Environmental factors affecting oxidation

Kagawa and Toyama in Tokyo followed 20 normal 11-yr-old school children once a week from June to December 1972 with a battery of pulmonary-function tests. Environmental factors studied included oxidant, ozone, hydrocarbon, nitric oxide, nitrogen dioxide, sulfur dioxide, particles, temperature, and relative humidity. Temperature was found to be the most important environmental factor affecting respiratory tests. The observers noted that pulmonary-function tests of the upper airway were more susceptible to increased temperature than those of the lower airway. Although the effect of temperature was the most marked, ozone concentration was significantly associated with airway resistance and specific airway conductance. Increased ozone concentrations usually occur at the same time as increased temperature, so their relative contributions could not be determined. 

Hamada N (1984) The content of lichen substances in Ramalina siliquosa cultured at various temperatures in growth cabinets. Lichenologist 16 96-98 Hamada N (1991) Environmental factors affecting the content of usnic acid in the lichen myco-biont of Ramalina siliquosa. Bryologist 94 57-59 Han D, Matsumaru K, Rettori D et al (2004) Usnic acid-induced necrosis of cultured mouse hepatocytes inhibition of mitochondrial function and oxidative stress. Biochem Pharmacol 67 439 51... 

PD affects approximately one million Americans (1% of people over 60 years of age). The average age of onset is 60 years of age, and PD is fairly uncommon in those under age 40. The etiology of PD is unknown, but genetic predisposition, environmental factors, or combinations of these have been proposed to explain why nerve cells in the substantia nigra deteriorate. About 15% of patients with PD have a first-degree relative with the disease. The pathogenesis of cell death (neuron degeneration) may be due to oxidative stress, mitochondrial... 

Oxidation-reduction reactions may affect the mobility of metal ions by changing the oxidation state. The environmental factors of pH and Eh (oxidation-reduction potential) strongly affect all the processes discussed above. For example, the type and number of molecular and ionic species of metals change with a change in pH (see Figures 20.5-20.7). A number of metals and nonmetals (As, Be, Cr, Cu, Fe, Ni, Se, V, Zn) are more mobile under anaerobic conditions than aerobic conditions, all other factors being equal.104 Additionally, the high salinity of deep-well injection zones increases the complexity of the equilibrium chemistry of heavy metals.106... 

These studies indicate that the charge transfer at the metal-oxide interface alters the electronic structure of the metal thin film, which in turn affects the adsorption of molecules to these surfaces. Understanding the effect that an oxide support has on molecular adsorption can give insight into how local environmental factors control the reactivity at the metal surface, presenting new avenues for tuning the properties of metal thin films and nanoparticles. Coupled with the knowledge of how particle size and shape modify the metal s electronic properties, these results can be used to predict how local structure and environment influence the reactivity at the metal surface. 

Little is known concerning the chemistry of nickel in the atmosphere. The probable species present in the atmosphere include soil minerals, nickel oxide, and nickel sulfate (Schmidt and Andren 1980). In aerobic waters at environmental pHs, the predominant form of nickel is the hexahydrate Ni(H20)g ion (Richter and Theis 1980). Complexes with naturally occurring anions, such as OH, SO/, and Cf, are formed to a small degree. Complexes with hydroxyl radicals are more stable than those with sulfate, which in turn are more stable than those with chloride. Ni(OH)2° becomes the dominant species above pH 9.5. In anaerobic systems, nickel sulfide forms if sulfur is present, and this limits the solubility of nickel. In soil, the most important sinks for nickel, other than soil minerals, are amorphous oxides of iron and manganese. The mobility of nickel in soil is site specific pH is the primary factor affecting leachability. Mobility increases at low pH. At one well-studied site, the sulfate concentration and the... 

The incremental reactivity of a VOC is the product of two fundamental factors, its kinetic reactivity and its mechanistic reactivity. The former reflects its rate of reaction, particularly with the OH radical, which, as we have seen, with some important exceptions (ozonolysis and photolysis of certain VOCs) initiates most atmospheric oxidations. Table 16.8, for example, also shows the rate constants for reaction of CO and the individual VOC with OH at 298 K. For many compounds, e.g., propene vs ethane, the faster the initial attack of OH on the VOC, the greater the IR. However, the second factor, reflecting the oxidation mechanism, can be determining in some cases as, for example, discussed earlier for benzaldehyde. For a detailed discussion of the factors affecting kinetic and mechanistic reactivities, based on environmental chamber measurements combined with modeling, see Carter et al. (1995) and Carter (1995). 

All the work described in this section thus has a common theme inasmuch as it deals with the influence of various environmental factors on the activity of homogeneous oxidation catalysts. In particular, the results shed valuable light on the ways in which temperature, the structure of the organic substrate, the concentration and the form of the catalyst, and reaction time may all affect the nature and kinetics of the various competing stages involved in the reaction of organic compounds with molecular oxygen. 

Miscellaneous, covering items such as environmental factors (e.g. humidity level affecting moisture pick-up of oxidized PAN fiber), testing equipment (not correctly calibrated). 

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