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Nitric oxide photochemical production

The reaction in water at pH 7.4 has been much studied since the discovery of the importance of nitric oxide. The products are as for the thermal and photochemical reactions, except that the final product is nitrite ion. This is to be expected since nitric oxide in aerated water at pH 7.4 also yields quantitatively nitrite ion25, by it is believed the series of equations 7-9, which involves oxidation to nitrogen dioxide, further reaction to give dinitrogen trioxide which, in mildly alkaline solution, is hydrolysed to nitrite ion. Under anaerobic conditions it is possible to detect nitric oxide directly from the decomposition of nitrosothiols using a NO-probe electrode system26. Solutions of nitrosothiols both in... [Pg.669]

Besides the photochemical dissociation, ozone decays in oxidation-reduction reactions with different species. The stratospheric 03 reacts rapidly with nitric oxide and products of photodissociation of halogenated hydrocarbons (Figure 9.5). [Pg.131]

Nitrosothiols decompose photochemically and thermally to give the corresponding disulphides and nitric oxide18 23 14 24 (equation 6). In most cases the nitric oxide has not been identified as the primary product but rather as its oxidized form, nitrogen dioxide. [Pg.669]

In addition to observations in Los Angeles, Blumenthal and White have reported measurements of a power-plant plume and an urban plume 35 and 46 km downwind from St. Louis, Nfissouri. Bgute 4-25 shows the evidence of extensive ozone buildup in the urban plume. Simultaneous measurements of scattering coefficient, 6>cat, trace the spread and dilution of suspended particulate material. It is interesting that in the urban plume, which spreads to 20 km in width, the ozone increases while the particulate matter decreases this suggests considerable photochemical production at an altitude of 750 m. Contrary to the statements of Davis and co-workers reported above, the power-plant plume causes a decrease, rather than an increase, in ozone. Nitric oxide in the plume reacts with the ozone as it mixes. This is clearly indicated by the distribution of particulate matter, which acts as a tracer. [Pg.158]

Besides ozone, the main indicator of photochemical pollution, other important concomitant products are peroxyacetylnitrate (PAN), hydrogen peroxide, nitrogen dioxide, hydroxyl radicals and various aldehydes that are both products and primary pollutants, particles, sulfates, nitrates, ammonium, chloride, water, and various types of oxygenated organic compounds. The most important precursors of photochemical pollution are nitric oxide and hydrocarbons. The measurement procedures for the hydrocarbons are not as highly developed as those for ozone and the nitrogen oxides. [Pg.268]

Chromium hexacarbonyl decomposes on strong heating (explodes around 210°C). The product is chromous oxide, CrO. In inert atmosphere the products are chromium and carbon monoxide. It also is decomposed by chlorine and fuming nitric acid. Photochemical decomposition occurs when its solutions are exposed to light. [Pg.222]

In the first step of photochemical smog production, sunlight (hv) acts on nitrogen dioxide to produce nitric oxide and free oxygen ... [Pg.43]

Trifluoronitrosomethane (b.p. 86.0°C, 767 mm Hg) is of considerable interest as a component of high temperature-resistant elastomers. This compound has been prepared by treatment of trifluoroiodomethane, in the presence of mercury, with nitric oxide in a photochemical reactor whose mercury lamp emitted radiation at 253.7 mp.. The preparation is particularly sensitive to the initial pressure of the gases, reactant ratio, irradiation time, intensity of the ultraviolet radiation, reaction temperature, and method of removal of nitric oxide from the product [60]. [Pg.208]

Nitrogen oxide (NOx) The result of photochemical reactions of nitric oxide in ambient air a major component of photochemical smog. It is a product of combustion from transportation and stationary sources and a major contributor to the formation of ozone in the troposphere and to acid deposition. [Pg.609]

Globally, the oxides of nitrogen, NO (nitric oxide), NO2 (nitrogen oxide), and N2O (nitrous oxide), are key species involved in the chemistry of the troposphere and stratosphere. NO and N2O are produced mostly by microbial soil activity, whereas biomass burning is also an important source of NO. Nitric oxide is a species involved in the photochemical production of ozone in the troposphere, is involved in the chemical produaion of nitric acid, and is an important component of acid precipitation. Nitrous oxide plays a key role in stratospheric ozone depletion and is an important greenhouse gas, with a global warming potential more than 200 times that of CO2. [Pg.43]

Although a-dicarbonyl compounds are not known to be products of the ozonolysis of olefins, biacetyl has been isolated in photochemically initiated reactions 14, 15) which result in the net oxidation of olefins in the gas phase. For example, when a mixture of ci5-2-butene, nitric oxide, and air is irradiated, small amounts of biacetyl are isolated. One of the pathways suggested to explain the production of biacetyl involves the reaction of ozone with ci5-2-butene (14) ... [Pg.253]

Two of the key assumptions of the thin-film model (see Section 6.03.2.1.1) are that the main bodies of air and water are well mixed, i.e., that the concentration of gas at the interface between the thin film and the bulk fluid is the same as in the bulk fluid itself, and that any production or removal processes in the thin film are slow compared to transport across it. It is quite likely that there are near-surface gradients in concentrations of many photochemically active gases. Little research has been published, although the presence of near-surface gradients (10 cm to 2.5 m) in levels of CO during the summer in the Scheldt estuary has been reported (Law et al., 2002). Gradients may well exist for other compounds either produced or removed photochemically, e.g., di-iodomethane, nitric oxide, or carbonyl sulfide (COS). Hence, a key assumption made in most flux calculations that concentrations determined from a typical sampling depth of 4-8 m are the same as immediately below the microlayer may well often be incorrect. [Pg.2917]

Primary photochemical processes also may yield vibrationally excited products. Flash photolysis of cyanogen, cyanogen bromide and cyanogen iodide in each case yields a product whose absorption spectrum identifies it as a vibrationally hot CN radical with up to 6 quanta of excitation. VibrationaUy excited nitric oxide in the ground electronic state (detected by the A absorption system) is... [Pg.293]

Sulfur and nitrogen oxides react in the atmosphere to produce sulfuric and nitric acid, respectively. These react with photochemical products and airborne particles under ambient conditions to produce acid aerosols. Mixtures of these acid aerosols and ozone are synergistic and cause respiratory effects that are significantly more severe than those of ozone or the acids aloneJ39 41 ... [Pg.74]

A production of ozone occurs only by that fraction of H02 radicals entering into reaction with NO, whereas the fraction entering into reaction with 03 causes a loss of ozone. The relative probability of each of the above reaction steps is determined by the steady-state concentrations of the corresponding H02 reactions partners. Apart from the photochemical production rate, the concentrations of the radicals depend critically on the extent of the recycling reactions of H02 with NO and 03, that is, on the concentrations of ozone and nitric oxide. Since the former may be considered fixed, it is the latter that becomes a crucial parameter. In order to provide a more quantitative... [Pg.218]


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See also in sourсe #XX -- [ Pg.94 ]




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