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TRACE emission

The physical state of a pollutant is obviously important a particulate coUector cannot remove vapor. Pollutant concentration and carrier gas quantity ate necessary to estimate coUector si2e and requited efficiency and knowledge of a poUutant s chemistry may suggest alternative approaches to treatment. Emission standards may set coUection efficiency, but specific regulations do not exist for many trace emissions. In such cases emission targets must be set by dose—exposure time relationships obtained from effects on vegetation, animals, and humans. With such information, a Ust of possible treatment methods can be made (see Table 1). [Pg.385]

Fig. 14 Normalized absorption and emission spectra of 8-o-PhOH-dG (upper trace) and 8-o-PhOH-dA in buffered water (10 mM MOPS, pH 7, 0.1 M NaCl) (black trace) and hexane (grey trace). Emission spectra recorded at 280 nm. Fig. 14 Normalized absorption and emission spectra of 8-o-PhOH-dG (upper trace) and 8-o-PhOH-dA in buffered water (10 mM MOPS, pH 7, 0.1 M NaCl) (black trace) and hexane (grey trace). Emission spectra recorded at 280 nm.
A chemical plant complex used large volumes of brackish water from an adjacent river for once-through cooling. Occasionally, trace emissions of caustic soda were present in the effluent river water, and the company was concerned with pH excursions. An engineer was assigned to make modifications to reduce the opportunity of having environmental insults. [Pg.27]

M. E. Kitto and D. L. Anderson, "Simultaneous collection of particles and acidic gases for tracing emissions from coal-fired power plants," presented at the Amer. Chem. Soc. National Meeting, New York, April, 1986. [Pg.85]

Simultaneous Collection of Particles and Acidic Gases for Tracing Emissions from Coal-Fired Power Plants... [Pg.86]

Diisocyanates are an important class of chemicals of commercial interest, which are frequently used in the manufacture of indoor materials. such as adhesives, coatings, foams and rubbers (Ulrich, 1989). In some types of particle board, the diisocyanates have replaced formaldehyde. Isocyanates are characterized by the electrophilic -N=C=0 group, which can easily react with molecules containing hydroxy groups, such as water or alcohols. On hydrolysis with water, primary amines are formed, while a reaction with alcohols leads to carbamates (urethanes). Polyurethane (PUR) products are then obtained from a polyaddition of diisocyanate and diol components. Compounds commonly used in industrial surface technology are 4,4 -diphenylmethane diisocyanate (MDI) and hexamethylene diisocyanate (HDI). The diisocyanate monomers are known as respiratory sensitizers and cause irritation of eyes, skin and mucous membrane. Therefore, polyisocyanates such as HDI-biuret and HDI-isocyanurate with a monomer content <0.5 % are used for industrial applications, and isocyanate monomers will not achieve high concentrations in ambient air. Nevertheless, it is desirable to measure even trace emissions from materials in private dwellings. [Pg.215]

Excitation spectrum its emission was monitored at a wavelength of A, s 05 nm. Right trace Emission spectrum excited at a wavelength of = 320 nm. [Pg.509]

Hazardous and Trace Emissions System HATREMS EPA Public C Emissions data are stored on pollutants not regulated by Primary Ambient Air Standards. Included data can be used for modeling... [Pg.354]

Hazardous and Trace Emissions Monitoring System HATREMS EPA Public C See Table X... [Pg.378]


See other pages where TRACE emission is mentioned: [Pg.21]    [Pg.137]    [Pg.96]    [Pg.91]    [Pg.130]    [Pg.174]    [Pg.35]    [Pg.6]    [Pg.526]    [Pg.351]    [Pg.253]    [Pg.388]   
See also in sourсe #XX -- [ Pg.388 ]




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