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Total ozone

Several parameters are observed total amount of ozone (Dobson spectrophotometer), absorption in the 9.6-micron band, and emission from the ozone at several different zenith distances. The value of each of these observations may be expressed as the sum of contributions from the different layers of the ozone. Total amount of ozone is, of course, merely the sum of the amounts in each layer the infrared absorption, however, is pressure-dependent and a pressure-dependence term must be introduced. The sums are somewhat more complicated for the emission, but still are easily calculated. The problem is to find a distribution of ozone which will give rise to the... [Pg.222]

Production of hydrogen fluoride from reaction of Cap2 with sulfuric acid is the largest user of fluorspar and accounts for approximately 60—65% of total U.S. consumption. The principal uses of hydrogen fluoride are ia the manufacture of aluminum fluoride and synthetic cryoHte for the Hall aluminum process and fluoropolymers and chlorofluorocarbons that are used as refrigerants, solvents, aerosols (qv), and ia plastics. Because of the concern that chlorofluorocarbons cause upper atmosphere ozone depletion, these compounds are being replaced by hydrochlorofluorocarbons and hydrofluorocarbons. [Pg.137]

This cycle accounts for 30—50% of the total photochemical ozone loss observed during spring in the lower stratosphere at mid-north latitudes (76). [Pg.495]

Although httie or no reduction in total organic carbon occurs during ozonation, partially oxidized polar compounds (containing, COOH,... [Pg.502]

Fig. 8-3. Relationship between Los Angeles Basin s urban sources of photochemical smog and the San Bernardino Mountains, where ozone damage has occurred to the ponderosa pines. The solid lines are the average daily 1-hr maximum dose of ozone (ppm), )uly-September 1975-1977. Source Adapted from Davidson, A., Ozone trends in the south coast air basin of California, in "Ozone/Oxidants Interaction with the Total Environment.". A ir Pollution Control Association, Pittsburgh, 1979, pp. 433-450. Fig. 8-3. Relationship between Los Angeles Basin s urban sources of photochemical smog and the San Bernardino Mountains, where ozone damage has occurred to the ponderosa pines. The solid lines are the average daily 1-hr maximum dose of ozone (ppm), )uly-September 1975-1977. Source Adapted from Davidson, A., Ozone trends in the south coast air basin of California, in "Ozone/Oxidants Interaction with the Total Environment.". A ir Pollution Control Association, Pittsburgh, 1979, pp. 433-450.
The discovery of ozone holes over Antarctica in the mid-1980s was strong observational evidence to support the Rowland and Molina hypothesis. The atmosphere over the south pole is complex because of the long periods of total darkness and sunlight and the presence of a polar vortex and polar stratospheric clouds. However, researchers have found evidence to support the role of CIO in the rapid depletion of stratospheric ozone over the south pole. Figure 11-3 shows the profile of ozone and CIO measured at an altitude of 18 km on an aircraft flight from southern Chile toward the south pole on September 21, 1987. One month earlier the ozone levels were fairly uniform around 2 ppm (vol). [Pg.160]

Air passing through the NO pathway enters the reaction chamber, where the NO present reacts with the ozone. The light produced is measured by the photomultiplier tube and converted to an NO concentration. The NO2 in the air stream in this pathway is unchanged. In the NO pathway, the NO- and N02-laden air enters the converter, where the NO2 is reduced to form NO all of the NO exits the converter as NO and enters the reaction chamber. The NO reacts with O3 and the output signal is the total NO concentration. The NO2 concentration in the original air stream is the difference between NO and NO. Calibration techniques use gas-phase titration of an NO standard with O3 or an NOj permeation device. [Pg.200]

Approaches used to model ozone formation include box, gradient transfer, and trajectoty methods. Another method, the particle-in-cell method, advects centers of mass (that have a specific mass assigned) with an effective velocity that includes both transport and dispersion over each time step. Chemistry is calculated using the total mass within each grid cell at the end of each time step. This method has the advantage of avoiding both the numerical diffusion of some gradient transfer methods and the distortion due to wind shear of some trajectory methods. [Pg.330]

Demerjian, K. L., and Schere, K. L., Application of a photochemical box model for O3 air quality in Houston, TX, in "Proceedings of Ozone/Oxidants Interactions with the Total Environment II." Air Pollution Control Association, Pittsburgh, 1979, pp. 329-352. [Pg.341]

While motor vehicles built today emit fewer pollutants (60% to 80% less, depending on the pollutant) than those built in the 1960s, cars and trucks still account for almost half the emissions of the ozone precursors VOCs and NO, and up to 90% of the CO emissions in urban areas. The principal reason for this problem is the rapid growth in the number of vehicles on the roadways and total miles driven. [Pg.399]

A typical ozone system consists of 100 g/hr at a concentration of 1.0 percent to 1.5 percent in air fed to the bottom of bleach collection tanks through ceramic spargers (pore size of approximately 100 t). The system contains air compression and drying equipment, automatic control features, and a flat-plate, air-cooled ozone generator. Regeneration of bleach wastes totaling about 10,000 gallons a year, and recovery of other chemicals can also be cost effective. [Pg.490]

Multistage porous diffuser contactors, which involve a single application of an ozone-rich gas stream and application of fresh ozone gas to second and subsequent stages with off-gases recycled to the first stage. Eductor-induced, ozone vacuum injector contactors, which include total... [Pg.492]

FIGURE S.30 Comparison of ambient levels of t h maximum ozone, annual average of total suspended particulate matter (TSP), and sulfur dioxide in selected cities from around the world to illustrate the v tacion in these levels from countr)i to country with respect to the United States. [Reproduced from the National Air Quality and Emission Trends Report (1992), with permission.] ... [Pg.252]

In densely populated areas, traffic is responsible for massive exhausts of nitrous oxides, soot, polyaromatic hydrocarbons, and carbon monoxide. Traffic emissions also markedly contribute to the formation of ozone in the lower parts of the atmosphere. In large cities, fine particle exposure causes excess mortality which varies between one and five percent in the general population. Contamination of the ground water reservoirs with organic solvents has caused concern in many countries due to the persistent nature of the pollution. A total exposure assessment that takes into consideration all exposures via all routes is a relatively new concept, the significance of which is rapidly increasing. [Pg.256]

Tonnage of air emissions, water emissions and liquid and solid effluent and tonnage of hazardous materials released into the environment. These two measures are related to one another. However, the first measure relates the total effluent, including nonpolluting materials. The second measure looks only at the tonnage of hazardous materials contained in the total effluent. Both measures can be important indicators. For example, for solid waste it is important to know the total volume of material for disposal and different upstream treatment techniques may affect the total volume. However, for ozone depleting chemicals, only the quantity of these gases is important and other components such as water vapor may be irrelevant. [Pg.126]

As of November 1, 1992, all gasoline sold in the 39 CO nonattainment areas contained 2.7 wt% oxygen during the winter months. Beginning January 1, 1995, regulations mandated that gasoline sold in the nine worst ozone non-attainment areas contain at least 2.0 wt% oxygen and not more than 1 vol% benzene and 25 vol% total aromatics. Other cities that have had mobile source emission problems can optin voluntarily to the use of reformulated fuels. [Pg.311]

Ozone was generated using a Welsbach ozonator at a total gas flow... [Pg.37]

N2 and 0 liquids. The limited miscibility of ozone in oxygen is of practical importance because the dense, ozone-rich layer which settles to the bottom, is easily expld. The mutual solubility of the two liqs decreases when the temp is reduced. Thus, liq ozone and oxygen are completely miscible above 93.2°K (at which temp the total pressure is 1.25 atm), but at 90.2°K (the atm-bp of liq oxygen), there is separation into two layers, containing 17.6 and 67.2 mole % ozone, respectively. [Pg.468]

Pineneozonide and Pineneoxoozonide. A compn corresponding to something between Cj oHj 03 and Cj 0Hj 604 was obtained by Harries Nere-sheuner (Ref 2) on treating right-rotary turpentine with weak ozone. It could be sepd into thick oily (80—90% of the total) and solid fractions. The mixt was insol in common org solvents, and puffed off when heated on a spatula... [Pg.474]


See other pages where Total ozone is mentioned: [Pg.608]    [Pg.608]    [Pg.346]    [Pg.381]    [Pg.608]    [Pg.608]    [Pg.346]    [Pg.381]    [Pg.1696]    [Pg.266]    [Pg.476]    [Pg.276]    [Pg.494]    [Pg.495]    [Pg.495]    [Pg.501]    [Pg.502]    [Pg.398]    [Pg.246]    [Pg.282]    [Pg.121]    [Pg.465]    [Pg.2339]    [Pg.84]    [Pg.387]    [Pg.246]    [Pg.164]    [Pg.176]    [Pg.4]    [Pg.26]    [Pg.7]    [Pg.485]    [Pg.402]    [Pg.161]    [Pg.1224]    [Pg.764]   
See also in sourсe #XX -- [ Pg.55 , Pg.56 ]




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