Abstract

The effect of carbon nanofibers (CNFs) and carbon nanotubes (CNTs) on the thermal and chemical stability of polypropylene (PP) when subjected to oxidation in a strong acid medium was studied. The effect of CNFs and CNTs on the crystalline morphology and the melting and crystallization temperatures was also studied. The thermal stability increased markedly; the decomposition temperature, for example, increased from 293C for pure PP to 312 and 320C for PP with CNFs and CNTs, respectively. The crystallization temperature increased perceptibly with the addition of CNTs or CNFs, from 107C for pure PP to 112 and 114C for PP with CNFs and CNTs, respectively. The oxidative degradation with nitric acid produced a reduction in molecular weight; however, this negative effect was less pronounced in the PP compositions with carbon nanoparticles. After 8 hours in nitric acid, this reduction was from 141,000 to 68,000 (for pure PP), to 75,000 (for PP-CNFs), and 79,500 (for PP-CNTs). X-ray diffraction showed that the alpha type crystallinity remains, irrespective of the nucleating agent. Finally, the intensity ratio between the (040) (at 16.7) and the (110) (at 13.9) reflections increased, which was taken as an indication of an increasing nucleating efficiency.

1. Introduction

It is well known that polypropylene (PP) is one of the most amply used commodity plastics, mainly because of the ease of processing and the inherent wide range of properties [1].Additionally, with the addition of filler particles, and especially nanoparticles, this commodity plastic can be tailored to cover many engineering applications. There are many studies that report on the use of different nanoparticles in polypropylene in order to impart or modify a given property. Clay [24], calcium carbonate [5], titanium dioxide [6], and carbon nanoparticles [7] have been used to enhance the mechanical and thermal properties, the chemical and flame resistance, and the barrier properties of PP. These nanoparticles may act as nucleating agents when incorporated into PP, promoting thus the heterogeneous crystalline growth.

This would be of utmost interest for applications such as lead-acid car battery cases and geomembranes, where the plastic, mainly PP or polyethylene (PE), is to be in contact with highly corrosive acid liquids [8]. The chemistry and semicrystallinity characteristics of polyolefins impart to them the good chemical and mechanical properties necessary to assure the extended life of the geomembranes in these applications. Another important application of PP is in lead-acid car battery cases in which their outstanding properties make it the ideal option for long time performance.

In both applications the PP is in contact with highly corrosive substances which can alter its composition and structure and significantly reduce its chemical and mechanical properties. In a previous work [7], the authors reported on the excellent nucleating ability of carbon nanoparticles (carbon nanotubes “CNTs” and carbon nanofibers “CNFs”), as compared to commercial nucleating agents for PP. The crystallization temperature of PP, from the melt, increased approximately 20°C above that of pure PP, using a concentration as low as 0.05 wt% of carbon nanoparticles. This excellent nucleating capacity of CNTs and CNFs has also been reported by other authors [913], though some authors have found that above 4 wt% this ability reaches a plateau and remains constant [14]. In addition to this nucleating effect, it has been found, via TGA, that these carbon nanoparticles increase the temperature for the onset of the PP decomposition [12, 13, 1517] by as much as 20°C [18].

In spite of the many reports on the enhancement of the PP properties, conveyed by the nucleating agents in general and by the carbon nanoparticles in particular, very little is known on the effect of these carbon nanoparticles on the chemical stability of PP compositions. The purpose of the present work is to study the relationship between the increase in the thermal and chemical resistance and the enhanced nucleation induced by CNFs, CNTs, and a commercial lithium benzoate (LiBe).

2. Experimental

2.1. Materials

The polymer used in this study was a commercial grade isotactic Polypropylene “PP” from Total Petrochemicals, USA, with an average molecular weight Mw of 150,000 and a melt flow rate of 15 g/10 min. The carbon nanoparticles used in this study, were: carbon nanofibers, Pyrograf III (CNFs), also known as Stacked-Cup Carbon Nanotubes (SCCNT), with a nominal surface area of 20 m2/g, from Applied Sciences, Inc., USA and multi-walled carbon nanotubes (CNTs), with a nominal surface area of 200 m2/g, from Nano-Lab, Inc., USA. The commercial lithium benzoate (LiBe) nucleating agent was from Micronisers Pty Ltd., Australia. The fuming nitric acid used was from Merck, USA.

2.2. Sample Preparation

A series of PP compositions with 0.05 wt% of each of CNFs, CNTs, and LiBe were prepared via melt mixing for 10 min, at 170°C and 50 rpm, in a Brabender torque rheometer mixing chamber. Very low nucleating agent concentrations (0.05 wt%) were in order to prevent the excess of nucleating particles from interfering with the spherulitic growth, as has been observed by other authors when using high CNTs or CNFs concentrations [9, 14, 19]. Plain PP was also passed through the mixer to produce blank samples. All compositions were then compression molded to produce 20 × 20 × 0.3 cm3 laminates, from which, 10 cm long and 1 cm wide strips were cut. These strips were immersed in fuming nitric acid at 80°C for periods of 2, 8, and 21 hours, after which, the samples were taken from the nitric acid bath, washed with distilled water until neutral pH, and finally, thoroughly washed with acetone, prior to analysis.

2.3. Evaluation

Following the nitric acid treatment and the appropriate washing, all samples were first analyzed for chemical changes with respect to the time in strong acid medium, using a Perkin-Elmer “Spectrum” FTIR spectrometer with an attenuated total reflectance (ATR) attachment. The spectra were obtained at 20 scans and a resolution of 4 cm−1. Two test specimens were used for each case. The samples were then subjected to thermal analysis using a Perkin-Elmer DSC-7 in order to establish the changes of the thermodynamic variables during treatment in a strong acid medium. Each sample of approximately 8 mg was first heated from room temperature to 180°C at 10°C/min, held there for 2 min, and then cooled down to room temperature at 10°C/min, all under nitrogen atmosphere. In order to study any change in the crystalline morphology, either due to the acid treatment or to the inclusion of nanoparticles, XRD was performed in a Siemens D5000 (25 mA, 35 kV) using CuKa X-ray radiation, at 0.6 degrees/min from 1 to 35 degrees. Finally, the samples were subjected to thermal analysis using a Shimadzu TGA-50 analyzer for studies of the thermal degradation, from room temperature to 400°C, at a heating rate of 10°C/min, under air atmosphere.

A gel permeation chromatograph GPC V-2000, with a refraction index detector and “styragel” columns, was used to determine the evolution of molecular weight and molecular weight distribution with respect to the time of treatment in the strong acid medium. Samples for GPC analysis were first dissolved in trichlorobenzene and then run at 140°C, at a flow rate of 1 mL/min.

3. Results and Discussion

Figure 1 shows the TGA results of the pure PP and the PP compositions with 0.05 wt% LiBe, CNTs, or CNFs, with zero hours of immersion in nitric acid. It can be observed that up to ~220°C, all 4 samples remain unaltered; but thereafter, the decomposition first occurs in the pure PP, followed by the nucleated compositions; the CNFs and CNTs compounds decompose at the highest temperatures, as shown in Table 1.

These results corroborate the enhanced thermal and chemical stability of the nucleated compositions. This enhanced stability is related to the crystalline structures produced in PP, in the presence of nucleating agents. Miltner et al. and Assouline et al. [19, 20] reported the nucleating ability of carbon nanoparticles and observed that these particles generate polymorphism in PP as well as transcrystallinity in the vicinity of CNTs. It is assumed that this greater molecular order hinders the oxidation of PP.

The increase in the decomposition temperature of the carbon-nucleated compositions may also be due to the barrier effect of the carbon nanoparticles, which when well dispersed, form a barrier that obstructs the oxygen diffusion [21], retarding thus the thermo-oxidative degradation of the polymer. The more marked effect of the CNTs, versus the CNFs, is probably related to the larger nominal surface area.

With respect to the decomposition of PP in nitric acid, Figure 2 shows the evolution of NO2 and CO with time, on samples immersed in nitric acid for 8 and 22 hours, as taken from the IR absorbance peaks at 1555 and 1710 cm−1, respectively. It is observed that as the immersion time in nitric acid increases, the presence of NO2 increases, becoming apparent after 8 hours in nitric acid and increasing its presence with time. The presence of CO on the other hand becomes apparent only after 22 hours in nitric acid.

The decomposition first involves the nitration of the PP chain, prior to the chain scission that starts to occur as a result of the formation of carbonyl groups. This is why the carbonyl bands in the FTIR analysis appear only after 22 hours in nitric acid [22]. This indicates that the PP oxidation in acid medium, quite different to that reported for PE [21], could be assumed to be due to the presence of the labile hydrogen atoms in the PP methyl groups. The greater concentration of NO2 in the compositions with CNFs or CNTs is simply because these nanoparticles tend to oxidize in strong acid medium [2325].

GPC results, showing the decrease in molecular weight of the pure PP samples with the time of immersion in nitric acid are presented in Figure 3(a). It is observed that after 2 hours in nitric acid, the decrease in molecular weight, (molecular weight taken at the peak of the GPC curves and designated as “Mp”), was negligible and remained at ~141,000 (i.e., 105.15). But after 8 hours in nitric acid, this decrease in Mp was considerable from ~141,000 to ~68,000 (i.e., 104.83).

Figure 3(b), on the other hand, shows that after 8 hours in nitric acid, the molecular weight, as taken at the peak of the GPC curve, decreased from 141,000, for the original PP, to 68,000 (PPPure), 71,000 (PPLiBe), 75,000 (PPCNFs), and 79,500 (PPCNTs). The differences in molecular weight after the 8 hours in nitric acid are really small. These small differences are assumed to arise because the nucleated crystalline structures provide a slightly better chemical stability for the PP nanocompounds. In addition, the carbon nanoparticles tend to act as free radical scavengers, as reported elsewhere [12, 13, 15, 23], further retarding a little bit the PP decrease in molecular weight. The degradation mechanism is assumed to involve the separation of the labile hydrogen atoms and their substitution by the NO2 groups in the amorphous phase of the main PP chain, followed by the chain scission. This results in the terminal carbonyl groups, as observed via the FTIR analysis.

Figure 4 shows the TGA curves of pure PP and PP compositions with 0.05 wt% LiBe, CNTs, or CNFs obtained in samples collected after 8 hours of immersion in nitric acid. First, it can be observed that all 4 samples remain unaltered up to ~240°C, that is, 20°C higher than that for samples with 0 hours in nitric acid (Figure 1). But thereafter, again, the decomposition first occurs in the pure PP, followed by the LiBe, CNFs, and CNTs compounds, as shown in Table 1.

Comparing the results among samples immersed in nitric acid for 0 and 8 hours (Figures 1 and 4, resp.), it can be observed that samples immersed in nitric acid (Figure 4), decompose at much higher temperatures, showing a 10 and 50 weight percent loss at temperatures ~42 and ~70°C higher, respectively, than those corresponding to samples without immersion in nitric acid (Figure 1).

Considering that the immersion in nitric acid tends to wash out the amorphous fraction of the PP samples, then, the immersed samples in Figure 4 surely have a greater crystalline fraction than the not immersed samples in Figure 1, producing thus the marked differences in thermal stability, which could be attributed entirely to the greater crystalline fraction.

The XRD diffractograms in Figure 5 show the position of the crystalline planes of pure PP and of the nucleated PP, with 0 and 8 hours of immersion in nitric acid. It can be observed that neither the nucleating agents nor the immersion in nitric acid have an effect on the position of the diffraction signals.

This indicates that the crystalline type remains the same alpha crystals. Both, pure PP and PP compositions with nucleating agent, either with 0 or with 8 hours of immersion in nitric acid, present the same peaks at 2(theta), that is, 13.9, 16.7, 18.3, 21.6, and 21.9 degrees, which correspond to the planes (110), (040), (130), (111), and (041), respectively, of this alpha morphology. These results coincide with those found for PP/SWNT and PP/MWNT, as reported by several authors [2628].

In addition, a clear tendency for the increase of the intensity ratio between the (040) (16.7 degrees) and the (110) (13.9 degrees) reflections can be observed. This increase can be taken as an indication of an increasing nucleating efficiency, as reported elsewhere [29].

Figure 6 shows the fusion thermograms of the different PP samples, where it can be observed that the peak fusion temperatures are very similar among them, 150.6°C for pure PP and 151.5°C for the nucleated PP compositions.

However, the fusion interval appears to be narrower for the PP compositions with nucleating agent, LiBe, CNTs, or CNFs, surely due to the greater crystal size homogeneity.

In addition, it is observed in the inserted Table that the enthalpy of fusion increases very slightly in the nucleated samples. Considering thus the very small enthalpy changes among the PP and the PP with the different nucleating agents, it can be concluded that the percent crystallinity remains approximately the same.

Figures 7(a) and 7(b) present the variation of the crystallization and fusion temperatures, respectively, as obtained in a DSC experiment for pure PP and the PP compositions with LiBe, CNTs, and CNFs, in samples collected after different times of immersion in nitric acid. Figure 7(a) shows that increased from 107°C for the PP to 110, 112, and 114°C, for the PP compositions with LiBe, CNFs, and CNTs, respectively. It is thus apparent, that the most efficient nucleating agents are the CNTs, followed closely by the CNFs. The slight difference among them is attributed to the greater nominal surface area of the CNTs. Figure 7(b), on the other hand, shows that is around °C in samples collected after 0 and 2 hours in nitric acid, but then decreases after 8 and 21 hours in nitric acid. It is also observed that, for all times of immersion in nitric acid, the nucleated PP compositions, especially those with CNFs or CNTs, present a higher than that of pure PP. This confirms the greater nucleating efficiency of the CNFs and CNTs, as shown in Figure 8.

The nucleating efficiency (NE) [30, 31] was calculated using (1) as follows: where is the measured crystallization temperature for the particular nucleating agent, and and are the crystallization temperatures of the nonnucleated and self-nucleated polymers, respectively. A value of equal to 140°C was obtained from the self-nucleation experiments. The crystallization time , was calculated using (2) as follows: where is the rate of cooling in the DSC crystallization experiment (°C/min), and and are the temperatures at the onset of crystallization and at the maximum rate of crystallization (i.e., at the peak of the DSC crystallization curve) [32]. These data is presented in Figure 8, where it can be observed that the most efficient nucleating agents are the CNTs, followed by the CNFs; but it can also be observed that pure PP presents an apparent negative nucleating efficiency, which could be attributed to the presence of grafted chemical groups on the main PP chain after the nitric acid treatment. The crystallization time is approximately the same for the 3 nucleating agents, that is, LiBe, CNFs, and CNTs; but this is markedly less than that for pure PP.

It is assumed that the greater nucleating efficiency of CNFs and CNTs, as observed in Figure 8, is the main reason for the slightly better thermal and chemical stability of the corresponding PP compounds, as obtained from the TGA and GPC analyses, and of the increased and , as obtained from the DSC analyses.

Finally, considering that the amount and morphology of the crystalline structure in a semicrystalline polymer greatly affects in a positive way its chemical and mechanical properties, the inclusion of carbon nanoparticles as nucleating agents in PP would ensure better chemical resistance and mechanical properties when subjected to aggressive environments along its useful life.

4. Conclusions

Carbon nanoparticles, such as CNTs and CNFs increased markedly the thermal and chemical properties of PP, acting as very efficient nucleating agents, even better than the commercial LiBe, The decomposition temperature increased from 293°C for the pure PP to 312 and 320°C, for the PP compositions with CNFs and CNTs, respectively. The oxidative degradation with nitric acid produced a reduction in molecular weight, as determined by DSC; however, this was much less pronounced in the PP compositions with carbon nanoparticles. This reduction was from 141,000 to 68,000, 75,000, and 79,500, for pure PP, PP-CNFs, and PP-CNTs, respectively.

XRD results showed that the crystalline type was not affected by the nucleating agent; it remained of the alpha type. In addition, it was found that the carbon nanoparticles are highly efficient nucleating agents for the crystallization of PP. The crystallization temperature (DSC) and the decomposition temperature (TGA) of PP, both increased with the addition of CNTs or CNFs.

In general the mechanical performance of PP composites can be enhanced by the addition of CNTs or CNFs as nucleating agents. This increased resistance of PP/carbon nanoparticles compositions to thermal and chemical attack increases the viability of using PP in such demanding applications as lead-acid car battery cases and films to be used as geomembranes.

Considering that the amount and morphology of the crystalline structure in a semicrystalline polymer greatly affects in a positive way its chemical and mechanical properties, it can be concluded that the inclusion of carbon nanoparticles as nucleating agents in PP would ensure better thermal and chemical resistance when subjected to aggressive environments.

Acknowledgments

The authors wish to thank CONACYT for its financial support to carry out this study, through Project 84424. In addition, one of the authors F. Avalos-Belmontes wishes to thank CONACYT for its support to spend a sabbatical at CIQA. Finally, the authors wish to thank M. Sánchez-Adame, A. Espinoza-Muñoz, M. C. Gonzalez-Cantu, T. Rodriguez-Hernandez, B. Huerta-Martinez, J. Rodriguez-Velazquez, J. F. Zendejo, E. Hurtado-Suarez, and P. Siller-Flores for their valuable technical and informatics support.