Abstract
In the current work, an effort has been made to create polymer composite materials using polybenzoxazine (PBz), which is synthesis from sustainable natural ingredients like furfurylamine (Fu), cardanol (Ca) and reinforced with granite dust made from industrial waste. Varied analytical approaches were used to examine the thermal, morphological, chemical structure, flame retardant and electrical properties of Ca-Fu-PBZ composites reinforced with granite dust at varied weight percentages (5, 10, 15 and 20 wt%). According to the weight percentage concentration of granite dust, the differential scanning calorimetry (DSC) data suggest that the value of Tg increased from 105 to 139°C. A pure Ca-Fu-PBZ benzoxazine matrix was found to have a dielectric constant of 3.97 at 1 MHz. Whereas 5, 10 and 20 wt percentages of reinforced Ca-Fu-PBZ composites with granite dust had dielectric constants of 3.54, 3.05, 2.51 and 2.02 at 1 MHz, respectively. For granite dust reinforced Ca-Fu-PBZ polybenzoxazine composites, the value of the limiting oxygen index (LOI) determined for the char yield obtained thermogravimetric analysis (TGA) shows greater values than those of the neat Ca-Fu-PBZ matrices. Using water contact angle, the hydrophobic behavior of polybenzoxazine composites reinforced with granite dust was investigated, and it was concluded that the hydrophobic behavior increased with the weight % of granite dust. Data from several investigations show that the thermally stable electrical insulation applications can employ the granite dust reinforced sustainable cardanol-furfurylamine based polybenzoxazine composites as potting compounds, sealants and composites.
Keywords
Introduction
Rapid industrialization and continued increase of human population, generation of wastes are correspondingly increased day by day. 1 Among the varied nature of solid industrial wastes produced granite dust wastes is one of the most important solid wastes 2 generated during the cutting and shaping of granites stones throughout the world, which contributes to environmental pollution 3 in the form of particulate matter. 4 Further, granite wastes are non-biodegradable 5 material and cause serious environmental pollution and disrupt ecological systems when dumped on land. 6 The granite waste dust is predominantly consists of large percentage content of silica (SiO2) with constituents of mica, feldspar (plagioclase), amphiboles (plagioclase feldspar, quartz and biotite) and other elements. 7 Currently, the utilization of granite waste was used as additives and fillers for the preparation of masonry products viz., bricks, tiles, paver blocks, etc to avoid pollution problems as well as to exploit its inherent properties and to reduce the cost products. 8 Granite waste 9 is also used as reinforcements for the preparation of polymeric resin based composites due to its higher flame retardant ability and thermal stability.
Benzoxazines are synthesized via condensation reaction of phenol, formaldehyde and primary amines. 10 Polybenzoxazines (PBz) can be obtained by the ring opening polymerization of benzoxazine monomer under heat treatment in the absence of any catalysts or curatives and forms no by-product. 11 Polybenzoxazines are a kind of thermosetting resin become evident for its superior properties such as molecular design flexibility, thermally stable, near-zero shrinkage upon polymerization, low dielectric constant and low melt viscosities also have much higher hydrophobicity with potential corrosion resistant behavior. 12 PBz materials 13 become an attractive substitute to conventional thermosetting polymers such as phenolic resins, epoxies, 14 unsaturated polyesters,15,16 vinyl ester resin, bismaleimides 17 and cyanate esters.18,19 The reinforcement of polybenzoxazines with organic-inorganic hybrid frame materials, 20 like carbon materials 21 (carbon black, 22 CNT and GO 23 ), silica materials 24 (POSS and SiO2),25,26 mesoporous materials (mobil composition of matter no. 41 and Santa Barbara Amorphous-15) metal oxides (TiO2, 27 Al2O3 28 and ZnO29,30) and bio resource materials 31 (rice husk and palm flower carbon), act as fillers to improve the properties of the base materials. 32 For instance, Amalorpavadoss et al 33 studied the GPTMS functionalized mesoporous silica (F-SBA-15) composites. Kurinchyselvan et al. 34 Reported the Cardanol benzoxazine-functionalized graphene oxide (GO-C-aps)-reinforced fluorinated benzoxazine (BAF-a) hybrid composites poly (GO-BAF-a) composites.
In the present work the sustainable polymeric binder namely benzoxazine was synthesized using cardanol with hetero-structured furfurylamine and paraformaldehyde through Mannich condensation in the absence of solvent at appropriate experimental conditions. The developed cardanol benzoxazines (Ca-Fu-PBZ) was analyzed using Fourier transform infrared (FTIR) studies. The varying weight percentages (5, 10, 15 and 20 wt%) of conditioned granite dust have been reinforced with Ca-Fu-PBZ bio-based benzoxazine to obtain composites in order to ascertain its suitability for industrial applications. Data resulted from thermogravimetric analysis (TGA), differential scanning calorimetry (DSC), scanning electron microscopy and EDAX (SEM), X-ray diffraction (XRD) and water contact angle studies are reported and discussed.
Experimental
Materials and methods
Sodium sulphate, chloroform, paraformaldehyde and sodium hydroxide were procured from Fine Chemicals (Alpha Chemicals Pvt. Ltd, Maharashtra). Cardanol and Eugenol were received from Satya Cashew Chemicals Pvt. Ltd (Tamil Nadu, India) and Avra Synthesis Pvt. Ltd (Hyderabad, India). Cardanol based benzoxazines was prepared as per the reported procedure.35,36
Conditioning of granite dust
Granite slurry waste generated during re-sizing of granite rocks by ACY granites, Sivagangai, Tamil Nadu, India was collected and used. The granite powder was washed well with plenty amount water and followed by acetone and dried in an air-oven at 110°C for overnight. The obtained granite powder was dried for a month in normal sunlight and the adsorbed moisture and low volatiles are removed by heating at 200°C in an oven for 48 h. The dried powder was then sieved with 425 μ mesh and the uniform size of the granite particles was collected and used as reinforcement.
Preparation of polymer composites
5 g of cardanol benzoxazine monomer and different weight percentages of 5 wt%, 10 wt%, 15 wt% and 20 wt% of granite dust were mixed separately and dispersed well in 15 mL of 1,4-dioxane. The cardanol benzoxazine and granite dust (Ca-Fu-PBZ)/GD were thoroughly mixed with efficient sonication and agitation and then they were separately poured into a Teflon coated silane treated glass plate. Then, the samples obtained were cured from 30°C to 220°C for 1 h time interval and post-cured at 240°C for 2 h to obtain (Ca-Fu-PBZ)/GD bio-benzoxazine composites. The cured composite samples were washed and cleaned with hexane solvent and then preserved for further characterization studies. 37
Characterization
The FTIR spectra of the benzoxazine monomers and Ca-Fu-PBZ bio-composites were recorded in the wave number range of 4000–400 cm−1 using SHIMADZU spectrometer by KBr pellet technique. Differential scanning calorimeter (DSC) and Thermogravimetric analysis (TGA) was recorded using a Netzsch STA 409 analyzer. The value of dielectric constant was evaluated by means of an impedance analyzer at room temperature using a platinum electrode from 1 Hz to 1 MHz using Solartron Impedance Analyzer 1260, UK. The powder XRD pattern of benzoxazines and polybenzoxazine bio-composites was obtained using a Bruker X-ray diffractometer with the Cu ka radiation (λ=1.5406 Å) at the scanning rate of 0.02° S−1 (2θ), in the range of 0–80°. The surface morphology of bio-polymer composite thin films was analyzed by means of a scanning electron microscope (SEM; JEOL JSM Model 6360). The surface of the composite films was covered with gold using Auto Fine Coater (JEOL JFC-1600) at a high vacuum pressure of 8 Pa/20 mA for 95 s. The value of water contact angle on the composite film surface was measured by means of a Kwoya goniometry, DMs 200, Japan with 5 μL of water as probe liquid. All the measurements are repeated twice.
Result and discussion
Spectral studies of (Ca-Fu-PBZ) and bio-composites
The granite dust reinforced Ca-Fu-BZ monomer was subjected to ring opening polymerization in the absence of any catalyst with heating to obtain the corresponding polybenzoxazine composites. The formation of Ca-Fu-PBZ matrices and its composites were ascertained from FTIR spectral analysis and the results obtained are presented in Figure 1. In the FTIR spectra the peak observed at 1247 cm−1 infers the formation of the aromatic ether (C-O-C) stretching and the disappearance of peak at 949 cm−1 confirms the ring opening polymerization occurred in the oxazine ring group and the peak observed at 1468 cm−1 evidences the transformation of tri substituted to tetra-substituted aromatic ring which in-turn confirms the development of polybenzoxazine network.
38
Further, the very low intensity peaks were observed at 1587, 999 and 751 cm−1 may be accredited to the extra cross-linking provided by furan moiety present in the Ca-Fu-PBZ. The broad absorption peak appeared at 1067 cm−1 ascertains the presence of Si-O-Si linkage in the granite dust and Ca-Fu-PBZ hybrid composites. The symmetric and asymmetric stretching vibrations of aliphatic chain of cardanol are observed at 2970 and 2871 cm−1 respectively. FTIR spectra of Ca-Fu-PBZ incorporated GD composites.
Thermal studies
Thermal stability, and dielectric constant and contact angle of Ca-Fu-PBZ reinforced GD composites.

DSC thermogram of Ca-Fu-PBZ incorporated GD composites.
The thermal degradation characteristic of the renewable
40
Ca-Fu-PBZ and granite dust reinforced Ca-Fu-PBZ composites was analyzed by thermogravimetric analysis and the results obtained are presented in Figure 3 and Table 1. The 10% and maximum mass loss (Td10 and Tmax) the amount of char yield at 800°C are calculated and are presented Table 1. The initial degradation and char residue of the composites were enhanced appreciably with increasing silica rich granite dust content. The value of char yield obtained for the neat matrix and for the 20 wt% granite dust reinforced Ca-Fu-PBz systems are 19.8% and 68.3% respectively. Consequently, the thermal stability and granite dust reinforced Ca-Fu-PBZ composites are higher than that of neat Ca-Fu-PBZ matrices. The significant improvement of thermal stability of polybenzoxazine composites may be explained due to the effective chemical interaction occurred between granite dust particles and polybenzoxazine matrix.
41
TGA thermogram of Ca-Fu-PBZ incorporated GD composites.
The flame retardant property
42
of granite dust reinforced Ca-Fu-PBZ composites was determined by using van Krevelen’s equation
43
from the char yield values of the polybenzoxazine composites and the results obtained are presented in Figure 4 and Tables 1. In the present work, Ca-Fu-PBZ and silica rich granite dust composites were fruitfully developed using renewable raw materials such as cardanol and furfurylamine. The LOI values of granite dust reinforced Ca-Fu-PBZ composites calculated are in the range of 30.5 to 44.9. The calculated LOI value of Ca-Fu-PBz matrix is 25.4 and that of 5, 10, 15 and 20 wt% of granite dust reinforced polybenzoxazine composites are 30.5, 35.8, 41.3 and 44.9 respectively. The LOI values of granite dust reinforced Ca-Fu-PBZ polybenzoxazine composites have higher values contrast with unmodified Ca-Fu-PBZ matrices. The increased LOI values may be due to the retarded and diminished formation of combustible gases which in turn reduce the exothermic nature of pyrolysis reaction and there by inhibits the combustion of the burning organic moieties.
44
In addition, the granite dusts dispense additional heat capacity which stabilizes the polymeric chains against thermal decomposition. The flame-retardant behavior of granite dust reinforced polybenzoxazine composites was significantly improved according to the percentage incorporation of granite dust in to polybenzoxazine matrices. Histogram of LOI values of Ca-Fu-PBZ incorporated GD composites.
Electrical studies
The dielectric constant
45
of neat Ca-Fu-PBZ benzoxazine matrix and varying weight percentages of granite dust incorporated Ca-Fu-PBZ benzoxazine composites as a function of frequency at room temperature and the values obtained are presented in Table 1. It is pragmatic that the dielectric constant vale of neat Ca-Fu-PBZ benzoxazine matrix was found to be 3.97 at 1 MHz are shown in Figure 5. The 5, 10, 15 and 20 wt percentages of granite reinforced Ca-Fu-PBZ materials possess the dielectric constant values of 3.54, 3.05, 2.51 and 2.02 at 1 MHz respectively. The dielectric constant value infers that the incorporation of granite dust will decrease the dielectric constant proportional to its content, may be as a result of effective interaction between the granite dust and Ca-Fu-PBZ matrix leading to the formation of non-polar insulating network throughout matrix.
46
Dielectric constant of Ca-Fu-PBZ incorporated GD composites.
Water contact angle (WCA) studies
The results of water contact angle measurements on neat matrix Ca-Fu-PBZ and 5, 10, 15 and 20 wt% granite dust reinforced Ca-Fu-PBZ are presented in Figure 6 and Table 1. From the Figure, it was inferred that the values of water contact angle obtained for granite dust reinforced composites are gradually enhanced according the increase in weight percent of granite dust in addition to the presence of long aliphatic chain moiety which synergistically contributes to better hydrophobic nature.
47
Water contact angle images of (a) 5 wt% GD, (b) 10 wt % GD, (c) 15 wt % GD, and (d) 20 wt % GD reinforced Ca-Fu-PBZ composites.
Chemical resistance test
Chemical resistance of the Ca-Fu-PBZ matrix and its composites were studied as per ASTM D 543 method. 48 For this purpose, three strong acids such as H2SO4, HCl, and HNO3; weak acids namely CH3 COOH, HCOOH and H3PO4; strong bases such as NaOH and KOH; weak bases such as ammonia and aniline were selected. The pre-weighed samples were immersed in sufficient quantity of chemicals for 24 h, removed and washed with plenty of distilled water and then dried. The samples are reweighed and the difference in weight was determined.
The Ca-Fu-PBZ matrix and granite dust incorporated Ca-Fu-PBZ composites is immersed in some strong and weak acids, strong and weak bases. Form these studies, we have noticed more or less weight gain is observed depending on acids and bases concentration. The weight gain observed in the entire polybenzoxazine composites systems is understandable, as inter-crosslinked matrices form three-dimensional networks that are chemically more stable.
Morphological studies
The X-ray diffraction patterns of Ca-Fu-PBZ benzoxazine based intercrossed linked matrices and various weight percentage (5, 10, 15 and 20) composition of granite dust loaded composites are displayed in Figure 7. The amorphous nature of broad diffraction patterns are appeared at 2θ = 20.61°. From this broad and amorphous diffraction patterns confirms that the uniform distribution of granite dust homogenously in the benzoxazine matrices. X-ray diffraction pattern of Ca-Fu-PBZ incorporated GD composites.
The SEM morphology and photographs of Ca-Fu-PBZ benzoxazine matrices and different compositions (5, 10, 15 and 20 wt%) of granite dust embedded PBz composites are accessible in Figures 8(a)–(f). The neat C-Fu-PBz benzoxazine matrices show a continuous and smooth structure [Figure 8(a)]. From the SEM photographs evidences that the homogeneous dispersion of the granite dust in the PBz matrix without any aggregation of granite dust, which resulted in a smooth surface morphology. The SEM studies indicated the existence of good interfacial bond between granite dust and the polymer with a homogeneous and denser structure. SEM microscopic images of (a) neat matrices, (b) 5 wt% GD, (c) 10 wt % GD, (d) 15 wt % GD, (e) and (f) 20 wt % GD reinforced Ca-Fu-PBZ composites.
EDAX spectroscopy was conducted to ascertain the composition of composites and the EDX spectrum of the of Ca-Fu-PBZ benzoxazine matrices and different compositions (5, 10, 15 and 20 wt%) of granite dust loaded PBz composites are offered in Figures 9(a)–(e). The neat Ca-Fu-PBz benzoxazine matrix elemental analysis confirmed that the presence of C = 71.32%, O = 24.46% and Si = 0.40%. The neat Ca-Fu-PBz benzoxazine matrix possesses the higher values of carbon, oxygen with traces of silicon impurity was observed. The EDX spectrum of various weight percentages of granite dust reinforced composites provides the composition of carbon, oxygen, and silicon. Consequently, the atomic percent of the 5% granite dust reinforced polybenzoxazine composites was found as C = 52.20%, O = 31.64%, Si = 11.21% and traces of some metal oxides like alumina, calcium, potassium and iron.
49
Figure 9(e) represents the elemental analysis of 20 wt% of granite dust reinforced polybenzoxazine composites possess the higher values of carbon, oxygen and silicon (C = 43.85%, O = 34.93%, Si = 15.76%). The composition values were strongly dependent upon the percentage of the granite dust in the in situ polymerization. EDAX images of (a) neat matrices, (b) 5 wt% GD, (c) 10 wt % GD, (d) 15 wt % GD, and (e) 20 wt % GD reinforced Ca-Fu-PBZ composites.
Conclusion
In the current work, the potential use of industrial waste and bio-based sustainable polymeric resin matrix for the production of composite materials with improved thermal stability, flame retardant behavior, and hydrophobic behavior is presented. All these benefits help to explain why research on cardanol polybenzoxazine composites has increased recently. Cardanol polybenzoxazine composites have a number of advantages, including one-pot solvent less atom-economized synthesis, polymers with good thermal stability, and low viscosity of benzoxazines expanding the range of potential applications. The process ability of the related resin may be hampered by certain restrictions like a high curing temperature. Numerous modifications, including the addition of fillers, the creation of blends, the functionalization of monomers, etc., have been tried to address these shortcomings.
A variety of 5, 10, 15 and 20 wt percent amounts of granite dust reinforced cardanol polybenzoxazine composites were prepared. By using the proper analytical procedures, the bio-benzoxazines (Ca-Fu-PBZ) and bio-benzoxazine composites thermal stability, morphology, and water contact angle were investigated. The acquired results from thermal experiments using techniques like DSC and TGA showed that the granite dust enhanced composites have better thermal stability than a plain Ca-Fu-PBZ based matrix. According to the findings of LOI experiments, benzoxazine matrices and composites based on cardanol exhibit better thermal behavior than clean benzoxazine matrix. The thermal, electrical and hydrophobic behavior of Ca-Fu-PBZ matrix and granite dust contained composites is superior to that of composites and standard synthetic benzoxazines. It has been achieved that the Ca-Fu-PBZ/granite dust is taken into account for the creation of high performance composite materials for a variety of industrial applications, as well as for efficient solid waste management. As a result, modified cardanol polybenzoxazine composites have demonstrated a noticeable improvement in characteristics as well as a broad range of applicability, including composites, adhesives, self-healants, etc. Due to this, cardanol polybenzoxazine composites' monomers and polymers occupy a unique position among other polybenzoxazines, necessitating further research on both the synthetic and application levels.
Footnotes
Acknowledgements
One of the authors (Dr.A.Chandramohan) acknowledges the financial support of Sri Sivasubramaniya Nadar College of Engineering, Kalavakkam, Tamil Nadu.
Declaration of conflicting interests
The author(s) declared no potential conflicts of interest with respect to the research, authorship, and/or publication of this article.
Funding
The author(s) disclosed receipt of the following financial support for the research, authorship, and/or publication of this article: This work was supported by the SSN Trust.
