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Modeling of transport phenomena in fixed-bed reactors for the Fischer-Tropsch reaction: a brief literature review

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Veröffentlicht/Copyright: 8. Juli 2016
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Abstract

Currently, few processes can be considered practical alternatives to the use of petroleum for liquid fuel production. Among these alternatives, the Fischer-Tropsch synthesis (FTS) reaction has been successfully applied commercially. Nevertheless, many of the fundamentals of this process are difficult to understand because of its complexity, which depends strongly on the catalyst and the reactor design and operating conditions, as the reaction is seriously affected by mass and heat transport issues. Thus, studying this reaction system with transport phenomena models can help to elucidate the impact of different parameters on the reaction. According to the literature, modeling FTS systems with 1D models provides valuable information for understanding the phenomena that occur during this process. However, 2D models must be used to simulate the reactor to correctly predict the reactor variables, particularly the temperature, which is a critical parameter to achieve a suitable distribution of products during the reaction. Thus, this work provides a general resume of the current findings on the modeling of transport phenomena on a particle/pellet level in a tubular fixed-bed reactor.

1 Introduction

The use of fuels from fossil sources has supported the industrialization of all countries around the world. A recent report by the U.S. Energy Information Administration provided projections of the estimated energy consumption in the United States (EIA 2015). From this report, one can observe the outstanding role of fossil sources even in the 2040s. Figure 1A shows the energy consumption projections for different sectors; the industry and transportation sectors are currently and will continue to be the greatest energy consumers in the near future, with the latter sector exhibiting the highest consumption of energy. In the transportation sector, the main consumers of liquid fuels are combustion engines, which are used to transport passengers and merchandise (e.g. light-duty vehicles, trucks, planes, and trains), with light-duty vehicles the most demanding energy consumers of liquid fuels (Figure 1B). However, fossil sources are nonrenewable, and their use has greatly contributed to severe pollution problems around the world, affecting ecosystems and changing the Earth’s temperature (greenhouse effect). Fossil fuels contribute more than 50% of the global CO2 emissions (Figure 2A). Although the energy supply for human activity contributes a significant portion of these emissions, the transportation sector is also an important contributor, comprising approximately 13% of the global emissions (Figure 2B; Climate Change 2014).

Figure 1: Energy consumption of fossil sources per year by sector (A) and barrels of oil equivalent consumed per day by the transport sector (B).Data taken from EIA (2015).
Figure 1:

Energy consumption of fossil sources per year by sector (A) and barrels of oil equivalent consumed per day by the transport sector (B).

Data taken from EIA (2015).

Figure 2: Global greenhouse gas emissions in the 2010 year (A) and global greenhouse gas emissions by source (B).Note: The fluorinated gases (1%) and waste and wastewater (3%) are not shown in the figure.Based on data from Climate Change 2014: Mitigation of Climate Change, IPCC.
Figure 2:

Global greenhouse gas emissions in the 2010 year (A) and global greenhouse gas emissions by source (B).

Note: The fluorinated gases (1%) and waste and wastewater (3%) are not shown in the figure.

Based on data from Climate Change 2014: Mitigation of Climate Change, IPCC.

Renewable energy sources are expected to continuously grow, reaching 10% of all consumed energy by 2040 (Figure 1A). Thus, the search for renewable sources as substitutions for fossil fuels has led to the development of processes that take advantage of biomass decomposition, which can help to alleviate pollution problems. Among these processes, Fischer-Tropsch synthesis (FTS) is a suitable candidate for liquid fuel production (Rauch and Kiennemann 2013).

The FTS reaction (hydrocarbon production) is an exothermic reaction that occurs on an industrial level at high pressures (1–4 MPa) and moderate temperatures (473–523 K), in which the synthesis gas (CO and H2 in gas phase) reacts on the surface of a porous solid with an active metal along its surface (Fe and Co are used industrially) to promote long-chain hydrocarbon formation. The reaction mainly produces paraffin and olefin hydrocarbons that coexist in gaseous, liquid, and solid phases depending on the size of their molecular chain and the pressure and temperature conditions inside the reactor.

Many efforts have been made to mathematically model this reaction system to understand the physical and chemical phenomena in the reaction, with the objective of maximizing the efficiency of the process. However, modeling the FTS reaction process is difficult because of the existence of the aforementioned three phases and the large number of compounds that are involved in the reaction in addition to the inherent problems that are associated with the operation of the reactor, the hydrodynamic conditions, and the temperature control of the reactor.

The chemistry of this reaction is very complex because of the large number of hydrocarbon compounds that form and other reactions that compete with the FTS reaction [Equations (1) and (2)], such as methane formation [Equation (3)], the Boudouard reaction [Equation (4)] and the water-gas shift (WGS) reaction [Equation (5)], which decrease the availability of reactants for the formation of desired hydrocarbons (>C5+). Moreover, the Boudouard reaction forms carbonaceous structures that foul the catalyst and occasionally decrease the catalyst activity by coke deposition.

(1)nCO+(2n+1)H2CnH(2n+2)+nH2O
(2)nCO+2nH2CnH2n+nH2O
(3)CO+3H2CH4+H2O
(4)2COCO2+C
(5)CO+H2OCO2+H2

The occurrence of parallel reactions illustrates the complications in modeling this reaction system. Thus, studying the reaction system on a catalytic particle level is preferable, which is defined as a microscale level to distinguish between the several scales that are involved in the process [Froment et al. 2011; i.e. catalyst pellets (microscale), catalyst arrays (mesoscale), and reactors (macroscale)]. However, many momentum, heat, and mass transport processes occur simultaneously even at the microscale, which are affected by the kinetics of the process and thermodynamic changes (e.g. chemical equilibrium and solubility). All these phenomena occur within a multiphase and multicomponent system inside pores.

Studies that have modeled FTS at the microscale (single catalyst particles or pellets) have provided important information regarding the effects of heat and mass transfer phenomena on the reaction behavior during FTS. For example, researchers have reported the effect of the shape of the solid catalyst (pellet: Shen et al. 1996a, Wu et al. 2013; spherical: Shen et al. 1996b, Zhan and Davis 2002, Wu et al. 2013; cylindrical: Shen et al. 1996a; eggshell: Wang et al. 2001, Jess and Kern 2012b), the transport phenomena in industrial-size pellets (millimeter: Shen et al. 1996a, Wang et al. 2001; micrometer: Wu et al. 2013, Hallac et al. 2015), mass transfer (internal resistance in nanometer-size pores: Jung et al. 2010), heat transfer (thermal effects inside the particles: Wang et al. 2001, Wu et al. 2013; effects in the liquid wax film that covers the particles: Wang et al. 2001), the associated chemistry (stoichiometry: Leconte et al. 1984; reaction mechanism: Rofer-DePoorter 1981), the kinetic reaction rate (Huff and Satterfield 1984, Yates and Satterfield 1991), the thermodynamic aspects (chemical equilibrium: Zhan and Davis 2002; solubility and reactivity in multiphase and multicomponent systems: Wang et al. 1999, 2001, Zhan and Davis 2002), and the configuration of the reaction system in microchannels (synthesis gas flow and catalyst arrangement: Derevich et al. 2013, Becker et al. 2014, 2016, Kaskes et al. 2016).

The complexity of this process has promoted the diversity of the approaches that are found in the literature, resulting in different proposals for the analysis of the FTS reaction. The search for the fundamentals of the FTS reaction inside the catalyst particle and the evaluation of the impact of different phenomena (momentum, heat, and mass transport) and chemical reaction kinetics (chosen catalyst and the reaction’s dependence on temperature and pressure) can provide a theoretical basis to improve the catalyst and reactor design. Moreover, dividing the problem into limited study systems could lead to useful proposals toward the comprehension of the FTS reaction system. Thus, the available literature on the modeling of transport phenomena during FTS can be grouped into three categories, which are differentiated by the scale of the studied system (Froment et al. 2011). These categories are defined here as follows: (i) microscale (catalyst pellets), which is discussed in Section 4.1; (ii) mesoscale (microchannels), which is discussed in Section 4.2; and (iii) macroscale [tubular fixed-bed reactors (TFBRs)], which is discussed in Section 4.3.

The aim of this work is to provide a general picture of this important and fascinating theme and briefly review some selected studies from the literature that we believe adequately exemplify the state-of-the-art FTS reaction.

2 Mechanisms and reaction rates for the FTS reaction

2.1 Proposed mechanisms for the FTS reaction

Four mechanisms have been postulated to explain hydrocarbon formation during the FTS reaction; nonetheless, great uncertainty remains regarding exactly how the reaction occurs on the catalyst. The mechanisms are based on the proposed monomer for the reaction (e.g. van der Laan and Beenackers 1999, Storsæter et al. 2006, Visconti et al. 2010, van Santen et al. 2013, and references therein). These proposals include the following: (a) a “carbide” mechanism, where CO is dissociated and forms a metal carbide, and posterior hydrogenation results in CHx species, which is proposed as the monomer; (b) an “enol” mechanism, where the adsorbed CO reacts with hydrogen to form oxymethylene (CHOH), which acts as an initiator of chain growth; (c) a “CO insertion” mechanism, where CO is inserted into a metal-methyl or metal-methylene carbon bond, and further hydrogenation creates terminated hydrocarbons; and (d) an “alkenyl” mechanism, where a surface vinyl species reacts with a surface methylene to form an allyl species.

van der Laan and Beenackers (1999) summarized two mechanisms for the formation of linear hydrocarbons as supported by experiments. FTS is a polymerization reaction and is believed to occur under the following steps: (i) reactant adsorption, (ii) chain initiation, (iii) chain growth, (iv) chain termination, (v) product desorption, and (vi) readsorption and further reactions. Different adsorbed species have been proposed to be responsible for chain initiation and growth. Figure 3 depicts the species that have been proposed so far. The reaction forms a complex mixture that mainly comprises linear and branched hydrocarbons and oxygenates (R-CH3 and R-CH=CH2; R-CH2-OH and H2O, where R is a proton or alkyl).

Figure 3: Proposed and observed chemisorbed species during FTS reaction.Adapted from van der Laan and Beenackers (1999).
Figure 3:

Proposed and observed chemisorbed species during FTS reaction.

Adapted from van der Laan and Beenackers (1999).

Once the monomer is formed on the active site, the polymerization reaction ensues, resulting in the formation of long chains of hydrocarbons. The distribution of the products of the polymerization reaction can be calculated with the so-called Anderson-Schulz-Flory (ASF) equation [Equation (6)], which ideally estimates the product distribution when the value of α (chain growth probability) is known.

(6)Wn=n(1-α)2αn-1,  with α=R^pR^p+R^t

As can be expected from Equation (6), the value of α is a function of the catalyst type. This parameter represents the fraction of hydrocarbon chains with n-carbon atoms that grow by reacting with the monomer. The FTS reaction commonly occurs on catalysts that are based on Ru, Fe, or Co as the active metal because these three elements have shown the greatest activity for this reaction. Ru-based catalysts have the highest activity toward the formation of hydrocarbons with high molecular weight; however, their high cost and low availability inhibit their use at an industrial scale (Dry 2002). However, a report regarding hybrid catalysts that use Ru as a promoter has shown interesting properties, such as suitable activity and selectivity for the production of liquid hydrocarbons based on commercial demands (Kibby et al. 2013). Thus, the value of α is large for a highly active catalyst. For example, researchers have reported the values of α for Ru (α=0.85–0.95), Co (α=0.70–0.80), and Fe (α=0.50–0.70), which agree with the well-known activities of each metal for FTS, and have concluded that the chain growth probability decreases with increasing reactor temperature and at higher H2/CO ratios (van der Laan and Beenackers 1999).

On the contrary, deviations in the product distribution as predicted by the ASF equation have been found. Among the main observed deviations is an overproduction of methane compared to the ASF-predicted fraction, whereas the amounts of C2 and C3 are usually smaller than the ASF-predicted fractions (van der Laan and Beenackers 1999, Puskas and Hurlbut 2003). The main causes of this behavior have been attributed to the assumption of a constant polymerization factor in the ASF equation; products can be readsorbed under real conditions, so several values for the polymerization parameter can coexist during the FTS reaction.

Furthermore, some modified ASF equations in the literature minimize the deviations in the predicted fractions of reaction products. For example, two α-ASF distribution [Equation (7)] fundamentally assumes the existence of two superimposed polymerization processes during the reaction. This equation has been useful to describe experimental data for the product distribution.

(7)Wnn=β(1-α)2α(n-1)+(1-β)(1-α)2α(n-1)

A more recent work (Förtsch et al. 2015) proposed a relationship that enhances the prediction of hydrocarbon fraction production. Although these authors’ proposed equation [Equation (8)] does not provide more insight into the understanding of the FTS mechanism, the equation can be useful to describe long-term or transient experimental data.

(8)n¯=1-μ1-α[1-(γ)(α)+(β)(α)2(1-α)(1-β)(1-α)(1-γ)]+μ1-α

where n̅ is defined as the average carbon number. This last equation may be useful to describe the behavior of the FTS reaction under non-steady-state conditions, where the selectivity of the reaction can be increased, as will be discussed in Section 3.

2.2 Kinetic and reaction rates for the FTS reaction

As mentioned above, the product distribution of the FTS reaction highly depends on the catalyst (Ru, Fe, or Co as the active metal) that is used in the reaction. Fe-based catalysts are used in industries for their low cost compared to the other metals and their high selectivity to olefins. Additionally, these catalysts’ high activity to the WGS reaction makes this element ideal when the synthesis gas has a low H2 concentration (van der Laan and Beenackers 1999, Dry 2002). However, Fe-based catalysts are sensitive to the presence of H2O; this compound inhibits the FTS reaction because of its adsorption onto active sites. On the contrary, Co-based catalysts have been reported to have the highest yield and selectivity toward linear paraffin hydrocarbons compared to Fe-based catalysts, exhibit low selectivity to the WGS reaction, and are not inhibited by water that forms as a by-product of the FTS reaction (van der Laan and Beenackers 1999).

According to the literature, most of the published kinetic rate equations are Langmuir-Hinshelwood-type equations. Comparing these equations is difficult because the reaction conditions (catalyst type, reactor feed composition, temperature, pressure, etc.) and the reactor type are usually quite different. Table 1 shows some reaction rates for Fe-based catalysts. The reaction rates of Langmuir-Hinshelwood-type equations involve the partial pressure of water in the denominator because this compound [which forms during the FTS reaction; Equations (1)–(3)] inhibits the reaction on this type of catalyst. In some of the kinetic equations, the partial pressure of water is related to the H2 partial pressure term, which is written as PH2O/PH2 and allows an analysis of the kinetic effects of H2O on the FTS reaction using the equilibrium of the WGS reaction. In contrast, the most predominant term in the Langmuir-Hinshelwood-type equations for Co-based catalysts is carbon monoxide (CO; Table 2) because the H2/CO ratios are higher than those for Fe-based catalysts. These differences in the reaction rate equations in Tables 1 and 2 can be explained by the different proposed reaction mechanisms for the FTS reaction and the variety of studied catalysts. A summary of kinetic parameters for Fe-based catalysts can be consulted in the works of Atwood and Bennett (1979) and Huff and Satterfield (1984). For example, it has been found that the activation energy for the FTS reaction is in the range of 37–103 kJ/mol for Fe-based catalysts and in the range of 37–100 kJ/mol for Co-based catalysts (e.g. Atwood and Bennett 1979, Yates and Satterfield 1991, Jess and Kern 2009, Chabot et al. 2015). On the contrary, the heat of the adsorption/desorption process (equilibrium constants) has been reported with a value of -100 kJ/mol (Atwood and Bennett 1979) and -8 kJ/mol (Huff and Satterfield 1984) for Fe-based catalysts and a value of -68.5 kJ/mol (Jess and Kern 2009) and 20 kJ/mol (Chabot et al. 2015) for Co-based catalysts.

Table 1:

Reaction rate equations for the FTS determined with Fe-based catalysts.

EquationCatalystReaction rateReactorReference
(1.1)Commercial promoted fused FeR^FT=A1PH21+A2PH2OPCOInternally recycle stirred tankAtwood and Bennett 1979
(1.2)Fe (16%)-Mn (84%) oxidesR^FT=A3PH2mPCOnTFBRBub et al. 1980
(1.3)Fused FeR^FT=A4PCOPH22PH2OKa+PCOPH2Continuous flow slurryHuff and Satterfield 1984
(1.4)100Fe/0.3Cu/0.2KR^FT=A5PCOPH2PCO+KbPH2O+KcPCO2R^WGS=A6(PCOPH2O-PCO2PH2/Kd)PCO+KePH2OStirred tank slurryZimmerman and Bukur 1990
(1.5)Fe-basedR^FT=A7PH21+1.6PH2OPCOTFBRJess et al. 1999
(1.6)Precipitated Fe K:Fe weight ratio of 0.005R^FT=A8PH2PCOPCO+KfPH2OR^WGS=A9(PH2OPCO-PCO2PH2Kg)(PCO+KhPH2O)2Continuous flow slurryMazzone and Fernandes 2006
(1.7)Commercial Fe-Cu-K-SiO2R^FT=A10PCOPH21/2PCO+KkPH2O+A11PCO(1-PH2PCO2KlPH2O/PCO)Continuous spinning basketvan der Laan and Beenackers 2000
(1.8)Unsupported Fe-CuR^FT=A12PCO-0.05PH20.6TFBRHallac et al. 2015

The Ai and Ki terms usually follow the Arrhenius and Van’t Hoff equations, respectively: Ai=Ai0exp(-Eai/RT) and Ki=Ki0exp(-ΔHAi/RT).

Table 2:

Reaction rate equations for the FTS determined with Co-based catalysts.

EquationCatalystReaction rateReactorReference
(2.1)Co-basedR^FT=A13PCOaPH2b(1+i=1NKiPCOcPH2d)2Berty (internal recycle)Sarup and Wojciechowski 1989
(2.2)Co/MgO/SiO2R^FT=A14PCOPH2(1+KrPCO)2Continuous flow slurryYates and Satterfield 1991
(2.3)Commercial Co-basedR^FT=A15PCO(1+A16PCO)2TFBRJess and Kern 2009
(2.4)Co/SiO2R^FT=A17PH2PCO(1+A18PH21/2+A19PCO+A20PCOPH21/2)2TFBRWu et al. 2010
(2.5)Co-basedR^FT=A21PCOPH20.5(1+A22PCO+A23PH20.5)2Trickle fixed-bed recycleBrunner et al. 2015
(2.6)Fe-Co-MnR^FT=kPbH2PH2(bCOPCO)0.5[1+2(bCOPCO)0.5+bH2PH2]2Fixed bedTorshizi et al. 2015
(2.7)Co/Al2O3R^FT=KsPCOaPH2b1-mFTPH2OPH2Continuous stirred tankMa et al. 2014
(2.8)Co-MnR^FT=kFTPCOPH221+KtPCOPH22R^WGS=kWGSPf(PCO-PH2PCO2KWGSPH2O)TFBRKeyser et al. 2000

The Ai and Ki terms usually follow the Arrhenius and Van’t Hoff equations, respectively: Ai=Ai0exp(-Eai/RT) and Ki=Ki0exp(-ΔHAi/RT).

Nevertheless, the variety of reaction rate equations allows inferring that these equations have decisive and different effects on predictions of the FTS reaction’s behavior. Moreover, special care should be taken when the reaction rate equation is determined experimentally for the FTS reaction because the catalyst can change the activity and selectivity as a function of time. Usually, the stabilization of the catalytic surface takes some time because of the formation of different chemisorbed species on the active sites and the occurrence of different transport phenomena, which can significantly affect the reaction. These effects can be considered reversible, but some changes at the catalytic sites are irreversible and negatively affect the activity of the catalyst because the activity sites are modified. Thus, the kinetic data from the literature were reported after a “prudent” amount of time had elapsed since the beginning of the reaction. For example, some works (e.g. Pour et al. 2014) reported that a “steady state” in the activity measurements was obtained after 4 h of operation. In other works (e.g. Morales et al. 2006, den Breejen et al. 2011), dozens of hours were required for the catalyst to reach “stationary” activity. In still other works (e.g. Bezemer et al. 2006), catalyst deactivation resulted in changes in the activity measurements; therefore, the “true” activity (in “steady state”) of the catalyst could only be obtained after several days of operation.

Broadly speaking, the deactivation of the catalyst during the FTS reaction can occur through different mechanisms, including poisoning, sintering, the reoxidation of active sites, and coke formation. Usually, the poisoning of catalysts occurs because of the presence of sulfur compounds in the reactor feed. The sintering of catalysts can occur during overheating in the reactor. Meanwhile, the reoxidation of active sites along the catalyst mainly occurs because of the presence of H2O, with Fe-based catalysts being more affected by this type of deactivation than Co-based catalysts. Coke production is strongly affected by the reaction temperature, and its accumulation on catalysts can cause the catalyst to break up (Espinoza et al. 1999). For example, it is reported that there are three causes of deactivation for the Fe-based catalysts in fixed-bed reactors; at the front of the reactor, sulfur poisoning and coke deposition are the two observed factors of the catalyst deactivation, whereas the occurrence of hydrothermal sintering and/or oxidation of the active sites predominates at the end of the reactor; this last factor is promoted by the increasing amount of H2O along the reactor (Dry 1990, Duvenhage and Coville 2006).

On the contrary, studies that discuss the transport phenomena that occur during the FTS reaction coupled with the kinetics of catalyst deactivation are scarce. Representative examples of these works include those of Hallac et al. (2015), who studied the loss in activity by fouling (coke) for an Fe-based catalyst in a TFBR, and Sadeqzadeh et al. (2012), who studied the deactivation of a Co-based catalyst by sintering in a TFBR. Thus, using the correct reaction rate equation is very important to obtain useful data from simulations.

Catalyst deactivation is an important issue in the design of chemical reactors and must be studied in depth because this process is multifactorial (e.g. catalyst composition, operating conditions, reactor type, time on stream, and feed composition), which could lead to misinterpretations of the kinetic data and erroneous reactor designs. Hence, the kinetic data should be carefully analyzed to obtain a true representation of the reaction through the reaction rate equation.

3 Non-steady-state operation in the FTS reaction (pulsed, periodic, or cyclic)

The ASF equation [Equation (6)] demonstrates that selectively producing the desired fraction of hydrocarbons, for example, gasoline (C5–C12) or diesel (C13–C20), is impossible. Thus, from an industrial point of view, using a catalyst with high chain probability (α) is highly recommended to produce long-chain hydrocarbons, which are cracked after their separation to the desired range of products. However, the selectivity of the reaction can be changed to some extent if the reactor is operated under non-steady-state conditions. For example, Peacock-López and Lindenberg (1984) used an α value of 0.95 in their simulations and showed that the implementation of a transient or on/off pulse operation allows the user to tune the range of products during FTS. Fundamentally, their proposal was to begin the FTS reaction with a determined H2/CO ratio at the appropriate pressure and temperature conditions. After a certain amount of time (defined by the desired product distribution and the activity of the catalyst), the supply of one reactant (e.g. CO) is suppressed from the reaction feed, increasing the reactor temperature at that moment. This change in the reaction leads to chain termination (cessation of hydrocarbon growth) and the desorption of the products. Once the product desorption has finished, the cycle is repeated again. In particular, these authors showed that pulse operation could effectively tune the hydrocarbon production in the C5–C20 range, which contrasts to the obtained selectivity under steady-state operation, where the major selectivity was to C20+ products. However, the effect of pulse operation depends on the probability chain growth (and as a consequence of the catalyst) because the yield to C5–C20 decreases at low values of α, at which point light hydrocarbon formation is favored (Peacock-López and Lindenberg 1986), probably because the degree of polymerization in this case is too low. The beneficial effect of non-steady-state operation (periodic change in composition) on the FTS selectivity was demonstrated by Silveston et al. (1986), who used a micropacked-bed reactor. These authors found that using Co and Ru as catalysts improved the selectivity to C7, whereas only methane was favored for Fe catalysts. The latter result reinforces the idea that only catalysts with high values of α could improve the selectivity to C5+ compounds.

Furthermore, Adesina et al. (1995) reviewed periodic FTS operation and concluded that the observed changes in the selectivity were too small to be implemented on a large scale despite the improvement in the selectivity from periodic operation with H2 pulsing. However, these authors proposed using CO pulsing as an alternative to H2 pulsing and using higher-frequency changes (forced cyclical changes) in the reactor feed to increase the yield to the desired compounds.

Recently, Iglesias-González and Schaub (2015) proposed the use of CO2 hydrogenation via the FTS reaction for the production of gaseous hydrocarbons (i.e. methane, ethane, propane, and butane) on an Fe-based catalyst, with potassium added as a promoter (100 g Fe:2 g K) to produce a renewable fuel. These authors proposed the occurrence of the reverse WGS reaction [called the CO2-shift reaction; Equation (5)], in which the hydrogenation of CO to hydrocarbons occurs by the FTS reaction once the CO is attached to the reaction media [Equation (1), with n=1–4]. These authors studied the effects of changes in the gas feed composition, considering operation over short periods when one reactant is lacking, during which the reactor should be kept hot. Their experimental and mathematical modeling study demonstrated that the catalytic surface experienced compositional changes when the gas feed through the reactor (>2 h) consisted of only H2 or CO2, which decreased the activity when the H2/CO2 mixture was fed into the reactor. Nevertheless, these authors observed that changes to the catalytic surface under an H2 atmosphere were reversible, and iron carbides could form again in the presence of a carbon source. However, changes to the catalytic surface under a CO2 atmosphere were irreversible; no explanation was provided for this last case because the characterization of their catalysts was not complete at that time. This study showed that the main limitation during transient operation is the periphery equipment of the reactor and not the reactor’s behavior itself. Additionally, one can model the reaction system using the steady-state rate equation, which simplifies the number and complexity of the equations that have to be solved. However, this reaction system can be described more easily than the FTS reaction, during which heavier hydrocarbon compounds are formed.

4 Steady-state modeling of FTS and considerations from the literature

4.1 Microscale (catalytic particles or pellets)

Studies on the catalytic particle (or pellet) scale have garnered great interest because several physical and chemical phenomena occur during the FTS reaction. In general, the mechanism by which synthesized gas molecules react on the catalytic surface of the particle is as follows: (i) the transport of reactive gas molecules from the bulk gas phase to the external catalyst surface, (ii) the adsorption of reactant molecules onto the active sites, (iii) the reaction of the adsorbed molecules on the catalytic surface, (iv) the desorption of products from the active sites, and (v) the transport of products to the bulk gas phase. Points (i) and (v) represent external mass transport and are generally not considered in modeling because they are not an industrially limiting stage due to the high gas hourly space velocity (GHSV) that is employed in industrial reactors (Shen et al. 1996a). Points (ii) to (iv) are normally involved in the reaction kinetics, the complexity of which is reflected in the variety of equations that are found in the literature, some of which are shown in Section 2.

Before reaction, the molecules should travel through the pores (usually with an intricate morphology); once the molecules reach the catalytic surface, the reaction proceeds by forming hydrocarbon chains of different sizes. Depending on the reaction conditions, the products can condense (capillary condensation) and/or produce liquid waxes that fill the pores of the pellet (Post et al. 1989, Shen et al. 1996a,b, Wang et al. 2001, Jung et al. 2010), as shown in Figure 4. Subsequently, new reactants in the gas phase must first solubilize in the liquid wax. Because of the existence of a concentration gradient, these reactants are then transported by diffusion through the liquid wax (e.g. n-C28H58; Wang et al. 2001) from the outside of the pores to the catalytic surface, where they react to produce hydrocarbon chains.

Figure 4: Illustration of a catalyst particle during the FTS reaction showing the regions where are frequently considered the transport phenomena balances.
Figure 4:

Illustration of a catalyst particle during the FTS reaction showing the regions where are frequently considered the transport phenomena balances.

Furthermore, the diffusivity coefficient is a property that measures the transport ability of a solute within a solvent or dissolution. When the solute and the diffusion media are in the same phase, the diffusivity is known as molecular. Froment et al. (2011) reported that the flux of the ith component in a mixture of N components can be driven by its own concentration gradient and those of all other species in the mixture; thus, the so-called Maxwell-Stefan equation [Equation (9)] can be obtained for ideal gases.

(9)Ni=-k=1N-1CtDikyi+yik=1NNkj=1,2,...,N-1

However, the diffusivity coefficient can be estimated by assuming a mean binary diffusivity of species i through a mixture (Dim); however, individual diffusivity coefficients are needed because of the difficulty in determining the flux from Equation (9). If the gas mixture in the system is considered ideal and the liquid wax that forms during the FTS reaction (where the ith compound must diffuse) is assumed to be a stagnant medium (the flux ratios are zero for k=2, 3, …), the mean binary diffusivity can be determined using Equation (10).

(10)1Dim=11-yik=2,3,NykDik

Equation (10) is useful to estimate the mean diffusivity of a diluted compound through a liquid mixture. It is not easy to estimate the molecular diffusivity of CO or H2 in the operation conditions of the Fischer-Tropsch reaction (mixture of hydrocarbons at high temperature and pressure). Furthermore, the reported values in the literature are scarce and usually are for very specific cases. For that reason, Makrodimitri et al. (2011) made a study using molecular dynamics simulations, where they performed the theoretical determination of the Maxwell-Stefan diffusion (DMS) coefficients of H2 and CO in two pure alkanes (n-C12 and n-C28). This coefficient is a kinetic factor, and according to the Fick’s law, it is related to the Fick diffusion coefficient (DFick) with the relation DABFick=QDABMS, where Q is a thermodynamic factor. They showed that the DMS coefficient has a strong dependence on the molar gas composition (CO or H2) and the type of liquid hydrocarbon considered (see Table 3) as well as the temperature and pressure. It can be seen from Table 3 that Makrodimitri et al.’s predicted values are close to those obtained experimentally, showing that the use of theoretical calculations can be a useful tool for the estimation of diffusivity coefficient in the conditions in where the FTS reaction occurs. Moreover, they found that, in diluted mixtures (molar gas fraction<0.1), the Q factor is close or equal to unity; therefore, the DMS and DFick diffusion coefficients are equal. This result is in agreement with the broad consensus in the literature to consider a diluted H2 (or CO) solution in the estimation of the diffusivity coefficient. In practical circumstances during the FTS reaction, it is expected that low concentrations of CO and H2 exist in the liquid wax, as the solubility of these gases decreases with the temperature and with the number of carbon atoms (molecular weight) of the liquid hydrocarbon mixture (Torres et al. 2013, Trinh et al. 2016).

Table 3:

Diffusivity of H2 and CO in liquid hydrocarbon.

Compound/mediaDAB×108 (m2/s)ConditionsReferenceType
H2/n-dodecane4.16–10.9T=443–567 K; P=1.45–3.45 MPaAkgerman 1984Experimental
H2/wax12.0P=2.1 MPa; T=473–513 KPost et al. 1989Experimental
H2/wax3.69–4.73T=475–504 K; P=1.4 MPaErkey et al. 1990Experimental
H2/wax4.0P=2.4 MPa; T=473–533 KJess and Kern 2009Estimated Wilke-Chang equation
H2/n-dodecane and H2/n-C283.8–4.5 and 3.0–3.6T=473 K; P=10–30 MPa; mole fraction of H2 (0.1–0.3)Makrodimitri et al. 2011Theoretical Maxwell-Stefan
H2/wax4.0T=493.15 K; P=2.0 MPaChabot et al. 2015Estimated empirical correlation
CO/wax1.17T=523–588 K; P=2 MPaAtwood and Bennett 1979Experimental
CO/n-dodecane1.8–4.62T=443–567 K; P=1.45–3.45 MPaAkgerman 1984Experimental
CO/wax1.51–2.17T=475–536 K; P=1.4 MPaErkey et al. 1990Experimental
CO/n-dodecane and CO/n-C281.9–2.5 and 0.91–1.25T=473 K; P=6–30 MPa; mole fraction of CO (0.1–0.4)Makrodimitri et al. 2011Theoretical Maxwell-Stefan

Nevertheless, the Maxwell-Stefan model does not adequately describe systems in which molecules collide frequently (gas phase) with the walls of the porous media. In such cases, the molecular and Knudsen diffusivities have an important effect on the mass transport; consequently, the dusty gas model [DGM; Equation (11)] could be suitable to describe these systems (Froment et al. 2011).

(11)pi=-RgT(Nk,iDK,i+jiyjND,i-yiND,jDD,ij)-(1DK,iBoptμpt)yi

The last term in Equation (11) corresponds to viscous flow, which is normally only considered when (Bopt/μDK,i)>1020 and corresponds to micrometer-size pores. The DGM could be applied to the FTS reaction because the pores of the catalyst particles were not completely filled with the liquid wax that was produced during the reaction. Although this model considers the possible interactions and collisions of molecules with the walls of the porous media (and therefore could accurately predict the gas transport inside the pores), it is not frequently used because of its inherent complexity for multicomponent gas system modeling.

A simplified equation for the description of molecular diffusion can be obtained from Equation (11) by neglecting the viscous flow (such as for nanometer-size pores), considering that reactant A diffuses through the liquid wax B (assuming a binary mixture), and assuming an equimolar counterdiffusion (NB=-NA), which results in Equation (12).

(12)1De,i=1DD,ij+1DK,i

Equation (12) is the sum of the resistances for the transport of gas molecules according to the molecular and Knudsen diffusivities and is known as the Bosanquet equation [Table 4, Equation (4.6)].

Table 4:

Common models used to evaluate the effective diffusivity.

Effects considered for the diffusivity estimationEffective diffusivity for species i (De,i)Reference
Isothermal conditions and porosity and tortuosity of the catalyst pelletDe,i=(εp/τ)Di,wax(4.1),Shen et al. 1996a,b, Jung et al. 2010
where Di,wax is the molecular diffusivity of ith compound in the liquid wax
Nonisothermal conditions and porosity and tortuosityDe,i=(εp/τ)Di,B(4.2),Wang et al. 2001, Wu et al. 2013
where Di,B=dexp(-e/T)

and d and e are constants
(4.3)
Combined diffusivity (De) as a result of molecular (DAB) and Knudsen (DK) diffusivitiesDe=(εp/τ)D(4.4)Hallac et al. 2015
εp=ρpVpore/(1-εb)(4.5)
D-1=DAB-1+DK-1(4.6)
DAB=0.945T(V˜-V˜0)MA0.239MB0.781(σAσB)1.134(4.7)
DK=4850dporeT/MA(4.8)
Liquid wax composition (n carbon atoms)Dn=D0exp(-0.3n)(4.9)Iglesia et al. 1993, Kuipers et al. 1995, Zhan and Davis 2002
Dn=D0n-0.6

where D0 is a constant
(4.10)

The literature does not frequently contain analyses of the prediction capability of different diffusive flux models. Among the few examples, Nanduri and Mills (2015) compared the prediction accuracy of five diffusion models for the FTS reaction with porous particles in an Fe-based catalyst: (i) the diffusion flux equation by Wang et al. (2001) [Table 4, Equation (4.3)], which was also used by Wu et al. (2013); (ii) the Wilke model [Equation (10)], which was also used by Mamonov et al. (2013) and Chabot et al. (2015); (iii) the Wilke-Bosanquet model [Equation (12); see Table 4, Equation (4.6)], which was also used by Hallac et al. (2015); (iv) the Maxwell-Stefan model [Equation (9)]; and (v) the DGM [Equation (11)]. Only the DGM and Wilke-Bosanquet model include both the molecular and Knudsen diffusivities.

The above authors performed numerical simulations with a 1D model to evaluate the ability of the five models to predict the concentration profiles for key compounds inside particles (spherical geometry) during the FTS reaction, assuming isothermal operation (493 K), a pressure system of 2.5 MPa, a molar feed ratio H2/CO=2, and a mean diameter pore of 25 nm. The vapor-liquid equilibrium (VLE) was estimated using the Soave-Redlich-Kwong (SRK) equation. All the models predicted a minimum concentration of CO and H2 at the center of the particle, whereas the H2O profile always presented a maximum at the center. However, the concentration profiles of CO2 were a function of the diffusion flux model that was used. For instance, the CO2 concentration profile exhibited a maximum at the center of the particle for the Wilke, Wilke-Bosanquet, and Maxwell-Stefan models, whereas the CO2 concentration increased to a maximum and then continuously decreased toward the center of the particle when using the Wang model and DGM. The latter CO2 concentration profile can be explained by the occurrence of the reverse WGS reaction [Equation (5)], where the CO2 that is produced is consumed to produce CO, which is used for the polymerization (FTS) reaction. Thus, this work demonstrated that only the DGM and Wang model predicted the WGS occurrence.

Moreover, the authors evaluated the prediction capability of the intraparticle liquid-vapor (L/V) ratios of the five models. Their results showed that the Wang model predicted the highest L/V ratio among the models. This result and the fact that the CO profile from the same model rapidly approached zero inside the particle suggest that important diffusional effects occurred because of the liquid wax that formed, whereas the Wilke-Bosanquet model and DGM exhibited similar trends for the CO concentration. However, the diffusional limitations of the last two models were attributed to Knudsen diffusion inside the particle pores.

The results of Nanduri and Mills (2015) showed the importance of understanding the coupled effect of the Knudsen and molecular diffusivities on a catalytic porous particle and considering the phase of the FTS reaction products because different kinetics can occur during each phase. Thus, from the point of view of mass transport, the pores of the catalytic particles are not completely filled with liquid wax for low degrees of polymerization in the FTS reaction (as with Fe-based catalysts). Thus, the Knudsen diffusivity contributes to the transport of gas compounds through the catalyst’s pores, and this transport is followed by the molecular diffusion of the compounds in the liquid wax. On the contrary, the heavy compounds that form under high degrees of polymerization (as with Co-based catalysts) are found in a liquid state; therefore, the main resistance to the mass transport will be from molecular diffusion.

Thus, the system could be divided into three regions to analyze the mass transport during the FTS reaction on a microscale level: (I) the gas mixture, which has a boundary at the gas-liquid wax interface; (II) the liquid wax between two boundaries, one that is located at the gas mixture-liquid wax interface and the other at the liquid wax-catalytic surface interface; and (III) the liquid wax at the interface with the external catalytic surface of the particle, where the FTS reaction occurs. These three regions are depicted in Figure 4. Region I is characterized by a convective process of reactants from the gas bulk toward the gas-liquid wax interface, where the solubilization of gas molecules occurs in the liquid wax. In region II, the molecules are transported by molecular diffusion in a liquid phase to the catalytic surface if the pores of the particle are totally filled with liquid wax because of differences in the concentrations between the two boundaries. Conversely, if the pores are not totally filled with liquid wax, both molecular and Knudsen diffusion are important for the transport of reactive molecules to the catalyst’s reactive surface. Finally, molecular diffusion through the liquid wax inside the pores and reactions on the catalytic surface occur in region III. The thickness of both the gas film (mass transfer external resistance) and the liquid wax are usually neglected during the analysis of the mass transport process because these values are very small; thus, only the diffusion effects inside the pores are usually considered.

On the contrary, several proposals from the literature evaluate the diffusion coefficients during the FTS reaction. Erkey et al. (1990) showed that the diffusivity of the synthesis gas in the liquid wax that forms during the FTS reaction can be assessed as the diffusion of synthesis gas through a pure hydrocarbon (e.g. n-alkane), with an average number of carbon atoms that is distinctive of the liquid wax. Some studies considered icosane (C20H42) as the representative liquid wax media (Hallac et al. 2015, and references therein). This hydrocarbon compound is typically obtained in FTS when the reaction is performed with Fe-based catalysts. Once the reactants diffuse through the liquid wax and react on the catalytic surface, the gaseous compounds that form are first solubilized in the liquid wax and then travel out of the pores by diffusion. Basically, the reactants diffuse toward the catalytic surface and the products counterdiffuse to the bulk gas phase of the reaction media. This counterdiffusion has not been studied in the literature (at least to our knowledge) possibly because the field flow within nanometer-size pores is quite complex.

Because the reaction system is heterogeneous (fluid phases plus a solid), the estimation of the diffusivity coefficient must consider the properties of the solid, which is known as the effective diffusivity. Several proposals have been presented in the literature, some of which are listed in Table 4.

The path that molecules traverse inside the catalyst pellet increases with the porosity. The trajectory that the molecules follow in their diffusion through the pores is not straight but instead follows a sinuous path. A measure of this sinuosity is the tortuosity, and the estimation of the effective diffusivity must include the difficulty of the transit within the pores of the compounds. For example, the effective diffusivity can be approximated by multiplying the molecular diffusivity by the relationship between the particle porosity (0<εp<1) and the tortuosity (τ>1; Shen et al. 1996a,b, Jung et al. 2010). This relationship implies that the effective diffusivity will be lower when the intricacy of the path increases because the ratio εp/τ will decrease as the tortuosity increases (see Table 4).

The FTS reaction is nonisothermal, so some authors have considered the effect of temperature on the diffusivity coefficient (e.g. Wang et al. 2001, Wu et al. 2013) using an Arrhenius-type model, which means that the process is thermally activated. Another method to estimate the effective diffusivity coefficient considers the composition (number of carbon atoms) of the liquid wax that forms during the FTS reaction. Two such models have been proposed: one by Iglesia et al. (1993), which predicts a strong dependence of the diffusivity with the number of carbon atoms [exponential type, Table 4, Equation (4.9)], and another that correlates the diffusivity with the size of the hydrocarbons using a power law equation [Table 4, Equation (4.10); Zhan and Davis 2002], which is less dependent on the composition of the liquid wax than the exponential model. Additionally, an analysis of these two proposed models shows that the true dependence of the diffusivity coefficient with the number of carbon atoms is less than the predicted value that is obtained with Equation (4.9) (Kuipers et al. 1995).

Furthermore, Hallac et al. (2015) calculated the effective diffusivity using a relationship between the molecular diffusivity (DAB) and the Knudsen diffusivity (DK) with the approximation of Bosanquet [Equation (12)]. These authors found that the Knudsen diffusivity was typically two orders of magnitude larger than the molecular diffusivity for the conditions of their study, so the contribution of DK to the effective diffusivity was negligible. This result agrees with the findings of Brunner et al. (2012), who also found that DK (3×10-6 m/s2) was two orders of magnitude larger than DAB (2×10-8 m/s2). This relationship coincides with models that only consider the molecular diffusivity with the physical argument that reactants must diffuse through pores that are completely filled with liquid wax; thus, the low solubility of the reactants in the liquid wax slows the mass transport process (Zhan and Davis 2002). Therefore, determining the solubility of reactants in the liquid wax (see Figure 4, region II) is essential to construct a phenomenological model that can describe the diffusional effects on the catalytic reaction.

Knowledge of the physical state (gas or liquid) in which the compounds are found inside the reaction medium is fundamental to obtain the best phenomenological description of the reaction system. Depending on the reaction conditions, some of the hydrocarbons that are produced could condensate, whereas the water and incondensable gasses (e.g. H2, CO, and CO2) that form always remain in a gaseous phase. The physical properties of the phases must be estimated to determine the diffusivity and heat transfer coefficients. Therefore, a descriptive model is desirable to evaluate the VLE in a multicomponent mixture because obtaining experimental data directly from the FTS equipment during operation is difficult and expensive. The determination of properties such as the solubility of the reactant compounds presents at least two challenges (Wang et al. 1999): (i) defining the liquid wax is not an easy task because this material is a complex mixture of hydrocarbons and its composition (and therefore its physical characteristics) is a function of the reaction conditions. To overcome this difficulty, the hydrocarbon mixture that comprises the liquid wax must be frequently lumped into one pseudo-component to simplify the analysis (Leibovici 1993, Lox and Froment 1993). (ii) Because of the substantial differences in the molecular properties of light compounds (gas phase) and the compounds that comprise the liquid wax, conventional thermodynamic descriptions such as the cubic equation of state are difficult to apply because their scope is not designed for systems where the gas-liquid mixtures have such asymmetrical properties.

Recently, Haarlemmer and Bensabath (2016) proved that estimating the flash parameters with the SRK and Peng-Robinson (PR) equations was possible. However, these equations have high computational costs; instead, these authors used Antoine’s law for their VLE calculations. Wang et al. (1999) developed a generalized correlation using a cubic equation of state to estimate the VLE (with an emphasis on the solubility) in the FTS reaction. These authors suggested that their correlation could be used for systems with a wide range of solutes, including CO, H2, CO2, CH4, C2H4, and C2H6, and heavy wax solvents in the C20–C61 range. These authors found that their equation provided good correlations for 406 experimental data points of 29 binary systems that were reported in the literature. The fit of the experimental data resulted in an absolute deviation of <6%, which was mentioned to be sufficient to meet the engineering requirements for the Fischer-Tropsch process design (Wang et al. 1999). Additionally, Wang et al. (2001) considered the thermodynamic equilibrium of the FTS reaction compounds that are present in both gas and liquid wax phases in the pores of the catalyst particle. The compounds’ concentrations were estimated using the modified SRK equation of state (MSRK EOS); this equation demonstrated a suitable representation of the diffusional effects for their study on the FTS reaction with data from an industrial Fe-Cu-K catalyst.

On the contrary, Zhan and Davis (2002) analyzed the diffusional limitations during the FTS with data from an Fe-based catalyst and determined the effective diffusivity coefficient by considering an exponential dependence with the amount of carbon atoms [Table 4, Equation (4.9)]. Evaluating this equation for a hydrocarbon with n+1 carbon atoms resulted in Equation (13):

(13)Dn+1=D0exp[-0.3(n+1)]=exp(-0.3)Dn0.74Dn

Equation (13) shows that the diffusivity of heavier hydrocarbons is always lower and can be approximated using a simple relationship between diffusivities: Dn+1/Dn≈0.74. This result agrees with the hydrocarbon chain growth probability that is predicted by the ASF equation because the formation of heavier compounds decreases when the diffusion of the compounds inside the pores decreases. Moreover, these authors concluded that the diffusion of heavy products in the liquid wax is not necessarily more difficult compared to that of light hydrocarbons because the solubility of the former compounds should also be considered. Thus, only a solubilized compound can diffuse inside and outside the catalyst’s pores, and the effect of the solubility prevails over that of all the other processes under the most common operating conditions for the FTS reaction. Consequently, if the solubility of heavier compounds is high enough, their concentration will be homogeneous in the liquid wax, and their diffusional limitations become less important than those of light hydrocarbons (Zhan and Davis 2002).

Because the liquid wax film on the catalyst is considered very thin (see Figure 4, region II), the diffusion of the components through the liquid is neglected. Thus, the presence of diffusional limitations inside the particle (see Figure 4, region III) is commonly determined using the dimensionless Thiele modulus (Φ), which was originally defined for a homogeneous first-order reaction (Thiele 1939) and is expressed in Equation (14):

(14)Φ=LPkADe,A

where Lp is a characteristic length of the reaction system, kA is the kinetic rate constant for a homogeneous first-order reaction, and De,A is the effective diffusivity. Aris (1957) noted that the effectiveness factor for different catalyst geometries can be approximated by a single function of the Thiele modulus if the length parameter Lp in Equation (14) is defined as the ratio between the volume of the pellet (Vp) and its external surface area (Sp). Then, the Thiele modulus is redefined as Equation (15):

(15)Φ=VpSpkADe,A=LPkADe,A

The simplest model from the literature that was designed to study the importance of mass transport restrictions during the FTS reaction analyzes a single catalytic particle or pellet, which allows the study of the different phenomena that occur inside the pores. Thus, a mathematical model for the diffusion of molecules inside pores and the occurrence of reactions on the catalytic surface (see Figure 4, region III) can be expressed in Equations (16) to (18) by considering isothermal and steady-state operating conditions:

(16)De,A1ξqddξ(ξqdcAdξ)=R^A
(17)Boundary condition (B.C.) 1: ξ=0,dcAdξ=0,
(18)B.C. 2: ξ=c,cA=cAs

where q is a geometric factor that is used to adjust Equation (16) to rectangular, cylindrical, or spherical coordinates; ξ is the spatial coordinate; c is the characteristic distance to the external catalyst surface; cA is the mass concentration; cAs is the mass concentration at the catalytic surface; and R^A is the reaction rate. Equation (16) indicates that the mass transport of species A by diffusion is determined by the rate at which this species can be transformed on the catalytic surface. B.C. 1 in Equation (17) establishes that the concentration of species A in the center of the particle is finite. B.C. 2 [Equation (18)] indicates that the concentration of species A on the catalyst’s surface is determined by the affinity of species A and the catalytic sites.

Furthermore, the effectiveness factor (η) should be evaluated to quantify the mass transfer resistance inside the particle (Figure 4, region III). This factor is defined according to Equation (19) as the ratio between the actual or observed reaction rate (R^A) and the rate when mass transfer resistance is absent (R^AO), which is calculated over the average particle volume (V).

(19)η=𝒱R^AdV𝒱R^A0dV

If η tends close to unity in Equation (19), the mass transfer resistance inside the particle is negligible; if the value tends to zero, high resistance to mass transfer is present inside the catalyst particle (intraparticle mass transfer resistance). Additionally, if the Thiele modulus (Φ) in Equation (14) tends to zero, the intraparticle mass transfer resistance is negligible, and the process is governed by the kinetics of the chemical reaction; otherwise (Φ much >0), the process is governed by intraparticle mass transfer.

Table 5 demonstrates the influence of the catalyst particle’s geometry in the solution of Equations (16) to (18) on the concentration profile and the effectiveness factor, where rp is the radius of the cylinder or sphere according to the coordinate system; Φ is the Thiele modulus as defined in Equation (14); I0 and I1 are the modified Bessel functions of zero and first orders, respectively; and ηa is an approximation of the effectiveness factors. The equations were solved by assuming isothermal and isobaric operating conditions and a homogeneous first-order kinetic rate.

Table 5:

Concentration profiles (cA/cAs) and effectiveness factors (η) obtained from the analytical solution of Equations (16) to (19) (Davis and Davis 2003).

qGeometric systemSolution cA/cAsLpηηa
0Rectangular

ξ=z

 ℓc=L
cosh[Φ(1-z/L)]cosh(Φ)(5.1)Ltanh(Φ)Φ(5.2)If Φ>2, then 1Φ(5.5)
1Cylindrical

ξ=r

 ℓc=rp
I0[Φ(r/rp)]I0(Φ)(5.3)rp/22I1(Φ)ΦI0(Φ)(5.4)
2Spherical

ξ=r

 ℓc=rp
(rpr)sinh[Φ(r/rp)]sinh(Φ)(5.6)rp/33Φ[1tanh(Φ)-1Φ](5.7)

Gonzo and Gottifredi (1983) and Wu et al. (2013) reported that the magnitude of internal mass transport limitations in a spherical catalytic particle can be determined using the mathematical inequality |1-η|≤0.05; thus, one can estimate the effectiveness factor in the absence of internal mass transfer resistances. When the value of Φ is >2, the value of η is approximately 0.4, which corresponds to severely restricted internal mass transport. Additionally, if Φ>2, the value of the η factor can be estimated by the above criterion or the approximation of Equation (5.5) in Table 5, indicating severe diffusional resistances. Moreover, the estimated value for the diffusivity is larger for ideal catalytic pores compared to that for a real porous particle because the tortuous nature of the latter pores must be considered.

An example of the effect of intraparticle resistance on the FTS reaction is the work by Post et al. (1989), who conducted an experimental study with both Fe- and Co-based catalysts in a fixed-bed microreactor system. In their study, the catalyst particle size varied between 0.2 and 2.6 mm (with a pore diameter between 10 and 220 nm), and the diffusional limitations were determined using the Thiele modulus [Equation (14)]. The main considerations for their model were the following: spherical particles, H2 as a representative reaction molecule, and a homogeneous pseudo-first-order reaction. Their results demonstrated that the reaction rate was severely limited by the intraparticle diffusion of H2 when the catalyst particle’s diameter was larger than 1 mm. Their analysis suggests that the effective reaction rate decreases significantly when the catalyst pores are filled with high-molecular-weight hydrocarbons that form during the FTS reaction, which agrees with the idea that molecular diffusivity is the main resistance to mass transfer when the pore is completely filled with liquid wax, as discussed above. To simplify the analysis of the FTS reaction, some researchers have considered that all the reaction products are present in a single phase, either vapor or liquid, during the development of their mathematical models (Shen et al. 1996a,b). Although this proposal is useful to analyze problems that consider that reaction products are present in a single phase, this approach is an oversimplification of the problem because it ignores the effect of the VLE in the FTS reaction. Thus, Shen et al. (1996a) analyzed the temperature dependence of η for the FTS reaction using data from an Fe-Cu-K precipitated catalyst. These authors studied the physical state of the reaction mixture in two different situations: one in which the compounds were present only in a gas phase and another in which the compounds were present in gas and liquid phases. Their results showed that the η values in the former case were always higher than those when considering the combination of the two phases, which reinforces the importance of considering the VLE in modeling the system.

On the contrary, Jung et al. (2010) solved the model of Equations (16) to (18) for a single cylindrical pore, only assuming diffusion along the axial coordinate with the parameters c=L and q=0 using a heterogeneous kinetic rate equation [e.g. Table 1; Equation (1.5)], and compared this solution to that from a pseudo-homogeneous first-order kinetic rate. These authors observed that the concentration profile from the pseudo-homogeneous first-order kinetic rate was always higher compared to that from the heterogeneous kinetic equation. This result agrees with those from Shen et al. (1996a) in terms of the error that is introduced by considering only a gas phase as the reaction media and not considering a reaction in a combined gas/liquid phase.

Nevertheless, the two above studies are an approximation because having a simple first-order kinetic reaction or a single heterogeneous kinetic rate in the FTS reaction is not realistic. In fact, both the kinetic rate of the main reaction (FTS reaction) and the kinetic rates of methane formation and the WGS reaction should be considered in the model, mainly when Fe-based catalysts are used to perform the FTS reaction. Shen et al. (1996a) used experimental information from an industrial Fe-Cu-K catalyst to study a combination of the FTS and WGS chemical reactions; their proposal suggested that a “single” reaction occurs during the FTS process. In this case, these authors considered the heat and mass transport resistances in the catalyst particle. The FTS and WGS reactions [Equations (1) and (5)] were summed, which can only be done if the ratio of the reaction rates is known or can be estimated. The resulting chemical equation is expressed in Equation (20):

(20)(1-χ)CO+(1+m2n-χ)H21nCnHm+(1-χ)H2O+χCO2, 1χ0

where χ is the WGS reaction rate (R^WGS) and the FTS reaction rate (R^FT) ratio (χ=R^WGS/R^FT). The parameter χ retrieves the limit cases for both reactions. The above authors proposed the use of representative families of compounds to facilitate the analysis; thus, C1–C6 hydrocarbons were chosen as representatives of the gas phase and C16+ hydrocarbons as representatives of the liquid phase. The authors’ simulations determined that significant mass transfer limitations occurred when a hydrocarbon with high molecular weight was chosen as the representative compound, which decreased the effectiveness factor and thus indicated strong diffusional limitations. For example, an η value of 0.82 was obtained for C2H6, whereas the effectiveness factor dropped to 0.77 when the C7H16 compound was chosen to represent the reaction medium. The authors extrapolated the behavior of η in the reactor and concluded that this factor had an average value of approximately 0.4 along the catalyst bed under optimal conditions during reactor operation because the PH2O/PCO ratio [a term in their WGS kinetic rate equation; e.g. Table 1, Equations (1.6) and (1.7)] increased along the catalyst bed, decreasing the reaction rate as H2O formed and inhibited the reaction. Nevertheless, the disadvantage of this proposal is the lumping of reaction products, which does not allow the different reaction products to be discriminated and therefore prevents the reaction selectivity from being studied.

Jung et al. (2010) simulated a cylindrical pore (average length of 675 mm) that was filled with liquid wax to assess the mass transfer restrictions from the limited dissolution of H2 and CO during FTS. These authors used a kinetic rate equation obtained with an Fe-based commercial catalyst [Table 1, Equation (1.5)]. This study proposed the existence of concentration gradients along the axial direction inside the pore without considering the concentration gradients along radial coordinates because of the insignificant size of the pore diameter (nanometer size) compared to the pore length. The authors found that only 13% of the pore was effectively used for the FTS reaction and attributed this result to the existence of severe diffusional limitations.

This result agrees with the findings of Wang et al. (2001), who simulated the FTS reaction and recorded experimental data from a spherical pellet of an industrial Fe-Cu-K catalyst. These authors introduced the rate equations for the formation of methane, alkanes (CnH2n+2, n≥2), and alkenes (CnH2n, n≥2) and the rate equation for CO2 reactions. Comprehensive kinetic rate equations were used to solve the model [see Table 6, Equations (6.1)–(6.6)] into their modeling. Their proposed model is expressed in Equations (21) to (26).

Table 6:

Reaction rates used for modeling the FTS reaction.

CatalystWGS and chain growthFischer-Tropsch reaction rate
Fe-based catalystWGS
R^CO2=kV(PCOPH2O/PH22-PCOPH20.5/KP)1+KVPCOPH2O/PH20.5(6.1)R^CnH2n+2=k5PH2j=1nαj1+(1+1K2K3K4PH2OPH22+1K3K41PH2+1K4)i=1N(j=1iαj)

For n≥2
(6.3)Wang et al. 2003a
R^CnH2n=k6(1-βn)j=1nαj1+(1+1K2K3K4PH2OPH22+1K3K41PH2+1K4)i=1N(j=1iαj)

For n≥2
(6.4)
R^CH4=k5MPH2α11+(1+1K2K3K4PH2OPH22+1K3K41PH2+1K4)i=1N(j=1iαj)(6.5)
Chain growth
αn=k1PCOk1PCO+k5PH2+k6(1-βn)(6.2)βn=k-6k6PCnH2nαAn-1k1PCOk1PCO+k5PH2+k-6k1PCO+k5PH2+k6i=2N(αAi-2PC(n-i+2)H2(n-i+2))(6.6)
Co-based catalystWGS
Not considered

Chain growth
R^CO=kPCO2/3PH22/3(1+KCOPCO2/3PH21/3)2(6.9)Ermolaev et al. 2015
Cα=11+kαPCO2/3PH22/3(1+Cβ)(6.7)k=aexp[Ea(1T-1T*)](6.10)
kα=bexp[Eb(1T-1T*)](6.8)Cβ=11+kβPH20.5,withkβ=cexp[Ec(1T-1T*)](6.11)
WGS
Not considered

Chain growth
(i) Liquid hydrocarbons:  R^CO=aPH2PCO(1+bPCO)2(6.14)Mamonov et al. 2013
W(Cn)=nαn-1(1-α)2(6.12)(ii) solid hydrocarbons: R^CO=cPH2RT(6.15)
α=1741.93P0.06492T-1.2317SV-0.00819R1-0.05565R20.016(6.13)with zi=zi0exp(-Ei/RT) (z=a, b, or c)(6.16)

Mass transport balance

(21)De,i1r2r(r2cs,ir)=-ρpj=1NRαijR^j,i=1,NPG
(22)B.C. 3: r=0,cs,ir=0
(23)B.C. 4: r=rP, -Decs,ir=km(cs,i-c)

Energy transport balance

(24)keff1r2r(r2Tsr)=-ρpj=1NR(-ΔHj)R^j
(25)B.C. 5: r=0,Tsr=0
(26)B.C. 6: r=rp, -keffTsr=hf(Ts-T)

Equation (21) is the mass transport equation for the species i and considers the diffusion into the particle and the rate of generation/consumption. B.C. 3 [Equation (22)] establishes that the concentration in the center of the pellet is finite. The above authors considered that the thickness of the liquid wax film that covers the catalyst pellet is very small [(lfilm/dp)<<1], so the external mass transfer limitation can be neglected. Consequently, km in Equation (23) is very large because (cs,i-c)≈0, which agrees with reports that external mass resistances under industrial operation can be neglected (Shen et al. 1996a). Thus, rather than consider B.C. 4, the above authors considered that the solubilization of gaseous reactants in the liquid wax is the prevalent effect in the absence of external mass transfer resistances. With this idea, the authors proposed the thermodynamic equilibrium expression yi=(φiL/φiV)xi to estimate the compounds’ composition (cs,i) in the liquid wax. The transport of energy [Equation (24)] in the pellet considers that the entirety of the reaction’s heat is transferred by conduction in the radial coordinates of the particle. B.C. 5 [Equation (25)] establishes that the temperature in the center of the pellet is finite. According to B.C. 6 [Equation (26)], the heat conduction from the particle dissipates at the solid-liquid wax interface by convection with the fluid around the catalyst particle. Thus, Wang et al. (2001) solved the model by considering a millimeter-size particle. These authors found that the effectiveness factor for CO (ηco) ranged from 0.14 to 0.28 for industrial-size pellets with diameters of approximately 2–4 mm, indicating severe diffusional limitations (Figure 5).

Figure 5: Variation of effectiveness factor with pellet size.Reprinted with permission from Wang et al. (2001, p. 4324). © Copyright 2001 American Chemical Society.
Figure 5:

Variation of effectiveness factor with pellet size.

Reprinted with permission from Wang et al. (2001, p. 4324). © Copyright 2001 American Chemical Society.

The authors also found that a catalytic reaction only occurred along 20% of the external section of the pellet (r/rp=0.8–1); thus, the interior of the particle was practically inert during the reaction, which they called “inert core thickness”. Figure 6 demonstrates this result: selectivity toward C5+ hydrocarbon compounds was only favored along the particle’s surface. Thus, the authors referred to this behavior of the catalyst particle as an eggshell-type catalyst, which appears to be a very attractive solution to lessen the intraparticle transport restrictions during the FTS reaction. With the existence of an inert core, the catalyst pellet (or eggshell) would avoid the depletion of CO inside the particle, thus maintaining the molar H2/CO ratio along the inner surface of the pellet according to differences in the obtained ratio from a uniform pellet. Therefore, an eggshell-type pellet could suppress the chain termination reaction in the deep catalytic area of the pellet, leading to the formation of heavier hydrocarbons (see Figure 6).

Figure 6: Effect of inert core radius on C5+ selectivity.Reprinted with permission from Wang et al. (2001, p. 4324). © Copyright 2001 American Chemical Society.
Figure 6:

Effect of inert core radius on C5+ selectivity.

Reprinted with permission from Wang et al. (2001, p. 4324). © Copyright 2001 American Chemical Society.

As would be expected from the above results, the authors also found a negative impact on the selectivity because of strong diffusional limitations. Light paraffinic hydrocarbons formed easily in the inner section of the catalyst pellet, whereas heavier hydrocarbons preferentially formed in the outer region because of the existence of severe intraparticle diffusion limitations. This result is reflected in the selectivity toward the desired (Figure 7A) and undesired (Figure 7B) products as the pellet size increased. Nevertheless, the authors mentioned that the size of the pellet must range from 2 to 4 mm under practical conditions to maintain a low pressure drop and effective heat removal. This last point suggests that a strong compromise must be made to achieve the best conditions between the catalyst’s performance and the pressure drop in the reactor.

Figure 7: Selectivity variations of C2+ and C5+ products with pellet radius (A), and selectivity variations of CO2 and CH4 with pellet radius (B).Reprinted with permission from Wang et al. (2001, p. 4324). © Copyright 2001 American Chemical Society.
Figure 7:

Selectivity variations of C2+ and C5+ products with pellet radius (A), and selectivity variations of CO2 and CH4 with pellet radius (B).

Reprinted with permission from Wang et al. (2001, p. 4324). © Copyright 2001 American Chemical Society.

In terms of the energy balance in the catalyst pellet, the above authors’ simulations determined that the temperature difference between the bulk gas and the outer surface of the catalyst pellet was 2 K, whereas the temperature difference between the outer surface of the pellet and its center was <0.02 K because of the excellent thermal conductivity of the catalyst (Fe-Cu-K). This last point indicates that the thermal resistance inside the catalyst pellet can be neglected and only the external thermal resistance must be considered when analyzing this reaction (Carberry 2001). This concept is relevant because the selectivity toward products is very sensitive to changes in the reaction temperature. An example is illustrated in Figure 8 through two cases, namely, for an Fe-based catalyst (Figure 8A) and for a Co-based catalyst (Figure 8B), where the selectivity of the reaction was estimated as a function of the reactor temperature. Although the selectivity of the reported compounds exhibited minor changes, the selectivity to olefins decreased significantly with only a 20-degree difference in the temperature of the reactor, which reflects the high sensitivity of the FTS reaction to the reaction temperature (van der Laan and Beenackers 1999).

Figure 8: Effect of the reactor temperature on the selectivity to C2–C4, C5–C9, CH4, and olefin/paraffin ratio for Fe-based catalyst (A and B, respectively; filled symbols: H2/CO=2; empty symbols: H2/CO=0.2) and selectivity to C5+, C25+, CH4, and olefin/paraffin ratio for Co-based catalyst (C and D, respectively; H2/CO=2.1).Data taken and adapted from Feyzi and Jafari (2012) for Fe-based catalyst and from Visconti et al. (2010) for Co-based.
Figure 8:

Effect of the reactor temperature on the selectivity to C2–C4, C5–C9, CH4, and olefin/paraffin ratio for Fe-based catalyst (A and B, respectively; filled symbols: H2/CO=2; empty symbols: H2/CO=0.2) and selectivity to C5+, C25+, CH4, and olefin/paraffin ratio for Co-based catalyst (C and D, respectively; H2/CO=2.1).

Data taken and adapted from Feyzi and Jafari (2012) for Fe-based catalyst and from Visconti et al. (2010) for Co-based.

On the contrary, Wu et al. (2013) simulated the FTS reaction using data from a micrometer-size Fe-based catalyst. Their work developed a comprehensive model for the FTS reaction that incorporated a mechanistic kinetic model and the probability of chain growth using a modified ASF distribution with two α values. As an approximation, the consumption of CO was estimated by the sum of both formation rate equations, namely, the equation for hydrocarbons [Equation (1)] and the reverse WGS reaction [Equation (5)]. Their multicomponent diffusion-reaction model analyzed the relationship between diffusion and the reaction and the influence of the reaction’s temperature and pressure and the size of the catalyst particle (micrometers) on the FTS reaction. Their mathematical model basically followed the form of Equations (21) to (26); however, these authors expressed their model in terms of the mole fraction and defined a dimensionless variable for the radial coordinate as r*=r/rp, in which not all of the volume of the particle is used during the reaction (Wang et al. 2001). Additionally, these authors considered that the thermal resistance between the external surface of the catalyst particle and the surrounding film of liquid wax could be neglected in Equation (26) (hf→∞). Additionally, the products were lumped by compound families because the authors considered including the nondominant products of the reaction unnecessary; this consideration simplified the problem and allowed the reaction system to be expressed in a useful form. Thus, the authors took the following compounds as the main representative products: CH4, C3H8, C10H22, C20H42, CO2, and H2O. These representative compounds were used to propose a system of independent reactions that could characterize the FTS reaction system when an Fe-based catalyst was used [Equations (27)–(31)].

(27)CO+3H2CH4+H2O
(28)3CO+7H2C3H8+3H2O
(29)10CO+21H2C10H22+10H2O
(30)20CO+41H2C20H42+20H2O
(31)CO+H2OCO2+H2

The results of Wu et al. (2013) for the concentration gradients for CO, H2, and chosen products showed that the FTS reaction mainly occurred in the outer shell of the catalyst particle, which agrees with the results by Wang et al. (2001). In their simulations, Wu et al. (2013) found that the temperature difference between the center of the catalyst particle and its surface was equal to 0.012 K because of the small particle diameter in their study (dp=115–120 μm). Likewise, the authors analyzed the effect of the temperature on the FTS reaction by changing the temperature of the bulk gas phase (503, 513, and 523 K) and observed that increasing the temperature decreased the production of long-chain hydrocarbons, whereas the selectivity toward methane increased. Their explanation for this trend was that the increase in the bulk gas-phase temperature promoted the WGS reaction, which in turn increased its participation in the consumption of the carbon source (CO) during the formation of heavier hydrocarbons. When the pressure in the reaction system varied (1.5, 2.1, and 3 MPa), no significant effect on the concentration profiles was observed for the reactants or products; the authors mentioned that this result mainly occurred because the pressure only exerts small effects on the diffusivities of the reactants in the liquid wax that is produced. Furthermore, the concentration profiles in the catalyst particles were calculated, which demonstrated that the CH4 and C10H22 concentrations were higher than the C3H8 concentration. The authors mentioned that this result occurred because of the high concentration of H2 that was available for the reaction. However, the behavior that was reported for the concentrations contrasted the expected behavior for these compounds (particularly the C3H8 compound), even when high deviations in the ASF distribution were present (e.g. Puskas and Hurlbut 2003). This result may have been a consequence of the representative compounds that were chosen because the range between the chosen hydrocarbons was very broad. Clearly, adequately estimating the selectivity using lumping methods is very complex.

4.2 Mesoscale: novel approach (microreactors)

Technological advances have led to the development of reaction systems that consist of microchannels to minimize the heat and mass transport resistances in the catalysts. The results obtained to date show that a smaller catalyst particle size implies less intraparticle resistance to mass transfer; therefore, in this condition, the intrinsic reaction rate would be obtained.

Thus, the development of heterogeneous reactors that are able to minimize the internal mass transfer in the catalyst presents an alternative to conventional slurry-phase reactor (SPR) and fixed-bed reactor. For example, Derevich et al. (2013) studied the hydrodynamic behavior during the FTS reaction in a vertical microchannel reactor with cylindrical geometry. In their study, a Co-based catalyst deposited in microparticles (50–300 µm) on the interior surface of the microchannels was used. Similarly to small catalyst particles, the hydrodynamic resistance could negatively affect the reactor operation when the microchannel mean diameter decreased below 0.4 mm. It is also necessary to consider the hydrodynamic effects on the smooth- and rough-walled microchannels for this type of reactor because these effects can be entirely different in both surfaces, and significant errors can be obtained if the ideal smooth-walled model is used for the pressure drop calculation instead of a more realistic model (rough-walled model).

Becker et al. (2014) conducted a simulation study to determine the form of the minimized diffusional restrictions in a microchannel reactor with a rectangular geometry. For this study, they assumed the Co-based catalyst adhered to the inner surface of the microchannels. The intention in this type of reactor is that the diffusional resistance of the reactants and products inside the catalyst layer is the only resistance to mass transport; thus, the porous network is the main variable to be optimized to achieve the maximum productivity for the desired hydrocarbons (C5+). In this regard, their work focused on the design of the catalyst coating rather than optimizing the process conditions. Thus, to study the reduction of diffusional limitations, they introduced the concept of “transport pores” (TP). Figure 9 shows that this type of reactor can be modeled on different scales. The different scales and their corresponding characteristic parameters are as follows:

  1. WM, LM, HM.

  2. Wm, Lm, Hm.

  3. wm, hm.

  4. lcat, lTP.

Figure 9: Representation for the different scale-levels for transport phenomena analysis in a microstructured reactor.(A) Micro-structured reactor, (B) Monolith, (C) One-channel, (D) Catalyst-coated and the gas flow and (E) Gas-wax-catalyst.
Figure 9:

Representation for the different scale-levels for transport phenomena analysis in a microstructured reactor.

(A) Micro-structured reactor, (B) Monolith, (C) One-channel, (D) Catalyst-coated and the gas flow and (E) Gas-wax-catalyst.

The magnitude order of these scales is depicted in Figure 9. Their mathematical model was established on the mesoscale of the reaction system. The transport balance was made on the structured catalyst layer (Figure 9E) instead of the macroscale (the whole reactor; Figure 9A). Becker et al. (2014) considered isothermal operation conditions and neglected the convective mass transport within the channels to simplify the model as much as possible. The concentration of reactants was assumed constant in the gas-liquid interface, meaning that the mass resistance due to the liquid wax film can be neglected (as is the case when the liquid wax film is very thin; otherwise, the external mass transport should be included in the model). They studied the mass transport for the reactive species (CO and H2) and the effect of diffusion on the reaction rate and selectivity in addition to the performance of the catalyst layer with and without TP.

In their model, it is supposed that the synthesis gas (CO and H2) flows inside the microchannels (convective mass flow) and that transversal diffusion occurs toward the catalyst layer (with a micrometer thickness), where the FTS reaction occurs. After the FTS reaction occurs, the compounds that form the liquid wax remain on the catalyst surface, and the reactant gases must first diffuse into the liquid wax before they reach the inner section of the TP to react at the catalytic surface.

Then, to develop the differential equations on the structured catalyst layer, the volume average process (Whitaker 1999, 2006) is applied to the local mass conservation equations for both the liquid wax and the solid catalytic phases. Thus, the volume fractions are defined as εi=Vi/V, where the volume V is defined as V=VTP+Vcat and the subindex i represents either cat (catalyst) or TP (transport pore). The mass balance in the inert TP filled with the liquid wax resulted in Equations (32) to (34):

(32)De,TPd2ci,TPdx2-kmaiεTP(ci,TP-ci,cat)=0
(33)B.C. 7: x=0, ci,TP=ci0,TP=PiHiνL
(34)B.C. 8: x=lTP,ncatJi,cat=0

where De,TP is the effective diffusivity of the ith compound in the TP, calculated with the relation De,TP=Di(εTP/τTP); ncat·Ji,cat is the diffusive mass flux in the normal direction to the catalyst surface; ncat is the unit normal vector, which in this case corresponds to -δx according to Figure 8; and De,cat is the effective diffusivity of the ith compound on the catalyst. B.C. 7 indicates the absence of mass transfer limitations between the gas and liquid phases, and finally, B.C. 8 indicates whether diffusion of the compounds stops at the end of the catalyst layer or in the monolith wall. Additionally, the mass balance inside the catalyst resulted in Equation (35):

(35)(1-εTP)De,catd2ci,catdx2+kmaiεTP(ci,TP-ci,cat)=(1-εTP)R^i

The authors did not provide the boundary conditions that they used for solving the differential equation; thus, we think that the following boundary conditions could apply [Equations (36) and (37)]:

(36)B.C. 9: x=0,   ncatJi,cat=(1-εTP)R^i
(37)B.C. 10: x=lTP,    ncatJi,cat=0

In this case, the unit normal vector for the TP is opposite in direction to the catalyst nTP=-ncat. The mass balance in the catalyst represented in Equation (35) indicates that the mass transport by diffusion and by the concentration gradient at the liquid-solid interface equals the reaction rate occurring on the catalyst. B.C. 9 in Equation (36) indicates that the mass transport of species i by diffusion is determined by the rate (supposing that is the effective rate on the TP volume) at which this species can be transformed on the catalytic surface considering that the TP is sufficiently small (dTPlTP), and B.C. 10 indicates whether diffusion of the compounds stops at the end of the catalyst layer or in the monolith wall.

The models described in Equations (32) to (37) and in Equations (21) to (26) are different because they are estimated at different scales in the reaction system. Equations (32) to (37) are at the scale of the catalyst layer (micrometer), whereas Equations (21) to (26) are defined at the catalyst porous particle scale. Furthermore, in Equations (32) to (34), the interfacial mass transfer part that connects the mass balance in the catalyst with the mass balance in the TP comes from the effective mass balance in the system rather than a boundary condition (see Figure 9).

From these results, it can be observed that this configuration of the reaction system enhanced the diffusion of the reaction compounds because the compounds can diffuse easily inside of the catalyst layer (τ→1) due to the regular geometry of the microchannel. The results suggest that the productivity can be high if the fraction of TPs in the reactor is optimized because this arrangement can provide a large catalyst surface area in contact with the reactants, resulting in an enhanced reaction rate (Becker et al. 2014, and references therein).

Although the TP (microchannels) improves the CO and H2 mass transport toward the catalytically active centers, these microchannels presents a practical disadvantage because the intrinsic catalytic activity is only achieved at small catalyst thicknesses (~100 mm). For larger catalyst thicknesses, the selectivity for desired fraction (e.g. C5+) decreases considerably. These adverse effects become more evident with the use of highly active catalysts because the polymerization reaction occurs rapidly, leading to light compounds, which is in agreement with the effect observed with the size of the catalyst pellets discussed above (see Figure 7). Therefore, Becker et al. (2014) suggested that a combination of highly active catalyst with a layer of 100 mm would lead to the best performance of the microstructured reactors. However, the main disadvantage with this type of reactor is the amount of catalyst that can be deposited in the walls of the channels because the amount will always be less than the amount of catalyst used in conventional reactors, which essentially limits the reactor productivity.

Once the behavior of the FTS reaction on the microscale (particle or pellet) and/or mesoscale is known, the next target is designing the reactor at the macroscale to achieve the best performance in productivity and selectivity. Then, simulations performed on the reactor scale can be used to determine the appropriate values of the parameters to enhance the catalyst lifetime, conversion, and selectivity, reducing the amount required for the expensive experimentation.

4.3 Macroscale: modeling of FTS reactors

4.3.1 Description of the common industrial reactors used for the FTS reaction

The challenge in the reactor design for the FTS reaction is its high exothermicity combined with the high temperature sensitivity of the reaction (see Figure 8), because treating large amounts of reactants at this scale produces a large amount of heat, which is hard to remove and therefore makes the temperature control of the reactor difficult. Thus, the reactor design and operating conditions are important decisions to manage this amount of heat and to maximize the heavy hydrocarbon products (>C5+).

In general, there are four types of reactors in the literature in which the FTS process can be performed on the commercial scale: (i) circulating fluidized-bed reactor (CFBR), (ii) fluidized-bed reactor, (iii) TFBR, and (iv) SPR. The fluidized-bed systems are categorized as high-temperature Fischer-Tropsch (HTFT) reactors [573<T (K)<623] (Steynberg et al. 1999, Chabot et al. 2015) and low-temperature Fischer-Tropsch (LTFT) reactors [473<T (K)<523] (Espinoza et al. 1999, Chabot et al. 2015). The LTFT reactor is a three-phase reaction system, i.e. the reaction media consists of synthesis gas and hydrocarbons in the gas phase, liquid wax, and solid catalyst, whereas a notable feature of HTFT reactors is the absence of a liquid phase, operating with a system composed of two phases: the synthesis gas and the produced hydrocarbons in the gas phase and the solid catalyst.

To conduct the FTS reaction on an industrial scale in the presence of a liquid phase at low temperature [473<T (K)<523], only two types of reactors are currently used (Saeidi et al. 2015): the TFBR (also known as a tubular reactor) and the SPR (also known as a slurry bubble column reactor). An industrial example of the application of the SPR is its use in the slurry-phase distillate (SPD) process developed by Sasol, in which the SPR is the heart of the process that converts natural gas into liquid fuels. The advantage of the SPR in comparison to the TFBR is that it allows the online removal and addition of the catalyst. This fact is especially important in the case of Fe-based catalysts, which suffer from a fast deactivation and should be replaced periodically, whereas, in the case of Co-based catalysts, this advantage is less important because Co-based catalysts have a long catalytic life (Jager 1998).

In the SPR, the synthesis gas is distributed from the bottom and rises through the suspension, which is maintained by the flow of the synthesis gas through the reactor content, consisting mainly of liquid wax products and the Fe-based catalyst particles of ~100 μm (Espinoza et al. 1999). Gaseous reactants diffuse from the gas bubbles through the liquid phase with the suspended catalyst, where they react to produce hydrocarbons and water. The heavier hydrocarbons are part of the slurry phase, whereas the lighter gaseous products and water diffuse through the liquid toward the gas bubbles. The main difficulty in the commercial application of SPRs is the separation of the liquid wax products from the catalyst. Among the existing commercial reactors for the FTS reaction, the slurry bubble column has higher potential productivity (≤25,000 bbl/day) compared to the TFBR (≤6000 bbl/day) and has a better CO conversion per path: 55%–65% for the former case and 30%–35% for the latter (Rytter and Holmen 2015). Furthermore, the selectivity to paraffins and olefins (%P/%O) is higher in the case of the TFBR (C5–C18: 53/40 and C13–C18: 65/28) compared to the SPR (C5–C12: 29/64 and C13–C18: 44/50). Additionally, the higher amount of olefins in the SPR is explained as a consequence of the smaller catalyst particles used, which facilitates the olefin compounds leaving the catalyst particle before a further hydrogenation can occur (Jager 1998).

Espinoza et al. (1999) found that it is important to distinguish the differences between the dense phase gas hold-up and the dilute phase gas hold-up for the scale-up of the SPR because the former is not affected by the column geometry, whereas, in the case of small diameter columns, the dilute phase gas hold-up is determined by the column geometry. Thus, for large diameter columns (>1 m), the dilute phase gas hold-up is unexpectedly constant for all fluidized systems, whereas the gas hold-up in the dense phase can vary widely depending on the gas, the particles, and the physical properties of the suspension. In the case of suspensions (or slurries), the prediction of porosity for the dense phase (i.e. gas hold-up) is often unreliable due to the high sensitivity of the liquid to the surface tension, which is sensitive to impurities. The prediction of the characteristics of the suspension and mixing conditions of the gas in a slurry bubble column reactor and the influence of the column diameter are important in the scaling problems. However, obtaining data on the design of this type of reactor is laborious, difficult, and expensive; for this reason, studies on the SPR in the literature are less common than for the TFBR. Moreover, the TFBR has the advantage of being easily scaled up using experimental data obtained with a single tube.

There are several studies using different approaches for the modeling of the TFBR. Here, we describe those that we believe to be representative.

4.3.2 Modeling of the FTS reaction on a TFBR

4.3.2.1 1D TFBR models

There are several studies that model the FTS reaction in the TFBR. Most of these studies use different approaches to explain the phenomena that occur during the chemical reaction and perform the modeling to achieve a description of the operational variables of the reactor. In this regard, the works mentioned herein studied the behavior of the reactor (operating temperature, conversion, yield, and selectivity) while varying the diameter of the catalyst particle (dp), the internal diameter of the reactor tube (DT), the height or length of the reactor (LT), the synthesis gas molar feed ratio (H2/CO), the coolant temperature (usually boiling water: Tcool), the mass flow rate of the reactor feed (F), and the recycle ratio (R).

Atwood and Bennett (1979) published a study on FTS reaction modeling at a time when computation capability was difficult to obtain and great effort was necessary to obtain the numerical results. They conducted an experimental study to measure the distribution of products and the reaction rates for the FTS reaction using both commercial Fe- and Co-based catalysts. Their simulations using a heterogeneous kinetic model considered a plug-flow velocity profile; however, the longitudinal mass and heat dispersions, as well as the radial temperature gradients inside the reactor tube, were not considered to simplify the analysis of their 1D model. Instead, the mass and energy balances were developed in the entire reactor (macroscale balance). The internal mass transfer resistance for the catalyst pellet was evaluated through the effectiveness factor, and the intraparticle temperature gradient was neglected because the heat generation function (β=rate of heat generated by chemical reaction/rate of heat transported by thermal conduction) was considered small. In essence, β is a measure of the nonisothermal effects and was calculated with the approximation β≈(Tcenter-Tsup)/TsupTmax/Tsup (Weisz and Hicks 1962); thus, when β→0, an isothermal condition in the pellet or particle catalyst is reached. From their analysis, the interfacial resistance (gas-particle) was considered through the material and energy balance results in Equations (38) and (39).

(38)kmaν(cAs-cAb)=-R^i
(39)hfaν(Tsup-Tb)(-ΔHi)R^i

These equations are driving linear force-type relationships that simplify the analysis by assuming that all the catalyst particles are subjected to the same concentration and temperature throughout the external surface. In the simulations, they used a H2/CO=2 and a reactor operating pressure of 2 MPa to study the behavior of the FTS reaction at different temperatures of synthesis gas (523, 553, and 583 K). Temperatures above 583 K created an unstable region in the reactor. They analyzed the effect of the particle diameter (dp: 2, 4, and 6 mm), flow rate (Rep: 25, 50, 75, and 100), tube diameter (DT: 20, 40, and 60 mm), and tube length (LT: 1.65–10 m) on the effective heat exchange area of the reactor (the sum of the area of all tubes in the reactor) and found that this area was minor with an increase in LT because the heat exchange was increased with the enlarged surface of the tubes and when the flow (F) in each tube of the reactor was decreased, which indicated a smaller amount of reagents reacting on the reactor, resulting in less heat that has to be removed. Finally, the use of small dp led to a decrease in the production of heavy hydrocarbons, resulting in less heat production; therefore, less heat exchange area was required.

Wang et al. (2003b) proposed a pseudo-homogeneous reactor model comprising mass and energy balances in the reactor [Equations (40)–(43)]. They called this a “heterogeneous model” despite the main supposition that the reaction system has pseudo-homogeneous behavior. An important consideration here is that the analysis of the heat and mass transfer in the reactor are obtained only by the balances in the axial coordinate of the reactor, neglecting the effects of the radial coordinate. This method resulted in a 1D model that can be solved “easily”:

Mass balance in the reactor

(40)ddz(usci)=24dp3ρp(1-εB)0rp(j=1NRαijR^j)r2dr (i=1,NPG)
(41)B.C. 11: z=0,ci=ci0

Energy balance in the reactor

(42)ρgCp,musdTbdz=24dp3(1-εB)0rp[j=1NR(-ΔHj)R^j]r2dr+4UDT(Tcool-Tb)
(43)B.C. 12: z=0,Tb=To

On the contrary, in the FTS reaction, the concentration gradients and temperature profiles inside the catalyst particles have important implications on the selectivity for the reaction products, which should be determined. The corresponding mass and heat transfer balances in the catalyst pellets are expressed in Equations (44) to (49).

Mass balance in the catalyst particle or pellet

(44)Deff,i1r2ddr(r2dcs,idr)=-ρpj=1NRαijR^j
(45)B.C. 13: r=0,dcs,idr=0
(46)B.C. 14:r=rp, -Dedcs,idr=km(cs,i-ci)

Energy balance in the catalyst particle or pellet

(47)keff1r2ddr(r2dTsdr)=-ρpj=1NR(-ΔHj)R^j
(48)B.C. 15: r=0,dTsdr=0
(49)B.C. 16: r=rp, -keffdTsdr=hf(Ts-Tg)

Wang et al. (2003b) assumed that the external mass transfer limitations can be considered absent because the film of heavy hydrocarbons (liquid wax) around the catalyst particle is very thin. Therefore, the mass transfer coefficient in Equation (46) can be supposed to be large, and then the boundary condition results in cs,i=ci. This concentration could be explained by assuming that there is a gas-liquid equilibrium at the interface between the catalytic particle and the gaseous phase (this is a reasonable supposition for the TFBR; Froment et al. 2011), taking into account the solubilization of the gas-phase compounds into the liquid wax [yi=(φiL/φiV)xi]. Thus, the value of ci can be obtained from the thermodynamic equilibrium. This consideration is only acceptable in a strongly exothermic reaction, if the operation conditions allow the supposition that there is not a sufficient temperature gradient in the catalyst pellet (e.g. small catalyst pellet size and/or high thermal conductivity in the pellet), leaving the main resistance to the heat transfer in the region between the liquid wax and the external surface of the catalyst particle (Carberry 1961, 2001, Weisz and Hicks 1962).

To obtain the solution of the model, momentum balance is also required. Almost all 1D models reviewed here used the momentum balance in the reactor given by Equations (50) and (51):

(50)dPdz=-fp(G2/ρg)dp1-εε3
(51)B.C. 17: z=0,P=P0

where fp=fp(Rep) is a function of the Reynolds number based on the catalyst particle (Rep) defined in Equation (52):

(52)Rep=dpμG1-ε

where G=ρus is the mass flux (or mass flow per unit area) in the axial direction and us is the superficial gas velocity. Most studies also used the Ergun correlation (Ergun 1952) expressed in Equation (53), but Wang et al. (2003b) used the correlation of Hicks (1970) expressed in Equation (54). There is a substantial difference in the behavior of both equations when the Reynolds number increases. In the case of the Equation (53), a continuous drop until an asymptotic value is observed, whereas Equation (54) always predicts an increase, which is the best physical description of the flow during the reactor operation (Hicks 1970).

(53)fp=1.75+150Rep
(54)fp=6.8(Rep1-ε)0.8

Essentially, all revised 1D transport phenomena models for the TFBR considered a plug-flow regime, which simplifies the analysis of the problem. However, Mamonov et al. (2013) simulated the FTS process with a Co-based catalyst [see Table 6, Equations (6.12)–(6.16)] for a laboratory-scale reactor without consideration of the plug-flow regime because they considered this assumption to be an oversimplification of the flow pattern. Instead, they used an expression for the linear gas velocity that depends on the temperature, pressure, and the conversion of CO, taking into account that these parameters vary throughout the reactor length. Equivalently, Moutsoglou and Sunkara (2011) conducted a simulation study in a multitube packed-bed reactor with an Fe-based catalyst, considering the changes in the mass flow rate of the gas through the packed tube as a function of the adsorption of CO and H2 on the catalytic surface and the incorporation into the fluid stream of the produced hydrocarbons (olefins and paraffins), some in the gas phase (Cn, n<20) and others in the liquid phase (Cn, n≥20). These changes in the molar volume of the mixture promote important changes in the flow pattern inside the reactor that have to be taken into account to achieve a proper description of the reactor behavior. For example, Mamonov et al. (2013) made use of the ratio between the molar flux of the ith component (Φi) and the linear velocity (u) to estimate the concentration of the compounds (Cii/u) along the reactor length. The concentration in this case has a strong relationship with the temperature, pressure, and CO conversion; therefore, its variation along the reactor will not be linear or a simple function of the reaction parameters.

Mazzone and Fernandes (2006) conducted a study to describe the polymerization of the CO and the distribution of products during the FTS reaction when the contribution of the WGS reaction is significant (which is the real situation during the FTS reaction on Fe-based catalysts). They supposed that alkyl and alkenyl mechanisms acted together during the FTS reaction. Their model assumes that the heat generated during the reaction is completely removed by the cooling water in the reactor jacket, allowing for consideration of isothermal operation in the reactor (543 K). The external mass transfer resistance between the catalyst and the gas phase, as well as the resistance to mass transfer within the particle, was considered negligible due to the very small diameter of particle used (dp=70 µm) in their simulations. To simplify the study, the concentration and temperature gradients within the tube in the radial coordinate were not considered, and it was assumed that the produced hydrocarbons were in equilibrium in the gas and liquid phases at the reactor outlet. The reactor pressure (1–4 MPa), the gas velocity (1–10 m/s), and the H2/CO feed ratio (0.5–2) were varied to study the influence of these parameters on the conversion, production, and distribution (selectivity) of the produced hydrocarbons. The total system pressure and the H2/CO ratio were the main factors that affected the reactor performance and should be adjusted depending on the desired hydrocarbon compound fraction. For example, the production of gasoline was favored by high pressures and high gas velocities, producing 4.8 wt% compared to only 1.9 wt% of diesel. Additionally, the selection of an adequate catalyst is critical to achieve the best performance in the reactor.

Moutsoglou and Sunkara (2011) conducted a study with an Fe-based catalyst using the rate equations derived from the alkyl and alkenyl reaction mechanisms (similar to Mazzone and Fernandes 2006) to predict the formation of paraffin and olefin compounds. Their model considered isothermal conditions and the kinetic effects derived from the hydrocarbon desorption and their integration into the bulk gas phase. They conducted simulations to evaluate the effects of varying the H2/CO ratio, pressure at the reactor inlet, and reactor length parameters on the selectivity and product distribution. The rate of carbon conversion increased with an increase in the inlet pressure, in agreement with the results of Wang et al. (2003b), and the same occurred with an increase of the reactor length and the H2/CO ratio. The selectivity to paraffins increased with an increase in the H2/CO ratio and length of the reactor (LT), whereas the selectivity to olefins increased with an increase in the inlet pressure of the reactor.

The control of the reaction temperature is not only performed using a cooling jacket in the TFBR; recirculating a fraction of the reactor effluent facilitates temperature control in the reactor. There is an increase in the temperature difference between the reactor core and the outer surface of the reactor when DT (diameter of the reactor tube) increases. The control of the reactor temperature is a key factor in the FTS reaction because the temperature determines the productivity and selectivity of the process. Thus, there is a necessity to develop mathematical models that can help in the understanding of the reactor behavior during the FTS reactions to economize and improve the design and scale-up of the reactors.

For example, Wang et al. (2003b) conducted a study in which CO, H2, CO2, H2O, N2, and hydrocarbons (n-paraffins and n-olefins) of up to 50 carbon atoms were selected as key compounds in the development of a mathematical model to evaluate the effects of the main process parameters on the FTS reaction using a recycling operation. They assumed that the particle bed does not offer resistance to heat transport through the reactor tube wall; in other words, they stated that the effective radial thermal conductivity in the particle bed tends to infinity (λrad→∞), and the resistance to heat conduction due to the reactor wall (λW→∞) was neglected. An excess of heat could increase the reactor temperature, causing the occurrence of a hotspot (Wang et al. 2003b). They observed that, when DT increases, the hotspot moves forward in the axial coordinate of the reactor (Figure 10A), severely affecting the selectivity to C5+ products, which finally leads to a large production of unwanted products (CH4 and CO2). This result is in agreement with the result reported by Atwood and Bennett (1979), who suggested that it is undesirable to use tubes with a DT >40 mm to perform the FTS reaction.

Figure 10: Effect of process parameters on the axial temperature profile in the fixed-bed reactor. Base conditions: dt=DT=32 mm, L=7.0 m, GHSV=500 h-1, Rcyc=R=3.0, TW=523 K, Pin=2.5 MPa, fresh synthesis gas composition (%); CO: 30.59; H2: 57.75; CO2: 7.0; N2: 4.08; CH4: 0.58.Reprinted with permission from Wang et al. (2003b). © Copyright 2003 Elsevier.Change of temperature along the reactor as function of: (A) Catalyst particle diameter, (B) Recycle ratio, (C) Cooling temperature, and (D) Reaction pressure.
Figure 10:

Effect of process parameters on the axial temperature profile in the fixed-bed reactor. Base conditions: dt=DT=32 mm, L=7.0 m, GHSV=500 h-1, Rcyc=R=3.0, TW=523 K, Pin=2.5 MPa, fresh synthesis gas composition (%); CO: 30.59; H2: 57.75; CO2: 7.0; N2: 4.08; CH4: 0.58.

Reprinted with permission from Wang et al. (2003b). © Copyright 2003 Elsevier.

Change of temperature along the reactor as function of: (A) Catalyst particle diameter, (B) Recycle ratio, (C) Cooling temperature, and (D) Reaction pressure.

When the recirculating effect was studied by Wang et al. (2003b), it was observed that, without recycling (R) to the reactor, the temperature near the reactor inlet increases rapidly, leading to a hotspot formation or thermal instability of the reactor (Figure 10B). The recirculation of a fraction of unreacted synthesis gas (diluted with light hydrocarbons) to the reactor inlet causes an increase in the linear velocity of the synthesis gas inside the reactor, which reduces the concentration of reactants and the reaction rate, preventing reactor overheating. As can be seen in Figure 10B, the temperature of the hotspot decreased and its location in the reactor moved backward as the value of R was increased, showing that the recycle operation is important to maintaining the thermal stability of the TFBR because recycling serves to boost the heat transfer parameters in the reactor. The last allows a greater control over the selectivity towards the desired products (e.g. C5+) and consequently prevents the formation of unwanted products (i.e. CH4 and CO2; Wang et al. 2003b).

The temperature in the cooling jacket (Tcool) also has a significant effect on the operation temperature and reactor performance. The heat load generated by the reaction must be absorbed by the refrigerant fluid in the cooling jacket. The rate of heat removal depends mainly on Tcool; therefore, when this temperature is lower than the temperature of the feed gas, there are no hotspots at the inlet reactor (see Figure 10C, where TW=Tcool). If Tcool increases (or consequently the reactor temperature increases), then the synthesis gas conversion is favored, but this has a negative effect on the selectivity to the desired products (Wang et al. 2003b). Nevertheless, under these operation conditions, the removal of heat by the cooling jacket does not have the same rate as that generated by the chemical reaction; hence, a hotspot could be formed. This hotspot could move toward the beginning of the catalyst bed with an increase in the reactor temperature (Wang et al. 2003b, Mamonov et al. 2013), affecting the selectivity towards the desired products (C5+). Therefore, it is necessary to properly select the operation conditions for each reactor to ensure efficient heat removal from the catalytic zone so that good conversion of the synthesis gas can be achieved in addition to maintaining an adequate selectivity and avoiding the appearance of hotspots. Additionally, increasing the reactor pressure increases the concentration of the gas reactants on the liquid wax due to the VLE that surrounds the catalyst particles, resulting in a greater availability of the reactants on the catalytic surface. This high reactant concentration increases the reaction rate; therefore, an additional generation of reaction heat is observed. Thus, if the pressure in the reactor increases, the temperature of the hotspots also increases, and their position in the reactor could move towards the reactor inlet (Wang et al. 2003b; see Figure 10D). However, an increase in pressure commonly improves the conversion of CO and the overall performance for producing C5+ products.

Since the discovery of the FTS reaction, the reaction rate has been extensively studied, and the number of publications that propose a reaction rate equation is large. However, there are few publications that report the quantitative value of the parameters for the rate equations for commercial catalysts (Jess and Kern 2009). For example, Lee and Chung (2012) found that, in most previous investigations of the FTS reaction, the reaction rate equations were developed with the use of lumped reaction models, with evident disadvantages due to their inability to predict the exact amount of heat released by the FTS reaction and therefore the real consumption of H2 and CO. They mentioned the differences that appear when only the reactant conversion is considered in the determination of the reaction heat released; for instance, if the same consumption amount of CO (10 moles) is considered, the formation of n-decane and methane results in a heat release of 1560 and 2060 kJ (at STP conditions), respectively. This difference demonstrates the need to obtain reaction rate equations that truly represent the FTS reaction and allow that the temperature of the reactor to be satisfactorily controlled if the heat released by the chemical reaction is accurately determined.

4.3.2.2 2D TFBR models

The 1D models proposed so far in the literature for the FTS reaction (e.g. Wang et al. 2003b, Mamonov et al. 2013) are useful because they provide understanding of the transport phenomena and the kinetic effects that occur as a result of the combination of reaction parameters, such as temperature, pressure, and particle size. However, on the macrolevel, these 1D models do not provide an accurate way to quantify the energy transport because the radial coordinate is not taken into account. Therefore, it is necessary to develop and study 2D models that consider the transfer of energy in both the axial and radial coordinates of the reactor to properly evaluate (as quantitatively as possible) the mass and energy transport.

Since the pioneering work of Bub et al. (1980), who discussed a 2D model for an FTS reactor, there have been few works reporting the 2D analysis of the reactor. Computer processing capacity has increased substantially in recent years, as well as the development of commercial simulators that can solve systems of partial differential equations, allowing for the solution of the complex equations that result from the momentum, mass, and energy balances. Thus, several studies for the FTS reaction that comprise 2D models have been published recently (e.g. Everson et al. 1996, Jess et al. 1999, Wu et al. 2010, Jess and Kern 2012a,b, Lee and Chung 2012, Aligolzadeh et al. 2015, Chabot et al. 2015). Examples of the 2D studies include the papers of Jess and Kern (2009, 2012a,b), who found that the prediction of the ignition temperature in the reactor by a 1D model can have an appreciable difference compared to the prediction using a 2D model. As an example, the first case (1D) resulted in a temperature of 528 K, whereas the second case (2D) resulted in a temperature of 520 K, which is a clear indication that the mathematical models must be solved considering as many physical aspects as possible regarding the FTS reaction and reactor. Recently, Ermolaev et al. (2015) published a work where they made use of a comprehensive 2D heterogeneous model using a Co-based catalyst [see Table 6, Equations (6.7)–(6.11)]. They supposed in their model that the pores of the catalyst particles were filled with liquid wax and water due to capillary condensation and validated their model against experimental data from a laboratory equipment and pilot-scale plant. Figure 11 shows a comparison of the temperature results along the reactor length for the predicted data and the experimental measurements (gas flow from left to right). Because there is a high conversion at the entrance of the reactor (due to the high amount of reactants in the fluid stream in contact with the catalyst), the temperature in that zone of the reactor increases suddenly, accompanied by the formation of a hotspot, such as is shown in Figure 11 (see also Figure 10). It can be observed from the theoretical results of Ermolaev et al. (2015) that the proposed model underestimates the temperature in the reactor zone where the increasing temperature occurs (thermocouples index 1–6). The authors indicated that the good prediction of the model after the seventh thermocouple index is due to the small thermal difference between the cooling jacket and the catalytic bed (~3°C), which provides efficient heat removal. Conversely, at the entrance of the reactor, error was introduced in the data fed to the model due to the estimation of the cooling water temperature (the average value of the temperature at the inlet and the outlet of the jacket). Despite this error, the proposed model has good prediction ability for the temperature in the reactor, providing valuable information and a good demonstration (via an experimental validation) that a 2D model is necessary for the simulation of the thermal behavior in a TFBR.

Figure 11: Temperature profile inside the single-tube reactor (2.1 m long; black, solid) and the water jacket temperature profile (black, dotted).The solid line (line red in the electronic version) is temperature profile along the reactor tube estimated by the theoretical model.Reprinted with permission from Ermolaev et al. (2015). © Copyright 2015 Elsevier.
Figure 11:

Temperature profile inside the single-tube reactor (2.1 m long; black, solid) and the water jacket temperature profile (black, dotted).

The solid line (line red in the electronic version) is temperature profile along the reactor tube estimated by the theoretical model.

Reprinted with permission from Ermolaev et al. (2015). © Copyright 2015 Elsevier.

A review of the emerging 2D modeling papers for the FTS reaction involves great effort in the analysis of the proposals to highlight the key differences and advantages in each particular case because the diversity of operating conditions, catalysts, and reactor types makes a straightforward comparison difficult. However, this effort should be conducted to gain better comprehension of the phenomena occurring during the FTS reaction in the pellet and during reactor operation.

4.3.3 Solution of the transport phenomena model using mathematical optimization

Recently, other types of simulation for the FTS reaction have been proposed. For example, Hallac et al. (2015) optimized their nonlinear model to obtain the best combination in their decision variables (dp, T, P, and yCO) for the FTS reaction using data for a Fe-based catalyst. They maximized the catalytic efficiency by selecting the productivity, defined as the multiplication of the effectiveness factor (η) by the intrinsic reaction rate (R^CO), as the objective function. Thus, when the productivity is maximized, η is also maximized; therefore, Φ is minimized. The constraints on the optimization algorithm were selected to meet the following physical conditions: (I) minimal heat transfer limitations from the outer liquid wax film and the catalyst particle, (II) low amount of CO in the gas inlet stream to prevent rapid catalyst deactivation by carbon deposition (H2/CO≥0.66, typical for the Fe-based catalysts used in the FTS reaction), (III) nonzero CO conversion, (IV) prevent pressure drops (ΔP/P) of the catalyst bed larger than 20%, and (V) keep the catalyst activity above 50% of its initial activity. To accomplish point (V), Hallac et al. (2015) used a deactivation model developed by Eliason and Bartholomew (1999) [Equation (55)] for an Fe-based catalyst to include the catalyst deactivation when the reactor temperature was between 523 and 553 K. With the use of this deactivation model, a value of 0.5 can be assigned to the residual activity parameter (a) to satisfy point (V).

(55)a=(1-a)e-kdt+a, with kd=Ade-Ed/(RgT).

Their proposal was to solve the problem by fixing the value of η at 0.99, which physically means that the mass and heat transfer limitations are overcome. Their optimization settings for this study were as follows: (a) a reaction temperature of 528.8 K, (b) a maximum pressure in the reactor of 3 MPa, and (c) a minimum CO composition (yCO) of 0.2. From their optimization results, it was determined that the optimum particle diameter (dp) was 80 μm, which was the lowest value allowed in the parameter constraints, and although it is preferable to have a smaller size (to diminish the mass and heat transport limitations), the pressure drop in the reactor resulting from this diminution is an important impediment to a further decrease in the catalyst particle size. Additionally, the optimum reaction temperature was determined with the goal of reducing the rate of catalyst deactivation. From their results, it was observed that, at 528.8 K, the reaction rate was maximized, and at the same time, this temperature contributed to reaching 50% residual activity after 1000 h of operation, achieving a long life-time for the catalyst. As can be expected, at higher reaction temperature, the reaction rate also increases, which causes the formation of hotspots and consequently a decrease in the selectivity toward C5+ compounds. The authors also found that, in addition to operation at high temperature, the catalyst deactivation was promoted at higher H2/CO ratios, changing the catalyst selectivity to the formation of CH4 and other light compounds. The effect of the H2/CO ratio on the catalyst deactivation is in agreement with the work of Keyvanloo et al. (2015), who found that a change in the H2/CO ratio caused an increase in the deactivation rate of their Co-based catalysts due to polymeric carbon deposition.

Hooshyar et al. (2012) analyzed the use of a structured catalytic bed reactor (Co-based catalyst) to enhance the productivity to C5+ compounds in the FTS reaction, where a 1D model for a fixed-bed reactor was proposed. This reaction system consists of a cross-flow structure that allows the mixture of gas and liquid phases, where the gas and liquid phases flow in diagonal pathways. With this arrangement in the catalyst bed, the heat transfer could be more effective in the radial coordinate compared to the case of a randomly packed bed. Consequently, a uniform temperature along the reactor can be obtained. The productivity increased more than 40% when the heat transfer coefficient was increased 2.5 times in the structured catalyst bed in comparison to the randomly catalyst bed, whereas the diffusion length in the catalyst particles decreased by a factor of 2. They concluded that the structural arrangement can also be used to reduce the reactor volume, albeit the reaction conversion will be the same.

Recently, Kaskes et al. (2016) performed a simulation for the FTS reaction by studying the reactor performance using a random packed bed (RPB) and a packed closed cross-flow structure (CCFS). In their study, the last configuration had a catalyst arrangement composed of lateral channels to have a preferential flow circulation of the reactants inside the bed. With this arrangement, the reactants can reach the catalytic surface easily, suggesting that, if the catalyst pellets are packed in a CCFS arrangement, the diameter of the pellets can be minor because the diameter will not induce a significant pressure drop in the reactor compared to the use of the typical RPB with small diameter particles. Thus, the reactor performance for each catalyst arrangement (RPB and packed CCFS) was studied using two catalytic activities reported by Yates and Satterfield (1991) for a Co-based catalyst. The reaction temperature was limited to a maximum of 530 K to avoid a thermal runaway in the reactor, and the reaction pressure was fixed at 1 MPa, which corresponded to the low limit value of the validity range of the reaction rate used. A minimum L/Dt ratio was set to 100 to maintain the plug flow reactor characteristics and to prevent the optimization process from leading to short tube lengths. The minimum average carbon selectivity C5+ was set at 0.90.

From their optimization results, they observed that, when a CCFS arrangement was used, the heat released during the FTS reaction was easily removed, allowing for good temperature control of the reactor, which promoted a reduction in the radial temperature gradients, increasing in the selectivity toward the desired hydrocarbon (e.g. C5+). Because the reaction heat can easily be removed from the reactor when the CCFS arrangement is used, catalysts with high activity offer great opportunity to effectively use the catalytic potential during the FTS reaction without thermal dissipation problems, whereas, in the case of RPB, this is not possible due to the presence of large temperature gradients inside the reactor, such as discussed above. Finally, the authors of this work mentioned that the optimization process for the FTS reaction tends to avoid the overestimation of the synthesis gas ratio and the particle diameters and the prediction of reactor productivity compared to those estimated in the case of FTS reactor modeling. Moreover, it is suggested that a good description of the catalyst behavior at the microlevel is desirable for the reactor design on the macrolevel, taking as a starting point the observations from the phenomena in the catalyst particle.

5 Conclusions

From the results discussed in this study, it can be concluded that controlling the operating reactor temperature of the TFBR is crucial to achieve the desired selectivity and productivity because the FTS reaction is highly sensitive to temperature due to its exothermicity. The selectivity of the reaction is also affected by mass transport on the catalyst particle and by the catalyst layer thickness (in the case of structured reactors), which hinders the diffusion of reactants and products inside the catalyst. On the contrary, there is still uncertainty about the mechanism that follows the FTS reaction; thus, more research should be performed in that direction to obtain kinetic equations that accurately represent the reaction because, in addition to the possible improvement in the estimation of the yield of the desired hydrocarbon products, these equations will allow for accurate estimation of the heat evolved during the reaction, resulting in the possibility to conduct efficient heat removal from the reactor. Additionally, there are still discrepancies about which of the diffusivity resistances predominate during the reaction (molecular and/or Knudsen), and there is also a need to investigate which of the diffusion flux models present the best description of the FTS reaction system. Furthermore, the deactivation data are scarce, so it is necessary to determine the kinetics of deactivation for the different mechanisms to describe the loss in activity in realistic reaction conditions. Finally, to properly perform the modeling of the TFBR, it is necessary to include both axial and radial directions (2D) in the model to obtain good estimations of the reactor parameters (such as recycling, cooling temperature, and type of catalyst) and to evaluate the impact of these parameters on the conversion, selectivity, and temperature along the reactor.

Nomenclature
a

catalyst activity

a

residual activity

av

specific superficial area

Ai

Arrhenius kinetic coefficient Ai=Ai0e-Eai/RT

Bo

Darcy’s permeability constant

cib

molar concentration of component i evaluated in the bulk

ci,cat, cis

molar concentration of component i evaluated at the catalyst surface

ci,0

inlet gas concentration of component i

ci,TP

concentration of species i in the transport pore (TP)

cs,i

liquid concentration of component i

Cn+

hydrocarbon composed by more than n-carbon atoms

Cp,m

residual heat capacity of jth reaction

dp

particle diameter

dpore

pore diameter

De,i

effective diffusivity for species i

DD,ij

binary diffusivity of species i through j

DK,i

Knudsen diffusivity

DT

internal diameter of the reactor tube

EAi

activation energy

F

inlet mass flux

fp

friction factor (pressure drop)

G

mass flux (or mass flow per unit area)

hf

convective heat transfer coefficient

Hi

Henry’s law solubility constant

Ji

mass flux of species i

ki

kinetic rate constant

keff

effective conductivity coefficient

km

mass transfer coefficient

Ki

equilibrium adsorption constant for species i

L, c

characteristic length

lcat

thickness of catalyst layer

lTP

transport pore (TP) depth

lfilm

liquid wax thickness

LT

reactor length or height

Mi

molecular weight of the ith compound (i=A, B)

NPG

number of key compounds involved

NR

total number of reactions involved in the balance

n

number of carbon atoms

ni

normal unit vector

average carbon number

Ni, Nk

molar flux density of i and k species, respectively

P

reaction pressure

Pi

partial pressure for component i

r

radial coordinate

r*

dimensionless particle radius

rp

radius of pellet

R

recycle ratio (recycle gas/fresh gas)

R^FT

reaction rate for FTS

R^WGS

reaction rate for WGS

Rg

universal gas constant

R^p

rate of chain propagation

R^t

rate of chain termination

R^i

rate of reaction for component i

Rep

Reynolds number based on a catalyst particle

Tb

bulk temperature

Tcool, TW

temperature of the coolant

Tsup

superficial pellet temperature

u

linear velocity

us

superficial gas velocity

Vpore

pore volume

V˜

specific molar volume

V˜0

specific molar volume of reference

Wn

mass fraction of the species with carbon number n

yi

molar fraction of component i in bulk gas phase

z

axial coordinate in the TFBR

Greek symbols
α

chain growth probability of hydrocarbons in the ASF distribution

α

chain growth probability of first distribution

α

chain growth probability of second distribution

αij

stoichiometric coefficient of component i in reaction jth

β

heat generation function

β

readsorption probability

γ

enhancement factor describing the deviation at C1

Hj

reaction heat of jth reaction

εB

bed voidage

εp

catalyst pellet porosity

εb

bulk porosity

εTP

porosity of transport pores (TP)

ha

approximate effectiveness factor

λrad

effective radial heat conductivity of the catalyst bed

λW

heat conductivity of the reactor wall

μ

fraction of second distribution function

ξ

spatial coordinate

ρp

apparent density

ρg

bulk gas density

νL

molar volume of the products in liquid phase

σi

hard-sphere diameter of species i

τ

tortuosity

φiV,φiL

fugacity coefficient of component i in gas phase (V) and liquid wax (L)

Superscripts and subscripts
a, b, c, d

exponents

q

geometric factor, to adjust Equation (16) to rectangular, cylindrical, or spherical coordinates

i

associated to species i

Acknowledgments

This work was supported by grants from Consejo Nacional de Ciencia y Tecnología-México (CONACYT; Project No. 156064). J.R.G. Sánchez-López is grateful to CONACYT for the scholarship granted by the retention and repatriation program (No. 232548).

References

Adesina AA, Hudgins RR, Silveston PL. Fischer-Tropsch synthesis under periodic operation. Catal Today 1995; 25: 127–144.10.1016/0920-5861(95)00103-MSuche in Google Scholar

Akgerman A. Diffusivities of Synthesis Gas and Fischer-Tropsch Products in Slurry Media. Final Report. DOE Report-DOE/PC/70032-T2, the U.S. Department of Energy (USDOE) Assistant Secretary for Fossil Energy, Washington, DC, USA, 1984.Suche in Google Scholar

Aligolzadeh H, Jolodar AJ, Mohammadikhah R. CFD analysis of hot spot formation through a fixed bed reactor of Fischer-Tropsch synthesis. Cogent Eng 2015; 2: 1006016.10.1080/23311916.2015.1006016Suche in Google Scholar

Aris R. On shape factors for irregular particles – I. The steady state problem. Diffusion and reaction. Chem Eng Sci 1957; 6: 262–268.10.1016/0009-2509(57)85028-3Suche in Google Scholar

Atwood HE, Bennett CO. Kinetics of the Fischer-Tropsch reaction over iron. Ind Eng Chem Process Des Dev 1979; 18: 163–170.10.1021/i260069a023Suche in Google Scholar

Becker H, Güttel R, Turek T. Optimization of catalysts for Fischer-Tropsch synthesis by introduction of transport pores. Chem Ing Technik 2014; 86: 544–549.10.1002/cite.201300142Suche in Google Scholar

Becker H, Güttel R, Turek T. Enhancing internal mass transport in Fischer-Tropsch catalyst layers utilizing transport pores. Catal Sci Technol 2016; 6: 275–287.10.1039/C5CY00957JSuche in Google Scholar

Bezemer GL, Radstake PB, Falke U, Oosterbeek H, Kuipers HPCE, van Dillen AJ, de Jong KP. Investigation of promoter effects of manganese oxide on carbon nanofiber-supported cobalt catalysts for Fischer-Tropsch synthesis. J Catal 2006; 237: 152–161.10.1016/j.jcat.2005.10.031Suche in Google Scholar

Brunner KM, Duncan JC, Harrison LD, Pratt KE, Peguin RPS, Bartholomew CH, Hecker WC. A trickle fixed-bed recycle reactor model for the Fischer-Tropsch synthesis. Int J Chem React Eng 2012; 10: 1–36.10.1515/1542-6580.2840Suche in Google Scholar

Brunner KM, Perez HD, Peguin RPS, Duncan JC, Harrison LD, Bartholomew CH, Hecker WC. Effects of particle size and shape on the performance of a trickle fixed-bed recycle reactor for Fischer-Tropsch synthesis. Ind Eng Chem Res 2015; 54: 2902–2909.10.1021/ie503174vSuche in Google Scholar

Bub G, Baerns M, Büssemeier B, Frohning C. Prediction of the performance of catalytic fixed bed reactors for Fischer-Tropsch synthesis. Chem Eng Sci 1980; 35: 348–355.10.1016/0009-2509(80)80106-0Suche in Google Scholar

Carberry JJ. The catalytic effectiveness factor under nonisothermal conditions. AIChE J 1961; 7: 350–351.10.1002/aic.690070239Suche in Google Scholar

Carberry JJ. Chemical and catalytic reaction engineering. Mineola, NY: Dover, 2001.Suche in Google Scholar

Chabot G, Guilet R, Cognet P, Gourdon C. A mathematical modeling of catalytic milli-fixed bed reactor for Fischer-Tropsch synthesis: influence of tube diameter on Fischer Tropsch selectivity and thermal behavior. Chem Eng Sci 2015; 127: 72–83.10.1016/j.ces.2015.01.015Suche in Google Scholar

Climate Change 2014. Mitigation of Climate Change, Working Group III Contribution to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change, IPCC 2014. https://www.ipcc.ch/report/ar5/wg3/. Accessed June 22, 2016.Suche in Google Scholar

Davis ME, Davis RJ. Fundamentals of chemical reaction engineering. New York: McGraw-Hill, 2003.Suche in Google Scholar

den Breejen JP, Frey AM, Yang J, Holmen A, van Schooneveld MM, de Groot FMF, Stephan O, Bitter JH, de Jong KP. A highly active and selective manganese oxide promoted cobalt-on-silica Fischer-Tropsch catalyst. Top Catal 2011; 54: 768–777.10.1007/s11244-011-9703-0Suche in Google Scholar

Derevich IV, Ermolaerv VS, Mordkovich VZ. Hydrodynamic limitations of microchannel Fischer-Tropsch reactor operation. World J Mech 2013; 3: 292–297.10.4236/wjm.2013.36030Suche in Google Scholar

Dry ME. Fischer Tropsch synthesis over iron catalysts. Catal Lett 1990; 7: 241–252.10.1007/BF00764506Suche in Google Scholar

Dry ME. The Fischer-Tropsch process: 1950–2000. Catal Today 2002; 71: 227–241.10.1016/S0920-5861(01)00453-9Suche in Google Scholar

Duvenhage DJ, Coville NJ. Deactivation of a precipitated iron Fischer-Tropsch catalyst – a pilot plant study. Appl Catal A Gen 2006; 298: 211–216.10.1016/j.apcata.2005.10.009Suche in Google Scholar

EIA. Annual Energy Outlook 2015. Available at: http://www.eia.gov/forecasts/aeo/pdf/0383(2015).pdf. Accessed June 22, 2016.Suche in Google Scholar

Eliason SA, Bartholomew CH. Reaction and deactivation kinetics for Fischer-Tropsch synthesis on unpromoted and potassium-promoted iron catalysts. Appl Catal A Gen 1999; 186: 229–243.10.1016/S0926-860X(99)00146-5Suche in Google Scholar

Ergun S. Fluid flow through packed columns. Chem Eng Prog 1952; 48: 89–94.Suche in Google Scholar

Erkey C, Rodden JB, Akgerman A. Diffusivities of synthesis gas and n-alkanes in Fischer-Tropsch wax. Energy Fuels 1990; 4: 275–276.10.1021/ef00021a010Suche in Google Scholar

Ermolaev VS, Gryaznov KO, Mitberg EB, Mordkovich VZ, Tretyakov VF. Laboratory and pilot plant fixed-bed reactors for Fischer-Tropsch synthesis: Mathematical modeling and experimental investigation. Chem Eng Sci 2015; 138: 1–8.10.1016/j.ces.2015.07.036Suche in Google Scholar

Espinoza RL, Steynberg AP, Jager B, Vosloo AC. Low temperature Fischer-Tropsch synthesis from a Sasol perspective. Appl Catal A Gen 1999; 186: 13–26.10.1016/S0926-860X(99)00161-1Suche in Google Scholar

Everson RC, Mulder H, Keyser MJ. The Fischer-Tropsch reaction with supported ruthenium catalysts: modelling and evaluation of the reaction rate equation for a fixed bed reactor. Appl Catal A Gen 1996; 142: 223–241.10.1016/0926-860X(96)00054-3Suche in Google Scholar

Feyzi M, Jafari F. Study on iron-manganese catalysts for Fischer-Tropsch synthesis. J Fuel Chem Technol 2012; 40: 550–557.10.1016/S1872-5813(12)60021-8Suche in Google Scholar

Förtsch D, Pabst K, Groß-Hardt E. The product distribution in Fischer-Tropsch synthesis: an extension of the ASF model to describe common deviations. Chem Eng Sci 2015; 138: 333–346.10.1016/j.ces.2015.07.005Suche in Google Scholar

Froment GF, Bischoff KB, DeWilde J. Chemical reactor analysis and design, 3rd ed., Hoboken, NJ: John Wiley & Sons, 2011.Suche in Google Scholar

Gonzo EE, Gottifredi JC. Rational approximations of effectiveness factor and general diagnostic criteria for heat and mass transport limitations. Catal Rev 1983; 25: 119–140.10.1080/01614948308078875Suche in Google Scholar

Haarlemmer G, Bensabath T. Comprehensive Fischer-Tropsch reactor model with non-ideal plug flow and detailed reaction kinetics. Comput Chem Eng 2016; 84: 281–289.10.1016/j.compchemeng.2015.08.017Suche in Google Scholar

Hallac BB, Keyvanloo K, Hedengren JD, Hecker WC, Argyle MD. An optimized simulation model for iron-based Fischer-Tropsch catalyst design: transfer limitations as functions of operating and design conditions. Chem Eng J 2015; 263: 268–279.10.1016/j.cej.2014.10.108Suche in Google Scholar

Hicks RE. Pressure drop in packed beds of spheres. Ind Eng Chem Fundam 1970; 9: 500–502.10.1021/i160035a032Suche in Google Scholar

Hooshyar N, Vervloet D, Kapteijn F, Hamersma PJ, Mudde RF, van Ommen JR. Intensifying the Fischer-Tropsch synthesis by reactor structuring – a model study. Chem Eng J 2012; 207–208: 865–870.10.1016/j.cej.2012.07.105Suche in Google Scholar

Huff GA Jr, Satterfield CN. Intrinsic kinetics of the Fischer-Tropsch synthesis on a reduced fused-magnetite catalyst. Ind Eng Chem Process Des Dev 1984; 23: 696–705.10.1021/i200027a012Suche in Google Scholar

Iglesia E, Reyes SC, Soled SL. Reaction-transport selectivity models and the design of Fischer-Tropsch catalysts. In: Becker ER, Pereira CJ, editors. Computer-aided design of catalysts. New York: Marcel Dekker, 1993: 199–257.10.1201/9781003067115-7Suche in Google Scholar

Iglesias-González M, Schaub G. Fischer-Tropsch synthesis with H2/CO2-catalyst behavior under transient conditions. Chem Ing Technol 2015; 87: 848–854.10.1002/cite.201400137Suche in Google Scholar

Jager B. Developments in Fischer-Tropsch technology. Natural Gas Conversion V. In: Parmaliana A, Sanfilippo D, Frusteri F, Vaccari A, Arena F, editors. Studies in Surface Science and Catalysis, Vol. 119. Amsterdam, Netherlands: Elsevier Science B.V., 1998: 25–34.Suche in Google Scholar

Jess A, Kern C. Modeling of multi-tubular reactors for Fischer-Tropsch synthesis. Chem Eng Technol 2009; 32: 1164–1175.10.1002/ceat.200900131Suche in Google Scholar

Jess A, Kern C. Influence of particle size and single-tube diameter on thermal behavior of Fischer-Tropsch reactors. Part I: particle size variation for constant tube size and vice versa. Chem Eng Technol 2012a; 35: 369–378.10.1002/ceat.201100615Suche in Google Scholar

Jess A, Kern C. Influence of particle size and single-tube diameter on thermal behavior of Fischer-Tropsch reactors. Part II: eggshell catalysts and optimal reactor performance. Chem Eng Technol 2012b; 35: 379–386.10.1002/ceat.201100616Suche in Google Scholar

Jess A, Popp R, Hedden K. Fischer-Tropsch-synthesis with nitrogen-rich syngas. Fundamentals and reactor design aspects. Appl Catal A Gen 1999; 186: 321–342.10.1016/S0926-860X(99)00152-0Suche in Google Scholar

Jung A, Kern C, Jess A. Modeling of internal diffusion limitations in a Fischer-Tropsch catalyst. In: Davis BH, Occelli ML, editors. Advances in Fischer-Tropsch synthesis, catalysts, and catalysis. Florida: CRC Press, Taylor and Francis Group, 2010; 12: 215–227.10.1201/9781420062571.ch12Suche in Google Scholar

Kaskes B, Vervloet D, Kapteijn F, van Ommen JR. Numerical optimization of a structured tubular reactor for Fischer-Tropsch synthesis. Chem Eng J 2016; 283: 1465–1483.10.1016/j.cej.2015.08.078Suche in Google Scholar

Keyser MJ, Everson RC, Espinoza RL. Fischer-Tropsch kinetic studies with cobalt-manganese oxide catalysts. Ind Eng Chem Res 2000; 39: 48–54.10.1021/ie990236fSuche in Google Scholar

Keyvanloo K, Fisher MJ, Hecker WC, Lancee RJ, Jacobs G, Bartholomew CH. Kinetics of deactivation by carbon of a cobalt Fischer-Tropsch catalyst: effects of CO and H2 partial pressures. J Catal 2015; 327: 33–47.10.1016/j.jcat.2015.01.022Suche in Google Scholar

Kibby C, Jothimurugesan K, Das T, Lacheen HS, Rea T, Saxton RJ. Chevron’s gas conversion catalysis-hybrid catalysts for wax-free Fischer-Tropsch synthesis. Catal Today 2013; 215: 131–141.10.1016/j.cattod.2013.03.009Suche in Google Scholar

Kuipers EW, Vinkenburg IH, Oosterbeek H. Chain length dependence of α-olefin readsorption in Fischer-Tropsch synthesis. J Catal 1995; 152: 137–146.10.1006/jcat.1995.1068Suche in Google Scholar

Leconte M, Theolier A, Rojas D, Basset JM. Stoichiometric and catalytic homologation of olefins on the Fischer-Tropsch catalyst Fe/SiO2, Ru/SiO2, Os/SiO2, and Rh/SiO2. Mechanistic implication in the mode of C-C bond formation. J Am Chem Soc 1984; 106: 1141–1142.10.1021/ja00316a067Suche in Google Scholar

Lee TS, Chung JN. Mathematical modeling and numerical simulation of a Fischer-Tropsch packed-bed reactor and its thermal management for liquid hydrocarbon fuel production using biomass syngas. Energy Fuels 2012; 26: 1363–1379.10.1021/ef201667aSuche in Google Scholar

Leibovici CF. A consistent procedure for the estimation of properties associated to lumped systems. Fluid Phase Equilib 1993; 87: 189–197.10.1016/0378-3812(93)85026-ISuche in Google Scholar

Lox ES, Froment GB. Kinetics of the Fischer-Tropsch reaction on a precipitated promoted iron catalyst. 2. Kinetic modelling. Ind Eng Chem Res 1993; 32: 71–82.10.1021/ie00013a011Suche in Google Scholar

Ma W, Jacobs G, Das TK, Masuku CM, Kang J, Pendyala VRR, Davis BH, Klettlinger JLS, Yen CH. Fischer-Tropsch synthesis: kinetics and water effect on methane formation over 25% Co/γ-Al2O3 catalyst. Ind Eng Chem Res 2014; 53: 2157–2166.10.1021/ie402094bSuche in Google Scholar

Makrodimitri ZA, Unruh DJM, Economou IG. Molecular simulation of diffusion of hydrogen, carbon monoxide, and water in heavy n-alkanes, J Phys Chem B 2011; 115: 1429–1439.10.1021/jp1063269Suche in Google Scholar PubMed

Mamonov NA, Kustov LM, Alkhimov SA, Mikhailov MN. One-dimensional heterogeneous model of a Fischer-Tropsch synthesis reactor with a fixed catalyst bed in the isothermal granules approximation. Catal Ind 2013; 5: 223–231.10.1134/S2070050413030100Suche in Google Scholar

Mazzone LCA, Fernandes FAN. Modeling of Fischer-Tropsch synthesis in a tubular reactor. Lat Am Appl Res 2006; 36: 141–148.Suche in Google Scholar

Morales F, Grandjean D, Mens A, de Groot FMF, Weckhuysen BM. X-ray absorption spectroscopy of Mn/Co/TiO2 Fischer-Tropsch catalysts: relationships between preparation method, molecular structure, and catalyst performance. J Phys Chem B 2006; 110: 8626–8639.10.1021/jp0565958Suche in Google Scholar PubMed

Moutsoglou A, Sunkara PP. Fischer-Tropsch synthesis in a fixed bed reactor. Energy Fuels 2011; 25: 2242–2257.10.1021/ef200160xSuche in Google Scholar

Nanduri A, Mills PL. Comparison of diffusion flux models for Fischer-Tropsch synthesis. Excerpt from the Proceedings of the 2015 COMSOL Conference in Boston, 2015.Suche in Google Scholar

Peacock-López E, Lindenberg K. The transient Flory model and its application to catalytic polymerization. 1. J Phys Chem 1984; 88: 2270–2275.10.1021/j150655a018Suche in Google Scholar

Peacock-López E, Lindenberg K. The transient Flory model and its application to catalytic polymerization. 2. J Phys Chem 1986; 90: 1725–1732.10.1021/j100399a052Suche in Google Scholar

Post MFM, van’t Hoog AC, Minderhoud JK, Sie ST. Diffusion limitations in Fischer-Tropsch catalysts. AIChE J 1989; 35: 1107–1114.10.1002/aic.690350706Suche in Google Scholar

Pour AN, Hosaini E, Tavasoli A, Behroozsarand A, Dolati F. Intrinsic kinetics of Fischer-Tropsch synthesis over Co/CNTs catalyst: effects of metallic cobalt particle size. J Nat Gas Sci Eng 2014; 21: 772–778.10.1016/j.jngse.2014.10.008Suche in Google Scholar

Puskas I, Hurlbut RS. Comments about the causes of deviations from the Anderson-Schulz-Flory distribution of the Fischer-Tropsch reaction products. Catal Today 2003; 84: 99–109.10.1016/S0920-5861(03)00305-5Suche in Google Scholar

Rauch R, Kiennemann AS. Fischer-Tropsch Synthesis to biofuels (BtL process). In: Triantafyllidis K, Lappas A, Stöcker M, editors. The role of catalysis for the sustainable production of bio-fuels and bio-chemicals. Great Britain: Elsevier Science, 2013: 397–443.10.1016/B978-0-444-56330-9.00012-7Suche in Google Scholar

Rofer-DePoorter CK. A comprehensive mechanism for the Fischer-Tropsch synthesis. Chem Rev 1981; 81: 447–474.10.1021/cr00045a002Suche in Google Scholar

Rytter E, Holmen A. Deactivation and regeneration of commercial type Fischer-Tropsch Co-catalysts – a mini-review. Catalysts 2015; 5: 478–499.10.3390/catal5020478Suche in Google Scholar

Sadeqzadeh M, Hong J, Fongarland P, Curulla-Ferré D, Luck F, Bousquet J, Schweich D, Khodakov AY. Mechanistic modeling of cobalt based catalyst sintering in a fixed bed reactor under different conditions of Fischer-Tropsch synthesis. Ind Eng Chem Res 2012; 51: 11955–11964.10.1021/ie3006929Suche in Google Scholar

Saeidi S, Nikoo MK, Mirvakili A, Bahrani S, Amin NAS, Rahimpour MR. Recent advances in reactors for low-temperature Fischer-Tropsch synthesis: process intensification perspective. Rev Chem Eng 2015; 31: 209–238.10.1515/revce-2014-0042Suche in Google Scholar

Sarup B, Wojciechowski BW. Studies of the Fischer-Tropsch synthesis on a cobalt catalyst II. Kinetics of carbon monoxide conversion to methane and to higher hydrocarbons. Can J Chem Eng 1989; 67: 62–74.10.1002/cjce.5450670110Suche in Google Scholar

Shen WJ, Zhou JL, Zhang BJ. Intraparticle diffusion effects in Fischer-Tropsch synthesis I. Modeling of diffusion and reaction. J Nat Gas Chem 1996a; 5: 59–68.Suche in Google Scholar

Shen WJ, Zhou JL, Zhang BJ. Intraparticle diffusion effects in Fischer-Tropsch synthesis II. Effects of particle size, temperature and pore structure. J Nat Gas Chem 1996b; 5: 107–115.Suche in Google Scholar

Silveston PL, Hudgins RR, Adesina AA, Ross GS, Feimer JL. Activity and selectivity control through periodic composition forcing over Fischer-Tropsch catalysts. Chem Eng Sci 1986; 41: 923–928.10.1016/0009-2509(86)87176-7Suche in Google Scholar

Steynberg AP, Espinoza RL, Jager B, Vosloo AC. High temperature Fischer-Tropsch synthesis in commercial practice. Appl Catal A Gen 1999; 186: 41–54.10.1016/S0926-860X(99)00163-5Suche in Google Scholar

Storsæter S, Chen D, Holmen A. Microkinetic modelling of the formation of C1 and C2 products in the Fischer-Tropsch synthesis over cobalt catalysts. Surf Sci 2006; 600: 2051–2063.10.1016/j.susc.2006.02.048Suche in Google Scholar

Thiele EW. Relation between catalytic activity and size of particle. Ind Eng Chem 1939; 31: 916–920.10.1021/ie50355a027Suche in Google Scholar

Torres R, de Hemptinne J-C, Machin I. Improving the modeling of hydrogen solubility in heavy oil cuts using an augmented Grayson Streed (AGS) approach. Oil Gas Sci Technol 2013; 68: 217–233.10.2516/ogst/2012061Suche in Google Scholar

Torshizi HO, Mirzaei AA, Bayat MH, Sarani R, Azizi HR, Vahid S, Golzarpour HR. Kinetics studies of fused Fe-Co-Mn (ternary) catalyst in Fischer-Tropsch synthesis. J Environ Chem Eng 2015; 3: 2243–2252.10.1016/j.jece.2015.07.027Suche in Google Scholar

Trinh T-K-H, de Hemptinne J-C, Lugo R, Ferrando N, Passarello J-P. Hydrogen solubility in hydrocarbon and oxygenated organic compounds. J Chem Eng Data 2016; 61: 19–34.10.1021/acs.jced.5b00119Suche in Google Scholar

van der Laan GP, Beenackers AACM. Kinetics and selectivity of the Fischer-Tropsch synthesis: a literature review. Catal Rev Sci Eng 1999; 41: 255–318.10.1081/CR-100101170Suche in Google Scholar

van der Laan GP, Beenackers AACM. Intrinsic kinetics of the gas-solid Fischer-Tropsch and water gas shift reactions over a precipitated iron catalyst. Appl Catal A Gen 2000; 193: 39–53.10.1016/S0926-860X(99)00412-3Suche in Google Scholar

van Santen RA, Markvoort AJ, Filot IAW, Ghouri MM, Hensen EJM. Mechanism and microkinetics of the Fischer-Tropsch reaction. Phys Chem Chem Phys 2013; 15: 17038–17063.10.1039/c3cp52506fSuche in Google Scholar PubMed

Visconti CG, Ballova Z, Lietti L, Tronconi E, Zennaro R, Forzatti P. Detailed kinetic study and modeling of the Fischer-Tropsch synthesis over a state-of-the-art cobalt-based catalyst. In: Davis BH, Occelli ML, editors. Advances in Fischer-Tropsch synthesis, catalysts, and catalysis. Florida: CRC Press, Taylor and Francis Group, 2010; 16: 293–315.Suche in Google Scholar

Wang YN, Li YW, Bai L, Zhao YL, Zhang BJ. Correlation for gas-liquid equilibrium prediction in Fischer-Tropsch synthesis. Fuel 1999; 78: 911–917.10.1016/S0016-2361(99)00020-4Suche in Google Scholar

Wang YN, Xu YY, Xiang HW, Li YW, Zhang BJ. Modeling of catalyst pellets for Fischer-Tropsch synthesis. Ind Eng Chem Res 2001; 40: 4324–4335.10.1021/ie010080vSuche in Google Scholar

Wang YN, Ma WP, Lu YJ, Yang J, Xu YY, Xiang HW, Li YW, Zhao YL, Zhang BJ. Kinetics modelling of Fischer-Tropsch synthesis over an industrial Fe-Cu-K catalyst. Fuel 2003a; 82: 195–213.10.1016/S0016-2361(02)00154-0Suche in Google Scholar

Wang YN, Xu YY, Li YW, Zhao YL, Zhang BJ. Heterogeneous modeling for fixed-bed Fischer-Tropsch synthesis: reactor model and its applications. Chem Eng Sci 2003b; 58: 867–875.10.1016/S0009-2509(02)00618-8Suche in Google Scholar

Weisz PB, Hicks JS. The behaviour of porous catalyst particles in view of internal mass and heat diffusion effects. Chem Eng Sci 1962; 17: 265–275.10.1016/0009-2509(62)85005-2Suche in Google Scholar

Whitaker S. The method of volume averaging. Dordrecht: Kluwer Academic Publishers, 1999.10.1007/978-94-017-3389-2Suche in Google Scholar

Whitaker S. Conservation equations. In: Ho CK, Webb SW, editors. Gas Transport in porous media. Dordrecht: Springer, 2006: 71–120.10.1007/1-4020-3962-X_6Suche in Google Scholar

Wu J, Zhang H, Ying W, Fang D. Simulation and analysis of a tubular fixed-bed Fischer-Tropsch synthesis reactor with Co-based catalyst. Chem Eng Technol 2010; 33: 1083–1092.10.1002/ceat.200900610Suche in Google Scholar

Wu J, Sun Q, Zhang Z, Pang L. Diffusion and reaction model of catalyst pellets for Fischer-Tropsch synthesis. China Petrol Process Petrochem Technol 2013; 15: 77–86.Suche in Google Scholar

Yates IC, Satterfield CN. Intrinsic kinetics of the Fischer-Tropsch synthesis on a cobalt catalyst. Energy Fuels 1991; 5: 168–173.10.1021/ef00025a029Suche in Google Scholar

Zhan X, Davis BH. Assessment of internal diffusion limitation on Fischer-Tropsch product distribution. Appl Catal A Gen 2002; 236: 149–161.10.1016/S0926-860X(02)00301-0Suche in Google Scholar

Zimmerman WH, Bukur DB. Reaction kinetics over iron catalysts used for the Fischer-Tropsch synthesis. Can J Chem Eng 1990; 68: 292–301.10.1002/cjce.5450680215Suche in Google Scholar

Received: 2015-7-29
Accepted: 2016-5-20
Published Online: 2016-7-8
Published in Print: 2017-4-1

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