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Environmental temperature change effect

Next, the signal processing to recover TL signals from large thermal noises is illustrated because the TL effect is very weak typically the largest value of AT is 10 ° and An is less than 10 . The former value is as small as the thermal fluctuation and easily affected by environmental temperature change. In order to recover the tme TL signal, the intensity of the... [Pg.3248]

The approach to the evaluation of vibrational spectra described above is based on classical simulations for which quantum corrections are possible. The incorporation of quantum effects directly in simulations of large molecular systems is one of the most challenging areas in theoretical chemistry today. The development of quantum simulation methods is particularly important in the area of molecular spectroscopy for which quantum effects can be important and where the goal is to use simulations to help understand the structural and dynamical origins of changes in spectral lineshapes with environmental variables such as the temperature. The direct evaluation of quantum time- correlation functions for anharmonic systems is extremely difficult. Our initial approach to the evaluation of finite temperature anharmonic effects on vibrational lineshapes is derived from the fact that the moments of the vibrational lineshape spectrum can be expressed as functions of expectation values of positional and momentum operators. These expectation values can be evaluated using extremely efficient quantum Monte-Carlo techniques. The main points are summarized below. [Pg.93]

To confirm their results and check for methodological problems, some studies have been carried out. As there was a probability that hypothermic conditions during temporary removal from dam may have affected the results, Pauluhn and Schmuck administered S-bioallethrin and deltamethrin to neonatal mice from postnatal day 10 to 16 under a hypo-, normo-, or hyperthermic environment, and measured the MAChR density at the age of 17 days [51]. Increase in MAChR in Cortex at PND 17 in animals treated with S-bioallethrin was observed. Meanwhile, no changes were observed in animals treated with deltamethrin. In addition, an enormous influence of environmental temperature on the density of MAChR receptors in the crude synaptosomal fraction of the cerebral cortex was ascertained. Tsuji et al. exposed mouse dams with their litters to D-allethrin by inhalation for 6 h from postnatal day 10 to 16. The inhalation administration method is the most relevant route of exposure for humans, including babies and infants, after indoor use of D-allethrin. The neonatal exposure to D-allethrin by inhalation did not induce effects either on the brain MAChR density or motor activity at 17 days and 4 months of age, or on performance in the leaming/memory test at 11 months of age [52]. Other unpublished studies with D-allethrin, S -bioallethrin, or deltamethrin were examined to confirm the results of Eriksson et al. and showed inconsistent results [53]. The reasons for discrepancy among these findings are unknown. [Pg.91]

However Smith and Symons (43, 44, 45) found that the theory of Franck and Platzman did not account for environmental (temperature, solvents, added salts) effects on the spectrum. They proposed instead a theory based on an electron in a box of radius r. Absorption of hv causes the resulting atom to contract, the electron preserving its radius as in the ground state. Environmental effects change this radius. [Pg.238]

Ivanov (1929) found a close inverse relationship between the value of lipid unsaturation of plants (determined by iodine value) and the latitude of their habitat. It was found that, with lower environmental temperatures, the iodine numbers of the lipids were greater (i.e. there was more unsaturation). The effect of increasing unsaturation is to lower the temperature at which the lipids change from liquids to a liquid-crystalline state, and so to lower the temperature at which the cells remain flexible. [Pg.15]

The greenhouse effect (planetary warming) has been the focus of much interest by environmentally active scientists for decades, (a) What are the most probable temperature changes at the equator and at the poles for 2050 (b) What... [Pg.533]

DNOC causes similar health effects in animals. In addition, injection of other dinitrocresols into animals caused similar effects. High environmental temperatures can worsen the harmful effects in some animals that swallow DNOC. Some animals exposed to DNOC for a long period show blood cell changes. Ducklings given high levels of DNOC in the diet for a short period developed cataracts. [Pg.15]

The strength of wood can be altered by environmental agents. The changes in pH, moisture, and temperature the influence of decay, fire, and UV radiation and the adsorption of chemicals from the environment can have a significant effect on strength properties. Environmentally induced changes must be considered in any discussion on the strength of treated or untreated wood. [Pg.212]

Covers the determination of the ability of rubber to withstand the environmental effects of high humidity and temperature. The effects are determined by noting the change in tensile strength after exposure over distilled water. [Pg.413]

For the determination of the thermal compatibility, the ASTM C 884-78 test method was followed. A layer of RPUMRPE mortar was applied to a slab of cured and air dried concrete. After the material cured for one week, the samples were subjected to five cycles of temperature change. In the first cycle, the specimens were placed in the environmental chamber at -6° 3°F (-21.1° 1,7°C) for 24 hours and then removed to room temperature at 73° 1,8°F (23 1°C) for 24 hours. Three beams with 1/2- to 2 inch (12- to 50-mm) overlays and four slab with 1/2-inch (12-mm) overlays were tested. No delaminations were found in the specimens. The direct shear tests were conducted to measure the effect of the thermal cycles. The results are shown in Table 8. [Pg.25]


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