Abstract
Demand is increasing for superhydrophobic materials in many applications, such as membrane distillation, separation and special coating technologies. In this study, we report a chemical vapor deposition (CVD) process to fabricate superhydrophobic carbon nanomaterials (CNM) on nickel (Ni)-doped powder activated carbon (PAC). The reaction temperature, reaction time and H2/C2H2 gas ratio were optimized to achieve the optimum contact angle (CA) and carbon yield (CY). For the highest CY (380%) and CA (177°), the optimal reaction temperatures were 702 °C and 687 °C, respectively. However, both the reaction time (40 min) and gas ratio (1.0) were found to have similar effects on CY and CA. Based on the Field emission scanning electron microscopy and transmission electron microscopy images, the CNM could be categorized into two main groups: a) carbon spheres (CS) free carbon nanofibers (CNFs) and b) CS mixed with CNFs, which were formed at 650 and 750 °C, respectively. Raman spectroscopy and thermogravimetric analysis also support this finding. The hydrophobicity of the CNM, expressed by the CA, follows the trend of CS-mixed CNFs (CA: 177°) > CS-free CNFs (CA: 167°) > PAC/Ni (CA: 65°). This paves the way for future applications of synthesized CNM to fabricate water-repellent industrial-grade technologies.
Similar content being viewed by others
Introduction
Superhydrophobic carbon-based nanomaterials (CNM) with contact angles (CA) > 150° have attracted tremendous scientific and commercial interests due to their various applications, including antifouling and self-healing membranes1, adsorbants2, anti-wetting X-ray sample holders3, ultrasensitive protein spectroscopy substrates, microarray devices4, drug delivery materials5, and others6,7. Both the surface roughness and surface chemistry can affect the hydrophobicity of the materials8. Growing CNM on other materials, rather than altering the surface chemistry9, can substantially transform the surface roughness of the nanomaterial and has recently gained popularity. Nanomaterials with altering surface chemistry may not effectively acquire superhydrophobicity due to the limitations of interfacial tension9,10. Therefore, new and/or improved methods are necessary to synthesize carbon superstructures consisting of different hybrids that could ensure a certain surface roughness needed for superhydrophobicity.
Methods such as chemical vapor deposition (CVD), template synthesis, electrochemical deposition, crystallization control, etc., have been utilized to yield geometrical surface structures11, among which CVD is widely used due to its wide availability, ease of handling, and high yield12. An ideal substrate for CVD is powder activated carbon (PAC) due to its wide precursor availability, low cost, and potential for chemical modifications13. Some researchers14,15,16,17 have used PAC to synthesize carbon nanofibers (CNFs) using ethylene (C2H4) and iron (Fe) catalysts in the CVD processes13,18,19,20,21. Alternatively, some researchers have modified the structure of CNM to achieve artificial superhydrophobic surfaces. For instance, Hong et al. used NF3 plasma to decrease the surface free energy of carbon nanotubes (CNTs), which produces a CA > 150°22. Most CNTs aggregate and often contain impurities, which may hamper optimization of the synthesis of superhydrophobic CNM23. Comparatively, PAC has sizes <100 µm and offers an economical and available substrate for CNM growth24. Unlike other substrates, PAC does not need to be chemically or physically removed from the functional bulk material25. Cleaning and washing processes negatively affect the surface of CNM and dramatically reduce the CA26. The hybrid PAC-CNF shows the combined properties of a classical PAC and CNFs while maintaining the chemical compatibility between these two materials. However, these studies have not considered the synthesis of different CNM, and the lack of optimization for increasing the carbon yield (CY) and CA have left scientists ignorant about the process. Therefore, our efforts in this study were focused on the determination of the optimum reaction conditions for efficient production of superhydrophobic CNM.
Herein, we successfully synthesized two hierarchical superhydrophobic CNM, carbon sphere (CS)-free CNFs and CS-mixed CNFs, using acetylene (C2H2) and a nickel (Ni) catalyst in thermal CVD at 650 and 750 °C, respectively. We found that optimization of the reaction conditions, such as the reaction temperature, reaction time, and gas ratio, was important to increase both the CY and CA. Both the CS-free CNFs and CS-mixed CNFs showed CA > 150° for a 4 µL droplet. Such hierarchical structure, i.e., CS nested in CNFs incorporated in PAC, is promising for applications in sorption2,27, membrane distillation28,29, organic mixture separation, water adsorptive purification, and catalysis30.
Results and Discussion
Catalyst impregnation
The transmission electron microscope (TEM) image in (Fig. 1(a)) clearly shows that the catalyst was successfully impregnated in the PAC. To further investigate, we performed energy dispersive X-ray analysis (EDX), shown in (Fig. 1(c)), which confirmed that the PAC is comprised of carbon (88 wt%), oxygen (7.1 wt%), Ni (3.3 wt%), and silicon (1.6 wt%). An extremely small amount of Ni was found to be sufficient to facilitate the formation of catalytic sites and to yield CS-free CNFs and CS-mixed CNFs depending on the reaction temperature.
Model establishment and analysis
The effects of reaction temperature, reaction time, and gas ratio on C2H2 decomposition were studied using a response surface method (RSM) central composite design (CCD)31. A total of 11 runs were performed, and multiple variable analysis i.e. analysis of variance (ANOVA) was used to study the effects on CY and CA. The responses from the resulting 11 runs are shown in Table 1. Using design of experiment (DoE), we fitted the response data of CY and CA to mean, linear, two-factor interaction (2FI), quadratic and cubic polynomial models, as shown in Tables S1 and S2, respectively (Supplementary Information). It was observed that although the coefficient of determination (R2) of the linear (0.9293) and 2FI (0.9325) models showed close correlation, the 2FI model was more significant, as its probability, Prob > F, value was calculated as 0.0239 < 0.0532. The 2FI model was chosen for CA analysis due to a higher R2 (0.9839), although Prob value of mean < 0.05.
Statistical analysis and modeling
The ANOVA results for the CY responses are displayed in Table 2. As revealed in Table 2, the main effects of the reaction temperature (A), the interaction of the reaction temperature and the gas ratio (AC), and the second-order effects of reaction time (B2) were significant, as their Prob > F values were less than 0.05. Therefore, we can conclude that A, AC and B2 were the major determinants for CY. The remaining reaction parameters, including the reaction time (B), the gas ratio (C), the interaction of A and B (AB) and the second-order effects of A (A2) were shown to have Prob > F values greater than 0.05. Hence, it can be concluded that these parameters had less effect on CY over the studied range. However, these model terms were not eliminated from the analysis in order to ensure that the selected 2FI model remained hierarchical. The regression equation for CY is given by eq. (1).
where A represents the reaction temperature, B the reaction time, and C is the gas ratio.
A comparison between the experimental results and the model values of CY predicted from the above eq. (1) is depicted in (Fig. 2(a)). A simulated model should be congruent with the results, which is indicated by a high R2 value. (Figure 2(a)) demonstrates the good convergence between the experimental and predicted values of CY.
The ANOVA results for the CA responses are displayed in Table 3. Similar to CY, the effect of A was found to be significant, with a Prob > F value less than 0.05. Compared to CY, we found significant second-order effects for the reaction temperature (A2). Therefore, we can conclude that A and A2 were the major determinants of CA. The remaining reaction parameters, such as B, C, the interaction of A and B (AB), the interaction of A and C (AC), and the second-order effect of B (B2), demonstrated Prob > F values greater than 0.05. Hence, it can be concluded that these parameters had less effect on CA over the studied range. The regression equation for CA is given by eq. (2).
where A represents the reaction temperature, B the reaction time, and C is the gas ratio.
A comparison of the experimental results with the model values of CA predicted from the above equation is shown in (Fig. 2(b)). A simulated model should be congruent with the results, which is indicated by a high R2 value. (Figure 2(b)) demonstrates the excellent convergence between the experimental and predicted values of CA.
Effects of reaction temperature, reaction time, and gas ratio
The effects of the process parameters on CY and CA were scrutinized to determine the conditions that favored the desired reaction. The interaction effects of the process parameters on CY and CA were graphically illustrated by CCD curves. These curves were plotted on the basis of the empirical model and are shown for CY in (Fig. 3(A–C)). Figure 3 shows the effects of the reaction temperature and reaction time on CY at fixed gas ratio 4.0 (Aa) and 1.0 (Ab). There was a notable increase in CY with increasing reaction temperatures, from 550 to 750 °C, as shown in both plots. This suggests that conducting the reaction at higher temperatures is recommended, which is in contrast to the results of other studies32,33,34. The Ni catalyst was not deactivated at higher temperatures. This suggests that PAC is an effective support for the Ni catalyst for C2H2 decomposition even at higher temperatures. Second, the decrease in the growth rate observed in previous studies at lower temperatures was due to progressive blocking of the active surface by excess carbon deposition on the front face of the catalyst particle, which is called catalyst poisoning35. This effect can be minimized by creating a PAC network around the Ni catalyst. Figure 3 shows the effects of the reaction time and gas ratio on CY at fixed reaction temperature 750 (Ba) and 550 °C (Bb). There was a steady increase in CY with increasing reaction time for a gas ratio of 4.0 at high temperature (Fig. 3(Ba)). Typically, the rate of diffusion for carbon into the catalyst decreases with increasing reaction time and eventually approaches zero, giving rise to no additional increase in the length or the yield35. The increased CY in this study may be due to an increase in the rate of C2H2 decomposition because the activity of the Ni catalyst remained high due to higher diffusivity of carbon atoms on the PAC-protected surface of the Ni catalyst particles exposed to a gaseous environment. However, a high reaction time was unfavorable at the maximum gas ratio of 4.0 at low temperature (Fig. 3(Bb)). Figure 3 shows the effects of the reaction temperature and gas ratio on CY at fixed reaction time 60 (Ca) and 20 min (Cb). Here, it can be seen that the effect of the gas ratio on CY was not significant, as a higher CY was seen at the gas ratio of 1.0 at high temperatures. This indicates that the gas ratio does not influence nucleation for carbon growth, while PAC has been used as a support for Ni catalysts at high temperatures for long reaction time, i.e. 60 min (Fig. 3(Ca)). It is well known that the presence of a higher H2 partial pressure, along with C2H2, can suppress catalyst poisoning effects, which in turn results in an increase in the length of CNM36. H2 has been recognized an ideal energy carrier in CVD processes and correlates with the structure of CNM. Any carbon atom that diffuses into the cluster will be diluted, which affects the amount of CNM that are formed. H2 gas has been shown to help control the deposition quality of carbon soot and, ultimately, the quantity of CNM. However, our study also indicates that the suppression of catalyst poisoning could be potentially minimized by using PAC, which would protect the Ni catalyst even at a higher flow of H2/C2H2 gas.
Figure 4 shows the effects of the reaction temperature and reaction time on CA at fixed gas ratio 4.0 (Aa) and 1.0 (Ab). Similar to CY, there was a notable increase in CA with increasing reaction temperatures, from 550 to 750 °C, as shown in both plots. The reaction time also showed similar effects. Figure 4 presents the effects of the reaction temperature and gas ratio on CA at fixed reaction time 60 min (Ca) and 20 min (Cb). It can be observed that the effects of the gas ratio on CA were negligible, as the lowest CA was seen at the gas ratio of 4.0 at high temperature, as shown in both plots. Note that an increased gas ratio can increase CY only a low reaction time 20 min (Fig. 3(Cb)) due to the generation of longer CNF production36. Alternatively, increasing the gas ratio can decrease CA may be due to the stimulation of CNF production, rather than CS. We found that extreme hydrophobicity largely depends on CS production in the CNF network, as it increases the surface roughness. This is well corroborated by the TEM and CA analyses.
Optimization study
The independent factors and responses considered important in C2H2 decomposition were optimized simultaneously using a numerical optimization method in the DoE software. All the factors and responses corresponding to the upper and lower limits of the experimental range had to satisfy the criteria defined for the optimum working conditions. The ultimate goal for C2H2 decomposition into CNM is to maximize the CY and CA. Several sets of combinations were predicted to be possible optimized conditions, which were further ranked by desirability. The optimum process conditions for the highest desirability were a reaction temperature of 702 °C, a reaction time of 40 min, and a gas ratio of 1.0, which gave the highest CY of 380%. Similarly, a reaction temperature of 687 °C, a reaction time of 40 min, and a gas ratio of 1, gave the highest CA of 177°. The experiments were performed at the predicted optimum conditions to experimentally verify the CY and CA results. These results show that the predicted CY and CA were close to the experimental values, with a mean error of 2.21%.
FE-SEM and TEM analyses
The morphologies of the deposited products, obtained using PAC/Ni, are shown in (Fig. 5). At 650 °C, only CNF-like materials were observed, as shown in the Field emission scanning electron microscope (FE-SEM) image (Fig. 5(a)). However, the TEM images suggested that two types of CNF were produced, specifically fishbone-type CNFs (Fig. 5(b)) and tubular CNFs (Fig. 5(c))37. Interestingly, no single predominant type of CNF was observed at 750 °C, as shown in the FE-SEM images (Fig. 5(e,f)) and TEM images (Fig. 5(g,h)). We observed fibers in the forms of ribbons, which were possibly twisted into a helix (Fig. 5(f)), and metal-encapsulated tubular CNFs (Fig. 5(h)). In addition, we observed a considerable amount of CS (Fig. 5(e–g))37. The average CNF diameter was shown to increase from 20–30 nm at 650 °C, as shown in (Fig. S1), to 40–55 nm at 750 °C, as shown in (Fig. S2(a)). This may be due to sintering of the Ni catalyst, facilitated by the decomposition of PAC functional groups38. The predominant CNF helix diameter was 130–170 nm at 750 °C, as shown in (Fig. S2(b)). In addition, CNFs synthesized at both 650 and 750 °C were found to consist of graphitic layers as confirmed from (Fig. 5(c,h)). It should be noted that previous studies have claimed that only one type of CNF was found when PAC was used as the substrate for metal catalysts18,19,20,21. This is possibly due to the use of C2H4 rather than C2H2 as well as the different reaction temperatures. As shown in (Fig. 5(d)), CNF precipitated across the Ni bottom and pushed the entire Ni particle off the PAC, suggesting a “base or root” growth model. This occurred because of the weak interaction between Ni and PAC, since the Ni catalyst was physically adsorbed on PAC. Therefore, the overall CNF growth process can be considered to occur in three main steps as shown in (Fig. S3): i) the carbon feedstock was supplied to the Ni/PAC surface to obtain an intermediate; ii) small carbon fragments, such as C2 and C3, were generated from the decomposition of C2H2 at 650/750 °C and subsequently deposited on the surface of the Ni catalyst; and iii) CNFs grew until the Ni was fully covered with excess carbon, where after the catalytic activity ceased and CNF growth stopped.
In addition to CNF, the synthesis of CS at 750 °C is another advantage of this study. Recently, there has been renewed interest in the synthesis and study of CS, with many scientists now attempting to prepare CS due to their high surface area, thermal stability, unique electronic properties, low density, and most importantly, their tailored structure39. CS have been used in lithium batteries, as catalyst supports, in drug delivery, for the encapsulation of active transition metals, and as lubricants39,40, to name a few. As shown in (Fig. 5(e,g)), CS differs from fullerene in that they are solid. Since the diameter of the obtained CS fell between 80 and 130 nm (Fig. S2(c)), one can classify these as less graphitized spheres (50–1000 nm)39. As shown in (Fig. 5(e,g)), all the CS tend to be connected, forming bead- or necklace-like structures, through van der Waals forces, which leads to agglomerated collections of CS. A possible growth mechanism of CS formation is shown in (Fig. S4). A detailed mechanism of carbon nucleation to produce CS was outlined by Deshmukh et al.39.
Raman analysis
We used Raman spectroscopy to characterize the nature of the present carbon. The peak at around 1593 cm−1 (G band) corresponds to the E2g mode of hexagonal graphite and was observed for all CNM as shown in (Fig. 6). This is related to the vibration of sp2-hybridized carbon atoms in a graphite layer41. This suggests that, similar to the CNFs, the CS were also composed of graphitic carbon, which is consistent with the previously discussed TEM and FE-SEM results. In addition, the band in the obtained CNM spectra at around 1314 cm−1 (D band) suggests the presence of defective amorphous carbon structures42,43. The relative intensity of the G and D bands can be related to the organizational degree of the carbon material. Ni doping did not change the overall structure of PAC, since it shows an ID/IG of 0.81. The IG/ID ratio observed for the CS-free CNFs at 650 °C (0.74) is slightly larger than that for the CS-mixed CNFs at 750 °C (0.70). It suggests the CS-free CNF consists of well-graphitic structure than that of CS-mixed CNF44.
FTIR analysis
Fourier transform infrared (FTIR) spectroscopy was used to investigate the surface chemistry and functional group quality of the CNM as shown in (Fig. 7). The FTIR spectrum of the CS-mixed CNFs (750 °C) illustrates only a few functional groups. Peaks at 1978 and 2136 cm−1 might be attributed from metal (Ni) carbonyl, whereas characteristic peak at 2333 cm−1 was due to adsorbed CO245. IR spectrum of CS-free CNF (650 °C) showed a range of functional groups. For example, peak at 1176 cm−1 was due to CO (epoxy or alkoxy). The dominant peaks at 1445 and 1564 cm−1 were appeared due to stretching vibrations of CNF aromatic rings45 and C=C stretch46, respectively. The emerging peaks at wave numbers 1742 cm −1 was associated with C=O group46. Relatively weak and strong peaks at 2854 and 2926 cm −1 were may be due to –CH and CH2 stretching47. All of these high-intense peaks were absent in CS-mixed CNF (750 °C) which suggests the functional groups were only sponsored by CNF rather than CS. In general, CNF is contaminated with amorphous carbon during the growth process in CVD which typically oxidized by air to produce a few functional groups48. Such observation is in agreement with the results obtained by the measurement of the zeta-potential of the CS-free CNFs (650 °C), as we discuss in “CA and hydrophobicity analyses” section. Typically, oxy-functional groups led to more negative values, and as seen in the CA measurement results, the CS-mixed CNFs (750 °C), which has a few of functional groups, should demonstrate higher hydrophobicity.
TGA
Thermogravimetric analysis (TGA) was performed to measure the purity, defects, and overall quality of the obtained CNM. The TGA of the produced CNM with their derivative spectra are presented in (Fig. 8). The oxidation temperature represents the temperature at which CNM loses weight and shows the highest derivative weight curve. This reflects the stability of CNM at a given temperature. No weight loss was observed for PAC/Ni or the CNM at 650 or 750 °C at degassing temperatures ranging from 100 to 400 °C. PAC/Ni degradation began at approximately 500 °C and resulted in a loss of nearly 80 wt%. Typically, amorphous carbon oxidizes at approximately 500 °C49 due to its lower activation energy and the presence of numerous heat-sensitive active sites50. The presence of oxy-functional groups in the CS-free CNFs (650 °C) was confirmed by FTIR spectroscopy (Fig. 7) and may be responsible for the weight loss at low decomposition temperatures, i.e., just slightly over 500 °C, compared to the CS-mixed CNFs (750 °C), which showed 100 wt% loss at just above 600 °C51. The ash content of the CS after combustion above 600 °C was 0 wt%, implying that the produced CS was less graphitized in structure41.
CA and hydrophobicity analyses
Superhydrophobic surfaces with a water CA higher than 150° have drawn great scientific and industrial interest7. We studied the hydrophobicity of PAC/Ni, CS-free CNF and CS-mixed CNF as shown in (Fig. 9(A)) (measured within 1 min of placing the drop on the sample). Since PAC/Ni is not a hydrophobic material, the PAC/Ni solution cast film shows a CA of 65° (Fig. 9(A(a)), and the lower apparent CA (167°) of the CS-free CNFs (650 °C) (Fig. 9(A(b)) is not much more hydrophobic than the CA (177) of CS-mixed CNFs (750 °C) (Fig. 9(A(c)). This suggests that the formation of CS could be a possible cause of the high hydrophobicity of the CS-mixed CNF surface, as the droplet rests on the heterogeneous CNF surface. The surface wettability of CNM can be thoroughly explained by two different factors, specifically the surface chemistry and the surface roughness10. First, since the CS-free CNFs (650 °C) contain oxygenated functional groups, as confirmed by FTIR (Fig. 7), they are capable of attracting water molecules on their surface, compared to the CS-mixed CNFs (750 °C), which contain a few functional groups. Second, superhydrophobic surfaces require a certain surface roughness, the effect of which is seen in the apparent contact angle, θ°52. The growth of CS on the CNF network imparts a rougher surface area compared with that of the CS-free CNFs and minimizes the cavities available to water droplets. These explanations have also been experimentally proven by Ma et al., who suggested that high-density CS are more hydrophobic than CS-free CNFs9.
Optical observations of the colloidal stability of the CS-free CNFs and CS-mixed CNFs are shown in (Fig. 9(B)). The CS-free CNFs were not well dissolved in neutral water and were found to precipitate rapidly to the bottom of the vial (Fig. 9(B(b)). However, the CS-mixed CNFs showed extreme hydrophobicity, and the material even floated on the water surface (Fig. 9(B(c)). These results agreed with the CA and ζ-potential analyses. The ζ-potential is the electric potential at the interfacial double layer, which is important in measuring the surface charge of the material, as shown in (Fig. 9(C)). The values between 0 and −49 obtained for the CS-free CNFs (650 °C) indicated the mutual repulsion of CNFs, which is due to the high surface charge, providing considerable solubility53. On the other hand, the ζ-potential values between 0 and −20 mV indicate the onset of the agglomeration of the CS-mixed CNFs and their floatability. The hydrophobic surfaces of CS-mixed CNFs do not favor bond formation with water molecules, and thus, they do not disperse in water (Fig. 9(B(c)).
Conclusion
RSM showed the interactions of different parameters in the process of CNM growth on PAC by CVD. CY and CA were taken as the responses, and a significant regression equation was obtained, which led to a successful optimization. Based on the results from the experimental design, we conclude that temperature plays an important role and that the reaction time was significant factors for CY. Meanwhile, the main experimental factor for CA was the reaction temperature. The optimization indicated that the best conditions were a reaction temperature of 702 °C, a gas ratio of 1, and a reaction time of 40 min, which gave the highest CY of 380%. Similarly, a reaction temperature of 687 °C, a gas ratio of 1, and a reaction time of 40 min led to the highest CA of 177°. As revealed by the SEM and TEM analyses, the CNM produced under optimal conditions produced CS-free CNF and CS-mixed CNF at 650 and 750 °C, respectively. It was also observed in the TEM and SEM images that CNM were densely grown on the catalyst. In addition, Raman analysis discovered that these CNM possessed a high degree of graphitization and few defects. This study illustrates, through the CA on the CNM surface, that a stable superhydrophobic material was formed with high CY.
Materials and Methods
Materials and reagents
Nickel (II) nitrate hexahydrate, PAC, acetone, C2H2, H2, and N2 were purchased from Sigma Aldrich, Malaysia. All chemicals were of analytical grade.
Synthesis of CNM
Catalyst impregnation
PAC (2 g) was added to 5 mL of nickel (II) nitrate hexahydrate (1 wt%) acetone solution and sonicated at 40 KHz for 1 h at 50 °C. After achieving a uniform dispersion of PAC, the acetone was evaporated, and the Ni-doped PAC was dried at 100 °C. The dried sample was thoroughly ground, and the resulting powder was then stored in a desiccator. The PAC-Ni samples were calcinated at 350 and 700 °C for 2 and 1 h, respectively, under an inert atmosphere (N2, 200 mL/min).
Growth of CNM using CVD
The CNM-PAC superstructure was synthesized by placing the Ni-doped PAC into a ceramic boat containing CVD reaction tubes16,18. The temperature was set within the 550–750 °C range. Then, C2H2 mixed with H2 at a ratio of 1–4 was passed through the reaction tube for 20–60 min. After growth of the CNM, the reactor was cooled under N2 flow (200 mL/min), the deposited CNM were collected from the ceramic boat, and the yield was calculated using eq. (3).
where W P and W C are the weight of the sample after and before the reaction, respectively.
Experimental design and optimization of CY and CA
To obtain the optimal CY and CA values, we investigated the growth conditions for CNM using the DoE (CCD Version 7), namely, the reaction temperature, gas ratio, and reaction time. The optimization criteria involved the maximization of CY and CA and the minimization of the time and temperature. Prior to calculating the optimum solution, a statistical regression model was derived through the DoE software, through which a number of runs were eliminated. In addition, ANOVA was performed to determine the significance of the model and interactions of the various parameters.
Characterizations
The surface morphologies and topologies of the Ni-doped PAC, CS-free CNFs, and CS-mixed CNFs were examined using FE-SEM (Hitachi-SU8000, Japan) and TEM (Hitachi-HT7700, 120 kV, Japan). For these experiments, the CNM were dispersed into fresh MilliQ water and mounted onto lacey copper grids for FE-SEM and TEM analyses. EDX combined with SEM (Quanta FEG 450, USA) was performed to confirm the Ni content of PAC using an X-Max silicon drift detector at 10 KeV. The Raman spectra of the CNM were acquired for 10 min at a laser power of 100 using an Ar + laser (514 nm) focused (50× objective) to a spot size of approximately 1.5–2.0 µm (Renishaw in Via, UK). FTIR spectroscopy, using a PerkinElmer® FTIR spectrometer, was used to study the surface modifications. The measured spectra were collected using an exposure time of 10 seconds with a laser power of 100. TGA was conducted under an O2 flow between 25 to 1000 °C at a heating rate of 100 °C/min (TGA/SDTA 851, Mettler Toledo, USA).
CA and zeta potential measurements
The CA between the CNM and water was calculated by placing a drop of water (4 µL) onto a glass microscope slide (76 × 26 × 1.2 mm) covered with double-sided adhesive tape and measuring the CA with a KRUSS Goniometer (DSA100). Each measurement was repeated in triplicate, and the average was taken. The zeta-potential, or surface charge, analysis of a 0.01 Wt% CNM suspension was determined using a Zetasizer Nano ZS instrument (Malvern, model ZEN3600) (United Kingdom).
References
Das, R., Ali, M. E., Hamid, S. B. A., Ramakrishna, S. & Chowdhury, Z. Z. Carbon nanotube membranes for water purification: A bright future in water desalination. Desalination 336, 97–109 (2014).
Chowdhury, Z. Z. et al. Preparation of carbonaceous adsorbents from lignocellulosic biomass and their use in removal of contaminants from aqueous solution. BioResources 8, 6523–6555 (2013).
Ciasca, G. et al. Wet sample confinement by superhydrophobic patterned surfaces for combined X-ray fluorescence and X-ray phase contrast imaging. Microelectronic Engineering 111, 304–309 (2013).
Ressine, A., Marko-Varga, G. & Laurell, T. Porous silicon protein microarray technology and ultra-/superhydrophobic states for improved bioanalytical readout. Biotechnology annual review 13, 149–200 (2007).
Yohe, S. T., Colson, Y. L. & Grinstaff, M. W. Superhydrophobic materials for tunable drug release: using displacement of air to control delivery rates. Journal of the American Chemical Society 134, 2016–2019 (2012).
Das, R., Abd Hamid, S. B. & Ali, M. E. Nanobiohybrid: a favorite candidate for future water purification technology. Advanced Materials Research 1131, 193–197 (2016).
Ciasca, G. et al. Recent advances in superhydrophobic surfaces and their relevance to biology and medicine. Bioinspiration & biomimetics 11, 011001 (2016).
Nakajima, A., Hashimoto, K. & Watanabe, T. Recent studies on super-hydrophobic films. Monatshefte für Chemie/Chemical Monthly 132, 31–41 (2001).
Ma, M., Mao, Y., Gupta, M., Gleason, K. K. & Rutledge, G. C. Superhydrophobic fabrics produced by electrospinning and chemical vapor deposition. Macromolecules 38, 9742–9748 (2005).
Lu, Z. et al. Superaerophobic electrodes for direct hydrazine fuel cells. Advanced Materials 27, 2361–2366 (2015).
Wang, X., Ding, B., Yu, J. & Wang, M. Engineering biomimetic superhydrophobic surfaces of electrospun nanomaterials. Nano Today 6, 510–530 (2011).
Das, R., Shahnavaz, Z., Ali, M. E., Islam, M. M. & Hamid, S. B. A. Can We Optimize Arc Discharge and Laser Ablation for Well-Controlled Carbon Nanotube Synthesis? Nanoscale Research Letters 11, 510 (2016).
Chen, X.-W., Timpe, O., Hamid, S. B., Schlögl, R. & Su, D. S. Direct synthesis of carbon nanofibers on modified biomass-derived activated carbon. Carbon 47, 340–343 (2009).
Ahmed, Y. M. et al. in NANOSCIENCE AND NANOTECHNOLOGY: International Conference on Nanoscience and Nanotechnology. 519–522 (2008).
AlSaadi, M. A., Al Mamun, A., Alam, M. Z., Amosa, M. K. & Atieh, M. A. Removal of cadmium from water by CNT–PAC composite: effect of functionalization. Nano 11, 1650011 (2016).
AlSaadi, M. A. et al. Synthesis of various carbon nanomaterials (CNMs) on powdered activated carbon. African Journal of Biotechnology 10, 18892–18905 (2011).
Mamun, A. et al. Optimisation of arsenic adsorption from water by carbon nanofibres grown on powdered activated carbon impregnated with nickel. Journal of Applied Sciences 9, 3180–3183 (2009).
Su, D. S. et al. Hierarchically structured carbon: synthesis of carbon nanofibers nested inside or immobilized onto modified activated carbon. Angewandte Chemie International Edition 44, 5488–5492 (2005).
Chen, X.-W., Su, D. S., Hamid, S. B. & Schlögl, R. The morphology, porosity and productivity control of carbon nanofibers or nanotubes on modified activated carbon. Carbon 45, 895–898 (2007).
Chen, X. W., Su, D. S. & Schlögl, R. Immobilization of CNFs on the surface and inside of the modified activated carbon. physica status solidi (b) 243, 3533–3536 (2006).
Delgado, J. J., Chen, X.-W., Su, D. S., Hamid, S. & Schlögl, R. A novel catalyst for synthesis of styrene: carbon nanofibers immobilized on activated carbon. Journal of nanoscience and nanotechnology 7, 3495–3501 (2007).
Hong, Y. C., Shin, D. H., Cho, S. C. & Uhm, H. S. Surface transformation of carbon nanotube powder into super-hydrophobic and measurement of wettability. Chemical physics letters 427, 390–393 (2006).
Das, R., Ali, M. E., Hamid, S. B. A., Annuar, M. & Ramakrishna, S. Common wet chemical agents for purifying multiwalled carbon nanotubes. Journal of Nanomaterials 2014, 237 (2014).
Mamun, A. et al. Synthesis of carbon nanofibers on impregnated powdered activated carbon as cheap substrate. Arabian Journal of Chemistry 9, 532–536 (2016).
Ward, J., Wei, B. & Ajayan, P. Substrate effects on the growth of carbon nanotubes by thermal decomposition of methane. Chemical Physics Letters 376, 717–725 (2003).
Tittmann-Otto, J. et al. Effect of cleaning procedures on the electrical properties of carbon nanotube transistors—A statistical study. Journal of Applied Physics 119, 124509 (2016).
Ibrahim, R. K., Hayyan, M., AlSaadi, M. A., Hayyan, A. & Ibrahim, S. Environmental application of nanotechnology: air, soil, and water. Environmental Science and Pollution Research 23, 13754–13788 (2016).
Das, R. et al. Multifunctional carbon nanotubes in water treatment: The present, past and future. Desalination 354, 160–179 (2014).
Teoh, M. M. & Chung, T.-S. Membrane distillation with hydrophobic macrovoid-free PVDF–PTFE hollow fiber membranes. Separation and Purification Technology. 66, 229–236 (2009).
Das, R., Hamid, S. B. A. & Annuar, M. S. M. Highly efficient and stable novel nanobiohybrid catalyst to avert 3,4-dihydroxybenzoic acid pollutant in water. Scientific Reports 6 (2016).
Whitcomb, P. J. & Anderson, M. J. RSM simplified: optimizing processes using response surface methods for design of experiments. (CRC press, 2004).
Chai, S.-P., Lee, K.-Y., Ichikawa, S. & Mohamed, A. R. Synthesis of carbon nanotubes by methane decomposition over Co–Mo/Al 2 O 3: Process study and optimization using response surface methodology. Applied Catalysis A: General 396, 52–58 (2011).
Villacampa, J. I. et al. Catalytic decomposition of methane over Ni-Al 2 O 3 coprecipitated catalysts: reaction and regeneration studies. Applied Catalysis A: General 252, 363–383 (2003).
Chen, J., Li, Y., Li, Z. & Zhang, X. Production of CO x-free hydrogen and nanocarbon by direct decomposition of undiluted methane on Ni–Cu–alumina catalysts. Applied Catalysis A: General 269, 179–186 (2004).
Sharma, S. & Lakkad, S. Morphology study of carbon nanospecies grown on carbon fibers by thermal CVD technique. Surface and Coatings Technology. 203, 1329–1335 (2009).
Taleshi, F., Hosseini, A., Mohammadi, M. & Pashaee, M. Effect of hydrocarbon gas on synthesis and diameter of carbon nanotubes. Indian Journal of Physics 87, 873–877 (2013).
Endo, M. & Kroto, H. Formation of carbon nanofibers. Journal of physical chemistry 96, 6941–6944 (1992).
Rinaldi, A. et al. Controlling the yield and structure of carbon nanofibers grown on a nickel/activated carbon catalyst. Carbon 47, 3023–3033 (2009).
Deshmukh, A. A., Mhlanga, S. D. & Coville, N. J. Carbon spheres. Materials Science and Engineering: R: Reports 70, 1–28 (2010).
Coville, N. J., Mhlanga, S. D., Nxumalo, E. N. & Shaikjee, A. A review of shaped carbon nanomaterials. South African Journal of Science 107, 01–15 (2011).
Chen, X. et al. Synthesis, growth mechanism, and electrochemical properties of hollow mesoporous carbon spheres with controlled diameter. The Journal of Physical Chemistry C 115, 17717–17724 (2011).
Eklund, P., Holden, J. & Jishi, R. Vibrational modes of carbon nanotubes; spectroscopy and theory. Carbon 33, 959–972 (1995).
Dillon, A. C. et al. A simple and complete purification of single-walled carbon nanotube materials. Advanced Materials 11, 1354–1358 (1999).
Eckmann, A. et al. Probing the nature of defects in graphene by Raman spectroscopy. Nano Letters 12, 3925–3930 (2012).
Coates, J. In Encyclopedia of Analytical Chemistry (John Wiley & Sons, Ltd, 2006).
Hong, N. et al. Co-precipitation synthesis of reduced graphene oxide/NiAl-layered double hydroxide hybrid and its application in flame retarding poly (methyl methacrylate). Materials Research Bulletin. 49, 657–664 (2014).
Avilés, F., Cauich-Rodríguez, J., Moo-Tah, L., May-Pat, A. & Vargas-Coronado, R. Evaluation of mild acid oxidation treatments for MWCNT functionalization. Carbon 47, 2970–2975 (2009).
Das, R. Nanohybrid Catalyst based on Carbon Nanotube: A Step-By-Step Guideline from Preparation to Demonstration. (Springer, 2017).
Hou, P. et al. Purification of single-walled carbon nanotubes synthesized by the hydrogen arc-discharge method. Journal of Materials Research 16, 2526–2529 (2001).
Datsyuk, V. et al. Chemical oxidation of multiwalled carbon nanotubes. Carbon 46, 833–840 (2008).
Rinzler, A. et al. Large-scale purification of single-wall carbon nanotubes: process, product, and characterization. Applied Physics A: Materials Science & Processing 67, 29–37 (1998).
Wenzel, R. N. Surface Roughness and Contact Angle. The Journal of Physical Chemistry 53, 1466–1467 (1949).
Das, R. et al. Covalent functionalization schemes for tailoring solubility of multi-walled carbon nanotubes in water and acetone solvents. Science of Advanced Materials 7, 2726–2737 (2015).
Acknowledgements
The authors would like to acknowledge the National Chair of Materials Sciences and Metallurgy, University of Nizwa, Oman and the University of Malaya PPP- Grant (6091-2016A) and RP044D-17AET for funding this research.
Author information
Authors and Affiliations
Contributions
M.A.A. and Q.F.A. discussed and initiated the idea. M.M.A. and M.A.A. conceived and designed the research. M.M.A., M.A.A. and H.M.A. performed experiments. M.M.A., M.A.A., R.D., M.K.A. and M.N. analyzed the data and wrote the manuscript; M.A.A., M.M.A., M.K.A., R.D., S.B., N.A.H., M.H.A. reviewed the manuscript.
Corresponding author
Ethics declarations
Competing Interests
The authors declare no competing interests.
Additional information
Publisher's note: Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Electronic supplementary material
Rights and permissions
Open Access This article is licensed under a Creative Commons Attribution 4.0 International License, which permits use, sharing, adaptation, distribution and reproduction in any medium or format, as long as you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made. The images or other third party material in this article are included in the article’s Creative Commons license, unless indicated otherwise in a credit line to the material. If material is not included in the article’s Creative Commons license and your intended use is not permitted by statutory regulation or exceeds the permitted use, you will need to obtain permission directly from the copyright holder. To view a copy of this license, visit http://creativecommons.org/licenses/by/4.0/.
About this article
Cite this article
Aljumaily, M.M., Alsaadi, M.A., Das, R. et al. Optimization of the Synthesis of Superhydrophobic Carbon Nanomaterials by Chemical Vapor Deposition. Sci Rep 8, 2778 (2018). https://doi.org/10.1038/s41598-018-21051-3
Received:
Accepted:
Published:
DOI: https://doi.org/10.1038/s41598-018-21051-3
This article is cited by
-
Treatment of textile wastewater using carbon-based nanomaterials as adsorbents: a review
Environmental Science and Pollution Research (2023)
-
Synthesis of carbon nanotubes on activated carbon using a metal-free NaCl catalyst: a novel and green approach
Applied Nanoscience (2022)
-
One-pot synthesis of reduced graphene oxide-based PANI/MnO2 ternary nanostructure for high-efficiency supercapacitor applications
Journal of Materials Science: Materials in Electronics (2022)
-
Production of Smart Cotton-nickel Blend Fibers Using Functional Polymers Comprising Ammonium Polyphosphate and Silicone Rubber
Fibers and Polymers (2022)
-
Development of Carbon Nanofibers/Pt Nanocomposites for Fuel Cell Application
Arabian Journal for Science and Engineering (2020)