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Kinetics, Catalysis, and Reaction Engineering
PHENOL HYDRODEOXYGENATION OVER A REDUCED AND SULFIDED NiMo/#-#l2O3 CATALYST Chrysovalantis Templis, Constantinos Revelas, Anestis Papastylianou, and Nikos G. Papayannakos Ind. Eng. Chem. Res., Just Accepted Manuscript • DOI: 10.1021/acs.iecr.8b06465 • Publication Date (Web): 28 Mar 2019 Downloaded from http://pubs.acs.org on March 28, 2019
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Industrial & Engineering Chemistry Research
PHENOL HYDRODEOXYGENATION OVER A REDUCED AND SULFIDED NiMo/γ-Αl2O3 CATALYST
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Chrysovalantis C. Templis, Constantinos J. Revelas, Anestis A. Papastylianou, Nikos G. Papayannakos*
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Corresponding Author
School of Chemical Engineering, National Technical University of Athens, 9, Heroon Polytechniou Str., Gr-15780 Zografos, Athens, Greece.
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*Tel.: (+30) 210 7723239, fax: +30 210 772 3155. E-mail:
[email protected] (N.G. Papayannakos).
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The authors declare no competing financial interest.
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Abstract
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sulfided form was investigated. Crushed particles (0.165-0.315 mm) were employed to
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determine the intrinsic reaction kinetics in either case. The internal diffusion phenomena
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within the catalytic particle of commercial dimensions and forms were also studied and the
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phenol effective diffusion coefficient and effectiveness factor for both forms of the catalyst
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were determined.
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The sulfided form was active to phenol conversion at higher temperatures in comparison to
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the reduced form. As indicated from the data acquired by phenol, cyclohexanol and benzene
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hydrotreatment experiments, phenol hydrodeoxygenation over the reduced and sulfided
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NiMo/γ-Al2O3 catalyst follows both parallel pathways: the direct deoxygenation (DDO) and
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the step-wise hydrogenation (HYD). The step-wise hydrogenation (HYD) pathway is
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favoured under the tested conditions. In the presence of the reduced catalyst cyclohexanol
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and cyclohexane are the main products and the selectivity towards cyclohexanol is high at
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low temperatures. In the presence of the sulfided catalyst, cyclohexane was the main
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hydrotreatment product together with a small amount of benzene.
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Conflict of interest
Phenol hydrodeoxygenation over a commercial NiMo/γ-Al2O3 catalyst in reduced and
Keywords Hydrodeoxygenation, phenol, NiMo/γ-Al2O3, kinetics, internal mass transfer phenomena.
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1. INTRODUCTION
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Cellulosic biomass can be converted into transportation fuels through three major pathways:
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syngas production by gasification, bio-oil production by pyrolysis or liquifaction and
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aqueous sugar production by hydrolysis1.
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Bio-oil is considered as an alternative to petroleum-based fractions for the production of a
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wide range of fuels and high value-added chemicals. The major organic compounds of the
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bio-oils are oxygenates like acids, alcohols, ethers, ketones, aldehydes, phenols, esters,
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sugars, furans, and nitrogen compounds. The phenolic compounds (phenol, guaiacol and
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other substituted phenol compounds) are formed by decomposition of lignin. The
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penetration of bio-oil in the market of transportation fuels requires its upgrading to increase
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heating value, thermal stability, and reduce viscosity and the content of oxygenates. There
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are two possible ways to upgrade bio-oil1,2 : (i) treatment with zeolites at atmospheric
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pressure and high temperatures and (ii) catalytic hydrodeoxygenation (HDO) under high
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pressure. The latter is currently extensively examined as it is based on the well known
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hydrotreatment process of petroleum fractions and appears to be very effective for the bio-
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oil upgrading. Phenols are considered as model compounds of bio-oil oxygenates and they
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have received considerable attention because of their low reactivity in the HDO process3.
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Two main pathways have been reported so far concerning phenol hydrodeoxygenation: the
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direct deoxygenation (DDO) and the step-wise hydrogenation (HYD). Different reaction
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conditions or catalysts favor one of the two pathways4.
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In DDO mechanism, the carbon-oxygen bond breaks immediately leading to the formation
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of benzene and water i.e. oxygen is removed from the very first step, while the aromaticity
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of the molecule is preserved. Cyclohexane and/or cyclohexene can be formed with further
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hydrogenation of the aromatic ring. On the other hand, in HYD mechanism the consecutive
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hydrogenation leads to the saturation of the phenolic compound forming cyclohexanol
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and/or cyclohexanone. Again, depending on the level of hydrogenation, cyclohexene and/or
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cyclohexane can also be formed as final products.
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Various catalytic systems have already been reported in literature for phenol hydrotreatment.
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Sulfided NiMo/γ-Al2O35-9 and sulfided ΝiW/γ-Al2O36 catalysts have been tested. Reduced
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ΝiMo catalysts have been tested on supports γ-Al2O36,7, ΤiO27 and ΑC10. Monometallic Ni
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catalysts supported on SiO211-15, on HZSM-516,18, on Al2O312,14,17,18,19, on mixed Al2O3 and
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HZSM-516,18 have also been tested. 2 ACS Paragon Plus Environment
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Industrial & Engineering Chemistry Research
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The reported reaction temperature varried within the range 150-350 oC, the tested pressure
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varried within the range 1-100 bar, and for the studies using fixed beds the WHSV varried
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within the range 0.5-107.5 h-1.
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For the hydrodeoxygenation of phenol over Ni containing catalysts, the most commonly
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referred deoxygenated products in the studies are benzene, cyclohexene and cyclohexane.
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The oxygenated products are cyclohexanol and cyclohexanone. In some studies they
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coexist11,16, while in some others only cyclohexanol was detected17. Depending on the metal
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and substrate active sites more products have been reported. Methylcyclopentane production
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by isomerisation of cyclohexane is referred in literature6,7,20. Moreover, traces of C12
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bicyclic products and C18 tri-cyclic products, oxygenated or non oxygenated, such as
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cyclohexyl
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dicyclohexyl ether13 and diphenylether9 can be derived from alkylation of oxygenated and/or
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non-oxygenated products.
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The high activity of NiMo/Al2O3 in hydrogenation processes, especially at low
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temperatures, is reported by Gandarias et al.6 and Platanitis et al.7. Moreover, Platanitis et
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al.7 have noticed that over a lab made NiMo/Al2O3 catalyst, the phenol HDO activity is
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higher over the reduced form than the one exhibited using the sulfided form. In that study
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the reduced catalyst was tested in a stand-alone process while the sulfided form was tested at
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conditions of simultaneous HDO and HDS. Gandarias et al.6 have also reported that another
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NiMo/Al2O3 catalyst was less active in the sulfided state in comparison to the reduced state.
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Several researchers use pseudo-first-order kinetics to determine reaction constants as a
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means of assessing catalyst activity for phenol conversion7,11,21,22,23. Shin and Keane11,
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Viljava and Krause21 and Yang et al.22 report that the first-order consideration for phenol
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conversion showed good fitting to the experimental data. Platanitis et al.7 carried out phenol
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hydrotreatment experiments over NiMo on various substrates and assuming pseudo-first
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order kinetics for phenol conversion, they calculated activation energies in the range 47-104
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kJ/mol. Activation energies for the individual steps of the phenol hydrodeoxygenation
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reaction scheme for other catalytic systems are in the range 30-150 kJ/mol16,21,24. Bjelic et
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al.25-27 presented a microkinetic model for eugenol hydrodeoxygenation including various
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catalytic systems and the activation energies of the individual steps lies within the range 30-
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150 kJ/mol.
cyclohexane8,20,
biphenyl20,
cyclohexylbenzene20,
cyclohexylphenol8,
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To the best of our knowledge, kinetic studies including the possible routes for product
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formation over NiMo/γ-Al2O3 during phenol hydrotreatment do not exist. The special
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interest in NiMo/Al2O3 catalysts lies in the fact that they are widely available and used in the
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petroleum industry for hydrotreatment of light to heavy fractions, they are relatively cheap
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and they appear very active and attractive for HDO applications. The aim of this
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communication is to model the kinetics of phenol hydrodeoxygenation over a commercial
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nickel-molybdenum catalyst supported on γ-alumina, in both the reduced and the sulfided
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form. A reaction scheme that includes the detected products is proposed for each form of the
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catalyst and kinetic equations for the individual steps of the reaction scheme are provided.
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Moreover, the estimation of the diffusion effects in the commercial catalyst particles is
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presented, which allows the calculation of global reaction rates that can be incorporated in
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continuum models for reactor simulation, scale-up and follow-up studies. In this way, the
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calculation of product composition and yields will provide full information on reactor
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performance for any catalyst size and reactor scale for a wide range of operating conditions.
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The power law kinetic model is used to relate reaction rates, reaction conditions and species
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concentration. This type of kinetics allows accurate calculation of reaction rates and
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effectiveness factors and is suitable for reactor simulation and scale-up studies as well as for
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the study of the internal diffusion effects.
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2. Experimental
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The experiments were carried out in a mini scale unit. A reactor tube of 2.1 mm internal
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diameter, coiled in spiral form, was loaded with the commercial NiMo/γ-Al2O3 catalyst. The
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coils of the spiral reactor are horizontal with a small inclination 3-4 deg. When running
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experiments to determine the intrinsic reaction kinetics, the reactor was loaded with 0.25 g
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of crushed catalyst with dimensions in the range of 0.160-0.315 mm. The catalytic beds of
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crushed particles were diluted with inert ceramic granules of the same size with the crushed
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catalyst, with a volume ratio of catalyst to inerts 1 : 0.5. When running experiments to study
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the internal mass transport phenomena, the reactor was loaded with 0.31 g of 4-lobe catalyst
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particles, at their commercial dimensions, creating a spiral string bed28. The diameter of the
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circumscribed circle around the particle cross section was 1.2±0.1 mm, the lobe diameter
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0.49±0.03 mm and the mean particle length 2.7 mm. The string beds of the catalyst particles
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in their commercial dimensions were diluted with cylindrical ceramic particles of 1.5 mm in
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diameter by adding an inert particle in between of two catalyst particles. In all experiments
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the liquid and gas were introduced cocurrently in upflow mode. 4 ACS Paragon Plus Environment
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The typical commercial catalyst used contained 2.6% wt. Ni and 12.3% wt Mo. The catalyst
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specific surface area was equal to 185 m2/g calculated with the Brunauer-Emmett-Teller
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method. The total pore volume was equal to 0.61 cm3/g and the average pore size was equal
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to 12.3 nm.
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The liquid feed of the phenol hydrotreatment experiments consisted of 1% wt phenol diluted
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in n-dodecane. WHSV varied between 11 and 36 gfeed gcat-1 h-1. The experiments with the
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reduced catalyst were performed at three pressures 20, 30 and 40 bar and four temperatures
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within the range 130-170 oC. The experiments with the sulfided catalyst were performed
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under constant pressure 30 bar and within the temperature range 200-250 oC. In all cases,
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the H2 feed flow rates were high enough (gas to liquid flow rate ratio G/L>420 Nl/l) to
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ensure negligible external mass transfer effects and hydrodynamics effects. This has been
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verified by conducting experiments varying the G/L ratio from 150 Nl/l to 900 Nl/l, because
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this ratio is the controlling parameter of the two phase flow characteristics29,30. It was proved
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that for G/L>420 Nl/l conversion and selectivities were practically independent from G/L.
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Hydrotreatment experiments of the products benzene and cyclohexanol were also performed
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in order to investigate the reaction scheme for phenol hydrodeoxygenation over the
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employed catalyst. For the investigation of the matrix effect on phenol HDO,
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hydrotreatment experiments were also conducted using n-hexane as solvent.
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Standard experiments were repeated at regular time intervals for the determination of
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catalyst activity level. The analysis of liquid samples at steady state conditions was
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conducted by gas chromatography by means of a Shimadzu GC2010 gas chromatographer
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supplied with an FID detector and a chromatography column DB-5. The length of the
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column was 30 m and its diameter 0.25 mm. Another chromatograph, DANI GC 1000,
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supplied with an FID detector and a DB-624 column of 30 m in length and 0.32 mm in
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diameter was used for the analysis of benzene and cyclohexane.
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The non-sulfided catalyst was reduced before use with hydrogen at 10 bars and gas flow rate
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of 6 Nl/h. The thermo-program of reduction included an initial temperature increase from 20
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oC
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latter period.
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For the preparation of the sulfided catalyst form, the catalyst was initially dehumidified in
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situ under hydrogen flow rate of 1 Nl/h for 2 h at 100 °C and 30 bar. Then, the temperature
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was raised first from 100 to 300 °C at a rate of 20 °C/h and second from 300 to 340 °C at a
up to 350 oC with a rate of 45 oC/h, a period of 4 hours at 350 oC and cooling after the
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rate of 10 °C/h. Sulfidation was continued for 4 h at 340 °C. For all sulfidation phases, a
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hydrogen flow rate of 1-1.25 Nl/h and a liquid flow rate corresponding to WHSV 16 h-1
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were applied. The sulfur-containing liquid feed (1.5% wt. sulfur in n-dodecane) was spiked
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with Sulfrzol. All chemicals were of high purity (≥99%). Dodecane was supplied from Alfa
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Aesar, hexane and cyclohexanol were supplied from Merck, benzene was supplied from
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Lach-Ner, phenol, cyclohexene and cyclohexane were supplied from Chemlab. Hydrogen
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was of high purity (>99%).
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3. Results
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3.1 Reduced crushed NiMo/γ-Al2O3 catalyst
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3.1.1 Activity -Selectivity
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During phenol hydrodeoxygenation experiments over the reduced NiMo/γ-Al2O3 catalyst,
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the main products detected within the studied conditions are cyclohexane and cyclohexanol.
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Very small yields of cyclohexene (