Comparison of Lumping Approaches to Predict the Product Yield in a Dual Bed VGO Hydrocracker
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Transcript of Comparison of Lumping Approaches to Predict the Product Yield in a Dual Bed VGO Hydrocracker
INTERNATIONAL JOURNAL OF CHEMICAL
REACTOR ENGINEERING
Volume 9 2011 Article A4
Comparison of Lumping Approaches toPredict the Product Yield in a Dual Bed
VGO Hydrocracker
Sepehr Sadighi∗ Arshad Ahmad†
Mansoor Shirvani‡
∗Universiti Teknologi Malaysia, sadighi [email protected]†Universiti Teknologi Malaysia, [email protected]‡Iran University of Science & Technology, [email protected]
ISSN 1542-6580Copyright c©2011 The Berkeley Electronic Press. All rights reserved.
Comparison of Lumping Approaches to Predict theProduct Yield in a Dual Bed VGO Hydrocracker
Sepehr Sadighi, Arshad Ahmad, and Mansoor Shirvani
Abstract
In this research, to predict the product yields of a pilot scale VGO hydroc-racking reactor charged with mono functional hydrotreating and hydrocrackingcatalysts, two different four-lump models are developed. The first one, calledcombined bed model, is a simplex in which there is no boundary between hy-drotreating and hydrocracking reactions through the reactor. The second one,called dual bed model, is a rigorous model in which hydrogen consumption andhydrotreating reactions are included. In this way, the reactor is subdivided intotwo different layers, so the effect of hydrotreating reactions on the hydrocrack-ing section can be considered. Results show that the absolute average deviation(AAD%) of the yield prediction for the combined bed and the dual bed models are8.23 percent and 5.87 percent, respectively. The main reason for the lower averagedeviation of the dual bed model is its higher accuracy to predict the yield of gaswhich is also the major advantage of this approach. However, the simplicity of thecombined bed model can make it more applicable and attractive, especially whenhydrogen consumption as well as sulfur, nitrogen and aromatic specifications ofthe feed and products are not accessible.
KEYWORDS: hydrotreating, hydrocracking, lump kinetic model, hydrogen con-sumption, dual bed hydrocracking reactor
1. Introduction
Processing of heavy feedstock into high value products has interested refiners worldwide due to increasing demand of light oil fractions and decreasing reserves of low sulfur crude oils. With the consideration of profit margins, hydrocracking has gained interest because of being an appropriate option for upgrading of heavy feedstock into various products. Moreover, it is a process in a refinery which improves the quality and quantity of the refined petroleum products.
Among all the commercially proven technologies for hydrocracking, those using fixed-bed reactors in series charged with different functionalities are very favorable. But, the main disadvantage of fixed-bed reactors is the loss of catalyst activity over time as a result of catalyst deactivation which reduces drastically the length of run (Alvarez et al., 2008). Typical reactions which occur in hydrocracking are (i) hydrogenation of polyaromatics, sulfur and nitrogen containing compounds, and (ii) cracking of higher carbon number (cyclo)-alkanes to lighter fractions (Balasubramanian & Pushpavanam, 2008). During the hydrotrating process (HDT) a portion of the hydrogen, dependent to hydrodesulfurization (HDS) and hydrodenitrogenation (HDN) reactions, is consumed and most of heavy sulfur and nitrogen compounds are converted to the light products.
Kinetic modeling of the reactions occurring in a hydrocracker and estimation of the rate coefficients is a crucial step in its design. An accurate estimation of the rate coefficients will enable us to optimize and control the product yield distribution in a hydrocracker. Ideally, the kinetic model should take into account all elementary reactions which the different components in the feedstock undergo. However, the complexity of hydrocracking feed makes it extremely difficult to characterize and describe its kinetic at a molecular level (Ancheyta et al., 1999).
One way of simplifying the problem is to consider the partition of the species into a few equivalent classes, the so-called lumps or lumping technique, and then assume each class is an independent entity (Krambeck, 1991). The major lumping methods interested in hydrocracking are continuum theory of lumping and discrete lumping approaches. In the first method, the reactive mixture is considered to form a continuum mixture with respect to its properties such as boiling point, molecular weight, carbon number or chemical species (Basak et al., 2004; Elizalde et al., 2009). But, in the discrete lumping approach, the reaction network is reduced to the limited number of reactions among the lumped components. The lumps, based on compound types present in feedstock and products (e.g., lumps of diesel, kerosene, gasoline, etc.), are often defined by boiling point ranges. This approach is attractive for kinetic modeling of complex mixtures because of its simplicity (Ancheyta et al., 2005).
1Sadighi et al.: Lumping Model for a Dual Bed VGO Hydrocracker
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However, it should be mentioned that lumped kinetics have the following major disadvantages: (1) they are strongly dependant to feedstock and catalyst; (2) they are only valid for the range of studied operating conditions, and also (3) if bench-scale trickle-bed reactors are used for the experimentation, reaction kinetics will be affected by hydrodynamics and mass transfer processes. If any of those parameters is to be changed, then the model must be refitted on the basis of a new experimental program.
To make the lumped models more accurate, it is possible to choose as many lumps as possible. However, this may lead to a large number of model parameters (e.g., rate constants). So, less number of species, especially in the case of limited number of experiments, can make the model more acceptable.
According to discrete lumping approach, there are many researches in which hydrocracking models with three-lump (Yui & Sanford, 1989; Callejas & Martinez, 1999; Aoyagi et al., 2003), four-lump (Aboul-Gheit, 1989; Valavarasu et al., 2005; Sadighi et al., 2010d), five-lump (Ancheyta et al., 1999; Almeida & Guirardello, 2005; Singh et al., 2005; Sadighi et al., 2010c) and six-lump (Sadighi et al., 2010a; Sadighi et al., 2010b) partitions have been developed. Moreover, for the other processes such as catalytic pyrolysis of heavy oil (Meng et al., 2006) and fluid catalytic cracking (Chen et al., 2007), eight-lump kinetic models were presented.
In the present study, two kinds of discrete lumping models for a dual bed pilot scale hydrocracking plant have been compared together. The first approach is a simplified model which considers only hydrocracking reactions. So, it is assumed that the catalytic bed operates like a bi-functional catalyst; hydrocracking reactions can be occurred uniformly through the bed. The second one is a rigorous approach which needs complementary data from the hydrogen consumption as well as sulfur, aromatic and nitrogen contents of the feed and products. This strategy is according to the previous study (Sadighi et al., 2010d). But its equations are formulated here in detail to make it more applicable for being used in a mathematical model. To have a more realistic model and closer to the industrial scenario, the measured yields for estimating the required parameters are calculated on the basis of mass flow rate of fresh VGO feed.
2. Experimental
The device, catalyst, feed and operating conditions were described completely in the previous work (Sadighi et al., 2010d). The reactor was composed of four sections. The first part, having a length of 100 mm, was packed with inert SiC particles. This section was used to provide a uniform distribution of gas and liquid. The two following sections with a length of 355mm and 865 mm were
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loaded with 63.5cm3 hydrotrating and 152 cm3 hydrocracking catalysts, respectively. The last section was also contained with 50mm of inert (Figure 1). Because in the under study process, two mono functional zeolite based hydrotreating and hydrocracking catalysts were used, the reactor can be called a dual bed VGO hydrocracker.
Figure 1. Sections of catalytic reactor bed
In this study, two types of commercial hydrotreating and hydrocracking (zeolite-based) catalysts with the same size of industrial application were applied. The characteristics of HDT and HDC catalysts are presented in Table 1. Before charging the feed, both catalysts were heated up to 1300C, and also they were held at this temperature about 6 hr for drying. Then, it is sulfided with an appropriate agent according to the manual of the catalyst vendor.
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Table 1- characteristics of HDT&HDC catalyst
Property HDT HDC
Size & Shape 1/16” & Quadralobe 1/16” & Cylindrical
Color Green Brown
Bulk density (kg/m3) 750 850
BET Surface Area (m2/g) 186.56 199.46
Langmuir Surface Area(m2/g) 259.20 273.71
Average Pore Diam (A0) 89.09 69.14
Main Ingredients Mo, Ni, Ti Zr, W, Ni, Si, Al
The hydrocracking feed was prepared by blending of the fresh VGO and recycle feed (unconverted oil) taken from Isomax unit of a real refinery. The feed properties are shown in Table 2. Mixing ratio of fresh and recycle feeds were 83.3 vol% and 16.7 vol %, respectively.
Table 2- Properties of fresh VGO and recycle feed
Property Fresh VGO Recycle Feed
[email protected]°C 0.8777 0.8738
Distillation Range (vol%)
ASTM D1160 ºC ºC
IBP 329.7 287.8
10% 390.6 390.7
30% 423.2 430.1
50% 445.6 452.9
70% 475.1 478.3
90% 523.7 517.1
End point 567.1 561.3
Nitrogen (ppmwt) 800 200
Sulfur (wt%) 1.4 0.03
Aromatics (wt%) 34 14.5
Asphalt & Resin (wt %) <0.1 <0.1
The pilot scale experiments were carried out under the following process
conditions: (1) H2/HC=1357 Nm3/Sm3; (2) LHSV=0.8, 0.9 and 1.05 hr-1; (3) Temperature=360°C, 370°C, 380°C and 390°C, and (4) Pressure =146 bar. The pressure, the range of LHSV and H2/HC were selected according to the recommendation of the catalyst manufacturer.
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3. Modeling approach for the dual bed hydrocracking reactor This work considers 4-lump mathematical model, i.e., VGO, distillate, naphtha and gas to match main products (Table 3). The kerosene and diesel, also light and heavy naphtha are lumped together as distillate and naphtha cuts, respectively. Additionally, it is assumed that only VGO (as hydrocracking feed) consumes hydrogen to be cracked to lighter cuts. So, the total consumed hydrogen in hydrocracking section can be calculated on the basis of cracked VGO. Therefore, hydrogen can be included in the mass balance equations without creating high complexity. Figure 2 illustrates the process pathways associated with the mentioned strategy. Note that if all pathways of reactions are considered, the model will include twelve kinetic parameters which should be estimated by using experimental data.
Table 3. Average properties of hydrocracking product (Sadighi et al, 2010d)
Lump Sp.g @15°C IBP-FBP (°C)
Gas 0.35 40-
Naphtha 0.75 40-160
Distillate 0.823 161-370
VGO 0.89 370+
Figure 2. The complete 4-lump kinetic model
5Sadighi et al.: Lumping Model for a Dual Bed VGO Hydrocracker
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The following assumptions are considered in the development of the present models (Mohanty et al., 1991):
1- Hydrocracking is a first order hydrocracking reaction and since hydrogen
is present in excess, the rate of hydrocracking can be taken to be independent of the hydrogen concentration.
2- The pilot reactor operates under isothermal conditions. 3- A plug flow pattern exists in the trickle bed reactor. 4- Hydrogen feed is pure. 5- The petroleum feed and the products are in the liquid phase in the reactor. 6- The pilot unit is in steady state operation. 7- Catalyst activity does not change with time; therefore simulation is only
valid for start of run conditions. For each reaction, the kinetic expression is formulated as the function of
mass concentration and kinetic parameters ( 0k , E ). Based on the mentioned
assumptions, rate constants of the proposed models are as follows:
Vacuum gas oil or Feed ( F ): )exp(0 RT
Ekk Fj
FjFj
(1)
Note that j in Eq. 1 represents distillate ( D ), naphtha ( N ) and gas (G )
Distillate ( D ): )exp( ''0' RT
Ekk Dj
DjDj
(2)
'j in Eq. 2 represents naphtha ( N ) and gas (G ).
Naphtha ( N ): )exp(0 RT
Ekk NG
NGNG
(3)
In equations 1 to 3, T and R are the bed temperature and ideal gas constant, respectively.
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From Figure 2, it can be found that for converting VGO to the lighter products, hydrogen should be consumed for each path. Therefore, the reaction rates for these products can be described as follows:
Distillate ( DR ):
G
NjDDjFFDD CkCkR
'')1( (5)
Naphtha ( NR ): NGNGDDNFFNN CkCkCkR )1( (6)
Gas ( GR ): NNGDDGFFGG CkCkCkR )1( (7) In equations 5 to 7, shows the consumed unit mass of hydrogen per unit mass of converted VGO which is added to the molecular structure of products (distillate, naphtha and gas) during hydrocracking reactions.
3.1. Combined bed model
In this approach, the hydrogen consumption is neglected. It is obvious that during hydrocracking and hydrotreating reactions, hydrogen molecule is absorbed in the hydrocarbon structure, but sulfur and nitrogen are removed. According to the experimental data (Sadighi et al, 2010d), this assumption can create 1% error in the mass balance which can be considered negligible. So, the coefficient in equations 5 to 7 is assumed to be zero.
Additionally, it is assumed that hydrocracking and hydrotreating reactions are carrying out simultaneously through the reactor bed similar to a bi-functional hydrocracking catalyst. Therefore, there is no boundary between hydrotrating and hydrocracking reactions. The scheme of combined bed model is illustrated in Figure 3(A).
So, the reaction rates ( jR ) can be formulated as follows:
Vacuum gas oil reaction ( FR ): F
G
DjFjF CkR
(4)
7Sadighi et al.: Lumping Model for a Dual Bed VGO Hydrocracker
Published by The Berkeley Electronic Press, 2011
Figure 3. Schematic representation of the developed lumping models (A) Combined bed model (B) Dual bed model
3.2. Dual bed model
In this approach, the reactor is divided into two distinguished layer. In the first one, after carrying out the hydrotrating reactions (Table 4), the product is entered to the second layer. Therefore, the second step is only involved of hydrocracking reactions. The scheme of the dual bed model is illustrated in Figure 3 (B).
Before entering the products of the hydrotrating step into the hydrocracking one, it is imagined that by using two pseudo streams, H2S and NH3 are extracted from the hydrotrating products. So, they are not involved in the mass balance equations of hydrocracking section. Because these components are stable and also their flow rates are negligible, this assumption will not create a considerable error for the mathematical model. After hydrotrating reactions, to calculate the mass flow rate of feed, naphtha and distillate, equations 8 to 10 are formulated. Because the contents of sulfur and nitrogen in the product of the reactor are less than 50 ppm, they have been neglected.
))(1( 200AfAp
VGO
HNfSfffh XX
Mw
MwXXmm (8)
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)7.(.
32
0
0NHHNc
N
Nff
Nh MwMwMwMw
Xmm (9)
)2.(.
22
00
SHHScS
SffDh MwMwMw
Mw
Xmm (10)
In above equations, 0fm is the mass flow rate of the fresh VGO; 0
fhm , 0Nhm , 0
Dhm
are the mass flow rate of the purified VGO, naphtha and distillate leaving the hydrotreating section, respectively; SfX , NfX , AfX are the mass fraction of
sulfur, nitrogen and aromatics in the fresh feed, respectively;
SHNHHVGOScNcSN MWMWMWMwMwMwMwMw232
,,,,,,, are the molecular weight
of nitrogen, sulfur, nitrogen lumped component (quinoline), sulfur lumped component (4,6-DMBT), VGO feed (420), hydrogen, ammonia and hydrogen sulfide, respectively. Table 4. Major reactions in the hydrotreating of VGO (Sadighi et al., 2010d)
Reaction Lumped component Consumed hydrogen Products
Hydrodesulfurization 4,6-DMBT 2 moles per S atom Distillate & H2S Hydrodenitrogenation Quinoline 7 moles per N atom Naphtha & NH3 Hydrodearomatization di-aromatics 2 moles per arom. molecule VGO
The reactions in the hydrocracking step are according to equations 5 to 7;
but the coefficient is calculated by the following quadratic polynomial equation (Sadighi et al., 2010d).
LHSVTLHSVTLHSVT ..... 122
222
11210 (12) In this equation, T is the reaction temperature (K); LHSV is liquid hourly space velocity of the reacting stream through the bed (hr-1). Also, 0 is the intercept
coefficient, 1 and 2 are the linear terms, 11 and 22 are the squared terms and
12 is the interaction term (Table 5).
Table 5. Coefficient values for the hydrogen consumption
Variable 0 1 2 11 22 12
T.LHSV 3441.319 -10.762 -18.906 0.00854 5.452 -0.00858
9Sadighi et al.: Lumping Model for a Dual Bed VGO Hydrocracker
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3.3. Model development and parameter estimation
In order to model the reactor, a cell network is applied. All beds from the inlet to the outlet are divided into a number (Nl=200) of well-mixed cells which are grouped along the flow direction. Mixing only occurs within each cell and back mixing is not accounted for between the adjacent cells. The accuracy of this approach for the VGO hydrocracking process in trickle bed regime was confirmed in the previous work (Sadighi et al., 2010d).
To improve the accuracy of the developed model, the volumetric flow rate in the reactor ( ) is considered variable, and it is calculated according to the density of output stream of each cell. Therefore, the mass balance equation for each cell can be written as follows:
)()()()('..)1()1( iiCiViRiiC jcatjj (13)
In Eq. 13, j ranges from the fresh feed ( F ) to the gas (G ), and a negative sign indicates reactant (fresh feed or VGO).
l
bcat N
ViV )( (14)
)()(
0
i
mi
G
fjj
(15)
)().(0 iiCm jj (16)
G
Fjj
G
Fj j
j
m
m
i .)(
10
0
(17)
0
)().(
f
lljj m
NNCY
(18)
In above equations, j is density of lumps (Table 3); i is the number of cells
which ranges from 1 to 200; C is the mass concentration of lumps; is the
effectiveness factor; ' is the catalyst volume fraction; )(iVcat is the volume of
hydrocracking catalyst in each cell; bV is the volume of the bed; Nl is the number
of cells (200); 0
fm is the mass flow rate of fresh feed, and jY is the yield of each
lump in the product stream leaving the reactor. The effectiveness factor for cylindrical catalyst in trickle bed regime and the bed void fraction are 0.7 (Mills & Dudukovic) and 0.35, respectively.
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For parameter estimation, sum of squared error, SQE , as given below, is minimized:
2
1)( pred
jntN
n
measjn
G
FjYYSQE
(19)
In Eq.19, tN , measjnY and pred
jnY are the number of test runs, the measured and the
predicted yields, respectively. For the combined bed model, equations 1 to 7 and 13 to 18 should be
solved simultaneously by applying the following boundary conditions:
f
fm
0
)0( ; ffC )0( ; 0)0( DC ; 0)0( NC ; 0)0( gC (20)
But, for the dual bed model, equations 1 to 7 and equations 12 to 18
should be solved simultaneously by applying the following boundary conditions:
)0()0(
0
N
fjjhm
(21)
N
fjjhN
NhN
fjjhD
DhN
fjjhf
fh
m
m
m
m
m
m0
0
0
0
0
0
1)0(
(22)
)0()0(
0
fh
f
mC ;
)0()0(
0
Dh
D
mC ;
)0()0(
0
Nh
N
mC ; 0)0( gC (23)
To develop the model, Aspen Custom Modeler (ACM) programming
environment (AspenTech, 2004) is used. Then Eq.19 is minimized by sequencing NL2Sol and Nelder-Mead algorithm which are both existed in Aspen Custom Modeler software. NL2Sol algorithm is a variation on Newton's method in which a part of the Hessian matrix is computed exactly and a part of that is approximated by a secant (quasi-Newton) updating method. To promote convergence from a poor initial point, a trust-region is used along with a choice of model Hessian. Hence, the approximate region is found with NL2Sol; then to fine tune the parameters; Nelder-Mead method is used.
To evaluate the estimated kinetic parameters, absolute average deviation of predictions ( %AAD ) is calculated by using the following expression.
11Sadighi et al.: Lumping Model for a Dual Bed VGO Hydrocracker
Published by The Berkeley Electronic Press, 2011
100
)(
%1 2
2
t
tN
n measjn
predjn
measjnG
Fj
N
Y
YY
AAD (24)
Moreover, the goodness of fitting of developed models is checked with analysis of variance (ANOVA) using Fischer test with 99% probability.
4. Results and discussions At first for the combined bed model, twelve kinetic parameters, frequency factors and activation energies were estimated by using the experimental data. After estimating parameters and predicting yields, the AAD% of the model was 8.28% in comparison to the measured data.
In Table 6, kinetic constants and the rate order of reactions at the mean operating temperature (3750C) to the highest one (kDN or distillate to naphtha) are presented. It is found that for the combined bed model, the rate orders of converting VGO to naphtha (kFN) and distillate to gas (kDG) are significantly lower than the highest value (kDN). It means that these reactions can be ignored. After eliminating the low-reaction-rate pathways and re-estimating the parameters (Table 7), the AAD% of the reduced model was found to be 8.23%. It can be concluded that the model reduction can improve the accuracy of the yield prediction which is the similar scenario with respect to the previous works (Sadighi et al., 2010a; Sadighi et al., 2010b; Sadighi et al., 2010c).
From Table 7, it is obvious that apparent activation energies of VGO to middle distillate and gas are 14.97 kcal/mol and 7.32 kcal/mol, respectively. The reported ones by Aboul-Ghiet (1989) were about 13-17.5 kcal/mol, and 18-19 kcal/mol, respectively. It is thought that the lower estimated activation energy for hydrocracking of feed to gas in this work is due to the higher hydrocracking activity of zeolite type catalyst. Additionally, the estimated activation energy (Botchwey et al., 2004) for formation of naphtha from middle distillate in the low severity temperature regime (340 to 370 0C) was about to 8.8 kcal/mol. Moreover the reported value for hydrocracking of kerosene to heavy naphtha in an industrial hydrocracking process charged with amorphous catalyst was 7.43 kcal/mol (Sadighi et al., 2010 a). It can be concluded that the estimated activation energy of distillate to naphtha in this work (7.11 kcal/mol) is not far from the others.
The simplified reaction-path network for the four-lump combined bed model is shown in Figure 4.
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Table 6. Kinetic parameters for complete network of combined bed model
Frequency Factor (m3.hr-1.m3 total cat-1)
Activation Energy (kcal/mol)
Rate order
k0FD 3.49E+05 EFD 15.80 kFD 0.61
k0FN 2.44E+07 EFN 69.30 kFN 3.79E-17
k0FG 3.34E-01 EFG 2.10 kFG 0.024
k0DN 900.84 EDN 7.49 kDN 1
k0DG 2.48E+07 EDG 34.07 kDG 2.98E-05
k0NG 1.10E+00 ENG 0 kNG 0.41
Table 7. Kinetic parameters for reduced network of combined bed model
Frequency Factor (m3.hr-1.m3 total cat-1 )
Activation Energy (kcal/mol)
Rate order
k0FD 1.82E+05 EFD 14.97 kFD 0.62
k0FN - EFN - kFN -
k0FG 2.29E+01 EFG 7.32 kFG 0.03
k0DN 660.20 EDN 7.11 kDN 1
k0DG - EDG - kDG -
k0NG 8.33E-01 ENG - kNG 0.32
Figure 4. The reduced 4-lump kinetic network for the combined bed model After following again the described strategy for the dual bed model, it was
found that the AAD% of the complete and reduced approaches were 6.77% and 5.87%, respectively. The apparent kinetic constants of those are presented in Tables 8 and 9, respectively. Also, the reduced kinetic network of this strategy is depicted in Figure 5.
13Sadighi et al.: Lumping Model for a Dual Bed VGO Hydrocracker
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Table 8. Kinetic parameters for the complete network of the dual bed model
Frequency Factor (m3.hr-1.m3 HCR cat-1)
Activation Energy (kcal/mol)
Rate order
k0FD 6.72E+07 EFD 23.37 kFD 0.57
k0FN 1.04E+08 EFN 24.63 kFN 0.33
k0FG 0 EFG 13.08 kFG 0
k0DN 0 EDN 2.14 kDN 0
k0DG 6.90E+03 EDG 28.15 kDG 1.43E-06
k0NG 1.55E+00 ENG 0 kNG 1
Table 9. Kinetic parameters for the reduced network of the dual bed model
Frequency Factor (m3.hr-1.m3 HCR cat-1 )
Activation Energy (kcal/mol)
Rate order
k0FD 1.32E+07 EFD 21.25 kFD 0.59
k0FN 1.42E+10 EFN 31.02 kFN 0.32
k0FG - EFG - kFG -
k0DN - EDN - kDN -
k0DG - EDG - kDG -
k0NG 1.514 ENG - kNG 1
Figure 5. The reduced 4-lump kinetic network for the dual bed model It should be noted that the kinetic constants and the kinetic network of the
combined bed model (Table 7 and Figure 4) show the performance of hydrotreating and hydrocracking sections together. But the related ones for the
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dual bed model (Table 9 and Figure 5) only demonstrate the performance of the hydrocracking catalyst.
Therefore, it can be understood that in comparison to the combined bed approach, the dual bed one can predict the yield of hydrocracking reactor with lower AAD% about 2.36%. The brilliant point in this approach which can be understood from Table 9 is its requirement to only five kinetic parameters (frequency factors and activations energies) to predict twelve sets of test runs (three levels of LHSV and four levels of temperature). But, this approach needs complete information from hydrogen consumption as well as sulfur, nitrogen and aromatic contents of the feed and product. In contrast, combined bed model needs seven parameters to predict the yield of products with AAD % of 8.23. But it is a simplex in which no hydrotrating or hydrogen consumption data is needed.
In the previous works (Sadighi et al., 2010a), it was reported that the activation energies for both light and heavy naphtha to gas were about to 9 kcal/mol for a dual-functional amorphous hydrocracking-hydrotreating catalyst. But, from Tables 7 and 9, it can be concluded that in this range of operating temperature, the activation energy for hydrocarcking of naptha to gas is independent to temperature (ENG=0). The reason for this phenomenon is supposed to be higher ability of zeolite type catalysts for hyrocracking (Shimada et al., 1997). So, gas formation from naphtha may be influenced by the nature of catalyst, and it is independent to temperature within the operating range.
The AAD percentages for all lumps are presented in Table 10. It can be concluded that the predictions of the combined and dual bed models are close together and they are acceptable for all products except to the case of gas for the combined bed model. Additionally, in the Table 11, the ANOVA of both strategies has been presented. The positive point in this table is acceptable difference between the F-critical and the F-test of the proposed models.
Table 10. The AAD% for the different dual bed lumping models
Lump Combined bed (Completed)
Combined bed (Reduced)
Dual bed (Completed)
Dual bed (Reduced)
Gas 21.04 20.7 11.00 9.26
Naphtha 4.92 5.34 8.29 7.04
Distillate 5.33 5.11 4.87 4.34
Un.VGO 1.83 1.76 2.90 2.85
Ave. 8.28 8.23 6.77 5.87
15Sadighi et al.: Lumping Model for a Dual Bed VGO Hydrocracker
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Table 11. ANOVA results of the developed models
Combined bed
(complete) Combined bed
(reduced) Dual bed
(complete) Dual bed (reduced)
DF* of regression 11 6 11 4
DF* of residual 36 41 36 43
R2-adjusted (%) 99.944 99.974 99.916 99.976
F-value 1789.69 3865.29 1189.87 4193.26
F-critical (1%) 2.79 3.28 2.79 3.79
*DF is degree of freedom
Figures 6 to 9 show comparisons between the measured yields and the predicted ones. To evaluate the accuracy of the prediction, the corresponding deviation plot is also presented. The deviation error reported in these figures was calculated as follows:
100Pr
%
yieldMeasured
yieldedictedyieldMeasuredError (25)
As it was resulted from Table 10, close mappings between the measured
and predicted yields by using both approaches can be understood. Moreover, it can be found that deviations are acceptably distributed evenly around the zero; but in the Figure 6, more deviation for the gas lump can be found for the combined bed model.
Additionally, the deviation plot for the predicted gas by the combined bed model in the Figure 6 demonstrates that in most of temperatures and LHSVs, the dual bed model predicts lower yield for the gas lump in comparison to the measured data. It is supposed that this deviation is because of disregarding the reactions which can produce gas in the hydrotreating layer. Conversely, for most of temperatures and LHSVs, the combined bed model predicts higher values for the yield of gas. It is supposed that the main reason for this deviation is the consideration of gas producing reactions in all points along the catalytic bed. Because of lower ability of hydrotreating catalyst to produce gas than that of hydrocracking one, the model predicts more gas in comparison to the measured values. Therefore the yield of gas can be laid between the values predicted by the combined and dual bed models.
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Figure 6. Predicted yields (♦, ▲&●), measured yields (□, ∆ & ○) and deviation plots for the prediction of gas lump
17Sadighi et al.: Lumping Model for a Dual Bed VGO Hydrocracker
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Figure 7. Predicted yields (♦, ▲&●), measured yields (□, ∆ & ○) and deviation plots for the prediction of naphtha lump
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Figure 8. Predicted yields (♦, ▲&●), measured yields (□, ∆ & ○) and
deviation plots for the prediction of distillate lump
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Figure 9. Predicted yields (♦, ▲&●), measured yields (□, ∆ & ○) and deviation plots for the prediction of VGO lump
5. Conclusions It was demonstrated that the product yields of a pilot scale VGO-hydrocracker could be predicted with the AAD% of 5.87% by using a four-lump rigorous model approach, called the dual bed model. This model could predict the yield of gas, naphtha, diesel and residue with the AAD% of 9.26%, 7.04%, 4.34% and 2.85%, respectively. These deviations for 12 test runs (48 observations) in three levels of LHSV and four levels of temperature can be satisfying. But to develop such a
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model, the hydrogen consumption of the process was needed. Moreover, sulfur, nitrogen and aromatic content of the feed and product should be analyzed. In contrast, there was a simpler four-lump approach, called the combined bed model which was capable of predicting the yield of products with the AAD% of 8.23%. This model could predict the yield of gas, naphtha, diesel and residue with the AAD% of 20.7%, 5.34%, 5.11% and 1.76%, respectively. The enormous deviation for the gas lump can be the disadvantage of this model. But, the advantage of this model over the dual bed model was its simplicity because it only required product yields to tune the model parameters. 6. Nomenclature
6.a Notations AAD Absolute Average Deviation, %
C Mass concentration, kg/m3
D Distillate
E Apparent activation energy, kcal/mol
G Gas
k Reaction rate constant, m3.hr-1.m3 cat-1
0k Frequency factor, m3.hr-1.m3 cat-1
LHSV Liquid Hourly Space Velocity, hr-1 0m Mass flow rate, kg/hr
Mw Molecular weight
SMw Molecular weight of sulfur (32)
NMw Molecular weight of nitrogen (14)
N Naphtha
lN Number of cells (200)
tN Number of experiments
R Ideal gas constant, 1.987 kcal.kmol-1.K-1
jR Reaction rate of lump j, kg.hr-1.m3 cat-1
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T Temperature, K or R
bV Total Volume of bed, m3
catV Volume of catalyst per cell, m3
VGO Vacuum Gas Oil
X Mass fraction of lumps
Y Yield of products
6.b Greek letters
Consumed mass of hydrogen per mass of VGO
122211210 ,,,,, Coefficient values for the hydrogen consumption
' Catalyst void fraction
Effectiveness factor
Volume flow rate, m3/hr
Density, kg/m3
6.c Subscripts
Af Aromatic in feed
Ap Aromatic in product
'Dj Distillate to lighter lumps
Dh Diesel in the output stream of hydrotrating bed
fh VGO feed or residue in the output stream of hydrotrating bed
Fj Feed to lighter lumps
i Cell number j Distillate, naphtha and gas lumps
'j naphtha and gas lumps
2H Hydrogen
SH 2 Hydrogen sulfide
n Number of experiments
Nc Nitrogen lumped component
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Nf Nitrogen in feed
Nh Naphtha in the output stream of hydrotrating bed
3NH Ammonia
Sc Sulfur lumped component
Sf Sulfur in feed
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