Lifetime controlling factors

There is no reason to believe that these surfactant effects upon regioselecti-vity are related to differences in molecularity. In this respect they differ from micellar control of elimination to substitution ratios. The controlling factors may be the orientation or conformation of reactants or intermediates in micelles or similar aggregates and changes in the lifetimes of intermediates (cf. van der Langkruis and Engberts, 1984). 

Durability. Grass-like surfaces intended for heavy-duty athletic use should have a service life of at least eight years, a common warranty period provided by suppHers. Lifetime is more or less proportional to the ultraviolet (uv) exposure (sunlight) and to the amount of face ribbon available for wear, but pile density and height also have an effect. Color is a factor generally uv absorption is highest with red fabrics and least with blue. In addition, different materials respond differendy to abrasive wear. These effects caimot be measured except in simulated field use and controlled laboratory experiments, which do not necessarily redect field conditions. 

Economic factors include (a) the capital cost of the control technology (b) the operating and maintenance costs of the technology and (c) the expected lifetime and salvage value of the equipment. 

The temperature dependence of luminescent metal complexes can be controlled by molecular design that affects the energy gap between the emitting state and the deactivating d-d or by altering the preexponential factor for thermal deactivation. The sometimes large temperature dependencies of lifetime and quantum yields for metal complexes also suggest their use as temperature sensors. 

Studies in rats reported renal tubular adenomas and adenocarcinomas in male and female animals at doses of 20 mg/kg/day (Kociba et al. 1977a). Metastasis to the lungs was observed. Combined incidences of renal tubular neoplasms in males (9/39, 23%) and in females (6/40, 15%) increased (p <0.05) over controls (males-1/90, females-0/90, 0%). The tumor incidence was not increased in the 0.2 and 2 mg/kg/day dose groups but there were some indications of hyperplasia in animals exposed to 2 m /kg/day. The EPA (1990f) evaluated these data and calculated a human potency factor of 7.8x10 (mg/kg/day) (qi ), representing 95% upper confidence limit of extra lifetime human risk. Based on this value, cancer risk levels of 10, 10, and 10 correspond to exposures of 0.001, 0.0001, 0.00001 mg/kg/day. 

The first thing that stands out in Table 6.2 is that the OH-CH4 rate constant, 6.2 X 10 15 cm3 molecule 1 s-1, is much smaller than those for the higher alkanes, a factor of 40 below that for ethane. This relatively slow reaction between OH and CH4 is the reason that the focus is on non-methane hydrocarbons (NMHC) in terms of ozone control in urban areas. Thus, even at a typical peak OH concentration of 5 X 106 molecules cm 3, the calculated lifetime of CH4 at 298 K is 373 days, far too long to play a significant role on urban and even regional scales. Clearly, however, this reaction is important in the global troposphere (see Chapter 14.B.2b). 

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