34 - utilization of triglycerides and related feedstocks for production of clean hydrocarbon fuels...
TRANSCRIPT
-
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
1/16
Utilization of Triglycerides and Related Feedstocks for Productionof Clean Hydrocarbon Fuels and Petrochemicals: A Review
Iva Kubickova David Kubicka
Received: 28 February 2010 / Accepted: 20 July 2010 / Published online: 5 August 2010 Springer Science+Business Media B.V. 2010
Abstract Catalytic deoxygenation of triglycerides and
related feedstocks for production of biofuels is reviewed inthis paper. Green diesel, triglyceride-based hydrocarbons in
diesel boiling range, is an attractive alternative to biodie-
sela product of transesterification of vegetable oils,
particularly due to its superior fuel properties and full
compatibility with current diesel fuels. Two basic approa-
ches to production of green diesel(i) hydrodeoxygen-
ation of triglycerides and related compounds over metal
sulfide catalysts and (ii) deoxygenation over supported
noble metal catalysts are thoroughly discussed from the
point of view of reaction conditions, catalyst composition
and reaction pathways and products. Furthermore, catalytic
cracking of triglycerides and related feedstocks over
microporous and mesoporous catalysts is reviewed as well.
It constitutes an interesting alternative to deoxygenation
using hydrotreating and noble metal catalysts as it does not
consume hydrogen. It provides a wide spectrum of prod-
ucts reaching from olefins to green gasoline and diesel.
Keywords Biofuels Vegetable oils Triglycerides
Deoxygenation Decarboxylation Hydrodeoxygenation
Noble metal catalysts Sulfided metal catalysts Zeolites
Introduction
Biofuels and their production and consumption have
become an inherent part of everyday life worldwide. Any
fuel of biological origin can be in principle called biofuel.
For the sake of clarity, we shall use the term biofuelexclusively for liquid transportation fuels produced from
renewable (biological) feedstocks in this review.
The use of biofuels has been promoted and supported in
the recent years, as it can contribute to (i) decreasing of CO2emissions from fossil energy sources, (ii) (renewed) devel-
opment of rural areas and (iii) partial reduction of the
complete dependence of world economy on the ever
declining fossil energy resources, particularly petroleum and
natural gas [17], the main feedstocks used for production of
transportation fuels. Due to the dispersed nature of emis-
sions originating from transportation and their increasing
amount [8], as a result of the continually wider spread of
road as well as air transport [3,4], these emissions are dif-
ficult to tackle. In addition to increasing the efficiency of the
internal combustion engines, constant enhancing of the fuel
quality is an indispensable tool. Biofuels play an important
role in the fuel quality improvement, as they can be denoted
clean fuels since they do not usually contain aromatics and
sulfur [2] and may improve some performance characteris-
tics of automotive fuels, e.g. octane number (bioethanol) and
cetane index (biodiesel) [1,7].
Biofuels are currently classified as the first generation
and the second generation biofuels [1, 3, 4, 7, 8]. Typical
first generation biofuels are bioethanol obtained by fer-
mentation of sugars (i.e. either from sugarcane or from
corn, sugar beet, wheat etc.) and biodiesel produced by
transesterification of vegetable oils with methanol [3,7,8].
Lignocellulosic bioethanol and fuels produced from bio-
mass-derived synthesis gas, i.e. mixture of CO and H2, are
usually called second generation biofuels [4, 7, 8]. Nev-
ertheless, the definition of the second generation biofuels is
not strict. Rather than to technological development/
maturity, it should refer to environmental benefits and
I. Kubickova D. Kubicka (&)
Department of Refinery and Petrochemical Research, Research
Institute of Inorganic Chemistry (VUANCH, a.s.), Areal
Chempark, Zaluz 1, 436 70 Litvinov, Czech Republic
e-mail: [email protected]
1 3
Waste Biomass Valor (2010) 1:293308
DOI 10.1007/s12649-010-9032-8
-
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
2/16
sustainability of different biofuels, i.e. to their greenhouse
gas emissions and cumulative energy-demand (fossil)
savings over the whole life cycle. Consequently, the same
biofuel, e.g. bioethanol, produced at two different locations
could be considered as second generation biofuel in one of
them and first generation biofuel in the other.
Owing to their chemical composition and physico-
chemical properties, triglycerides were used to fuel the firstdiesel engines (soybean oil in 1920s) [7]. After decades
dominated by the cheaper hydrocarbon-based fuels derived
mainly from petroleum and to a lesser extent from coal, a
renewed interest in alternative (renewable) feedstocks for
fuel production led inevitably to development of triglyc-
eride-based fuels and fuel components [1]. Since the high
density and viscosity prevent the direct use of triglycerides
as fuels for the modern diesel engines [7, 9], alternative
approaches have been sought. Until now, two basic con-
cepts have been applied industriallytransesterification
and hydrotreating [10].
The product of transesterification of vegetable oils(Fig.1), typically rapeseed, soybean and palm oil, with
methanol that complies with the appropriate quality stan-
dard (e.g. EN 14214 [11]) is called biodiesel or FAME
(fatty acid methyl esters). Biodiesel is along with bioeth-
anol the most important biofuel of the so-called first gen-
eration and it is mostly popular in Europe due to the
suitable climatic conditions for production of rapeseed and
the highest share of diesel-engine-driven cars in the world.
The production of biodiesel has been extensively reviewed
over the past years [1214]. The main advantages of this
process are its simplicity and mild reaction conditions
allowing small-scale production practically anywhere. On
the other hand, it suffers from several drawbacks, the most
important being the use of a homogenous catalyst and the
need of its neutralization and separation and production of
glycerol of a rather low quality as a by-product. The newly
developed process that uses a heterogeneous solid catalyst
can tackle these disadvantages as there is no need to neu-
tralize and separate the catalyst and consequently high
purity glycerol is obtained [15].
However, there exist other disadvantages of biodiesel
related to its fuel properties that cannot be easily dealt with.
The main drawbacks include low thermal and oxidation
stability in comparison with ordinary diesel fuel, which
limit the use of biodiesel in the modern diesel engines to
low concentration biodiesel-diesel mixtures (up to 7 vol%,
[11]). The efforts aimed at increasing efficiency of the
diesel engines led to application of higher injections pres-sures and smaller injection nozzles diameters. Under these
conditions biodiesel tends to polymerize and form deposits
on the nozzles that can cause their plugging. Consequently,
the safe use of neat biodiesel or high concentration bio-
dieseldiesel blends requires approval of the engine man-
ufacturer [16].
The chemical nature of biodiesel has to be changed to
deal efficiently with the stability issues discussed above.
Upgrading of triglycerides into hydrocarbons constitutes a
promising alternative to transesterification. Even though
the product of this upgrading could be in principle called
biodiesel, we shall call it green diesel in this review tostress its different chemical nature and avoid confusion as
the term biodiesel is widely accepted as a synonym for
fatty acid methyl esters.
Conversion of triglycerides into hydrocarbons necessi-
tates elimination of oxygen from the feedstock, i.e. deoxy-
genation. Deoxygenation, as a general term for oxygen
elimination, can refer to different chemical reactions. In the
case of triglycerides, these include hydrodeoxygenation and
hydrodecarboxylation (Fig.1) [17, 18]. Hydrodeoxygen-
ation consists of several consecutive reaction steps, in which
oxygen is removed in the form of water and the resultingn-
alkane has the same number of carbon atoms as the corre-
sponding fatty acid bound in the original triglyceride. Hy-
drodecarboxylation refers to a process where oxygen is
removed as CO2 by decarboxylation of fatty acid reaction
intermediate formed by hydrotreating of the corresponding
triglyceride. Consequently, the resulting n-alkane has one
carbon atom less than the corresponding fatty acid bound in
the original triglyceride [17, 18]. In contrast to hydrode-
carboxylation, decarboxylation proceeds only in carboxylic
CH2
CH
CH2
COO
COO
COO
R
R
R
+ CH3OHcat.
H2
cat.
H2
cat.
H2
cat.
CH3COO3 R
CH33 R
H3 R
H3 R
+
+
+
+
C3H8O3
C3H8
C3H83 CO2
+
+
+3 CO
6 H2O
3 H2OC3H8 +Deoxygenation
Biodiesel
Green diesel
1)
2)
3)
4)
Fig. 1 A simplified scheme of
the main reaction paths in
transformation of triglyceridesinto biofuels via catalytic
processes; (1)
transesterification, (2)
hydrodeoxygenation, (3)
hydrodecarboxylation, (4)
decarbonylation
294 Waste Biomass Valor (2010) 1:293308
1 3
-
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
3/16
acids and does not involve reaction with hydrogen [17,18].
Moreover, decarbonylation has been proposed as a plausible
reaction in transformation of triglycerides into hydrocarbons
(Fig.1) [19]. In general, these reactions could be denoted as
selective deoxygenation since oxygen is eliminated either in
form of water or CO2 and the molecular weight of the
product corresponds to that of the alkyl chains of fatty acids
bound in triglycerides. In addition to selective deoxygen-ation, oxygen can be eliminated from triglycerides by non-
selective deoxygenation, i.e. by their cracking that results in
formation of shorter chain oxygenates, hydrocarbons and
CO2. The hydrocarbons obtained in non-selective deoxy-
genation consist, besides alkanes, of naphthenes and aro-
matics, formed by secondary reactions.
Production of hydrocarbons from triglycerides is now
accomplished also commercially [20, 21] in a process
called NexBTL (Neste Oil, Porvoo, 29 170 kt/a) and
other production units have been announced [21]. Other
companies (e.g. Petrobras, Eni ?UOP) have announced or
patented production of green diesel (hydrocarbons) fromtriglycerides [2226]. Nevertheless, the production capac-
ity of biodiesel (ca. 21 Mt/a in Europe, with production ca.
7.7 Mt/a in 2008 [27]) is currently significantly larger than
the production of green diesel (0.34 Mt/a [28]), i.e. the
product of hydrotreating of triglycerides.
Recently, several reviews dealing with upgrading of
biomass to fuels and chemicals [1, 2932] and specific
reviews focusing primarily on biodiesel production [12,
13], deoxygenation in general [33] and upgrading of tri-
glycerides into biodiesel and/or green hydrocarbons [10,
34] have been published. In this contribution, we aim at
reviewing of deoxygenation chemistry and processes used
for upgrading of triglycerides and related feedstocks, such
as fatty acids, into green hydrocarbons (e.g. green diesel).
The review will be divided into three main sections based
on the nature of catalysts used. In the first part, deoxy-
genation of triglycerides and related feedstocks, mainly
fatty acids and their monoesters, over supported noble
metal catalysts, particularly Pd and Pt, will be discussed.
The second section will focus on the use of conventional
hydrotreating catalysts, i.e. NiMo, CoMo, NiW sulfides,
in triglycerides upgrading to hydrocarbons and the
activity and selectivity of these catalysts. The final part
will review the performance of micro- and mesoporous
molecular sieves in cracking of triglycerides to hydro-
carbon fractions.
Supported Noble Metal Catalysts
Supported noble metals, such as Pt, Pd, Ru, are a versatile
class of catalysts that are applied in different industrial
processes, the most important being various hydrogenations,
including selective hydrogenations of oxygenated interme-
diates to produce fine chemicals [31], and isomerization,
hydrocracking, cyclization and dehydrogenation of hydro-
carbons [35,36]. The supported noble metal catalysts were
proposed to be efficient deoxygenation catalysts [37] and
their activity and selectivity were studied comprehensively
by Murzin et al. [34,3846]. The group was even awarded a
patent covering the method of hydrocarbon production byusing noble metal catalysts [47,48].
Stearic acid was used as the principle model compound
to study deoxygenation using noble metal catalysts [38,39,
41] as it is a typical reaction intermediate in deoxygenation
of triglycerides [10, 17, 18, 38, 41] (Table1). A wide
variety of supported metal catalysts was investigated to
find the most promising metal-support combinations active
in deoxygenation of stearic acid [39]. Pt and Pd supported
on active carbon were the only catalysts providing signif-
icant yield of desired deoxygenation products. These con-
sisted almost exclusively of a mixture of C17hydrocarbons
among which n-heptadecane was the most abundantproduct. It was accompanied by 1-heptadecene and other
C17 isomers [38, 39]. In addition to Pt/C and Pd/C, Ru
supported on MgO exhibited under the same reaction
conditions (N2, 300C, 0.6 MPa) almost complete con-
version of stearic acid, however, formation of C17 hydro-
carbons was not observed. Instead, a condensation product
of two stearic acid molecules (a symmetrical ketone C35)
was formed (Fig.2) [39]. Besides Pd/C, Pd supported on
SBA-15 was shown to be active and selective in stearic
acid deoxygenation, in fact TOF on Pd/SBA-15 was higher
than that on Pd/C (0.72 vs. 0.13 s-1)[45], however in the
case of Pd/C the TOF is based on Pd loading rather than on
exposed Pd atoms. The other tested supported metal cata-
lysts gave much lower conversion of stearic acid (\50%)
under the above-mentioned reaction conditions [39].
Interestingly, formation of the symmetric ketone
(Fig.2) was observed on Pt and Pd supported on alumina,
suggesting that the support plays a crucial role in deter-
mining the selectivity as Ru/C provided predominantly C17hydrocarbons [39]. The formation of the ketone was
observed also in presence of hydrogen over Pt/Al2O3 and
Pt/TiO2where it was accompanied by formation of an ester
(octadecyl stearate, Fig.2) [49]. The formation of con-
densation products was ascribed to the catalytic role of the
oxide support under hydrogen-deficient environment, i.e.
when hydrogen spill-over could occur thanks to the pres-
ence of Pt, the formation of condensation products was
greatly suppressed [49]. Presence of vacancy oxygen sites
plays an important role in determining the selectivity
towards condensation products. It was shown that Pt sup-
ported on TiO2, i.e. a support having more oxygen vacancy
sites than Al2O3, favors the formation of symmetrical
ketones from acids and esters in comparison with Pt/Al2O3.
Waste Biomass Valor (2010) 1:293308 295
1 3
-
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
4/16
Moreover, these vacancies were reported to be responsible
for the significantly higher formation of C8hydrocarbons in
methyl octanoate deoxygenation over Pt/TiO2 in compari-
son with Pt/Al2O3. This is a consequence of higher CO
cleavage activity of Pt/TiO2 [49]. Further evidence of the
role of catalytically active oxide phase was provided, whena commercial NiMo/Al2O3, i.e. non-sulfided oxide-phase
catalyst, was used in hydrogen-rich environment. Hydro-
genation products were formed at the expense of dec-
arboxylation/decarbonylation products [50].
Owing to the low acidity of the used supports (C, SiO2,
Al2O3), cracking was negligible with Pt, Pd, Rh, Ir
(selectivity\5%), but it was pronounced when Ni catalysts
were used (selectivity[15%) [39]. Similarly, cracking was
virtually absent in deoxygenation of methyl stearate over
Pt/Al2O3[49]. It can be hence concluded that supported Pt
and Pd catalysts are efficient deoxygenation catalysts
yielding with high selectivity hydrocarbons that have one
carbon atom less than the corresponding fatty acid or fatty
acid part of an ester, i.e. the feed undergoes either decar-
boxylation or decarbonylation.
The effect of Pd dispersion on deoxygenation of a
mixture consisting of palmitic (59 mol%) and stearic acid
(40 mol%) was investigated using four 1 wt% Pd/C (sib-
unit) catalysts under standard deoxygenation conditions(300C, 1.7 MPa, dodecane solvent). Their Pd dispersions
were in the range 1872% [46]. The effect of Pd dispersion
was significant. The catalysts with the lowest and highest
dispersion showed the lowest initial deoxygenation rate
(TOF = 30 and 12 s-1, respectively) while the catalysts
with medium dispersion exhibited significantly higher ini-
tial reaction rates (TOF=76 and 109 s-1 for Pd disper-
sions 47 and 65%, respectively) [46]. These results suggest
that there is an optimum Pd crystallite size. The low
activity of highly dispersed Pd was attributed to strong
interaction of Pd crystallites with the support [46]. Fur-
thermore, the acidity/basicity of Pd/C catalysts (determinedby the pH measurement of catalyst slurry) was reported to
affect deoxygenation of ethyl stearate [41].
The important consequence of the decarboxylation/dec-
arbonylation reaction route proposed for supported noble
metal catalysts is that deoxygenation of fatty acids and/or
esters (including triglycerides) does, in principle, not require
presence of hydrogen atmosphere [38, 39]. This constitutes a
significant advantage over hydrogenation-based processes,
such as those using hydrotreating catalysts, due to the
Table 1 An overview of reaction conditions and catalysts used for deoxygenation of triglycerides and related feedstocks over supported noble
metal catalysts
Model compound Catalyst Reaction conditions Reference
Fatty acids
Stearic acid Pd/C He, H2Ar, H2; 300C; 1.7 MPa; SBR [38,41]
Caprylic acid Pd/C (NiMo/Al2O3) H2He; 300400C; 2.1 MPa; FBR [50]
Various acids (i.e. heptanoic, octanoic) Pd/SiO2 (Ni/Al2O3) H2, N2; 330C, atm.; FBR [37]Stearic, oleic, linoleic acids Pd/C He, H2He; 300C; 1.5 MPa; SBR [51]
Stearic acid Various catalysts N2; 300C; 0.6 bar; SBR [39]
Oleic, linoleic acids Pd/C Ar, H2Ar; 300360C; 1.54.2 MPa; SBR [43]
Esters
Ethyl stearate Pd/C He, H2Ar, H2; 300360C; 1.74 MPa; SBR [38,41]
He, N2, H2Ar, H2; 300320C; 0.61.7 MPa; SBR [38,41]
Methyl octanoate Pt/Al2O3; Pt/TiO2 H2He; 330C, atm.; FBR [49]
Methyl stearate Pt/Al2O3 H2He; 300350C; 0.7 MPa; SBR [49]
Triglycerides
Tristearin Pd/C, He, H2Ar, H2; 300360C; 1.74 MPa; SBR [38]
Tricaprylin Pd/C, (NiMo/Al2O3) H2He, 300400C, 2.1 MPa, FBR [50]
SBR semi-batch reactor, FBRfixed bed reactor
COOHR H
2
cat.CHOR H2O+
2 H2
cat.OHCH2R 2 H2O+COOHR
1)
2)
2
H2cat.
CH2COOR R
H2O
+
COOH2 R
RCOR + CO2 +
3 H2O
3)
4)
Fig. 2 A simplified scheme of partial deoxygenation reactions of
fatty acids; (1, 2) partial hydrogenation (deoxygenation), (3)
condensation, (4) esterification
296 Waste Biomass Valor (2010) 1:293308
1 3
-
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
5/16
suppressed hydrogen consumption. On the other hand, the
elimination of one carbon atom per one fatty acid in order to
form CO or CO2 results, however, in lower hydrocarbon
yield, on weight basis, as compared with the hydrogenation
processes. Even though high conversion of stearic acid and
its esters was observed under inert atmosphere (N2, He),
presence of hydrogen was found to be beneficial for catalyst
stability [38,49,51].It was demonstrated that when inert atmosphere (He) was
replaced by hydrogen atmosphere, the conversion of methyl
octanoate immediately increased to the levels observed
during deoxygenation carried out under hydrogen atmo-
sphere [49]. The fast deactivation in inert atmosphere was
ascribed to formation of heavy products and unsaturated
hydrocarbons that took part in oligomerization reactions
leading eventually to coke formation. Owing to fast satu-
ration of unsaturated intermediates under hydrogen atmo-
sphere, the fast catalyst deactivation was greatly diminished
[49]. Similar results were reported also for fixed-bed deox-
ygenation of stearic acid over Pd/C (360C, 1 MPa, Ar or5% H2in Ar) where stable conversion was achieved only in
presence of H2[52].The effect of hydrogen concentration in
the reaction atmosphere was studied in ethyl stearate deox-
ygenation [41]. With decreasing H2concentration (different
H2/He mixtures) the initial reaction rate decreased as did the
selectivity to n-heptadecane. At the same time, the selec-
tivity to stearic acid, i.e. an intermediate in ethyl stearate
deoxygenation, was increasing [41]. This suggests that ethyl
stearate yields primarily stearic acid which is subsequently
deoxygenated and that higher partial pressure of hydrogen is
beneficial for the subsequent reaction step. Since ethyl
stearate was reported to decompose to ethylene and stearic
acid in absence of catalyst at temperatures around 300C
[53], the positive effect of hydrogen could be attributed to
preservation of the catalyst activity due to hydrogenation of
unsaturated reaction intermediates as observed in methyl
octanoate deoxygenation [49].
In contrast to studies performed with esters of saturated
fatty acids, an optimum hydrogen concentration in the
reaction gas was reported for fatty acids [38,51]. In semi-
batch operation the conversion of stearic acid increased
when instead of pure hydrogen atmosphere a mixture
containing 5% H2 in Ar [38] or 10% H2 in He [51] was
used. Furthermore, the initial reaction rate of stearic acid
conversion was higher in He then in 10% H2 in He. Nev-
ertheless, under inert atmosphere the reaction rate dropped
significantly after ca. 10 min [51], presumably due to cat-
alyst deactivation as observed in the case of fatty esters
deoxygenation discussed above. It was proposed that the
inhibition of stearic acid deoxygenation at high hydrogen
partial pressure may be a consequence of competitive
dissociative adsorption of stearic acid and hydrogen [51].
The presence of adsorbed hydrogen leads to fast
hydrogenation of the adsorbed carboxylate, a product of
carboxylic acid dissociative adsorption, before it can
undergo decarboxylation [54].
The importance of hydrogen on deoxygenation of car-
boxylic acids was further confirmed by studies using dif-
ferent solvents [41,51]. It was proposed that some solvents
may act as hydrogen donors and consequently affect
deoxygenation. Dodecane was found to undergo dehydro-genation (conversion ca. 2%) over Pd/C under typical
deoxygenation conditions (300C, 1.5 MPa) and hydrogen
was formed [51]. Analogously, the initial rate of formation
of stearic acid from ethyl stearate in inert atmosphere was
higher in dodecane than in mesitylene [41]. The difference
could be explained by the different nature of the solvents
used. While dodecane can act as hydrogen-donor solvent,
mesitylene cannot. The initial rate of n-heptadecane for-
mation remained, however, unaltered by the solvent change
[41] suggesting that the initial deoxygenation was not
affected by hydrogen availability.
Unsaturated fatty acids and their esters are relevant probemolecules for deoxygenation (Table1) since majority of
fatty acids bound in naturally occurring triglycerides have at
least one double bond [55]. As expected, hydrogen plays an
important role in their transformation to hydrocarbons. It was
demonstrated that the double bond hydrogenation of oleic
and linoleic acid precedes their deoxygenation in hydrogen-
rich atmosphere [43,51]. Consequently,n-heptadecane was
the main reaction product. While the kinetics of stearic and
oleic acid deoxygenation were indistinguishable under 10%
H2in He, under He atmosphere deoxygenation of oleic acid
was significantly slower [51]. The authors propose that the
lower deoxygenation rate in absence of hydrogen is due to
cis-CC double bond adsorption [51], which may compete
with carboxylic group adsorption. Moreover, under hydro-
gen-deficient conditions, dehydrogenation of fatty acids
occurs yielding polyunsaturated acids and aromatics and
consequently resulting in faster catalyst deactivation [43].
The reported high selectivity to methyl stearate in methyl
oleate deoxygenation (300C, 1.5 MPa, Pd/C) under differ-
ent atmospheres (Ar, 5% H2 in Ar, H2) suggests that
hydrogen transfer plays an important role as well [43].
Deoxygenation of different fatty acids (C17C22) in
dodecane under argon (300C, 1.7 MPa, Pd/C) was shown
to be independent of their chain length; the initial deoxy-
genation rate of C17, C18 and C20 fatty acids was virtually
identical [56]. Same conclusion was reached also for
deoxygenation of palmitic and stearic acid under 5% H2in
Ar [46]. The different rate of deoxygenation observed in
the case of the C19 and C22 fatty acids was attributed to
their impurities, i.e. unsaturated fatty acids and phospho-
rus, respectively. The final conversion dropped from about
90% to approximately 20% when the mentioned impurities
were present [56].
Waste Biomass Valor (2010) 1:293308 297
1 3
-
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
6/16
Gaseous products formed and detected during deoxy-
genation of fatty acids could provide essential information
about its reaction mechanism over noble metal catalysts.
Nevertheless, due to facile reactions of CO, CO2, H2 and
H2O on catalyst surface, the observed composition of gas
phase is difficult to interpret unambiguously and several
proposals have been put forward [37, 39, 50, 51]. More-
over, the mechanism may be strongly affected by catalystchoice and reaction conditions, particularly reaction
atmosphere (inert or H2). The fundamental and yet not fully
understood issue concerns formation of hydrocarbons
having one carbon atom less than the original fatty acid.
Both decarboxylation and decarbonylation have been pro-
posed to explain formation of these hydrocarbons [37,39,
4951]. On the other hand, it is widely accepted that
hydrocarbons with the same carbon atom number as the
original fatty acids are produced by consecutive hydroge-
nation steps where the formation of reaction intermediates
(aldehydes and alcohols) is accompanied by formation of
water [39,4951].Carbon dioxide was detected as a major gaseous product
in deoxygenation of several carboxylic acids on Pd/SiO2.
Its formation was explained byab adsorption of primary
and secondary acids followed by the adsorbed CC bond
hydrogenolysis and hydrogen-assisted desorption of the
corresponding hydrocarbon and CO2 [37]. In contrast, no
significant amount of CO2 was obtained in deoxygenation
of caprylic acid under H2 atmosphere [50]. Bimolecular
reaction between adsorbed caprylic acid and hydrogen
yielding n-heptane, CO and water was proposed. It was
suggested that the initial hydrogenolysis of caprylic acid to
adsorbed n-heptane and formic acid is followed by fast
decomposition of formic acid to CO and water [50]. Par-
allel formation of CO2 and CO was observed in deoxy-
genation of oleic and stearic acids with CO2 being the
predominant gaseous product both under He and 10% H2in
He atmosphere (CO2/CO =89) [51]. The CO2 yield (in
He) was higher than expected from the yield of n-hepta-
decane. It was hence suggested that part of the primarily
formed CO underwent reaction with adsorbed water
(formed in decarbonylation) yielding CO2 and H2 [51].
When 10% H2in He was used as reaction atmosphere, only
n-heptadecane was observed in the liquid phase, i.e. no
heptadecenes were detected. However, the gas phase con-
tained both CO and CO2 [51]. This could be explained
either by hydrogenation of heptadecenes from decarbony-
lation [51] or by partial hydrogenation of CO2 from
decarboxylation [52].
Composition of gaseous products from triglyceride
deoxygenation is similar to that of fatty acid deoxygenation
as a facile hydrogenolysis of triglycerides yielding fatty
acids and propane precedes the actual deoxygenation [50].
In addition to hydrogenolysis, direct decarboxylation/
decarbonylation of methyl octanoate was suggested for its
gas-phase deoxygenation [49].
Supported Metal Sulfides Catalysts
Supported metal sulfides catalysts belong to the most
important industrial catalysts as they are used in hydro-treating and hydrocracking applications to remove sulfur
and nitrogen from petroleum fractions [57]. Moreover, the
first hydrotreating catalysts were developed for upgrading
of coal-derived liquids that contain, in contrast to petro-
leum feedstock, significant amounts of oxygenated com-
pounds [58]. It is therefore not surprising that they have
been suggested to be suitable catalysts for deoxygenation
of renewable feedstocks (Table2)[10,17,19,59,60]. In
fact, the up-to-date the only industrial application of tri-
glyceride deoxygenation relies on the use of supported
metal sulfide catalyst [20].
The reactivity of oxygenated compounds in deoxygen-ation over sulfided catalysts differs significantly. The most
challenging is deoxygenation of heterocyclic compounds
(furanes) and phenols that usually require reaction tem-
peratures above 350C [33, 61]. On the other hand, alco-
hols, aldehydes and ketones can be deoxygenated rather
easily, typically at temperatures below 250C[33,61]. All
these types of oxygenated compounds are present in bio-
oils and their different reactivity/stability makes the
deoxygenation of bio-oils very demanding [61,62]. On the
contrary, feedstocks containing triglycerides and fatty acids
are characterized by a rather uniform composition and
intermediate reactivity among oxygenated compounds.
Temperatures just below 300C are sufficient to accom-
plish their complete deoxygenation [61].
Early studies with model compounds (diethyl sebacate,
ethyl decanoate, decanoic acid) indicated that esters of
carboxylic acids are more prone to deoxygenation than
acids [17]. It was shown that deoxygenation of acids and
their esters involve two parallel reaction pathways(i)
hydrodeoxygenation and (ii) hydrodecarboxylation of
esters or decarboxylation of acids [17]. Similar product
distribution has been observed also for deoxygenation of
triglycerides [18,19,63] as well as other esters and acids
[6365]. The main products were, in all cases, n-alkanes
having either the same number of carbon atoms (hydro-
deoxygenation) as or one carbon atom less (hydro-
decarboxylation/decarboxylation) than the original acid,
regardless whether it was a free acid or acid bound in an
ester [1719,63]. The origin of triglycerides, in particular
their degree of unsaturation, has been shown to influence
significantly the product distribution; with increasing
degree of unsaturation the products contained higher con-
centrations of cyclic hydrocarbons, mainly alkylnaphthenes
298 Waste Biomass Valor (2010) 1:293308
1 3
-
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
7/16
[66]. The reaction conditions as well as the nature of the
catalyst were found to affect the product distribution, i.e.
the extent of hydrodeoxygenation and hydrodecarboxyla-tion/decarboxylation [17,18].
Under identical reaction conditions (280310C) an
increase in overall hydrogen pressure (from 0.7 to 7 MPa)
suppressed hydrodecarboxylation of triglycerides at the
expense of their hydrodeoxygenation [10,67]. On the other
hand, increasing reaction temperature (from 280 to 310C)
promoted hydrodecarboxylation over hydrodeoxygenation
at constant pressure (7 MPa) [10, 17, 18]. These findings
were also supported by thermodynamic calculations [68].
However, the influence of reaction conditions is greatly
affected by the choice of the catalyst. The effect of tem-
perature increase, i.e. promotion of hydrodecarboxylationover hydrodeoxygenation, has been found to be more
pronounced over NiMo than CoMo catalysts [17] while
NiW catalyst has shown significantly higher sensitivity to
reaction pressure changes than NiMo and CoMo catalysts
[10]. Moreover, it was demonstrated that the yield of
decarboxylation products from carboxylic acids exceeds
that of hydrodecarboxylation products from esters of the
corresponding acid [17].
In the case of triglycerides, fatty acids and alcohols were
observed as reaction intermediates [18] while in the case of
shorter chain esters, e.g. methyl heptanoate, in addition to
acids and alcohols, traces of aldehydes were found as well[64,65]. The formation of aldehydes is not surprising since
they are plausible reaction intermediates of carboxylic
acids hydrogenation to alcohols. Nonetheless, it does not
confirm the decarbonylation pathway in deoxygenation of
carboxylic acids and their esters, which has been proposed
by several researchers [19,69]. Under reaction conditions
of triglycerides deoxygenation (ca. 260300C, 17 MPa,
NiMo) the main oxygenated reaction intermediates, fatty
alcohols and acids, tend to undergo esterification, a
competing reaction to deoxygenation, and form corre-
sponding esters and water (Fig.2) [18, 70]. As water is
released during this reaction, it could be considered as apartial deoxygenation reaction since the ester undergoes
subsequently deoxygenation as any other ester.
Formation of n-alkanes in deoxygenation reactions is
accompanied by formation of water and CO2/CO, the pri-
mary products of hydrodeoxygenation and hydro-
decarboxylation/decarboxylation, respectively [18,60,63].
However, CO2 can undergo subsequent hydrogenation
under typical hydrotreating conditions leading to carbon
monoxide and ultimately methane [63], which increases
hydrogen consumption. In the specific case of triglycerides,
propane is formed during deoxygenation from the glycerol
backbone [18,63].In addition to standard hydrotreating catalysts (NiMo,
CoMo sulfides), the performance of individual sulfides (Ni,
Mo) has been investigated to understand in more detail the
role of individual components of hydrotreating catalysts on
their selectivity [18]. Salient differences in activity and
selectivity have been observed. The monometallic sulfide
catalysts were less active than the bimetallic ones, with Ni
sulfide catalyst being the least active. This is in agreement
with the activity trends reported for hydrodesulfurization
[57,58]. Hence, Ni acts as a promoter in the NiMo sulfide
catalysts during deoxygenation [18]. While NiMo sulfide
catalyst yielded both hydrodeoxygenation and hydrode-carboxylation products in conversion of rapeseed oil, Ni
sulfide catalyst yielded exclusively hydrodecarboxylation
products and Mo sulfide catalyst almost exclusively
hydrodeoxygenation products [18]. A higher selectivity of
Ni and Co sulfides to decarboxylation in comparison with
MoS2 was reported previously also by Landa and Weisser
[58]. This suggests that the different electronic properties
of the individual metal sulfides [71, 72] affect the
adsorption of triglycerides and consequently the preferred
Table 2 An overview of
reaction conditions and catalysts
used for deoxygenation of
triglycerides and related
feedstocks over supported metal
sulfide catalysts
BRbatch reactor, FBR fixed bed
reactor
Model compound Catalyst Reaction conditions Reference
Fatty acids
Decanoic acid NiMo/Al2O3 H2; 280C; 7 MPa; FBR [84]
Esters
Methyl laurate NiMoP/Al2O3 H2; 300C; 5 MPa; FBR [63]
Diethyl sebacate NiMo/Al2O3, CoMo/Al2O3 H2; 260300C; 7 MPa; FBR [84]
Methyl heptanoate NiMo/Al2O3, CoMo/Al2O3 H2; 250C; 1.5 MPa; FBR [64,65]
NiMo/Al2O3 H2; 250C; 7.5 MPa; BR
Vegetable oils
Rapeseed
oil/gas oil mixture
NiMo/Al2O3 H2; 350C; 4.5 MPa; FBR [63]
Rapeseed oil NiMo/Al2O3, CoMo/Al2O3,
Ni/Al2O3, Co/Al2O3
H2; 250310C; 0.77 MPa; FBR [18,67,74]
NiMo/Al2O3 H2; 310360C; 715 MPa; FBR [28]
Waste Biomass Valor (2010) 1:293308 299
1 3
-
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
8/16
deoxygenation pathway [18]. Moreover, unsupported MoS2catalysts with different degree of stacking, i.e. with dif-
ferent morphology, were shown to affect the selectivity in
hydrodeoxygenation of phenols. Hydrogenation was
favored by higher degree of stacking (exfoliated MoS2)
while lower degree of stacking favored hydrogenolysis.
The exfoliated MoS2 catalyst exhibited also the highest
activity (per edge Mo site) [73].The activity of hydrotreating catalysts is affected by the
nature of the support and its properties [57]. Several efforts
to understand the role of support on the activity and
selectivity metal sulfides catalysts used for deoxygenation
of triglycerides were reported [67, 74]. Specifically, mes-
oporous materials have shown great potential as catalyst
supports [75,76] and have been reported to provide some
advantages over conventional alumina support in hydro-
treating applications [77, 78]. Organized-mesoporous-
alumina-supported CoMo sulfided catalysts gave higher
conversion of triglycerides than industrial-alumina-sup-
ported CoMo under the same reaction conditions(250310C, 7 MPa) [74]. In contrast, SiMCM-41-sup-
ported CoMo sulfided catalyst showed significantly worse
performance than any of the alumina-based catalysts. The
yield of hydrocarbons was only ca. 40% for CoMo/Si
MCM-41 at 290C, while yields over[90% were achieved
when alumina-supported catalysts were used. It was sug-
gested that this is due to the differences in interactions
between the active phase and support originating from the
differences in support composition [67,74]. Incorporation
of Al in MCM-41 support enhanced the activity of the
CoMo sulfided catalyst in comparison with SiMCM-41-
supported CoMo catalyst; however the deoxygenation
activity remained lower than that of alumina supports [67].
Deactivation of the metal sulfide catalysts during
deoxygenation of triglycerides and related feedstocks is of
vast importance, particularly because these catalysts strive
for sulfur, which is in the typical triglyceride feedstocks
virtually absent, to avoid reduction of the sulfide phase and
hence to keep their activity [57,58]. Indeed, the conversion
of rapeseed oil over a NiMo/Al2O3 sulfided catalyst
decreased rapidly (from 100% to ca. 85% after 144 h time-
on-stream) in absence of hydrogen sulfide source [79]. On
the other hand, when dimethyldisulfide was added to
rapeseed oil, complete conversion and full selectivity to
hydrocarbons was preserved over long time-on-stream (ca.
250 h) [79]. Alternatively, mixing of triglyceride-rich
feedstock in a primary petroleum-derived feedstock, i.e.
sulfur containing fraction such as straight-run gas oil, could
be used to avoid the addition of dimethyldisulfide or
another hydrogen sulfide source. Despite co-processing, i.e.
upgrading of triglycerides together with petroleum frac-
tions, was demonstrated to be feasible [19,80,81], it was
argued that there are drawbacks that make it inferior to
stand-alone processing of triglycerides followed by their
blending to petroleum-derived diesel fuels [82,83]. These
include mainly reduced process flexibility as additional
issues have to be dealt with (e.g. sulfur content of the final
product, effect of water and carbon oxides on the catalyst
lifetime, separation of carbon oxides from the recycle gas,
etc.) [82, 83]. Consequently, most refiners seem to favor
stand-alone triglyceride processing [20,21,23,82,83].The stand-alone processing of triglycerides into diesel-
fuel-range hydrocarbons allows enhancing the fuel quality
as the primary green diesel has poor cold flow properties
[28] and cannot be therefore used directly in diesel fuel
blending, but in low blending concentrations. It has been
demonstrated that cold-flow-properties additives are inef-
ficient at as low concentration of n-alkanes (obtained by
triglyceride hydrotreating) in diesel fuel as 5% [28]. Other
properties of the green diesel, such as density, cetane
index, sulfur and aromatics content, are superior to those of
conventional diesel fuel [28, 80, 81]. Consequently, mild
isomerization would suffice to convert the triglyceride-hydrotreating product into an excellent diesel-fuel blending
fraction. In fact, this is implemented in the NexBTL and
Ecofining processes [20,21,23,26].
While hydrogen sulfide helps in preserving the activity of
hydrotreating catalysts during deoxygenation, it may also
interfere with deoxygenation itself. The effects of hydrogen
sulfide, ammonia and water on deoxygenation of various
oxygenated compounds were studied in detail [64,8486].
Water inhibited the rate of hydrodeoxygenation and
hydrodecarboxylation of esters only slightly, but it supported
hydrolysis of esters to corresponding acids. Consequently,
the overall conversion of diethylsebacate was not increased
due to water addition [84]. In contrast, the addition of water
was reported to decrease conversion of methyl and ethyl
heptanoate (ca. 510% decrease in conversion as a result of
addition of 5000 ppm H2O) [85]. Interestingly, inhibition of
hydrogenation reactions by water, as showed by the decrease
of the molar ratio of saturated-to-unsaturated hydrocarbons,
was observed for NiMo, but not for CoMo catalyst [85].
Ammonia exhibited a strong inhibition effect both on
hydrodeoxygenation as well as hydrodecarboxylation, but
the inhibition of the hydrodecarboxylation was more pro-
nounced [84]. In contrast to ammonia and water, hydrogen
sulfide promoted deoxygenation of esters over both NiMo
and CoMo catalysts [64, 84, 86]. From the two principal
deoxygenation pathways, primarily hydrodecarboxylation
was promoted by hydrogen sulfide [84, 86]; the hydro-
deoxygenation route was affected only slightly [84]. These
observations were explained by the increase in density of
Brnsted acid sites of the sulfide phase as a consequence of
H2S addition [84]. Furthermore, the addition of hydrogen
sulfide resulted in the formation of sulfur containing prod-
ucts, namely thiols and sulfides, during deoxygenation of
300 Waste Biomass Valor (2010) 1:293308
1 3
-
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
9/16
alkyl heptanoates [64]. It is obvious that particularly the
involvement of hydrogen sulfide in deoxygenation is rather
complex as it takes part in the reactions, affects the catalyst
acidity and hence its selectivity, and protects the catalyst
from desulfurization and its subsequent deactivation.
Having covered the main aspects of triglycerides and
related feedstocks transformation into hydrocarbons over
sulfided hydrotreating catalysts, the issue of the mecha-nism of this transformation remains to be addressed.
There is agreement that two parallel pathways play an
important role in deoxygenation of fatty acids and their
esters over sulfided catalysts, namely hydrodeoxygenation
and decarboxylation/decarbonylation [10, 1719, 63, 65,
66, 69]. However, their details are not fully understood,
particularly the formation of fatty acids that have been
identified as reaction intermediates [17, 18, 66, 69]. Gusmao
has proposed initial degradation of triglyceride to two fatty
acid molecules, a ketene and acrolein. The latter two inter-
mediates are, however, very reactive under hydrotreating
conditions and undergo fast hydrogenation [69]. Conse-quently, the proposed mechanism is hard to prove.
In deoxygenation of methyl heptanoate, hydrolysis was
proposed to be responsible for formation of carboxylic acid
as reaction intermediate since formation of methanol was
observed [65]. Due to absence of water in the feedstock and
rapid formation of heptanoic acid, occurrence of acid-cat-
alyzed hydrolysis is questionable. It was therefore sug-
gested that alkaline hydrolysis could take place as a result
of attack of OH- or SH- group on the carboxylic group of
the ester [65]. Nevertheless, glycerol formation, which
should be an intermediate in this reaction route, has not
been reported in deoxygenation of triglycerides. On the
other hand, fatty alcohols have been found to be reaction
intermediates of triglycerides transformation [18], i.e. it is
plausible that glycerol or other C3 alcohols could exist
under hydrotreating conditions. In fact, propyl esters of
fatty acids have been identified among triglyceride deox-
ygenation products [18].
Alternatively, fatty acids could be also formed by
hydrogenolysis of CO bond, which has been recently
reported in deoxygenation of tricaprylin over Pd/C and,
more importantly, over NiMo/Al2O3 (even though non-
sulfided) [50].
The fatty acid intermediates undergo hydrodeoxygen-
ation (total hydrogenation) yielding water and decarbox-
ylation/decarbonylation resulting in formation of CO2 and
CO [10,1719,63,65,66,69]. Under typical hydrotreating
conditions, subsequent reactions involving CO2 hydroge-
nation to CO (reversed watergas-shift reaction), CO2 or
CO hydrogenation to methane (methanization) and reaction
of CO with water to CO2and H2(watergas-shift reaction)
have to be considered. Consequently, it is difficult to
determine whether carbon oxides are formed via
decarboxylation or decarbonylation of fatty acids [63] or
both. Furthermore, the origin of hydrodeoxygenation and
decarboxylation activity of hydrotreating catalysts is also
not fully understood. Some results suggest that it could be a
consequence of different properties of individual metal
sulfides since NiS was found to yield selectively hydrod-
ecarboxylation products while MoS2 yielded almost
exclusively products of total hydrogenation (hydrodeoxy-genation) [18].
Acidic micro- and mesoporous molecular sieves
catalysts
Zeolites belong to the most important industrial catalysts,
particularly for production of clean fuels [35,36,87,88]. In
particular, tunable acidbasic properties, easy modification
by ion-exchange and molecular sieving properties have
contributed to wide-spread industrial use of zeolites [88].
Moreover, extensive research of zeolites and related mate-rials leads to discoveries of new structures and new potential
commercial applications [88]. It is hence not surprising that
they were suggested for upgrading of vegetable oils into
biofuels [8993]. Catalytic cracking using zeolites resulting
in oxygen elimination from the products can be considered
as unselective deoxygenation. It does not require hydrogen,
which is significant advantage over deoxygenation using
hydrotreating catalysts. Furthermore, unselective deoxy-
genation differs from the selective processes using sup-
ported noble metals or hydrotreating catalysts by the nature
of products. While the selective deoxygenation processes
provide almost exclusivelyn-alkanes with minimum loss of
carbon atoms, products of the unselective deoxygenation
include, in addition ton-alkanes, aromatics, naphthenes and
iso-alkanes having a broad distribution of molecular
weights. The broad molecular-weight distribution of prod-
ucts can be regarded as a disadvantage in comparison with
the selective processes since more complex downstream
treatment of the products is necessary in order to use all
products efficiently.
Catalytic cracking of vegetable oils and related feed-
stocks was usually investigated at temperatures in the range
350550C (Table3) under atmospheric pressure in the
presence of alumina [9496], zeolites [89, 91, 96104],
amorphous aluminosilicates [91, 96, 101], mesoporous
molecular sieves [92, 102, 105, 106], micro/mesoporous
materials [93,103,107], aluminophosphates [101,108] and
sulfated zirconia [109,110]. In addition to acidic catalysts,
the performance of basic oxides, such as MgO and CaO
was studied as well [94,96]. The use of basic catalysts is
together with thermal cracking and pyrolysis of triglycer-
ides out of the scope of this paper. Main products of acidic
catalytic cracking of vegetable oils are hydrocarbon gases
Waste Biomass Valor (2010) 1:293308 301
1 3
-
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
10/16
(C3C5), so-called organic liquid product (OLP, i.e. mix-
ture of aliphatic and aromatic hydrocarbons with traces of
oxygenates) and coke [89,91]. Oxygen is typically elimi-
nated as carbon oxides and water [89,91,96]. The organic
liquid product (OLP) consists mainly of gasoline and diesel
fractions [89,91,96]. The yield of OLP, which is desired
for potential biofuel applications, depends predominantly
on the density and strength of Brnsted acid sites of the
cracking catalysts.
Typically, the yield of OLP decreases with increasingconcentration and strength of acid sites that support over-
cracking leading to gaseous products [98]. For example,
enhanced yields of gasoline and kerosene at the expense of
gases and diesel were achieved while increasing of Si/Al
ratio of HZSM-5 from 50 to 400. Concurrently, the aro-
matics content of OLP decreased from about 52 to 35 wt%
and only small yields of coke (\2 wt%) were formed
[102]. Analogously, amorphous silicaalumina and MCM-
41 gave high yield of OLP (up to 65 wt%), which was
however accompanied by coke formation (912 wt%) [98,
102]. The formation of coke contributing to lower yields of
OLP could be suppressed by addition of zeolites [98].Owing to their pore dimensions, large molecules cannot
enter their pore system and, more importantly, cannot be
formed in the pores and cause thus their blockage. Fur-
thermore, the yield of OLP can be affected by reaction
conditions, i.e. with increasing reaction temperature and
residence time the yield of OLP for a given catalyst
decreases, e.g. due to an increase in temperature from 450
to 500C the yield of OLP dropped from 54 to 40 wt% over
HZSM-5 [98].
HZSM-5 zeolite has been the most extensively inves-
tigated zeolite for application in catalytic cracking of tri-
glycerides [89,91,97,98,102,104]. It is more active than
zeolites USY and Beta that deactivate much faster [89].
Similarly, silicoalumino-phosphates, i.e. another group of
microporous solids, exhibited significantly lower activity
than HZSM-5 [108]. For example, the yield of OLP was
54 wt% at 450C and 3.6 h-1 over HZSM-5, but only
36 wt% over SAPO-5. This was assigned to the fast
deactivation of SAPO materials by coking [108] but couldbe also caused by the lower density and strength of
Brnsted acid sites in these catalysts. Modification of
HZSM-5 by potassium [99] and platinum [100] led to
lower density of acid sites in ZSM-5 and consequently
lower activity in cracking of triglycerides.
As a result of strong acidity and unique pore dimensions
and architecture of HZSM-5, high yields of aromatic
hydrocarbons (8095 wt% of OLP), mainly benzene and
toluene, were obtained in the organic liquid product (OLP).
In contrast, mildly acidic amorphous silicaalumina pro-
vided OLP containing significant concentrations of aliphatic
hydrocarbons (1030 wt% of OLP) in addition to aromatics(2550 wt% of OLP) [98]. However, C6C9aromatics were
also the main hydrocarbons present in OLP when SAPO-5
and SAPO-11, i.e. mildly acidic microporous silicoalumi-
no-phosphates, were used. In contrast, MgAPO-36, i.e. a
non-acidic alumino-phosphate, provided aliphatic hydro-
carbons in concentrations similar to those of aromatics [91].
It clearly shows the importance of densityof acid sites as well
as of their strength. This was also demonstrated by studies
using potassium-loaded ZSM-5 [99]. Apart from decreased
Table 3 An overview of reaction conditions and catalysts used for deoxygenation of triglycerides and related feedstocks over microporous and
mesoporous catalysts
Model compound Catalyst Reaction conditions Reference
Fatty acids
C12C24 fatty acid mixture HZSM-5, composite MCM-41/HZSM-5 400450C, atm.; FBR [93]
Esters
Methyl octanoate ZnHZSM-5, HZSM-5 H2, 400500C, atm., FBR [111,112]CsNaX, NaX, MgO Methanol, 425C, atm., FBR [113]
Vegetable oils
Soybean oil Al2O3, MgO 300500C, atm.; FBR [94]
Canola oil SAPO 5, SAPO-11, HZSM-5, MgAPO-36 330550C, atm.; FBR [101]
HZSM-5, HY, silicaaluminaa 400550C, atm.; FBR [98]
KHZSM-5 400550C, atm.; FBR [96]
PtHZSM-5 400550C, atm.; FBR [100]
Palm oil (incl. palm kernel
oil, palm olein oil)
HZSM-5, USY, zeolite b, KHZSM-5a 350450C, atm.; FBR [105]
MCM-41 (various Si/Al) 450C, atm.; FBR [92,105]
Used vegetable oil HZSM-5, SZrO2a H2; 280430C; BR [110]
BR batch reactor, FBRfixed bed reactora Used either neat or in physical mixtures of given materials
302 Waste Biomass Valor (2010) 1:293308
1 3
-
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
11/16
conversion of triglycerides, the impregnation of HZSM-5
with potassium resulted in decreased yields of gasoline-
range hydrocarbons, particularly aromatics. This change can
be attributed to the decreased density of Brnsted acid sites,
which is responsible for the lower yields of aromatics that are
formed over strong acid sites [99]. Based on the differences
in product distribution over HZSM-5 and KZSM-5 it can
be suggested that the catalyst acidity plays a crucial role inthe reactions consecutive to deoxygenation, namely aroma-
tization and oligomerization, but does not affect the initial
deoxygenation so severely.
The other investigated zeolites, Beta and USY, provided
a different product distribution within OLP. In contrast to
ZSM-5 favoring formation of gasoline-range hydrocarbons
and gaseous products, formation of diesel-like product was
prominent particularly over USY and to a lesser extent over
Beta [89]. The difference can be attributed mainly to pore
dimensions and architecture of the zeolites, as the dimen-
sions of ZSM-5 pores restrict the formation of diesel-like
products. The rate of coke formation increased in the orderHZSM-5\H-Beta\HUSY [89]. This corresponds
well with the increasing pore diameter of these zeolites and
presence of cavities in USY allowing the formation of coke
precursors inside zeolite pores.
In addition to type and modification of microporous solids
used as catalysts in triglyceride cracking, co-feeding of
steam affects the product distribution within organic liquid
products. Particularly, the formation of aromatics was sup-
pressed in presence of steam. In the case of HZSM-5 the
total yield of aromaticsdecreasedfrom 8095 to 7487 wt%.
It was proposed that the hydride transfer reactions were
inhibited due to presence of steam [98]. In contrast, catalyst
lifetime was prolonged as a result of steam addition [98,
100], which was explained by possible competitive adsorp-
tion of coke and water molecules [98]. Alternatively, the
prolonged catalyst lifetime could be explained by the sup-
pressed formation of aromatics and hence the suppressed
formation of coke precursors. Finally, the formation of light
olefins was promoted by steam, e.g. the gas yield over
HZSM-5 increased from 25 to 34 wt% due to steam addi-
tion at 450Cand3.6 h-1 [98], which is inline with the other
observations, i.e. the suppressed aromatization.
Besides catalytic cracking of triglycerides, cracking of
fatty acids and their mixtures with triglycerides is of high
importance, as these mixtures generated in oleochemical
industry cannot be directly used as a feed for base-cata-
lyzed transesterification. During cracking over HZSM-5
(Si/Al = 50) temperature and weight-hourly space velocity
were identified as the most important process variables
affecting the gasoline yield. A maximum yield of gasoline
(44 wt%) was obtained at 440C and 3.7 h-1 [103].
Methyl octanoate was used as a model component rep-
resenting esters (Table3), i.e. triglycerides, to understand
the influence of catalyst acidity/basicity on deoxygenation
of esters in more detail [111113]. Methyl octanoate
underwent condensation reactions yielding C15-symmetri-
cal ketone (8-pentadecanone) and hydrolysis producing
octanoic acid (at 500C, 0.1 MPa) (Fig.1). Through
cracking and decarboxylation/decarbonylation of these
intermediates, olefins, and subsequently aromatics were
formed [111]. The aromatization of methyl octanoate onHZSM-5 was more effective than aromatization of
n-octane that occurred by its cracking to olefins and their
subsequent oligomerization and aromatization [111].
Modification of HZSM-5 by Zn (0.3 wt%) increased sig-
nificantly aromatization of n-octane, but did not influence
aromatization of methyl octanoate, i.e. Zn does not affect the
reaction steps leading to formation of aromatics from methyl
octanoate [112]. Moreover, high selectivity to o-xylene at
low conversions of methyl octanoate over both HZSM-5
and Zn/HZSM-5 indicates that direct ring closure occurs,
possibly before deoxygenation. On the contrary, o-xylene
was not observed at low conversions ofn-octane. Hence, thearomatization pathways differ for methyl octanoate (direct
ring closure) and n-octane (cracking and subsequent oligo-
merization and cyclization) [112].
Methyl octanoate conversion (420C, 0.1 MPa) over
basic zeolites, such as CsNaX and NaX, is strongly
affected by solvent choice (10% methyl octanoate in sol-
vent). While in a non-polar solvent (nonane) fast deacti-
vation within 300 min time-on-stream (TOS) was
observed, in a polar solvent (methanol) the conversion
remained stable during the same (TOS). The difference was
explained by strong adsorption of methyl octanoate and
subsequent condensation reactions in nonane. On the con-
trary, methanol competed for adsorption sites with methyl
octanoate by forming adsorbed formate and carbonate
species that led to lower methyl octanoate coverage and, in
turn, to suppression of condensation reactions and to better
catalytic stability [113]. Owing to the strong adsorption on
the basic sites of CsNaX, methyl octanoate cannot be
desorbed before decomposing. The direct decomposition
routes involve decarbonylation and deacetylation yielding
heptenes and hexenes, respectively. Moreover, octenes and
other hydrogenated products are formed by hydrogenation/
dehydration. The formation of these products is assisted by
the surface hydrogen produced from methanol decompo-
sition [113]. Moreover, the poor performance of MgO
indicates that apart from catalyst basicity, the polar envi-
ronment in zeolite micropores plays an essential role [113].
Aiming at higher yields of OLP, particularly in the diesel
range, mesoporous and composite (micro/mesoporous)
catalysts have been studied in detail by the group of Bhatia
[93, 102, 103]. The possible advantages of the composite
catalysts over both microporous and mesoporous materials
were discussed in detail by Cejka and Mintova [76,114].
Waste Biomass Valor (2010) 1:293308 303
1 3
-
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
12/16
The key issues, in connection with triglyceride cracking,
appear to be the adjustment between strong and weak acid
sites, and improvements in the molecular traffic. Several
composite microporous/mesoporous materials (HZSM-5/
MCM-41, HZSM-5/SBA-15) have been shown to give
higher conversion and enhanced yields of the organic liquid
products as compared with the parent materials [93,102].
A comparison of catalytic cracking of a fatty acidmixture (FAM) and used palm oil (UPO) over HZSM-5
and HZSM-5/MCM-41 composite catalyst at 400450C
and 2.54.5 h-1 clearly demonstrated significantly
enhanced conversion of UPO when using the composite
catalyst (from 50 to 70% at 400C). The UPO conversion
enhancement decreased with increasing cracking temper-
ature. On the other hand, only slight increase in conversion
of FAM was observed. The enhancement of conversion
during cracking was hence attributed to reduced diffusional
constrains when composite catalyst was used [107]. Most
of the composite catalysts (HZSM-5/MCM-41, HZSM-
5/SBA-15) having different content of the mesoporousphase gave slightly higher conversion of FAM (9098% at
450C) than the parent HZSM-5 (90%). As expected, the
conversion over the neat mesoporous materials was sig-
nificantly lower (6070%) owing to their lower density and
strength of acid sites [93]. Consequently, the yield of
gasoline increased in comparison with mesoporous cata-
lysts when composite catalysts and HZSM-5 were used.
In fact, the yield of gasoline fraction was the highest
(44 wt%) for composite catalysts having 1030% of mes-
oporous phase [93], presumably due to better molecular
traffic control to and from Brnsted acid sites located in the
micropores of HZSM-5. Similar optimum range for
maximizing gasoline yield was found also for cracking of
palm oil over HZSM-5/MCM-41 composite catalysts
[102].
Fluid catalytic cracking (FCC) of hydrocarbons is the
largest refining catalytic process [87]. As a catalytic
cracking process, FCC constitutes an interesting industrial
possibility for upgrading of triglycerides into hydrocarbon
fuel components without hydrogen consumption and with
minimum capital cost investment [115]. The addition of
rapeseed oil (up to 30%) to vacuum gas oil (VGO), a
typical FCC feedstock, was shown to result in decreasing
yield of liquid hydrocarbon product and in increasing yield
of C3/C4 olefins with increasing rapeseed oil concentration
[116, 117]. At the same time, the amount of gasoline
fraction in the liquid products increased. The oxygen
originating from triglycerides was eliminated mainly as
water a partially as CO and CO2. Moreover, traces of
phenols and carboxylic acids were identified in the liquid
products [116]. The yield of light olefins and of aromatics
in gasoline increased with increasing reaction temperature
in the range 450520C during these micro-activity test
(MAT) experiments [116]. MAT is a standardized test for
evaluation of FCC catalysts performance (ASTM D-3907).
Similar results were obtained when rapeseed oil was
replaced by animal fats (510% in VGO). Cracking of neat
animal fat over dealuminated zeolites yielded predomi-
nantly aliphatic hydrocarbons at 400C, while at 550C
alkyl aromatics were the prevailing products [118]. The
impurities present in triglycerides have a detrimental effecton catalyst activity. In particular, Ca and P, i.e. typical
impurities of vegetable oils, were found to deteriorate the
catalyst cracking activity. Their negative impact was larger
than that of water formed during cracking of triglycerides
that could plausibly cause hydrothermal damage of zeolites
[116].
The reaction pathways of triglyceride cracking over
acidic zeolites have been recently studied by Benson [119].
Propylbenzene and phenylbutene have been suggested to
be the primary aromatic intermediates in cracking of
unsaturated mono-, di- and triglycerides. They are formed
by cyclization of intermediates originating from crackingof the acid moiety after its double bond protonation [119].
As an alternative, initial cracking along the glycerol
backbone (cleavage of CO bonds) was proposed [119].
Moreover, an overview of reaction pathways in catalytic
cracking of triglycerides was provided by Kloprogge [55].
There is general agreement that cracking of triglycerides
includes deoxygenation, cracking (via b-elimination and
c-hydrogen transfer), oligomerization and aromatization.
Details of the proposed reaction pathways are beyond the
scope of this review and can be found in the review [55]
and the original papers [91,95,96,98,101,120].
Conclusions and outlook
Production of biofuels can help in tackling the ever
increasing greenhouse gas emissions from transportation.
Deoxygenation of triglycerides and related feedstocks, both
selective and non-selective, has a potential to become a key
process for the production of biofuels since it provides
high-quality hydrocarbon-based fuels. Selective deoxy-
genation provides green diesel as the main product and
relies on the use of supported noble metal catalysts and
metal sulfide catalysts. Unselective deoxygenation, on the
other hand, uses zeolite-based catalysts and yields a wide
spectrum of products ranging from gases to diesel-like
products. The present paper reviews the main aspects of the
three deoxygenation systems.
Supported noble metal catalysts show an enormous
potential, particularly thanks to their high selectivity and
moderate hydrogen consumption. Owing to the fact that
decarboxylation/decarbonylation is favored over supported
noble metal catalysts, majority of oxygen is eliminated in
304 Waste Biomass Valor (2010) 1:293308
1 3
-
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
13/16
the form of carbon oxides and hydrogen is ideally needed
only to saturate olefinic compounds present in the feed-
stock and to stabilize catalyst activity. Pd supported on
active carbon has been found to be a very promising cat-
alyst for an industrial application. The origin of its high
activity and selectivity, as compared with Pt and other
supports, is not yet fully understood.
Supported metal sulfide catalysts have been used ashydrotreating catalysts over several decades. Development
of deoxygenation processes based on these catalysts can
thus use the vast experience gathered during application of
these catalysts. In fact, the first commercial deoxygenation
process (NexBTL) relies on a hydrotreating catalyst [121].
Nevertheless, significant differences among conventional
hydrotreating catalysts have been found, particularly in
their selectivity to hydrodeoxygenation and hydrodecarb-
oxylation. This is of immense importance since hydrogen
consumption that is typically much larger than over sup-
ported noble metal catalysts could be reduced by fine
tuning of catalyst composition and properties.Microporous and mesoporous molecular sieves trans-
form triglycerides and related feedstocks into hydrocarbons
in absence of hydrogen. Consequently, gaseous olefins and
rather highly aromatic liquid products are formed. These
can be used for production of green gasoline components
and for chemical syntheses. The main drawback of this
approach is, apart from need of upgrading of the primary
cracking products, the fast deactivation of the catalysts.
Owing to the increasing environmental awareness, bio-
fuels will play an important role in future transportation
fuels. This will create a strong demand for development of
new sustainable processes for their production. The inher-
ently high oxygen content of biomass-derived feedstocks,
as compared with fossil raw materials, predetermines
deoxygenation to become a key process in production of
biofuels. We can also expect intensive research efforts to
tackle the fundamental mechanistic aspects of deoxygen-
ation as their understanding is crucial for development of
more efficient deoxygenation catalysts.
Acknowledgments The financial support from the Czech Science
Foundation (GACR, P106/10/1733) is gratefully acknowledged.
References
1. Naik, S.N., Goud, V.V., Rout, P.K., Dalai, A.K.: Production of
first and second generation biofuels: a comprehensive review.
Renew. Sustain. Energy Rev. 14, 578597 (2010)
2. Demirbas, A.: Progress and recent trends in biofuels. Prog.
Energy Combust. Sci. 33 , 118 (2007)
3. Schaub, G.: Synthetic fuels and biofuels for the transportation
sectorprinciples and perspectives. Erdoel Erdgas Kohle 122,
3438 (2006)
4. Schaub, G., Vetter, A.: BiokraftstoffeEine Ubersicht. Chem.
Ing. Tech. 79 , 569578 (2005)
5. European Biofuels Technology Plattform: Strategic Research
Agenda & Strategy Deployment Document. CPL Press (2008).
www.biofuelstp.eu
6. Anon: SustainableBiofuels:Prospectsand Challenges. The Royal
Society, London (2008). http://royalsociety.org/sustainable-
biofuels-prospects-and-challenges/. Accessed 2 Aug 2010
7. Demirbas, A.: BiofuelsSecuring the Planets Future Energy
Needs. Springer-Verlag London Limited, London (2009)
8. Luke, H.W.: BTL fuelsa promising option for the future.
Erdol Erdgas Kohle 121 , 35 (2005)
9. Van Gerpen, J.H., Peterson C.L., Goering C.E.: Biodiesel: an
alternative fuel for compression ignition engines. ASAE dis-
tinguished lecture no. 31, pp 122 (2007)
10. Kubicka, D.: Future refining catalysisintroduction of biomass
feedstocks. Collect. Czech. Chem. Commun. 73, 10151044
(2008)
11. The European standards organization (CEN): European fuel
standardsEN 590 (diesel), EN 14 214 (biodiesel). European
Committee for Standardization (CEN), Brussels 2008(EN14214)
2004 (EN590)
12. Ma, F., Hanna, M.A.: Biodiesel production: a review. Bioresour.
Technol.70 , 115 (1999)
13. Meher, L.C., Sagar, D.V., Naik, S.N.: Technical aspects of
biodiesel production by transesterificationa review. Renew.
Sustain. Energy Rev. 10 , 248268 (2006)
14. Knothe, G., Krahl, J., van Gerpen, J.: The Biodiesel Handbook.
AOCS Press, Champaign (2005)
15. Bournay, L., Casanave, D., Delfort, B., Hillion, G., Chodorge,
J.A.: New heterogeneous process for biodiesel production: a
way to improve the quality and the value of the crude glycerin
produced by biodiesel plants. Catal. Today106, 190192 (2005)
16. European Automobile Manufacturers Association (ACEA),
Alliance of Automobile Manufacturers (AAM), Engine Manu-
facturers Association (EMA), Japan Automobile Manufacturers
Association (JAMA): Worldwide Fuel Charter, 4th edn. (2006).
http://www.jama.or.jp/wwfc/pdf/WWFC_Sep2006_Brochure.pdf/.
Accessed 2 Aug 2010
17. Laurent, E., Delmon, B.: Study of the hydrodeoxygenation of
carbonyl, carboxylic and guaiacyl groups over sulfided CoMo/
c-Al2O3 and NiMo/c-Al2O3 catalysts. I. Catalytic reaction
schemes. Appl. Catal. A 109 , 7796 (1994)
18. Kubicka, D., Kaluza, L.: Deoxygenation of vegetable oils over
sulfided Ni, Mo and NiMo catalysts. Appl. Catal. A 372,
199208 (2010)
19. Huber, G.W., OConnor, P., Corma, A.: Processing biomass in
conventional oil refineries: production of high quality diesel by
hydrotreating vegetable oils in heavy vacuum oil mixtures.
Appl. Catal. A 329 , 120129 (2007)
20. Jakkula, J., Niemi, V., Nikkonen, J., Purola, V.-M., Myllyoja, J.,
Aalto, P., Lehtonen, J., Alopaeus, V.: Process for producing
hydrocarbon component of biological origin. United States
Patent, US 7,232,935 (2007)21. Maula, H.: Neste commissions second NExBTL plant. http://
www.biodieselmagazine.com/article.jsp?article_id=3632(2009).
Accessed 5 Feb 2010
22. H-Bio process. http://www2.petrobras.com.br/tecnologia/ing/
hbio.asp(2010). Accessed 5 Feb 2010
23. Gross, S.: UOP and Italys ENI s.p.a. announce plans for facility
to produce diesel fuel from vegetable oil (2007). http://www.
uop.com/pr/releases/PR.EniEcofiningFacility.pdf. Accessed 5
Feb 2010
24. Craig, W.K., Soveran, D.W.: Production of hydrocarbons with
relatively high cetane rating. United States Patent, US 4,992,605
(1991)
Waste Biomass Valor (2010) 1:293308 305
1 3
http://www.biofuelstp.eu/http://royalsociety.org/sustainable-biofuels-prospects-and-challenges/http://royalsociety.org/sustainable-biofuels-prospects-and-challenges/http://www.jama.or.jp/wwfc/pdf/WWFC_Sep2006_Brochure.pdf/http://www.biodieselmagazine.com/article.jsp?article_id=3632http://www.biodieselmagazine.com/article.jsp?article_id=3632http://www2.petrobras.com.br/tecnologia/ing/hbio.asphttp://www2.petrobras.com.br/tecnologia/ing/hbio.asphttp://www.uop.com/pr/releases/PR.EniEcofiningFacility.pdfhttp://www.uop.com/pr/releases/PR.EniEcofiningFacility.pdfhttp://www.uop.com/pr/releases/PR.EniEcofiningFacility.pdfhttp://www.uop.com/pr/releases/PR.EniEcofiningFacility.pdfhttp://www2.petrobras.com.br/tecnologia/ing/hbio.asphttp://www2.petrobras.com.br/tecnologia/ing/hbio.asphttp://www.biodieselmagazine.com/article.jsp?article_id=3632http://www.biodieselmagazine.com/article.jsp?article_id=3632http://www.jama.or.jp/wwfc/pdf/WWFC_Sep2006_Brochure.pdf/http://royalsociety.org/sustainable-biofuels-prospects-and-challenges/http://royalsociety.org/sustainable-biofuels-prospects-and-challenges/http://www.biofuelstp.eu/ -
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
14/16
25. Pinho, A.R., Silva, M., Silva Neto, A.P., Cabral, J.A.R.: Cata-
lytic cracking process for the production of diesel from vege-
table oils. United States Patent, US 7,540,952 B2 (2009)
26. Petri, J.A., Marker, T.L.: Production of diesel fuel from biore-
newable feedstocks. United States Patent, US 7,511,181 B2
(2009)
27. The EU biodiesel industrystatistics. http://www.ebb-eu.org/
stats.php(2010). Accessed 25 Feb 2010
28. Simacek, P., Kubicka, D., Sebor, G., Pospsil, M.: Fuel prop-
erties of hydroprocessed rapeseed oil. Fuel 89, 611615 (2010)
29. Huber, G.W., Iborra, S., Corma, A.: Synthesis of transportation
fuels from biomass: chemistry, catalysts, and engineering.
Chem. Rev. 106 , 40444098 (2006)
30. Corma, A., Iborra, S., Velty, A.: Chemical routes for the
transformation of biomass into chemicals. Chem. Rev. 107,
24112502 (2007)
31. Maki-Arvela, P., Holmbom, B., Salmi, T., Murzin, D.Yu.:
Recent progress in synthesis of fine and specialty chemicals
from wood and other biomass by heterogeneous catalytic pro-
cesses. Catal. Rev. Sci. Eng. 49 , 197340 (2007)
32. Gallezot, P.: Catalytic routes from renewables to fine chemicals.
Catal. Today 121, 7691 (2007)
33. Furimsky, E.: Catalytic hydrodeoxygenation. Appl. Catal. A
199, 147190 (2000)
34. Lestari, S., Maki-Arvela, P., Beltramini, J., Max Lu, G.Q.,
Murzin, D.Yu.: Transforming triglycerides and fatty acids into
biofuels. ChemSusChem 2 , 11091119 (2009)
35. Rigutto, M.S., van Veen, R., Huve, L.: Zeolites in hydrocarbon
processing. Stud. Surf. Sci. Catal. 168 , 855913 (2007)
36. Corma, A., Martinez, A.: Zeolites in refining and petrochemis-
try. Stud. Surf. Sci. Catal. 157 , 337366 (2005)
37. Maier, W.F., Roth, W., Thies, I., Rague Schleyer, P.v.: Gas
phase decarboxylation of carboxylic acids. Chem. Ber. 115,
808812 (1982)
38. Kubickova, I., Snare, M., Eranen, K., Maki-Arvela, P., Murzin,
D.Yu.: Hydrocarbons for diesel fuel via decarboxylation of
vegetable oils. Catal. Today 106, 197200 (2005)
39. Snare, M., Kubickova, I., Maki-Arvela, P., Eranen, K., Murzin,
D.Yu.: Heterogeneous catalytic deoxygenation of stearic acid
for production of biodiesel. Ind. Eng. Chem. Res. 45, 57085715
(2006)
40. Snare, M., Kubickova, I., Maki-Arvela, P., Eranen, K., Warna,
J., Murzin, D.Yu.: Production of diesel fuel from renewable
feeds: Kinetics of ethyl stearate decarboxylation. Chem. Eng. J.
134, 2934 (2007)
41. Maki-Arvela, P., Kubickova, I., Snare, M., Eranen, K., Murzin,
D.Yu.: Catalytic deoxygenation of fatty acids and their deriva-
tives. Energy Fuels 21 , 3041 (2007)
42. Lestari, S., Simakova, I., Tokarev, A., Maki-Arvela, P., Eranen,
K., Murzin, D.Yu.: Synthesis of biodiesel via deoxygenation of
stearic acid over supported Pd/C catalyst. Catal. Lett. 122,
247251 (2008)
43. Snare, M., Kubickova, I., Maki-Arvela, P., Chichova, D., Era-
nen, K., Murzin, D.Yu.: Catalytic deoxygenation of unsaturatedrenewable feedstocks for production of diesel fuel hydrocarbons.
Fuel 87, 933945 (2008)
44. Simakova, I., Simakova, O., Romanenko, A.V., Murzin,
D.Yu.: Hydrogenation of vegetable oils over Pd on nano-
composite carbon catalysts. Ind. Eng. Chem. Res. 47, 7219
7225 (2008)
45. Lestari, S., Maki-Arvela, P., Eranen, K., Beltramini, J., Max Lu,
G.Q., Murzin, D.Yu.: Diesel-like hydrocarbons from catalytic
deoxygenation of stearic acid over supported Pd nanoparticles
on SBA-15 catalysts. Catal. Lett. 130 , 4851 (2009)
46. Simakova, I., Simakova, O., Maki-Arvela, P., Simakov, A.,
Estrada, M., Murzin, D.Yu.: Deoxygenation of palmitic and
stearic acid over supported Pd catalysts: effect of metal dis-
persion. Appl. Catal. A 355 , 100108 (2009)
47. Murzin, D.Yu., Kubickova, I., Snare, M., Maki-Arvela, P.,
Myllyoja, J.: Method for manufacture of hydrocarbons. United
States Patent, US 7,491,858 (2009)
48. Murzin, D.Yu., Kubickova, I., Snare, M., Maki-Arvela, P.,
Myllyoja, J.: Method for the manufacture of hydrocarbons. PCT
International Application WO 2006/075057 A2 (2006)
49. Do, P.T., Chiappero, M., Lobban, L.L., Resasco, D.E.: Catalytic
deoxygenation of methyl-octanoate and methyl-stearate on Pt/
Al2O3. Catal. Lett. 130 , 918 (2009)
50. Boda, L., Onyestyak, G., Solt, H., Lonyi, F., Valyon, J., Ther-
nesz, A.: Catalytic hydroconversion of tricaprylin and caprylic
acid as model reaction for biofuel production from triglycerides.
Appl. Catal. A 374 , 158169 (2010)
51. Immer, J.G., Kelly, M.J., Lamb, H.H.: Catalytic reaction path-
ways in liquid-phase deoxygenation of C18 free fatty acids.
Appl. Catal. A 375 , 134139 (2010)
52. Lestari, S., Maki-Arvela, P., Bernas, H., Simakova, O., Sjoholm,
R., Beltramini, J., Max Lu, G.Q., Myllyoja, J., Simakova, I.,
Murzin, D.Yu.: Catalytic deoxygenation of stearic acid in a
continuous reactor over a mesoporous carbon-supported Pd
catalyst. Energy Fuel 23, 38423845 (2009)
53. Colson, A.: Formation of ethylene hydrocarbon from esters.
C. R. Acad. Sci. Ser. IIc Chim. 147, 10541057 (1999)
54. Davis, J.L., Barteau, M.A.: Hydrogen bonding in carboxylic
acid adlayers on Pd(111): evidence for catemer formation.
Langmuir5 , 12991309 (1989)
55. Kloprogge, J.T., Duong, L.V., Frost, R.L.: A review of the
synthesis and characterisation of pillared clays and related
porous materials for cracking of vegetable oils to produce bio-
fuels. Environ. Geol. 47 , 967981 (2005)
56. Simakova, I., Simakova, O., Maki-Arvela, P., Murzin, D.Yu.:
Decarboxylation of fatty acids over Pd supported on mesoporous
carbon. Catal. Today 150 , 2831 (2010)
57. Topsoe, H., Clausen, B.S., Masoth, F.E.: Hydrotreating Catal-
ysis. Springer-Verlag, Berlin (1996)
58. Weisser, O., Landa, S.: Sulphide Catalysts, Their Properties and
Applications. Pergamon, Oxford (1973)
59. Senol, O.I., Viljava, T.R., Krause, A.O.I.: Hydrodeoxygenation
of methyl esters on sulphided NiMo/c-Al2O3and CoMo/c-Al2O3catalysts. Catal. Today 100 , 331335 (2005)
60. Simacek, P., Kubicka, D., Sebor, G., Pospsil, M.: Hydropro-
cessed rapeseed oil as a source of hydrocarbon-based biodiesel.
Fuel 88, 456460 (2009)
61. Elliott, D.C.: Historical developments in hydroprocessing bio-
oils. Energy Fuel 21 , 17921815 (2007)
62. Bridgwater, A.V.: Catalysis in thermal biomass conversion.
Appl. Catal. A 116 , 547 (1994)
63. Donnis, B., Egeberg, R.G., Blom, P., Knudsen, K.G.: Hydro-
processing of bio-oils and oxygenates to hydrocarbons. under-
standing the reaction routes. Top. Catal. 52 , 229240 (2009)
64. Senol, O.I., Viljava, T.R., Krause, A.O.I.: Effect of sulphiding
agents on the hydrodeoxygenation of aliphatic esters on sulph-ided catalysts. Appl. Catal. A 326 , 236244 (2007)
65. Ryymin, E.M., Honkela, M.L., Viljava, T.R., Krause, A.O.I.:
Insight to sulfur species in the hydrodeoxygenation of aliphatic
esters over sulfided NiMo/c-Al2O3 catalyst. Appl. Catal. A358,
4248 (2009)
66. Rocha Filho, G.N.d., Brodzki, D., Djega-Mariadassou, G.:
Formation of alkanes alkylcycloalkanes and alkylbenzenes
during catalytic hydrocracking of vegetable oils. Fuel 72,
543549 (1993)
67. Kubicka, D., Bejblova, M., Vlk, J.: Conversion of vegetable oils
into hydrocarbons over CoMo/MCM-41 catalysts. Top. Catal.
53, 168178 (2010)
306 Waste Biomass Valor (2010) 1:293308
1 3
http://www.ebb-eu.org/stats.phphttp://www.ebb-eu.org/stats.phphttp://www.ebb-eu.org/stats.phphttp://www.ebb-eu.org/stats.php -
8/12/2019 34 - Utilization of Triglycerides and Related Feedstocks for Production of Clean Hydrocarbon Fuels and Petrochemi
15/16
68. Smejkal, Q., Smejkalova, L., Kubicka, D.: Thermodynamic
balance in reaction system of total vegetable oil hydrogenation.
Chem. Eng. J. 146 , 155160 (2009)
69. Gusmao, J., Brodzki, D., Djega-Mariadassou, G., Frety, R.:
Utilization of vegetable oils as an alternative source for diesel-
type fuel: hydrocracking on reduced Ni/SiO2 and sulphided
Ni-Mo/c-Al2O3. Catal. Today 5, 533544 (1989)
70. Landa, S., Andrzejak, A., Weisser, O.: Uber die Eigenschaften
von Sulfidkatalysatoren XIV. Zur Hydrierung von Sauren.
Collect. Czech. Chem. Commun.27 , 979986 (1962)
71. Thakur, D.S., Delmon, B.: The role of group VIII metal promoter
inMoS2 andWS2 hydrotreating catalysts:I. ESRstudies of CoMo,
NiMo, and NiW catalysts. J. Catal. 91, 308317 (1985)
72. Zakharov, I.I., Startsev, A.N., Zhidomirov, G.M.: Quantum
chemical study of the electronic structure of the Ni/MoS2 hyd-
rodesulfurization catalysts. J. Mol. Catal. A 119, 437447 (1997)
73. Yang, Y.Q., Tye, C.T., Smith, K.J.: Influence of MoS2 catalyst
morphology on the hydrodeoxygenation of phenols. Catal.
Commun. 9, 13641368 (2008)
74. Kubicka, D., Simacek, P., Zilkova, N.: Transformation of veg-
etable oils into hydrocarbons over organized-mesoporous-alu-
mina-supported CoMo catalysts. Top. Catal. 52, 161168 (2009)
75. Cejka, J.: Organized mes