Chun-Hsiang Hsu1, Zheng-Bang Pan1, Chuan-Ren Chen1, Ming-Xue Wei2, Chang-An Chen1, Hong-Ping Lin1, Chun-Han Hsu3. 1. Department of Chemistry, National Cheng Kung University, Tainan City 70101, Taiwan. 2. Department of Resources Engineering, National Cheng Kung University, Tainan City 70101, Taiwan. 3. General Education Center, National Tainan Junior College of Nursing, Tainan City 700, Taiwan.
Abstract
In this study, an economic, sustainable, and green synthesis method of multiporous carbons from agricultural waste, water caltrop shell (denoted as WCS), was presented. To prepare the WCS biochar, the dried WCS was first carbonized to a microporous carbon with a surface area of around 230 m2 g-1 by using a top-lit-updraft method. Then, the microporous WCS biochar was directly mixed with an appropriate amount of ZnO nanoparticles and KOH as activating agents via a solvent-free physical blending route. After further activation at 900 °C, the resulted carbons possess both micropores and mesopores that were named as WCS multiporous carbons. The carbon yield of the prepared WCS multiporous carbons with high surface area in the range of 1175-1537 m2 g-1 is up to 50%. Furthermore, the micropore/mesopore surface area ratio can be simply tuned by controlling the ZnO content. For supercapacitor applications, the as-prepared WCS multiporous carbon electrodes showed high specific capacitance (128 F g-1 at 5 mV s-1) with a good retention rate at 500 mV s-1 scan rate (>60% compared to the capacitance at 5 mV s-1) and low Ohmic resistance in a 1.0 M LiClO4/PC electrolyte. In addition to the ZnO nanoparticles, CaCO3 nanoparticles with low environmental impact were also used to prepare the WCS multiporous carbons. The assembled supercapacitors also demonstrate high specific capacitance (102 F g-1 at 5 mV s-1) and good retention rate (∼70%).
In this study, an economic, sustainable, and green synthesis method of multiporous carbons from agricultural waste, water caltrop shell (denoted as WCS), was presented. To prepare the WCS biochar, the dried WCS was first carbonized to a microporous carbon with a surface area of around 230 m2 g-1 by using a top-lit-updraft method. Then, the microporous WCS biochar was directly mixed with an appropriate amount of ZnO nanoparticles and KOH as activating agents via a solvent-free physical blending route. After further activation at 900 °C, the resulted carbons possess both micropores and mesopores that were named as WCS multiporous carbons. The carbon yield of the prepared WCS multiporous carbons with high surface area in the range of 1175-1537 m2 g-1 is up to 50%. Furthermore, the micropore/mesopore surface area ratio can be simply tuned by controlling the ZnO content. For supercapacitor applications, the as-prepared WCS multiporous carbon electrodes showed high specific capacitance (128 F g-1 at 5 mV s-1) with a good retention rate at 500 mV s-1 scan rate (>60% compared to the capacitance at 5 mV s-1) and low Ohmic resistance in a 1.0 M LiClO4/PC electrolyte. In addition to the ZnO nanoparticles, CaCO3 nanoparticles with low environmental impact were also used to prepare the WCS multiporous carbons. The assembled supercapacitors also demonstrate high specific capacitance (102 F g-1 at 5 mV s-1) and good retention rate (∼70%).
During the last decades,
electrochemical double-layer
capacitors, also named as supercapacitors, are energy storage devices
that store the electrical energy in the interface between the charged
surface of the electrode and the electrolyte solution.[1,2] The supercapacitors have become noticeable because of their excellent
cycle ability, high power density, and high charge/discharge rate
performance compared to batteries.[3] Although
supercapacitors provide higher power in the same volume, they are
not able to store the same amount of charge as batteries do. This
makes supercapacitors suitable for those applications where power
burst is needed, but high energy storage is not required.[4] However, the limitation of its low energy density
increases both the volume and cost of the device. Because of their
low pore volume, the commercially available microporous carbons (pore
size < 2 nm) are not very attractive.[5] Therefore, it is a key issue to design a nanostructured porous carbon
with pore properties specifically tailored for the supercapacitor
application.[6]Nowadays, porous carbon
materials are widely utilized as electrode materials for supercapacitors
owing to their low cost, excellent cycle stability, and easy manufacturing.[7] Among them, multiporous carbons with three-dimensional
mesoporous/microporous structures have become popular in recent years.[8] Multiporous carbons have high potential in applications
such as fuel cells, hydrogen storage devices, dye adsorption, and
energy storage devices.[9] Many methods have
been used for the preparation of porous carbon materials, including
catalytic activation, polymer blend carbonization, organic aerogel
carbonization, and nanocasting.[10,11] Nanocasting involves
using various templates (colloids or mesoporous silica), which has
proven to be particularly efficient.[12] However,
the removal of silica requires the toxic hydrofluoric acid, which
renders the complex and nonenvironment-friendly process. Consequently,
recent studies have investigated the feasibility for synthesizing
porous carbons using nanoparticles as templates, for example, magnesium
and calcium salts, such as magnesium acetate,[13] calcium citrate,[14] and calcium carbonate.[15] These methods yield carbons with mesopores ranging
from 2 to 20 nm. However, they usually use either sucrose or formaldehyde
resin as a carbon precursor. Sucrose requires acid to catalyze polymerization,
while formaldehyde resin produces tar during pyrolysis.[16] Thus, finding more suitable carbon precursors
is still required. Furthermore, these traditional synthesis procedures
are complicated, expensive, time-consuming, and toxic. Hence, they
cannot be commercialized. Development of simple low-cost strategies
for the synthesis of multiporous carbons remains a significant challenge.Previously, our group has used ZnO nanoparticles as hard templates
to prepare mesoporous carbons by using petroleum pitch as the carbon
precursor.[17] The effects of the carbonization
temperature and ZnO/pitch weight ratio on the physical properties
of the multiporous carbons were studied in detail. These results showed
that the specific surface area and pore volume can be easily improved
by adjusting the ZnO/pitch ratio. Although industrial residual petroleum
pitch shows good potential as the carbon precursor, we still tried
to find other cheap and natural carbon precursors. For the sustainable
purpose, biochar derived from agriculture waste is an alternative
because of its rich abundance and availability. Recently, activated
carbons have gained great interest for their utilization as supercapacitor
electrodes because they can be readily prepared from cheap biomass
residues and wastes.[18]In Guantian
District, Tainan, Taiwan, the annual yield of water caltrop is around
3400 tons. For storage and sale, farmers and merchants peel off the
shell from water caltrop. Because of the high lignin content in the
water caltrop shell (denoted as WCS), it takes about 7.79 million
NT dollars to deal with the discarded shells every year. In practice,
the lignin in the WCS can be converted into carbons after pyrolysis.
Thus, WCS has been carbonized already to biochar at Guantian District
by using a top-lit-updraft (TLUD) method via a suitable carbonization
furnace.[19] To increase the
value of the WCS biochar, introducing meso-/micropore surface area
to improve the accessibility and absorption capacity of the WCS biochar.
In this paper, we provided a simple synthetic method by directly blending
the WCS biochar with inorganic ZnO or CaCO3 nanoparticles
and activating agents (KOH) to introduce the mesopores and micropores
into the WCS biochar after high-temperature pyrolysis. The electrochemical
properties of the WCS multiporous carbons for supercapacitors in an
organic electrolyte were evaluated in this study.
Results and Discussion
Using WCS as the Carbon
Precursor
WCS was previously carbonized to biochar in a TLUD
carbonization
furnace at Guantian District, Tainan, Taiwan (see Supporting Information, Figure S1). After washing with an
appropriate amount of H2O to remove the inorganic residuals
in the WCS biochar, the physical properties of the biochar were analyzed.
The scanning electron microscopy (SEM) image shows that the WCS biochar
exhibits many macropores (the pore size is about 30–60 μm)
(Figure a). However,
as can be seen in the SEM image (Figure b), a smooth surface of WCS biochar presents
no micropores even at high magnification. The N2 adsorption–desorption
isotherms of the WCS biochar show type I isotherm with a specific
surface area up to 230 m2 g–1 (Figure c, curve I). This
indicates a mainly microporous structure (pore size < 2 nm).
Figure 1
(a,b) SEM images of the
WCS biochar; (c) N2 sorption isotherms of the WCS biochar
(I) and the WCS multiporous carbon (II); the inset shows a pore size
distribution curve (Horváth–Kawazoe model) for curve
II; and (d) SEM and (e,f) HR-TEM images of the WCS multiporous carbon.
(a,b) SEM images of the
WCS biochar; (c) N2 sorption isotherms of the WCS biochar
(I) and the WCS multiporous carbon (II); the inset shows a pore size
distribution curve (Horváth–Kawazoe model) for curve
II; and (d) SEM and (e,f) HR-TEM images of the WCS multiporous carbon.To introduce mesopores, 20 nm ZnO nanoparticles were used as the
activating agent (Figure S2). The surface
area of the resulted porous carbon is 1537 m2 g–1 when the weight ratio of WCS biochar/ZnO/KOH is 1.0:2.0:0.80 (Figure c, curve II). Compared
to the WCS biochar, the SEM image of the WCS multiporous carbon clearly
exhibits a porous texture with pore size approximately equal to 20
nm. Moreover, the high-resolution transmission electron microscopy
(HR-TEM) images presented in Figure e,f show that the WCS multiporous carbon has both mesopores
and micropores. The detailed textural properties of the WCS multiporous
carbons synthesized with different compositions are listed in Table . The thermogravimetric
analysis (TGA) curve (Figure S3) shows
that the WCS multiporous carbons exhibit good thermal stability even
at 500 °C and the inorganic residual is less than 3 wt %. In
brief, these results show that the WCS biochar can be activated by
ZnO nanoparticles and KOH to produce high surface area multiporous
carbons with yield up to 48 wt %.
Table 1
Specific Surface Area and Porous Parameters of Porous
Carbons
sample (WCS biochar/ZnO/KOH)
SBETa/m2 g–1
Smesob/m2 g–1
Smicroc/m2 g–1
pore volume/cm3 g–1
carbon yieldd (%)
ZnO (1/2/0.8)
1537
791
745
0.89
48
CaCO3 (1/2/0.8)
1305
529
776
0.77
48
For Supercapacitor Application
ZnO (1/2/1)
1438
769
708
0.96
46
CaCO3 (2/1/1.2)
1435
701
733
0.84
44
BET surface area.
Mesopore
surface area.
Micropore
surface area.
Carbon yield/%
= weight of carbon/weight of WCS biochar.
BET surface area.Mesopore
surface area.Micropore
surface area.Carbon yield/%
= weight of carbon/weight of WCS biochar.
Effect
of the ZnO/WCS Biochar Ratio on the Meso-/Micropore
Surface Area
Interestingly, the content of the meso-/micropore
surface area can be easily controlled by adding different amounts
of ZnO nanoparticles at a fixed KOH/WCS biochar weight ratio. As the
weight ratio of ZnO/WCS biochar increases from 0.5 to 2.5, both specific
surface area and mesopore surface area increase significantly (Figure ). This phenomenon
can be ascribed to the reaction between ZnO and carbon at 900 °C
(eqs –3).[20] The additional reduction
process allows the introduction of mesopores via pore widening. However,
when the ratio of the ZnO/WCS biochar reaches 3.0, excessive corrosion
of the carbon structure leads to lower specific surface area and carbon
yield. A scheme of the mesopore formation mechanism is shown in Figure . Briefly, using
easily removable ZnO nanoparticle and KOH as activating agents, multiporous
carbons with a highly connective porous structure can be produced.
Figure 2
Textural
parameters of the WCS multiporous carbons (WCS biochar/KOH/ZnO = 1.0/0.5/0.5–3.0
in weight ratio).
Figure 3
Scheme of the formation mechanism of the mesopore
and micropore in the WCS biochar by using ZnO nanoparticles and KOH
as activating agents.
Textural
parameters of the WCS multiporous carbons (WCS biochar/KOH/ZnO = 1.0/0.5/0.5–3.0
in weight ratio).Scheme of the formation mechanism of the mesopore
and micropore in the WCS biochar by using ZnO nanoparticles and KOH
as activating agents.Figure a shows the Raman spectrum
of the WCS biochar and WCS multiporous carbons. Two broad peaks at
1350 cm–1 (D-band) and 1580 cm–1 (G-band) can be observed. To analyze the defect level of the carbons,
the integrated intensity ratio of the D band to the G band was calculated.
The high ID/IG values (0.71 and 0.75) reveal similar defect level in these carbon
materials. The surface composition of the WCS biochar and WCS multiporous
carbons was investigated by X-ray photoelectron spectroscopy (XPS),
as shown in Figure b,c. The high-resolution C 1s spectra were deconvoluted into three
main peaks. The peak at 284.8 eV can be attributed to the sp2-hybridized carbon (sp2 C–C). Meanwhile, the peaks
at 285.8 and 288.4 eV demonstrate the presence of C–O and C=O
bonds, respectively. From the XPS results, both WCS biochar and WCS
multiporous carbon show high carbon content (77.3 and 85.9%). This
indicates that after further pyrolysis of the WCS biochar, the unstable
oxygen functional groups and defects in the WCS biochar were eliminated,
which is consistent with the Raman results.
Figure 4
(a) Raman spectra and
XPS spectra of the (b)
WCS biochar and (c) WCS multiporous carbons.
(a) Raman spectra and
XPS spectra of the (b)
WCS biochar and (c) WCS multiporous carbons.
WCS Multiporous
Carbons as the Electrode Material
for Supercapacitor Applications
Although various activating
agents or nanotemplating methods have been used to prepare porous
carbons with high surface area (>2000 m2 g–1), the low tap density (0.3–0.4 g cm–3)
and carbon yield[17] make it difficult to
employ them as electrode materials for supercapacitor applications.
In contrast, for WCS multiporous carbons, the tap density can be well
controlled at around 0.6–0.7 g cm–3, which
is suitable for the preparation of supercapacitor devices. Herein,
WCS multiporous carbons were used as electrode materials and 1.0 M
LiClO4/PC was used as an electrolyte to assemble supercapacitors.As can be seen from Figure a, the cyclic voltammetry (CV) curves of these electrodes
show a quasi-rectangular shape at a fast scan rate, suggesting the
ideal capacitor behavior and reversible redox reaction. The specific
capacitance of the WCS multiporous carbons was calculated by integrating
the CV curve area in a 0–1.5 V voltage window with a scan rate
varying from 5.0 to 500.0 mV s–1. Owing to the high
specific surface area, the WCS multiporous carbon supercapacitor has
capacitance up to 128 F g–1 at a slow scan rate
(5.0 mV s–1). The gravimetric capacitance of the
samples at different scan rates is shown in Figure b. As the scan rate increases from 5 to 500
mV s–1, the decrease in capacitance is less than
40%. Furthermore, Figure c shows the cycling performance of the WCS multiporous carbons.
At a scan rate of 100 mV s–1, the above-mentioned
electrodes show a high initial specific capacity of 98 F g–1 and retain 98 F g–1 (>99%) after 10,000 cycles.
Thus, these specific capacities and retention rates of the WCS multiporous
carbon are comparable to those of many reported literature studies
in the organic electrolyte systems.[21−25] This demonstrates that the WCS multiporous carbon electrodes exhibit
high capacity values, high rate performances, and good capacitance
retention, which can be ascribed to the high pore accessibility in
the meso-/microporous structure.[26−28]
Figure 5
(a) CV curves
at scan
rates of 5 and 500 mV s–1, (b) specific capacitance
at different scan rates, and (c) cycling performance at a scan rate
of 100 mV s–1 for the WCS multiporous carbon electrodes.
(a) CV curves
at scan
rates of 5 and 500 mV s–1, (b) specific capacitance
at different scan rates, and (c) cycling performance at a scan rate
of 100 mV s–1 for the WCS multiporous carbon electrodes.The galvanostatic charge/discharge (GCD) curves
of the WCS multiporous carbon electrode under different current densities
all reveal nearly symmetrical triangular shapes (Figure a). Furthermore, as can be
seen from the Nyquist plot (Figure b), in a high-frequency region, the semicircle of the
WCS multiporous carbon electrode has a small diameter, which confirms
the low ionic diffusion resistance within the multiporous carbon matrix.
To evaluate the energy storage performance of the WCS multiporous
carbon supercapacitor, Ragone plots (energy density vs powder density)
are shown in Figure c. The gravimetric values exhibit a high power density of 6564 W
kg–1 at 4.35 W h kg–1 energy density.
To further explore the feasibility of the WCS multiporous carbon,
a 1500 F-class pouch cell-typed supercapacitor has been prepared to
evaluate its electrochemical performance (Figure S4).
Figure 6
(a) GCD
curves under different current densities, (b) Nyquist plots, and (c)
Ragone plot for the WCS multiporous carbon electrodes in a 1.0 M LiClO4/PC electrolyte.
(a) GCD
curves under different current densities, (b) Nyquist plots, and (c)
Ragone plot for the WCS multiporous carbon electrodes in a 1.0 M LiClO4/PC electrolyte.
WCS
Multiporous Carbons Prepared by CaCO3 Nanoparticles
Apart from ZnO nanoparticles, WCS multiporous carbons can also be
prepared with CaCO3 nanoparticles and KOH via the same
activation procedure. The dimension of CaCO3 nanoparticles
is around 50 nm, as shown in Figure S3.
As shown in Figure a, the CaCO3 nanoparticles are also capable of increasing
both the pore volume and surface area. At WCS biochar/CaCO3/KOH weight ratio = 1.0:2.0:0.8, the porous carbon exhibits a specific
surface area up to 1305 m2 g–1 (Figure b and Table ). For the CaCO3 activating
agent, the decomposition of CaCO3 to CaO (eq ) produces CO2 for physical
activation (eqs and 5).
Figure 7
(a) SEM images and (b)
N2 sorption
isotherms for the WCS multiporous carbon prepared by the CaCO3 nanoparticle and its (c) CV curves and (d) Nyquist plots
in a 1.0 M LiClO4/PC electrolyte.
(a) SEM images and (b)
N2 sorption
isotherms for the WCS multiporous carbon prepared by the CaCO3 nanoparticle and its (c) CV curves and (d) Nyquist plots
in a 1.0 M LiClO4/PC electrolyte.The CV (Figure c)
of the as-prepared WCS multiporous carbon also shows quasi-rectangular
curves with symmetric shape. The capacitance values were 102 and 73
F g–1 at 5 and 500 mV s–1 scan
rates, respectively, with a retention rate up to 70%. The Nyquist
plots present similar impedance behavior to that of the ZnO activating
agent, in which the resistance is only 1.0 Ω (Figure d).
Conclusions
In this research, we proposed
a facile solvent-free physical blending method to synthesize the WCS
multiporous carbons with high surface area (>1200 m2 g–1) from the WCS biochar precursor by using ZnO
and CaCO3 nanoparticles for the formation of mesopores
and KOH to produce micropores. Conclusively, the physical blending
method provides a facile way to fabricate the multiporous carbons
from different carbon precursors. The porous structure can be easily
tuned by adjusting the template to biochar weight ratio. With large
surface area, high porous connectivity, and appropriate bulk density,
the multiporous carbons can be assembled to high-performance supercapacitors
with high power density and good retention rate at high scanning rate
(>60%). In future, introduction of high content of nitrogen into
the carbon matrix of the biochars or multiporous carbons will be studied
for catalytic and electrochemical applications.
Experimental
Section
Synthesis of the WCS Multiporous Carbons via
a Physical Blending Method
To synthesize the WCS multiporous
carbons, x g (x = 10.0–50.0
g) of inorganic ZnO or CaCO3 nanoparticles, 10.0 g of carbon
precursor (WCS biochar, from Guantian District, Tainan), and y g (y = 8.0–20.0 g) of the KOH
activating agent were directly blended into a homogeneous mixture
by using a blender. The resulted powder was then sealed in a stainless-steel
container and heated in a furnace. The heating rate was set at 8 °C
min–1 and held at 900 °C for 2 h. After cooling
to room temperature, the sample was washed with water to remove the
alkaline oxides and then soaked in 37% HCl solution to remove the
residual inorganic activation agents. The following solution was then
filtrated, washed, and dried at 100 °C in an oven for 5 h, yielding
the WCS multiporous carbons. A scheme of the synthetic process is
presented in Figure S5 (see the Supporting Information).
Structural Characterization
The thermal
stability of the sample was characterized using a TGA
(TA Instruments Q50, USA), heated from 100 to 800 °C with a ramp
rate of 20 °C min–1 under air. SEM images of
the WCS biochar and WCS multiporous carbon were recorded using a field
emission scanning electron microscope (JEOL JSM7000F, USA). The N2 sorption isotherms of the samples were taken at 77 K on a
Micrometric TriStar II apparatus to estimate the pore size, pore volume,
and surface area. A micro-Raman spectrometer from Renishaw with a
He–Ne laser source with a wavelength of 633 nm was used to
determine the structure of the carbon samples. The XPS spectra of
the samples were recorded using a PHI 5000 VersaProbe ESCA spectrometer
with Al Kα as the excitation source. The XPS analysis results
were calibrated against the C 1s peak at 284.8 eV as an internal standard.
Electrochemical Measurement
A symmetrical
two-electrode capacitor cell was used to examine
the electrochemical performance of the carbon electrodes. Both electrodes
were made by depositing 2.0 mg carbons on a 1.0 cm2 stainless
foil, which acted as a current collector. The cell consisted of two
carbon electrodes, sandwiching a cellulose filter paper as the separator.
CV measurements were conducted between 0 and 1.5 V in a 1.0 M LiClO4/PC electrolyte at sweep rates ranging from 5 to 500 mV s–1. Plots of the specific capacitance versus the voltage
were calculated using the following formula: C =
2I/vm, where I =
current (A), v = scan rate (V s–1), and m denotes the mass (g) of the carbon material
in one electrode. GCD tests were performed in 1.5 V at current densities
up to 18.0 A g–1 in a 1.0 M LiClO4/PC
electrolyte. The specific gravimetric capacitance of a single electrode
(F g–1) determined from the galvanostatic cycles
was calculated by means of the formula: C = 2I/(dV/dt)m, where dV/dt = slope of the discharge
curve (V s–1). Electrochemical impedance spectroscopy
measurements were conducted at an open-circuit voltage (0 V) over
the frequency range of 1 mHz to 100 kHz with a 5.0 mV amplitude.
Authors: Yan Zhang; Lina Zhang; Kang Cui; Shenguang Ge; Xin Cheng; Mei Yan; Jinghua Yu; Hong Liu Journal: Adv Mater Date: 2018-07-31 Impact factor: 30.849
Authors: Tiago C Mendes; Changlong Xiao; Fengling Zhou; Haitao Li; Gregory P Knowles; Matthias Hilder; Anthony Somers; Patrick C Howlett; Douglas R MacFarlane Journal: ACS Appl Mater Interfaces Date: 2016-12-15 Impact factor: 9.229