有机物对厌氧氨氧化菌活性影响研究进展

厌氧氨氧化反应(Anammax)功能菌世代时间长,生长条件苛刻,在有机物存在的条件下,反应过程和脱氮效果极易受到影响。因此,如何降低有机物对厌氧氨氧化菌(AAOB)活性的影响,是其应用的难点。近年来,研究者在有机物对Anammox反应影响方面开展了大量研究,本文主要综述了有机物的浓度和种类对AAOB活性的影响,并建议控制低浓度有机物环境下(100~200 mg/L以下),可降低有机物对AAOB活性的抑制;同时,可调控不同种类和浓度有机物的异位利用,形成Anammox-反硝化协同作用、Anammox-甲烷化-反硝化耦合作用等实现同步脱碳除氮。最后认为,在有机物对Anammox的影响方面,还可进一步开展AAOB的新陈代谢机制、与其他菌种的竞争合作机理以及耦合作用下菌种富集纯化等方面的研究。     

厌氧氨氧化的生态因子研究进展

厌氧氨氧化生物脱氮技术是近年来发展起来的新型的生物脱氮技术,其实质是氨的亚硝化与亚硝化产物以氨为电子供体的还原相偶联.从生态因子的角度出发,综述了厌氧氨氧化的影响因子(生物因子及非生物因子)的研究进展.并对厌氧氨氧化的应用前景进行了展望,提出了其今后的研究方向.     

短程硝化-厌氧氨氧化工艺的挑战与对策

短程硝化-厌氧氨氧化（PN/A）工艺与传统生物脱氮工艺相比，具有能耗低、设备简单、污泥产率低等诸多优点，在污水脱氮领域备受关注。本文首先总结了PN/A工艺在实际应用中存在的一些挑战，比如，处理高C/N废水效果不佳、亚硝酸盐氧化细菌（NOB）抑制困难、启动缓慢等。然后，针对上述挑战，提出了一些PN/A工艺的改进措施。可使用多种预处理技术来降低废水有机物含量，以减弱高C/N比废水的负面影响；根据NOB、厌氧氨氧化菌（AnAOB）、氨氧化细菌（AOB）之间生长条件的差异，通过调控温度、pH、溶解氧等环境条件或添加抑制剂来抑制NOB的生长。接着，总结了PN/A工艺快速启动的方法，即通过添加化学物质、物理场、外加AnAOB种泥，并给予AnAOB最佳生长条件等方法，实现PN/A工艺的快速启动。最后，展望了PN/A工艺未来有待深入研究的方向。     

生物膜脱除方式对受污染源水生物接触氧化修复系统除磷性能的影响

针对生物接触氧化修复工艺存在的生物膜内磷累积导致系统除磷性能恶化的问题,以受污染源水为对象,开展表层生物膜脱除(SBD)和全层生物膜脱除(FBD)两种排泥方式对系统除磷长效性和运行稳定性的影响研究.结果表明,生物接触氧化修复系统启动1周后除磷效率达46.9%,随后系统除磷性能迅速恶化.采用FBD方式后系统除磷效果得以恢复,溶解性磷酸盐(DP)去除率维持在30%以上近1个月,生物膜饱和吸磷量达(318.5±21.5)mgTPm-2填料表面积.相比而言,采用SBD方式处理后系统除磷性能未能得到有效改善,30%以上DP去除率仅维持1周左右,生物膜饱和吸磷量仅为FBD的0.68倍.推测不同脱除方式对生物膜二次成膜过程微生物菌群结构重建和污染物去除性能影响显著,FBD处理后系统二次成膜过程溶解氧扩散不受限制,聚磷菌相对反硝化菌更易定殖、富集.镜检结果表明,FBD处理后填料表面仍附着少量微生物及其分泌物(如胞外多聚物等),与新填料表面光滑特性相比,其较高的孔隙率和较强的生物亲和性有利于微生物快速附着成膜,保证排泥强化除磷后系统氨氮、高锰酸盐指数、总氮去除性能稳定.     

HEMA与HEA辐射共聚制备固定化微生物载体的结构与性能

应用低温辐射技术辐射诱导甲基丙烯酸β-羟乙酯(HEMA)和丙烯酸羟乙酯(HEA)共聚合制备了高分子载体,用增殖细胞技术固定氨氧化细菌。利用红外光谱(FT-IR)、X射线光电子能谱(XPS)、X射线衍射(XRD)、扫描电子显微镜(SEM)以及接触角和含水率的测试对聚合物载体进行了性能表征。结果表明:经充分溶胀后的聚合物表面水接触角几乎为0,含水率为450%,润湿性能良好;聚合物表面具有极性官能团;聚合物的非晶结构有利于小分子尤其是水分子的渗透和扩散,多孔结构有利于微生物的生长和繁殖。以聚合物为载体固定化氨氧化细菌在处理含氨废水的过程中实现了短程硝化,在3种氨氮负荷(100、1502、00 mg/L)条件下,氨氮去除率和亚硝化率可分别达到95%和90%以上。     

一株硫酸盐型厌氧氨氧化菌的分离和鉴定

以硫酸盐为电子受体、氨为电子供体的反应称为硫酸盐型厌氧氨氧化,这是一个新的生物反应.迄今为止,虽已证明硫酸盐型厌氧氨氧化的存在,但并未获得进行该反应的微生物.本课题组从长期稳定运行的厌氧脱氮除硫反应器污泥中,分离获得了一株硫酸盐型厌氧氨氧化菌.形态观察、生理试验和16SrDNA序列比对表明,该菌株可归入Bacillus benzoevorans.以Biolog板检测发现,该菌株可利用多种碳源,基质多样性明显.其最适代谢pH为8.5,最适代谢温度为30℃.研究证明,该菌株可在无氧条件下,同时去除氨氮和硫酸盐,具有硫酸盐型厌氧氨氧化活性.这一发现为硫酸盐型厌氧氨氧化的确认提供了生物学证据,为新型生物脱氮除硫工艺的研发打下了基础,为微生物学增加了新的内容,为地球氮素和硫素循环提供了新的认识.     

微生物燃料电池阴极脱氮

微生物燃料电池(MFC)阴极电子受体的多样性可实现其阴极脱氮,从而将产生的电能合理利用,因此阴极脱氮成为了MFC的一个研究方向,同时也为实际废水中氮素的去除提供了新的可能。然而在反应过程中有众多因素会导致NOx-N与其他电子受体竞争阳极电子的现象,影响阴极反硝化过程对于电子的利用率,从而造成脱氮效率低等现实问题。目前已有许多研究通过优化MFC自身结构弥补产电的缺陷,及将与其他工艺系统耦合实现同步硝化反硝化等方法,取长补短以增加脱氮效率,降低对碳源的需求,以此解决微生物燃料电池阴极脱氮出现的问题。本文从MFC不同的脱氮历程、MFC工艺条件(pH、C/N、DO)、极室分隔材料等影响MFC阴极脱氮的因素及影响其阴极反硝化微生物群落构成等方面,进行了综述并预测未来研究方向。     

铱（III）离子催化铈（IV）离子氧化异丁醇的反应动力学及机理

在酸性介质中用氧化还原滴定法研究了铈（IV）离子在痕量铱（III）离子催化作用下,于25～40 ℃区间氧化异丁醇（BA）的反应动力学.结果表明反应对铈（IV）离子为一级,对异丁醇的表观反应级数为正分数.准一级速率常数kobs随[H＋]及催化剂[Ir(Ⅲ)]增加而增大,随[HSO4-]增加而减小.在氮气保护下,反应不能引发丙烯酰胺聚合,说明在反应中没有自由基产生.提出了催化剂、底物和氧化剂间生成双核加合物的反应机理,通过kobs与HSO4-的依赖关系,找到本反应体系的动力学活性物种是Ce(SO4)2＋,并计算出平衡常数、速控步骤的速率常数及相应的活化参数.     

亚硝酸盐氮溶液标准物质的研制

建立了水中亚硝酸盐氮标准物质的研制方法.采用亚硝酸钠作为原料,采用重量–容量法配制水中亚硝酸盐氮溶液标准物质,将配制值作为标准值.亚硝酸钠纯度采用氧化还原滴定法测定,扣除还原性杂质对滴定结果的影响,并进行了不确定度评定,最终得到亚硝酸钠的纯度(质量分数)为99.48％,纯度的相对标准不确定度为0.2％.制备的亚硝酸盐氮...     

对氨分子敏感的一种方酸二酰胺(SQDAM)新型PVC膜电极

氨是中性分子,它在水溶液中主要以NH_3·H_2O形式存在。氮的测定目前国内外大多数使用氨气敏电极,系将待测液中的氨通过透气膜后改变内充液的pH,再用pH电极测定此变化,间接确定氨含量.也有用硝化菌作为生物催化层的(双膜)电极测定氨。但对中性分子氨敏感的中性载体单膜电极尚未见文献报道.我们在合成双臂型方酰胺多齿     

Achieving the nitrite pathway using FA inhibition and process control in UASB-SBR system removing nitrogen from landfill leachate

An up-flow sludge blanket(UASB) and sequencing batch reactor(SBR) system was introduced to remove organics and nitrogen from landfill leachate.The synergetic effect of free ammonia(FA) inhibition and process control was used to achieve the nitrite pathway in the SBR.In previous research,inhibition of FA on nitrite oxidizing bacteria(NOB) activity has been revealed and the process control parameters(DO,ORP and pH) exactly indicate the end-point of nitritation.The method was implemented in the SBR achieving s...     

Stable partial nitritation of mature landfill leachate in a continuous flow bioreactor: Long-term performance,microbial community evolution,and mechanisms

A continuous flow bioreactor was operated for 300 days to investigate partial nitritation (PN) of mature landfill leachate, establishing the long-term performance of the system in terms of the microbial community composition, evolution, and interactions. The stable operation phase (31–300 d) began after a 30 days of start-up period, reaching an average nitrite accumulation ratio (NAR) of 94.43% and a ratio of nitrite nitrogen to ammonia nitrogen (NO₂⁻-N/NH₄⁺-N) of 1.16. Some fulvic-like and humic-like compounds and proteins were effectively degraded in anaerobic and anoxic tanks, which was consistent with the corresponding abundance of methanogens and syntrophic bacteria in the anaerobic tank, and organic matter degrading bacteria in the anoxic tank. The ammonia-oxidizing bacteria (AOB) Nitrosomonas was found to be the key functional bacteria, exhibiting an increase in abundance from 0.27% to 6.38%, due to its collaborative interactions with organic matter degrading bacteria. In-situ inhibition of nitrite-oxidizing bacteria (NOB) was achieved using a combination of free ammonia (FA) and free nitrous acid (FNA), low dissolved oxygen (DO) with fewer bioavailable organics conditions were employed to maintain stable PN and a specific ratio of NO₂⁻-N/NH₄⁺-N, without an adverse impact on AOB. The synergistic relationships between AOB and both denitrifying bacteria and organic matter degrading bacteria, were found to contribute to the enhanced PN performance and microbial community structure stability. These findings provide a theoretical guidance for the effective application of PN-Anammox for mature landfill leachate treatment.     

High-performance system for partial nitritation of reject water resistant to temperature fluctuation

A sequencing batch reactor (SBR) applying partial nitritation for reject water treatment was operated for 330 days at a laboratory scale. The system was repeatedly exposed to sudden temperature drops from 24 to 17 °C. The nitrogen loading rate (NLR) was increased incrementally from 0.4 to 1.5 kg/(m³ day) with the aim to evaluate temperature stability of the process at different NLR value. Total nitrite nitrogen (TN^IIIN) represented 94–99% of oxidised nitrogen in the effluent throughout the entire operation of the reactor. It was found that the pH profile during the SBR cycle, nitrogen removal efficiency and concentration of N-species in the effluent did not show significant changes following temperature decreases occurring within the entire applied range of the NLR. Simultaneously, the nitrogen removal rate increased proportionally with the NLR where the nitrogen oxidation efficiency reached 48–58% regardless of actual temperature and NLR. These observations clearly demonstrate the temperature stability of applied partial nitritation system during the tested temperature fluctuations.     

电极面积对老龄垃圾渗滤液为底物的微生物燃料电池性能影响

构建生物阴极型双室微生物燃料电池,处理老龄垃圾渗滤液。研究了阳极与阴极面积比值对微生物燃料电池产电能力和对老龄垃圾渗滤液处理效果的影响。结果表明,阳极与阴极面积比为1:2、2:2、2:1的3组生物阴极型微生物燃料电池输出电压分别为408、452、396mV,最大电功率密度分别为145.73、237.65、136.50mW/m³,内阻分别为350、200、400Ω,COD的去除率分别为21.18%、20.20%、22.31%。3组微生物燃料电池运行30d后,垃圾渗滤液中氨氮、硝酸盐氮、亚硝酸盐氮浓度均下降,其中,氨氮去除率分别为80.88%、73.61%和66.17%,其去除效果与产电性能相关。     

Simulation of aerobic landfill in laboratory scale lysimeters — effect of aeration rate

Aeration of municipal landfills contributes to the acceleration of organic matter degradation and to the decrease of pollutant emission into air, water, and soil. Biodegradation of organic matter present in municipal waste, deposited in a landfill, by microorganisms under anaerobic conditions is a slow process. The aim of the study was to carry out simulations of an aerobic landfill in lysimeters, to determine the influence of aeration rate on the degradation of organic matter present in landfills, and to formulate a mathematical model defining the changes of carbon content in leachate and in gas produced. In this work, simulation of aerobic landfill leachate degradation was carried out in laboratory scale lysimeters with the working volume of 15 L. The changes of BOD5, COD, and ammonium nitrogen concentration during aeration were similar for all aeration rates. During aeration, the BOD5 index decreased by 99.9 %, COD decreased by 95.1 %, and ammonium nitrogen concentration by 93 %. The proposed kinetic model defines the processes of organic carbon content changes in simulated leachate and the quantity of carbon dioxide for aerobic landfill simulation quite well.     

Application of Catalytic Wet Air Oxidation to Treatment of Landfill Leachate on Co／Bi Catalyst

Catalytic wet air oxidation(CWAO) was employed to reduce the organic compounds in landfill leachate and the effects of temperature, oxygen pressure, catalyst dosage, and concentration of the organic compounds on the TOC and CODcr removal rates were studied. The degradation kinetics of landfill leachate was also investigated and an exponential experiential model consisting of four influential factors was established to describe the reduction of the organic compounds in the landfill leachate. Meanwhile, the GC-MS technique was used to detect the components of the organic intermediates for the inference of the decomposition mechanisms of the organic compounds in landfill leachate. The results reveal that the reaction temperature and the catalyst dosage are the most important factors affecting the degradation reaction of the organic compounds and that the principal intermediates confirmed by GC-MS are organic acids at a percentage of more than 88% with no aldehydes or alcohols detected. The decomposition mechanisms of the organic compounds in landfill leachate were inferred based on the GC-MS information as follows;the activated gas phase O2 captured the hydrogen of the organic pollutants to produce free radicals, which then initiated the catalytic reaction. So most of the organic compounds were oxidized into CO2 and H2O ultimately. In general, catalytic wet air oxidation over catalyst Co3O4/Bi2O3 was a very promising technique for the treatment of landfill leachate.     

静态法和EXAFS技术研究Eu(III)在钛酸纳米管上的吸附行为和微观机制

结合静态实验和X射线吸收精细结构谱学(EXAFS)技术研究了pH、时间、有机配体等环境因素对放射性核素Eu(III)在钛酸纳米管上的吸附行为和微观机制的影响.宏观实验结果表明:Eu(III)在钛酸纳米管上的吸附在pH<6.0条件下受离子强度影响,而在pH>6.0条件下不受离子强度影响;腐殖酸HA/FA在低pH条件下可以促进Eu(III)在钛酸纳米管上的吸附,而在高pH条件下抑制Eu(III)在钛酸纳米管上的吸附.EXAFS微观分析结果表明:在pH<6.0条件下,吸附属于外层吸附机理;在pH>6.0条件下,吸附属于内层吸附机理.pH<6.0时,中心原子Eu周围只有Eu-O一个配位层,其平均键长为2.40,配位数在9左右;随着pH逐渐升高,第一配位层的配位数下降,表明吸附Eu原子配位的对称性下降.当吸附时间延长或pH升高,吸附原子Eu周围出现了Eu-Eu和Eu-Ti第二配位层,其平均键长分别为3.60和4.40,配位数分别在2或1左右,表明形成了内层吸附产物或表面沉淀或表面多聚体.腐殖酸HA/FA的存在,可以改变Eu(III)在钛酸纳米管表面的吸附形态和微观原子结构,Eu(III)不仅可以与钛酸纳米管的表面羟基直接键合形成二元表面复合物(Eu-TNTs),还可以通过HA/FA的桥连作用形成三元表面复合物(HA/FA-Eu-TNTs).这些研究结果对于评估放射性核素Eu(III)与纳米材料在分子水平上的作用机理及分析Eu(III)在环境中的物理化学行为具有重要的意义.     

Evaluation of the stability of shortcut nitrification-denitrification process based on online specific oxygen uptake rate monitoring

Shortcut nitrification-denitrification (SCND) is widely concerned because of its low energy consumption and high nitrogen removal efficiency. However, the current difficulty lies in the stable maintenance of SCND performance, which leads to the challenge of large-scale application of this new denitrification technology. In this study, the nitrogen removal pathway from complete nitrification-denitrification (CND) to SCND was rapidly realized under high free ammonia (FA), high pH and low dissolved oxygen (DO) conditions. The variations of specific oxygen uptake rate (SOUR) of activated sludge in both processes were investigated by an online SOUR monitoring device. Different curves of SOUR from CND to SCND process were observed, and the ammonia peak obtained based on SOUR monitoring could be used to control aeration time accurately in SCND process. Accordingly, the SOUR ratio of ammonia oxidizing bacteria (AOB) to nitrite oxidizing bacteria (NOB) (SOUR_AOB/SOUR_NOB) was increased from 1.40 to 2.93. 16S rRNA Miseq high throughput sequencing revealed the dynamics of AOB and NOB, and the ratio of relative abundance (AOB/NOB) was increased from 1.03 to 3.12. Besides, SOUR_AOB/SOUR_NOB displayed significant correlations to ammonia removal rate (P<0.05), ammonia oxidation rate / nitrite oxidation rate (P < 0.05), nitrite accumulation rate (P < 0.05) and the relative abundance of AOB/NOB (P < 0.05). Thus, a strategy for evaluation the SCND process stability based on online SOUR monitoring is proposed, which provides a theoretical basis for optimizing the SCND performance.     

新型Al、Ti改性MCM-41材料对污水中Cu~（2＋）的吸附研究

研究了改性介孔硅基材料（以下简称MCM-41）对污水中重金属铜离子的吸附行为。在MCM-41材料中加入Al、Ti两种诱因金属离子来合成新的Al-Ti-MCM-41及Ti-Al-MCM-41改性材料,通过氮气吸附―脱附等温线对Al-Ti-MCM-41（1∶1）样品进行了表征,考察了吸附剂的投加量、Cu2＋初始浓度和吸附温...     

Influence of Free Ammonia on Completely Autotrophic Nitrogen Removal over Nitrite (CANON) Process

Free ammonia (FA) plays a significant role in the stable, long-term, completely autotrophic nitrogen removal over nitrite (CANON) system operation. The influence of FA on the CANON process in a sequencing batch biofilm reactor was explored. Under controlled FA concentrations of 5.0?mg L^?1 to 10.0?mg L^?1, nitrite-oxidizing bacteria (NOB) was inhibited and achieved partial nitrification, which was important for a successful and quick start-up of the CANON process from activated sludge. However, NOB was acclimated to the condition after the process start-up. Ammonia-oxidizing bacteria (AOB) and anaerobic ammonium-oxidizing bacteria (AnAOB) activities were unaffected when FA concentration was increased from 10?mg L^?1 to 17?mg L^?1, but NOB was completely inhibited only for a short time. The AOB and AnAOB activities were inhibited and the CANON system was deteriorated when FA concentration reached 30?mg L^?1 to 32.5?mg L^?1 at pH?8.5, whereas NOB activity was unaffected. Correlation analysis showed that FA concentration higher than 20?mg L^?1 resulted in the deterioration of the system.