生物法处理NOx废气的研究进展

氮氧化物（NOx）是主要的大气污染物之一，是治理大气污染的一大难题，以当前国内外生物处理NOx的研究现状进行了系统的论述，介绍了生物过滤法处理氮氧化物的基本原理，分析了生物过滤法处理氮氧化物存在的问题，并预测该技术的未来发展趋势。     

挥发性有机物和臭味的生物过滤处理

生物过滤法是一种较新的空气污染控制方法,它利用微生物降解或／转化空气中的挥发性有机物以信硫化氢、氨等恶臭物质。本文主要介绍生物过滤法处理废气的基本原理,讨论填料种类、湿度、ｐＨ、温度等影响生物过滤法性能参数。同是综述了生物过滤法的应用范围以及对生物过滤法的改进。     

挥发性有机物和臭味的生物过滤处理

生物过滤法是一种较新的空气污染控制方法 ,它利用微生物降解或 /转化空气中的挥发性有机物以及硫化氢、氨等恶臭物质。本文主要介绍生物过滤法处理废气的基本原理 ,讨论填料种类、湿度、pH、温度等影响生物过滤法性能参数。同时综述了生物过滤法的应用范围以及对生物过滤法的改进。     

生物滤塔和NRB在有氧条件下去除废气中的NOx

研究了有氧条件下氮氧化物在生物滤塔内的传质机理,结果表明,当含NOx废气中氧气含量为20%、氧化度为80%时,被生物滤塔内微生物吸附分解的NOx仅占被净化的NOx的12%左右,而88%左右的NOx没有被微生物及时分解,而是转入液相中形成NO3-和NO2-.在此基础上,提出了采用生物滤塔和硝酸盐脱除反应器(nitrate...     

络合吸收结合生物转化去除氮氧化物技术

介绍了络合吸收结合生物转化处理NOx 技术的基本原理和目前的研究进展情况 ,并分析了该技术处理氮氧化物存在的问题和未来发展方向     

氮氧化物的生物治理技术

阐述了生物法去除氮氧化物的原理及去除氮氧化物的脱氮菌，介绍了国内外生物法治理氮氧化物的研究进展，最后提出了生物法处理氮氧化物存在的问题以及未来的发展趋势。     

生物转鼓工艺好氧同步处理工业废气中的SO2和NOx

为提升基于脱硫脱硝工艺的生物转鼓对工业废气中SO2、NOx的处理效果,在好氧条件下,分析了生物转鼓的启动过程、稳态下的生物相群落结构,考察了不同进气质量浓度下生物转鼓对SO2、NOx的处理效果和去除负荷,并探讨了生物转鼓同步脱硫脱硝过程中N和S的转化途径.结果表明:生物转鼓的启动挂膜需耗时约25d;门水平的脱硫脱硝优势...     

造纸废水治理技术研究现状及展望

介绍了造纸废水的各种处理技术：生物处理技术、絮凝沉淀法、过滤法、气浮法、造纸废水中主要碱回收技术、光催化氧化技术、人工湿地处理系统，并分析了治理技术的发展趋势。     

燃煤电厂氮氧化物控制技术与应用

简述了氮氧化物污染造成的危害 ,分别论述了燃煤电厂锅炉中 NOx和 N2 O形成的机理及主要控制技术 ,分析了目前国内电厂主要应用的控制措施及存在的问题 ,并提出研究开发具有自主知识产权的低投资、低运行成本的燃煤电站低NOx燃烧技术是当前急待解决的问题。     

生物法净化低浓度工业废气的技术进展

综述了生物法净化有害气体的发展历史与现状，介绍了有机废气、SO2、H2S、NOx废气处理的生物净化实验研究和工业应用情况。     

Sensitivity of nitrogen dioxide concentrations to oxides of nitrogen controls in the United Kingdom

There is a possibility of further controls on emissions to the atmosphere of nitrogen oxides to meet air quality objectives in the UK. Data in the National Air Quality Archive were used to calculate the likely sensitivity of hourly concentrations of nitrogen dioxide in ambient urban air to changes in the total oxides of nitrogen. Since the role of atmospheric chemical reactions is to make the response non-linearly dependent on the emissions control, we seek to establish the magnitude and sign of the effects that this non-linearity might cause. We develop a quantitative approach to analysing the non-linearity in the data. Polynomial curve fits have been developed for the empirical ratio NO₂ : NO_x (the ‘yield’). They describe nitrogen dioxide concentrations using total oxides of nitrogen. The new functions have the important feature of increased yield in winter episodes. Simpler functions tend to omit this feature of the yields at the highest hourly concentrations. Based on this study, the hourly nitrogen dioxide objective in the UK may require emissions control of no more than ≈50% on total oxides of nitrogen at the most polluted sites: other sites require less or even no control.     

固定源氮氧化物排放及控制技术应用

固定源是氮氧化物排放的一个主要来源.通过对主要固定源氮氧化物生成机理及现有的排放控制技术进行论述,分析我国固定源氮氧化物排放的实际情况,提出我国固定源氮氧化物排放控制还处于起步阶段,氮氧化物排放标准相对宽松,氮氧化物排放控制技术有待进一步普及,并提出固定源氮氧化物排放治理的一些建议.     

固定源氮氧化物排放及控制技术应用

固定源是氮氧化物排放的一个主要来源。通过对主要固定源氮氧化物生成机理及现有的排放控制技术进行论述，分析我国固定源氮氧化物排放的实际情况，提出我国固定源氮氧化物排放控制还处于起步阶段，氮氧化物排放标准相对宽松，氮氧化物排放控制技术有待进一步普及，并提出固定源氮氧化物排放治理的一些建议。     

Considerations in Setting Standards for Oxides of Nitrogen

Since 1959 the California Department of Public Health has held responsibility for setting standards for ambient air quality and for motor vehicle emissions. The need for standards for oxides of nitrogen involves consideration both of direct effects and effects resulting from participation in photochemical smog reactions. This paper discusses the various effects of concern and describes the department’s program for establishing air quality standards which will become the basis for vehicle emission standards and serve as guides for control of other sources of oxides of nitrogen.     

Calculating Air Quality and Its Control

Air quality is shown as a function of averaging times of five minutes to one year for carbon monoxide, hydrocarbons, nitric oxide, nitrogen dioxide, nitrogen oxides, oxidant, and sulfur dioxide in Chicago, Cincinnati, Los Angeles, New Orleans, Philadelphia, San Francisco, and Washington, D. C. Concentrations are approximately lognormally distributed for all pollutants in all cities for all averaging times. Maximum concentration is inversely proportional to averaging time to an exponent. The exponent is a function of the standard geometric deviation. General air quality and control parameters are derived and shown for one example, nitrogen oxides in Washington, D. C. These values are compared to one air quality standard.     

The impact of motor vehicle control technologies on future photochemical ozone formation in the United Kingdom

Legislation to control motor vehicle exhaust emissions has been introduced in the United Kingdom in stages since the early 1970s. Recently, a further step has been taken towards reducing future exhaust emissions of carbon monoxide, unburnt hydrocarbons and oxides of nitrogen in the 'Luxembourg agreement' (Lubinska, 1985). In this paper, the possible impact of these proposed controls on photochemical air pollution formation in the United Kingdom is investigated, including an evaluation of the relative merits of the two principal emission control options for petrol-driven cars: 'Lean Burn' engines and 'Catalyst' exhaust gas treatment.     

Cleaning of Stack Gases Containing High Concentrations of Nitrogen Oxides

Multistage gas absorption of 1–50% nitric oxide, nitrogen dioxide, and nitrogen tetraoxide from air with water or caustic solutions can produce colorless stack discharges. The rate at which NO is oxidized to No₂ in the gas phase and the solubility rate of No₂ in water or solution are highly concentration dependent so that reductions of stack gas concentrations of nitrogen oxides below approximately 200 ppm appear to be impractical. High efficiency absorption combined with elevated discharge of the cleaned, colorless gases is an acceptable method of air pollution control for many troublesome operations. Experiences in the fields of rocketry and nuclear energy are cited. Engineering modifications of metal pickling operations have been found especially helpful in producing effective control at an acceptable cost.     

Problems of Meeting Multiple Air Quality Objectives for Coal-Fired Utility Boilers

Gaseous wastes and particulate emissions are produced in the process of burning coal to produce electrical energy. In attempting to control these gaseous wastes, changes in the operation efficiency of boilers and secondary equipment are likely to result, and in addition liquid and solid waste streams are produced. The interrelationships among the various forms of wastes and the effects of air quality control on process efficiency are often overlooked in studies of environmental quality management.

The study was undertaken to evaluate the technical alternatives for handling gaseous and particulate emissions from coal-fired boilers and to determine the feasibility of meeting several standards simultaneously. The gaseous emissions of major importance in the combustion of coal are parti culates, oxides of sulfur, and oxides of nitrogen. Particulates can be controlled by a tradeoff among further preparation at the mine (for additional ash removal), type of boiler, use of dust control equipment and high stacks for dispersion of residual emissions, if ambient air standards are considered. Oxides of sulfur reduction depends currently on fuel substitution, limestone additives in the boiler and some form of contact process such as wet scrubbing, or the use of high stacks. Oxides of nitrogen control in coal fired boilers is restricted to small reductions by either changes in boiler operation, such as lower excess air levels, adsorption during wet scrubbing or by dispersion from high stacks.     

Visibility Regulations

Experiments were conducted to investigate the appearance of contaminants in fluorocarbon-film bags which have been widely used as photochemical reactors and storage containers in air pollution research. Clean air stored in such bags was gradually contaminated by a wide range of heavy hydrocarbons (≥ C₅ ) as well as by nitrogen oxides. Warming a bag dramatically increased the contamination rate for hydrocarbons. The substances observed in the bags appear to have originated in the air outside the bags and appeared in the bags due to the permeability of the film. When a bag was stored in a controlled clean environment, the rate of contamination by hydrocarbons was dramatically reduced. Experiments in which high concentration mixtures of hydrocarbons and nitrogen oxides were stored in the bags likewise showed that some high molecular weight hydrocarbons as well as NO and NO₂ permeate through the bag walls. Decontamination of the bags can be accomplished by storing them in a clean environment.     

Transformations,Lifetimes, and Sources of NO2, HONO,and HNO3 in Indoor Environments

Recent research has demonstrated that nitrogen oxides are transformed to nitrogen acids in indoor environments, and that significant concentrations of nitrous acid are present in indoor air. The purpose of the study reported in this paper has been to investigate the sources, chemical transformations and lifetimes of nitrogen oxides and nitrogen acids under the conditions existing in buildings. An unoccupied single family residence was instrumented for monitoring of NO, NO₂, NO_y, MONO, HNO₃, CO, temperature, relative humidity, and air exchange rate. For some experiments, NO₂ and HONO were injected into the house to determine their removal rates and lifetimes. Other experiments investigated the emissions and transformations of nitrogen species from unvented natural gas appliances. We determined that HONO is formed by both direct emissions from combustion processes and reaction of NO₂ with surfaces present indoors. Equilibrium considerations influence the relative contributions of these two sources to the indoor burden of HONO. We determined that the lifetimes of trace nitrogen species varied in the order NO ~ HONO > NO₂ >HNO₃. The lifetimes with respect to reactive processes are on the order of hours for NO and HONO, about an hour for NO₂, and 30 minutes or less for HNO3. The rapid removal of NO₂ and long lifetime of HONO suggest that HONO may represent a significant fraction of the oxidized nitrogen burden in indoor air.