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Trapped materials

Other Chromates and Dichromates. The wet operations employed in the modem manufacture of the chromates and dichromates are completely enclosed and all stacks and vents equipped with scmbbers and entrainment traps to prevent contamination of the plant and its environment. The continuous process equipment that is used gready faciHtates this task. The trapped material is recycled. [Pg.138]

Given simple centered flow conditions where the driver, target, and momentum trapping materials are the same, the minimum trapping width is given by [20]... [Pg.196]

The second method used to reduce exliaust emissions incorporates postcombustion devices in the form of soot and/or ceramic catalytic converters. Some catalysts currently employ zeolite-based hydrocarbon-trapping materials acting as molecular sieves that can adsorb hydrocarbons at low temperatures and release them at high temperatures, when the catalyst operates with higher efficiency. Advances have been made in soot reduction through adoption of soot filters that chemically convert CO and unburned hydrocarbons into harmless CO, and water vapor, while trapping carbon particles in their ceramic honeycomb walls. Both soot filters and diesel catalysts remove more than 80 percent of carbon particulates from the exliatist, and reduce by more than 90 percent emissions of CO and hydrocarbons. [Pg.335]

In order to ascertain that the NDELA formation does not occur as a result of trapping of the smoke or during the analysis, we added diethanolamine to tobacco prior to extraction with ethyl acetate in the presence of ascorbic acid. The control value for NDELA was 121 ppb and the experiment with 5.5 iqg diethanolamine addition yielded 113 ppb NDELA. For control of the smoke analysis we added 5.5 mg of DELA in the solvent trap and smoked cigarettes known to be free of DELA. Analysis of the trapped material showed no significant quantities of NDELA, so that artifactual formation of this nitrosamine during smoke collection and analysis can be ruled out. [Pg.255]

In this work we present results obtained both with batch and continuous flow operation of the gas-recycle reactor-separator utilizing Ag and Ag-Sm203 electrocatalysts and Sr(lwt%) La203 catalysts, in conjunction with Linde molecular sieve 5A as the trapping material, and discuss the synergy between the catalytic and adsorption units in view of the OCM reaction network. [Pg.388]

Figure 9. A log-log plot of the annual average ( Paxs/ °Thxs) as a function of sediment trap particle composition, and as a function of total mass flux. Note the importance of particle composition on the ( Paxs/ °Thxs) of trapped material, with a high opal fraction leading to higher ratios. Note also the poor relationship between ( Paxs/ °Thxs) and mass flux. This data was compiled by Chase et al. (in press-b) and includes data from that study, as well as from Lao et al. (1993), Scholten et al. (2001), and Yu et al. (2001a). Figure 9. A log-log plot of the annual average ( Paxs/ °Thxs) as a function of sediment trap particle composition, and as a function of total mass flux. Note the importance of particle composition on the ( Paxs/ °Thxs) of trapped material, with a high opal fraction leading to higher ratios. Note also the poor relationship between ( Paxs/ °Thxs) and mass flux. This data was compiled by Chase et al. (in press-b) and includes data from that study, as well as from Lao et al. (1993), Scholten et al. (2001), and Yu et al. (2001a).
NO release and reduction assisted by noble metal. This phase, which we will call the regeneration phase, is necessary to clean-up the catalyst surface before its saturation (the NO,.Trap material has a limited number of adsorption sites). [Pg.223]

One of the most promising processes is the active DeNO based on NO -trap materials. It has been developed for lean-burn gasoline engines. Cerium compounds are thought to intervene in different steps of the whole process (1) NO oxidation, (2) NO storage, (3) Nitrate desorption and NO reduction. Most probably, the main role of OSC materials is to accelerate HC partial oxidation during rich-spikes (giving CO and H2 as NO reducers). However, this beneficial effect of OSC compounds competes with a detrimental reaction,... [Pg.255]

In some cases, the gas can be trapped, such as with sodium hydroxide, and changes in the mass of trapping material used as a measure of the amount of gas. Trapping agents may also trap water which must be accounted for. Other trapping agents and methods are also available. [Pg.181]

Various sample enrichment techniques are used to isolate volatile organic compounds from mammalian secretions and excretions. The dynamic headspace stripping of volatiles from collected material with purified inert gas and trapping of the volatile compounds on a porous polymer as described by Novotny [3], have been adapted by other workers to concentrate volatiles from various mammalian secretions [4-6]. It is risky to use activated charcoal as an adsorbent in the traps that are used in these methods because of the selective adsorption of compounds with different polarities and molecular sizes on different types of activated charcoal. Due to the high catalytic activity of activated charcoal, thermal conversion can occur if thermal desorption is used to recover the trapped material from such a trap. [Pg.246]

The Zn isotope composition of sediment trap material collected over more than one year at the site of the 1991-1992 EUMELI experiment (18° 28 N, 21° 03 W, z = 3851 m)(0° 11.59 N, 110° 31.18 W, z = 3100 m) near the upwelling off the coast of Mauritania, central Atlantic (Marechal et al. 2000), is on average similar to that of clay minerals (0.24 0.14%o), which is consistent with the composition of the settling material. A subtle increase of 8 Zn values of 0.20%o over Spring and Summer in the fractions collected at depths of 1000 and 2500 m suggests, however, that surface productivity preferentially removes the light isotopes from surface water. [Pg.417]

Marechal (1998) reports a relatively large seasonal fluctuation of 0.2%o in sediment trap material at the EUMELI site (see above) at depths of 1000 and 2500 m with maximum depletion of Cu during Spring and Summer. In contrast to Zn, Archer and Vance (2002) found that Cu (and Fe) in Belingwe black shales is signiflcantly lighter with 8 Cu values down to -1.0%o. [Pg.419]

Three purge and trap methods are used to determine 29 halocarbons (Method 601), seven aromatics (Method 602, including four of the halo-carbons), and acrolein and acrylonitrile (Method 603). The three methods are distinctly different in the sorbent trap materials, GC columns, and... [Pg.74]

Occasionally an acid job may leave a quantity of acid trapped in the formation, or chemicals used in i frac or other workover job may be trapped Such trapped materials may break out weeks or even months later and cause temporary treating upsets. [Pg.138]

Zooplankton population samples for isotope analysis were composites of 50-200 individuals. Population samples are less variable in isotope composition than are samples of individuals. Replicate isotope analyses of composite samples of zooplankton or POM collected at different locations within the lake varied by no more than 0.5%. Larger organisms such as molluscs, insects, and fish were analyzed individually. Molluscs were soaked in dilute HCl to remove carbonates and then rinsed copiously with distilled water. Fish muscle was analyzed. Sediment trap material was collected in replicate cylinders (11.4-cm diameter, 76.2-cm length) suspended at 4.5-m depth. All isotope samples were dried at 60 °C before analysis. [Pg.105]

Total-P Flux. Two approaches were combined to calculate removal by deposition. During the stratified period deposition was determined from the mass flux, measured by using sediment traps suspended at eight levels in the water column, and the P concentration in the sediment trap material. Positioning of traps at key depths allowed primary and resuspended flux components to be deconvoluted. [Pg.296]

Deposition during the mixed period (up to day 165) was calculated from a mass balance on water-column Si and the Si P ratio in sediment trap material, because sediment traps overestimate the net particle deposition flux in a mixing water column (19). Our calculations assumed that losses of dissolved reactive Si resulting from diatom uptake that are not accounted for by increases in particulate biogenic Si are caused by Si deposition. The estimate of mixed-period P deposition was conservative because we assumed that nondiatom particulate P was removed at a rate similar to diatom P. We also assumed that loss of P in traps resulting from diagenesis-dissolution was negligible. The use of short collection periods (2-3 weeks) and a poison should minimize loss. [Pg.296]

Resuspension of bottom sediments presents a potential problem for flux estimates. However, our results suggest minimal resuspension during stratification. As a part of a separate study, Hurley (unpublished data) measured pigment fluxes to the sediment surface. Sediment trap material was dominated by chlorophyll a and pheophorbide a (a grazing indicator). Surface sediments, however, were dominated by pheophytin a, a relatively stable chlorophyll degradation product. The lack of any substantial amounts of pheophytin in trap material suggested that if resuspension of particulates from the surface sediment was important, it was probably minimal. [Pg.439]

Particle-bound Hg concentrations of sediment trap material exhibited strong seasonal response and accounted for the differences between the Hg flux and mass and carbon fluxes late in the summer. Particle-bound HgT content in spring and early summer was below 200 ng/g, but during late summer stratification it reached levels between 200 and 400 ng/g. Levels were highest following breakdown of thermal stratification and remained high throughout the fall (>350 ng/g). The elevated HgT levels after overturn most likely represented a shift from dissolved to particle-bound Hg. [Pg.441]

Unfortunately, the latter was unsufficiently controlled so that the technique remained more of an art than a science and about 20 % of the sample were trapped in the column, i.e., the chromatographic recovery was 80 %. In contrast to the elution order, the trapped material had the highest molar mass 29),... [Pg.173]

An inert gas is bubbled through the sample. The volatile hydrocarbons are transferred into the vapor phase and trapped over a sorbent bed containing 2,6-diphenylene oxide polymer (Tenax GC). A methyl silicone (3% OV-1 on Chromosorb-W, 60/80 mesh) packing protects the trapping material from contamination. Other adsorbents such as Carbopack B and Carbosieve S III may also be used. If pentane and other low boiling hydrocarbons need to be detected, the sorbent trap should be filled with activated charcoal, silica gel, and Tenax, respectively, in equal amounts. [Pg.163]


See other pages where Trapped materials is mentioned: [Pg.66]    [Pg.423]    [Pg.84]    [Pg.473]    [Pg.481]    [Pg.481]    [Pg.34]    [Pg.321]    [Pg.256]    [Pg.103]    [Pg.409]    [Pg.54]    [Pg.423]    [Pg.392]    [Pg.77]    [Pg.112]    [Pg.381]    [Pg.66]    [Pg.19]    [Pg.304]    [Pg.310]    [Pg.439]    [Pg.441]    [Pg.977]    [Pg.665]    [Pg.186]    [Pg.318]    [Pg.358]   
See also in sourсe #XX -- [ Pg.381 ]




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