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Nitrogen-water system

Nitrogen - Water System. The interaction parameters for the nitrogen - water system have been evaluated using the data of Wiebe and Gaddy (10), Paratella and Sagramora (Vj ), Rigby and Prausnitz (12)and O Sullivan and Smith (13). As with the two previous systems, only one constant interaction parameter was necessary to correlate the vapor phase composition while the interaction parameter for the aqueous liquid phase increased monotonically with temperature. A comparison of the calculated and experimental vapor phase and aqueous liquid phase compositions is given in Table I. [Pg.398]

TABLE I. Experimental and Calculated Aqueous Liquid and Vapor Phase Compositions for the Nitrogen - Water System. [Pg.400]

FIGURE 4.2 Pressure-temperature diagrams, (a) Methane + water or nitrogen + water system in the hydrate region, (b) Hydrocarbon + water systems with upper quadruple points, (c) Multicomponent natural gas + water systems, (d) Hydrocarbon + water systems with upper quadruple points and inhibitors. [Pg.198]

Figure 5. Gas holdup as a function of radial position for nitrogen-water system. Figure 5. Gas holdup as a function of radial position for nitrogen-water system.
Figure 7. Comparison of radial distribution of gas holdup with and without solids in a nitrogen-water system. Figure 7. Comparison of radial distribution of gas holdup with and without solids in a nitrogen-water system.
Figure 8. Cumulative bubble length distribution as a function of axial position in a nitrogen-water system. Figure 8. Cumulative bubble length distribution as a function of axial position in a nitrogen-water system.
Figure 21 Volumetric mass transfer coefficient, k a, as a function of superficial gas velocity at different pressures in a nitrogen-water system. (From Letzel, 1997.)... Figure 21 Volumetric mass transfer coefficient, k a, as a function of superficial gas velocity at different pressures in a nitrogen-water system. (From Letzel, 1997.)...
Figure 9.15 Flow patterns for the nitrogen/water system observed for the smooth mixer in the microchannel used at the TU/e. The images were recorded at the indicated superficial gas (Ug) and superficial liquid velocities (U ). The channel has a rectangular... Figure 9.15 Flow patterns for the nitrogen/water system observed for the smooth mixer in the microchannel used at the TU/e. The images were recorded at the indicated superficial gas (Ug) and superficial liquid velocities (U ). The channel has a rectangular...
Finally, Table 2 shows enthalpy calculations for the system nitrogen-water at 100 atm. in the range 313.5-584.7°K. [See also Figure (4-13).] The mole fraction of nitrogen in the liquid phase is small throughout, but that in the vapor phase varies from essentially unity at the low-temperature end to zero at the high-temperature end. In the liquid phase, the enthalpy is determined primarily by the temperature, but in the vapor phase it is determined by both temperature and composition. [Pg.93]

GL 27] [R 3] ]P 29] By means of sulfite oxidation, the specific interfacial area of the fluid system nitrogen/water was determined at Weber numbers ranging from lO " to 10 [10]. In this range, the interface increases from 4000 m m to 10 000 m m . The data are - with exceptions - in accordance with optically derived analysis of the interface and predictions from calculations. At stiU larger Weber number up to 10, the specific interfacial area increases up to 17 000 m m, which was determined optically. [Pg.649]

Nitrate Removal for Small Public Water Systems 600375030 Nitrogen in the Subsurface Environment... [Pg.221]

A. Analysis of Wastewater and Natural Waters. The presence of certain anions in wastewater effluents can cause deterioration of natural water systems. Phosphorous and nitrogen can be present in several chemical forms in wastewaters. Phosphorous is usually present as phosphate, polyphosphate and organically-bound phosphorus. The nitrogen compounds of interest in wastewater characterization are ammonia, nitrite, nitrate and organic nitrogen. Analyses are often based on titrimetric, and colorimetric methods (3). These methods are time consuming and subject to a number of interferences. Ion Chromatography can be used to determine low ppm concentrations of these ions in less than thirty minutes with no sample preparation. [Pg.236]

Constant use of this liquid nitrogen delivery system requires control of the environment within the X-ray enclosure to eliminate condensation of water on the phase separator located above the crystal sample. If this water were to reach the sample, the crystal would experience a temporary increase in temperature that can result in loss of crystallinity. Dehumidification of the hutch eliminates this potential problem. Removal of ambient humidity has the added benefit of reducing the formation of ice on all components that use liquid nitrogen, particularly the dewars used to store crystals before and after X-ray analysis. [Pg.180]


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See also in sourсe #XX -- [ Pg.398 , Pg.527 , Pg.528 , Pg.530 ]




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