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。     

一株异养硝化-反硝化不动杆菌的分离鉴定及脱氮活性

[目的]分离筛选并鉴定一株异养硝化-反硝化细菌,并探讨其在脱氮中的作用.[方法]富集培养分离筛选微生物,通过形态观察和生理生化特征及16S rDNA鉴定细菌,定时测定其OD600研究生长曲线,正交试验研究其脱氮影响因素和最佳条件,与污水处理厂活性污泥共同作用检验其脱氮活性.[结果]分离到一株异养硝化-反硝化细菌,鉴定结果表明是一株不动杆菌,命名为Acinetobacter sp.YF14,这是已知报道的第一株进行异养硝化和好氧反硝化的不动杆菌.该菌在12 h时进入对数期,22 h时进入稳定期,45 h以后进入衰亡期.该菌能进行异养硝化,3d后氨氮和总氮的去除率可以达到92％和91％,且无硝酸盐氮和亚硝酸盐氮积累.好氧条件下该菌能进行反硝化,在硝酸盐和亚硝盐培养基中均能将氮几乎完全去除.对该菌脱氮的影响程度大小依次为转速＞接种量＞碳源＞碳氮比＞ pH.当转速为160 r/min,碳源取葡萄糖,接种量1％,碳氮比为8∶1,pH为6.5时,脱氮效果最好.该菌株可以提高活性污泥对于生活污水总氮脱除率约30％.[结论]菌YF14可以明显加强活性污泥脱氮效果,显示了良好的应用前景.     

滇池可培养好氧反硝化细菌多样性及其脱氮特性

【目的】氮污染已成为当今水体污染的一个重要因素,为了解滇池可培养好氧反硝化细菌的多样性,获得高效好氧反硝化细菌资源,为污染水体或浅层地下水的生物修复提供材料。【方法】采用富集培养方法从滇池沉积物和水体样品中分离好氧反硝化细菌,对好氧反硝化细菌的16S r RNA基因序列进行系统发育分析,并筛选其中的高效好氧反硝化细菌。【结果】分离出260株好氧反硝化菌,经16S rRNA基因序列分析,260株菌分属于2门13科14属的59个种。假单胞菌属(Pseudomonas)为优势细菌属,其次是不动杆菌属(Acinetobacter)、气单胞菌属(Aeromonas)和代尔夫特菌属(Delftia)。筛选到12株高效好氧反硝化细菌菌株,其中8株属于假单胞菌(Pseudomonas spp.),4株为不动杆菌(Acinetobacter spp.)。定量分析发现菌株N15-6-1的反硝化效果较好。对菌株N15-6-1的脱氮条件优化结果显示,在以蔗糖为碳源,温度为30–35℃、C/N=12、静止培养时,反硝化能力较强,其在48 h内硝态氮的去除率达到98.81%,总氮的去除率达96.27%。【结论】滇池存在着较丰富的可培养好氧反硝化细菌,好氧反硝化细菌的分离丰富了好氧反硝化菌的种类,其中的高效脱氮菌株为污染水体或浅层地下水的生物修复提供了初步的候选菌株。     

耐高浓度氨氮的异养硝化好氧反硝化菌株U1的鉴定及其脱氮特性

【背景】城市垃圾渗滤液是一种成分复杂的有机废水,含氮量高,如果未经处理直接排放到环境中会造成严重的环境污染。【目的】筛选可以耐受垃圾渗滤液中高浓度氨氮并高效去除污水中氮素的异养硝化好氧反硝化菌株,为解决垃圾渗滤液的氮素污染提供功能菌株。【方法】从垃圾渗滤液中筛选分离能耐受高氨氮浓度的菌株,通过测定各菌株的脱氮能力,筛选到一株脱氮能力最强的菌株,命名为U1,通过测定16S rRNA基因序列和生理生化特性确定该菌株为铜绿假单胞菌。进一步研究了菌株U1在不同初始氨氮浓度、碳源、转速、初始pH、碳氮比等单因素变量下的脱氮能力,并结合L₉（3⁴）正交试验研究了菌株U1的最佳脱氮条件。【结果】分离出一株铜绿假单胞菌并命名为U1。该菌株的最优脱氮条件为:初始氨氮浓度为1 000 mg/L,红糖和柠檬酸三钠的混合碳源,pH 6.0,C/N为10,转速为130 r/min,菌株U1的最大总氮去除率为64.37%,最大氨氮去除率为76.73%。对于总氮和氨氮含量分别是2 345 mg/L和1 473.8 mg/L的垃圾渗滤液,菌株U1最大总氮去除率为27.86%...     

耐冷亚硝酸盐型反硝化菌Pseudomonas tolaasii Y-11的鉴定及其脱氮特性

摘要:【目的】反硝化细菌在生物脱氮中具有重要作用,而耐冷亚硝酸盐型反硝化细菌研究较少,本文从长期淹水的冬水田泥土分离获得一株耐冷高效去除亚硝酸盐氮和总氮的好氧反硝化细菌Y-11,明确其分类地位以及除氮特性,以期为后续利用该菌在初冬到春末处理亚硝酸盐水体污染奠定基础。【方法】通过形态学特征、特异性磷脂脂肪酸以及16S rRNA基因测序分析对该菌株进行鉴定;在好氧条件下以亚硝酸钠为唯一氮源,分别研究不同初始温度、转速、pH、碳源、接种量以及亚硝酸盐氮浓度对该菌去除亚硝酸盐氮和总氮的影响,确定最适降解条件。【结果】分离得到的菌株Y-11,经鉴定归于托拉斯假单胞菌(Pseudomonas tolaasii);在国内外尚无该种菌具有反硝化作用的报道,是对亚硝酸盐型反硝化细菌的进一步补充。Y-11菌株的最适脱氮条件为15 ℃,200 r/min,pH7.0,100 mL反硝化培养基中最适接种量为1.5×108 CFU,最佳碳源为乙酸 钠,亚硝酸盐氮为10 mg/L;以乙酸钠为电子供体,15 ℃、初始pH为7.2、150 r/min 振荡培养,48 h对亚硝酸盐氮和总氮的去除率分别为100%和61.28%。【结论】Y-11是一株具有较高反硝化能力的托拉斯假单胞菌,能高效地去除亚硝酸盐氮和总氮,其最适温度是15 ℃左右,是一株耐冷反硝化细菌。     

耐低温好氧反硝化菌Aeromonas sp.的分离鉴定及脱氮条件优化

【目的】从冬季活性污泥和河水底泥中分离筛选得到耐低温好氧反硝化菌，并对影响脱氮的关键因子进行优化，以提高低温条件下的脱氮效果。【方法】采用富集纯化法分离筛选耐低温好氧反硝化菌株。通过形态观察和16S rRNA基因系统发育分析等方法对筛选菌株进行菌种鉴定。以NO3–-N去除率为响应目标，采用Box-Behnken试验设计及响应面回归分析法优化影响脱氮效果的关键因子（C/N、温度、pH和摇床转速），确定最佳培养条件。【结果】从东北寒冷地区冬季河水底泥样品中分离得到的一株耐低温好氧反硝化菌Z6，菌落呈白色半透明圆形，菌体细胞为短杆状，大小为（0.8–1.6）μm×（0.6–0.8）μm，革兰氏染色阴性。与气单胞菌属（Aeromonas）的16S rRNA基因序列高度同源，鉴定该菌为气单胞菌。采用响应面分析方法得到菌株Aeromonas sp. Z6的最佳脱氮条件为：C/N 5.9，温度12°C,pH 6.8，摇床转速155 r/min，在此条件下对NO₃^–-N的去除率为89.72%，与预测值（90.34%）无显著差别。【结论】首次报道气单胞菌（Ae...     

一株轻度嗜盐反硝化细菌的分离鉴定和反硝化特性初探

从处理高盐度废水的成熟活性污泥中分离筛选得到1株轻度嗜盐反硝化细菌GYL, 通过对该菌株的形态观察、生理生化实验以及16S rDNA序列分析, 确定该菌株为盐单胞菌(Halomonas sp.)。该菌株能在盐度为10%的培养液中生长, 最适盐度为2%~7%, 最适pH为7.5~8.5, 最佳碳源为蔗糖, 在25°C~30°C的温度范围内脱氮效率达到80%以上。对该菌株的异养硝化能力进行了测定, 其对氨氮的去除率可达98.3%, 说明该菌株可实现同步硝化反硝化, 即该菌可以独立完成生物脱氮的全部过程。     

海水反硝化细菌富集培养及性能研究

目的：建立一种海水反硝化细菌的富集培养方法,为海水反硝化微生物在实际应用中处理硝酸盐氮做基础工作。方法：选取污水处理厂缺氧池活性污泥,利用人工海水富集培养反硝化细菌。结果：经过25d,可以培养出反硝化速率为4.83mg/（gMLSS·h）、反硝化强度为110mg/（L·h）的海水反硝化细菌培养物。结论：该培养物可利用柠檬酸钠、葡萄糖、甲醇、乙醇、可溶性淀粉作为唯一碳源进行反硝化,其中以柠檬酸钠和乙醇作碳源时硝酸盐氮去除效果最佳,经过12h,去除率即可达到100%。pH在7～8范围内时,改变pH对去除率的影响不大,但当pH〈6时,去除率明显下降。温度在35℃时,去除效果最好,并且随着温度的降低,去除率也降低。     

一株荧光假单胞杆菌的分离鉴定与反硝化特性

【目的】从污水厂的活性污泥中获得一株高效反硝化细菌。【方法】采用低温驯化,进行初筛、复筛选取一株反硝化活性最高的菌株,命名为L2,通过形态学、生理生化特征及16S r RNA基因序列分析研究其分类地位,系统研究理化因素对该菌株反硝化性能的影响。【结果】菌株在低温条件下能够稳定高效地进行反硝化,鉴定该菌株为荧光假单胞杆菌(Pseudomonas fluorescens),其反硝化最适接种量为10%,温度为20°C,p H为7.0,盐浓度为0.5%,碳源为葡萄糖,C/N为5.0,能够耐受较高初始硝态氮浓度。【结论】菌株L2是一株耐低温、耐高浓度初始硝态氮、耐低C/N、兼性厌氧、高效反硝化的荧光假单胞杆菌。     

分离于河口区芦苇湿地1株好氧反硝化菌的鉴定及其反硝化特性

【目的】筛选高效脱氮且N_2O释放量少的好氧反硝化细菌,并对菌株的反硝化特性进行研究,可为河口湿地富营养化水体的生物修复提供技术支撑。【方法】经BTB培养基初筛和反硝化能力测定,从辽河河口区芦苇湿地土壤中分离得到1株具有较高反硝化能力的好氧反硝化菌C3。经形态观察、生理生化鉴定和16S rRNA序列分析,对菌株进行鉴定。研究温度、碳源、pH及C/N对其生长量、反硝化能力及N2O释放的影响。【结果】筛选得到的高效好氧反硝化细菌C3,经鉴定属于假单胞菌属(Pseudomonas sp.)。反硝化特性研究结果表明,该菌最适碳源为柠檬酸三钠,在温度为30°C、pH为7.0、C/N为10时生长速率和脱氮效率最高且N_2O释放量较少。在此条件下,该菌在36 h内使NO_3~–由179.55 mg/L降至5.08 mg/L,脱氮率高达97.17%。该菌株在整个反硝化过程中中间产物N_2O的最大累积量较低,为0.22 mg/L。【结论】从湿地土壤中分离所得好氧反硝化菌C3为假单胞菌属的1个种(Pseudomonas sp.),该菌株在高效除氮和低N_2O累积方面均具有明显优势,对后续河口湿地富营养化水体治理具有重要意义。     

Monitoring denitrification by pH-Stat titration

An improved pH-stat titrimetric procedure was developed, validated, and extensively applied to monitor biological heterotrophic denitrification in a lab-scale sequencing batch reactor (SBR). So far, titrimetric procedures were not successful in monitoring denitrification processes in full-scale wastewater (WW) treatment plants, mainly because the stoichiometric ratio between proton production and nitrate reduction is highly variable due to variability of both biomass and influent WW characteristics. In this article, a new titration procedure is proposed where a simple calibration step is performed before each experimental test. This procedure allows for the assessment of (i) nitrate content in a sample of mixed liquor; (ii) the maximum denitrification rate of sludge when fed on acetate; and (iii) the denitrification potential (DNP) of different substrates. As for (i), validation by comparison with spectrophotometric measures indicated an average discrepancy of less than 3% on more than 40 samples; as for (ii) and (iii) collected values compared well with literature data. The titrimetric method proposed here is also capable of assessing the biomass anoxic yield in a very simple way, since it does not require any analytical nitrate determination. According to the results of this experimentation, titrimetry appeared to be a simple, inexpensive, and powerful tool for monitoring and operating denitrification processes in WW treatment plants.     

Aerobic denitrification in various heterotrophic nitrifiers

Various heterotrophic nitrifiers have been tested and found to also be aerobic denitrifiers. The simultaneous use of two electron acceptors (oxygen and nitrate) permits these organisms to grow more rapidly than on either single electron acceptor, but generally results in a lower yield than is obtained on oxygen, alone. One strain, formerly known as Pseudomonas denitrificans, was grown in the chemostat and shown to achieve nitrification rates of up to 44 nmol NH₃ min^–1 mg protein^–1 and denitrification rates up to 69 nmol NO _inf3 ^sup–1 min^–1 mg protein^–1.Unlike Thiosphaera pantotropha, this strain needed to induce its nitrate reductase. However, the remainder of the denitrifying pathway was constitutive and, like T. pantotropha, Ps. denitrificans probably possesses the copper nitrite reductase.     

Removal of highly elevated nitrate from drinking water by pH-heterogenized heterotrophic denitrification facilitated with ferrous sulfide-based autotrophic denitrification

The performance of acetic acid-supported pH-heterogenized heterotrophic denitrification (HD) facilitated with ferrous sulfide-based autotrophic denitrification (AD) was investigated in upflow activated carbon-packed column reactors for reliable removal of highly elevated nitrate (42 mg NO₃-N l⁻¹) in drinking water. The use of acetic acid as substrate provided sufficient internal carbon dioxide to completely eliminate the need of external pH adjustment for HD, but simultaneously created vertically heterogenized pH varying from 4.8 to 7.8 in the HD reactor. After 5-week acclimation, the HD reactor developed a moderate nitrate removal capacity with about one third of nitrate removal occurring in the acidic zone (pH 4.8–6.2). To increase the treatment reliability, acetic acid-supported HD was operated under 10% carbon limitation to remove >85% of nitrate, and ferrous sulfide-based AD was supplementally operated to remove residual nitrate and formed nitrite without excess of soluble organic carbon, nitrite or sulfate in the final effluent.     

Effects of pentachlorophenol on the bacterial denitrification process

The use of pentachlorophenol (PCP) was banned or restricted in many countries worldwide because of its adverse influences on the ecological environment and humans. However, the potential disrupting effects of PCP on denitrifying microorganisms have warranted more analysis. In this study, the impacts of PCP on denitrification were investigated by using Paracoccus denitrificans as a model denitrifying bacterium. Compared with the control, the presences of 10 and 50 μM of PCP were found to significantly decrease the denitrification efficiencies from 98.5 to 87.2% and 68.7%, respectively. The mechanism studies showed that PCP induced the generation of reactive oxygen species, which decreased the vital enzymes activities related to glycolysis process, causing the disturbance of the metabolism of P. denitrificans utilizing carbon source (glucose) and the growth of the cell, and subsequently the generation of electron donor (NADH) for denitrification via NAD⁺ reduction was severely depressed. Further studies indicated that PCP also decreased the genes expression of several key enzymes responsible for denitrification, such as napA of nitrate reductase (NAR), nirS of nitrite reductase, norB of nitric oxide reductase, and nosZ of nitrous oxide reductase; however, there was only the enzyme activity of NAR was remarkably inhibited.     

Simultaneous nitrification and denitrification in a mixed methanotrophic culture

Simultaneous nitrification and denitrification using a mixed methanotrophic culture was investigated. When both NO₃ ^–-N (108 mg l^–1) and NH₃-N (59 mg l^–1) were added into batch reactors, nitrate removal was complete within 10 h at the rate of 47 mg NO₃ ^–-N g VSS^–1 day^–1 when dissolved oxygen (DO) concentration was maintained at 2 mg DO l^–1. Ammonia removal started simultaneously with nitrate removal at a slower rate of 14 NH₃-N g VSS^–1 day^–1. No significant accumulation of nitrite or nitrate during ammonia utilization suggested the occurrence of simultaneous nitrification and denitrification.     

好氧甲烷氧化耦合反硝化极限脱氮系统的效能及应用

【目的】探究甲烷浓度、温度和氮浓度对好氧甲烷氧化耦合反硝化(AME-D)极限脱氮系统的影响,分析该系统微生物群落结构,并对贵阳某污水处理厂尾水进行应用研究。【方法】采用阶段性实验研究甲烷浓度、温度和氮浓度对系统脱氮效能的影响,通过16SrRNA基因测序技术分析系统中微生物群落结构,利用共焦显微拉曼光谱仪分析实际废水水质变化特征。【结果】甲烷进气比为3%、温度为30°C、氮浓度为20 mg/L时脱氮效果最好,系统的总氮、氨氮和硝酸盐氮平均去除率分别为93.66%、96.13%和92.25%;系统中的主要甲烷氧化菌分别为Methylosarcina(1.84%)、Methylovulum(0.01%)和Crenothrix(0.14%),以及兼性甲烷氧化菌属Methylocystis(1.9%),主要的亚硝化菌为Nitrosomonas(0.008%),硝化菌为Nitrospira (0.42%),反硝化菌为Hyphomicrobium (1.19%)和Pseudomonas (0.61%);采用该系统处理贵阳某污水处理厂尾水时,出水总氮平均浓度达到0.96mg/L,能达到极限脱氮的目的,拉曼光谱分析显示系统对硝酸盐氮和亚硝酸盐氮有较高的去除,甲烷被氧化形成的中间产物可能为醇类或醛类物质,为反硝化菌提供所需碳源。【结论】AME-D极限脱氮由多种微生物协同实现,其功能微生物为甲烷氧化菌、亚硝化菌、硝化菌和反硝化菌,应用研究显示该系统在城镇污水处理系统中具有较大的应用潜力。     

Nitrite inhibition of denitrification by Pseudomonas fluorescens

Using a pure culture of Pseudomonas fluorescens as a model system nitrite inhibition of denitrification was studies. A mineral media with acetate and nitrate as sole electron donor and acceptor, respectively, was used. Results obtained in continuous stirred-tank reactors (CSTR) operated at pH values between 6.6 and 7.8 showed that growth inhibition depended only on the nitrite undissociated fraction concentration (nitrous acid). A mathematical model to describe this dependence is put forward. The maximum nitrous acid concentration compatible with cell growth and denitrification activity was found to be 66 mug N/L. Denitrification activity was partially associated with growth, as described by the Luedeking-Piret equation. However, when the freshly inoculated reactor was operated discontinuosly, nitrite accumulation caused growth uncoupling from denitrification activity. The authors suggest that these results can be interpreted considering that (a) nitrous acid acts as a proton uncoupler; and (b) cultures continuoulsy exposed to nitrous acid prevent the uncoupling effect but not the growth inhibition. Examination of the growth dependence on nitrite concentration at pH 7.0 showed that adapted cultures (grown on CSTR) are less sensitive to nitrous acid inhibition than the ones cultivated in batch. (c) 1995 John Wiley & Sons, Inc.     

羟胺氧化还原酶在生物脱氮中的研究进展

羟胺氧化还原酶(hydroxylamine oxidoreductase,HAO)属于多血红素蛋白酶家族,每个单体由7个电子转移血红素和1个催化血红素组成。HAO既可分别催化羟胺和肼的氧化反应,也可催化羟胺、一氧化氮及亚硝酸盐的还原反应。不同硝化细菌中,HAO的最适温度、p H、底物、产物特异性及酶抑制剂等存在差异。作为生物硝化过程的关键酶,HAO在提升生物脱氮速率及清除硝化中间产物(羟胺)对生物的毒害方面发挥重要作用。本文系统综述了HAO在脱氮微生物中的分布、蛋白结构、表达调控及其活性等,总结其在不同硝化细菌中的生物化学特性,最后对HAO进一步的研究方向进行展望,有助于深入理解生物脱氮过程和微生物体内羟胺代谢的机理,为优化废水处理工艺提供新的指导。     

好氧反硝化生物脱氮技术的研究进展

好氧反硝化生物脱氮技术自提出以来,凭借能实现同步硝化反硝化、节省基建投资及运行费用等诸多优点,受到国内外环境领域学者的广泛关注。本文首先总结了近年来好氧反硝化菌种的筛选分离情况,以及环境因子对好氧反硝化菌脱氮效能的影响,包括溶解氧(dissolved oxygen,DO)、碳氮比(C/N)、温度等。然后深入探讨了好氧反硝化生物脱氮技术的原理,好氧反硝化过程中的关键功能基因及酶,同时介绍了分子生物技术在好氧反硝化研究过程中的应用,以及好氧反硝化生物脱氮技术在实际应用方面的研究现状。最后,基于目前的研究瓶颈问题,对未来好氧反硝化生物脱氮技术的研究方向提出了科学展望。     

好氧反硝化微生物学机理与应用研究进展

近年来,关于好氧反硝化过程的研究主要集中在三个方面:分别是好氧反硝化菌株的分离和脱氮性能表征,好氧反硝化微生物的应用潜力分析,以及好氧反硝化过程的机理研究。好氧反硝化菌株分布范围广泛,可从多种环境中分离得到,种属以Pseudomonas sp.、Alcaligenes sp.和Paracoccus sp.为主。好氧反硝化菌株及菌群在实验室条件下表现出优良的耐冷、耐盐特性,并具有可降解毒性有机物及N_2O减排的潜力。关于好氧反硝化过程的机理研究表明,虽然硝酸盐作为电子受体的竞争力比氧气弱,但反硝化作为辅助电子传递途径,可提高产能效率,防止NAD(P)H的过量积累。因此,硝酸盐可与氧气同时参与微生物的新陈代谢,即发生好氧反硝化现象。未来除了继续分离更新更好的好氧反硝化菌株外,应加强对好氧反硝化机理及实际生物强化方面的研究。