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Level sources

Fig. 14-7. Distribution of sensitivity to ethylene sulfide odor in 33 individuals. The abscissa is the percentage of the individuals who detected the presence of ethylene sulfide at various levels. Source Dravnicks, A., and Jarke, F., J. Air PoIIut. Control Assoc. 30, 1284-1289 (19801. Fig. 14-7. Distribution of sensitivity to ethylene sulfide odor in 33 individuals. The abscissa is the percentage of the individuals who detected the presence of ethylene sulfide at various levels. Source Dravnicks, A., and Jarke, F., J. Air PoIIut. Control Assoc. 30, 1284-1289 (19801.
For sources having a large component of emissions from low-level sources, the simple Gifford-Hanna model given previously as Eq. (20-19), X = Cqju, works well, especially for long-term concentrations, such as annual ones. Using the derived coefficients of 225 for particulate matter and 50 for SO2, an analysis of residuals (measured minus estimated) of the dependent data sets (those used to determine the values of the coefficient C) of 29 cities for particulate matter and 20 cities for SOj and an independent data set of 15 cities for particulate matter is summarized in Table 20-1. For the dependent data sets, overestimates result. The standard deviations of the residuals and the mean absolute errors are about equal for particulates and sulfur dioxide. For the independent data set the mean residual shows... [Pg.335]

It is important to quantify the sound pressure levels in dB generated by each source and for each frequency (31.5-8000 Hz) in order to establish which noise will be masked or prevalent. It must be noted that when the pressure levels of two noises differ by more than 10 dB, the resulting level is equal to that of the higher-level source in other words, the noise at the higher level masks the noise at the lower level, which will not be perceptible to the listener (or the phonometer). In this case it is useless to reduce the latter noise, as the composed noise will remain the same, being influenced by the higher-level noise only. [Pg.797]

Wilson, D. J., A. G. Robins, and J. E. Fackrell. 1982b. Predicting the spatial distribution of concentration fluctuations from a ground level source. Atmospheric Environ. 16(3) 479-504. [Pg.68]

In tlie case of a ground level source with no effective plume rise (H = 0), tlien... [Pg.374]

Having determined tlie stability class. Figs. 12.6.2. and 12.6.3. may be used to evaluate ay and a as a function of downwind distance from tlie source. Figures 12.6.2. and 12.6.3. apply strictly to open, level country and probably underestimate tlie plume dispersion potential from low level sources in built-up areas. Altliough tlie vertical spread may be less than tlie values for class F witli... [Pg.375]

Fig. 3.6 A diagram linking macroscopic and microscopic levels. [Source list Century Science Chemistry, (Hunt Grayson, 2006, p. 51)]... Fig. 3.6 A diagram linking macroscopic and microscopic levels. [Source list Century Science Chemistry, (Hunt Grayson, 2006, p. 51)]...
Chemical Terrorism on local, national, and international levels (Source A FOA Briefing Book on Chemical Weapons)... [Pg.37]

A burning dump emits an estimated 3 g/s of oxides of nitrogen. What is the average concentration of oxides of nitrogen from this source directly downwind at a distance of 3 km on an overcast night with a wind speed of 7 m/s Assume that this dump is a point ground-level source. [Pg.216]

FIGURE 11.5 Extracted ion chromatogram of patient sample at typical low level. (Source Zahlsen, K. et al. LCGCN Amer. 23, 390, 2005. With permission.)... [Pg.307]

Other source conditions. The source height and the source area are also important source characteristics. The greatest impact is typically associated with ground-level sources, so elevated sources are not considered in the model discussion below. [Pg.63]

As this are ground—level sources the dispersion and deposition is over much shorter distances than the emissions from the industry ejected from high chimneys. Buijsman (5), calculated the ammonia emission in the Netherlands. He estimates the total emission into the atmosphere to be 130000 ton per year of which 110000 tons from animal manure. [Pg.31]

The inventory made by Buijsman in the Netherlands should be caracterised as a quite rough estimate. This is demonstrated by the assumptions on which he based his calculations. For instance he neglected the emission from stables for laek of reliable data. If the Government wants to reduce the acid precipitation, there will be paid attention to ammonia. As it is released from ground level sources reduction of ammonia emission has more effect on acid deposition in the region than in the case with S02 and NOx. [Pg.34]

If we consider downwind ground level concentrations on the plume centreline (y=0) for a ground level source (H=0) equation (1) becomes ... [Pg.249]

These rhythms can already occur at the cellular level. Source-. Goldbeter [31]. [Pg.256]

Most pheromone biologists have used the Sutton formula. For elevated odor sources, a more complicated version of the equation exists. However, compared with the concentration differences at different distances from the source, those between elevated and ground-level sources are minuscule (Elkinton etal., 1984). [Pg.10]

Identify major high-level sources of uncertainty. [Pg.173]

Various curing conditions are followed for various product lines. The following are temperature-steam pressure equivalents of saturated steam at sea level. Source Steam Tables of Marks and Davis, Longmans Green Co. [Pg.279]

Uncertainty is reported as the fraction of the observed value at the la confidence level. Source Reference 60. [Pg.165]

Trends identification of zones and areas with stagnant or increasing PM, NOx and NO2 levels. Sources of information were annual reports (2004/461/EC), AirBase and time extension notifications. Separate analysis of the trends of NOx and NO2 levels helps to identify areas influenced by increasing primary N02 emissions from diesel vehicles. [Pg.6]

Keywords Dioxins Effects Furans Levels Sources Trends Abbreviations... [Pg.72]

Zuccato, E., Calvarese, S., Mariani, G., Mangiapan, S., Grasso, P., Guzzi, A., Fanelli, R., 1999. Level, sources and toxicity of polychlorinated biphenyls in the Italian diet. Chemosphere 38, 2753-2765. [Pg.752]

FIGURE 8.5 Spider web diagram of sensory qualities of wild apricot vermouth of different sugar levels (source Abrol, 2009). [Pg.276]

Tuncel et al. tabulated S/Se ratios for particles from many locations (4). The ratio is about 3000 at rural sites downwind, but outside of coal-burning areas. In the midst of the ORV, it is depressed to about 1700, in agreement with the model. In the midst of cities in which substantial coal is burned, the ratio is depressed to 1000 or less. Except for a few samples at Allegheny Mt. collected downwind from three power plants, Tuncel et al. did not see sudden drops in the S/Se ratio that one would expect to see occasionally in fresh plumes from coal-fired plants. A major flaw in the Gor-don/Olmez model is the assumption of uniform vertical concentration profiles, which is surely a poor assumption just beyond a source. Most power plants have tall stacks, whereas, measurements are at ground level. The S/Se ratio will surely be depressed near the plume centerline, but the effect will usually be washed out before the plume hits ground level. However, around cities, there are probably some ground level sources. [Pg.79]

FIG. 8-30 The five levels of process control and optimization in manufacturing. Time scales are shown for each level. (Source Seborgetal, Process Dynamics and Control, 2ded., Wiley, New York,... [Pg.20]


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