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Mechanical evaluations

In general, more than one of these techniques is necessary to get a complete picture of how the system is operating and to determine what might have led to the loss in performance. [Pg.284]

Perhaps the first line of investigation should be a mechanical evaluation of the system to rule out causes such as instrumentation or valves. Typical investigations include an instrument check they should be tested and calibrated. Filters should be checked for channeling. Valves should be checked to determine if they are functioning properly. Filters and softeners should be checked to determine whether the specific flow rate or flux is within design guidelines. [Pg.284]

Once mechanical issues have either been ruled out or identified as causes for poor performance, the performance of the RO system [Pg.284]


An RTD curve, for instance, can be represented in algebraic form in more than one way and for different purposes. The characteristic bell shape of many RTDs is evident in the real examples of Figure 5.4. Such shapes invite comparison with some well-known statistical distributions and representation of the RTD by their equations. Or a realistic mechanism may be postulated, such as a network of reactor elements and a type of flow pattern, and the parameters of that mechanism evaluated from a measured RTD. [Pg.507]

The principal test to establish the chemical resistance of the polymeric landfill liners to liquid wastes and industrial effluents is the immersion of geomembrane in a sample either of a defined chemical mixture or of a leachate from an existing storage site. This is performed either at various elevated temperatures in order to generate an Arrhenius diagram, or at fixed temperatures of 50 °C and at 20 °C, and is followed by a number of, primarily, mechanical evaluation tests. [Pg.166]

Several techniques arising from cyclic voltammetry help the interested reader to peer into the future. Derivative polarograph (di/dV against Vt) increases the sharpness of detection of dissolved radicals and molecular fragments. Microelectrodes can be used with potential sweep circuitry. The use of varying electrical wave forms (instead of the linear potential variation) offers much to be learned in the future. Automation and the use of pattern recognition in mechanism evaluations... [Pg.708]

The full quantum mechanical evaluation of the reaction cross-section or is described. [Pg.52]

Statistical Mechanical Evaluation Of Surface Area From Physical Adsorption Of Gases. E. L. Fuller and J. B. Condon, Colloids and Surfaces 171 (1989) 37... [Pg.282]

Zimmer, M. (2000). Molecular mechanics evaluation of the proposed mechanisms for the degradation of urea by urease. J. Biomol. Struct. Dyn. 17, 787-797. [Pg.1444]

Mechanism Evaluate Rate law parameters Design PBR CSTR... [Pg.620]

It is fully acknowledged today that the determination of the conformational maps (values of potential energy as a function of and ) for the different amino acid residues of proteins may represent an essential step on the road leading towards the theoretical elucidation and prediction of protein conformations. It is therefore natural that their study should have been at the center of empirical research and was also the first objective of the quantum mechanical evaluations. The evaluations have been carried out extensively, in particular by... [Pg.72]

Recently, a modified small punch testing (MSP) method has been developed for mechanical evaluation of ceramic and ceramic/metal composite materials used in FGMs [5]. In the present study, the MSP method was applied to evaluate TiC-based ceramics, which are employed as ceramic-side materials in a TiC/Ni3Al FGM. Because the TiC/Ni3Al FGMs apparently show different damage behavior at temperatures from 1208 to 1373 K, the fracture strength and deformation of TiC-based ceramics were measured at these two critical temperatures. The differences in the behaviors of different TiC sintered bodies and their... [Pg.445]

The UCR EPA chamber is a new large indoor environmental chamber constructed at the University of California at Riverside (UCR) under United States EPA funding for the purpose of evaluating gas-phase and secondary aerosol mechanisms for ground-level air pollution. The major characteristics of this chamber, the results of its initial characterization for gas-phase mechanism evaluation, and examples of initial gas-phase mechanism evaluation experiments, are described. It is concluded that the chamber has lower or at most comparable background effects than other chambers previously used for mechanism evaluation, and can provide useful mechanism evaluation data at NOx levels as low as 2 ppb. Future research directions to utilize the capabilities of this chamber are discussed. [Pg.28]

Therefore, the radical source and NOx offgasing rates indicated by the characterization data for the first series of experiments for this chamber is probably as low as one can obtain for reactors constructed of FEP Teflon film, which is generally believed to be the most inert material that is practical for use as chamber walls. Although die radical source and NOx offgasing rates for the second series of experiments is higher (see also Figure 3), they are still about an order of magnitude lower than observed for the UCR and UNC chambers previously used for mechanism evaluation. [Pg.36]

Summary of initial chamber and mechanism evaluation experiments. [Pg.38]

Note that the characterization runs were modelled using the default charaeterization parameters used when modelling the mechanism evaluation runs, not with the values that were adjusted to fit the individual experiments. Therefore, the relatively large variability and average model error for the model simulations of A([03]-[N0]) in those experiments provides a measure of the variability of the chamber effects parameters (e.g., HONO offgasing) to which these experiments are sensitive. The relatively low average bias is expeeted because the chamber effects parameter values were derived based on these data. [Pg.38]

Fits of experimental A([03]-[NO]) measurements to SAPRC-99 model calculations for the initial chamber and mechanism evaluation experiments. [Pg.39]

For the single VOC - NOx or VOC - CO - NOx experiments, the model is able to simulate the A([03]-[N0]) to within 25% or better in most cases, which is better than the 30% seen in previous mechanism evaluations with the older chamber data (Carter and Lurmann, 1990, 1991 Gery et al., 1989, Carter, 2000). However, there are indications of non-negligible biases in model simulations of certain classes of experiments. The cleaner conditions and the relatively lower magnitude of the chamber effects may make the nm-to-run scatter in the model performance may be less than in the simulations of the previous data, and this tends to make relatively small biases in the model performance more evident. There are, for example, definite biases in the model to under predict O3 formation and NO oxidation in the surrogate - NOx experiments carried out at lower ROG/NOx ratios. These cases are discussed further elsewhere (Carter, 2004b). [Pg.39]

As indicated on Table 2, the initial evaluation experiments included nms with NOx levels as low as 2-5 ppb, which is considerably lower than in experiments used previously for mechanism evaluation. Most of the experiments used in die previous SAPRC-99 mechanism evaluation had NOx levels greater than 50 ppb, and even die low NOx TVA and CSIRO experiments had NOx levels of —20 ppb or greater, except for a few characterization nms (Carter, 2004a, and references therein). However, there is no indication in any difference in model performance in simulating the results of these very low NOx experiments, compared to those with the higher NOx levels more representative of diose used in the previous evaluation. [Pg.39]

The future research directions for the UCR EPA chamber will of course depend on funding availability and the interests of the funding agencies, but we would expect the research would be designed to take full advantage of its capabilities. In any case, we expect to continue the ozone reactivity and gas-phase mechanism studies that are currently underway, with the mechanism evaluation being focused on aromatics, whose mechanism are the most... [Pg.40]

As discussed in more detail by Cocker (2004), we will also utilize the chamber for well-characterized experiments needed to develop and evaluate models for secondary organic aerosol (SOA) formation. The temperature control capabilities of this chamber permit systematic studies of temperature and humidity effects that are not possible with existing outdoor chambers or with indoor chambers using blacklights (whose intensities are temperature-dependent). The established capability of this chamber for gas phase mechanism evaluation is an important characteristic in this regard, since the model cannot properly simulate SOA formation if it does not also properly simulate the formation of the SOA precursors from the gas-phase reactions. [Pg.41]

A database for mechanism evaluation is therefore not complete without reeommendations for appropriate inputs to auxiliary mechanisms. Such chamber effects models have aheady been developed for the SAPRC chambers as part of the process of evaluating SAPRC-99 and related mechanisms (e.g. Carter, 2000), and these form the basis of the auxiliary mechanisms applied in the present study. [Pg.243]


See other pages where Mechanical evaluations is mentioned: [Pg.247]    [Pg.973]    [Pg.18]    [Pg.19]    [Pg.284]    [Pg.284]    [Pg.271]    [Pg.247]    [Pg.337]    [Pg.2]    [Pg.97]    [Pg.183]    [Pg.450]    [Pg.13]    [Pg.29]    [Pg.32]    [Pg.37]    [Pg.37]    [Pg.40]    [Pg.40]    [Pg.41]    [Pg.232]    [Pg.232]    [Pg.234]    [Pg.234]    [Pg.236]    [Pg.244]   
See also in sourсe #XX -- [ Pg.284 ]

See also in sourсe #XX -- [ Pg.284 ]

See also in sourсe #XX -- [ Pg.333 ]




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