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Atmospheric emissions Balanced" process

Figure 4-13 shows an example from a three-dimensional model simulation of the global atmospheric sulfur balance (Feichter et al, 1996). The model had a grid resolution of about 500 km in the horizontal and on average 1 km in the vertical. The chemical scheme of the model included emissions of dimethyl sulfide (DMS) from the oceans and SO2 from industrial processes and volcanoes. Atmospheric DMS is oxidized by the hydroxyl radical to form SO2, which, in turn, is further oxidized to sulfuric acid and sulfates by reaction with either hydroxyl radical in the gas phase or with hydrogen peroxide or ozone in cloud droplets. Both SO2 and aerosol sulfate are removed from the atmosphere by dry and wet deposition processes. The reasonable agreement between the simulated and observed wet deposition of sulfate indicates that the most important processes affecting the atmospheric sulfur balance have been adequately treated in the model. [Pg.75]

Unlike water and solid waste, no comprehensive study has been published on air pollution from textile operations. Textile mills produce atmospheric emissions from all manner of processes, and these have been identified as the second greatest problem for the textile industry [8], There has been much speculation about air pollutants from textiles but, in general, air emissions data for textile manufacturing operations are not readily available [9-11]. Most published data are mass balance not direct measurements [12, 13], Direct reading tubes and gas chromatog-raphy/mass spectrometry (GC/MS) have been used more recently to get more reliable data [14, 15]. Hopefully, in the future air emissions data will continue to be collected from textile operations, and better definitions of industry norms can be expected. Considerable effort is now underway in that regard [14, 16]. [Pg.253]

Phase II Mass Balance. (/) Determine raw material iaputs. 2) Record water usage. 3) Assess present practice and procedures. (4) Quantify process outputs. (5) Account for emissions to atmosphere, to wastewater, and to off-site disposal. (6) Assemble iaput and output information. (7) Derive a preliminary mass balance. (8) Evaluate and refine the mass balance. [Pg.226]

Input is balanced by output in a steady-state system. The concentration of an element in seawater remains constant if it is added to the sea at the same rate that it is removed from the ocean water by sedimentation. Input into the oceans consists primarily of (1) dissolved and particulate matter carried by streams, (2) volcanic hot spring and basalt material introduced directly, and (3) atmospheric inputs. Often the latter two processes can be neglected in the mass balance. Output is primarily by sedimentation occasionally, emission into the atmosphere may have to be considered. Note that the system considered is a single box model of the sea, that is, an ocean of constant volume, constant temperature and pressure, and uniform composition. [Pg.897]

For the CO2 recovery from fossil based power stations an additional primary energy input is required, producing supplementary CO2 emissions. The overall energy efficiency of the methanol vectors and the CO2 balance of the fossil based recovery process will be compared to the CO2 recovery from the atmosphere and to the conventional crude oil-gasoline system. [Pg.363]

Quantifying outputs. To calculate the second half of the material balance, the outputs from unit operations and the process as a whole need to be quantified. Outputs include primary product, byproducts, wastewater, gaseous wastes (emissions to atmosphere), and liquid and solid wastes that need to be stored and/or sent off-site for disposal and reusable or recyclable wastes. It is important to identify appropriate units of measurement. [Pg.146]

At steady state the emissions of a species into the atmosphere is just balanced by its rate of removal. The global mean abundance (expressed, say, in Tg) divided by the emission rate (Tg yr ) is equal to the global mean lifetime (yr). The inverse of the overall global mean lifetime is the sum of the inverse lifetimes of each of the removal processes. For a substance that is removed from the atmosphere by reaction with OH radicals, photolysis in the stratosphere, uptake by oceans, destruction at the land surface, and precipitation (washout). [Pg.1098]


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