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Measurement of Transport Parameters

The transport parameters at 25 3°C for He, O2, N2 and CO2 were measured using a mass spectrometric technique [32, 33] and barometric techniques on a Balzers QMG 420 quadrupole mass spectrometer (Liechtenstein) MKS Barotron [34], respectively. The upstream pressure was 0.8-0.95 at, and the downstream pressure was about 10-3 mm Hg for spectrometric method, while for barometric technique that pressure was in the range of 0.1-1 mm Hg therefore, the reverse diffusion of penetrating gas was negligible. The permeability coefficients P were estimated using the formula P = Js L/Dp, where Js (cm (STP)/cm 9 s) [Pg.42]


Alger, M.M., andT.J. Stanley, "Measurement of Transport Parameters in Polymer Films Flux Overshoot Produced by a Step Change in Temperature", J Mem Sci 1989, 10., pp 87 - 99. [Pg.223]

Membrane Properties of p-222I. Copolyoxamide p-222I was selected for thorough study on the basis of encouraging results of measurements of transport parameters for this and related polymers. These results, obtained on ultrathin films prepared from trlfluoroacetlc acid solutions, are shown in Table II. [Pg.363]

Measurement of transport parameters The main measurement of interest under this heading is of the excluded/inaccessible pore volume (IPV) of polymer relative to tracer as parameterised by the core permeability. If this quantity is known, then it should be included in the simulation studies since it may have some effect on the relative breakthrough times of polymer and tracer. However, it has been found that the IPV effect is usually dominated by the frontal retardation of the polymer as a result of adsorption/retention, and it is not generally of major importance in the assessment of the outcome of the polymer flood. Other measurements, such as of polymer dispersion coefficient and viscous fingering parameters, are primarily of importance for interpreting detailed core flood experiments since they do not scale in a simple way to the field and cannot therefore be used directly in the polymer field-scale simulations. [Pg.330]

Permeation cells and chemical polarization Measurement of transport parameters and chemical filters... [Pg.413]

The role of radionuclides as tracer of the chemical transport in river is also reinforced by the fact that each of the U-Th-Ra elements has several isotopes of very different half-lives belonging to the U-Th radioactive series. Thus, these series permit comparison of the behavior of isotopes of the same element which are supposed to have the same chemical properties, but very different lifetimes. These comparisons should be very helpful in constraining time scales of transport in rivers. This was illustrated by Porcelli et al. (2001) who compared ( " Th/ U) and ( °Th/ U) ratios in Kalix river waters and estimated a transit time for Th of 15 10 days in this watershed. The development of such studies in the future should lead to an important progress in understanding and quantifying of transport parameters in surface waters. This information could be crucial for a correct use of U-series radioactive disequilibria measured in river waters to establish weathering budgets at the scale of a watershed. [Pg.565]

Simulation and predictive modeling of contaminant transport in the environment are only as good as the data input used in these models. Field methods differ from laboratory methods in that an increase in the scale of measurement relative to most laboratory methods is involved. Determination of transport parameters (i. e., transmission coefficients) must also use actual contaminant chemical species and field solid phase samples if realistic values are to be specified for the transport models. The choice of type of test, e.g., leaching cells and diffusion tests, depends on personal preference and availability of material. No test is significantly better than another. Most of the tests for diffusion evaluation are flawed to a certain extent. [Pg.234]

Phenomena such as nuclide transport by particles or nuclide transport in colloidal form will interfere with a kinetic approach to predicting nuclide migration. The results indicate that the measurement of kinetic parameters may be as important to understanding the migration of a nuclide through a geologic media as the measurement of the equilibrium-sorption value (Kj). [Pg.190]

These examples illustrate that an increasing number of trace gases must be measured simultaneously if even limited subsets of stratospheric photochemistry and transport are to be understood. The combined uncertainties will also become less of a constraint as simultaneous measurements of trace gas abundances can be compared to values derived from other observed abundances and simple photochemical relationships. As important is the improved measurement of photochemical parameters from laboratory studies as well as the search and study of other mechanisms that may be occurring in the stratosphere. Concerted effort in all of these categories is required to avert future failure in predicting shifts in stratospheric photochemistry, like the Antarctic ozone hole. [Pg.166]

Measurements of kinetic parameters of liquid-phase reactions can be performed in apparata without phase transition (rapid-mixing method [66], stopped-flow method [67], etc.) or in apparata with phase transition of the gaseous components (laminar jet absorber [68], stirred cell reactor [69], etc.). In experiments without phase transition, the studied gas is dissolved physically in a liquid and subsequently mixed with the liquid absorbent to be examined, in a way that ensures a perfect mixing. Afterwards, the reaction conversion is determined via the temperature evolution in the reactor (rapid mixing) or with an indicator (stopped flow). The reaction kinetics can then be deduced from the conversion. In experiments with phase transition, additionally, the phase equilibrium and mass transport must be taken into account as the gaseous component must penetrate into the liquid phase before it reacts. In the laminar jet absorber, a liquid jet of a very small diameter passes continuously through a chamber filled with the gas to be examined. In order to determine the reaction rate constant at a certain temperature, the jet length and diameter as well as the amount of gas absorbed per time unit must be known. [Pg.282]

The coupling of the phosphorylation reaction to electron transport has generally been quantitatively evaluated by measurements of two parameters the ATP/ei ratio, and the dependence of the rate of electron transport on concomitant phosphorylation. Both measurements were subjects of major experimental controversies, but can be said to have reached a measure of general consensus in recent years. [Pg.160]

The measurement of transport properties, kinetics parameters, and physical properties is not an easy job. Bard and Faulkner [14] give a description of the experimental techniques that can be used to estimate electrochemical properties. [Pg.418]

Biochemical oxygen demand and chemical oxygen demand are two important water quality parameters in wastewater engineering. The accurate measurement of these parameters is essential in the proper design of wastewater treatment systems and in the study of the transport and fate of eontaminants in the aquatic environment. [Pg.556]

Fig. 1. Microcirculation of a human colon carcinoma grown in the dorsal skin chamber in a severe-combined immunodeficient mouse. (Adapted from Leunig et al., 1992b.) Note that angiogenesis leads to formation of numerous blood vessels. Such a transparent preparation can permit noninvasive, continuous measurement of transport processes in normal and tumor tissues (Jain, 1985b). Parameters we can measure include hemodynamic (e.g., blood flow, vasomotion) metabolic (e.g., pH, p02, Ca2+) transport (e.g., permeability, diffusion, binding), and cell-cell interactions (e.g., adhesion, deformability). Fig. 1. Microcirculation of a human colon carcinoma grown in the dorsal skin chamber in a severe-combined immunodeficient mouse. (Adapted from Leunig et al., 1992b.) Note that angiogenesis leads to formation of numerous blood vessels. Such a transparent preparation can permit noninvasive, continuous measurement of transport processes in normal and tumor tissues (Jain, 1985b). Parameters we can measure include hemodynamic (e.g., blood flow, vasomotion) metabolic (e.g., pH, p02, Ca2+) transport (e.g., permeability, diffusion, binding), and cell-cell interactions (e.g., adhesion, deformability).
Fig. 8. Interstitial velocity profiles. Representative regions in the microcirculation. Circles represent locations of fluorescence photobleaching experiments. The arrows inside the circles represent the direction of the interstitial fluid velocity at these locations. The nearby values show magnitudes of the velocity in fim/s. (a) An area where interstitial flow parallels blood flow in the vessels, (b) Interstitial flow is opposite prevailing blood flow, (c) Fluid is absorbed from the interstitium into a postcapillary venule. (From Chary and Jain, 1989, with permission.) The photobleaching technique has provided the first and to date the only measurements in the literature of interstitial convective velocities. We have now further improved this technique to permit measurements of binding parameters (Kaufman and Jain, 1990, 1991, 1992a, b) and of transport parameters in light-scattering media (Berk et al., 1993). Fig. 8. Interstitial velocity profiles. Representative regions in the microcirculation. Circles represent locations of fluorescence photobleaching experiments. The arrows inside the circles represent the direction of the interstitial fluid velocity at these locations. The nearby values show magnitudes of the velocity in fim/s. (a) An area where interstitial flow parallels blood flow in the vessels, (b) Interstitial flow is opposite prevailing blood flow, (c) Fluid is absorbed from the interstitium into a postcapillary venule. (From Chary and Jain, 1989, with permission.) The photobleaching technique has provided the first and to date the only measurements in the literature of interstitial convective velocities. We have now further improved this technique to permit measurements of binding parameters (Kaufman and Jain, 1990, 1991, 1992a, b) and of transport parameters in light-scattering media (Berk et al., 1993).
Preparation, measurement, transport, and mixing of reactants. These preliminary operations are common to other analytical methods and are a key step in kinetic methods as regards measurement of the parameter by which the process is monitored. [Pg.2410]

P. Fott, G. Petrini Determination of transport parameters of porous catalysts from permeation measurements. Appl. Catal., 2, 367-378 (1982). [Pg.224]

Independent Determination of Diffusion Coefficients. Independent methods for the determination of diffusion coefficients serve as a reference for the determination of transport parameters. Different methods can be applied to determine diffusion coefficients independently from transport experiments, e.g. determination of the lag-time (27), pulsed-field gradient NMR (25), and permeability measurements (P). [Pg.33]

The parameterization of impedance-based models is difficult for operating profiles that have high ampere-hour throughput in short times. Such conditions result in non-steady-state conditions and do not allow precise measurements of impedance parameters. Therefore, Thele et al. extended the ECM presented in Figure 9.19 by means of an electrolyte transport model, which describes the generation and transport of sulfuric acid inside the porous electrodes [47]. They removed the Warburg impedance and expressed the OCV as the difference between the positive and negative standard potentials [18] ... [Pg.273]

Q. Dong, Ph.D. Thesis, Distributed Measurement and Determination of Transport Parameters in PEFCs, The Permsylvania State University, 2005. [Pg.375]

To detect any degradation of the capability for core coohng or any deterioration of components important to safety (e.g. by means of the measurement of operating parameters for heat transport, monitoring for leaks of reactor coolant and the detection of loose parts in the system) ... [Pg.23]


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