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The influence of temperature on emission

Temperature was measured with a mercury thermometer with a range from 0 to 30 C. Air velocity was 0.3 to 0.4 m/s in this temperature region. The relationship is linear and the equations expressing emission [g/m /h] relative to temperature [°C] for different solvents are  [Pg.1231]

1- trichloroethane extraction naphtha petroleum(mineral) spirits wood preservatives [Pg.1231]


The following is an example of applying an INNOVA gas analyzer, a real-time monitoring system, to study the influence of temperature on VOC emissions, by using the so-called C-history method (Zhang et al., 2007a). [Pg.87]

The influence of temperature on PL spectra is considered in section 6. In general, in agreement with the Boltzmann law, the intensity of PL increases when the temperature decreases. Furthermore, a much better resolution of vibrational fine structure of the emission (fluorescence and phosphorescence) can be observed at low temperature. [Pg.38]

Van der Wal J.F., Hoogeveen A.W. and Wouda P. (1997) The influence of temperature on the emission of volatile organic compounds from PVC flooring, carpet and paint. Indoor Air, 7, 215-221. [Pg.141]

FIGURE 9. Schematic representation of the potentials of excimers and ground-state pairs in pair and stack structures, showing the influence of temperature on the energies of emission. [Pg.510]

Hansted, L., Jakobsen, H. B. and Olsen, C.E. (1994). Influence of temperature on the rhythmic emission of volatiles from Ribes nigrum flowers in situ. Plant, Cell and Environment 17 1069-1072. [Pg.171]

Accurate modeling is only possible by the consideration of wavelength-dependent optical and temperature-dependent thermodynamic parameters and the correct application of the thermal accommodation coefficient which is dependent on the ambient particle conditions and is described in detail elsewhere (Schulz et al., 2006 Daun et al., 2007). Moreover, Michelsen (2003) suggested the inclusion of a nonthermal photodesorption mechanism for heat and mass loss, the sublimation of multiple cluster species from the surface, and the influence of annealing on absorption, emission, and sublimation. A more general form of the energy equation including in more detail mass transfer processes has been derived recently by Hiers (2008). For practical use, Equation (1) turns out to be of sufficient physical detail. [Pg.226]

Sulzmann et al. [386] have studied the onset of CO2 formation behind incident shock waves in CO/O2 /Ar mixtures containing about 80 % ai on by means of emission intensity measurements at 3064 and 4470 A, and also at 4.25 and 5.07 pm. They also investigated the influence of hydrogen on the induction period [387]. Temperatures were in the range 1500—3000 K. In comparing the results of the experiments with an analytical expression for the induction times, they considered reaction (Ixii) to be the initiating step in both cases, viz. [Pg.189]

Luminescence spectra of barbiturates have been studied, usually for analytical purposes by room- 3 61-65 or low-temperature (77 K) techniques. 3,56,65-67 The structure-luminescence relationships 3,68 and the influence of substituents on the fluorescence characteristics were also investigated. 3,69-71 Only 5,5-disubstituted barbiturates, as the dianion species, show significant fluorescence at 420 nm. However, the dianions of other barbiturates exhibit very weak emissions or none at all, except for 5-phenylbarbituric acid.53 Barbiturates also exhibit low-temperature flu-... [Pg.238]

However, low-temperature spectroscopy, in particular the fluorescence-narrowed emission, can in principle tell one further thing about the influence of proteins on chromophores. There can be a quasi-continuous tail at energies below the ZPL peak, and it represents coupling of the dipole transition to the low-frequency modes (the phonons) of the protein or the solvent. The relative strength of the ZPL to the phonon tail is the Debye-Waller factor and is a measure of the strength of the phonon-chro-mophore coupling. The phonon band is expected to be homogeneously broadened. Unfortunately, at this point no one has been able to use low-temperature spectroscopy to resolve the ZPL and the Debye spectrum in a protein, or observe the Debye factor as a function of temperature. We look forward to these important measurements. [Pg.163]

Moore, T. R. and Dalva, M. 1993. The influence of temperature and water table position on carbon dioxide and methane emissions from laboratory columns of peatland soils. J. Soil Sci. 44 651-664. [Pg.742]

The role of isoprene chemistry in controlling atmospheric composition and climate, and the influence of temperature and land use change on isoprene emissions, should not be underestimated. The field observations of OH in isoprene-rich, NO c-poor environments discussed above indicate that isoprene has a considerably smaller effect on OH concentrations than chemistry models predict. This conclusion, based on direct measurements of OH and comparison with model predictions, is also supported by observations of other atmospheric species undertaken in VOC rich NO poor environments. Discrepancies between isoprene concentration measurements and model predictions when constrained to isoprene emission inventories have been reported, as have discrepancies between model predictions of isoprene oxidation product concentrations and those measured. Large model underestimates of OH reactivity and SOA formation under isoprene-rich conditions also point towards significant uncertainties in the OH-initiated isoprene oxidation mechanism. [Pg.75]

The results of over 1 year of continuous, on-line acoustic emission (AE) structural surveillance of high temperature / high pressure steam headers, gained on 2 M-scale 600MW supercritical multifuel ENEL power units in normal operation, are presented in the paper. The influence of background noise, the correlation between plant operating conditions (steady load, load variations, startup / shutdown transients) and AE activity and the diagnostic evaluation of recorded AE events are also discussed. [Pg.75]

As mentioned above, the interpretation of CL cannot be unified under a simple law, and one of the fundamental difficulties involved in luminescence analysis is the lack of information on the competing nonradiative processes present in the material. In addition, the influence of defects, the surface, and various external perturbations (such as temperature, electric field, and stress) have to be taken into account in quantitative CL analysis. All these make the quantification of CL intensities difficult. Correlations between dopant concentrations and such band-shape parameters as the peak energy and the half-width of the CL emission currently are more reliable as means for the quantitative analysis of the carrier concentration. [Pg.154]

It would appear that measurement of the integrated absorption coefficient should furnish an ideal method of quantitative analysis. In practice, however, the absolute measurement of the absorption coefficients of atomic spectral lines is extremely difficult. The natural line width of an atomic spectral line is about 10 5 nm, but owing to the influence of Doppler and pressure effects, the line is broadened to about 0.002 nm at flame temperatures of2000-3000 K. To measure the absorption coefficient of a line thus broadened would require a spectrometer with a resolving power of 500000. This difficulty was overcome by Walsh,41 who used a source of sharp emission lines with a much smaller half width than the absorption line, and the radiation frequency of which is centred on the absorption frequency. In this way, the absorption coefficient at the centre of the line, Kmax, may be measured. If the profile of the absorption line is assumed to be due only to Doppler broadening, then there is a relationship between Kmax and N0. Thus the only requirement of the spectrometer is that it shall be capable of isolating the required resonance line from all other lines emitted by the source. [Pg.782]

Fig. 7.1.6 Influence of pH and temperature on the luminescence of Cbaetopterus photoprotein elicited by old dioxane and Fe2+ in 20 mM phosphate buffer. Left panel the effect of pH in phosphate buffer solutions of various pH values, at 22°C. Right panel the effect of temperature at pH 7.2. Luminescence was initiated by the injection of Fe2+. The time lag of the light emission after the Fe2+ injection was also shown in the right panel. From Shimomura and Johnson, 1966. Fig. 7.1.6 Influence of pH and temperature on the luminescence of Cbaetopterus photoprotein elicited by old dioxane and Fe2+ in 20 mM phosphate buffer. Left panel the effect of pH in phosphate buffer solutions of various pH values, at 22°C. Right panel the effect of temperature at pH 7.2. Luminescence was initiated by the injection of Fe2+. The time lag of the light emission after the Fe2+ injection was also shown in the right panel. From Shimomura and Johnson, 1966.
The book focuses on three main themes catalyst preparation and activation, reaction mechanism, and process-related topics. A panel of expert contributors discusses synthesis of catalysts, carbon nanomaterials, nitric oxide calcinations, the influence of carbon, catalytic performance issues, chelating agents, and Cu and alkali promoters. They also explore Co/silica catalysts, thermodynamic control, the Two Alpha model, co-feeding experiments, internal diffusion limitations. Fe-LTFT selectivity, and the effect of co-fed water. Lastly, the book examines cross-flow filtration, kinetic studies, reduction of CO emissions, syncrude, and low-temperature water-gas shift. [Pg.407]

During chase incubation at 4°C, no significant change of the cell-associated fluorescence intensity should be detected over time. Because of the reduced incubation temperature, the metabolism of the cells is minimized, resulting in an inhibition of active uptake processes. Upon subsequent addition of monensin, the fluorescence emission signals should not be altered as well. In doing so, any direct influence of monensin on the quantum yield of the fluorescein label can be excluded [25],... [Pg.652]

Tingey, D. T., M. Manning, L. C. Grothaus, and W. F. Burns, The Influence of Light and Temperature on Isoprene Emission Rates from Live Oak, Physiol. Plant., 47, 112-118 (1979). [Pg.262]


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