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In the atmosphere

More precisely, the rate of ozone formation depends closely on the chemical nature of the hydrocarbons present in the atmosphere. A reactivity scale has been proposed by Lowi and Carter (1990) and is largely utilized today in ozone prediction models. Thus the values indicated in Table 5.26 express the potential ozone formation as O3 formed per gram of organic material initially present. The most reactive compounds are light olefins, cycloparaffins, substituted aromatic hydrocarbons notably the xylenes, formaldehyde and acetaldehyde. Inversely, normal or substituted paraffins. [Pg.261]

Hydrogen chloride released dissolves in water during condensation in the crude oil distillation column overhead or in the condenser, which cause corrosion of materials at these locations. The action of hydrochloric acid is favored and accelerated by the presence of hydrogen sulfide which results in the decomposition of sulfur-containing hydrocarbons this forces the refiner to inject a basic material like ammonia at the point where water condenses in the atmospheric distillation column. [Pg.329]

More complex ions are created lower in the atmosphere. Almost all ions below 70-80 km are cluster ions. Below this altitude range free electrons disappear and negative ions fonn. Tln-ee-body reactions become important. Even though the complexity of the ions increases, the detemiination of the final species follows a rather simple scheme. For positive ions, fomiation of H (H20) is rapid, occurring in times of the order of milliseconds or shorter in the stratosphere and troposphere. After fomiation of H (H20), the chemistry involves reaction with species that have a higher proton affinity than that of H2O. The resulting species can be... [Pg.818]

Ferguson E E 1979 ion-moiecuie reactions in the atmosphere K/nef/cs of Ion-Molecule Reactions ed P Ausioos (New York Pienum)... [Pg.827]

The ozone fonnation in the atmosphere is induced by radiation and a result of tliree-body collisions of the oxygen atoms with O2 molecules. This process requires a higher gas density and is, therefore, not efficient in the ionosphere. [Pg.2810]

Oxygen occurs free in the atmosphere (21% by volume. 23 by weight). The proportion is constant over the earth s surtace it is also constant for many miles upwards, because the turbulence of the atmosphere prevents the tendency for the lighter gases, for example helium, to increase in amount at higher altitudes. [Pg.260]

Deliquescence and efflorescence. A substance is said to deliquesce (Latin to become liquid) when it forms a solution or liquid phase upon standing in the air. The essential condition is that the vapour pressure of the saturated solution of the highest hydrate at the ordinary temperature should be less than the partial pressure of the aqueous vapour in the atmosphere. Water will be absorbed by the substance, which gradually liquefies to a saturated solution water vapour will continue to be absorbed by the latter until an unsaturated solution, having the same vapour pressure as the partial pressure of water vapour in the air, is formed. In order that the vapour pressure of the saturated solution may be sufficiently low, the substance must be extremely soluble in water, and it is only such substances (e.g., calcium chloride, zinc chloride and potassium hydroxide) that deliquesce. [Pg.43]

It must be emphasised that deliquescence and efflorescence are relative properties, since they depend upon the actual presence of water vapour in the atmosphere, which varies considerably with place and time. [Pg.43]

Fig. 77,13, 1 illustrates a distillation unit when it is desired to protect the distillate from moisture in the atmosphere. The drying tube may be filled with anhydrous calcium chloride held in position by loose plugs of glass wool or with a loose plug of cotton wool. Fig. 77,13, 2 depicts the use of an air condenser for liquids of boiling point above 140-150°. [Pg.86]

In combination, carbon is found as carbon dioxide in the atmosphere of the earth and dissolved in all natural waters. It is a component of great rock masses in the form of carbonates of calcium (limestone), magnesium, and iron. Coal, petroleum, and natural gas are chiefly hydrocarbons. [Pg.16]

Ozone s presence in the atmosphere (amounting to the equivalent of a layer 3 mm thick under ordinary pressures and temperatures) helps prevent harmful ultraviolet rays of the sun from reaching the earth s surface. Pollutants in the atmosphere may have a detrimental effect on this ozone layer. Ozone is toxic and exposure should not exceed 0.2 mg/m (8-hour time-weighted average - 40-hour work week). Undiluted ozone has a bluish color. Liquid ozone is bluish black and solid ozone is violet-black. [Pg.21]

Gr. neos, new) Discovered by Ramsay and Travers in 1898. Neon is a rare gaseous element present in the atmosphere to the extent of 1 part in 65,000 of air. It is obtained by liquefaction of air and separated from the other gases by fractional dishhation. [Pg.25]

Gr. xenon, stranger) Discovered by Ramsay and Travers in 1898 in the residue left after evaporating liquid air components. Xenon is a member of the so-called noble or "inert" gases. It is present in the atmosphere to the extent of about one part in twenty million. Xenon is present in the Martian atmosphere to the extent of 0.08 ppm. the element is found in the gases evolved from certain mineral springs, and is commercially obtained by extraction from liquid air. [Pg.124]

The increase of carbon dioxide in the atmosphere (even if its overall amount is only 0.035%) affects our global climate, although other... [Pg.216]

Shooter, D. Nitrogen Dioxide and Its Determination in the Atmosphere, /. Chem. Educ. 1993, 70, A133-A140. [Pg.225]

Water drops condensed in the atmosphere have much larger dimensions than gas molecules hence they are subject to the interference phenomena mentioned at the end of the last section. This alters the color of the scattered light. Smoke and dust particles are also larger and may absorb as well. [Pg.677]

For this reason blue radiation from the sun is scattered preferentially by particles in the atmosphere and the result is that a cloudless sky appears blue. [Pg.122]

It is the use of LIDAR devices as tools for spectroscopic measurements on the various gases present in the atmosphere which concerns us here. These include ozone, carbon dioxide, the CFCs (chlorofluorocarbons, such as CFC-11, trichlorofluoromethane, and CFC-12, dichlorodifluoromethane, used as refrigerants) and all those molecules regarded as atmospheric pollutants. [Pg.379]

Measurements of ozone (O3) concentrations in the atmosphere are of particular importance. Ozone absorbs strongly in the ultraviolet region and it is this absorption which protects us from a dangerously high dose of ultraviolet radiation from the sun. The vitally important ozone layer lies in the stratosphere and is typically about 10 km thick with a maximum concentration about 25 km above the surface of the earth. Extreme depletion of ozone in a localised part of the atmosphere creates what is known as an ozone hole. [Pg.380]

We saw in Section 9.3.8 that spectroscopy, in the form of LIDAR, is a very important tool for measuring ozone concentration directly in the atmosphere. A useful indirect method involves the measurement of the concentration of oxygen which is formed from ozone by photolysis ... [Pg.384]

Air pollution can be considered to have three components sources, transport and transformations in the atmosphere, and receptors. The source emits airborne substances that, when released, are transported through the atmosphere. Some of the substances interact with sunlight or chemical species in the atmosphere and are transformed. Pollutants that are emitted directiy to the atmosphere are called primary pollutants pollutants that are formed in the atmosphere as a result of transformations are called secondary pollutants. The reactants that undergo transformation are referred to as precursors. An example of a secondary pollutant is O, and its precursors are NMHC and nitrogen oxides, NO, a combination of nitric oxide [10102-43-9] NO, and NO2. The receptor is the person, animal, plant, material, or ecosystem affected by the emissions. [Pg.366]

Transport and Transformation. Once emitted into the atmosphere, the fate of a particular poUutant depends upon the stabihty of the atmosphere, which determines the concentration of the species, the stabihty of the poUutant in the atmosphere, which determines the persistence of the substance. Transport depends upon the stabUity of the atmosphere which, in turn, depends upon the ventilation. The stabUity of a poUutant depends on the presence or absence of clouds, fog, or precipitation the poUutant s solubUity in water and reactivity with other atmospheric constituents (which may be a function of temperature) the concentrations of other atmospheric constituents the poUutant s stabUity in the presence of sunlight and the deposition velocity of the poUutant. [Pg.367]

The StabUity or persistence of a poUutant in the atmosphere depends on the poUutant s atmospheric residence time. Mean residence times and principal atmospheric sinks for a variety of species are given in Table 2. Species like SO2, (NO and NO2), and coarse particles have lifetimes less than... [Pg.367]

Because of the mixture of VOCs in the atmosphere, the composition of smog reaction products and intermediates is extremely complex. formed via reaction 16, is important because when dissolved in cloud droplets it is an important oxidant, responsible for oxidising SO2 to sulfuric acid [7664-93-9] H2SO4, the primary cause of acid precipitation. The oxidation of many VOCs produces acetyl radicals, CH CO, which can react with O2 to produce peroxyacetyl radicals, CH2(C0)02, which react with NO2... [Pg.372]


See other pages where In the atmosphere is mentioned: [Pg.80]    [Pg.81]    [Pg.115]    [Pg.148]    [Pg.340]    [Pg.799]    [Pg.818]    [Pg.1389]    [Pg.2087]    [Pg.43]    [Pg.68]    [Pg.305]    [Pg.4]    [Pg.77]    [Pg.441]    [Pg.29]    [Pg.137]    [Pg.379]    [Pg.949]    [Pg.37]    [Pg.377]    [Pg.366]    [Pg.369]    [Pg.372]    [Pg.372]    [Pg.372]    [Pg.373]   


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Abiotic degradation in the air compartment (atmosphere)

Absorption in the atmosphere

Abundance in the Earth and atmosphere

Amounts of Constituents in the Atmosphere

Atmosphere lead in the

Atmosphere mercury in the

Atmosphere, chemistry in the

Attenuation of Solar Radiation in the Atmosphere

Biogeochemical Cycling of Macroelements in the Atmosphere

Biomarkers in the atmosphere

Breakdown in the Atmosphere

Bromide in the atmosphere

Buoyancy of a Rising (or Falling) Air Parcel in the Atmosphere

Cadmium in the Atmosphere

Carbon dioxide content in the atmosphere

Carbon dioxide in the atmosphere

Carbon fluxes in the atmosphere-plant-soil system

Charged particles in the atmosphere

Chemical Compounds in the Atmosphere

Chlorine in the atmosphere

Corrosion testing in the atmosphere

Cosmic rays in the atmosphere

Energy and Mass Transfer in the Atmosphere

Evaporation Processes in the Atmosphere

Excited Species in the Middle Atmosphere

Formation and Loss of O3 in the Clean Atmosphere

Formation of Ions in the Middle Atmosphere

Formation of singlet oxygen in the atmosphere

Formation of singlet oxygen in the contaminated atmosphere

Further reactions of iodine in the containment atmosphere

Gases in the atmosphere

Hazardous Wastes in the Atmosphere

Homogeneous Elementary Reactions in the Atmosphere and Rate Constants

Hydrogen in the atmosphere

Hydrogen sulfide in the atmosphere

In the Venusian atmosphere

Indirect Photolysis in the Atmosphere (Troposphere)— Reactions with Hydroxyl Radical (HO)

Isotopes in the Ocean and Atmosphere

Lidar in the study of atmospheric chemistry stratospheric measurements

Lidar in the study of atmospheric chemistry tropospheric measurements

Liquid Water in the Atmosphere

NO in the Upper Atmosphere

Nitrogen Oxides in the Atmosphere

Note on Times of Mixing in the Atmosphere and Oceans

Nucleation in the Atmosphere

Occurrence in rainwater, freshwater, and the atmosphere

Organic Pollutant Particles in the Atmosphere

Organics in the Atmosphere from Natural Sources

Other Forms of Water in the Atmosphere

Oxidation of Methane in the Natural Atmosphere and OH Radical Chain Reaction

Oxygen in the atmosphere

Ozone in the Atmosphere

Parameters in the Atmospheric Diffusion Equation

Percentage of nitrogen in major New England rivers that originates from fossil-fuel derived atmospheric deposition onto the landscape

Persistence of aerosols in the atmosphere

Phase Transitions in the Solid Elements at Atmospheric Pressure

Photochemical, reactions in the atmosphere

Photodissociation in the Upper Atmosphere

Photolysis Rates in the Atmosphere

Photolysis of SO2 in the Modern Atmosphere

Physical Transformations of Trace Substances in the Atmosphere

Pollutant Particles in the Atmosphere

Potential electrical, in the atmosphere

Pressure in the Atmosphere

Primary Reactions of the Calcite-Carbonate-Equilibrium with Atmospheric Contact in Infinitely Diluted Solutions

RADIOGENIC COMPONENTS IN THE BULK EARTH AND ATMOSPHERE

Radiative Flux in the Atmosphere

Radiative Transfer Processes in the Atmosphere

Reaction in the atmosphere

Reserves and fluxes of methane in the atmosphere-ocean-land system

Residence time in the atmosphere

Residence times of sulfate aerosols in the atmosphere

Scattering in the atmosphere

Solar Radiation in the Atmosphere

Sources and dispersion of microorganisms in the atmosphere

Sources of Trace Gases in the Atmosphere

Speciation in the Atmosphere

Speciation of metals in the atmosphere

Sulfur oxidation in the atmosphere

Temperature in the Lower Atmosphere

Temperature in the atmosphere

The Influence of Reductions in Atmospheric Sulphate Deposition on Ion

The burning of a fuel particle in an oxidizing atmosphere

The ionic atmosphere in more detail

Time Scales of Mixing in the Atmosphere and Oceans

Trace gases in the atmosphere

Transformation of sulfur compounds in the atmosphere

Transformations in the atmosphere

Transformations of Sulfur in the Atmosphere

Transport of Chemicals in the Atmosphere

Transport of HTO in the atmosphere

Typical Particle Concentrations in the Atmosphere

Variation of Pressure with Height in the Atmosphere

Variation of Wind with Height in the Atmosphere

Volume percentages of some variable gases (inorganic and organic) in the atmosphere

Water Equilibrium in the Atmosphere

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