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Influence of the Ni-Co/Al-Mg catalyst loading in the continuous aqueous phase reforming of the bio-oil aqueous fraction

Abstract

The effect of catalyst loading in the Aqueous Phase Reforming (APR) of bio-oil aqueous fraction has been studied with a Ni-Co/Al-Mg coprecipitated catalyst. Because of the high content of water in the bio-oil aqueous fraction, APR could be a useful process to convert this fraction into valuable products. Experiments of APR with continuous feeding of aqueous solution of acetol, butanol and acetic acid as the only compound, together with a simulated and a real aqueous fraction of bio-oil, were carried out. Liquid products in the liquid effluent of the APR model compounds were quantified and the reaction pathways were revised. The increase of catalyst loading produced an increase of gas production and a gas with higher alkanes content. Acetol was the compound with the highest reactivity while the conversion of acetic acid was very low. The presence of acetic acid in the feed caused catalyst deactivation. Lozano, P.; Simón, A.I.; García, L.; Ruiz, J.; Oliva, M.; Arauzo, J.

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Influence of the Ni-Co/Al-Mg catalyst loading in the continuous aqueous phase reforming of the bio-oil aqueous fraction

Author: Lozano, P.; Arauzo, J.; Oliva, M.; García, L.; Ruiz, J.; Simón, A.I.
Year: 2021
DOI: 10.3390/pr9010081
Source: https://zaguan.unizar.es/record/99760/files/texto_completo.pdf
p ocesses
A icle
In luence o he Ni-Co/Al-Mg Ca alys Loading in he
Con inuous Aqueous Phase Re o ming o he Bio-Oil
Aqueous F ac ion
Pablo Lozano, Ana I. Simón, Lucía Ga cía * , Joaquín Ruiz, Mi iam Oli a and Jesús A auzo


Ci a ion: Lozano, P.; Simón, A.I.;
Ga cía, L.; Ruiz, J.; Oli a, M.; A auzo,
J. In luence o he Ni-Co/Al-Mg
Ca alys Loading in he Con inuous
Aqueous Phase Re o ming o he
Bio-Oil Aqueous F ac ion. P ocesses
2021,9, 81. h ps://doi.o g/10.3390/
p 9010081
Recei ed: 4 Decembe 2020
Accep ed: 29 Decembe 2020
Published: 1 Janua y 2021
Publishe ’s No e: MDPI s ays neu-
al wi h ega d o ju isdic ional clai-
ms in published maps and ins i u io-
nal a ilia ions.
Copy igh : © 2021 by he au ho s. Li-
censee MDPI, Basel, Swi ze land.
This a icle is an open access a icle
dis ibu ed unde he e ms and con-
di ions o he C ea i e Commons A -
ibu ion (CC BY) license (h ps://
c ea i ecommons.o g/licenses/by/
4.0/).
The mochemical P ocesses G oup (GPT), A agon Ins i u e o Enginee ing Resea ch (I3A),
Uni e sidad de Za agoza, Ma iano Esquillo S/N, 50018 Za agoza, Spain; [email p o ec ed] (P.L.);
[email p o ec ed] (A.I.S.); j uizp@uniza .es (J.R.); mi oli a@uniza .es (M.O.); ja auzo@uniza .es (J.A.)
*Co espondence: luciag@uniza .es
Abs ac :
The e ec o ca alys loading in he Aqueous Phase Re o ming (APR) o bio-oil aqueous
ac ion has been s udied wi h a Ni-Co/Al-Mg cop ecipi a ed ca alys . Because o he high con en
o wa e in he bio-oil aqueous ac ion, APR could be a use ul p ocess o con e his ac ion in o
aluable p oduc s. Expe imen s o APR wi h con inuous eeding o aqueous solu ion o ace ol,
bu anol and ace ic acid as he only compound, oge he wi h a simula ed and a eal aqueous ac ion
o bio-oil, we e ca ied ou . Liquid p oduc s in he liquid e luen o he APR model compounds
we e quan i ied and he eac ion pa hways we e e ised. The inc ease o ca alys loading p oduced
an inc ease o gas p oduc ion and a gas wi h highe alkanes con en . Ace ol was he compound wi h
he highes eac i i y while he con e sion o ace ic acid was e y low. The p esence o ace ic acid in
he eed caused ca alys deac i a ion.
Keywo ds:
aqueous phase e o ming; Ni ca alys ; bio-oil; ace ol; bu anol; ace ic acid; aqueous ac ion
1. In oduc ion
Biomass is a enewable aw ma e ial sou ce o ene gy and chemical compounds.
Biomass can be con e ed by biological and he mochemical p ocesses. The mos impo an
he mochemical p ocesses a e combus ion, gasi ica ion and py olysis. The py olysis p ocess
makes i possible o con e biomass in o gas, liquid and solid p oduc s. The as py olysis
o biomass ca ied ou a high hea ing a es, a a inal empe a u e o 450–500
◦
C and
e y sho con ac ime o p oduc s, maximizes he liquid ac ion called bio-oil [
1
]. The
bio-oil, also called py olysis oil, can be sepa a ed in o an aqueous ac ion and nonaqueous
(ligninic) ac ion by adding wa e . The aqueous ac ion con ains mainly compounds
de i ed om he depolyme isa ion o cellulose and hemicellulose, such as o ganic acids,
including ace ic acid; ke ones, such as ace ol, also named hyd oxyace one; and alcohols,
among o he s. These oxygena ed compounds can p oduce hyd ogen and liquid compounds
by e o ming p ocesses.
Ca aly ic s eam e o ming wo ks a low a mosphe ic p essu es and empe a u es in
he ange o 550–800
◦
C. So, Cho ne e al. s udied he con e sion o he aqueous ac ion
o bio-oil by ca aly ic s eam e o ming o hyd ogen p oduc ion and obse ed ha nickel-
based ca alys s achie ed a good con e sion o H
2
, al hough coke was p oduced which
deac i a ed he ca alys [
2
–
5
]. Ga cia e al. [
6
] in es iga ed he composi ion o he ca alys
in his p ocess using nickel ca alys s modi ied wi h cobal o ch omium o dec ease he
amoun o coke ha o med on he ca alys . O he s udies ha e been ca ied ou in ixed
and luidized beds o imp o e he p oduc ion o hyd ogen by ca aly ic s eam e o ming o
he aqueous ac ion o bio-oil, a ying he ope a ing condi ions, and he nickel ca alys
has been suppo ed on alumina, modi ied wi h cobal , coppe , ce ium, magnesium o
calcium [
7
–
10
]. Howe e , his p ocess equi es a lo o ene gy o apo ize wa e , and he
gas ob ained is ich in CO.
P ocesses 2021,9, 81. h ps://doi.o g/10.3390/p 9010081 h ps://www.mdpi.com/jou nal/p ocesses
P ocesses 2021,9, 81 2 o 17
Aqueous Phase Re o ming (APR) is a p ocess de eloped by Dumesic and co-wo ke s,
wi h i s i s e e ence in 2002 [
11
]. This p ocess is app op ia e o con e aqueous s eams
wi h low o ganic con en because i does no need o apo ize wa e , which educes ene gy
equi emen s o hyd ogen p oduc ion. The empe a u e is a ound 220–270
◦
C a mode a e
p essu es o 25–50 ba . Ano he ad an age o he APR p ocess is ha empe a u es and
p essu es a e a ou able o wa e -gas shi (WGS) eac ion, esul ing in a gas wi h low CO
con en . Mo e ad an ages can be ound in he e iew o Da da e al. [
12
]. A signi ican
numbe o s udies ha e ocused on he APR o alcohols and polialcohols, such as e hylene
glycol, glyce ol and so bi ol. Howe e , he s udies o APR which ha e ocused on he
con e sion o compounds de i ed om biomass py olysis a e sca ce [13].
The e a e also some s udies o he bio-oil aqueous ac ion e o ming unde supe c i -
ical condi ions. Supe c i ical wa e condi ions equi e empe a u es highe han 374
◦
C
and p essu es highe han 221 ba . Supe c i ical wa e e o ming o model compounds o
bio-oil aqueous ac ion, such as ace ic acid, ace ol and bu anol wi hou and wi h ca alys ,
was s udied by O iz and co-wo ke s [
14
,
15
]. Chakinala e al. [
16
] s udied he e ec o
se e al ca alys s o he con e sion o he bio-oil aqueous ac ion in supe c i ical wa e
condi ions. Howe e , hese a e condi ions conside ably mo e exigen han hose needed in
he APR p ocess. The co osion o ma e ials in supe c i ical wa e is a ele an aspec .
A andia e al. [
17
] s udied he aqueous phase e o ming o ep esen a i e model
compounds o a bio-oil aqueous ac ion, such as ace ic acid, e hanol, ace ol and ca echol,
as well as a mix u e o all o hem. They s udied he in luence o di e en nickel-based
ca alys s a 230
◦
C and 32 ba . The expe imen s we e pe o med in a con inuous ixed-bed
eac o wi h a ca alys weigh /mass low a e o o ganics o 7.5 g ca alys min/g o ganic.
This wo k ocused on gas p oduc ion, and some quali a i e analyses o he liquid phase
we e ca ied ou wi h he pu pose o iden i ying he p oduc compounds in liquid phase
a e he APR eac ion.
Lou’s g oup pe o med some s udies ocused on aqueous phase e o ming o he
low boiling ac ion o ice husk py olyzed bio-oil. They employed a eal eed ob ained
by e apo a ing o he c ude oil unde acuum. The expe imen s we e pe o med in a
s ainless-s eel au ocla e a 260
◦
C. They analysed he e ec o a pla inum ca alys [
18
], he
size o P /Al2O3[19] and he ecyclabili y o P ca alys s suppo ed on mixed oxides [20].
Vispu e and Hube s udied hyd ogen and alkane p oduc ion om he aqueous ac ion
o bio-oil by aqueous phase p ocessing. A eal aqueous ac ion de i ed om oak wood was
i s hyd ogena ed. Then, APR was pe o med o hyd ogen p oduc ion wi h a P /Al
2
O
3
ca alys a 265 ◦C and 55.1 ba [21].
Oasmaa and Meie [22] de e mined he p esence o bu anol in he alcohol ac ion o
bio-oil. Bu anol has been conside ed a model compound o bio-oil and i s con e sion o
hyd ogen has been s udied by s eam e o ming as he only compound and in mix u es
[
23
–
26
]. The s udy o he APR o bu anol is ele an bo h as a model compound o bio-oil
and because n-bu anol can be p oduced by biological p ocesses and has been p oposed as
an al e na i e o con en ional gasoline and diesel uels.
This wo k p esen s an expe imen al s udy wi h he pu pose o con e ing he aqueous
ac ion o bio-oil and some model compounds in aluable p oduc s by APR.
Nickel ca alys s ha e been widely used in his p ocess because hey a e inexpen-
si e and ha e high ac i i y and selec i i y o hyd ogen, bu hey can be deac i a ed by
ca bon deposi s on hei su ace. Remón e al. de eloped a Ni-based ca alys p epa ed
by cop ecipi a ion, which modi ied he suppo wi h Mg and he ac i e phase wi h Co.
This ca alys has been employed in s eam e o ming p ocess o glyce ol and he aqueous
ac ion o bio-oil [
27
–
31
] and has shown good esul s and he lowes coke p oduc ion
among all hose es ed. Thus, in he p esen wo k, he e ec o ca alys loading in he
APR p ocess employing a Ni-Co/Al-Mg ca alys was s udied. Expe imen s wi h ca alys
weigh /o ganic mass low a e (W/m) a io om 5–40 g ca alys min/g o ganic ha e been
pe o med eeding ace ol, bu anol and ace ic acid indi idually as model compounds o
he aqueous ac ion o bio-oil. Also, a mix u e o ace ol, bu anol and ace ic acid was also
P ocesses 2021,9, 81 3 o 17
employed and was inally s udied a eal aqueous ac ion o bio-oil. Ope a ing condi ions
in luence he con e sion o he o ganic compounds o gas and liquid p oduc s. In his
wo k, quan i a i e analyses o gas and liquid p oduc s o he model compounds we e
ca ied ou . Quali a i e analyses o liquid s eam o he APR o he eal aqueous ac ion
we e pe o med. To he bes o ou knowledge, his is he i s ime ha ca alys loading
has been s udied in he APR o model compounds o he bio-oil aqueous ac ion. This
wo k con ibu es o inc easing he knowledge o con e ing he bio-oil aqueous ac ion
in o aluable p oduc s, gases and liquids. The speci ic ole o Ni-Co/Al-Mg ca alys on
APR has been analysed and p o ides ele an esul s in academic ields, such as yields o
p oduc s. Mo eo e , he obse ed ca alys deac i a ion is signi ican o pe o m he p ocess
in an indus ial scale.
2. Ma e ials and Me hods
The expe imen al sys em was de eloped and manu ac u ed by PID Eng&Tech (Mad id,
Spain). This enabled he con inuous eeding o he aqueous solu ion by means o a high-
pe o mance liquid ch oma og aphy (HPLC) pump. Tempe a u e and p essu e o he
expe imen s we e app op ia ely con olled. The ca alys , wi h a pa icle size be ween
160 m and 250
µ
m, was mixed wi h ine sand o he same size and placed inside he
ubula eac o be ween qua z wool suppo s. The s ainless s eel ubula eac o had an
inne diame e o 9 mm. Mo e de ails abou his ins alla ion can be ound in p e ious
wo ks [27,28].
The gas low was analyzed wi h an Agilen 3000 Mic o GC equipped wi h a molecula
sie e column, a Plo U column and The mal Conduc i i y De ec o s (TCD), whe e N
2
,
H
2
, CH
4
, CO
2
, CO, C
2
H
6
and C
3
H
8
can be quan i ied. The liquid low exi ing om he
eac o was dep essu ized, cooled and analysed wi h an Agilen 7820A GC equipped wi h
an Agilen 7693A au oma ic injec o , an HP-FFAP Agilen 19091F-105 capilla y column and
a Flame Ioniza ion De ec o (FID), whe e liquid p oduc s we e quan i ied. P e iously, he
compounds in he liquid p oduc we e iden i ied by Gas Ch oma og aphy-Mass Spec om-
e y (GC-MS). Due o he complexi y o he eal aqueous ac ion i s liquid e luen was
quali a i ely analysed by GC-MS/FID.
All he expe imen s we e ca ied ou a 40 absolu e ba o sys em p essu e, 227
◦
C o
eac ion empe a u e and a eeding low a e o 1 mL/min. The amoun o ca alys in he
eac ion bed was adjus ed o ob ain a ca alys weigh /o ganic low a e a io (W/m) om
5 g o 40 g ca alys min/g o ganic. The expe imen s we e pe o med mos ly o 3 h.
The ca alys used was p epa ed by cop ecipi a ion in he labo a o y. This ca alys , Ni-
Co/Al-Mg, had a Ni mola con en o 28% exp essed as Ni/(Ni+Al+Co+Mg) and Mg/Al
and Co/Ni a omic a ios o 0.26 and 0.10, espec i ely. Thus, he mola composi ion o each
me al in he ca alys was 54.91% Al, 28% Ni, 14.28% Mg and 2.8% Co. Mo e explana ions
abou i s p epa a ion and cha ac e iza ion ha e been desc ibed by Remón e al. [
8
]. This
ca alys has been employed in he s eam e o ming o glyce ol and he aqueous ac ion
o bio-oil [
29
–
31
]. The Ni-Co/Al-Mg ca alys was calcined in ai a mosphe e a a inal
empe a u e o 750
◦
C o 3 h. Be o e he APR eac ion, he ca alys was in si u educed
wi h a hyd ogen low a e o 100 cm3(STP)/min a 650 ◦C o 1 h.
Ace ol (pu i y:
≥
97.5%, Sigma-Ald ich, S . Louis, MO, USA), 1-bu anol (pu i y:
≥99.5%, Scha lau, Sen mena , Spain) and ace ic acid (pu i y: ≥99.5%, Pan eac, Ba celona,
Spain) we e ed as only compound wi h 5 w % in deionized wa e . A simula ed aqueous
ac ion o bio-oil wi h 5 w % o ace ol, 5 w % o bu anol and 5 w % o ace ic acid in
deionized wa e was also employed as eed. Mo eo e , a eal aqueous ac ion o bio-oil
was also used as eed in he APR expe imen s.
The bio-oil gene a ed om pine sawdus was supplied by Biomass Technology G oup
BV (BTG). The aqueous ac ion was ob ained by adding he bio-oil slowly o dis illed
wa e in 1:2 weigh a io wi h cons an s i ing. This was he same p ocedu e employed in
he wo k o Remón e al. [
8
]. The ul ima e analysis and Ka l Fische analysis o he aqueous
P ocesses 2021,9, 81 4 o 17
ac ion o bio-oil can be ound in ha wo k. The chemical analysis o he aqueous ac ion
o bio-oil ca ied ou by GC-FID is shown in Table 1.
Table 1. Chemical analysis o he aqueous ac ion o bio-oil.
Compound A ea FID%
Ace one 2.63
Me hanol 9.20
E hanol 16.91
Ace ol 15.29
2-Cyclopen en-one-1 1.23
1-Hyd oxy- 2- bu anone 3.07
Ace ic acid 37.74
Fu u al 1.17
Fo mic acid 0.33
P opanoic acid 2.02
1,2 Cyclopen anedione, 3-me hyl 4.86
Phenol, 2 –me hoxy 1.21
Bu anal, 3-me hyl 2.05
Phenol, 2,6-dime hoxy 1.27
Pen anoic acid, 4–oxo 1.03
The compound wi h highes a ea FID % was ace ic acid (37.74), ollowed by e hanol
(16.91) and ace ol (15.29). These main componen s ha e been s udied in o he published
wo ks, such as he s udy by Pan e al. [
18
], in which ace ic acid and ace ol we e he
compounds wi h he highes a ea pe cen age in low-boiling ac ion by GC-MS. The
au ho s also de ec ed o he compounds, such as e hanol, o mic acid, u u al and phenol,
2-me hoxy, among o he s. Vispu e and Hube also iden i ied hyd oxyace one (ace ol) and
ace ic acid in he aqueous ac ion o bio-oil [21].
Mass balance and ca bon balance we e pe o med o alida e he expe imen s. Mass
balance was de e mined as he summa ion o he amoun o gases and liquid e luen s
om he eac o di ided by he amoun o he aqueous solu ion ed. The mass balance was
conside ed eliable i he esul was 100
±
5%. Gas p oduc s we e de e mined om he gas
analysis ca ied ou by GC. Liquid p oduc s we e de e mined by weigh . Gas analysis was
used o p o ide he a e age gas composi ion, yields o gas p oduc s and ca bon con e sion
o gases.
The H2yield was calcula ed as ollows:
H2yield mmolH2
molH2max=
nH2 ×1000
nC ed ×R(1)
whe e nH
2
a e he moles o H
2
gene a ed, nC ed a e he moles o ca bon a om ed and R is
he a io o e o ming. R is he numbe o moles o H
2
pe moles o ca bon a om when he
compound p oduces in he e o ming eac ion he maximum amoun o H
2
and CO
2
. R
is 7/3 o ace ol, 3 o bu anol and 2 o ace ic acid. nC ed was calcula ed as he moles o
compound ed mul iplied by he a oms o ca bon in he compound.
Yields o gas p oduc s we e calcula ed as ollows:
Yield o gas i mmol C
mol C ed=
ni Ci ×1000
nC ed (2)
whe e ni a e he moles o gas i gene a ed (CH
4
, CO, CO
2
, C
2
H
6
o C
3
H
8
) and Ci is he
numbe o ca bon a oms in one molecule o gas i.
The ca bon yield o gases was calcula ed as a pe cen age, di iding he moles o ca bon
in gases (CH4, CO, CO2, C2H6and C3H8) by he moles o ca bon in he eed.
To al O ganic Ca bon (TOC) analysis o he liquid e luen allowed us o de e mine
he ca bon in liquids, which was employed oge he wi h he ca bon con e sion o gases o
P ocesses 2021,9, 81 5 o 17
calcula e he ca bon balance. The ca bon in liquids con ained all he o ganic compounds in
he liquid e luen , as well as he uncon e ed o ganic compounds ed.
GC-FID analysis was employed o quan i a i ely de e mine he liquid p oduc s in he
APR expe imen . The ca bon yield o liquids was calcula ed as he pe cen age o ca bon
moles in liquid p oduc s excep he o ganic compound ed di ided by he moles o ca bon
in he eed.
The yields o liquid p oduc s we e calcula ed as ollows:
Yield o liquid i mmol C
mol C ed=
ni Ci ×1000
nC ed (3)
whe e ni a e he moles o liquid i gene a ed ( o example, e hanol in he APR o ace ic acid)
and Ci is he numbe o ca bon a oms in one molecule o liquid i.
Global esul s o he phase gas a e p esen ed o he 3 h o expe imen and he
e olu ion o gas yields. Time-on-s eam was s udied in o de o know he ca alys s abili y
a he ope a ing condi ions o he APR p ocess.
Liquid p oduc s we e collec ed e e y hou o expe imen . The quan i a i e esul s o
liquids p oduc s analysed by GC-FID p esen ed in ables co espond o he second hou o
he expe imen , which is conside ed mo e ep esen a i e o he whole expe imen .
3. Resul s
3.1. APR o Ace ol
Figu e 1shows ca bon yield o gases and ca bon yield o liquids o he expe imen s
o ace ol APR wi h W/m o 5, 20 and 40 g ca alys min/g ace ol.
P ocesses 2021, 9, x FOR PEER REVIEW 5 o 18
whe e ni a e he moles o gas i gene a ed (CH4, CO, CO2, C2H6 o C3H8) and Ci is he
numbe o ca bon a oms in one molecule o gas i.
The ca bon yield o gases was calcula ed as a pe cen age, di iding he moles o ca -
bon in gases (CH4, CO, CO2, C2H6 and C3H8) by he moles o ca bon in he eed.
To al O ganic Ca bon (TOC) analysis o he liquid e luen allowed us o de e mine
he ca bon in liquids, which was employed oge he wi h he ca bon con e sion o gases
o calcula e he ca bon balance. The ca bon in liquids con ained all he o ganic compounds
in he liquid e luen , as well as he uncon e ed o ganic compounds ed.
GC-FID analysis was employed o quan i a i ely de e mine he liquid p oduc s in
he APR expe imen . The ca bon yield o liquids was calcula ed as he pe cen age o ca -
bon moles in liquid p oduc s excep he o ganic compound ed di ided by he moles o
ca bon in he eed.
The yields o liquid p oduc s we e calcula ed as ollows:
Yield o liquid i mmol C
mol C ed= ni Ci × 1000
nC ed (3)
whe e ni a e he moles o liquid i gene a ed ( o example, e hanol in he APR o ace ic
acid) and Ci is he numbe o ca bon a oms in one molecule o liquid i.
Global esul s o he phase gas a e p esen ed o he 3 h o expe imen and he e o-
lu ion o gas yields. Time-on-s eam was s udied in o de o know he ca alys s abili y a
he ope a ing condi ions o he APR p ocess.
Liquid p oduc s we e collec ed e e y hou o expe imen . The quan i a i e esul s o
liquids p oduc s analysed by GC-FID p esen ed in ables co espond o he second hou
o he expe imen , which is conside ed mo e ep esen a i e o he whole expe imen .
3. Resul s
3.1. APR o Ace ol
Figu e 1 shows ca bon yield o gases and ca bon yield o liquids o he expe imen s
o ace ol APR wi h W/m o 5, 20 and 40 g ca alys min/g ace ol.
0
20
40
60
40
20
Ca bon yield o p oduc s (%)
W/m (g ca alys min/g ace ol)
Gases
Liquids
5
Figu e 1. Ca bon yield o gases and liquids in he Aqueous Phase Re o ming (APR) o ace ol a
di e en ca alys loading (T = 227 °C, 40 ba , 5 w % ace ol, Ni-Co/Al-Mg ca alys , 1 mL/min aque-
ous eeding a e).
Figu e 1.
Ca bon yield o gases and liquids in he Aqueous Phase Re o ming (APR) o ace ol a
di e en ca alys loading (T = 227
◦
C, 40 ba , 5 w % ace ol, Ni-Co/Al-Mg ca alys , 1 mL/min aqueous
eeding a e).
We obse ed a signi ican inc ease in ca bon yield o gases when he W/m a io
inc eased om 5 o 40 g ca alys min/g ace ol. Thus, a 5 and 40 g ca alys min/g ace ol,
he ca bon yield o gases was 5.46% and 46.69% espec i ely. The ca bon yield o liquids
showed a maximum a W/m a io o 20 g ca alys min/g ace ol wi h a alue o 34.79%. A
he highes W/m a io (40 g ca alys min/g ace ol), he ca alys a ou ed gas p oduc ion,
p obably by b eaking C-C bonds in he ace ol molecule.
The esul s o gases and liquids p oduc s in he APR o ace ol a e shown in
Table 2. The gas wi h he highes con en was CO
2
, ollowed by CH
4
and H
2
, since

P ocesses 2021,9, 81 6 o 17
hey we e he modynamically a ou ed a he APR condi ions o low empe a u e while
he con en o C
2
H
6
and CO was e y small as he modynamically expec ed. We obse ed
a clea inc ease in H
2
con en and a dec ease in CO
2
con en when he W/m a io inc eased,
as well as an inc ease in he con en o me hane, which indica es ha e o ming, c acking
and me hana ion eac ions we e boos ed by he ca alys . CO con en showed a dec ease
when he W/m a io inc eased. Alkanes con en , CH
4
and C
2
H
6
, showed a signi ican
inc ease when he W/m a io inc eased om 5 g o 20 g ca alys min/g ace ol, while he
inc ease om 20 g o 40 g ca alys min/g ace ol was small. The yields o all gases (H
2
, CH
4
,
CO, CO
2
and C
2
H
6
) inc eased when he W/m a io inc eased, which is in acco dance wi h
he inc ease o ca bon yield o gases wi h W/m a io (Figu e 1).
Table 2.
Resul s o he APR expe imen s o ace ol (T = 227
◦
C, 40 ba , 5 w % ace ol, Ni-Co/Al-Mg
ca alys , 1 mL/min aqueous eeding a e).
W/m (g Ca alys min/g Ace ol) 5 20 40
Mass balance (%) 100.59 95.18 95.14
Ca bon balance (%) 89.79 90.15 89.78
Mola gas composi ion (%)
H210.85 25.36 33.70
CH416.99 23.18 23.72
CO 0.76 0.30 0.18
CO271.25 50.89 42.07
C2H60.14 0.27 0.32
Yields o gas p oduc s
H2yield (mmol H2/mol H2max) 2.8 36.7 101.2
CH4yield (mmol C/mol C ed) 10.4 78.4 166.3
CO yield (mmol C/mol C ed) 0.5 1.0 1.3
CO2yield (mmol C/mol C ed) 43.6 172.1 294.9
C2H6yield (mmol C/mol C ed) 0.2 1.8 4.5
Yields o liquid p oduc s
Ace aldehyde (mmol C/mol C ed) 16.6 0 10.2
Ace one (mmol C/mol C ed) 11.4 6.6 13.6
E hanol (mmol C/mol C ed) 29.2 112.8 165.0
Ace ic acid (mmol C/mol C ed) 15.7 0 0
1,2-p opanediol (mmol C/mol C ed) 195.2 228.5 133.2
The ca alys in luenced in he WGS eac ion: inc easing H
2
con en and dec easing
CO con en . This could ha e also a ou ed me hana ion and Fische –T opsch eac ions o
gene a e CH
4
and C
2
H
6
, espec i ely. The gas yield e olu ion wi h ime showed a s able
pe o mance, which indica es ha no deac i a ion o he ca alys was obse ed in he APR
o ace ol.
The liquid p oduc s analysed in he APR o ace ol we e ace aldehyde, ace one, e hanol,
ace ic acid and 1,2-p opanediol. Among hem, e hanol and 1,2-p opanediol we e he ones
wi h he highes yields in all condi ions. The yield o e hanol inc eased signi ican ly when
he W/m a io inc eased om 5 g o 40 g ca alys min/g ace ol, wi h alues o 29.2 and
165.0 mmol C/mol C ed, espec i ely. Howe e , he yield o 1,2-p opanediol showed a
maximum a he W/m a io o 20 g ca alys min/g ace ol.
These esul s seem o indica e ha 1,2-p opanediol is an in e media e in he ou e
o e hanol, and ha he hyd ogena ion o he ace ol i s akes place o p oduce 1, 2-
p opanediol. Nex , as he ca alys /o ganic a io inc eases in a subsequen s ep, he c acking
and b eaking o C-C bonds a e p oduced o gene a e e hanol. The eac ion pa hways o
he con e sion o 1,2-p opanediol o e hanol ha e been p oposed by Remón e al. [27].
These esul s a e in acco dance wi h o he wo ks, which indica e ha ace ol is an
in e media e in APR o glyce ol, which is p oduced om he dehyd a ion o glyce ol in he
acid cen es o he ca alys suppo , and hen ace ol is hyd ogena ed o 1,2-p opanediol
P ocesses 2021,9, 81 7 o 17
in he me al cen es o he ca alys [
32
]. In he APR o ace ol, he hyd ogen needed o
hyd ogena e ace ol is supplied by he con e sion o ace ol o gases p oduc s.
3.2. APR o Bu anol
Figu e 2shows he ca bon yield o gases and ca bon yield o liquids o he expe imen s
o bu anol APR wi h he W/m a ios o 5, 10, 20 and 40 g ca alys min/g bu anol.
P ocesses 2021, 9, x FOR PEER REVIEW 7 o 18
and 165.0 mmol C/mol C ed, espec i ely. Howe e , he yield o 1,2-p opanediol showed
a maximum a he W/m a io o 20 g ca alys min/g ace ol.
These esul s seem o indica e ha 1,2-p opanediol is an in e media e in he ou e o
e hanol, and ha he hyd ogena ion o he ace ol i s akes place o p oduce 1, 2-p opane-
diol. Nex , as he ca alys /o ganic a io inc eases in a subsequen s ep, he c acking and
b eaking o C-C bonds a e p oduced o gene a e e hanol. The eac ion pa hways o he
con e sion o 1,2-p opanediol o e hanol ha e been p oposed by Remón e al. [27].
These esul s a e in acco dance wi h o he wo ks, which indica e ha ace ol is an
in e media e in APR o glyce ol, which is p oduced om he dehyd a ion o glyce ol in
he acid cen es o he ca alys suppo , and hen ace ol is hyd ogena ed o 1,2-p opanediol
in he me al cen es o he ca alys [32]. In he APR o ace ol, he hyd ogen needed o hy-
d ogena e ace ol is supplied by he con e sion o ace ol o gases p oduc s.
3.2. APR o Bu anol
Figu e 2 shows he ca bon yield o gases and ca bon yield o liquids o he expe i-
men s o bu anol APR wi h he W/m a ios o 5, 10, 20 and 40 g ca alys min/g bu anol.
0
10
20
30
40
10
40
20
Ca bon yield o p oduc s (%)
W/m (g ca alys min/g bu anol)
Gases
Liquids
5
Figu e 2. Ca bon yield o gases and liquids in he APR o bu anol a di e en ca alys loading (T =
227 °C, 40 ba , 5 w % bu anol, Ni-Co/Al-Mg ca alys , 1 mL/min aqueous eeding a e).
We obse ed a signi ican inc ease in he ca bon yield o gases wi h he inc ease o
he W/m a io. Thus, he ca bon yield o gases we e 2.28% and 34.67% a W/m a ios o 5
and 40 g ca alys min/g bu anol, espec i ely. The ca bon yield o liquids was smalle han
4% and did no p esen a clea endency. Simila ly o ace ol, he inc ease o he W/m a io
a ou ed gas p oduc ion, p obably due o he b eaking o C-C bonds in he bu anol mol-
ecule. Howe e , p oduc ion o liquids was signi ican ly lowe han o ace ol ega dless
o he amoun o ca alys used. The lowe yield o liquids ob ained om bu anol compa ed
o ace ol could be ela ed o he lowe eac i i y o only one –OH g oup in bu anol agains
he ca bonyl and –OH g oups in ace ol.
Table 3 shows he esul s o gases and liquids p oduc s in he APR o bu anol. The
gases ob ained in he APR o bu anol we e H2, CH4, CO, CO2, C2H6 and C3H8. H2 showed
he highes con en in he gas a all he W/m a ios s udied. The con en o H2 dec eased
wi h he inc ease o W/m a io, wi h alues o 60.96% and 37.94% a 5 and 40 g ca alys
min/g bu anol, espec i ely. Howe e , H2 yield inc eased when he W/m a io inc eased,
ha is, he ca alys loading inc eased. On he con a y, CH4, CO2, C2H6 and C3H8 con en
Figu e 2.
Ca bon yield o gases and liquids in he APR o bu anol a di e en ca alys loading
(T = 227 ◦C, 40 ba , 5 w % bu anol, Ni-Co/Al-Mg ca alys , 1 mL/min aqueous eeding a e).
We obse ed a signi ican inc ease in he ca bon yield o gases wi h he inc ease o
he W/m a io. Thus, he ca bon yield o gases we e 2.28% and 34.67% a W/m a ios o
5 and 40 g ca alys min/g bu anol, espec i ely. The ca bon yield o liquids was smalle
han 4% and did no p esen a clea endency. Simila ly o ace ol, he inc ease o he W/m
a io a ou ed gas p oduc ion, p obably due o he b eaking o C-C bonds in he bu anol
molecule. Howe e , p oduc ion o liquids was signi ican ly lowe han o ace ol ega dless
o he amoun o ca alys used. The lowe yield o liquids ob ained om bu anol compa ed
o ace ol could be ela ed o he lowe eac i i y o only one –OH g oup in bu anol agains
he ca bonyl and –OH g oups in ace ol.
Table 3shows he esul s o gases and liquids p oduc s in he APR o bu anol. The
gases ob ained in he APR o bu anol we e H
2
, CH
4
, CO, CO
2
, C
2
H
6
and C
3
H
8
. H
2
showed
he highes con en in he gas a all he W/m a ios s udied. The con en o H
2
dec eased
wi h he inc ease o W/m a io, wi h alues o 60.96% and 37.94% a 5 and 40 g ca alys
min/g bu anol, espec i ely. Howe e , H
2
yield inc eased when he W/m a io inc eased,
ha is, he ca alys loading inc eased. On he con a y, CH
4
, CO
2
, C
2
H
6
and C
3
H
8
con en
in he p oduc gas inc eased wi h he inc ease o he W/m a io. As expec ed in APR,
he le els o CO we e e y low, and showed a end owa d lowe le els as he W/m
a io inc eased. The yields o mos o gases (H
2
, CH
4
, CO
2
, C
2
H
6
and C
3
H
8
) inc eased
when he ca alys loading inc eased. CO yield did no show a clea endency, wi h e y
low alues. These alues we e a consequence o he pa icipa ion o he ca alys in he
WGS eac ion. The mos ele an esul in he gas p oduc ion was a signi ican amoun
o C
3
H
8
p oduced. Gas p oduc ion also showed he end owa d highe alues as he
ca alys /o ganic a io inc eased. Gas composi ion showed some selec i i y endencies
wi h he inc ease o ca alys loading: Bu anol e o ming o H
2
was no a ou ed, while
C
3
H
8
gene a ion was p omo ed. Me hana ion and Fische –T opsch eac ions we e also
p omo ed a high ca alys loading. No deac i a ion o he ca alys was obse ed in he
P ocesses 2021,9, 81 8 o 17
APR o bu anol. The highes yields o gases we e gene a ed a he highes W/m a io,
wi h alues o 36.6 mmol H
2
/mol H
2
max, 31 mmol CH
4
/mol C ed and 248.1 mmol C
in C
3
H
8
/mol C ed. H
2
yield and CH
4
yield p esen ed alues conside ably smalle han
hose ob ained in he APR o ace ol a he same W/m a io.
Table 3.
Resul s o he APR expe imen s o bu anol (T = 227
◦
C, 40 ba , 5 w % bu anol, Ni-Co/Al-Mg
ca alys , 1 mL/min aqueous eeding a e).
W/m (g Ca alys min/g Bu anol) 5 10 20 40
Mass balance (%) 97.10 97.61 97.40 97.22
Ca bon balance (%) 92.24 88.64 87.46 86.98
Mola gas composi ion (%)
H260.96 42.65 37.69 37.94
CH44.22 7.77 8.75 10.68
CO 0.83 0.19 0.11 0.14
CO218.29 21.58 22.31 22.23
C2H60.18 0.33 0.40 0.49
C3H815.52 27.47 30.73 28.53
Yields o gas p oduc s
H2yield (mmol H2/mol H2max) 6.6 19.1 27.1 36.6
CH4yield (mmol C/mol C ed) 1.4 10.4 18.9 31.0
CO yield (mmol C/mol C ed) 0.3 0.3 0.2 0.4
CO2yield (mmol C/mol C ed) 5.9 29.0 48.1 64.4
C2H6yield (mmol C/mol C ed) 0.1 0.9 1.7 2.8
C3H8yield (mmol C/mol C ed) 15.1 110.8 198.6 248.1
Yields o liquid p oduc s
Bu aldehyde (mmol C/mol C ed) 37.2 23.7 15.6 13.2
2-pen anone (mmol C/mol C ed) 2.6 9.5 13.6 18.7
The liquids p oduc s iden i ied in he APR o bu anol (bu aldehyde and 2-pen anone)
di e ed subs an ially om he APR o ace ol. The yield o bu aldehyde was 37.2 mmol
C/mol C ed a he W/m a io o 5 g ca alys min/g bu anol and dec eased o 13.2 a he
W/m a io o 40 g ca alys min/g bu anol. The yield o 2-pen anone inc eased om 2.6
o 18.7 mmol C/mol C ed when he W/m a io inc eased om 5 o 40 g ca alys min/g
bu anol, espec i ely.
3.3. APR o Ace ic Acid
Figu e 3shows ca bon yield o gases and ca bon yield o liquids o he expe imen s
o ace ic acid APR wi h W/m a ios o 5, 10, 20 and 40 g ca alys min/g ace ic acid.
Like he o he wo model compounds, he p oduc ion o gases was highe when i was
used wi h he highes amoun o ca alys pe o ganic. Howe e , a ema kable di e ence is
ha he ace ic acid was less eac i e wi h his ca alys han bu anol and ace ol, wi h alues
o ca bon yields below 2%, ega dless how much ca alys was used bo h o liquids and
o gases.
A close look a he esul s o he gases and liquids p oduced is shown in Table 4. The
gases de ec ed by GC we e H
2
, CH
4
, CO
2
and C
2
H
6
, wi h he C
2
H
6
in esidual amoun s.
The H
2
con en dec eased wi h he inc ease o W/m a io om 50.13% o 34.68% a W/m
a ios o 5 and 40 g ca alys min/g ace ic acid, espec i ely. The con en s o CH
4
and CO
2
in
he p oduced gas inc eased when he W/m a io inc eased. The yields o all gases (H
2
, CH
4
,
CO
2
and C
2
H
6
) inc eased when he W/m a io inc eased, excep o W/m a ios o 5 and
10 g ca alys min/g ace ic acid, which had e y simila alues. Gas composi ion showed
some selec i i y endencies wi h he inc ease o ca alys loading: Ace ic acid e o ming o
H
2
was no a ou ed, while me hana ion and Fische –T opsch eac ions we e p omo ed.
These esul s can co obo a e he endency obse ed in he APR o ace ol and bu anol,
which indica es ha me hana ion was a ou ed using a high ca alys loading.
P ocesses 2021,9, 81 9 o 17
P ocesses 2021, 9, x FOR PEER REVIEW 9 o 18
alues o ca bon yields below 2%, ega dless how much ca alys was used bo h o liquids
and o gases.
A close look a he esul s o he gases and liquids p oduced is shown in Table 4. The
gases de ec ed by GC we e H2, CH4, CO2 and C2H6, wi h he C2H6 in esidual amoun s.
The H2 con en dec eased wi h he inc ease o W/m a io om 50.13% o 34.68% a W/m
a ios o 5 and 40 g ca alys min/g ace ic acid, espec i ely. The con en s o CH4 and CO2
in he p oduced gas inc eased when he W/m a io inc eased. The yields o all gases (H2,
CH4, CO2 and C2H6) inc eased when he W/m a io inc eased, excep o W/m a ios o 5
and 10 g ca alys min/g ace ic acid, which had e y simila alues. Gas composi ion
showed some selec i i y endencies wi h he inc ease o ca alys loading: Ace ic acid e-
o ming o H2 was no a ou ed, while me hana ion and Fische –T opsch eac ions we e
p omo ed. These esul s can co obo a e he endency obse ed in he APR o ace ol and
bu anol, which indica es ha me hana ion was a ou ed using a high ca alys loading.
0
1
2
3
4
5
6
10
40
20
Ca bon yield o p oduc s (%)
W/m (g ca alys min/g ace ic acid)
Gases
Liquids
5
Figu e 3. Ca bon yield o gases and liquids in he APR o ace ic acid a di e en ca alys loading (T
= 227 °C, 40 ba , 5 w % ace ic acid, Ni-Co/Al-Mg ca alys , 1 mL/min aqueous eeding a e).
Table 4. Resul s o he APR expe imen s o ace ic acid (T = 227 °C, 40 ba , 5 w % ace ic acid, Ni-
Co/Al-Mg ca alys , 1 mL/min aqueous eeding a e).
W/m (g Ca alys min/g Ace ic Acid) 5 10 20 40
Mass balance (%) 96.66 97.09 98.31 95.78
Ca bon balance (%) 106.02 96.68 95.18 95.02
Mola gas composi ion (%)
H2 50.13 48.11 41.24 34.68
CH4 16.46 18.35 21.91 25.92
CO 0 0 0 0
CO2 33.15 33.44 36.63 39.15
C2H6 0.26 0.10 0.22 0.26
Yields o gas p oduc s
H2 yield (mmol H2/mol H2 max) 2.3 2.0 2.9 4.5
CH4 yield (mmol C/mol C ed) 1.5 1.6 3.0 6.7
CO yield (mmol C/mol C ed) 0 0 0 0
CO2 yield (mmol C/mol C ed) 3.0 2.8 5.1 10.1
C2H6 yield (mmol C/mol C ed) 0.05 0.02 0.06 0.13
Figu e 3.
Ca bon yield o gases and liquids in he APR o ace ic acid a di e en ca alys loading
(T = 227 ◦C, 40 ba , 5 w % ace ic acid, Ni-Co/Al-Mg ca alys , 1 mL/min aqueous eeding a e).
Table 4.
Resul s o he APR expe imen s o ace ic acid (T = 227
◦
C, 40 ba , 5 w % ace ic acid,
Ni-Co/Al-Mg ca alys , 1 mL/min aqueous eeding a e).
W/m (g Ca alys min/g Ace ic Acid) 5 10 20 40
Mass balance (%) 96.66 97.09 98.31 95.78
Ca bon balance (%) 106.02 96.68 95.18 95.02
Mola gas composi ion (%)
H250.13 48.11 41.24 34.68
CH416.46 18.35 21.91 25.92
CO 0 0 0 0
CO233.15 33.44 36.63 39.15
C2H60.26 0.10 0.22 0.26
Yields o gas p oduc s
H2yield (mmol H2/mol H2max) 2.3 2.0 2.9 4.5
CH4yield (mmol C/mol C ed) 1.5 1.6 3.0 6.7
CO yield (mmol C/mol C ed) 0 0 0 0
CO2yield (mmol C/mol C ed) 3.0 2.8 5.1 10.1
C2H6yield (mmol C/mol C ed) 0.05 0.02 0.06 0.13
Yields o liquid p oduc s
E hanol (mmol C/mol C ed) 16.7 2.4 2.5 2.6
We also obse ed he dec ease o gas yields wi h ime-on-s eam, which indica es he
deac i a ion o ca alys in he APR o ace ic acid.
The highes yields o H
2
and CH
4
we e ob ained using he highes W/m a io, which
was 4.5 mmol H
2
/mol H
2
max and 6.7 mmol CH
4
/mol C ed. The H
2
and CH
4
yields we e
conside able smalle han hose ob ained wi h bu anol.
E hanol was he only liquid p oduc analysed. The yields o e hanol we e smalle
han 17 mmol C/mol C ed. This low alue o e hanol yield was a consequence o he low
amoun o ca bon yield o liquids.
3.4. APR o a Simula ed Aqueous F ac ion o Bio-Oil
Besides he s udy o he indi idual model compounds, once he independen be-
ha iou o he h ee compounds we e es ablished, we conside ed ha i would be in e -
P ocesses 2021,9, 81 16 o 17
Au ho Con ibu ions:
Concep ualiza ion, L.G. and M.O.; me hodology, J.R.; alida ion, P.L., J.R.,
and L.G.; o mal analysis, P.L. and A.I.S.; in es iga ion, P.L.; w i ing—o iginal d a p epa a ion, L.G.;
w i ing— e iew and edi ing, L.G., M.O., J.R. and J.A.; isualiza ion, L.G. and J.R.; supe ision, M.O.,
L.G. and J.A.; p ojec adminis a ion, M.O. and L.G.; unding acquisi ion, M.O., L.G. and J.A. All
au ho s ha e ead and ag eed o he published e sion o he manusc ip .
Funding:
This esea ch was unded by AEI/FEDER, UE (p ojec CTQ2017-86893-R), he A agón
Go e nmen ( e . T22_20R), co- unded by FEDER 2014-2020) “Cons uyendo Eu opa desde A agón”
and A agón Go e nmen and La Caixa (p ojec 2012/GA LC 088).
Da a A ailabili y S a emen :
Mos o da a a e a ailable in his manusc ip . Mo e speci ic da a can
be eques ed om he co esponding au ho .
Acknowledgmen s:
The au ho s like o acknowledge Olga Ma ín o he help in he analysis o he
liquids p oduc s.
Con lic s o In e es :
The au ho s decla e no con lic o in e es . The unde s had no ole in he design
o he s udy; in he collec ion, analyses, o in e p e a ion o da a; in he w i ing o he manusc ip , o
in he decision o publish he esul s.
Re e ences
1. Cze nik, S.; B idgwa e , A. O e iew o applica ions o biomass as py olysis oil. Ene gy Fuels 2004,18, 590–598. [C ossRe ]
2.
Wang, D.; Cze nik, S.; Mon ane, D.; Mann, M.; Cho ne , E. Biomass o hyd ogen ia as py olysis and ca aly ic s eam e o ming
o he py olysis oil o i s ac ions. Ind. Eng. Chem. Res. 1997,36, 1507–1518. [C ossRe ]
3.
Wang, D.; Cze nik, S.; Cho ne , E. P oduc ion o hyd ogen om biomass by ca aly ic s eam e o ming o as py olysis oils. Ene gy
Fuels 1998,12, 19–24. [C ossRe ]
4.
Ma que ich, M.; Cze nik, S.; Cho ne , E.; Mon ane, D. Hyd ogen om biomass: S eam e o ming o model compounds o
as -py olysis oil. Ene gy Fuels 1999,13, 1160–1166. [C ossRe ]
5.
Cze nik, S.; F ench, R.; Feik, C.; Cho ne , E. Hyd ogen by ca aly ic s eam e o ming o liquid byp oduc s om biomass
he mocon e sion p ocesses. Ind. Eng. Chem. Res. 2002,41, 4209–4215. [C ossRe ]
6.
Ga cia, L.; F ench, R.; Cze nik, S.; Cho ne , E. Ca aly ic s eam e o ming o bio-oils o he p oduc ion o hyd ogen: E ec s o
ca alys composi ion. Appl. Ca al. A Gen. 2000,201, 225–239. [C ossRe ]
7.
Bimbela, F.; Oli a, M.; Ruiz, J.; Ga cia, L.; A auzo, J. Hyd ogen p oduc ion ia ca aly ic s eam e o ming o he aqueous ac ion
o bio-oil using nickel-based cop ecipi a ed ca alys s. In . J. Hyd og. Ene gy 2013,38, 14476–14487. [C ossRe ]
8.
Remon, J.; Med ano, J.A.; Bimbela, F.; Ga cia, L.; A auzo, J. Ni/Al-Mg-O solids modi ied wi h Co o Cu o he ca aly ic s eam
e o ming o bio-oil. Appl. Ca al. B En i on. 2013,132, 433–444. [C ossRe ]
9.
Bimbela, F.; Ab ego, J.; Pue a, R.; Ga cia, L.; A auzo, J. Ca aly ic s eam e o ming o he aqueous ac ion o bio-oil using
Ni-Ce/Mg-Al ca alys s. Appl. Ca al. B En i on. 2017,209, 346–357. [C ossRe ]
10.
Med ano, J.A.; Oli a, M.; Ruiz, J.; Ga cia, L.; A auzo, J. Hyd ogen om aqueous ac ion o biomass py olysis liquids by ca aly ic
s eam e o ming in luidized bed. Ene gy 2011,36, 2215–2224. [C ossRe ]
11.
Co igh , R.; Da da, R.; Dumesic, J. Hyd ogen om ca aly ic e o ming o biomass-de i ed hyd oca bons in liquid wa e . Na u e
2002,418, 964–967. [C ossRe ] [PubMed]
12.
Da da, R.; Shabake , J.; Hube , G.; Co igh , R.; Dumesic, J. A e iew o ca aly ic issues and p ocess condi ions o enewable
hyd ogen and alkanes by aqueous-phase e o ming o oxygena ed hyd oca bons o e suppo ed me al ca alys s. Appl. Ca al. B
En i on. 2005,56, 171–186. [C ossRe ]
13.
Co onado, I.; S ek o a, M.; Reinikainen, M.; Simell, P.; Le e s, L.; Leh onen, J. A e iew o ca aly ic aqueous-phase e o ming o
oxygena ed hyd oca bons de i ed om bio e ine y wa e ac ions. In . J. Hyd og. Ene gy 2016,41, 11003–11032. [C ossRe ]
14.
O iz, F.; Campana io, F.; Olle o, P. Supe c i ical wa e e o ming o model compounds o bio-oil aqueous phase: Ace ic acid,
ace ol, bu anol and glucose. Chem. Eng. J. 2016,298, 243–258. [C ossRe ]
15.
O iz, F.; Campana io, F. Hyd ogen p oduc ion om supe c i ical wa e e o ming o ace ic acid, ace ol, 1-bu anol and glucose
o e Ni-based ca alys . J. Supe c i . Fluids 2018,138, 259–270. [C ossRe ]
16.
Chakinala, A.; Chin haginjala, J.; Seshan, K.; an Swaaij, W.; Ke s en, S.; B ilman, D. Ca alys sc eening o he hyd o he mal
gasi ica ion o aqueous phase o bio-oil. Ca al. Today 2012,195, 83–92. [C ossRe ]
17.
A andia, A.; Co onado, I.; Remi o, A.; Gayubo, A.; Reinikainen, M. Aqueous-phase e o ming o bio-oil aqueous ac ion o e
nickel-based ca alys s. In . J. Hyd og. Ene gy 2019,44, 13157–13168. [C ossRe ]
18.
Pan, C.; Chen, A.; Liu, Z.; Chen, P.; Lou, H.; Zheng, X. Aqueous-phase e o ming o he low-boiling ac ion o ice husk py olyzed
bio-oil in he p esence o pla inum ca alys o hyd ogen p oduc ion. Bio esou . Technol. 2012,125, 335–339. [C ossRe ]
19.
Chen, A.; Chen, P.; Cao, D.; Lou, H. Aqueous-phase e o ming o he low-boiling ac ion o bio-oil o hyd ogen p oduc ion: The
size e ec o P /Al2O3.In . J. Hyd og. Ene gy 2015,40, 14798–14805. [C ossRe ]
20.
Chen, A.; Guo, H.; Song, Y.; Chen, P.; Lou, H. Recyclable CeO
2
-Z O
2
and CeO
2
-TiO
2
mixed oxides based P ca alys o
aqueous-phase e o ming o he low-boiling ac ion o bio-oil. In . J. Hyd og. Ene gy 2017,42, 9577–9588. [C ossRe ]

P ocesses 2021,9, 81 17 o 17
21.
Vispu e, T.; Hube , G. P oduc ion o hyd ogen, alkanes and polyols by aqueous phase p ocessing o wood-de i ed py olysis oils.
G een Chem. 2009,11, 1433–1445. [C ossRe ]
22.
Oasmaa, A.; Meie , D. No ms and s anda ds o as py olysis liquids-1. Round obin es . J. Anal. Appl. Py olysis
2005
,73,
323–334. [C ossRe ]
23.
Bimbela, F.; Oli a, M.; Ruiz, J.; Ga cia, L.; A auzo, J. Ca aly ic s eam e o ming o model compounds o biomass py olysis liquids
in ixed bed: Ace ol and n-bu anol. J. Anal. Appl. Py olysis 2009,85, 204–213. [C ossRe ]
24.
Med ano, J.A.; Oli a, M.; Ruiz, J.; Ga cia, L.; A auzo, J. Ca aly ic s eam e o ming o bu anol in a luidized bed and compa ison
wi h o he oxygena ed compounds. Fuel P ocess. Technol. 2014,124, 123–133. [C ossRe ]
25.
Bizka a, K.; Ba io, V.; Ya u, A.; Requies, J.; A ias, P.; Camb a, J. Hyd ogen p oduc ion om n-bu anol o e alumina and
modi ied alumina nickel ca alys s. In . J. Hyd og. Ene gy 2015,40, 5272–5280. [C ossRe ]
26.
Bizka a, K.; Ba io, V.; A ias, P.; Camb a, J. Sus ainable hyd ogen p oduc ion om bio-oil model compounds (me a-xylene) and
mix u es (1-bu anol, me a-xylene and u u al). Bio esou . Technol. 2016,216, 287–293. [C ossRe ]
27.
Remon, J.; Gimenez, J.R.; Valien e, A.; Ga cia, L.; A auzo, J. P oduc ion o gaseous and liquid chemicals by aqueous phase
e o ming o c ude glyce ol: In luence o ope a ing condi ions on he p ocess. Ene gy Con e s. Manag.
2016
,110, 90–112.
[C ossRe ]
28.
Ga cia, L.; Valien e, A.; Oli a, M.; Ruiz, J.; A auzo, J. In luence o ope a ing a iables on he aqueous-phase e o ming o glyce ol
o e a Ni/Al cop ecipi a ed ca alys . In . J. Hyd og. Ene gy 2018,43, 20392–20407. [C ossRe ]
29.
Remon, J.; B ous , F.; Vale e, J.; Chhi i, Y.; Ala a, I.; Fe nandez-Aka egi, A.R.; A auzo, J.; Ga cia, L. P oduc ion o a hyd ogen- ich
gas om as py olysis bio-oils: Compa ison be ween homogeneous and ca aly ic s eam e o ming ou es. In . J. Hyd og. Ene gy
2014,39, 171–182. [C ossRe ]
30.
Remon, J.; B ous , F.; Volle, G.; Ga cia, L.; A auzo, J. Hyd ogen p oduc ion om pine and popla bio-oils by ca aly ic s eam
e o ming. In luence o he bio-oil composi ion on he p ocess. In . J. Hyd og. Ene gy 2015,40, 5593–5608. [C ossRe ]
31.
Remon, J.; Ja au a-Co doba, C.; Ga cia, L.; A auzo, J. Analysis and op imisa ion o H-2 p oduc ion om c ude glyce ol by s eam
e o ming using a no el wo s ep p ocess. Fuel P ocess. Technol. 2016,145, 130–147. [C ossRe ]
32.
Waw ze z, A.; Peng, B.; H aba , A.; Jen ys, A.; Lemonidou, A.; Le che , J. Towa ds unde s anding he bi unc ional hyd odeoxy-
gena ion and aqueous phase e o ming o glyce ol. J. Ca al. 2010,269, 411–420. [C ossRe ]
33.
Roy, B.; Sulli an, H.; Lecle c, C. E ec o a iable condi ions on s eam e o ming and aqueous phase e o ming o n-bu anol o e
Ni/CeO2and Ni/Al2O3ca alys s. J. Powe Sou ces 2014,267, 280–287. [C ossRe ]
34.
Roy, B.; Sulli an, H.; Lecle c, C. Aqueous-phase e o ming o n-BuOH o e Ni/Al
2
O
3
and Ni/CeO
2
ca alys s. J. Powe Sou ces
2011,196, 10652–10657. [C ossRe ]
35.
Nozawa, T.; Mizukoshi, Y.; Yoshida, A.; Nai o, S. Aqueous phase e o ming o e hanol and ace ic acid o e TiO
2
suppo ed Ru
ca alys s. Appl. Ca al. B En i on. 2014,146, 221–226. [C ossRe ]