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Emission sampling

Method 25 applies to the measurement of volatile organic compounds (VOC) as nonmethane organics (TGNMO), reported as carbon. Organic particulate matter will interfere with the analysis, and, therefore, in some cases, an in-stack particulate filter will be required. The method requires an emission sample to be withdrawn at a con-... [Pg.2203]

Schneider, E., P. Krenmayr, and K. Varmuza, A Routine Method for the Analysis of Mononitro-PAH in Immission and Emission Samples, Monatsh. Chem, 121, 393-401 (1990). [Pg.542]

A loading hypothesis resulting from a knowledge of the emission structure can be proved by emission sampling, followed analysis and application of MVDA. This means that emitters which pollute the environment can be identified. [Pg.264]

Brenner KS. 1986. Pu-foam-plug technique and extractive co-distillation (Bleidner apparatus), versatile tools for stack emission sampling and sample preparation. Chemosphere 15 1917-1922. [Pg.593]

Emissions Sampling of Combustion Effluents from a Stationary Diesel Engine That Bums a Coal-Derived Liquid Fuel... [Pg.130]

Other Gaseous Emissions. Emissions samples for SO3 and chlorides measurements were also included in this program. In total,... [Pg.136]

Piispanen, W. Webb, P. Trayser, D. "Emissions Sampling for Utility Diesel Synfuel Tests" ... [Pg.137]

Our experiment has demonstrated the possibility of the carbon nanotubes synthesis by low temperature (substrate temperature was 500°C) vapor deposition method from the ethanol vapor. Field emission samples were produced with different catalyst distribution on the substrate surface. [Pg.268]

CEN-Norm-Entwurf Dioxins (2/1992), Annex 3, CEN/TC 264/WG I.. .Determination of the mass concentration of polychlorinated dibenzo-p-dioxins (PCDDs) and dibenzofurans (PCDFs) - Stationary source emissions - Sampling"... [Pg.414]

FIG. 25-39 Measurement system schematic for continuous emissions sampling for total gaseous organics. [Pg.1961]

After PCDEs were detected in a fly ash from a municipal waste incinerator in Finland [36], the occurrence of PCDEs in combustion wastes has not been studied much. PCDEs could be formed during incomplete combustion by condensation from chlorophenols as has been indicated for PCDDs [54], but de novo synthesis is also possible [55]. The formation of chlorinated compounds is always possible during combustion in the presence of organic material and chloride. The formation of PCDEs de novo in combustion has been described in the literature review of Kurz s thesis [4]. Briefly, diphenyl can be formed from the phenoxy radical and benzene which in turn can be formed from alkene radicals. If the formed molecule does not already contain chlorine, chlorination of diphenyl ether can occur, e.g., in the presence of HCl. It has been suggested, however, that PCDEs, in contrast to PCDDs and PCDFs, are not formed to a great extent de novo on solid surfaces or in the gas phase in thermal processes during metal reclamation processes [56]. When PCDEs were analyzed in emission samples of a metal reclamation plant in Finland, all PCDEs were below 4 ng nr3. [Pg.168]

Net release reduction. Estimates of emissions reduction (tons/year) vary in accuracy. Additional emissions sampling and more detailed engineering analysis would be needed to improve these estimates. Where possible, generation and transfer of releases in other media were included in estimating the net change in release. [Pg.359]

Figure 28-14 Block diagram of a typical ICP atomic emission Sample ... Figure 28-14 Block diagram of a typical ICP atomic emission Sample ...
Morselli L, ZappoU S, Liberti A, et al. 1989. Evaluation and comparison of organic and inorganic compounds between emission and emission samples from municipal solid waste incinerator. [Pg.788]

Nesnow, S., Triplett, L. L., and Slaga, T. J. (1983). Mouse skin tumor initiation-promotion and complete carcinogenesis bioassays Mechanisms and biological activities of emission samples. Environ Health Perspect 47, 255-268. [Pg.188]

Fig. 9 demonstrates that exposure of the graded substrates to NH3 and SO2 causes asymmetric enhancement and quenching, respectively. The spectral changes correspond to a modest color change. Furthermore, the fact that the curves all coalesce at about 600 nm indicates that the EEF is Influenced to a depth of about 0.2 Jim the composition leading to 600-nra PL, CdSo.5800.5, occurs at about this distance from the surface based on AES data. Our expectation was that repetition of this experiment with the more basic amines would affect the EEF to greater depths (coalescence at longer wavelengths for spectra like those in Fig. 9). However, spectral noise from these weakly emissive samples has frustrated our attempts to clearly see this effect thus far. Fig. 9 demonstrates that exposure of the graded substrates to NH3 and SO2 causes asymmetric enhancement and quenching, respectively. The spectral changes correspond to a modest color change. Furthermore, the fact that the curves all coalesce at about 600 nm indicates that the EEF is Influenced to a depth of about 0.2 Jim the composition leading to 600-nra PL, CdSo.5800.5, occurs at about this distance from the surface based on AES data. Our expectation was that repetition of this experiment with the more basic amines would affect the EEF to greater depths (coalescence at longer wavelengths for spectra like those in Fig. 9). However, spectral noise from these weakly emissive samples has frustrated our attempts to clearly see this effect thus far.
Bart et al. (62) have described the enclosure of a Mettler TA-1 thermoanalyzer in a sealed system in order to permit the examination of samples containing alpha and beta/gamma emissions. Samples containing plutonium and uranium may be studied by TG with no radiation hazard to the operator. All balance components could be reached through glove ports. [Pg.134]

Concentrations of the aforementioned species are obtained using the emission sampling system shown in Figure 1. Since emissions vary significantly between startup and normal operation, a wide range of analyzer capability is required. [Pg.329]

Due to the complex composition of ambient particles, the compound-specific analysis of metallic components is a difficult task. As a consequence, most studies of metallic compounds have been performed in emission samples where the compounds are in an enriched state and the composition is generally less complex. Examples for compound specific analysis in source samples include lead compounds in automotive emissions (Habibi 1973), vanadium compounds in fly ashes (Henry and Knapp... [Pg.39]

PMT shot noise induced by dark current, atomizer background emission, sample matrix emission, or scattered radiation source intensity. [Pg.116]

E. Dabek-Zlotorzynska, M. Piechowski, M. McGrath and E.P.C. Lai, Determination of low-molecular-mass carboxylic acids in atmospheric aerosol and vehicle emission samples by capillary electrophoresis, J. Chromatogr. A, 910, 331-345, 2001. [Pg.973]

Reactions of Nltro-PAH - There are several possible sources of nltro-PAH found in primary emission samples. These compounds may be formed during the combustion process, in the tall pipe, during the filter collection procedure, or a combination of any of these processes. [Pg.308]

OOOO s Air emission sampling methods from stationary sources... [Pg.11]


See other pages where Emission sampling is mentioned: [Pg.2956]    [Pg.160]    [Pg.527]    [Pg.412]    [Pg.560]    [Pg.131]    [Pg.133]    [Pg.135]    [Pg.137]    [Pg.201]    [Pg.394]    [Pg.329]    [Pg.542]    [Pg.2956]    [Pg.571]    [Pg.72]    [Pg.51]    [Pg.414]    [Pg.170]    [Pg.212]    [Pg.280]   
See also in sourсe #XX -- [ Pg.263 ]




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