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Emissions point source

Id. Additional conditions limit releases of PCBs from an emission point source to less than 10 ppm and limit the PCB concentration in wastewaters to 3 microgram per liter, about 3 ppb. [Pg.360]

One important sem source that is not based on thermionic emission is the field emission (fe) source. Fe-sem systems typically give images of much higher resolution than conventional sems due to the much narrower energy distribution (on the order of 0.25 eV) of the primary electron beam. A fe source is a pointed W tip from which electrons tunnel under the influence of a large electric field. This different mechanism of electron generation also results in a brightness comparable to a conventional thermionic source with much less current. [Pg.271]

Bubble Policy The bubble concept introduced under PSD provisions of the Clean Air Act Amendments of 1977 was formally proposed as EPA policy on Jan. 18, 1979, the final policy statement being issued on Dec. 11, 1979. The bubble pohcy allows a company to find the most efficient way to control a plant s emissions as a whole rather than by meeting individual point-source requirements. If it is found less expensive to tighten control of a pollutant at one point and relax controls at another, this woiild be possible as long as the total pollution from the plant woiild not exceed the sum of the current hmits on individual point sources of pollution in the plant. Properly apphed, this approach would promote greater economic efficiency and increased technological innovation. [Pg.2158]

Often batch process equipment needs to be located inside buildings. This is usually the case when the process needs to be shielded from extreme heat/cold conditions, the elements, and/or needs to be kept sterile. This leads to the need to provide adequate building ventilation to avoid buildup of hazardous material due to leaks and other process emissions. When the operation of a process involves opening, cleaning, charging etc., point source ventilation may also need to be provided. [Pg.27]

The third category for interactions is high dose (III). The effects produced by this level of interaction can be seen by the casual observer. The result of high-dose exposure is destruction or severe injury of the forest system. High-dose conditions are almost always associated with point source emissions. The pollutants most often involved are SO2 and hydrogen fluoride. Historically, the most harmful sources of pollution for surrounding forest ecosystems have been smelters and aluminum reduction plants. [Pg.120]

A version of the Gifford-Hanna model was evaluated (50) using 1969 data for 113 monitoring stahons for particulate matter and 75 stations for SO2 in the New York metropolitan area. This version differed from Eq. (20-19) in considering major point source contributions and the stack height of emission release. This model produced results (Table 20-2) comparable to those of the much more complicated COM model (51). [Pg.336]

The behavior of these pollution roses is intuitively plausible, because considerable hydrocarbon emissions come from motor vehicles which are operated in both winter and summer and travel throughout the urban area. On the other hand, sulfur dioxide is released largely from the burning of coal and fuel oil. Space heating emissions are high in winter and low in summer. The SO2 emissions in summer are probably due to only a few point sources, such as power plants, and result in low average concentrations from each direction as well as large directional variability. [Pg.360]

In this chapter we focus our attention on some of the point sources of air emissions within different types of plant operations, along with the methods of abatement. Although we do not make direct comparisons between prevention and control methodologies until Chapter 6, the reader should gain an appreciation for the simplicity of applying pollution prevention as opposed to incorporating engineering controls in many situations. [Pg.53]

The fourth source type option in SCREEN is for volume sources, which is selected by entering V or V for source type. The volume source algorithm is based on a virtual point source approach, and may be used for non-buoy ant sources whose emissions occupy some initial volume. The inputs requested for volume sources are as follows ... [Pg.312]

PM CALCULATOR-. PM Calculator will calculate controlled emissions for filterable PM2.5 and filterable PM 10 for point sources. Click the filename to download the file ... [Pg.334]

Note that this equipment is applicable only for stationary point source emission control. [Pg.400]

In the calculations that were made to predict ground level concentrations from a VCM reactor blow off, the Pasquill-Gifford-Holland dispersion model was used as a basis for these estimations. Calculations were made for six different stability classes and ground level concentrations, and at various distances from the point source of emission. [Pg.362]

While process and equipment modification are generally the preferred alternatives for reducing emissions from a plant, some form of control is necessary before emissions are discharged into the environment. Technologies discussed in this section are applicable in preventing emissions from point sources such as process or tank vents. These technologies fall into two main categories ... [Pg.1251]

The solid-flame model, presented in Section 3.5.2, is more realistic than the point-source model. It addresses the fireball s dimensions, its surface-emissive power, atmospheric attenuation, and view factor. The latter factor includes the object s orientation relative to the fireball and its distance from the fireball s center. This section provides information on emissive power for use in calculations beyond that presented in Section 3.5.2. Furthermore, view factors applicable to fireballs are discussed in more detail. [Pg.176]

The entire development on atmospheric dispersion lias been limited to eniissioiis from a "point" (e.g., stack) source. Altliough most dispersion applications involve point sources, in some instances tlie location of the emission can be more accurately described physically and niatlicmatically by either a line source or an area source. [Pg.379]

PLUVUE is a model tliat predicts tlie transport, atmospheric difinsion, chemical conversion, optical effects and surface deposition of point-source emissions. [Pg.386]

The Shoreline Dispersion Model (SDM) is a multipoint Gaussian dispersion model tliat can be used to determine ground-level concentrations from tall stationary point source emissions netir a shoreline emaromnent. SDM is used in conjunction witli MPTER algoritlnns to calculate concentrations when fumigation conditions do not exist. [Pg.386]

The short wavelength of x-rays naturally makes them difficult to focus. Electrons, on the other hand, can rather easily be controlled to give beams a few square microns in cross section, a fact that made possible the x-ray emission electron-microprobe (9.9). Clearly, such a concentrated electron beam striking one side of a suitable thin target can give rise to an x-ray spot on the other, and this spot can be small enough to be regarded as a point source of x-rays. [Pg.292]


See other pages where Emissions point source is mentioned: [Pg.569]    [Pg.1753]    [Pg.366]    [Pg.366]    [Pg.366]    [Pg.191]    [Pg.170]    [Pg.421]    [Pg.421]    [Pg.381]    [Pg.65]    [Pg.66]    [Pg.239]    [Pg.296]    [Pg.315]    [Pg.400]    [Pg.416]    [Pg.53]    [Pg.55]    [Pg.55]    [Pg.281]    [Pg.301]    [Pg.338]    [Pg.348]    [Pg.418]    [Pg.567]    [Pg.357]    [Pg.795]    [Pg.882]    [Pg.159]    [Pg.354]    [Pg.381]    [Pg.186]   
See also in sourсe #XX -- [ Pg.238 ]




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