J. He et al. / Applied Catalysis A: General 510 (2016) 11–19
17
three successive runs exhibits a lower GVL yield, which may be
resulted from insoluble organics deposited on the surface of the cat-
alyst. Fig. S16 illustrates the TG analyses of fresh Al7Zr3-300, used
Al7Zr3-300 catalysts (after four times) calcined at 300 ◦C for 4 h or
10 h. 24.5% of loss weight in total was observed for used Al7Zr3-
300 catalyst (after four times) calcined at 300 ◦C for 4 h, which was
larger than that of fresh Al7Zr3-300. It was indicated that the deac-
tivation of Al7Zr3-300 after successively used four times could be
ascribed to insoluble organics or polymer deposits on the used cata-
lyst, and calcination of the catalyst for 4 h at 300 ◦C may be not fully
enough to remove the organic matters. By prolonging the calcina-
tion time from 4 to 10 h, the total loss weight of the used Al7Zr3-300
catalyst was less (Fig. S16), which demonstrated that insoluble
organics or polymer deposited on the used catalyst could be signif-
icantly removed after longer calcination time at 300 ◦C. Moreover,
the deduction could be further confirmed by the carbon residues
and BET surface areas of those fresh and used catalysts (Table S4 and
Fig. S17). The concentrations of both acid and base sites of the used
Al7Zr3-300 catalyst after four times calcined at 300 ◦C for 10 h were
evaluated by NH3-TPD and CO2-TPD, respectively (Fig. S18). The
total acid and base density of the regenerated Al7Zr3-300 catalyst
(i.e., the Al7Zr3-300 catalyst was recovered in the fourth cycle and
calcined at 300 ◦C for 10 h) was 1.87 and 1.28 mmol/g, respectively,
which were close to those of the fresh Al7Zr3-300 catalyst (total
acid and base density: 1.98 and 1.35 mmol/g, respectively). There-
fore, carbon deposits, leading to the deactivation of the Al7Zr3-300
catalyst after four successive cycles, could be removed by regen-
eration of the catalyst at a calcination temperature of 300 ◦C for
10 h.
Fig. 8. Recyclability of Al7Zr3-300 on the synthesis of GVL from EL. Reaction condi-
tions: 1 mmol EL, 5 mL 2-propanol, 0.072 g Al7Zr3-300, T = 220 ◦C, t = 4 h.
To verify whether the catalytic process was heterogeneous or
homogeneous, the Al7Zr3-300 catalyst was removed from the reac-
tion solution by filtration after reacting for 2 h at 220 ◦C. The filtrate
without solid catalyst was continued to react at 220 ◦C for another
2–8 h. As shown in Fig. S14, stable yields of GVL (around 49%) were
observed after removal of the Al7Zr3-300 catalyst, while a sharp
increase in GVL yield was detected in the presence of the cata-
lyst for reacting an additional 2 h. Moreover, the ICP analysis of the
solution demonstrates that below 0.5 ppm zirconium and 0.7 ppm
aluminium anions leached into the alcoholic solution. These results
demonstrated that Al7Zr3-300 was heterogeneous in the produc-
tion of GVL from EL.
The catalytic performance of Al7Zr3-300 was further compared
with those of reported catalysts in the production of GVL from
levulinic acid or its esters in alcohols. As shown in Table S5, the
Al7Zr3-300 catalyst was found to exhibit comparable catalytic
activity with other catalysts. In this respect, Al7Zr3-300 prepared
through this cheap and facile approach shows a promising poten-
tial to be used a heterogeneous catalyst for converting biomass
derivatives into GVL.
3.8. Catalyst recycling
It is of great importance and significance to prepare a catalyst
with good recyclability. The catalytic stability of the Al7Zr3-300
catalyst was investigated for the conversion of EL to GVL in 5 mL
2-propanol under the same conditions. After the reaction was fin-
ished, the reused catalyst was collected by centrifugation, washed
with water, ethanol and acetone three times in the ultrasonic
respectively, dried at 100 ◦C for 2 h and subsequently calcined at
300 ◦C for 4 h, then the recovered catalyst was used for the next
run under the identical reaction conditions. The results are pre-
sented in Fig. 8, a visibly decrease in yield of GVL and conversion of
EL are found in four consecutive cycles. It was reported that some
organic compounds, which were considered as by-products, would
be formed in the production of GVL from EL through CTH process
[66]. We inferred that some of insoluble organics or polymers were
generated from those organic compounds including by-products,
unreacted EL, synthesized GVL, and some intermediates through a
series of reactions such as aldol addition and condensation. After
reusing for four consecutive cycles, the regenerated Al7Zr3-300 by
calcination at 300 ◦C for 10 h exhibited GVL yield (82.4%) as high as
the fresh catalyst (83.2%).
4. Conclusions
In this study, a series of Al2O3–ZrO2 catalysts were prepared by
a simply co-precipitation method, and the morphologies and cat-
alytic activities of those prepared catalysts were characterized and
investigated for conversion of EL to GVL. Various reaction param-
eters, such as Al/Zr mole ratios, calcination temperature, reaction
temperature and reaction time, catalyst dosage, and different alco-
hols as hydrogen donor, have been studied. Al7Zr3 calcined at 300 ◦C
was found to exhibit the highest catalytic activity for the produc-
tion of GVL from EL. A high GVL yield of 83.2% with an excellent
EL conversion of 95.5% was obtained when 2-propanol was used
as hydrogen donor at 220 ◦C for 4 h. Notably, a maximum GVL
yield of 88.6% could be achieved while the mass ratio of EL and
Al7Zr3-300 reached 1:1. It could be concluded that the addition of
Al to ZrO2 enlarged the surface area as well as increased the num-
ber of catalytic effective acid and base sites on those catalysts for
producing GVL from EL. Moreover, the increased contents of acid
sites along with the introduction of Al species into mixed oxides
were almost assigned to Lewis acid sites, which could promote the
CTH process for GVL production. Poisoning and leaching experi-
ments verified that the acid–base properties might contribute to
superior activity of Al7Zr3-300 in the production of GVL from EL,
and that the catalytic system was truly heterogeneous. Further-
more, a slight loss on catalytic activity could be observed after
the catalyst was reused four times, which was demonstrated to
be caused by the insoluble organic species deposited on the sur-
To shed light on the deactivation of Al7Zr3-300 after succes-
sively used for four times and its regeneration through calcination
at 300 ◦C for 4 or 10 h, XRD, TG analyses, N2-adsorption–desorption,
elemental analyses and TPD were used to characterize the fresh
and used Al7Zr3-300 catalysts. Fig. S15 shows the XRD patterns of
the fresh and used Al7Zr3-300 catalysts, it is clearly seen that the
Al7Zr3-300 catalyst after one run almost shows no changes in com-
parison with fresh Al7Zr3-300; nevertheless, the Al7Zr3-300 after