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Oxidant control strategy

Urban Polluted Air Urban polluted air contains a few hundred species of hydrocarbons and oxygen containing volatile organic compounds (OVOCs) (Lewis et al. 2000), and the observation of OH and HO2 concentrations there validates the reaction model with the whole set of these VOCs. Comparisons between the model calculation and observation of OH and HO2 concentrations in urban air are also interesting from the point of checking the dependence of O3 formation rate on NOx and VOC in the polluted atmosphere, and are important as validation of a reaction model for the discussirai of the oxidant control strategy as described in the previous section. From these viewpoints, many measurements of and the comparison with model calculations have been made in urban air, and the values of (3-20) X 10 molecules cm for OH, and (1-12) x 10 molecules cm (4-50 pptv) for HO2 concentration, which are similar or higher than in the marine boundary layer, have been reported (Stone et al. 2012). [Pg.335]

T. W. Tesche and C. S. Burton, "Simulated Impact of Alternative Emissions Control Strategies on Photochemical Oxidants in Los Angeles," RF78-22R, Systems Applications, Inc., San Rafael, California,... [Pg.88]

Agent Hydrolysis and Treatment of Metal Parts (Steps 8, 10, 13, and 16), 115 Treatment of Hydrolysates and Dunnage by Supercritical Water Oxidation (Steps 11, 12, and 14), 116 Assessment of Integration Issues, 118 Component Integration, 118 Process Operability, 119 Monitoring and Control Strategy, 119 Maintenance Issues, 119 Process Safety, 120 Worker Health and Safety, 121 Public Safety, 121... [Pg.15]

The most complete data on ozone and other oxidant concentrations have been obtained for the Los Angeles air basin, because of the severity of the problem there. Further measurements are needed in the central and eastern areas of the United States, to broaden the foundations of a national control strategy. Such studies should be designed with specific goals in mind, and not carried out as routine monitoring exercises. [Pg.5]

Rational air pollution control strategies require the establishment of reliable relationships between air quality and emission (Chapter 5). Diffusion models for inert (nonreacting) agents have long been used in air pollution control and in the study of air pollution effects. Major advances have been made in incorporating the complex chemical reaction schemes of photochemical smog in diffusion models for air basins. In addition to these deterministic models, statistical relationships that are based on aerometric data and that relate oxidant concentrations to emission measurements have been determined. [Pg.5]

A realistic and detailed chemical model has great value. The stepwise addition of various primary pollutants can be made to evaluate the importance of each, llie effects of various emission control strategies on the chemistry of oxidant formation can be studied easily and quickly. It is possible to calculate the importance and concentration of various reactive intermediates. One can estimate the concentrations of various compounds that have not yet been observed in smog. And it is possible to pinpoint some of the important gaps, in order to stimulate future experimental studies. [Pg.32]

An important consequence is that control of atmospheric organic aerosol concentrations can be achieved by two types of control strategies specific control of precursors with high afa may prove to be as efficient as total hydrocarbon and nitrogen oxides emission control. [Pg.61]

During episodes of severe oxidant pollution, the weather is generally very hot (85-100 F or about 29-38 C) and the relative humidity may be either low or moderately high on class 2 and 3 days, depending on the behavior of the marine layer. The small difference between means of maximal hourly concentrations on high-pollution days in 1972-1974 suggests continuation of heavy primary-pollutant emission in spite of current control strategies. [Pg.599]

Air Pollution Control Strategies and Risk Assessments for Tropospheric Ozone and Associated Photochemical Oxidants, Acids, Particles, and Hazardous Air Pollutants... [Pg.871]

Given that the source of oxidants for S02 in both the gas and liquid phases is the VOC-NO chemistiy discussed earlier and that a major contributor to acid deposition is nitric acid, it is clear that one cannot treat acid deposition and photochemical oxidant formation as separate phenomena. Rather, they are very closely intertwined and should be considered as a whole in developing cost-effective control strategies for both. For a representative description of this interaction, see the modeling study of Gao et al. (1996). [Pg.922]

Wolff, G. T., and P. E. Korsog, Ozone Control Strategies Based on the Ratio of Volatile Organic Compounds to Nitrogen Oxides, J. Air Waste Manage. Assoc., 42, 1173-1177 (1992). [Pg.941]

Molecular-level design of catalytic ensemble structures on surfaces in a controllable manner, based on new chemical concepts and strategies regarding composition or structure, provides a promising opportunity for the development of novel and efficient catalysts active for selective oxidation. Novel strategies and concepts for the creation of active ensemble structures on flat and porous surfaces may emerge from self-assembly and in situ transformation of precursors immobilized on the surfaces, with the aid of in situ characterization by sophisticated physical techniques [1-6]. [Pg.43]


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See also in sourсe #XX -- [ Pg.324 , Pg.335 ]




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