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Pilot plants references

Hydrogen permeance of 100 Nm /m h bar at 500°C can be achievable today during tests on the industrial pilot plant (refer to Chap. 10), values up to 24 Nm /m h bar° have been measured at 436°C this value should double by operating at 500°C. [Pg.221]

Review of coal Hquefaction research may be found ia References 1—3. Hereia, those processiag schemes for coal Hquefactioa that, siace the 1970s, have received atteatioa beyoad the laboratory to pilot plants or process development units are presented. [Pg.280]

A reaction was believed to be thermally neutral, as no rise in temperature was observed in the laboratory. No cooling was provided on the pilot plant, and the first batch developed a runaway. Fortunately the relief valve was able to handle it. Subsequent research showed that the reaction developed 2 watts/kg/°C. Laboratory glassware has a heat loss of 3-6 watts/kg/°C, so no rise in temperature occurred. On the 2.5-m3 pilot plant reactor, the heat loss w as only 0.5 watt/kg/°C [21]. Reference 22 lists heat losses and cooling rates for vessels of various sizes. [Pg.382]

Follow the example of Reference [32], using scale-up rules. A pilot plant test run has been conducted using a laboratory equipped test vessel. Design equivalent process results for a 10,000 gallon tank are ... [Pg.319]

It is well known that during liquefaction there is always some amount of material which appears as insoluble, residual solids (65,71). These materials are composed of mixtures of coal-related minerals, unreacted (or partially reacted) macerals and a diverse range of solids that are formed during processing. Practical experience obtained in liquefaction pilot plant operations has frequently shown that these materials are not completely eluted out of reaction vessels. Thus, there is a net accumulation of solids within vessels and fluid transfer lines in the form of agglomerated masses and wall deposits. These materials are often referred to as reactor solids. It is important to understand the phenomena involved in reactor solids retention for several reasons. Firstly, they can be detrimental to the successful operation of a plant because extensive accumulation can lead to reduced conversion, enhanced abrasion rates, poor heat transfer and, in severe cases, reactor plugging. Secondly, some retention of minerals, especially pyrrhotites, may be desirable because of their potential catalytic activity. [Pg.30]

In the following, selected examples taken from the more recent literature of pilot plant and production electroorganic syntheses will be presented. For a modern review the reader is also referred to recent monographs, such as Industrial Electrochemistry by Pletcher and Walsh, 2nd edn. [10] and modern reviews. [Pg.151]

Robinson and Walsh have reviewed earlier cell designs. The performance of a 500 A pilot plant reactor for copper ion removal is described. Simplified expressions were derived for mass transport both in single pass [243] and batch recirculation [244]. For a detailed discussion of the principle and the role of the rotating cylinder electrode reactor in metal ion removal the reader is referred to Refs. [13] and [241] (46 references). [Pg.188]

A model for crystallization point of the urea melt sprayed into the granulator was developed based on acoustic spectra recorded from sensor position A during a trial period of 24 hours. A flow sheet of the liquid urea feed process can be seen in Figure 9.7. Sensor A is mounted onto an orifice plate inserted in the main supply pipeline of liquid urea (see Figures 9.6 and 9.7). The reference values used to calibrate the model are the crystallization temperature (called the jc point ), as determined by the pilot plant laboratory (heat table visual nucleation/crystallization detection). [Pg.287]

Customers names, projects, and compounds must be coded so that only the management knows these details. The laboratory, pilot plant, and industrial-scale plant chemists and engineers know the codes and refer to each project accordingly. [Pg.149]

The use of the MRR procedure in this study was applied to water samples from a combined ozonation-GAC process in which several ozone doses and ozone contact times were evaluated. The goal was to determine the effects of the combined treatments on the micropollutants and mutagenic activity. In this chapter, data from gas chromatographic (GC) analyses are not reported. Compounds identified by GC-mass spectrometry (GC-MS) and their concentration ranges at the different points of the pilot plant have been published in references 9 and 10. Sampling points allowed for the comparison of the various ozone treatments alone or in combination with GAC and the determination of the effects of postdisinfection. [Pg.608]

Recommended reference operating conditions for Cu precipitation in the pilot plant system include a 90Z to 100Z stoichiometry, initial Cu concentrations of 150 to 180 g/L, and crystallization periods of 24 hours. A seed solution will not be necessary. Also, reaction temperature has no effect on Cu removal or efficiency of acid regeneration for solutions containing 100 or 150 g/L Cu. [Pg.315]

The feed-stream is pressurized to the operation pressure by a metering pump, and the air which is used as oxidant in the oxidation reaction, is compressed to the operational pressure in a four-stage compressor. Both streams are mixed in a static mixer inside the reaction chamber as it is shown in Fig. 9.4-10. The reactor has been described in the section 9.4.4.I. A more etal ed description of the pilot plant can be found in reference [7]. [Pg.522]

In this second, completely revised edition, process and plant automation are introduced in a separate section and methods to transfer pilot plant qualifications and process data to production arc presented. The guidelines for process and plant evaluation and qualifications have been updated and enlarged. Trouble shooting is concentrated in a section of its own and literature has been updated with 1(H) new quotations to include references as recent as 2002. and 100 new tables and figures have been added. [Pg.396]

For convenience, pilot plant tests at 0.5 LHSV and 2300 psia hydrogen with ICR 106 catalyst will be referred to as "high severity." Those at 1.5 LHSV and 2300 psia with ICR 106 catalyst will be referred to as "intermediate severity," and those at 1.0 LHSV and 1750 psia with ICR 113 catalyst will be referred to as "moderate severity."... [Pg.84]

The many preexponential factors, activation energies and reaction order parameters required to describe the kinetics of chemical reactors must be determined, usually from laboratory, pilot plant, or plant experimental data. Ideally, the chemist or biologist has made extensive experiments in the laboratory at different temperatures, residence times and reactant concentrations. From these data, parameters can be estimated using a variety of mathematical methods. Some of these methods are quite simple. Others involve elegant statistical methods to attack this nonlinear optimization problem. A discussion of these methods is beyond the scope of this book. The reader is referred to the textbooks previously mentioned. [Pg.19]

Gregory and Root in 1961 (9) prepared what they termed a "statistical analysis" of the literature covering bark utilization and, in addition, reviewed examples of commercial and pilot plant operations. They found 52 references on use of bark in composition boards. The report concludes with sections covering "Limitations and Hurdles in Bark Utilization" and a discussion of "Future Opportunities."... [Pg.253]

Fig. 6.18 XANES spectra of cobalt reference compounds and of a CoPt/ Al203 Fischer-Tropsch catalyst in different stages of its working life. Samples labeled after FTS were taken from a pilot plant operated at commercially relevant conditions (220 °C, 20 bar, relatively high conversion of 50-70%). Although these catalysts were exposed to significant partial pressures of the byproduct water, the XANES indicate further reduction during usage. (Adapted from [55]). Fig. 6.18 XANES spectra of cobalt reference compounds and of a CoPt/ Al203 Fischer-Tropsch catalyst in different stages of its working life. Samples labeled after FTS were taken from a pilot plant operated at commercially relevant conditions (220 °C, 20 bar, relatively high conversion of 50-70%). Although these catalysts were exposed to significant partial pressures of the byproduct water, the XANES indicate further reduction during usage. (Adapted from [55]).
There are many differences between pilot plant and laboratory operation. These can be illustrated by reference to the following operations ... [Pg.169]

Figure 14.1 Pilot plant process for isolation of rye starch. (From reference 2, modified)... Figure 14.1 Pilot plant process for isolation of rye starch. (From reference 2, modified)...

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See also in sourсe #XX -- [ Pg.21 , Pg.23 , Pg.474 ]




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