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Converted deposition flux

The mass flux ms,Gr is the sum of the reaction product deposited on the liquid film and non-converted material flux, of the dust deposited on the particles coming from separator into granulator and of the attrition mass flux coming from separator into granulator, which leads to the growth of particles. [Pg.476]

Figure 13-5 is the box model of the remote marine sulfur cycle that results from these assumptions. Many different data sets are displayed (and compared) as follows. Each box shows a measured concentration and an estimated residence time for a particular species. Fluxes adjoining a box are calculated from these two pieces of information using the simple formula, S-M/x. The flux of DMS out of the ocean surface and of nss-SOl back to the ocean surface are also quantities estimated from measurements. These are converted from surface to volume fluxes (i.e., from /ig S/(m h) to ng S/(m h)) by assuming the effective scale height of the atmosphere is 2.5 km (which corresponds to a reasonable thickness of the marine planetary boundary layer, within which most precipitation and sulfur cycling should take place). Finally, other data are used to estimate the factors for partitioning oxidized DMS between the MSA and SO2 boxes, for SO2 between dry deposition and oxidation to sulfate, and for nss-SO4 between wet and dry deposition. [Pg.352]

Fig. 13.9. EQCM data obtained during the "break-in" of a poly(vinylferrocene) film (T = 23.7 nmol cm 2). Frames a and b, respectively, correspond to the current- and mass change-potential curves for the first two redox cycles in aqueous 0.1 mol dm-- NaCI04 immediately following deposition from CH.CI ,. In frame a, the current (electron flux) was converted to the equivalent mass flux of counter ions, for subsequent correlation with the total (observed) gravimetric response of frame b. Potential scan rate 5mVs l. The star symbol denotes the first anodic scan responses. (Adapted from Ref. [37] with permission.)... Fig. 13.9. EQCM data obtained during the "break-in" of a poly(vinylferrocene) film (T = 23.7 nmol cm 2). Frames a and b, respectively, correspond to the current- and mass change-potential curves for the first two redox cycles in aqueous 0.1 mol dm-- NaCI04 immediately following deposition from CH.CI ,. In frame a, the current (electron flux) was converted to the equivalent mass flux of counter ions, for subsequent correlation with the total (observed) gravimetric response of frame b. Potential scan rate 5mVs l. The star symbol denotes the first anodic scan responses. (Adapted from Ref. [37] with permission.)...
Depending on a control switch, the 3D emission and dry deposition tendencies can be converted into a surface flux by calculating the total column integral within the IFS. [Pg.117]

DFG MAK 4 mg/m as total dust SAFETY PROFILE The pure unaltered form is considered a nuisance dust. Some deposits contain small amounts of crystalline quartz and are therefore fibrogenic. When diatomaceous earth is calcined (with or without fluxing agents) some silica is converted to cristobalite and is therefore fibrogenic. Tridymite has never been detected in calcined diatomaceous earth. See also other silica entries. [Pg.1226]

Figure 5.3. Forest N cycling and acidification. Atmospheric N inputs and N outputs to drainage waters are shown in italics. Soil processes (left) and plant processes (right) are clustered within ovals. Dashed lines indicate soil-plant exchanges (plant N uptake or organic N return to soil). Solid lines show processes within soils or plants. Dotted lines show fluxes into or out of forests. Values in brackets refer to net consumption [-] or production [+] of 1 mol associated with the transformation of 1 mol N. When forest N cycles are closed (small N inputs and outputs), the sum of consumed and produced by soil and plant processes is zero and no acidity is generated. When 1 mol of organic N is mineralized (1 mol consumed) and subsequently nitrified (2 mol produced), 1 mol remains to acidify soil or drainage water if nitrate is not removed from soil and converted to organic form by plants. Denitrification to any of three gaseous products consumes 1 mol H. Direct inputs of acidity can also result from ammonium and nitrate deposition. Reprinted from Nadelhoffer (2001) with permission from Elsevier... Figure 5.3. Forest N cycling and acidification. Atmospheric N inputs and N outputs to drainage waters are shown in italics. Soil processes (left) and plant processes (right) are clustered within ovals. Dashed lines indicate soil-plant exchanges (plant N uptake or organic N return to soil). Solid lines show processes within soils or plants. Dotted lines show fluxes into or out of forests. Values in brackets refer to net consumption [-] or production [+] of 1 mol associated with the transformation of 1 mol N. When forest N cycles are closed (small N inputs and outputs), the sum of consumed and produced by soil and plant processes is zero and no acidity is generated. When 1 mol of organic N is mineralized (1 mol consumed) and subsequently nitrified (2 mol produced), 1 mol remains to acidify soil or drainage water if nitrate is not removed from soil and converted to organic form by plants. Denitrification to any of three gaseous products consumes 1 mol H. Direct inputs of acidity can also result from ammonium and nitrate deposition. Reprinted from Nadelhoffer (2001) with permission from Elsevier...
Contrary to the air depletion by scavenging, the air was enriched relatively with insoluble N2 and less soluble compounds such as CO2 and H2S. As described later there is a continuous flux of CO2 through the oceans to the sediments converted as carbonate. Due to the low oxygen level, H2S remains in the atmosphere for the first half of the earth s history. Small amounts of SO2 from volcanic exhalations may have been in the air and in seawater after wet deposition. It is likely that... [Pg.60]

As in the previous section, this flux-based rate expression can then be converted into an expression that quantifles the deposition rate (dt/dx) ... [Pg.171]

This profile resembles the exposure profile of the assembly, indicating that the heat flux controls the buildup of the scraped fraction. It is generally assumed that some of the loosely adhering deposits may be converted into the tenacious layer on the surface, but little is known about the processes that might be responsible for such a conversion. [Pg.347]


See other pages where Converted deposition flux is mentioned: [Pg.183]    [Pg.488]    [Pg.343]    [Pg.148]    [Pg.371]    [Pg.575]    [Pg.389]    [Pg.177]    [Pg.599]    [Pg.340]    [Pg.341]    [Pg.118]    [Pg.310]    [Pg.393]    [Pg.3183]    [Pg.4491]    [Pg.130]    [Pg.275]    [Pg.291]    [Pg.475]    [Pg.536]    [Pg.539]    [Pg.542]    [Pg.104]    [Pg.523]    [Pg.262]    [Pg.542]    [Pg.169]    [Pg.8]    [Pg.701]    [Pg.430]    [Pg.26]    [Pg.66]    [Pg.175]    [Pg.755]    [Pg.145]    [Pg.20]    [Pg.21]    [Pg.15]    [Pg.282]    [Pg.370]   
See also in sourсe #XX -- [ Pg.242 ]




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Deposition flux

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