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G. Mani et al.
Journal of Solid State Chemistry 301 (2021) 122301
condensation of urea, melamine, dicyandiamide and thiourea [8,16].
Various strategies have been adopted for improving the catalytic activity
of gCN [9,17,18], among which physical compounding of gCN with
metal oxides has drawn wide attention [19–21].
was dissolved gradually in 5.5 ml deionized water with constant stirring
to keep the temperature low. To the above CuSO4 clear solution, NaOH
solution was added very slowly with constant stirring. A bluish-black
precipitate appears suddenly. The reaction flask was heated for 45 min
to 1 h while maintaining the temperature at 80ꢀC and stirring the reac-
tion mixture intermediately. The brownish-black thick precipitate of
copper oxide thus obtained was washed with a sufficient amount of
deionized water and filtered free of alkali. It was then dried to remove
any trace of water. The precipitate was ground using mortar and pestle
and used for further synthesis.
CuO, a covalent p-type semiconductor with a bandgap between 1.21
eV and 1.7 eV [22] is well studied for its catalytic activity in various fields
especially in solid propellants [23–25]. It has been reported that cop-
per(II) oxide nanocrystals are suitable additives for catalytic decompo-
sition of AP, and can significantly reduce the high-temperature
decomposition and increase the heat release during decomposition of AP
[24,26–29]. Synthesis of high-quality CuO nanomaterials with chemical
purity, crystallinity, phase selectivity and size homogeneity via a feasible
cost-effective method is still a challenge in materials synthesis [30].
Increasing awareness towards green chemistry and sustainability has
stimulated a desire to develop an eco-friendly burn rate modifier for
composite solid propellants [6]. As a step closer to it, we have synthe-
sized a burn rate catalyst based on gCN with reduced metal content. To
the best of our knowledge, there are still very few reports on gCN based
burn rate modifiers for composite solid propellants [6,20,31,32]. Earlier,
Hosseini et al. reported the synthesis of CuO nanoparticles on
The reaction of formation of CuO can be summarized as follows:
CuSO4 :5H2O þ 2NaOH → CuðOHÞ2 ↓ þ Na2SO4 þ 5H2 O
(1)
Δ
CuðOHÞ2
CuO þ H2O
!
2.1.3. Synthesis of gCN/CuO (gCNCuO) composite
The gCN/CuO composite was synthesized via a facile sonochemical
approach (Fig. 1). A series of four gCN/CuO composites were synthesized
with varying CuO content. The typical procedure for the synthesis of
gCNCuO1 (1: 1) is as follows: 0.2 g of gCN was well dispersed in 45 ml of
methanol by ultrasonication for 30 min. To this, 0.2 g of CuO was added.
The mixture was sonicated for another 1 h and dried at 60ꢀC for 4 h.
Finally, the blackish-grey powder obtained is calcinated at 300ꢀC for 3 h
in the air to strengthen the interaction between leaf-shaped CuO and gCN
matrix. The other composites were also prepared using the same pro-
cedure by changing the concentration of CuO. The ratios between gCN
and CuO in the other prepared composites were 1: 0.6, 1: 0.3 and 1: 0.15
and are represented as gCNCuO2, gCNCuO3, and gCNCuO4 respectively.
three-dimensional
nitrogen-doped
graphene-based
frameworks
(CuO@3D-(N)GFs) for AP decomposition [33]. Zhang et al. synthesized
microwave-assisted m-g-C3N4/CuO through microwave-pretreatment
and mixing-calcination methods. By using this catalyst the decomposi-
tion temperature of AP was decreased by 136ꢀC and heat release was
increased by seven times [34]. Very recently Chandrababu et al. reported
the decomposition kinetics of AP using (Cu/Cu2O)/g-C3N4 nano-
composite via FWO method. Even though the E values for the decom-
position reactions were not decreased, the reaction rate increased
tremendously [35]. Here, we have undertaken an attempt to quantita-
tively interpret the kinetic parameters for the decomposition of AP in
presence of a gCN-CuO catalyst using the Coats-Redfern (CR) method.
Although kinetic compensation effect has been known for long time, not
much efforts have been undertaken to explain the kinetics of AP
decomposition using kinetic compensation effect. In this work we could
successfully normalize the activation energy by applying Kinetic
Compensation Correction. Thus, an effort to extent homogeneous system
to heterogeneous became sensible. Different from previous results on AP
decomposition using copper oxide doped polymeric carbon nitride
catalyst, for the first time we have made use of in-situ TG-MS for inter-
preting the decomposition pattern of AP via evolved gas analysis. TG-MS
helped us to understand the decomposition products in presence of the
synthesized catalyst and effective interaction between NH3 & HClO4
molecules. In this work, CuO modified gCN binary composites were
synthesized by a facile sonochemical approach.
3. Characterization
The composition and phase purity of the as-synthesized samples were
analyzed by a Rigaku Miniflex 600 powder x-ray diffractometer with
monochromatized Cu-Kα (λ ¼ 1.5425 Å) incident radiation. XRD patterns
were recorded in the range of 10-80ꢀ 2θ. Crystalline phases were iden-
tified by comparing diffraction patterns with JCPDS values. FT-IR spectra
of the samples were recorded by a PerkinElmer 400 Spectrometer in the
range 4000-400 cmꢁ1. Field Emission Scanning Electron Microscopic
(FE-SEM) images and Energy Dispersive X-ray (EDAX) analysis was
recorded on Carl Zeiss instrument model Ultra-55 operating at 20 kV.
High-Resolution Transmission Electron Microscopy (HRTEM) images
were taken using a JEOL JEM-2100 microscope at an accelerating voltage
of 200 kV. The Brunauer-Emmet-Teller (BET) specific surface area, pore
size and pore volumes of the samples were analyzed by a Thermo Fischer
Scientific Surfer particle analyzer. All the samples were degassed at 150
ꢀC for 4 h before nitrogen adsorption measurements were taken. The EPR
spectra of gCNCuO1 was recorded at room temperature using JEOL JES-
FA Series A EPR spectrometer at a working frequency range of 8.75–9.65
GHz.
2. Experimental
The following chemicals were purchased and used as received. Cop-
per Sulphate (Rankem, 99.5%), Sodium Hydroxide pellets (Rankem,
97%), Urea (Spectrum, 99%) and Ammonium Perchlorate (APEP, ISRO,
Aluva, >99%). All the chemicals were of analytical grade.
3.1. Catalytic activity measurement
2.1. Synthesis
To evaluate the catalytic activity of the as-prepared CuO decorated
2.1.1. Synthesis of gCN
gCN composites, ammonium perchlorate (average particle size <100 μm)
gCN was synthesized by the thermal condensation of urea. Typically,
about 5 g of urea was taken in a silica crucible and heated in a muffle
furnace at 530ꢀC for 4 h at a heating rate of 3ꢀC/min. After cooling it to
room temperature naturally, a pale yellow colored gCN powder was
obtained. This was then manually grounded to a fine powder using a
mortar and pestle and used for further analysis.
were thoroughly mixed with the catalysts by a physical grinding method.
i.e. AP was taken in a mortar to which catalysts were added and ground
physically using pestle for 30 min. Thermogravimetric (TG) and differ-
ential scanning calorimetric (DSC) analysis were used to investigate the
thermal decomposition of the mixture (98% AP: 2% catalyst by mass)
from 50ꢀC to 450ꢀC under N2 atmosphere at a heating rate of 5ꢀC/min.
The measurements were performed on a PerkinElmer 8000 TG analyzer
and TA instruments TG-DSC Q600 with a sample mass of 5.7 ꢂ 0.1 mg in
an alumina crucible. The evolved gas analysis was done using TG-GC-MS
coupled technique on a PerkinElmer TGA 8000 coupled PerkinElmer
2.1.2. Synthesis of leaf-shaped CuO
About 4.7 g CuSO4.5H2O was dissolved in 35 ml of deionized water
very slowly to get a greenish-blue solution. Then around 1.7 g of NaOH
2