Q. Zhang et al.
AppliedCatalysisA,General574(2019)10–24
immobilization of BAILs is therefore the foremost strategy to solve the
separation and recovery problems. Owing to fascinating morphological
and textural properties, hierarchically porous nitrogen-doped carbons
(NHPCs) are selected as the supports for the immobilization of BAILs.
The NHPCs are prepared by a single step CaCO3 nanoparticle-directed
nanocasting approach combined with K2C2O4 chemical activation
during carbonization of glucose and urea/melamine. Functionalization
of the NHPCs via quaternary ammonization by 1,3-propanesultone
followed by anion exchange with HSO3CF3 results in the GU‒[C3N]
[SO3CF3] and GM‒[C3N][SO3CF3] (C3 = PrSO3H); moreover, by
changing initial urea-to-glucose weight ratio in the preparation sys-
tems, nitrogen element contents and thereby Brønsted acid site den-
sities, BET surface areas and meso/micropore proportions of the NHPCs
can be well-adjusted, which may obviously influence the catalytic ac-
tivity of the resulting GU‒[C3N][SO3CF3].
respectively, and the process followed by modified literature method
[11]. Typically, glucose (8.9, 6.7 and 3.4 g, respectively) and urea (1.1,
3.3 and 6.6 g, respectively) were thoroughly ground into powder with
K2C2O4 and then with CaCO3 nanoparticles (particle size of 50–70 nm,
Fig. S1a, purchased from Zhejiang Tianshi Nano Technology Co. LTD,
China) at a weight ratio of (glucose + urea)-to-K2C2O4-to-CaCO3 of
1:1:1. The mixture was firstly heated to 250 °C at a ramp of 5 °C min−1
and held for 10 min. Afterwards, the mixture was continuously heated
to 750 °C at the same ramp heating rate and held for 1 h. Finally, the
furnace was cooled down to 200 °C in 2 h. The above process was car-
ried out under flowing nitrogen gas. After cooling to room temperature,
the black product was washed with diluted HCl for several times to
remove inorganic impurities such as calcium oxide nanoparticles and
potassium compounds generated during the calcination process, and
then it was further washed with water until the filtrate was neutral in
acidity. NHPCs were finally obtained after air-drying at 100 °C for 12 h,
and it was denoted as GU‒x (G and U represent glucose and urea, re-
spectively). Here, x = 1, 2 and 3, respectively, representing GU with
different nitrogen element contents (Table S1 of supplementary in-
formation). Additionally, the other NHPC support (denoted as GM‒2)
was also prepared following the above process and using melamine as a
nitrogen precursor, and the weight ratio of (glucose + melamine)-to-
K2C2O4-to-CaCO3 was 1:1:1 (in which weight ratio of glucose-to-mel-
amine was 2:1). The absence of residual potassium and calcium in as-
prepared various GU/GM supports were confirmed by a Leeman
Prodigy Spec (I) ICP-AES determination after the samples were calcined
in flowing air gas at 600 °C followed by dissolving with dilute HNO3.
Functionalization of GU/GM supports with BAILs was carried out by
the following process. Typically, GU/GM support (0.6 g) was dispersed
in 10 mL toluene solution containing 1,3-propane sultone (0.15 g or
1.26 mmol), and the mixture was continuously stirred at toluene re-
fluxing temperature (110 °C) for 12 h. Afterwards, the mixture was
cooled to room temperature, and HSO3CF3 (0.1 mL or 1.13 mmol) was
added. The resulting mixture was stirred vigorously at room tempera-
ture for 12 h, and then it was rested at room temperature for another
12 h. The solid was obtained by centrifugation, and then it was washed
with abundant dichloromethane at room temperature until the ad-
sorbed BAILs were removed completely. Finally, the product was dried
at 80 °C for 12 h, and it was denoted as GU‒[C3N][SO3CF3]‒x or
GM‒[C3N][SO3CF3]‒2 (C3 = PrSO3H; x = 1, 2 and 3).
Pyrolysis biofuels are produced from fast pyrolysis of waste bio-
mass, and they are promising candidates to replace petroleum fuels
[23–25]. However, raw pyrolysis biofuels are a mixture of acids, alco-
hols, furans, aldehydes, esters, ketones, sugars and multifunctional
compounds [26,27], which lead to them unfavorable properties in-
cluding low heating value, immiscibility with petroleum fuels, thermal
and chemical instability as well as corrosiveness because of their high
oxygen content (20–50 wt.%) and high acidity (pH = 2.5–3) [28–31].
Accordingly, the direct use of fast pyrolysis biofuels is limited, and they
need to be upgraded, e.g., catalytic hydrotreating, to reduce oxygen
content and therefore to satisfy the requirements of boiler fuels or the
additive for the petroleum fuels. Prior to the catalytic hydrotreating, it
is crucial to reduce acidity and oxygen content to a large extent, which
can increase the stability and decrease hydrogen consumption in sub-
sequent upgrading steps. As one of the small oxygenates, acetic acid is
abundant in raw pyrolysis biofuels (ca. 1–10 wt.%) [31], and removal
of acetic acid can remarkably decrease the acidity and improve the
stability of fast pyrolysis biofuels. Ketonization and esterification of
acetic acid are two promising catalytic processes for raw pyrolysis
biofuel pretreatment; moreover, esterification affords a simpler and
more effective process. Acid-catalytic esterification of acetic acid with
methanol or ethanol is a common strategy to reduce the acidity and
viscosity of raw pyrolysis biofuels [32,33]. However, oxygen content of
raw pyrolysis biofuels is unchanged. Both the yielded water and ester is
expected to be eliminated continuously if a continuous process is to
operate via reactive distillation, as a consequence, oxygen content is
decreased, together with high yield of the ester because of the complete
esterification equilibria. For this purpose, alcohols with boiling points
higher than water are chosen to avoid alcohol loss during distillation.
PrSO3H/SBA-15-, resin- or zeolite-catalyzed esterifications of acetic
acid with high boiling point alcohols such as benzyl alcohol, o-cresol,
m-cresol, p-cresol or anisyl alcohol have been studied [31,34–36].
Here the GU/GM‒[C3N][SO3CF3] are successfully applied in cata-
lytic esterification of acetic acid with benzyl alcohol or 4-methox-
ybenzyl alcohol to produce benzyl acetate or 4-methoxybenzyl acetate
in a simulated pyrolysis biofuel environment by using toluene as the
representative of non-polar lignin derivative, and the yielded benzyl
acetate or 4-methoxybenzyl acetate are value-added chemicals
[37–39]. It shows that esterification activity of the GU/GM‒[C3N]
[SO3CF3] outperforms Amberlyst-15 resin and HY zeolite. The excellent
esterification activity of the prepared catalysts is explained in terms of
super strong Brønsted acidity and unique hierarchically porous struc-
ture; additionally, macro/meso/micropore proportion of the catalysts
affects the esterification activity.
2.2. Characterization of BAIL-functionalized NHPCs
Nitrogen (N, %) and sulfur (S, %) element contents in as-prepared
catalysts were determined by a EuroVector CHNS EA3000 elemental
analyzer. FESEM observations were performed on a XL-30 ESEMFEG
field emission scanning electron microscope. Nitrogen gas adsorption/
desorption isotherms were measured on a Micromeritics ASAP 2020
PLUS HD88 surface area and porosity analyzer, and the samples were
outgassed under vacuum at 363 K for 1 h and 373 K for another 12 h
before the measurement. BET surface area (SBET) was calculated using
Brunauer–Emmett–Teller (BET) equation, pore diameter (Dp) was esti-
mated from BJH desorption determination, and pore volume (Vp) was
estimated from the pore volume determination using the adsorption
branch of the N2 isotherm curve at P/P0 = 0.99 single point. Mercury
porosimetry measurement was performed on a Micromeritics Autopore
V mercury porosimeter. Raman scattering spectra were recorded on a
Jobin-Yvon HR 800 instrument with an Ar+ laser source at 488 nm in a
macroscopic configuration. XPS was performed on an Axis Ultra DLD
instrument with a monochromated Al-Kα source at a residual gas
pressure of below 10−8 Pa.
2. Experimental
The Brønsted acid strength of the catalysts was measured by a
WDDY-2008 J microcomputer automatic potentiometric titration in-
strument [40]. The sample (50 mg) was suspended in acetonitrile under
stirring for 24 h, and then the suspension was titrated with 0.1 mol L−1
n-butylamine/acetonitrile solution. The Brønsted acid site density (A,
2.1. Preparation of BAIL functionalized NHPCs
Firstly, NHPCs with different nitrogen contents were prepared by
using glucose anhydrous and urea as carbon and nitrogen precursors,
11