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Journal ArticleDOI

Mass transfer towards a reactive particle in a fluid flow: Numerical simulations and modeling

TL;DR: In this article, the authors investigate the interplay between convection, diffusion, and reaction by computational fluid dynamics and establish a model for the mass transfer coefficient accounting for diffusion and internal first-order chemical reaction.
About: This article is published in Chemical Engineering Science.The article was published on 2019-05-18 and is currently open access. It has received 10 citations till now. The article focuses on the topics: Mass transfer coefficient & Mass transfer.

Summary (2 min read)

Introduction

  • OATAO is an open access repository that collects the work of Toulouse researchers and makes it freely available over the web where possible.
  • Biomass gasification processes also represent an active engineering field for solid fluid interactions.
  • Investigating mass transfer coefficients between the dispersed solid phase and the continuous fluid phase at the particle scale, referred to as micro scale, where the interplay between the two phases is fully resolved, helps to propose closure laws which can be used to improve the accuracy of large scale models through multi scale analysis.

1.2. Literature overview

  • Many studies have been carried out to analyze and model cou pling phenomena in particulate flow systems.
  • For a solid spherical particle experiencing first order irreversible reaction in a fluid flow, Juncu (2001) and Juncu (2002) investigated the unsteady conjugate mass transfer under creeping flow assumption.
  • Wehinger et al. (2017) also performed numerical simulations for a single catalyst sphere with three pore models with different com plexities: instantaneous diffusion, effectiveness factor approach and three dimensional reaction diffusion where chemical reaction takes place only within a boundary layer at the particle surface.
  • In order to fully understand the interplay between convection, diffusion and chemical reaction the authors have carried out fully coupled direct numerical simulations to validate a model which predicts the evolution of the Sherwood number accounting for all transport phenomena.
  • The prediction of the mass transfer coefficient is validated through numerical simulations over a wide range of dimensionless parameters.

2.1. Internal diffusion and reaction

  • The authors consider a porous catalyst spherical bead of diameter d p 2r p, effective diffusivity D s within the particle, and effective reactivity k s .
  • Please note that dimensional quantities are distin guished from dimensionless quantities by a ‘‘*” superscript.
  • A reac tant is being transferred from the surrounding fluid phase to the solid phase, where it undergoes a first order irreversible reaction.
  • The solution is available in transport phenomena textbooks such as Bird et al. (2015): Cr C C s sinh /rð Þ 2r sinh /=2ð Þ ð2Þ where r r =d p is the dimensionless radial position, C s the surface concentration, and / d p k s D s q is the Thiele modulus.
  • The effectiveness factor g (Eq. (4)) for a catalyst particle is defined as the internal rate of reaction inside the particle, to the rate that would be attained if there were no internal transfer lim itations.

2.2. Particle surface concentration with external diffusion

  • Assuming a purely diffusive regime, mass transfer in the fluid phase is governed by the following equation: @C @t D fr2C ð5Þ.
  • The concentration profile in the fluid phase can be found through integrating Eq. (5), at steady state, with two Dirichlet boundary conditions, C jr r p C s and C jr 1 C 1.
  • The authors aim in this section at finding the particle surface concentration at steady state.
  • The dimensionless numbers governing the problem, in the absence of convection in fluid phase, are the Thiele modulus / and the dif fusion coefficient ratio c D s D f .

2.3. General model including convection effects

  • When the particle is experiencing an external convective stream, no analytical solution can be deduced for the surface con centration due to the inhomogeneity of the velocity and concentra tion fields.
  • Similarly to the diffusion reaction problem presented in the first case, where the Sherwood number was evaluated analyt ically, it will be instead evaluated from one of the correlations established for convective diffusive problems by Feng and Michaelides (2000), Whitaker (1972) and Ranz and Marshall (1952)).
  • In a general case, the molar flux towards the particle surface (Eq. (6)) can be written as: N f Sh D f d p C s C 1 ð10Þ which under steady state conditions is equal to the consumption rate in the particle N f d p 6 gk sC s ð11Þ where g is the effectiveness factor Eq. (4).
  • The internal reaction changes only the concentration gradient inside the particle, and thus, does not change the value of the external Sherwood number.
  • The authors assume that the concentration over the particle surface is equal to its average C s .

3.1. Numerical simulations

  • The authors define the full flow domain as X, the part of X occupied by the solid particle as P and the part of X occupied by the fluid as X n P.
  • The authors compare the unsteady predictions of the model to com puted results through two sets of simulations (each of them at a fixed Reynolds number).
  • The model has shown its ability to predict the characteristic time of the mean concentration evolution and a good agreement has been observed between the model and the numerical simulations, although the authors assumed the mass transfer rate to be constant.
  • Typically, the charac teristic time is less than a second for a gas solid system and around tens of seconds for liquid solid systems.

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Citations
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Journal ArticleDOI
TL;DR: In this paper, a new 0-D model for the steam reforming of methane inside a spherical catalyst particle (Ni/α -Al2O3) placed in a hot methane/steam atmosphere is presented.

17 citations

Journal ArticleDOI
TL;DR: In this article, a model-based framework is proposed to address the effect of model uncertainty on catalyst identification, designing and optimization in the I-S thermochemical process for hydrogen production, where the most endothermic high temperature step is the sulfuric acid decomposition.

16 citations

Book ChapterDOI
01 Jan 2021
TL;DR: The role of zeolites in the treatment of water is discussed in this paper, where some possible mechanisms for zeolite modification and characterization, as well as a proposition for a sustainable process, is given to the possibilities of the regeneration and reuse of zerosite in the process of water purification, while discussing the mechanisms of ion desorption.
Abstract: One of the effective and economically viable methods in wastewater treatment is sorption, if for this sorbent, material of a natural, readily available origin is used, a material which can be effectively regenerated multiple times. Zeolites are natural or synthetic hydrated microporous aluminosilicates whose structure is characterized by the existence of the channel occupied by exchangeable cations and zeolite water. Due to their high cation exchange capacity, low cost, good thermal stability, and selectivity, which is based primarily on the fact that the channel dimensions determine which ions can enter and replace the naturally occurring cations, zeolites play a vital role among the sorbents for the removal of pollutants from the natural sources of water and wastewater. In order to completely understand the role of zeolites in the treatment of water, this paper discusses the structure of zeolites, some possible mechanisms for zeolite modification, the characterization of zeolites, and as a proposition for a sustainable process, consideration is given to the possibilities of the regeneration and reuse of zeolites in the process of water purification, while discussing the mechanisms of ion desorption. In order to address the problem of the resulting liquid waste after zeolite regeneration, the possibilities of using electrolysis with a dimensionally stable anode have been considered. The resorbed heavy metal ions from the zeolite could be concentrated by solvent extraction, and the metal ions would be returned by electrolysis to the production process, where pure cathode metals would be used in industry at the end of the cycle. In this way, the metal ions that pollute water are transformed into useful components that are economically viable. This paper outlines the most important characteristics of zeolites and modification options to make the most efficient use of the available zeolite and the desired result in the application of zeolites, to solve a specific problem of water treatment.

14 citations

Journal ArticleDOI
TL;DR: Results show that in the process of clinoptilolite in adsorption is dominant reaction process, and with respect to comparative analysis of price and performance, NaCl found to be the most suitable clinoptILolite regenerated agent.
Abstract: Current study aimed to investigate modified natural clinoptilolite for removal of calcium and magnesium from the groundwater. Feasibility of clinoptilolite for groundwater hardness removal in production and operation was verified by static adsorption experiment and the experiment of fixed bed and degasification column. Subsequently, the main parameters for groundwater treatment using clinoptilolite were also explored. Results show that in the process of clinoptilolite in adsorption is dominant reaction process. The adsorption equilibrium time was unchanged when the hardness of raw water changes from 450 to 550 mg/L. With respect to comparative analysis of price and performance, NaCl found to be the most suitable clinoptilolite regenerated agent. The adsorption efficiency was high when the residence time was 20-25 min in the pilot experiments. The reaction mechanism was mainly substitution reaction according to ion equilibrium, and the treatment capacity of the degasifier combined with the fixed bed was 20% higher than that of with only fixed bed.

11 citations

Journal ArticleDOI
TL;DR: In this paper, a reactive Sherwood number model for convective mass transfer around reactive particles in a dilute regime is proposed and validated with Particle-Resolved Simulation (PRS).

9 citations

References
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Journal Article
01 Jun 1978
TL;DR: In this paper, the authors evaluated the applicability of the standard κ-ϵ equations and other turbulence models with respect to their applicability in swirling, recirculating flows.
Abstract: The standard κ-ϵ equations and other turbulence models are evaluated with respect to their applicability in swirling, recirculating flows. The turbulence models are formulated on the basis of two separate viewpoints. The first perspective assumes that an isotropic eddy viscosity and the modified Boussinesq hypothesis adequately describe the stress distributions, and that the source of predictive error is a consequence of the modeled terms in the κ-ϵ equations. Both stabilizing and destabilizing Richardson number corrections are incorporated to investigate this line of reasoning. A second viewpoint proposes that the eddy viscosity approach is inherently inadequate and that a redistribution of the stress magnitudes is necessary. Investigation of higher-order closure is pursued on the level of an algebraic stress closure. Various turbulence model predictions are compared with experimental data from a variety of isothermal, confined studies. Supportive swirl comparisons are also performed for a laminar flow case, as well as reacting flow cases. Parallel predictions or contributions from other sources are also consulted where appropriate. Predictive accuracy was found to be a partial function of inlet boundary conditions and numerical diffusion. Despite prediction sensitivity to inlet conditions and numerics, the data comparisons delineate the relative advantages and disadvantages of the various modifications. Possible research avenues in the area of computational modeling of strongly swirling, recirculating flows are reviewed and discussed.

5,396 citations

Journal Article

2,679 citations

Journal ArticleDOI
TL;DR: In this paper, the Nusselt number for a wide range of packing materials and tube arrangements is given for randomly packed beds and compact (void fraction less than 0.65) staggered tube bundles.
Abstract: Previously obtained experimental heat transfer data have been collected and are illustrated along with minor variations of the standard correlations. Analysis of data for heat transfer in randomly packed beds and compact (void fraction less than 0.65) staggered tube bundles indicates that the Nusselt number for a wide range of packing materials and tube arrangements is given by provided NRe ≥ 50. The correlations presented in this paper are not necessarily the most accurate available; however, they have wide application, are easy to use, and are quite satisfactory for most design calculations.

1,048 citations

Journal ArticleDOI
TL;DR: In this article, the published heat transfer data obtained from steady and nonsteady measurements are corrected for the axial fluid thermal dispersion coefficient values proposed by Wakao and Funazkri.

993 citations

Frequently Asked Questions (14)
Q1. What are the contributions in this paper?

In this paper, the mass transfer problem is treated by coupling external convection diffusion in the fluid phase to diffusion reaction in the solid phase through appropriate boundary conditions, namely continuity of concentration and conti fiency of flux at the particle interface. 

The dimensionless numbers governing the problem, in the absence of convection in fluid phase, are the Thiele modulus / and the dif fusion coefficient ratio c D sD f . 

The prediction of this effective Sherwood number in such systems has a key role in terms of modeling while it allows to estimate the equilibrium internal mean concentration of the particle without using the determination of the surface concentration (unknown in such situations). 

the charac teristic time is less than a second for a gas solid system and around tens of seconds for liquid solid systems. 

The flux density within the fluid film surrounding the particle can be written as:N f k f C s C 1 ð6Þ which is equal to the flux density through the solid surface Eq. (3), yielding:k f C s C 1D s C s d p / tanh /=2ð Þ 2ð7Þk f represents the mass transfer coefficient in the fluid phase which can be obtained from the Sherwood number 

The constant k s of a first order irreversible chemical reac tion is also assumed constant due to homogeneous distribution of the specific area within the porous media experiencing the cat alytic reaction. 

The interplay between the different transport phenomena can be quan tified through an effective Sherwoodnumber assuming steady state. 

The authors solved the whole problem in two ways: (i) through boundary fitted numerical simulations of the full set of equations and (ii) through a simple semi analytical approach that couples a correlation for the external transfer to an analytical solution of the internal diffusion reaction equation. 

The external mass transfer coefficient k f 2D f =d p defined in (6) is obtained ana lytically from Fick’s law applied to the steady profile of external dif fusion in an infinite domain, C rð Þ C s C 1 r pr þ C 1. 

The concentration profile in the fluid phase can be found through integrating Eq. (5), at steady state, with two Dirichlet boundary conditions, C jr r p C s and Cjr 1 C 1. 

In a general case, the molar flux towards the particle surface (Eq. (6)) can be written as:N f Sh D f d p C s C 1ð10Þwhich under steady state conditions is equal to the consumption rate in the particleN f d p 6 gk sC s ð11Þwhere g is the effectiveness factor Eq. (4). 

The prediction of the mass transfer coefficient is validated through numerical simulations over a wide range of dimensionless parameters. 

The major result of their study is that their simple model based on decoupled treatment of internal and external mass transfer gives very accurate results. 

The asymptotic limits of the model have been analyzed and are in accordance with general expectations for slow and fast reaction rates.