水中的硝酸盐氮和总氮。方法】富集筛选出一株新型高效好氧反硝化细菌,对其进行16S rRNA基因鉴定。利用响应面法对其影响脱氮因素进行优化并探索其最佳脱氮条件。研究其对含硝酸盐氮废水的反硝化能力及脱氮特性。【结果】从活性污泥中筛选获得一株新型高效好氧反硝化细菌SY-D-22,经鉴定为葡萄球菌属(Staphylococcus)。响应面法优化其最佳反硝化条件为：pH 8.18,C/N为13.39,温度31.43°C,摇床转速130 r/min。当以最佳碳源柠檬酸钠为唯一碳源时,对于100 mg/L浓度的NO₃^--N去除率可达100%,同时对于总氮(total nitrogen,TN)的去除率为95.34%,具有高效脱氮能力。【结论】从活性污泥中筛选出一株新型好氧反硝化细菌Staphylococcus SY-D-22,通过响应面法条件优化,菌株的硝酸盐氮去除率达到100.00%,总氮去除率达到...     

不同氮源下好氧反硝化菌Defluvibacter lusatiensis str.DN7的脱氮特性

研究了不同氮源下好氧反硝化菌Defluvibacter lusatiensis str.DN7的脱氮特性。结果表明:菌株均能以硝酸盐和亚硝酸盐为唯一氮源进行好氧反硝化作用。反应4 h,NO-3-N和NO-2-N的去除率分别达83.35%和85.72%。亚硝酸盐完全还原比硝酸盐提前42 h。硝酸盐还原过程中基本无亚硝酸盐积累,而亚硝酸盐还原过程中则检测到明显的硝酸盐积累,反应4 h,NO-3-N积累量达到21.83 mg/L。培养液中同时存在硝酸盐和亚硝酸盐时,菌株优先选择硝酸盐作电子受体。亚硝酸盐共存对硝酸盐还原无显著影响,但培养液中残留的NO-2-N随亚硝酸盐比例上升而增加,当亚硝酸盐比例从10%升至50%时,NO-2-N残留量由3.38 mg/L增至7.60 mg/L。少量硝酸盐的加入对亚硝酸盐的还原产生抑制作用。当硝酸盐比例为10%时,72 h NO-2-N的去除率仅为74.79%,远低于以亚硝酸盐为唯一氮源情况(去除率100%)。以氨氮为唯一氮源时,菌株同时进行异养硝化和好氧反硝化反应,72 h,NH+4-N去除率达85.66%,且基本无硝酸盐或亚硝酸盐积累。少量氨氮共存(氨氮比例<30%)有利于促进菌株的好氧反硝化作用,反之亦然。     

一株高效好氧反硝化菌的分离及特性

利用富集培养的方法从南昌市郊某养鱼塘采样分离出22株反硝化细菌,其中8株反硝化率较高,从中选择一株效果最好的作为研究对象,命名为HS-N62,对其生长特性进行了深入研究。结果表明:硝酸盐氮初始浓度为140mg/L,菌株HS-N62在12h内对硝酸盐氮的去除率可达96%,而且没有亚硝酸盐氮的积累。该菌最适生长温度范围为30°C-37°C,最适生长pH范围6.0-8.0,最适C/N比为10:1,并能利用多种碳源生长。运用正交试验探讨了该菌株最适的反硝化条件。反硝化菌株HS-N62还具有较好的除磷能力,12h除磷率达到67.7%(初始磷酸盐浓度57mg/L)。通过形态学特性和生理生化分析以及16S rRNA基因序列分析,菌株HS-N62与Pseudomonas sp.亲缘关系最为接近,相似性达99%,初步鉴定该菌为假单胞菌属(Pseudomonas sp.)。     

1株滩涂沉积物反硝化细菌的鉴定及其性能研究

利用富集培养法从江苏沿海滩涂沉积物中分离筛选获得1株具有反硝化性能的细菌,命名为MD5。通过形态学观察、糖发酵及16S r DNA序列分析对其进行了分类鉴定、系统发育地位及反硝化性能等方面的研究。结果表明,该菌株能在厌氧条件下利用硝酸钠进行反硝化反应,在初始硝酸盐质量浓度为1 500 mg/L、30℃培养条件下,144 h后培养基中硝酸盐脱除率可达90.1%;在好氧培养条件下,该菌株可使能力测试管中硝酸盐质量浓度下降89.3%。菌株MD5的形态学、糖发酵结果与盐单胞菌一致,且基因序列与盐单胞属(Halomonas)细菌Halomonas sp.IW11-1(AB305262.1)的序列同源性达到99%,表明菌株MD5为1株盐单胞属细菌。本研究分离得到的菌株MD5在厌氧和好氧条件下均具有较强的反硝化能力,对海洋沉积物脱氮具有一定的意义。     

一株好氧反硝化菌的分离及特性研究

从土壤中分离得到一株好氧反硝化细菌CY1, 该菌株在厌氧和好氧条件下均具有反硝化能力。硝酸盐氮初始浓度为137.25 mg/L, 30 h内硝酸盐氮去除率分别为99.98%(厌氧)和60.16%(好氧)。通过形态学特征、生理生化特性及16S rDNA同源性比较对菌株CY1进行鉴定, 初步判断CY1为泛养副球菌(Paracoccus pantotrophus)。     

耐碱反硝化菌株的分离鉴定与功能检测

【目的】分离获得耐碱反硝化菌株,确定其反硝化活性和耐碱能力。【方法】分离、纯化,获得耐碱反硝化菌株;通过形态观察、生理生化试验和16S rRNA基因测序分析,确定菌株分类地位;试验起始硝酸盐浓度和起始pH对分离菌株反硝化活性的影响。【结果】从实验室稳定运行的高效反硝化反应器中分离获得耐碱反硝化菌株R9,经鉴定归于Diaphorobater nitroreducens;菌株R9能够以甲醇为电子供体、硝酸盐为电子受体进行异养生长,当起始硝氮浓度为50 mg/L、起始pH为9.0时,288 h内硝氮去除率达93.25%;高浓度硝氮可抑制其反硝化活性,半抑制常数Ki为202.73 mg N/L;菌株R9的耐碱性良好,起始pH为11.0时的硝氮去除率是pH为9.0时的86%。【结论】菌株R9归于Diaphorobater nitroreducens,最适生长pH为9.0左右,是一株耐碱反硝化菌。     

好氧反硝化菌的选育及其初步应用

采用间歇曝气、极限稀释和酸碱指示剂培养基相结合的办法,从池塘底泥中成功分离到好氧反硝化菌株H2,经生理生化和16S rDNA序列分析,初步判断为芽孢杆菌属(Bacillus sp.).在室内模拟养殖水体中,菌株H2在15 d中对亚硝酸盐和硝酸盐的最高降解速率分别达到0.885 mg/L·d和0.46 mg/L·d,试验结束时,总氮去除率达到45.2%.结果表明,菌株H2具有应用于养殖水体生物脱氮领域的巨大潜力.     

好氧反硝化菌Defluvibacter lusatiensis str.DN7的分离鉴定和异养硝化性能

从稳定运行处理竹子加工废水的生物接触氧化反应器中分离得到一株好氧反硝化菌DN7,其72 h NO3-降解率达99.4％.细胞显微镜观察显示,菌株为革兰氏阴性小杆菌,大小为0.5 μm×1.5 μm,菌落为乳白色.通过生理生化特性及16S rDNA同源性分析,初步推断该菌株为根瘤菌中的Defluvibacter lusatiensis str.碳源、C/N、硝酸盐初始浓度、溶解氧(DO)、pH对DN7反硝化性能影响的结果表明:菌株对柠檬酸钠、葡萄糖等小分子有机物的利用较好;C/N为9时,脱氮率达99.0％;硝酸盐浓度低于138.48 mg·L-1情况下,DN7脱氮率在96％以上,且亚硝酸盐浓度均在1.0mg·L-1以下;菌株DN7对DO不敏感,中性偏碱性环境有利于DN7反硝化反应的进行;DN7具有良好的异养硝化性能,72 h铵氮降解率达84.7％.     

一株耐盐的卓贝儿氏菌(Zobellella sp.)的分离鉴定及其硝酸盐还原能力

【背景】好氧反硝化是指在有氧条件下进行反硝化作用,使得硝化和反硝化过程能够在同一反应器中同时发生,是废水脱氮最具竞争力的技术。红树林湿地中蕴藏着丰富的微生物资源,分布着大量好氧反硝化微生物。【目的】了解耐盐微生物的脱氮机制,为含盐废水生物脱氮的工程实践提供理论依据,对一株分离于红树林湿地中的耐盐好氧细菌A63的硝酸盐异化还原能力进行分析。【方法】利用形态学特征及16S rRNA基因序列测定分析,对其种属进行了鉴定,采用单因子实验测定该菌在不同环境因子下的硝酸盐还原能力,并对其反硝化脱氮条件进行了优化。【结果】初步判定该菌株为卓贝儿氏菌(Zobellellasp.),其能在盐度0%-10%、pH5.0-10.0、温度20-40°C范围内进行反硝化脱氮和硝酸盐异化还原为氨(dissimilatorynitratereductiontoammonium,DNRA)作用。菌株A63最适生长碳源为柠檬酸钠(1.2 g/L),适宜脱氮盐度为3%、pH 7.0-7.5、温度30-35°C,且C/N为10。在最适脱氮条件下,该菌株12h内能将培养基中208.8mg/L硝态氮降至0,且仅有少量铵态氮生成,无亚硝态氮积累,脱氮率高达99%。此外,该菌株在高盐度、低C/N比、弱酸性和低温等不利生境中DNRA作用显著。【结论】细菌A63生长范围宽,脱氮效率显著,适用于海水养殖废水处理。研究为今后开发高效含盐废水生物脱氮工艺奠定了基础,对于加深氮素转化规律的认识、丰富生物脱氮理论有着重要意义。     

好氧反硝化菌Defluvibacter lusatiensis str. DN7的分离鉴定和异养硝化性能

从稳定运行处理竹子加工废水的生物接触氧化反应器中分离得到一株好氧反硝化菌DN7,其72 h NO₃^-降解率达99.4%.细胞显微镜观察显示,菌株为革兰氏阴性小杆菌,大小为0.5 μm×1.5 μm,菌落为乳白色.通过生理生化特性及16S rDNA同源性分析,初步推断该菌株为根瘤菌中的Defluvibacter lusatiensisstr.碳源、C/N、硝酸盐初始浓度、溶解氧(DO)、pH对DN7反硝化性能影响的结果表明:菌株对柠檬酸钠、葡萄糖等小分子有机物的利用较好;C/N为9时,脱氮率达99.0%;硝酸盐浓度低于138.48 mg·L^-1情况下,DN7脱氮率在96%以上,且亚硝酸盐浓度均在1.0 mg·L^-1以下;菌株DN7对DO不敏感,中性偏碱性环境有利于DN7反硝化反应的进行;DN7具有良好的异养硝化性能,72 h铵氮降解率达84.7%.     

细菌好氧反硝化研究进展

阐述了好氧反硝化细菌的种类及有关性质 ,并从电子理论、氧的浓度、反硝化酶系等方面对细菌好氧反硝化的作用机制进行了探讨 ,对细菌好氧反硝化的研究概况、进展及其研究意义和目前存在的问题作了较为详细的介绍。     

一株脱氮细菌鉴定及其效果研究

针对传统人工湿地治理污染河湖水工艺中存在的脱氮效率低、环境安全性差等问题，从污水处理厂生化池污泥中分离纯化获得菌株TY（CGMCC1.18865，该菌种已于2020年在中国普通微生物菌种保藏中心入库），通过配水试验，验证菌株脱氮特性，并进一步以火山岩为填料，采用湿地模拟系统装置对比附配TY菌的湿地系统与传统湿地系统对污染水体的脱氮效果的差异；通过16S rRNA基因序列分析，鉴定获得的菌株TY，同时对其表现出的反硝化作用进行分析研究。结果表明：分离获得的TY菌株为假单胞菌属（Pseudomonas sp.），配水试验中对氨氮和总氮的去除率分别为84.2%和93.6%。通过对模拟湿地系统出水氨氮、总氮和化学需氧量（COD）监测，发现30 d平均去除率分别可提升至94.3%、88.0%和82.3%，较传统湿地分别提高27.9%、28.8%和7.3%。研究表明，TY菌脱氮过程中有少量的硝态氮和亚硝态氮的积累，可降低对环境的不利影响、有利于脱氮反应连续进行，从而提高人工湿地脱氮效率，具有进一步探究的前景。     

Concurrent nitrite oxidation and aerobic denitrification in activated sludge exposed to volatile fatty acids

The goal of this research was to investigate the simultaneous occurrence of nitrification and denitrification by activated sludge exposed to volatile fatty acids (VFAs) during aerobic wastewater treatment using a single-stage reactor. A mixture of VFAs was spiked directly into a continuous-stirred tank reactor (CSTR) to assess subsequent impacts on nitrite removal, nitrate formation, CO(2) fixation, total bacterial density, and dominant nitrite oxidizing bacteria (NOB) concentration (i.e., Nitrospira). The activity of the periplasmic nitrate reductase (NAP) enzyme and the presence of nap gene were also measured. A rapid decrease in the nitrate formation rate (>70% reduction) was measured for activated sludge exposed to VFAs; however, the nitrite removal rate was not reduced. The total bacterial density and Nitrospira concentration remained essentially constant; therefore, the reduction in nitrate formation rate was likely not due to heterotrophic uptake of nitrogen or to a decrease in the dominant NOB population. Additionally, VFA exposure did not impact microbial CO(2) fixation efficiency. The activity of NAP enzyme increased in the presence of VFAs suggesting that nitrate produced as a consequence of nitrite oxidation was likely further reduced to gaseous denitrification products via catalysis by NAP. Little, if any, nitrogen was discharged in the aqueous effluent of the CSTR after exposure to VFAs demonstrating that activated sludge treatment yielded compounds other than those typically produced solely by nitrification.     

Simultaneous occurrence of denitrification and nitrate ammonification in sediments of the French Mediterranean Coast

Dissimilatory nitrate reductions in coastal marine sediment of Carteau Cove (French Mediterranean Coast) were studied between April 1993 and July 1994. Simultaneous determination of denitrification and dissimilatory nitrate reduction to ammonium was achieved by using a combination of acetylene blockage and 15N techniques. After short incubations (maximum 5 h), a part of 15N labelled nitrate added to the sediment was recovered as ammonium without incorporation in organic matter. The result indicate that a fraction of nitrate was reduced to ammonium by a dissimilatory mechanism instead of denitrifying. Denitrifying and nitrate ammonifying activities ranged from 0 to 19.8 μmol l-1 d-1 and from 2.3 to 83.2 μmol l-1 d-1, respectively. Denitrification rates were highest in early spring whereas nitrate ammonification were highest in fall. The recovery of nitrate reduced as N2O-N plus ammonium was between 40 and 100%, the highest nitrogen losses were recorded in July. Depending on the station and time of year denitrification accounted for between 0 and 43% of the total nitrate reduction whereas dissimilatory nitrate reduction to ammonium (DNRA) accounted for between 18 and 100%. The reduction rate data suggest that the pathway of nitrate reduction to ammonium may be important in coastal sediments. This revised version was published online in July 2006 with corrections to the Cover Date.     

Dissimilatory nitrate reduction by Pseudomonas alcaliphila with an electrode as the sole electron donor

Denitrification and dissimilatory nitrate reduction to ammonium (DNRA) were considered two alternative pathways of dissimilatory nitrate reduction. In this study, we firstly reported that both denitrification and DNRA occurred in Pseudomonas alcaliphila strain MBR with an electrode as the sole electron donor in a double chamber bio‐electrochemical system (BES). The initial concentration of nitrate appeared as a factor determining the type of nitrate reduction with electrode as the sole electron donor at the same potential (?500 mV). As the initial concentration of nitrate increased, the fraction of nitrate reduced through denitrification also increased. While nitrite (1.38 ± 0.04 mM) was used as electron acceptor instead of nitrate, the electrons recovery via DNRA and denitrification were 43.06 ± 1.02% and 50.51 ± 1.37%, respectively. The electrochemical activities and surface topography of the working electrode catalyzed by strain MBR were evaluated by cyclic voltammetry and scanning electron microscopy. The results suggested that cells of strain MBR were adhered to the electrode, playing the role of electron transfer media for nitrate and nitrite reduction. Thus, for the first time, the results that DNRA and denitrification occurred simultaneously were confirmed by powering the strain with electricity. The study further expanded the range of metabolic reactions and had potential value for the recognization of dissimilatory nitrate reduction in various ecosystems. Biotechnol. Bioeng. 2012; 109: 2904–2910. © 2012 Wiley Periodicals, Inc.