Subscriber access provided by University of Glasgow Library
Article
Modifying MgO with Carbon for valorization of lignin to aromatics Wei Lv, Yuting Zhu, Jing Liu, Chenguang Wang, Ying Xu, Qi Zhang, Guanyi Chen, and Longlong Ma ACS Sustainable Chem. Eng., Just Accepted Manuscript • DOI: 10.1021/ acssuschemeng.8b05237 • Publication Date (Web): 15 Feb 2019 Downloaded from http://pubs.acs.org on February 19, 2019
Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.
is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.
Page 1 of 17 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
Modifying MgO with Carbon for valorization of lignin to aromatics
promising way to provide aromatic chemicals and recently has drawn great attention but still remains a challenge due to its complex linkages through relatively stable C-O and stubborn C-C bonds.4-5 The C-O bond takes up two-thirds of the all linkages and the β-O-4 ether bond accounts for
Wei Lv a, b, Yuting Zhu b, Jing Liu b, Chenguang Wang b, b
b
a*
Ying Xu , Qi Zhang , Guanyi Chen , Longlong Ma
>50% of the monomer linkages in lignin. In general, C-O
a, b *
bonds are observably weaker and more unstable than C-C a
School of environmental science and engineering, Tianjin University,
bonds.6-8 Therefore, selective hydrolysis / hydrogenolysis
No.92 Weijin Rd, Nankai District, Tianjin 300000, P.R. (China)
cleavage of the C-O bond in β-O-4 linkage is a dominant
b
Guangzhou Institute of Energy Conversion, Chinese Academy of
target in lignin valorization to aromatics, which greatly
Sciences; CAS Key Laboratory of Renewable Energy; Guangdong
depends on the metal activity and the acid-base properties of catalytic metalsites.3-4, 9-10
Provincial Key Laboratory of New and Renewable Energy Research
Basic-catalyzed
and Development. No.2 nengyuan Rd, Tianhe District, Guangzhou
hydrolysis
of
lignin
is
one
exceptional route for the production of simple aromatic
510640 (China)
chemicals under mild conditions. The cleavage of ether Corresponding author:
[email protected],
[email protected] linkages is a dominant reaction in alkaline delignification processes.11-12 The concentration and the nature of the base
We developed a Pd-doped catalyst that the support
are both of the most important factors for high selectivity
MgO was modified with carbon species via methanol
and yield of the products.12-14 Generally, the stronger base,
thermal annealing, catalyzing the cleavage of β-O-4
the higher conversion is given since the polarization of the
lignin-type dimers and actual lignin into aromatics.
base governs the kinetics and the mechanism of the
Methanol as a carbon precursor was processed to carbon
depolymerization reaction.2,
species that loaded metal palladium. The carbon species
base-catalyzed lignin hydrolysis reaction, in acid-
supported Pd on MgO surface changed the acid-base
catalyzed delignification of lignocellulose biomass, the
strength and affected the catalytic activity of C-O bond
hydrolytic cleavages of ether linkages also play a
hydrolysis / hydrogenolysis. The β-O-4 linkage in dimer
dominant role because of the stubborn linkages of lignin
was effectively fractured over Pd/MgO-C, and catalyst’s
units.2, 16 Further, in HDO case, the acid sites are required
strong acid facilitated aldehyde decarboxylation to alkyl
in the HDO mechanism.17
aromatics while relatively weak acid and strong base were
15
Like the behavior of the
Metal Pd possesses outstanding catalytic properties
highly selective for stable aromatics (such as 1-methoxy-
for valorization of lignin to aromatics, and by now,
4-propylbenzene and 1-methoxy-4-(proplenlyl) benzene). considerable attention still being paid to increasing the Allowing Pd/MgO-C-700 to be successfully applied to activity of Pd for lignin C-O bond cleavage via modulation
pine depolymerization, to give 24.6 wt% of aromatics and
of the electron structure, combine with other metals or/and
almost β-O-4 linkages were broken at 160 ℃ , and
acid/base regants.18 Lots of supports were used to tune the
surprisingly, 77.2% of 2-methoxy-4-(proplenlyl)phenols
reactivity via metal-support interaction.19 For instance,
was obtained. The reaction pathways for lignin
under mild hydrogenolysis conditions, the lignin from pine
valorization are hypothesized over Pd/MgO-C catalyst.
and olive tree was degraded into monomeric, dimeric and oligomers over Al-SBA-15 supported Ni, Pd, Pt, Ru, and
Introduction
Pd/C via selective cleavage of the aryl-O-aliphatic and Lignin is an important aromatic biopolymer with
aryl-O-aryl linkages. 20-21 Doping Pd with other atoms is
highly cross-linked polymer that comprise up to 30% of
another efficient method. Yan et al. prepared the bimetallic
the weight and more than 40% of the energy content of
PdNi catalyst for lignin model hydrogenolysis.
lignocellulosic biomass.
1-3
The valorization of lignin is a
Due to the extremely multifunctional groups of the
1
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 2 of 17
Materials
lignin substrate, it is hard to valorized lignin by 1~2 kinds of reactions to realize. Integrated hydrogen-processing of
Ethyl
lignin and model compounds, including upgrading of pyrolysis
oils,
involves
hydrogenolysis,
(EtOAc,
99%),
methanol,
Fe(NO3)3.9H2O, citric acid, nano MgO (primary particles
HDO,
d ≈10~30nm, BET area 135 m2/g) and PdCl2 were
hydrogenation and transalkylation (hydroalkylation) etc.2, 7, 18
acetate
analytical grade and were provided from Shanghai
Thus, multifunctional catalyst is necessary to be
Aladdin biochemical technology co., LTD (Shanghai,
developed for addressing several types of reactions during
China) and used as received. The lignin linkage (β-O-4)
lignin valorization. Bifunctional catalysts containing both
models
metal and acid components, were employed to get rid of
of
3-Hydroxy-2-(2-methoxyphenoxy)-1-(4-
methoxyphenyl) propan-1-one (95 wt %) and 1-(4-
the deactivation problem caused by the conventional
hydroxy-3-methoxyphenyl)-2-(2-methoxyphenoxy)
sulfide-based HDO catalysts. Kou and Lercher et al.
propane-1, 3-diol (97 wt %) were purchased (from
reported a functional catalyst that combined Pd/C, Pt/C,
Shanghai baishun biotechnology co. LTD., China).
Ru/C, or Rh/C with phosphoric acid to catalyze the HDO
Preparation of MgO-C samples
of phenolic components into cycloalkanes and methanol.22 During the reaction, metal-catalyzed hydrogenation and
Carbon was grown on MgO that MgO supported Fe,
acid-catalyzed hydrolysis/dehydration were supposed to
impregnating appropriate amounts of ferric nitrate. A
couple together, which differs from the mechanism for
detailed description of this nanohybrids interface catalysts
22-23
A systematic kinetic study revealed
were produced as follows. For example, 0.364g
that the dual catalytic functions was indispensable and that
Fe(NO3)3.9H2O, 0.173g citric acid were dissolved in 3.0
the acid-catalyzed steps determined the overall HDO
mL deionized water. 1.0g nano MgO power was added
sulfide catalysts.
24
Further, Kou and Dyson substituted the Pd/C
slowly in mixed solution under magnetic stirring. The
and mineral acid by metal nanoparticles and Brönsted
milk-like light-orange slurry was aged at 80°C under
acidic IL, providing a more efficient and less energy-
vigorous stirring for 8 h. Then the little amount of water in
reaction;
Last but not a least,
the slurry was removed at 105 ℃ and was grinded to
etheric C-O bonds in lignin was clipped efficiently over C
power. The light-orange power was calcined at a heating
supported metal catalyst such as Ru, Ni, Pd, and Cu under
rate of 4°C/min from 30 to 450 °C and kept at 450 °C for
demanding upgrading process.
basic conditions.
23
25-26
2 h in static air. The calcined power was reduced in H2 at
Herein, we developed a multifunctional catalyst
500°C for 2h in the next step and then was heated in N2
(Pd/MgO-C) that MgO as support was modified by carbon
flow to 700°C for 1h. After that power was exposed to a
and palladium for conversion of β-O-4 lignin-type dimers
methanol vapor for 10 min at the given temperature (500,
(and actual lignin) into valuable aromatics. The acid-base
600, 700 and 800℃). Methanol was placed in Simax spiral
properties of catalyst was modulated via carbon
mouth gas washing bottle that heated in the 65℃ water
modification and palladium loading, while C is achieved
bath and methanol vapor was carried to the surface of
from methanol thermal annealing hydroxides. In this
power by N2 (80 mL/min). The samples were denoted by
strategy, the Palladium were incorporated on defect C
MgO-C-500, MgO-C-600, MgO-C-700 and MgO-C-800,
through processing C with a small calculated amount of
respectively.
HCl. Modulating the high temperature of methanol
Pd/MgO-C and Pd/MgO catalysts Preparation
thermal annealing to impact the carbon species to affect
To improve catalytic activity, palladium was
the acid-base strength of catalysts. Which was highly
incorporated
selective for the hydrolysis/hydrogenolysis of the lignin C-
impregnation using PdCl2 as a precursor to reach a final
O linkages and decarbonylation of aromatic aldehydes to
Pd loading of 5 % (wt.). Typically, PdCl2 was dissolved in
stable aromatics.
a mixture solvents (ethanol and a small stoichiometric of
Experimental section
HCl), and then MgO-C or nano-MgO power was added
onto
2
ACS Paragon Plus Environment
the
nanohybrids
by
wetness
Page 3 of 17 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
slowly with magnetic stirring. After drying overnight at
TPD) was carried out on a ChemStarTM. The sample (about
80°C and treating in H2 at 300°C for 2 h to decompose the
150 mg) was pretreated at 300 °C for 30 min in a flow of
metal precursor, the resulting catalysts were stored and
30 cc/min He. After pretreatment, the sample was cooled
used to catalytic reaction.
to 120°C and exposed to CO2 for 60 min. After sweeping
Catalyst Characterization
with He for 30 min to remove physisorbed CO2, the temperature was increased linearly at a rate of 10°C/min
Pd, Fe and Mg elemental content (wt.%) of the
to 800 °C in He. The amount of CO2 was quantified by
catalysts were measured by Inductively Coupled Plasma
pulse calibration. Temperature-programmed desorption of
Mass Spectrometry-Optical Emission Spectrometer (ICP-
NH3 (NH3-TPD) was carried out with the same scheduler
OES; Agilent 7900, Agilent Technologies, Santa Clara,
except the gas CO2 changed to 8% NH3/He mixed gas.
CA). C, H and N elemental content (wt.%) of the catalysts Typical process for β-O-4 linkage substrate and
were determined by an elemental analyzer (vario EL cube,
lignocellulose depolymerization
Elementar Analysensysteme GmbH, Hanau, Germany). And O content was calculated by mass difference. Power
Typically, 0.1mmol of the lignin model (3-Hydroxy-
X-ray diffraction (XRD):Bruker Endeavor D4 with Cu
2-(2-methoxyphenoxy)-1-(4-methoxyphenyl)propan-1-
Kα radiation (40 kV and 30 mA) was used to analyze the
one (a1) or Guaiacylglycerol-beta-guaiacyl Ether (b1)), 5
catalysts. They were recorded with 0.0167°steps over the
mL of H2O and 20mL ethyl acetate (EtOAc) were put into
5 to 80°angular range. X-ray photoelectron spectrometer
50 ml autoclave (Hastelloy alloy, made by Anhui Kemi
(XPS): XPS spectra were performed on a Thermo Machinery Technology Co., Ltd.) equipped with a
ESCALAB 250Xi equipped with a monochromatic Al Kα
mechanical stirring, and then 30 mg of catalyst was added.
X-ray source and a delay-line detector. The spectra were
A total of 15 bar of H2 was charged. As for
obtained using the aluminum anode (Al Kα=1486.6 eV)
depolymerization of real lignin, 200 mg of pine as a
operating at 150W. The samples were dried in a vacuum at
substance and 100mg catalyst were placed into 50 ml
120 °C for 10 h and the charge neutralizer system was used
stainless autoclave. The depolymerization reaction was
for all of the analyses. The base pressure was 1 × 10 -8 Pa.
conducted at 160℃. All of degradation reactions were
High resolution spectra were recorded with 20 eV pass
heated to the given temperatures (100,120,140 and 160℃)
energy. The binding energy (BE) was calibrated to the C
and then kept for 4h with continuous stirring at 500 rpm.
1s signal (284.8 eV) as a reference. The curve fitting
After that, the reactor was cooled immediately in an iced-
procedure was conducted using an approximation based
water bath.
on a combination of the Gaussian and Lorentzian functions with subtraction of a Shirley-type background. Scanning
All of materials were took out form the reactor, the
electron microscope (SEM) images of the fresh was
solvents are still two phases and catalyst located at the
obtained on a Hitach S-4800 instrument (10 kV). Scanning
interface of two solvents. 4.0 mL of EtOAc phase product
transmission electron microscopy (STEM) was performed
and 1.0 mL H2O phase product were took and placed
using a JEM-2100F electron microscope operated at 200
together in a rotary evaporator, then removed the solvents
kV, equipped with a spherical-aberration (Cs) probe
and added 5.0 mL ethanol to dissolve the products.
corrector (CEOS GmbH) and a high-angle annular dark
Detailed products were detected by GC–MS (Agilent
field (HAADF) detector. A probe semi-angle of 25m rad
7890A-5975C) equipped with a Pxi-17Sil MS Cap.
and an inner collection semi-angle of the detector of 88m
Column (30m ×0.25 mm ×0.25μm) and compositions
rad were used. Compositional maps were obtained with
were identified according to the NIST MS library. The
energy-dispersive X-ray spectroscopy (EDX) using four
oven temperature was programmed as 40°C hold 5 min,
large-solid-angle symmetrical Si drift detectors. For EDX
and then ramped up to 300°C with 5.2 °C /min and hold
analysis, Pd K, Mg K, C K and O K peaks were used.
for another 4 min. The quantitative analysis of products
Temperature-programmed desorption of CO2 (CO2-
were analyzed by high performance liquid chromatograph
3
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering
(HPLC Waters e2695) with the reverse phase C18 column.
pine valorization was measured by using a Bruker
The mobile phase was 5 mM sulfuric acid aqueous soluti
AvanceШ 400 MHz spectrometer. About 50mg non-
on with a flow rate of 0.5 ml/min and the column tempera
volatile fractions were dissolved in dimethylsulfoxide-d6
ture was maintained at 50 °C. In addition, the components
([D6] DMSO) (0.7 mL). For the HSQC analysis, the
of pine was measured according to NREL K-lignin
collecting and processing parameters were listed as
analysis (NREL LAP Determination of structural
follows: number of scans, 84; receiver gain, 203;
carbohydrates and lignin in biomass).
27
acquisition time, 0.2129/0.0636s; relaxation delay, 2.0 s;
Pd/MgO-C-700 catalyst recuperation and reuse:the
pulse width, 10s; spectrometer frequency, 400.15/100.61
first run condition: 100 mg of pine power, 100 mg
MHz; and spectral width, 4807.8/20124.9 Hz.28 The data
Pd/MgO-C-700 catalyst, 20 mL EtOAc and 5mL H2O, at
was processed with MestReNova software.
160℃ for 4h. In this work, EtOAc and H2O were applied
Results and discussion
to recover the used catalyst from the residue. The
Catalyst characterization
Pd/MgO-C-700 catalyst is relatively apolar and mainly To elucidate reasons for the catalytic activity of the
located in EtOAc phase. While the residue stayed at the
Pd/MgO-C samples in hydrolysis-hydrogenolysis lignin bottom of H2O phase. After EtOAc/H2O extraction, the model compound, we investigated the composites with a EtOAc phase containing part of the Pd/MgO-C-700 was series
removed and fresh EtOAc was added. This was repeated
of
characterization
techniques.
Before
characterizing, the carbon modified Pd/MgO-C catalysts until the EtOAc phase remained relatively clear. The were prepared from reduction under H2 at 300 °C. recoverable catalyst was used to verify stability and recyclability under the first run reaction conditions. Pd/MgO-C-500℃ Pd/MgO-C-600℃ Pd/MgO-C-700℃ Pd/MgO-C-800℃ MgO-C Pd/MgO
Feedstock conversion, monomer quantification and yield calculations
Intensity (a.u.)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 4 of 17
Model compound and pine conversion and monomer
*
* MgO
◆
C
▼Fe
★
Pd
O3
2
* *
★ ★
* *
★
◆
▼
aromatics yield were calculated by the weight comparison
▼ ▼
between the recovered and the feedstock as shown in Eq.
10
20
30
40 50 2θ (degree)
60
70
80
(1). The yield of any monomer aromatic and total monomer aromatics were calculated as shown in Eq. (2)
Fig.1 XRD patterns of fresh Pd/MgO-C catalysts prepared by
and (3), respectively. Conversion(%) =
different temperature
𝑀0 −𝑀𝑛 𝑀0
Fig.1 shows the XRD pattern of Pd/MgO-C catalyst
∙ 100% (1)
obtained by methanol thermal annealing at 500~800°C. 𝑌𝑖𝑒𝑙𝑑 𝐱 monomer aromatic (%) =
𝑀𝑥 /𝑊𝑥 𝑀0/𝑊0
𝑌𝑖𝑒𝑙𝑑total monomer aromatics (%) =
∙ 100% (2)
𝑀𝑡𝑜𝑡𝑎𝑙 𝑀𝑙𝑖𝑔𝑛𝑖𝑛
All Pd/MgO-C samples have the characteristic diffraction peaks of the C and MgO structure with Pd metal.29-30 For
∙ 100% (3)
instance, the diffraction peaks at 25.9°and 42.6°in the
In the equations, M0: the weight of feedstock; Mn: the
curves are attributed to the (002) and (100) plane of the
weight of unreacted feedstock; Mx: the weight of x product;
graphite-like structure of the C,30 respectively. This
Wx: the molecular weight of x product; W0: the molecular
structure of graphitic carbon were further confirmed in
weight of model compound. Mtotal: the weight of total
Raman and XPS analysis (Fig.2 and Fig.5). Other four
monomer aromatics; Mlignin: the weight of lignin in pine.
peaks at 42.88°, 62.30°, 74.69°and 78.63°is the (200), (220), (311) and (222) plane of the structure of MgO.
1
H-13C HSQC NMR analysis of non-volatile fraction
Another three peaks at 40.12°, 46.66° and 68.12° To investigate the degradation of β-O-4 linkages
correspond to the Pd (111), (200) and (220) planes in the
performance, NMR spectra of non-volatile fractions from
4
ACS Paragon Plus Environment
Page 5 of 17
Pd/MgO-C catalysts, respectively.
A
oxidation and the resources potential to Pd (111) crystal plane preferred orientation, that’s why Pd is more suitable for practical application of biomass depolymerization.
5
Adsorbed volume (cm3/g, STP)
To our knowledge, Pd (111) has more resistance to
500
5 600
40 700
2, 5 40
However, the peak at 56.40° (PDF#46-1211)was assigned
800
0.0
to a weak PdO diffraction peak in 500℃ and 600℃ pre-
0.2
0.4 0.6 Relative pressure (p/p0 )
0.8
1.0
0.8
treatment temperature cases. With the pre-treatment
500 600 700 800
B
temperature further increasing, the weak PdO2 diffraction
3
dV/dlog(D) Pore Volume (cm /g)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
peak at 54.55°(PDF#34-1101) was observed and the weak PdO peak at 56.40° further decreased (Fig.1). These changeable Pd species might be related to the effect of pretreatment temperature (Fig.2). Both PdO and PdO2 species
0.6
0.4
0.2
0.0 0
8
16
had little contribution to the cleavage of β-O-4, and the
24 32 Pore diameter (nm)
40
48
Fig. 2 (A) N2 adsorption-desorption isotherms and (B) Proe size
amount of Pd active sites decreased. distribution curves of Pd/MgO-C catalysts
Fe was used to facilitate surface carbon growth and
Fig.2 shows N2 adsorption–desorption isotherms (A)
was remained on the catalyst. The size of Fe species was
and pore size distributions (B) of four different Pd/MgO-
cling to change during the thermal annealing process
C catalysts. The catalysts textural properties are also
because of the evaporation of metal atoms at high
summarized in Table 1. The nitrogen sorption isotherms of
temperature and the dissolving of carbon species on the
the all of catalysts showed a typical IV isotherm with a
nanoparticles.31-32 The smaller Fe nanoparticles was too
hysteresis loop, indicating a mesoporous structure. 35 The
active and gave rise to much carbon dissolved at the
slow capillary condensation step in the range of P/P0 =
beginning, the excess carbon would form a continuous thin
0.4~1.0 might be attributed to the C mixture species. The
layer of graphite. While metal Fe nanoparticle with a
SBET, VP and DBJH values for the catalysts obviously
moderate and suitable size could nucleate growth to
increased from 66.39 m2g-1, 0.04 cm3g-1 and 5.81 nm to
33
carbon tube/rob on MgO. The larger metal Fe or metallic
134.06 m2g-1, 0.22 cm3g-1 and 6.58 nm when the pre-
oxide (Fe2O3 and Fe3O4) particles could not efficiently
treatment temperature increased from 500℃ to 800℃,
catalyze the decomposition of carbon stocks and cannot
indicating Fe metal species participated in and probably
supply enough carbon to nucleate the carbon tube, carbon
catalyzed the carbonization process36. The similar
stocks was in the form of amorphous carbon.32, 34 From the
phenomena were observed for Fe-N-C and Co-N-C
results of Fig.1, Fe species (Fe, Fe2O3 and Fe2O3) were
materials prepared 35, 37.
observed in catalysts. When the thermal annealing temperature were 500 ℃ and 600 ℃ , small metal Fe
Table 1 Textural properties of Pd/MgO-C on BET measurements
nanoparticles contributed to much graphite and carbon
Catalyst
SBET (m2g-1)
VP (cm3g-1)
DBJH (nm)
Pd/MgO-C-500
66.39
0.04
5.81
Pd/MgO-C-600
87.44
0.07
6.37
Pd/MgO-C-700
113.04
0.19
6.45
tube/rob formation (Fig.2 and Fig.5a~b). While more amorphous carbon, less graphite and carbon tube/rob were given because of the formation of larger metal Fe or metallic oxide (Fe2O3 and Fe3O4) particles when thermal annealing temperature increased to 700 ℃ and 800 ℃ (Fig.2 and Fig.5c~d).
5
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering
Pd/MgO-C-800
134.06
0.22
basic sites in Pd/MgO-C catalysts. While all samples have
6.58
the broad desorption peak of the media basic site located Raman spectroscopy is a powerful tool for
between 300 and 680°C with the central of peak at about
identifying the nature of carbon species. The Raman
500°C.47, 49 The amount of total basic sites on these samples
spectra of the carbon from methanol thermal annealing are
allow to estimate the density of basic sites (Table 2). The
shown in Fig.2. Both peaks of D band (amorphous carbon)
density of basic sites was increased when the thermal
and G band (graphitic carbon) broaden with locating at 939~1490 cm-1 and 1490 ~1782 cm-1, respectively.
annealing temperature increased, which may be attributed to
38-39
the surface area of catalyst because the highest pre-treatment
The ID/IG value increased (from 1.7 to 7.0) with pyrolysis
temperature was in keep with the highest surface area of
temperature increasing, indicating that more structural
catalyst (Fig.2). Among all of the catalysts, Pd/MgO-C-800
defects and less graphitization degree were produced at higher
pyrolysis
temperatures.36,40
Moreover,
contains the largest amount of basic sites (2.77mmol/g).
the
A
-1
CO2 signal intensity (a.u.)
appearance of the 2D bands (2440~3270cm ) indicate three types of graphene, single-layer graphene (2620 cm1
), bilayer and few-layer graphene (2650 cm-1) and
graphitic graphene (2661 cm-1) in all of samples.38, 41-42
500℃
600℃
700℃
Therefore, the carbon species are in the form of rob-like 800℃
carbon, amorphous carbon and graphene, introducing
200
300
400 500 Temperature (℃ )
600
700
more defects that causes a change in vibration energy B
levels.43-44 The defects of carbon material is helpful to NH3 signal intensity (a.u.)
loading metal and metallic oxide,45 that’s why a large proportion of palladium species were observed on carbon species (Fig.6 b, c, e and f ). D
500℃
600℃ 700℃ 800℃
G
100
Intensity (a.u.)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 6 of 17
2D
800℃ (ID/IG=7.0) 700℃ (ID/IG=4.4)
400 500 Temperature (℃ )
600
700
catalysts after different temperature treatment
500℃ (ID/IG=1.7)
2000
300
Fig.4 CO2-TPD (A) and NH3-TPD (B) profiles of the Pd/MgO-C
600℃ (ID/IG=3.6)
1000
200
NH3-TPD are used to determine the density of acid
3000 -1
Raman shift (cm )
sites in Pd/MgO-C samples prepared at different thermal Fig.3 Raman spectra of Pd/MgO-C catalysts
annealing temperatures (Fig. 4B and Table 1). Commonly, the desorption peaks with TD at about > 300°C,
The acid-base property of catalysts are reported to play crucial roles in promoting the activity of cleavage the
300~450°C and 450~650°C were denoted as the weak,
linkage β-O-4 with molecular hydrogen.2, 46 Here, the acid-
medium and strong acid site, respectively.50-51 It can be
base property of Pd/MgO-C catalysts were investigated by
seen from Fig.4B, all catalysts showed three desorption
TPD analyses. Fig.4 displays CO2-TPD and NH3-TPD profiles
peaks of a weak, a medium and a strong acid site. Except
of the catalysts. Generally, the desorption peak of the basic
for Pd/MgO-C-800, all samples possess two broader
sites are determined from CO2 desorption temperatures
desorption peaks in the range of 300~450 ℃ and
(TD), i.e., TD<300℃, 300<TD<600℃ and TD>600℃
450~650 ℃ . The desorption peaks of the acid sites
is assigned to weak basic site, media basic site and strong
decrease and shift to lower temperature with the thermal
basic site, respectively.
47-48
As shown in Fig. 4A, no
annealing temperature increasing. However, when the
desorption peak is found below 300°C, implying no weak
thermal annealing temperature was 800℃, the desorption
6
ACS Paragon Plus Environment
Page 7 of 17
eV, 337.2 eV, 338.42eV, and 340.0 eV (Fig.5B), these can
peak of the acid site shifted to higher temperature.
be assigned to Pd0, Pd2+, Pd4+, and Pd0, respectively.52-55 Table 2 Basic and acidic properties of Pd/MgO-C catalysts
As shown in Table 3, although the total Pd content of each
Amount of basic
Amount of acidic
catalyst was a little difference, changes occurred (except
sites (mmol g-1) a
sites (mmol g-1) b
for Pd2+ was a little difference) in the relative amounts of
Sample
Pd0, Pd2+ and Pd4+. For instance, the area ratio of Pd0 Pd/MgO-C-500
1.19
8.03
Pd/MgO-C-600
2.64
5.39
Pd/MgO-C-700
2.72
4.78
Pd/MgO-C-800
2.77
6.46
(Pd3d5+0 and Pd3d3+0) was increased when the pretreatment temperature increased, while the area ratio of Pd4+ was decreased when the pre-treatment temperature increased. There were mainly related to the catalyst surface area that affected by the pre-treatment temperature (Table 2). The higher surface area facilitates Pd species
The total concentration of base calculated based on CO2-TPD
dispersion, leading to more Pd4+ decreased and converted
calibration pulse. b The total concentration of acid calculated based on
to Pd0. However, no PdO species was observed on the
NH3-TPD calibration pulse.
profiles by XRD analysis (Fig.1), it may be attributed to
a
the low crystallinity of PdO species in XRD. Chemical states of surface atoms on the catalysts were
2
C-C SP bonding graphene
investigated by XPS. Fig. 5 shows the C1s and Pd3d spectra
3
C-C SP bonding graphene oxide
C-O-C
O-C=O Pd/MgO-C-500
Intensity
of Pd/MgO-C catalysts. The BE and the area ratio of the type of C1s and Pd3d in catalysts are summarized in Table 2. In the C1s spectrum (Fig. 5A), the wide peak ranging from 282 to 295 eV can be resolved into four individual component peaks at 284.0, 284.8, 286.0 and 288.5 eV, respectively,
Pd/MgO-C-600
Pd/MgO-C-700
Pd/MgO-C-800
39, 43
292
290
288
286 284 Binding energy (eV)
282
280
3
corresponding to the C–C SP bonding graphene oxide, C–C SP3 bonding graphene, C–O-C and O–C=O bonds,
respectively.
When
the
pre-treatment
Pd 3d5+4
Pd 3d5+2 Pd 3d5+0
Pd 3d3+0
temperature Pd/MgO-C-500
increased, the C content of Pd/MgO-C was decreased from Intensity
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
19.49% to 12.68% (Table 5). The area ratio of C–C bond (SP3 bonding graphene oxide and SP3 bonding graphene)
Pd/MgO-C-600
Pd/MgO-C-700
was also decrease when pre-treatment temperature
Pd/MgO-C-800
increased. This result is also well consistent with the effect
344
342
340
338
336
334
332
330
Binding Energy (eV)
of pre-treatment temperature on the size of Fe specie
Fig.5 The XPS C1s and Pd3d spectra of the Pd/MgO-C catalysts
particles (the relatively lower pre-treatment temperature Table 3 The area ratio of the type of C1s and Pd3d in Pd/MgO-C
gave rise to smaller metal Fe nanoparticle that was
catalysts by XPS analysis
beneficial to graphene or/ and graphene oxide formation). On the other hand, the area ratio of O-C=O bond was
Binding energy
increased when the pre-treatment temperature increased
(eV) C1s or Pd3d
Area (%)
500℃
600℃
700℃
800℃
from 500℃ to 700℃, and then decreased to 9.79% at 800℃. Additionally, the area ratio of C-O-C bonds were
(O-C=O) 288.5
18.47
20.42
23.65
9.79
(C-O-C) 286.00
19.78
19.99
19.12
34.15
(sp3 C-C) 284.8
12.65
10.68
10.00
8.95
not big difference under 700℃, while reached to a high value of 34.15% at 800 ℃ . The reasons for these phenomena are unclear. Deconvolution of the Pd3d spectra suggests that there were four components peaks at Pd3d BE values of 335.13
7
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
(sp2 C-C) 284.0
49.09
48.91
47.23
47.11
(Pd0 ) 335.13
5.35
5.37
13.67
15.06
Page 8 of 17
decreased from 19.49% to 12.68% when the pre-treatment temperature increased from 500 ℃ to 800 ℃(Table 4). However, it is hard to identify the Pd and Fe nanoparticles
2+
(Pd ) 337.20
69.68
69.93
68.46
68.89
(Pd4+) 338.42
18.37
16.21
10.27
8.23
(Pd0 ) 340.00
6.60
8.50
7.60
7.82
in SEM image mainly due to their low weight metal addition (Table 4). The content of Fe and Pd were a little difference the theoretical additive value (~5.0 wt. %). Notably, the relatively higher C weight were given (19.8~25.86%) form the EDS analysis (Table 3). ICP-OES analysis of Pd/MgO-C samples was added (Table 4). Table 4 shows the content of C decreased from 19.49% to 12.68% when the pre-treatment temperature increased from 500℃ to 800℃. The content of Fe and Pd were a little difference the theoretical additive value (~5.0 wt. %).
Fig.6 SEM images (a) Pd/MgO-C-500, (b) Pd/MgO-C-600, (c) Pd/MgO-C-700, (d) Pd/MgO-C-800
SEM and TEM images were taken to investigate the morphology and structure of the materials. As shown in Fig.6, the magnified scanning electron microscopy (SEM) images show that these anomalous rod-like carbons were formed on the surface of MgO support (Fig.6a~c). The rod-like carbon probably assembled on Fe nanoparticles. The formation of rod-like carbon is mainly depended on
Fig.7 TEM image of Pd/MgO-C-700 catalyst (a~f), and element
the moderate metal Fe nanoparticle size, as Chenguang Lu
mapping (g~i)
et.al reported in their research. They found that graphite
Transmission electron microscopy (TEM; Fig.6a~f)
was given instead of rob-like carbon when metal Fe
and elemental mapping (Fig.6g~i) showed that carbon rob
particle very small. The small Fe particles were very active
(Fig.6b, be labeled with blue imaginary line), amorphous
and dissolved too much carbon covering the surface of Fe
carbon and graphite carbon (Fig.6a, c and d) were the form
nanoparticle, resulting in excess carbon formed a
of C species on the spherical MgO or covered/encased the
continuous thin layer of graphite. However, the large Fe
spherical MgO. (Fig. 6a~d and Fig.2). The Pd
34
nanoparticles
could
not
efficiently
catalyze
nanoparticles were loaded on carbon species. The mean Pd
the
particle size is about 1.7~22 nm (Fig.6f). Moreover,
decomposition of carbon stocks, and cannot supply
graphitic carbon with a spacing of 0.39 nm is observed on
enough carbon to nucleate robs. Only the moderate size of
MgO support (Fig.2 and Fig.6d).
Fe nanoparticle can ensure a suitable carbon supply for the nucleation and growth of robs.32,
34
Table 4 Element of Pd/MgO-C catalyst was detected by ICP-OES and
Thus, no rob-like
elemental analysis
carbon generation in Pd/MgO-C-800 material is attributed to the large Fe nanoparticles sintered/aggregated and a
Element
wt.%
portion of Fe2O3 and Fe3O4, which is in good consistent 500℃
600℃
700℃
800℃
Mg
32.06
33.69
34.53
37.58
Fe
4.78
4.26
4.35
4.27
with the diffraction peaks of Fe2O3 and Fe3O4 at 700℃ and 800℃ (Fig.1). Correspondingly, the content of C
8
ACS Paragon Plus Environment
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
Pd
4.25
4.37
4.62
4.50
C
19.49
17.64
15.3
12.68
H
0.83
0.37
1.26
0.85
O
38.42
39.50
39.94
40.12
N
0.05
0.17
0
0
100 Pd/MgO-C-700
90 Pd/MgO-C-600
Monomer selectivity (%)
Page 9 of 17
Pd/MgO-C-800 Pd/MgO-C-500
80
70
60
Pd/MgO
50 MgO-C
40 50
The depolymerization activity of the catalyst Recently, the strategy of coupling reactions have
60
70 80 Conversion (%)
90
100
Fig.8. Catalytic results of Guaiacylglycerol-beta-guaiacyl Ether (a1)
been employed in the depolymerization of the primary β-
depolymerization. Reaction conditions: 30 mg of catalyst, 0.1m mol
O-4 lignin models (containing about 50% of all linkages)
of a1, 20 mL of EtOAc and 5 mL H2O, 15 bar of H2, 140°C, 1 h.
such as, hydrolysis / hydrodeoxygenation, hydrogenolysis, Here, we investigated the
With Pd/MgO-C catalysts, a further enhanced
depolymeirzation of model compound with hydrolysis /
conversion of a1 and monomer selectivity of product
hydrogenolysis /decarbonylation approaches (Fig.8 and
obtained. For instance, in Pd/MgO-C-600 case, 92.3% of
Table 5). Only 19.6% of a1 was converted and 12.5% of
conversion and 85.6% of monomer selectivity were given.
guaiacol (1) was given without a catalyst (Entry 1 in Table
Pd/MgO-C-700 was not only exhibited high activity for
5), implying that EtOAc/H2O combined with H2 showed a
breaking Cβ-O bond (conversion >99%) but providing a
weaker effect on breaking Cβ-O-4 bond through hydrolysis
good yield of monomer aromatic (>95%). Although,
or/and dehydration under 140℃.
Pd/MgO-C-500 and Pd/MgO-C-800 gave 86.8% and 90.4%
hydrogenation and so on.2,
56
of dimer compounds’ conversion, relative lower monomer When a1 was depolymerized over MgO-C (or
aromatic yields were given, owing to the formation of 8a
Pd/MgO) catalyst, the conversion of a1 reached 49.3% (or
(condensation product). Notably, the strength of catalyst
65.7%) with 41.8% (or 58.2%) of monomer selectivity.
acid/base properties played important roles for oligomer
These results confirmed that both MgO-C and Pd/MgO
depolymerization and monomers yield. Both of Pd/MgO-
catalysts were able to cleave the linkage of β-O-4 in a1. In
C-600 and Pd/MgO-C-700 possessed the close-up
Pd/MgO catalyst case, the monomer product of 1, 5a,
acid/base strength and contributed to a higher conversion
6a/7a, 3a and a little of a-2 dimer were obtained (Entry 9
and yield. On the other hand, the higher density of acid site
in Table 5). These were thereby inferred that a1 was
(and more strong acid site at 450~650℃) in Pd/MgO-C-
dehydrated to a-2 with the help of alkalinity and then the
500 and Pd/MgO-C-800 gave birth to a lower monomer
hydrolysis of a-2 was conducted. The product of 5a, 6a/7a,
yield (Table 2 and Table 5).
3a mainly derived hydrogenation and decarboxylation reactions over Pd active site. For MgO-C catalyst, only
The effect of acid/base activity of catalyst on
12.3% of 5a was given that could be lack of Pd active site
product distribution was assessed. As shown in Table 5,
for a-2 hydrogenolysis, while some part of a1 was
both in Pd/MgO-C-500 and Pd/MgO-C-800 catalyst cases,
hydrolyzed and then released a relative higher yield of
except, cleavage of β-O-4 model afforded the main
6a/7a through hydrogenolysis (Entry 10 in Table 5).
product guaiacol (1), as well as the relative higher yield of
Remarkably, MgO-C catalyst showed a relative weaker
4a (20.1% /18.3 %), 2a (8.5% / 10.6%) and 8a (12.0 % /
effect on a1 conversion and the cleavage of a-2 than
6.5 %). Nevertheless, only 4.8% and 2.9% of 4a were
Pd/MgO catalyst. Although both MgO-C and Pd/MgO
found in Pd/MgO-C-600 and Pd/MgO-C-700 cases,
catalysts were able to cleave the linkage of β-O-4 in a1,
respectively, and high yield of 1, 5a and 6a/7a were
the introduction of acidity on catalyst is essential for
afforded. They could be seen that the high density of acid
cleaving β-O-4 linkage under mild reaction condition.
site and more strong acid site were prone to obtain 4a and
9
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 10 of 17
Table 5 Results of Pd/MgO-C catalytic cleavage of β-O-4 model compound a1 and main products observed [a]
Product yield (%) Entry
Catalyst
1
2a
3a
4a
5a
6a/7a
8a
1
Free
19.6
12.5
-
5.8
-
2.2
4.0
-
2
Pd/MgO-C-500
86.8
76.7
8.5
19.2
20.1
11.4
3.4
12.0
3
Pd/MgO-C-600
92.3
85.6
11.3
15.2
4.8
32.2
15.6
3.3
4
Pd/MgO-C-700
99.5
95.4
11.9
23.6
2.1
35.2
20.4
-
5
Pd/MgO-C-800
90.4
81.6
10.6
17.8
18.3
15.6
10.3
6.5
63.9
57.8
6.7
13.4
3.5
21.9
10.6
-
Pd/MgO-C-700
82.5
78.6
8.6
19.5
2.9
28.7
17.4
-
100
99.4
14.0
24.1
1.8
32.4
20.8
1.2
9a
Pd/MgO
65.7
58.2
-
7.4
-
44.8
4.6
(a-2) 4.5
10a
MgO-C-700
49.3
41.8
-
5.5
-
12.3
16.9
(a-2) 6.7
b
6
c
7
d
8
[a]
Conversion (%)
conditions: 30 mg of catalyst, 0.1 mmol of a1 model compound, 20 mL of EtOAc and 5 mL H2O, 15 bar of H2, 140°C, 1 h. The products were
determined by GC-MS with acetophenone as internal standard. [a] 140°C, [b] 100°C, [c] 120°C, [d] 160°C.
Table 6 The result of main products from the cleavage of b1 model compound over MgO-C catalysts [a]
Structure and name
Entry
1
2
3
4
5
6
7
8
Reaction
Free
Cat.-
Cat.-
Cat.-
Cat.-
condition
cat.
500
600
700
800
100℃
120℃
160℃
21.1
92.5
98.0
100
96.9
79.8
90.4
100
15.4
88.6
93.9
98.3
92.3
73.1
86.3
99.5
2.6
2.8
19.4
20.3
14.2
9.7
11.9
15.6
3.1
24.4
6.6
1.9
15.7
2.8
2.2
3.7
-
-
11.1
21.8
14.6
17.9
19.6
22.1
Conversion (%)
Yield (%)
10
ACS Paragon Plus Environment
Page 11 of 17 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
[a]
-
12.2
15.3
11.5
13
11.5
13.7
12.0
10.7
10.3
13.1
9.4
15. 6
8.7
9.2
10.5
-
14.8
10.8
11.4
12.9
8.3
9.8
13.9
-
9
11.5
10.2
7.4
4.6
7.3
8.1
-
2.6
3.1
11.6
8.2
9.4
10.4
11.4
-
11.7
2.4
-
5.5
-
-
2.0
conditions: 30 mg of catalyst, 0.1 mmol of b1 model compound, 20 mL of EtOAc and 5 mL H2O, 15 bar of H2, 100~160°C, 1 h. The products were
determined by GC-MS and quantified by HPLC.
2a (derived from 4a decarbonylation reaction). Lower
kinetics and the mechanism of the depolymerization
density of acid site with more weak and media acid sites
reaction.2,
(Table 2 Pd/MgO-C-600 and Pd/MgO-C-700), as expected,
medium acid sites are lead to good yield of 5a, 3a and
resulted in a decrease of 4a with a concomitant drop in
6a/7a (Entry 3-5 in Table 5). These stable products are
condensation product (8a). The results are in good
likely to contribute to the high monomer aromatic yields.
15
It is important to note that weak or/and
consistent with the reports by and Bruijnincx et.al.56 Furthermore, another dimer b1 degradation was also Meanwhile, from the variation of 2a, 4a and 8a yields in conducted to assess the effect of catalyst acid/base Table 5, much lower yield of 2a than 4a (Entry 2 and 5 in properties on b1 conversion and product distribution. As Table 5, Scheme 1) demonstrated that the decarbonylation shown in Table 5. Without Pd/MgO-C catalyst, 21.1% of reaction cannot keep up with aldehyde formation.56-57 With b1 was converted with 15.4% of guaiacol (1) and 10.7% decarbonylation being too slow, larger molecular weight of 6b-1 (Entry 1 in Table 5), ascribing to the hydrolysis of compounds were formed, such as 8a (Scheme 1).2, 17, 56 b1 and b-2 was took off formaldehyde under the effect of Contrary to relative lower density of acid site catalyst with EtOAc/H2O combined with H2 at 140℃.With catalysts, weak or/and medium acid site (Entry 3 and 4 in Table 5), the model b1 also afforded excellent conversion and good the yield of 2a is higher than 4a with little trace of 8a. yield of guaiacol (1). The influences of acid/base density Marks et.al reported similar effect was found in the tandem on product of 4b, 2b, 7b, 7b-1 and 10b were similar to the catalytic system, where a weaker acid was employed to catalytic active effect on 4a, 2a, 5a and 8a. Namely, the remove reactive intermediates more effectively over Pd high density of basic site is attributed to from 4b, 2b and catalyst, giving rise to higher yields.58 Indeed, it is quite 10b, and relative low density of acid sites and high density necessary
that
the
kinetics
of
hydrolysis
and of basic sites were contributed to 7b-1, 7b and 5b.
decarbonylation are carefully matched. Obviously, the Furthermore, b1 was efficiently cleaved at 100℃ with high density of base site (Table 2) had effect on the higher conversion and yields of guaiacol (71.3%), 7b increase of 5a yield with little amount of 8a (Table 5). (17.9%), 3b (11.5%) and 5b (9.4%). And a higher Usually, the high content of alkaline gave higher conversion and monomer aromatic yield than that from a1 conversion since the polarization of the base governs the
11
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 12 of 17
(Table 5 and Table 6). These results show that the β-O-4
hydrogenolysis), followed by acid-catalyzed hydrolysis
linkage in b1 is easier to fracture than that in a1 under the
step to 1 and 6a/7a (1 and 6b) and then rearrangement to
same reaction condition. They are associated with the
Hibbert’s Ketone 3a (3b).2 Another reaction pathway is
different between Cα-OH of β-O-4 alcohol and -Cα=O of
that a1 (b1) is dehydrated on Cα-OH by acid catalysis, as
β-O-4 ketone. The function group -Cα=O ketone in b1
well as the deprotonation of Cγ-OH for breaking off the
lowers the dissociative energy of Cβ-O-4 bond by 40~50
Cγ-carbon to a significant amount of a-2 (b-2) with
kJ·mol-1 than that Cα-OH of β-O-4 alcohol to the cleavage
formaldehyde. a-2 (b-2) goes on a slower acid-catalyzed
of Cβ-O-4 linkage in a1.
8, 56, 59-60
hydrolysis step to 1 and 4a (4b). With the help of strong acid and sufficiently metal Pd active, the decarbonylation
The effect of temperature on a1 (b1) conversion and reaction
is
carried
out
and
then
generates
the
the product yield were investigated over Pd/MgO-C-700 corresponding methyl-substituted product 2a (2b), whilst catalyst. The conversion of a1 (b1) and the yield of repolymerization takes place instead to give 8a (10b).7 monomer products increased when the temperature raised, Furthermore, an alternative pathway is also observed, the while the yield of 4a (4b) decreased, especially,, 8a (10a) enol ether a-2 (b-2) converted to 5a (5b) by appeared at 160℃ (Entry 4 and 6~8 in Table 5 and Table hydrogenation.61 Base for the cleavage of ether linkages is 6). Moreover, the increasing yield of 1, 5a (5b), 3a (3b) also kind of important. In the presence of base, the and 7b/7b-1 stable products were given when degradation structure of a1 involves a free phenolic OH functional temperature raised. Which were attributed to more intermediate
a-2
(b-2),
a-3
(b-3)
and
group in the para-position of the α-aryl ether group, which
(b-4) is meant to crack by converting phenolate unit into the
depolymerization to 1, 5a (5b), 7b/7b-1 and Hibbert’s
corresponding quinone methide intermediate (a-4). The ketones 3a (3b) (Scheme 1 and 2) when temperature
Cγ-carbon in a-4 is fractured to release formaldehyde and
elevated. The intermediates a-2, a-3, b-2, b-3 and b-4 a-2 via basic-catalyzed dealkylation reaction, which also hardly detected, demonstrating fast hydrolysis and contributes to 1 and 5a (or/and to 1, 4a and 2a) (Scheme hydrogenolysis were carried out. However, a high yield of
1). Model compound b1 is a β-Aryl ether that its Cα-
2a/2b was given at 160 ℃ due to the increased acid
position of the propane side chain possesses a free concentration
of
the
reaction
system
(the
acid alcoholic OH group and its phenolic OH group in the
concentration was increased owing to a portion of EtOAc paraposition is etherified. In the present of base, the hydrolyzed to acetic acid and ethanol at 160℃).The model
cleavage of β-O-4 linkage in b1 contains deprotonated
compound a1 (b1) depolymerization show that a1 (b1) hydroxyl groups in Cα or Cγ (b-4), which serve as compounds were almost converted with high yield of nucleophiles
in
replacing
the
neighboring
aroxy
monomer aromatics under 140℃ (Entry 4 in Table 5 and substituent by forming an oxirane ring (8b). Then 8b is Table 6). opened by addition of a hydroxide ion to form an The depolymerization mechanistic perceive provided
intermediate (9b) with glycol groups. Finally, the 9b was
by the model compounds are proposed in Scheme 1 and 2.
converted into 7b/7b-1 via dehydration and hydrogenation
Initial acid catalyzed dehydration of the Cα-OH in a1
reactions, as displayed in Scheme 2.
forms enol ethers a-3 (b1 converted to b-3 through
12
ACS Paragon Plus Environment
Page 13 of 17 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
Scheme 1. Proposed mechanism for the cleavage of β-O-4 model a1 and possible pathways to products
Scheme 2. Proposed mechanism for the cleavage of β-O-4 model b1 and possible pathways to products
Finally, we focused on pine power (real lignin)
(Fig.9), the monomer aromatics was obtained in
as a substrate. In this work, pine is consisted of
24.6 wt % yields (lignin based), and the selectivity
42.69% cellulose, 22.6% hemicellulose, 22.93%
of 2-methoxy-4-propylphenol was 77.2% (label 17
lignin, 0.59% ash, 4.89% moisture, and 4.90 %
in Fig.9). Other aromatics’ selectivity’s (label 10~19)
coloring matter. Pine was directly subjected to
are likely to depended on the effect of acid-base
depolymerization over Pd/MgO-C- 700 catalyst in
properties
EtOAc/H2O solvents under 160℃. Pine power was
hydrogenation process and decarbonylation. A large
pretty much dissolved in liquid phase. Form the
amount
result of liquid products GC-MS and GC analysis
of
of
MgO-C-700
products
from
on
hydrolysis,
cellulose
and
hemicellulose were also obtained, for instance,
13
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering
hexane-2, 5-dione (label 9), ethane-1, 2-diol, butan-
Pd/MgOC-700 catalyst (Fig.12). During the first two runs,
1-ol, ethyl 2-hydroxypropanoate and glucose. It
stronger Pd and MgO diffraction peaks were observed than
should be pointed out that little amount of β-O-4
the previous run (run-1 and run-2 in Fig.12), implying Pd and
linkages was found on the spectrum of HSQC
MgO
species
were
aggregated
during
depolymerization process. Even worse, PdO and PdO2
(Fig.10, Aγ and Aβ). This indicates that MgO-C-700
species appeared after the third run, displaying some
catalyst possesses strong activity of fracturing β-O-
active sites of Pd/MgO-C-700 catalyst were oxide. 4 linkages in pine. Therefore, the aggregation of Pd species and MgO as well 1
2
O
19
4
O
3
9
O
O O
6
5
O
22
OH
O
23
O
10
11
OH
OH
OH
OH
deactivation
OH
13
OH
16
14
OH
OH
15
OH
decreasing
ability
of
pine
depolymerization.
OH
OH
O O
O
O
the
OH
O O OH
12
and
OH
O
21
O
O
O
O
O
OH
HO O
9 OH O
O
OH
O
OH 8 O
O
O O
O
as metal Pd oxidation were responsible for catalyst
O O
17
O
O
O
O
7 O
HO
20
OH
O
HO
OH HO
OH
O
O OH
17
O
O
18
OH
HO
O
11
6
10
5
2 3
4
internal standard
100
23 15 13 14 16
12
7
8
18
pine conversion monomer aromatics yield
22 19 20 21
80
6
9
12
15
18
21
24
Conversion and yield (%)
1
27
Retention time (min)
Fig.9 GC-MS spectrum of liquid product from pine valorization over Pd/MgO-C-700 catalyst.
60
40
20
Reaction conditions: 100mg of Pd/MgO-C-700, 200mg of Pine 0 run-1
material (about 40 mesh), EtOAc/H2O = 4:1, 15 bar of H2, 160°C, 4 h.
run-2 Run times
run-3
Fig.11 Pine conversion and monomer aromatics yield from the reactions over fresh and spent Pd/MgO-C-700 catalysts.
* MgO
*
◆
C
☆
▼Fe
O3
Fe3O4
2
PdO
@ PdO
2
★
Pd
* Intensity (a.u.)
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
Page 14 of 17
fresh
◆
▼
★
*
★
* *
★
run-1
▼
run-2 ☆
run-3
Fig.10 The spectrum of HSQC of products (removed solvents)
10
from pine degradation over Pd/MgO-C-700 catalyst
20
30
40 50 2θ (degree)
@
60
70
80
Fig.12 XRD patterns of fresh and spent Pd/MgO-C-700 catalyst
In order to investigate catalyst stability and recyclability, the recycle experiments of pine valorization were
performed
over
Pd/MgO-C-700
and
Associated content
the
characterization of catalyst after every run reaction were analyzed by XRD analysis. From Fig.11, the types of
Author Information
products did not changed, however, the conversion of pine and the yield of monomer aromatics were obviously
Corresponding Author
decreased. After the third run, both the pine conversion
E-mail address:
[email protected],
[email protected] and monomer aromatics yield were decreased from 95.7%
Tel.: +86-20-37029721; Fax: +86-20-87057673
and 24.6% to 68.2% and 11.3%, respectively. These undesired result of repeat reactions mainly ascribed to the
Notes
decreased of metal Pd and MgO activities with the
The authors declare no competing financial interest.
increasing times of Pd/MgO-C-700 catalyst reuse. The decreased of metal Pd and MgO activities were well
Acknowledgements
consistent with the characterization of the spent
This work was supported by NSFC (Natural Science
14
ACS Paragon Plus Environment
Page 15 of 17 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
Foundation of China) project (No. 51606205, 51676191,
treated lignin for the production of green chemicals. Bioresource
51536009) and CAS Pioneer Hundred Talents Program.
Technol 2011, 102 (7), 4917-4920. 12. Yuan, Z. S.; Cheng, S. N.; Leitch, M.; Xu, C. B., Hydrolytic
Keywords:
C-O ester cleavage, β-O-4 lignin-type
degradation of alkaline lignin in hot-compressed water and ethanol.
dimers, depolymerization, C modified MgO, acid-base
Bioresource Technol 2010, 101 (23), 9308-9313.
property, palladium catalyst.
13. Roberts, V. M.; Stein, V.; Reiner, T.; Lemonidou, A.; Li, X. B.; Lercher,
J.
A.,
Towards
Quantitative
Catalytic
Lignin
Reference
Depolymerization. Chem-Eur J 2011, 17 (21), 5939-5948. 14.
1. Ferrini, P.; Rinaldi, R., Catalytic Biorefining of Plant Biomass to
Mahmood, N.; Yuan, Z. S.; Schmidt, J.; Xu, C. B., Production of
Non-Pyrolytic Lignin Bio-Oil and Carbohydrates through Hydrogen
polyols via direct hydrolysis of kraft lignin: Effect of process
Transfer Reactions. Angew Chem Int Edit 2014, 53 (33), 8634-8639.
parameters. Bioresource Technol 2013, 139, 13-20.
2. Li, C.; Zhao, X.; Wang, A.; Huber, G. W.;Zhang, T., Catalytic
15. Toledano, A.; Serrano, L.; Labidi, J.,Organosolv lignin
Transformation of Lignin for the Production of Chemicals and Fuels.
depolymerization with different base catalysts. J Chem Technol Biot
Chemical reviews 2015, 115 (21), 11559-11624.
2012, 87 (11), 1593-1599.
3. Van den Bosch, S.; Schutyser, W.; Vanholme, R.; Driessen, T.;
16. Li, W. Z.; Dou, X. M.; Zhu, C. F.; Wang, J. D.; Chang, H. M.;
Koelewijn, S. F.; Renders, T.; DeMeester, B.; Huijgen, W. J. J.; Dehaen,
Jameel, H.; Li, X. S., Production of liquefied fuel from
W.;Courtin, C. M.; Lagrain, B.; Boerjan, W.; Sels, B.F., Reductive
depolymerization of kraft lignin over a novel modified nickel/H-beta
lignocellulose fractionation into soluble lignin-derived phenolic
catalyst. Bioresource Technol 2018, 269, 346-354.
monomers and dimers and processable carbohydrate pulps.Energy
17. Mortensen, P. M.; Grunwaldt, J. D.; Jensen, P. A.; Knudsen, K. G.;
Environ. Sci. 2015, 8 (6), 1748-1763.
Jensen, A. D., A review of catalytic upgrading of bio-oil to engine fuels.
4. Somerville, C.; Youngs, H.; Taylor, C.;Davis, S. C.; Long, S. P.,
Appl Catal a-Gen 2011, 407 (1-2), 1-19.
Feedstocks for Lignocellulosic Biofuels. Science 2010, 329 (5993),
18. Tuck, C. O.; Perez, E.; Horvath, I. T.; Sheldon, R. A.; Poliakoff, M.,
790-792.
Valorization of Biomass: Deriving More Value from Waste. Science
5. Galkin, M. V.; Dahlstrand, C.; Samec, J. S. M., Mild and Robust
2012, 337 (6095), 695-699.
Redox-Neutral Pd/CCatalyzed Lignol -O-4 Bond Cleavage through a
19. Besson, M.; Gallezot, P.; Pinel, C., Conversion of Biomass into
Low-Energy-Barrier Pathway. Chemsuschem 2015, 8 (13), 2187-2192.
Chemicals over Metal Catalysts. Chemical reviews 2014, 114 (3),
6. Zaheer, M.; Kempe, R., Catalytic Hydrogenolysis of Aryl Ethers: A
1827-1870.
Key Step in Lignin Valorization to Valuable Chemicals. Acs Catal 2015,
20. Toledano, A.; Serrano, L.; Pineda, A.; Romero, A. A.; Luque, R.;
5 (3), 1675-1684.
Labidi, J., Microwaveassisted depolymerisation of organosolv lignin
7. Shuai, L.; Amiri, M. T.; Questell-Santiago, Y. M.; Heroguel, F.; Li,
via mild hydrogen-free hydrogenolysis: Catalyst screening. Appl Catal
Y. D.; Kim, H.; Meilan, R.; Chapple, C.; Ralph, J.; Luterbacher, J. S.,
B-Environ 2014, 145, 43-55.
Formaldehyde stabilization facilitates lignin monomer production
21. Torr, K. M.; van de Pas, D. J.; Cazeils, E.; Suckling, I. D., Mild
during biomass depolymerization. Science 2016, 354 (6310), 329-333.
hydrogenolysis of in-situ and isolated Pinus radiata lignins.
8. Wang, M.; Zhang, X. C.; Li, H. J.; Lu, J. M.; Liu, M. J.; Wang, F.,
Bioresource Technol 2011, 102 (16), 7608-7611.
Carbon Modification of Nickel Catalyst for Depolymerization of
22. Zhao, C.; Kou, Y.; Lemonidou, A. A.; Li, X. B.; Lercher, J. A.,
Oxidized Lignin to Aromatics. Acs Catal 2018, 8 (2), 1614-1620.
Highly Selective Catalytic Conversion of Phenolic Bio-Oil to Alkanes.
9. Kelley, P.; Lin, S. B.; Edouard, G.; Day, M. W.; Agapie, T., Nickel-
Angew Chem Int Edit 2009, 48 (22), 3987-3990.
Mediated Hydrogenolysis of C-O Bonds of Aryl Ethers: What Is the
23. Yan, N.; Yuan, Y. A.; Dykeman, R.; Kou, Y. A.; Dyson, P. J.,
Source of the Hydrogen? J Am Chem Soc 2012, 134 (12), 5480-5483.
Hydrodeoxygenation of LigninDerived Phenols into Alkanes by Using
10. Lohr, T. L.; Li, Z.; Assary, R. S.; Curtiss, L. A.; Marks, T. J., Mono-
Nanoparticle Catalysts Combined with Bronsted Acidic Ionic Liquids.
and tri-ester hydrogenolysis using tandem catalysis. Scope and
Angew Chem Int Edit 2010, 49 (32), 5549-5553. 24. Zhao, C.; He, J.
mechanism (vol 9, pg 550, 2016). Energ Environ Sci 2017, 10 (9),
Y.; Lemonidou, A. A.; Li, X. B.; Lercher, J. A., Aqueous-phase
2042-2042.
hydrodeoxygenation of bio-derived phenols to cycloalkanes. J Catal
11. Lavoie, J. M.; Bare, W.; Bilodeau, M., Depolymerization of steam-
2011, 280 (1), 8-16.
15
ACS Paragon Plus Environment
ACS Sustainable Chemistry & Engineering 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
25. Geboers, J.; Van de Vyver, S.; Carpentier, K.; Jacobs, P.; Sels, B.,
Chem Int Edit 2018, 57 (24), 7071-7075.
Hydrolytic hydrogenation of cellulose with hydrotreated caesium salts
37. Liu, W. G.; Zhang, L. L.; Liu, X.; Liu, X. Y.;Yang, X. F.; Miao, S.;
of heteropoly acids and Ru/C. Green Chem 2011, 13 (8), 2167-2174.
Wang, W. T.; Wang, A. Q.; Zhang, T., Discriminating Catalytically
26. Deuss, P. J.; Scott, M.; Tran, F.; Westwood, N. J.; de Vries, J. G.;
Active FeNx Species of Atomically Dispersed Fe-N-C Catalyst for
Barta, K., Aromatic Monomers by in Situ Conversion of Reactive
Selective Oxidation of the C-H Bond. J Am Chem Soc 2017, 139 (31),
Intermediates in the Acid-Catalyzed Depolymerization of Lignin. J Am
10790-10798.
Chem Soc 2015, 137 (23), 7456-7467.
38. Wei, D. C.; Liu, Y. Q.; Wang, Y.; Zhang, H.L.; Huang, L. P.; Yu, G.,
27. Sluiter;, A.; Hames;, B.; Scarlata;, R. R. C.; Sluiter;, J.; Templeton;,
Synthesis of N-Doped Graphene by Chemical Vapor Deposition and Its
D.; Crocker, D., Determination of structural carbohydrates and lignin
Electrical Properties. Nano Lett 2009, 9 (5), 1752-1758.
in biomass. Version 08-03-2012, 1-18. http://www.nrel.gov /biomass/
39. Wang, S. X.; Yang, L. P.; Stubbs, L. P.; Li, X.; He, C. B., Lignin-
analytical_procedu res.html 2008.
Derived Fused Electrospun Carbon Fibrous Mats as High Performance
28. Lv, W.; Si, Z.; Tian, Z. P.; Wang, C. G.; Zhang, Q.; Xu, Y.; Wang,
Anode Materials for Lithium Ion Batteries. Acs Appl Mater Inter 2013,
T. J.; Ma, L. L., Synergistic Effect of EtOAc/H2O Biphasic Solvent
5 (23), 12275-12282.
and Ru/C Catalyst for Cornstalk Hydrolysis Residue Depolymerization.
40. Wang, S. P.; Wang, J.; Zhu, M. L.; Bao, X. B.; Xiao, B. Y.; Su, D.
Acs Sustain Chem Eng 2017, 5 (4), 2981-2993.
F.; Li, H. R.; Wang, Y., Molybdenum-Carbide-Modified Nitrogen-
29. Zhang, Y. J.; Wang, H. L.; Yuan, H. K.; Shi, F., Hydroxyl Group-
Doped Carbon Vesicle Encapsulating Nickel Nanoparticles: A Highly
Regulated Active Nano-Pd/C Catalyst Generation via in Situ
Efficient, Low-Cost Catalyst for Hydrogen Evolution Reaction. J Am
Reduction of Pd(NH3)(x)Cl-y/C for N-Formylation of Amines with
Chem Soc 2015, 137 (50), 15753-15759.
CO2/H-2. Acs Sustain Chem Eng 2017, 5 (7), 5758-5765.
41. Gupta, A.; Chen, G.; Joshi, P.; Tadigadapa, S.; Eklund, P. C., Raman
30. Zhang, X. F.; Dong, P.; Zhang, Y. J.; Yang, X. K.; Xia, S. B.; Jin, Z.
scattering from highfrequency phonons in supported n-graphene layer
H.; Xu, M. L., Pd Nanoparticles Self-Assembled on FluorineModified
films. Nano Lett 2006, 6 (12), 2667-2673.
MWCNTs as Electro-Catalysts for Methanol Electro-Oxidation. Nano
42. Ni, Z. H.; Wang, H. M.; Kasim, J.; Fan, H. M.; Yu, T.; Wu, Y. H.;
2017, 12 (3) DOI: 10. 1142/S179329201750031X.
Feng, Y. P.; Shen, Z. X., Graphene thickness determination using
31. Liu, B. L.; Wu, F. Q.; Gui, H.; Zheng, M.; Zhou, C. W., Chirality-
reflection and contrast spectroscopy. Nano Lett 2007, 7 (9), 2758-2763.
Controlled Synthesis and Applications of Single-Wall Carbon
43. Das, A.; Pisana, S.; Chakraborty, B.; Piscanec, S.; Saha, S. K.;
Nanotubes. Acs Nano 2017, 11 (1), 31-53.
Waghmare, U. V.; Novoselov, K. S.; Krishnamurthy, H. R.; Geim, A.
32. Li, Y.; Cui, R. L.; Ding, L.; Liu, Y.; Zhou, W. W.; Zhang, Y.; Jin, Z.;
K.; Ferrari, A. C.; Sood, A. K., Monitoring dopants by Raman
Peng, F.; Liu, J., How Catalysts Affect the Growth of Single-Walled
scattering in an electrochemically top-gated graphene transistor. Nat
Carbon Nanotubes on Substrates. Adv Mater 2010, 22 (13), 1508-1515.
Nanotechnol 2008, 3 (4), 210-215.
33. Li, M. H.; Liu, X. Y.; Zhao, X. L.; Yang, F.; Wang, X.; Li, Y.,
44. Graf, D.; Molitor, F.; Ensslin, K.; Stampfer, C.; Jungen, A.; Hierold,
Metallic Catalysts for Structure-Controlled Growth of Single-Walled
C.; Wirtz, L., Spatially resolved raman spectroscopy of single- and
Carbon Nanotubes. Topics Curr Chem 2017,375 (2), DOI:
fewlayer graphene. Nano Lett 2007, 7 (2), 238-242. 45. Crossley, S.;
10.1007/s41061-017-0116-9.
Faria, J.; Shen, M.; Resasco, D. E., Solid Nanoparticles that Catalyze
34. Lu, C. G.; Liu, J., Controlling the diameter of carbon nanotubes in
Biofuel Upgrade Reactions at the Water/Oil Interface. Science 2010,
chemical vapor deposition method by carbon feeding. J Phys Chem B
327 (5961), 68-72.
2006, 110 (41), 20254-20257.
46. Wang, J. D.; Li, W. Z.; Wang, H. Z.; Ma, Q. Z.; Li, S.; Chang, H.
35. Liu, W. G.; Zhang, L. L.; Yan, W. S.; Liu, X. Y.; Yang, X. F.; Miao,
M.; Jameel, H., Liquefaction of kraft lignin by hydrocracking with
S.; Wang, W. T.; Wang, A. Q.; Zhang, T., Single-atom dispersed Co-N-
simultaneous use of a novel dual acid-base catalyst and a
C catalyst: structure identification and performance for hydrogenative
hydrogenation catalyst. Bioresource Technol 2017, 243, 100-106.
coupling of nitroarenes. Chem Sci 2016, 7 (9), 5758-5764.
47. Huang, X. M.; Atay, C.; Koranyi, T. I.; Boot, M. D.; Hensen, E. J.
36. Liu, W. G.; Chen, Y. J.; Qi, H. F.; Zhang, L. L.; Yan, W. S.; Liu, X.
M., Role of Cu-Mg-Al Mixed Oxide Catalysts in Lignin
Y.; Yang, X. F.; Miao, S.; Wang, W. T.; Liu, C. G.; Wang, A. Q.; Li, J.;
Depolymerization in Supercritical Ethanol. Acs Catal 2015, 5 (12),
Zhang, T., A Durable Nickel Single-Atom Catalyst for Hydrogenation
7359-7370.
Reactions and Cellulose Valorization under Harsh Conditions. Angew
48. Lv, Y.; Li, J.; Feng, S.; Liu, P. L.; Hao, F.; Xiong, W.; Luo, H. A.,
16
ACS Paragon Plus Environment
Page 16 of 17
Page 17 of 17 1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Sustainable Chemistry & Engineering
Multi-walled carbon nanotubes supported nickel nanoparticles doped
60. Lancefield, C. S.; Ojo, O. S.; Tran, F.; Westwood, N. J., Isolation
with magnesia and copper for adiponitrile hydrogenation with high
of Functionalized Phenolic Monomers through Selective Oxidation
activity and chemoselectivity under mild conditions. Chem Eng J 2018,
and C-O Bond Cleavage of the beta-O-4 Linkages in Lignin. Angew
346, 203-216.
Chem Int Edit 2015, 54 (1), 258-262.
49. Bai, C. H.; Li, A. Q.; Yao, X. F.; Liu, H. L.; Li, Y. W., Efficient and selective aerobic oxidation of alcohols catalysed by MOF-derived Co catalysts. Green Chem 2016, 18 (4), 1061- 1069. 50. Chatterjee, A.; Jensen, V. R., A Heterogeneous Catalyst for the Transformation of Fatty Acids to alpha-Olefins. Acs Catal 2017, 7 (4), 2543-2547. 51. Jiang, F.; Zeng, L.; Li, S. R.; Liu, G.; Wang, S. P.; Gong, J. L., Propane Dehydrogenation over Pt/TiO2-Al2O3 Catalysts. Acs Catal 2015, 5 (1), 438-447. 52. Fu, P. F.; Zhang, P. Y.; Li, J., Photocatalytic degradation of low concentration formaldehyde and simultaneous elimination of ozone byproduct using palladium modified TiO2 films under UV254+185nm irradiation. Appl Catal BEnviron 2011, 105 (1-2), 220-228. 53. Wang, Y.; Yao, J.; Li, H. R.; Su, D. S.; Antonietti, M., Highly Selective Hydrogenation of Phenol and Derivatives over a Pd@Carbon Nitride Catalyst in Aqueous Media. J Am Chem Soc 2011, 133 (8), 2362-2365. 54. Yin, F. X.; Ji, S. F.; Wu, P. Y.; Zhao, F. Z.; Li, C. Y., Deactivation behavior of Pd-based SBA-15 mesoporous silica catalysts for the catalytic combustion of methane. J Catal 2008, 257 (1), 108-116. 55. Zheng, Y.; Kovarik, L.; Engelhard, M. H.; Wang, Y. L.; Wang, Y.; Gao, F.; Szanyi, J., LowTemperature Pd/Zeolite Passive NOx, Adsorbers: Structure, Performance, and Adsorption Chemistry. J Phys Chem C 2017, 121 (29), 15793-15803. 56. Jastrzebski, R.; Constant, S.; Lancefield, C. S.; Westwood, N. J.; Weckhuysen, B. M.; Bruijnincx, P. C. A., Tandem Catalytic Depolymerization of Lignin by Water-Tolerant Lewis Acids and Rhodium Complexes. Chemsuschem 2016, 9 (16), 2074-2079. 57. Ito, H.; Imai, T.; Lundquist, K.; Yokoyama, T.; Matsumoto, Y., Revisiting the Mechanism of beta-O-4 Bond Cleavage during Acidolysis of Lignin. Part 3: Search for the Rate-Determining Step of a Non-Phenolic C-6-C-3 Type Model Compound. J Wood Chem Technol 2011, 31 (2), 172-182. 58. Lohr, T. L.; Li, Z.; Marks, T. J., Selective Ether/Ester C-O Cleavage of an Acetylated Lignin Model via Tandem Catalysis. Acs Catal 2015, 5 (11), 7004-7007. 59. Luo, N. C.; Wang, M.; Li, H. J.; Zhang, J.; Liu, H. F.; Wang, F., Photocatalytic OxidationHydrogenolysis of Lignin beta-O-4 Models via a Dual Light Wavelength Switching Strategy. Acs Catal 2016, 6 (11), 7716-7721.
17
ACS Paragon Plus Environment