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Original article
9 (
1_suppl
); S522-S527
doi:
10.1016/j.arabjc.2011.06.018

Thiophene hydrodesulfurization over CoMo/Al2O3-CuY catalysts: Temperature effect study

UER of Applied Chemistry, EMP, BP 17 Bordj El-Bahri, 16111 Algiers, Algeria
Petrochemical Synthesis Laboratory, Chemistry and Hydrocarbons Faculty, Université M’Hamed BOUGARA, 01, Independence Avenue, Boumerdes, Algeria

⁎Corresponding author. Tel./fax: +213 24 81 68 48. bou.hamada@gmail.com (Boudjema Hamada)

Disclaimer:
This article was originally published by Elsevier and was migrated to Scientific Scholar after the change of Publisher.

Peer review under responsibility of King Saud University.

Abstract

CoMo/γ-Al2O3-CuY catalysts are prepared by physically mixing CoMo/γ-Al2O3 catalyst with Cu-exchanged Y zeolite. The CuY zeolite is prepared by the solid state ion exchange technique. The thiophene hydrodesulfurization is performed in a fixed bed reactor at high temperature and atmospheric pressure. The results show that the presence of CuY zeolite particles in CoMo/Al2O3 catalyst can have a noticeable effect on both the conversion and product selectivities. An increasing zeolite loading in catalyst results in a decrease of the thiophene HDS activity. This decrease is probably caused by the formation of heavy compounds and the deactivation of the zeolite at high temperatures.

Keywords

Hydrodesulfurization
Thiophene
CoMo/γ-Al2O3 catalyst
CuY zeolite
1

1 Introduction

Today, the production of environment-friendly transportation fuels demands a reduction of sulfur contents below the level required by the regulations. The new environmental norms limit the sulfur concentration in gas oil to less than 10 wppm (Narlikar and Fu, 2010; Yang, 2003). These increasingly stringent regulations have allowed the hydroprocessing research community worldwide to join their efforts in order to obtain acceptable sulfur values in fuels. Thus, tremendous advances have been made particularly without changing drastically the processing conditions. Among the sulfur removal of petroleum feedstock processes, catalytic hydrodesulfurization (HDS) is identified as one of the most promising way to reduce sulfur compounds to the acceptable level. In this process, more sulfided catalysts that combine transition metal promoters such as Ni and Co with Mo/Al2O3 are used. An effective HDS process works with the use of heavy and residual distillates requires the use of catalysts with appropriate balance between cracking and hydrogenolysis functions (Narlikar and Fu, 2010; Yang, 2003; Dos Santos et al., 2009). The higher thermal stability of catalyst in extreme working conditions for a long time is also required. Many catalysts have been studied for sulfur removal at a temperature ranges from 473 to 773 K. The CoMo/Al2O3 catalyst is highly efficient in removing the most part of sulfur compounds (thiols, sulfides, and disulfides), but less efficient when used to remove thermostable aromatic derivatives of thiophene, benzothiophene and dibenzothiophene that strongly hinder the catalyst HDS activity (Yang, 2003; Dos Santos et al., 2009; Pour et al., 2010). Several studies have been made to design a new HDS catalyst by changing or modifying the support, the preparation technique and the active phase formulation (Pour et al., 2010; Homma et al., 2005). The use of hydrotreating catalysts supported on transition metals containing (Ag+, Cu2+, Ni2+) micro- and mesoporous materials reported an excellent performance on deep desulfurization (Yang, 2003; Gong et al., 2009; Hernandez-Maldonado and Yang, 2004).

The porous silicate-alumina materials are characterized by the higher surface areas than the traditional γ-Al2O3, but the major side effect is their rapid deactivation at a high temperature in the presence of reactive molecules (Delahay and Coq, 2002; Benaliouche et al., 2008). Recent studies showed that the addition of a small amount of HY zeolite to Al2O3 increases the HDS activity by 1.2 times compared with the Al2O3 supported CoMo catalyst (Navarro et al., 1999; Ren et al., 2008; Fujikawa, 2009). Noble metals, especially platinum (Pt), supported on zeolites showed also high and stable activity in HDS of thiophene (Kanda et al., 2009). The thiophene HDS catalytic activity of these zeolites is attributed to a combination of several factors: (i) enhanced adsorption of the reactant thiophene on these high specific surface area zeolites, (ii) hydrocracking due to high acidity of the zeolite substrate and, in the case of transition metals, (iii) an enhancement of hydrogenolysis reactivity over the metal (Topsøe et al., 1996; Navarro et al., 1999; Brooks, 1980). Thus, in our present study, we focused on studying the temperature effect on the catalytic activity of CoMo/Al2O3 in the presence of small amounts of CuY zeolites. In the HDS tests, the thiophene is used as a model compound.

2

2 Materials and methods

2.1

2.1 Catalysts preparation and characterization

Three bifunctional catalysts samples are prepared by loading a sulfided CoMo/γ-Al2O3 catalyst with a small amount of Cu-exchanged zeolites via a manual mechanical mixing. The industrial CoMo/γ-Al2O3 catalyst is provided by Procatalyse (MoO3 = 14%, CoO = 3%). The obtained catalysts noted as CoMo, CoMo1 and CoMo2 contain a zeolite loading (wt%) rate of 0, 10 and 20, respectively. Before the use of the CoMo/γ-Al2O3 catalyst, a mass of 4 g is dried at 673 K for 1 h, then sulfided ex-situ in a fixed bed reactor with 15% of H2S/H2 mixture at atmospheric pressure and at the same temperature for 4 h (heating ramp of 10 K/min). Finally, the sample is flushed in a nitrogen flow. The Cu-exchanged zeolite is prepared according to the solid state ion exchange technique (SSIE) (Benaliouche et al., 2011). Prior to the ion exchange, the H form of Y zeolite is obtained by heating the commercial NH4-Y zeolite (supplied by Zeolyst International, SiO2/Al2O3 = 5.2; Na2O = 0.2%) from room temperature to 773 K at 2 K/min in a dry nitrogen atmosphere. The sample is kept at that temperature for 6 h. After that, the obtained HY zeolite is thoroughly manually mixed with the appropriate amount of CuCl2 salt (supplied by Merck, purity ⩾ 99.8%). The calculated amount of CuCl2 salt is sufficient to produce the fully Cu-exchanged zeolite. After that, the obtained reactive mixture is heated at 873 K in a dry nitrogen atmosphere for 10 h. The chemical analysis of both Cu-exchanged zeolite and CoMo/γ-Al2O3 catalyst is performed by Inductively-Coupled Plasma spectrometer (Activa Jobin Yvon ICP-OES). The crystalline structure of the Cu-exchanged zeolite is examined by Philips X’pert PRO diffractometer. The powder X-ray diffraction (XRD) patterns are collected over a 2θ-range of 3–50° using Cu-Kα radiation (λ = 1.54030 Å). The porosity of catalysts is measured by adsorption and desorption of nitrogen at 77 K using a Quantachrome NOVA 3200 surface analyzer. The hydrogen temperature-programmed reduction (H2-TPR) is performed after activation by sulfidation of all catalysts at atmospheric pressure. First, the sulfide sample of 60 mg is loaded in a U-shaped quartz flow reactor of a conventional setup equipped with a thermal conductivity detector (TCD). After that, the sample is heated with a temperature program from room temperature to 1323 K (heating rate of 10 K min−1) under a gas flow (50 ml min−1) of H2/Ar mixture (5% H2). In such a way, the catalyst samples are reduced and the amount of consumed H2 is measured by a TCD detector. The amount of H2O produced in the reduction was removed by a cold trap placed before the TCD detector. These conditions are in accordance with the literature (Dos Santos et al., 2009; Brooks, 1980; Tanaka et al., 1996).

2.2

2.2 Catalytic tests reaction

The experiments for thiophene HDS are carried out at atmospheric pressure in a continuous flow fixed-bed reactor and at different temperatures (573, 593 and 613 K). Thiophene is introduced at a rate of 9.718 μmol/s into the reactor containing sulfided catalyst (about 60 mg) by flowing hydrogen (50 ml/min) through a thiophene trap cooled at 273 K. Products are analyzed on-line by using an HP Hewlett 5890 Series II gas chromatograph analyzer equipped with a flame ionized detector (FID). The reaction is conducted after the catalyst sample reached the desired temperature and until the stabilization of the reaction rate. Before HDS model reaction, all catalysts are sulfided under the same operation conditions cited previously in H2-TPR analysis.

3

3 Results and discussion

3.1

3.1 Characterization of catalysts

The results of chemical analysis and textural characterization of the catalysts are reported in Table 1. The external surface area and micropore volume are calculated using the t-plot method. The total surface area is calculated according to the BET model. The results show that the commercial CoMo/Al2O3 has a chemical composition of 2.42 wt% Co and 9.26 wt% Mo. It has a pore volume of 0.48 cm3/g and a surface area of 184 m2/g. These results are in concordance with those obtained in the literature (Homma et al., 2005; Rana et al., 2004). For Cu-exchanged zeolite, the results reveal that H cations are almost completely exchanged by Cu2+ and the exchange degree is estimated at about 92% (determined by ICP elemental analysis). The Si/Al ratios for both HY, and Cu-exchanged forms obtained are nearly equal. We notice that all textural parameters values of the HY zeolite (total pore volume, the microporous volume and the total surface area) decrease after ion exchange with copper. This behavior may be explained by the fact that zeolite pore access can be partially blocked when Cu ions are in large numbers at sites inside the cages, leading to a reduction in measured volume and total surface area (Benaliouche et al., 2008). In order to analyze the effect of both the ion exchange and the sulfidation operations on the crystalline structure of the HY and CuY zeolites, we present in Fig. 1, the XRD analysis of the parent HY zeolite and its Cu-exchanged form. We also made XRD measurements for CoMo/Al2O3 (spectrum not shown) but no appreciable changes are observed. The diffractrogram of the parent HY zeolite shows the characteristic peaks of the faujasite framework that closely matches those from the literature (Breck, 1974; Treacy and Higgins, 2001). This result indicates the highly pure and crystalline nature of the parent zeolite. For Cu-exchanged zeolites, the XRD profiles show similar characteristic peaks of HY zeolites with a very slight decrease in intensities. These results indicate that Cu2+ ions seem to be well dispersed in the zeolite framework and the structure integrity of Cu-exchanged zeolite is maintained after the ion exchange and sulfidation treatment. We notice the appearance of a significant diffraction lines at 2θ values of 44° and 46° for CuY and sulfided CuY zeolites, respectively. These results suggest the formation of a small amount of CuO (ICDD #00-005-0661) and Cu2S species (ICDD #00-053-0522). These observations may indicate that sulfidation of Cu-exchanged Y zeolites leads to the formation of sulfided Cu2+ and, probably, reduced Cu species.

Table 1 Chemical composition and textural parameters of catalysts.
Symbol Content of metals (wt%) Si/Al Pore volume (cm3/g) Surface area (m2/g)
Total pore Micropore BET External surface
CoMo Co Mo 0.480 0.003 184 178
2.42 9.26
HY Na Al 2.60 0.352 0.270 717 44
0.08 9.34
CuY Cu Al 2.64 0.273 0.203 401 27
9.08 8.74
The XRD patterns of parent HY zeolites (a), Cu-exchanged Y zeolites (b) and sulfided Cu-exchanged Y zeolites (c).
Figure 1
The XRD patterns of parent HY zeolites (a), Cu-exchanged Y zeolites (b) and sulfided Cu-exchanged Y zeolites (c).

3.2

3.2 Temperature programmed reduction (H2-TPR) analysis

The reducibility of Co, Mo and Cu sites in CoMo/Al2O3 catalyst and Cu-exchanged Y zeolite is studied by H2-TPR. These analyses are carried out on sulfided samples treated after thiophene HDS test. Fig. 2I and II, show the H2-TPR profiles of the CoMo/Al2O3 catalyst and Cu-exchanged Y zeolite compared with those of the fresh sulfided samples. As expected, TPR signal of CoMo/Al2O3 catalyst (Fig. 2I) gives two main peaks corresponding to H2S physisorbed gas (peak below 500 K) and the hardly reducible molybdenum species, respectively (peak above 900 K). The broad band between 600 and 900 K is attributed to both Co0 species and Co–Mo–S phase (Ribeiro et al., 2007; Resini et al., 2003). This phase is responsible for HDS activity. We observe also a slight shift of all peaks after thiophene HDS test. The first peak is slightly shifted to higher temperature whereas the second one to lower. These results may indicate the relative stability of the active phase on the catalyst after the catalytic treatment.

Temperature programmed reduction of CoMo/Al2O3 catalyst (I) and Cu-exchanged Y zeolites (II), before treatments (a) and after thiophene HDS test (b).
Figure 2
Temperature programmed reduction of CoMo/Al2O3 catalyst (I) and Cu-exchanged Y zeolites (II), before treatments (a) and after thiophene HDS test (b).

For Cu-exchanged Y zeolite, the H2-TPR pattern of the fresh sulfided (Fig. 2II(a)) sample is composed of three well-separated reduction peaks, at low temperatures (two peaks below 600 K) and high temperatures (one peak at 1168 K). The low-temperature peaks at 388 and 518 K can be attributed to the H2S physisorbed gas and to the easier reducible species (Cu2+ to Cu0 and/or Cu2+ to Cu+) respectively. According to literature, these species are mostly located on the accessible sites in the supercages and/or sodalite units of the zeolite (Ribeiro et al., 2007; Resini et al., 2003). The higher temperature peak observed at 1168 K seems to be much more intense than those cited previously and can be ascribed to the formation of metallic copper (Cu0) from Cu+ ions. These species mainly situated in the hexagonal prisms are more resistant to the reduction than those located in the supercages of the zeolite. The hardly reducible copper species are known to be stabilized by the negatively charged zeolite framework (Ribeiro et al., 2007; Cid et al., 1995). The H2-TPR profile obtained after the HDS reaction of thiophene (Fig. 2II(b)) reveals that the changes are more noticeable for high temperature reduction peaks. The intensity of this peak increases and shifts to low temperatures from 1168 to 748 K. We also note that the low temperature peaks overlapped to form one peak at 462 K with a shoulder reaching the maximum at 390 K. All these behaviors may be explained by both the reduction and the migration of more accessible Cu species from different site positions in zeolite during the HDS reaction of thiophene (presumably the migration of copper species from less accessible sites in hexagonal prism to the supercages of the zeolite). The effect of the oxidation of some copper species is not excluded. Similar results are reported by Cid, R., and al using Ni2+-exchanged USY zeolite (Cid et al., 1995).

3.3

3.3 Catalytic activity

The results of the thiophene HDS catalytic activity over CoMo, CoMo1 and CoMo2 catalysts are presented in Fig. 3. The values of thiophene conversion obtained after 16 h, show their dependence on both the HDS temperatures and the amount of CuY zeolites added to CoMo/Al2O3 catalyst. We observe that the thiophene conversion rate increases with the increase of temperature for all samples. As proposed by Topsøe et al. (1996), Brooks (1980) and Ribeiro et al. (2007), the HDS of thiophene compounds proceeds via two main pathways: (i) direct desulfurization (DDS) by the hydrogenolysis of the C–S bond and (ii) hydrogenation (HYD) of the aromatic ring followed by C–S bond hydrogenolysis. According to Topsøe et al. (1996), the increase of the thiophene HDS activity over CoMo/Al2O3 catalyst is attributed mainly to the formation of Co–Mo–S active site on the S-edge of MoS2, which favors the direct desulfurization (DDS) of thiophene because of the participation of sulfur vacancy. In our case, the CoMo sample showed a high catalytic activity at 573 K of about 46 and 54% greater than CoMo1 and CoMo2 samples, respectively. This threshold value is reduced to 45% and 38% for CoMo1 and CoMo2, respectively, when the temperature is increased to 593 K. After that, widening of the gap between the estimated conversion rates is obtained at 613 K. All these behaviors may be explained by the fact that the HDS activity of the CoMo catalyst contains a contribution of both the support and the cobalt-molybdenum sulfide phases (Co–Mo–S). However, for CoMo1 and CoMo2 catalysts, we have in addition to support and the Co–Mo–S phase contributions there are a new dual functions for HDS in which both the Cu species and the acid zeolite substrate contribute to desulfurize thiophene at reaction conditions. Indeed, the presence of strong acid sites in CuY zeolite pores may cause fast deactivation (poisoning of active sites) and coke formation in the CoMo1 and CoMo2 catalysts during the HDS of thiophene particularly at high temperatures. These species can block the active sites of the catalyst leading to the reduction of HDS activity (Caeiro et al., 2006; Carsten et al., 2008; Corma et al., 1996). On the other hand, the fact that the formation of sulfided Cu+ and the reduced Cu species (as indicated by XRD and TPR analyses) that migrated to the supercages of the zeolite causes a harder diffusion of reactant through pores of catalyst is not excluded. The reaction products in the HDS of thiophene over CoMo/Al2O3 catalysts mixed with various amounts of CuY zeolites are given in Table 2. We found that C4 hydrocarbons are formed as main reaction products in the HDS of thiophene for all catalysts. Small amounts of butane (product obtained by hydrogenation of butenes) are detected particularly for CoMo1 and CoMo2 samples. No cracking C1-C3 hydrocarbons products are detected. This indicates that CoMo/Al2O3 catalysts have low cracking activities for hydrocarbons. The selectivity results also reveal that the products formed by both hydrodesulfurization of thiophene (1-butene) and double-bond isomerization of 1-butene (trans- and cis 2 butene) are sensitive to the temperature changes particularly for samples containing zeolite loading (wt%) rate less then 10%. Indeed, the values obtained for CoMo catalyst reveal that the increase of temperature from 573 to 613 K leads to increase in the amounts of iso- and 1-butene products of about 2.5% (from 49.4% to 51.9%). Consequently, a decrease of the cis-2-butene from 29.5% to 27.9% is observed. The values obtained for trans-2-butene are nearly equal (about 21%). Nearly the same evolution is observed for CoMo1 at which the variation of hydrodesulfurization and isomerization products is estimated to be about 4.5%. However, for CoMo2 sample, only the value of butane decreases from 0.43% to 0.26% together with the temperature increase. Such behavior may be explained by the fact that the hydrogenation sites on CoMo2 catalyst are affected by the deactivation process.

Thiophene conversion over CoMo/Al2O3 catalysts after 16 h: (a) CoMo, (b) CoMo1 and (c) CoMo2.
Figure 3
Thiophene conversion over CoMo/Al2O3 catalysts after 16 h: (a) CoMo, (b) CoMo1 and (c) CoMo2.
Table 2 Products distribution over CoMo/Al2O3 catalysts in the HDS of thiophene at 573, 593 and 613 K, after reaction for 16 h.
Catalyst Selectivity of hydrocarbon (%)
n-Butane Iso- and 1-butene Trans-2-butene Cis-2-butene
573 K 593 K 613 K 573 K 593 K 613 K 573 K 593 K 613 K 573 K 593 K 613 K
CoMo 49.4 51.3 51.9 21.1 21 20.2 29.5 27.7 27.9
CoMo1 0.23 0.28 0.3 43.9 47.4 48.4 26.07 22.7 22.1 29.8 29.62 29.2
CoMo2 0.43 0.33 0.29 43.07 43.3 43.2 26.7 26.6 27.11 29.8 29.77 29.4

4

4 Conclusion

Successful preparations of bifunctional catalysts using a physical mixture of industrial CoMo/Al2O3 catalyst and Cu-exchanged zeolite (prepared by solid state ion exchange) are described in the present study. The crystalline structure of Cu-exchanged zeolite is maintained after the ion exchange and sulfidation treatment at high temperatures. Sulfidation of Cu-exchanged Y zeolite at high temperatures leads to the formation of both sulfided and reduced Cu2+ species. These species can migrate to the external surface layers and to supercages of the zeolites causing a harder diffusion of reactant through pores of zeolites. The thiophene HDS study of the bifunctional CoMo/Al2O3 catalysts at high temperatures reveals that the increase of CuY zeolites loading in CoMo/Al2O3 can have an influence on both the conversion and the product selectivities. Indeed, in spite of the synergetic effect between the metal sulfide particles and the acidic zeolite function, increasing CuY zeolite loading results in a decrease of the final thiophene HDS activity. The lower activity may be caused by a decrease in thiophene adsorption in the zeolite due to the coke formation in pores. The fact that poisoning of active sites reduces the atomic dispersion of Co, Mo, Cu sulfide species and consequently the attenuation of the thiophene hydrogenolysis over these metals is not excluded. The reaction products in the HDS of thiophene over CoMo/Al2O3 catalysts are mainly C4 hydrocarbons with n-butane as a minor product. The hydrodesulfurization and isomerization products are sensitive to the temperature changes particularly for samples containing zeolite loading (wt%) rate less than 10%.

References

  1. , , , , , . Micropor. Mesopor. Mater.. 2008;111:80-88.
  2. , , , . In situ FTIR studies of propene adsorption over Ag- and Cu-exchanged Y zeolites. Micropor. Mesopor. Mater. 2011 doi: 10.1016/j.micromeso.2011.04.040
    [Google Scholar]
  3. , . Zeolite Molecular Sieves. New York: Wiley; .
  4. , . Surf. Tech.. 1980;10:379-397.
  5. , , , , , , , . J. Mol. Catal.. 2006;255:131-158.
  6. , , , , , . Appl. Catal.. 2008;336:89-100.
  7. , , , , , . Appl. Catal.. 1995;125:169-183.
  8. , , , , , . Appl. Catal.. 1996;142:139-150.
  9. Delahay, G., Coq, B., 2002. Zeolites for cleaner technologies. In: Guisnet, M., Gilson, J.P. (Eds.), Catalytic Science Series, vol. 3. ICP, London, pp. 345–373.
  10. , , , , . App. Catal.. 2009;352:114-123.
  11. , . Top. Catal.. 2009;52:872-879.
  12. , , , , , . Fuel. Proc. Tech.. 2009;90:122-129.
  13. , , . J. Am. Chem. Soc.. 2004;126:992-993.
  14. , , , . Catal. Today. 2005;106:238-242.
  15. , , , , , . Top. Catal.. 2009;52:765-771.
  16. , , . Oxford Handbook of Nanoscience and Technology: Applications. Vol vol. 3. Oxford University press; .
  17. , , , , , , , . Fuel. Proc. Tech.. 1999;61:73-88.
  18. , , , , , . J. Nat. Gas Chem.. 2010;19:91-95.
  19. , , , . J. Catal. Today. 2004;98:67-74.
  20. , , , , , , . Appl. Catal.. 2008;344:175-182.
  21. , , , , , , , , , . J. Catal.. 2003;214:179-190.
  22. , , , , , , , , . Appl. Catal.. 2007;70:384-392.
  23. , , , . Catal. Today. 1996;29:209-213.
  24. , , , . Hydrotreating Catalysis: Science and Technology. Vol vol. 11. Berlin: Springer-Verlag; .
  25. , , . Collection of Simulated XRD Powder Patterns for Zeolites. New York: Elsevier; . pp. 17–374.
  26. , . Adsorbents: Fundamentals and Applications. Wiley-Interscience; . pp. 344–361
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