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Modeling an Extraction Process

Suppose the goal of the process is to produce a wastewater flow which meets the requirement. [Pg.515]

A The output variables should be controlled, this can be achieved by manipulating the input variables Fb,, Fa,oui, FB,outFsteam and F. [Pg.515]

Process Dynamics and Control Modeling for Control and Prediction. Brian Roffel and Ben Betlem. 2006 John Wiley Sons Ltd. [Pg.515]

Q Indicate in which way a single feed-forward control loop could be used usefiil. Mention a disadvantage of this control. [Pg.516]

A Feed-forward extension. One possible extension could be to create a flow ratio controller FrC between Fa and Fa this is a form of feed-forward control, the aniline outlet concentration could in that case reset the ratio. A general disadvantage of feed-forward control is that it is model-based (prone to modeling errors), in this case of ratio control the two models from Fa and Fp to the aniline outlet concentration are similar, which is an advantage. Another disadvantage is that variations in aniline concentration XA,m me not taken care of by the flow-ratio feed-forward controller. [Pg.516]


An experiment with these factors was done for mathematical modeling of an extraction process ... [Pg.321]

Successful approaches to designing an extraction process begin with an appreciation of the fundamentals (basic phase equilibrium and mass-transfer principles) and generally rely on both experimental studies and mathematical models or simulations to define the commercial technology. Small-scale e3q)eriments using representative feed usually are needed to accurately quantify physical properties and phase equilibrium. Additionally, it is common practice in industry to perform... [Pg.1706]

The coupling of supercritical fluid extraction (SEE) with gas chromatography (SEE-GC) provides an excellent example of the application of multidimensional chromatography principles to a sample preparation method. In SEE, the analytical matrix is packed into an extraction vessel and a supercritical fluid, usually carbon dioxide, is passed through it. The analyte matrix may be viewed as the stationary phase, while the supercritical fluid can be viewed as the mobile phase. In order to obtain an effective extraction, the solubility of the analyte in the supercritical fluid mobile phase must be considered, along with its affinity to the matrix stationary phase. The effluent from the extraction is then collected and transferred to a gas chromatograph. In his comprehensive text, Taylor provides an excellent description of the principles and applications of SEE (44), while Pawliszyn presents a description of the supercritical fluid as the mobile phase in his development of a kinetic model for the extraction process (45). [Pg.427]

One possibility for increasing the minimum porosity needed to generate disequilibria involves control of element extraction by solid-state diffusion (diffusion control models). If solid diffusion slows the rate that an incompatible element is transported to the melt-mineral interface, then the element will behave as if it has a higher partition coefficient than its equilibrium partition coefficient. This in turn would allow higher melt porosities to achieve the same amount of disequilibria as in pure equilibrium models. Iwamori (1992, 1993) presented a model of this process applicable to all elements that suggested that diffusion control would be important for all elements having diffusivities less than... [Pg.198]

Concerning the structure of dispersed CLAs, the model originally proposed by Sebba [57] of a spherical oil-core droplet surrounded by a thin aqueous film stabilized by the presence of three surfactant layers is, in our opinion, essentially correct. However, there is still little direct evidence for the microstructure of the surfactant interfaces. From an engineering point of view, however, there is now quantitative data on the stability of CLAs which, together with solute mass transfer kinetics, should enable the successful design and operation of a CLA extraction process. [Pg.672]

Extraction processes that proceed according to the model of ion-pair extraction are described by a formalism different from that presented in section 16.4.2, and are based on partition of single ions and their association in the organic phase [76] (see also section 2.6). The Born equation has been widely used to describe the transfer of an ion of the charge q and radius r from vacuum to the liquid (water) of the dielectric constant e ... [Pg.694]

Adsorption to mineral surfaces such as Fe and Al (hydr)oxides has long been known to be an important process that limits the mobility of heavy metals and metalloid species in aqueous systems (e.g., Stumm 1992). The sorption of ionic species in MSWI bottom ash has been recently studied in detail by Meima Comans (1998, 1999). These authors used a sequence of selective chemical extractions to determine sorbent concentration, namely Fe and Al (hydr)oxides. Their model calculations suggested that Zn(II) and M0O4 sorbed to Fe (hydr)oxides, while Pb(II) and Cu(II) appeared to have a greater affinity for Fe (hydr)oxides. The sorption of Cd(Il) was found to be very weak. The interpretation of... [Pg.615]

Figure 17. An empirical model was developed to describe the extraction process, taking account of the observation that [U02(DBP)2(HDBP)2] was the predominant uranyl species in the organic phase at aqueous phase acidities of less than 2 M, while [U02(N03)2(HDBP)2] predominated at higher acidities. The curves derived from this model, and a revised model which took into account the presence of other organic phase species such as H[U02(N03)3] (HDBP), are shown in Figure 18. The latter model gave a good description of the system in the aqueous phase acidity range 1 -7 M. Figure 17. An empirical model was developed to describe the extraction process, taking account of the observation that [U02(DBP)2(HDBP)2] was the predominant uranyl species in the organic phase at aqueous phase acidities of less than 2 M, while [U02(N03)2(HDBP)2] predominated at higher acidities. The curves derived from this model, and a revised model which took into account the presence of other organic phase species such as H[U02(N03)3] (HDBP), are shown in Figure 18. The latter model gave a good description of the system in the aqueous phase acidity range 1 -7 M.
Supercritical fluid extraction system - Hewlett Packard Model 7680A totally automated system with unlimited-capacity reciprocating pump, specially designed extraction chamber with safety interlocks, a variable restrictor nozzle and analyte collection trap. The operation of the extractor is controlled by a personal computer which is a Microsoft Windows-based system. An animated status screen provides real-time monitoring of the extraction process. Table II gives the SFE conditions for the HP extractor. [Pg.183]


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