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双语推荐:硝化反硝化

短程硝化反硝化是指将硝化过程控制在亚硝化阶段,随后在缺氧条件下进行反硝化的生物脱氮过程。以亚硝酸盐为电子受体的短程硝化反硝化,其关键是如何实现亚硝酸盐的积累。本文主要介绍了以亚硝酸盐为电子受体的短程硝化反硝化的机理,以及影响亚硝酸盐积累的多种因素,包括C/N、FA(游离氨)、DO、pH等,探讨了短程硝化反硝化实现的主要工艺的途径。
Shortcut nitrification-denitrification was a process of biological denitrification vianitrite during which nitrification was controlled to the nitrite-typenitrification and subsequently denitrification happened under the anoxic condition. With nitrite as electron acceptor shortcut nitrification and denitrification, the most important thing was how to realize the accumulation of nitrite. The mechanism of shortcut nitrification-denitrification to nitrite as electron acceptor, a variety of factors influenced the accumulation of nitrite, including the C/N, FA ( free ammonia) , DO, pH. The processes of partial nitrification-denitrification were discussed finally.

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利用BaPS系统测定了不同施氮量(0,240,312 kg/hm2)、不同采样深度(0~20,20~40,40~60,60~80 cm)及作物不同生育时期等条件下黑土的硝化反硝化和呼吸速率。结果表明:BaPS系统能够用于测定黑土硝化反硝化和呼吸作用;随着采样深度的增加,黑土硝化速率和呼吸速率降低,而反硝化速率升高,各土层间差异极显著(F值分别为85.5**,791.3**,220.2**);评价黑土硝化反硝化及呼吸速率以0~20 cm土层监测数据为宜;随着施氮量的增加,黑土硝化反硝化及呼吸速率均呈现增加的趋势;黑土硝化反硝化和呼吸速率随季节的变化呈先升高后降低的趋势,三者约在7月上旬出现最高峰;适宜施氮量下(240 kg/hm2)黑土硝化速率最高为161.85μg/(kg·h),反硝化速率最高为325.23μg/(kg·h),呼吸速率最高为63.45 mg/(kg·d),施氮量增加,反硝化速率和呼吸速率升高。
In this study,a BaPS (Barometric Process Separation)technique was used to determine nitrifi-cation,denitrification and respiration rates in black soil of northeastern maize field under different nitro-gen fertilizer application rates (0,240,31 2 kg/hm2)at different soil depths (0-20,20-40,40-60, 60-80 cm)and in different growth periods .The results showed that BaPS could be used in determining rates of nitrification,denitrification and respiration in black soil .With the deepening of the sampling depth,rates of nitrification and denitrification decreased while that of respiration increased,and the dif-ferences between different soil layers were extremely significant (F values were respectively 85.5**, 791.3** and 220.2**).To evaluate nitrification,denitrification and respiration rates in black soil, monitoring data of 0-20 cm soil layer were most suitable;With the increase of N application amount, rates of nitrification,denitrification and respiration in black soil showed a strengtheni

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基于添加流离填料的连续流A/O生物膜应器,研究城市污水生物脱氮特征。系统在富氧条件(溶解氧大于1.5 mg·L-1)下连续运行113 d,氨氮和总氮去除率均稳定在50%。系统稳定运行阶段好氧区和出水均无亚硝酸盐或硝酸盐积累现象,表现出良好的同步硝化反硝化特征。16S rDNA分析表明,实现这一现象的主要功能细菌为好氧区存在的好氧反硝化菌;FISH分析表明,不同好氧区的好氧反硝化菌的活性和相对数量不同。结果证明系统内发生的同步硝化反硝化主要由好氧反硝化作用实现,硝化反应产生的硝酸盐类物质得到去除。根据试验结果与微生物学分析,提出了在富氧水环境中通过同步硝化反硝化途径脱氮的生物膜模型。
For municipal wastewater treatment, a continuous anoxic/aerobic system (A/O) combined with flow separate filler was developed to investigate nitrogen removal performance. A/O was running stably for 113 days under oxygen-enriched condition (dissolved oxygen, DO>1.5 mg·L-1). Removal of ammonia nitrogen and total nitrogen reached 50%, while nitrite and nitrate were not accumulating during the stable process. Simultaneous nitrification and denitrification was obvious in the aerobic zone. 16S rDNA results showed that functional bacterias were aerobic denitrifying bacteria (ADB) in the biofilm of the aerobic zone, and FISH results showed the activities of ADB along the aerobic zone. Aerobic denitrification was the main form of simultaneous nitrification and denitrification in the system, consuming nitrite and nitrate from nitrification. A nitrogen removal pathway modelvia simultaneous nitrification and denitrification in the biofilm under oxygen-rich water environment was establis

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结合国内外研究,从宏观环境理论、微环境理论以及微生物学理论三方面阐明了同步硝化反硝化的脱氮机理,并对同步硝化反硝化的影响因素进行了综述,提出了该技术今后的研究方向。
According to the latest research both at home and abroad,the nitrogen removal mechanism of simultaneous nitrification and denitrification is briefly introduced from three aspects including mac-roenvironment theory,microenvironment theory and microbiology theory.The paper also expounds the affecting factors of simultaneous nitrification and denitrification and gives the research direction of simultaneous nitrification and denitrification finally.

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采用5点取样法对海南岛吊罗山自然保护区内单优青皮林森林土壤进行取样,分析海拔高度、土层深度、季节及土壤理化性质对土壤的硝化反硝化作用影响因素。结果表明:海拔高度及土层深度对硝化反硝化作用影响不同;季节对其有显著影响(p<0.05),雨季土壤的硝化反硝化作用强度是旱季的几十至上百倍;土壤理化性质对土壤硝化作用没有影响(p>0.05),但全磷、全钾、有效磷、速效钾和含水率均与反硝化作用强度呈显著负相关(p<0.05)。以上结果说明,在研究区青皮林土壤氮素转化过程中,季节是重要影响因素,土壤部分理化性质是反硝化作用的重要影响因素。
5 point sampling method was adopted to take soil sample in the Vatica mangachapoi single-spe-cies-dominated forest of Diaoluoshan Nature Reserve,Hainan Island.The effects of altitude,soil layer depth,season and soil physical &chemical properties on the soil intensity of nitrification-denitrification were analyzed.The results showed that the altitude and soil layer depth had no significant effect on the soil nitrification-denitrification(p>0.05 ).The season had a significant effect on them (p 0.05 ),but the total phosphorus,total potassium,available phosphorus,available potassium and moisture content were significantly negative related to the soil intensity of denitrification(p<0.05 ). This suggests that the season is an important influence factor,and part of soil physical&chemical proper-ties are one of the important factors affecting soil denitrification intensity in the process of soil nitrogen transformation in the research area.

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传统的生物脱氮技术是通过投加有机碳源作为电子供体,利用异养反硝化微生物,经过硝化反硝化过程,将硝酸盐还原为氮气。近年来以铁基质为电子供体的自养反硝化菌的发现,为生物脱氮领域引入了全新的概念和思路。铁基质自养反硝化的实现是以NO-3作为电子受体,单质铁或Fe(Ⅱ)作为电子供体,通过微生物的氧化还原应获取能量的新型代谢途径。概述了目前国内外对铁基质自养反硝化菌的研究现状及应机理,并就铁自养反硝化微生物应用于污水处理领域的前景进行了展望。
The traditional biological removal of nitrate utilizes heterotrophic denitrifying bacteria throughout the nitrification and deni‐trification stages to convert nitrate to nitrogen with the extra organic matters as the electron donor .However ,a brand-new concept and mentality for the biological nitrogen removal are introduced with several isolated strains of Fe-dependent denitrifying bacteria in recent years .It is a new discovery of microbial metabolism that microorganisms utilize NO -3 as electron acceptors and Fe or Fe(Ⅱ ) as electron donors and get energy through the biochemical reaction for growth .In this paper ,the characteristics and mechanisms of Fe(Ⅱ )-dependent autotrophic denitrifying bacteria are reviewed ,and prospects of these bacterium are also discussed .

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以湖南桃源县一长期种植水稻的酸性土壤为研究对象,在微宇宙培养条件下设置了4个水分梯度处理,分别为田间持水量(water holding capacity,WHC)的30%、60%、90%和淹水2 cm 深。考察了水分条件变化对硝化反硝化作用影响,并结合定量 PCR 和限制性末端片段长度多态性(T-RFLP)技术研究了硝化-反硝化微生物的响应特征。结果表明,30% WHC 处理土壤无明显的硝化反硝化作用发生,硝化作用主要发生于60% WHC 和90% WHC 处理土壤,90% WHC 处理土壤硝化作用明显强于60% WHC,并检测到明显的N2 O释放,表明该水分条件可能发生了硝化-反硝化耦合作用。淹水处理土壤氧化还原势Eh 显著低于非淹水处理土壤,无明显的硝化作用发生,但能检测到N2 O释放且释放量小于90% WHC 处理土壤。除培养初期(7 d)外,反硝化功能基因 nirS 和 nirK,以及氨氧化细菌(AOB)amoA 基因的丰度先随着水分增加而增加,并在淹水处理中小幅下降,三者之间呈明显的正相关关系,且 AOB amoA、 nirS 和 nirK 基因丰度均在90% WHC 处理中最高,与该处理中硝化反硝化活性最高相一致。 T-RFLP 结果表明,培养2周后,nirS 基因为代表的反硝化微生物群落组成对水分梯度变化产生明显响应,Eh 和含水率 Cw 是影响其群落
To investigate the effect of moisture change on nitrification and denitrification and their corresponding functional microbes, an acidic paddy soil from Taoyuan, Hunan Province was selected as the study object, and soil microcosm experiment containing 4 different water holding capacity (WHC) levels (30% WHC, 60% WHC, 90% WHC, and waterlog) was set up in this study. Results showed that no active nitrification and denitrification occurred in 30% WHC treatment as there were no obvious ammonia consumption and nitrate accumulation, while nitrification was active in 60% WHC and 90% WHC treatments as indicated by the obvious accumulation of nitrate in those two treatments. Meanwhile, significant ammonia consumption and N2 O emission were only observed in 90% WHC treatment, implying that a much stronger nitrification in 90% WHC treatment than in 60% WHC treatment and the co-occurrence of nitrification and denitrification in 90% WHC treatment. In waterlog treatment, relatively lower N

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异养硝化细菌能够将环境中的还原态氮氧化成硝态氮,有效去除环境中氮素的污染,为生物脱氮技术提供了一个新的思路。本文简述了异养硝化细菌的研究现状,包括异养硝化细菌的种类、富集培养方法、硝化反硝化功能以及影响硝化功能的因素等。
Heterotrophic nitrification converts nitrogen compounds in the environment into nitrite and nitrate ,thus effectively reduces pollution .It could be a new application of the biological denitrification technology . This article reviews current studies relating to the heterotrophic nitrification that includes various bacterial culture methods , nitrification ,denitrification ,functions and affecting factors .

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全球每年通过人类活动新增的"活性"氮导致全球氮循环严重失衡,并引起水体的富营养化、水体酸化、温室气体排放等一系列环境问题。河流作为重要的氮汇,其氮循环对整个生态系统氮收支的影响、水体氮污染的改善和减少温室气体的排放与控制气候变化均具有重要意义。为了有助于理解反硝化过程中控制反硝化产物组成的影响因子,以利于增加反硝化最终产物氮气的释放,减少温室气体氧化亚氮的释放,从而加强对河流氮输送和氧化亚氮排放的管理,就河流反硝化的如下关键问题进行了综述:第一,河流反硝化作用的发生地点、时间以及其主要影响因素;第二,河流反硝化对河流氮负荷变化的响应机制;第三,河流系统的水文和地形地貌的变化对反硝化的影响,换言之,河流反硝化与河流水力学滞留时间及河流氮负荷的关系;第四,从生态系统尺度上讲,与陆地、海洋等生态系统相比,河流系统单位面积的反硝化率的时空变化特征,以及河流系统总的反硝化通量所占比例;第五,河流反硝化研究的主要方法。
Anthropogenic inputs of“new”active nitrogen(N)into the environment have caused water eutrophication, acidification as well as greenhouse gas emission.In this paper, the following issues were reviewed :when and where did the river denitrification occur? How dids denitrification respond to N concentration and load? What were relationships between river denitrification and water residence time and N load? How did river hydrology and geomorphology influence N losses from the denitrification? What were the characteristics of river denitri-fication rates at ecosystem scale? In addition, methods for measuring river denitrification were discussed.

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热带亚热带独特的土壤性质可能使得反硝化机理有别于温带土壤.文章综述了热带亚热带地区土壤氮素生物反硝化的研究进展,试图更好地了解该地区土壤反硝化在全球氮(N)循环以及在全球环境变化和生态系统响应互作中的角色.热带亚热带土壤反硝化强度普遍较温带地区弱,且随着土地利用方式和耕作管理措施的不同而呈现较大的时空变异性.影响土壤水分状况和土壤碳(C)、N 转化特性和速率的因素即为区域和农田尺度上的反硝化影响因素.湿润型热带亚热带土壤由于含有丰富的氧化物而致使土壤氧化还原势较高,这也是导致该地区土壤反硝化势较温带地区较低的关键土壤因素之-.然而土壤pH 值不是该地区土壤反硝化势较低的主要限制因素.有机C 矿化过程较土壤全氮含量和土壤C/N 比在决定湿润型亚热带土壤反硝化势方面更为重要.愈来愈多的证据表明热带亚热带土壤反硝化的生态环境效应不同于温带地区,热带亚热带地区土壤反硝化对全球变暖的贡献应综合考虑其对其它温室气体(如CH4,CO2)排放和氮沉降的影响.热带亚热带土壤生态系统具有-些防止土壤氮素反硝化损失的机制和保氮策略.然而,热带亚热带生态系统对全球变化的响应机制及其生物地球化学调控机制仍然不清楚,这些研究对于反硝化和其
Denitrification has been extensively studied in soils from temperate zones in industrialized countries. However, few studies quantifying denitrification rates in soils from tropical and subtropical zones have been reported. Denitrification mechanisms in tropical/subtropical soils may be different from other soils, due to their unique soil characteristics. The identification of denitrification in the area is crucial to understand the role of denitrification in the global nitrogen (N) cycle in terrestrial ecosystems, and in the interaction between global environmental changes and ecosystem responses. We review the existing literature on microbially-mediated denitrification in tropical/subtropical soils, attempting to provide a better understanding about and new research directions for denitrification in these regions. Tropical and subtropical soils might be characterized by generally lower denitrification capacity than temperate soils, with greater variability due to land use a

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