Research Article | Open Access
Luke J. Sweetman, Leighton J. Alcock, Jason D. McArthur, Elise M. Stewart, Gerry Triani, Marc in het Panhuis, Stephen F. Ralph, "Bacterial Filtration Using Carbon Nanotube/Antibiotic Buckypaper Membranes", Journal of Nanomaterials, vol. 2013, Article ID 781212, 11 pages, 2013. https://doi.org/10.1155/2013/781212
Bacterial Filtration Using Carbon Nanotube/Antibiotic Buckypaper Membranes
The preparation of free-standing carbon nanotube “buckypaper” (BP) membranes consisting of either single-walled carbon nanotubes (SWNTs) or multi-walled carbon nanotubes (MWNTs), and the antibiotic ciprofloxacin (cipro), is reported. The electrical, mechanical and morphological properties of these membranes have been characterised and are compared to those of the corresponding buckypaper membranes containing the surfactant Triton X-100 (Trix). Analysis of scanning electron microscopic images of the surfaces of SWNT/cipro and SWNT/Trix (Trix = Triton X-100) buckypapers revealed that the diameter of their surface pores was significantly smaller than that of the corresponding materials prepared using MWNTs. Similarly, the average internal pore diameter of both SWNT buckypapers was found to be smaller than that of their MWNT counterparts, after analysis of binding isotherms derived from nitrogen adsorption/desorption measurements performed on the materials. All four buckypaper membranes examined were found to be >99% effective for removing Escherichia coli (E. coli) from aqueous suspensions. However, buckypapers containing ciprofloxacin outperformed their counterparts containing the surfactant. Both MWNT buckypapers were more effective at preventing passage of E. coli than their analogues containing SWNTs, while fluorescence microscopic examination of stained membrane surfaces demonstrated that buckypapers composed of SWNTs had greater bactericidal properties.
Guarding water supplies against contamination from pathogenic organisms remain one of the most important challenges facing society [1, 2]. While filtration methods are effective for removing microbial contaminants, the susceptibility of nanofiltration and reverse osmosis membranes to fouling necessitates the use of additional disinfection processes to ensure that pathogenic organisms do not enter water supplies [3, 4]. A further weakness of current nanofiltration membranes is they lack analyte specificity [4, 5]. Consequently, there is an ongoing need to develop new membrane materials [5, 6].
Membranes composed of aligned arrays of carbon nanotubes (CNTs) have shown very high permeabilities towards water and gases [7, 8], as well as the ability to discriminate between molecules or nanoparticles on the basis of differences in their sizes . They have also proven effective for removing bacteria and virus particles from water samples , while several other studies have shown that CNTs have antimicrobial properties [10, 11]. This effect was more pronounced with single-walled carbon nanotubes (SWNTs) than multi-walled carbon nanotubes (MWNTs), which was attributed in part to the greater ability of the former to physically penetrate bacterial cell walls . Inspired in part by these results, Brady-Estévez and coworkers studied the antibacterial properties of CNT membranes and composite materials [12, 13]. One of their first studies involved buckypapers made from SWNT dispersions prepared in dimethylsulfoxide . These materials were prepared without the assistance of a dispersant molecule and proved highly effective at removing E. coli from aqueous solutions. Metabolic and viability assays performed on the surface of the BPs after they had been used for filtration experiments showed that the majority of the bacteria that had been retained were metabolically inactive and had compromised membranes. These buckypapers also proved effective at removing viral particles from solution, highlighting their potential utility for treatment of contaminated water supplies.
We recently used macrocyclic ligands to assist in the preparation of aqueous dispersions of SWNTs and buckypapers that retained the ligand molecules . Comparison to buckypapers prepared using Triton X-100 (Trix) as the dispersant revealed that incorporation of the macrocycles sometimes resulted in dramatic changes to the physical and morphological properties of the membranes, as well as their permeability towards water. We therefore considered that it might also be possible to use antibiotics with appropriate structural features to form CNT dispersions and buckypapers which retain antibiotic molecules and consequently display enhanced bactericidal activity. Further support for this proposal was provided by studies which showed that CNTs can remove antibiotics from aquatic environments by an adsorption mechanism [15, 16]. However, to date the only studies that have used antibiotics to disperse CNTs focussed on the preparation of modified electrodes containing thin films composed of MWNTs and the antibiotic ciprofloxacin (cipro; Figure 1) [17–19].
In this paper we report on the ability of free-standing SWNT and MWNT buckypapers containing ciprofloxacin to filter solutions containing Escherichia coli (E. coli) and the bactericidal properties of the buckypapers. In addition, the physical and morphological properties of MWNT/cipro and SWNT/cipro buckypapers are compared to each other and to those of the corresponding membranes containing the surfactant Trix, which has no significant antibacterial activity.
All chemical reagents were used as received from suppliers, without any further purification. SWNTs produced by the HiPco process were obtained from Unidym (Lot no. P2150), while thin MWNTs prepared by a chemical vapour deposition method were obtained from Nanocyl (Lot no. 081010). Ciprofloxacin hydrochloride was purchased from MP Biomedicals LLC.
2.2. Preparation of Dispersions
All dispersions were prepared in Milli-Q water (18.2 ΩM cm) using a SWNT or MWNT concentration of 0.1% (w/v), and either Trix or ciprofloxacin present at a concentration of 1.0% (w/v). In order to facilitate formation of dispersions, a high energy (400 W) sonication horn ( mm; Branson 450, Ultrasonics) was used with the following parameters: (; s; s). For a typical experiment 15 mg of CNTs were dispersed in 15 mL of dispersant solution. During sonication the reaction vial was placed inside an ice/water bath to minimize increases in temperature. A sonication time of 30 min was employed to prepare all CNT dispersions used for synthesising the buckypapers described in this paper.
2.3. Preparation of Buckypapers
In order to produce a small, circular buckypaper (approximate diameter 47 mm) two dispersions, prepared as described previously, were combined and added to a further 50 mL of dispersant solution (either 1.0% (w/v) Trix or cipro) and then subjected to treatment in a conventional ultrasonic bath (Unisonics; 50 Hz, 150 W) for 3 min. The solution was then diluted to a total volume of 250 mL using Milli-Q water and filtered under vacuum through a polytetrafluoroethylene (PTFE) membrane filter (5 μm diameter pore size; Millipore) housed in an Aldrich glass filtration unit, by using a Vacuubrand CVC2 pump to apply a vacuum between 30 and 50 mbar.
2.4. Characterisation Techniques
Absorption spectra (400–1000 nm) of all dispersions were obtained using a Cary 500 UV-vis-NIR spectrophotometer and quartz cuvettes. The dispersions were first diluted with Milli-Q water to ensure that the measured absorbances were within the optimal range of the instrument.
The surface morphology of buckypapers was examined using a JEOL JSM-7500FA FESEM. Prior to analysis, the buckypapers were cut into small strips and mounted on a small, conductive stub using carbon tape. The samples exhibited sufficient electrical conductivity to be imaged without prior sputter coating. Images obtained by scanning electron microscopy (SEM) were analysed using Image Pro Plus software to obtain quantitative information concerning the average diameter of surface pores. The average surface pore diameters of the buckypapers reported in Table 1 were determined using a single buckypaper sample. Energy Dispersive X-ray (EDX) spectroscopic analysis of the surface of buckypapers was performed concurrently to obtain information about the identity of elements present.
a: surface pore diameter derived by Image Analysis of SEM micrographs. b: buckypaper surface area obtained through Brunauer, Emmett and Teller (BET) analysis of isotherms derived from nitrogen adsorption/desorption measurements . cAverage internal pore diameter. dObtained through application of Horvath-Kawazoe (HK) and Barrett, Joyner and Halenda (BJH) methods to isotherms derived from nitrogen adsorption/desorption measurements [21, 22]. eAverage nanotube bundle diameter. fInsufficient data to enable calculation of this value. gData taken from .|
The contact angles of buckypapers were measured using the sessile drop method and a Data Physics SCA20 goniometer fitted with a digital camera. The contact angles of 2 μL Milli-Q water droplets on the surfaces of the buckypapers were calculated using the accompanying Data Physics software (SCA20.1). The mean contact angle was calculated using measurements performed on a minimum of five water droplets.
The electrical conductivity of buckypapers was determined using a standard two-point probe method . Details of the procedure employed to measure sample conductivities were described by us previously . Measurements were performed on three separate strips of membrane for each type of buckypaper, with the average values reported in Table 2. The mechanical properties of buckypapers were examined using a Shimadzu EZ-S universal testing device and buckypaper samples cut into small rectangular strips measuring . The latter were stretched using a 10 N load cell at a strain rate of 1 mm min−1 until sample failure. The tensile strength was determined as the maximum stress measured, while the ductility was the percentage elongation at breaking point. The Young’s modulus and sample toughness were also determined. Values for each of the previously mentioned mechanical properties are reported in Table 2 for each of the buckypapers examined and are the average of results obtained using three different strips of membrane.
Nitrogen adsorption/desorption isotherms were obtained for each type of buckypaper using a surface area analyzer (ASAP 2010 or ASAP 2020, Micromeretics) operating at 77 K and a single sample of each type of membrane. Prior to analysis, residual gas trapped within samples was removed under vacuum at 200°C. The resulting isotherms were analysed using the Horvath-Kawazoe (HK) and Barrett, Joyner and Halenda (BJH) methods to determine the distribution of small and large pores, respectively [21, 22]. In addition, multipoint Brunauer, Emmett and Teller (BET) analysis of the isotherms was used to calculate the specific surface areas of the samples .
2.5. Bacterial Filtration and Imaging Experiments
Escherichia coli JM109 was selected as the model bacterium throughout the course of this study. A single colony of E. coli was inoculated into 5 mL of Luria-Bertani (LB) broth and grown at 37°C for 16 h with shaking at 200 rpm. The overnight culture (1 mL) was used to inoculate 20 mL of prewarmed LB broth, which was subsequently incubated at 37°C with shaking until an OD600 of 0.5 (midexponential growth phase) was obtained. For filtration experiments, 1 mL of freshly prepared cells was suspended in 50 mL sterile saline solution (0.9% (w/v) NaCl) giving a final cell concentration of c.a. 107 mL−1. Prior to testing, the buckypaper membranes were sterilised by soaking in 70% ethanol and thoroughly washed with sterile saline to remove any remaining solution, and the glass filter holder and flask to be used for the filtration process were sterilized using an autoclave. Bacterial suspensions were filtered through dry buckypapers using a vacuum of approximately 200–300 mbar at room temperature (21°C). To determine the extent of removal of E. coli, a dilution series was prepared from the filtrate by plating onto LB agar and incubating overnight at 37°C. The numbers of colonies present after this period of time were then counted by direct visual inspection and converted to log removal values. Table 3 shows the average log removal values for each buckypaper after performing three separate experiments.
aComplete removal was observed for all membranes analyzed.|
The viability of E. coli on buckypaper membranes was examined using a live/dead assay performed in accordance with the procedure developed by Brady-Estévez et al. . Immediately after filtration experiments, buckypapers were either stained with propidium iodide (PI) followed by counter staining with SYTO-16 or stained with PI followed by counter staining with 4′,6-diamidino-2-phenylindole (DAPI). Staining was performed by adding 50 μL of PI solution in the dark. The stained buckypapers were then allowed to develop for c.a. 5 min before being rinsed with Milli-Q water. This process was then repeated for the counter stain, after which the buckypaper was again rinsed and stored in the dark prior to imaging using fluorescence microscopy.
Quantitative analysis of the fluorescent images was performed using the area-based estimation method outlined by Kang et al. . This required each of the images obtained to be effectively split into two separate images showing the individual fluorescence attributable to each dye used to stain the buckypaper surface. These images were then converted to 8-bit greyscale images in which the colour intensity was converted into a 256 increment scale, with 0 corresponding to completely black and 255 to completely white. The software package used enabled the distribution of the brightness of pixels within the individual images to be determined. From the resulting curves, a threshold intensity value was chosen between 0 and 255 for all images, which allowed the subsequent production of a binary black and white image. In the latter, the white pixels were considered as representing the presence of fluorescence at a particular location on the buckypaper surface. Therefore by determining the ratio of black to white pixels in the image the percentage of the total buckypaper area that was fluorescing as a result of the presence of either live or dead bacteria could be calculated. By comparing these values for the two dyes used to stain each buckypaper, the percentage of dead bacteria could then be determined. The previous experiments were performed in triplicate for SWNT/Trix and MWNT/Trix membranes, but only once, each for the corresponding buckypapers containing ciprofloxacin.
In addition to performing image analysis of buckypaper surfaces, the filtrates obtained after filtering solutions containing E. coli using either a SWNT/cipro or an MWNT/cipro membrane were stained and imaged to determine if any bacteria had crossed these buckypapers. In order to obtain images, a sample of the filtrate (c.a. 1 mL) was centrifuged and the resulting pellet resuspended in sterile saline prior to casting onto a poly-L-lysine-coated microscope slide. The sample was then dried in air and stained with a combination of PI and DAPI as described previously.
3. Results and Discussion
3.1. Preparation and Characterisation of Dispersions Containing Ciprofloxacin
The ability of ciprofloxacin to disperse SWNTs has not been reported previously. Figure 2(a) shows the absorption spectrum of a 3 mL aqueous sample containing 0.1% (w/v) SWNTs and 1.0% (w/v) ciprofloxacin, which had been sonicated for different periods of time. A series of features related to the so-called van Hove singularities is apparent , and the absorbance at all wavelengths increased as the duration of sonication was lengthened. Both observations indicate that the SWNTs were becoming increasingly dispersed in the presence of the antibiotic. By plotting the absorbance of the solution at a given wavelength as a function of sonication time (e.g., Figure 2(b)), it can be seen that treatment for 30 min was sufficient to ensure significant dispersion of the SWNTs. Similar results to these were obtained when absorption spectra were recorded for a solution containing 0.1% (w/v) MWNTs and 1.0% (w/v) ciprofloxacin, although as expected the spectra lacked features attributable to the van Hove singularities.
3.2. Preparation and Characterisation of Buckypapers Containing Ciprofloxacin
Buckypapers were made by vacuum filtration of dispersions containing a total of either 30 or 90 mg of CNTs and either 1% (w/v) cipro or 1% (w/v) Trix. The thickness of all BPs was similar (50 μm) regardless of their composition. Figure 3 presents SEM micrographs of the buckypapers, which reveal that their surface morphology varied depending on the dispersant and type of CNT used. Inspection of the micrographs also suggests that the diameter of the surface pores of the MWNT/Trix membrane are larger than that of the other buckypapers. This was further investigated by quantifying the diameter of the pores present on the surface of each of the four membranes using Image Pro Plus software. The results of this analysis are presented in Table 1 and confirm that the surface pores were the largest in the case of the MWNT/Trix membrane ( nm). However, these were only slightly larger than those present on the surface of the MWNT/cipro buckypaper ( nm). Inspection of the data in Table 1 also shows that the surface pores of both MWNT buckypapers are at least 2.5 times larger than those present for either SWNT membrane, suggesting that the choice of CNT is a major factor in determining surface morphology. This view is supported by an examination of the surface diameters of other SWNT buckypapers reported in our previously published study into the properties of a range of such materials. This included buckypapers synthesised from dispersions prepared using several low molecular mass dispersants including a cyclodextrin, a calixarene, a porphyrin, and a phthalocyanine . For each of the latter materials analysis of the average surface pores evident in SEM images using Image Pro Plus software revealed that they were <50 nm, which is smaller than that of both MWNT buckypapers examined as part of the current study.
Further information about the surface area and average internal pore morphology of the BPs was obtained through analysis of nitrogen adsorption/desorption isotherms. Figure 4 shows the isotherms obtained for the SWNT/cipro, MWNT/cipro, and MWNT/Trix buckypapers. All may be categorized as general type IV isotherms that exhibit hysteresis at higher relative pressures. The isotherm for the SWNT/cipro buckypaper (Figure 4(a)) is very similar to those reported previously for other buckypapers prepared using the same type of SWNTs and low molecular mass dispersants including Trix . In keeping with these previous results, the extent of nitrogen adsorption and desorption is significant at all relative pressures. In contrast, the isotherms obtained for the MWNT/cipro and MWNT/Trix buckypapers (Figures 4(b) and 4(c)) show that nitrogen adsorption and desorption occur predominantly at . This suggests that there are significant differences between the internal morphologies of SWNT and MWNT buckypapers.
In order to investigate this hypothesis further, each of the isotherms in Figure 4 was subjected to analysis using the Barrett, Joyner and Halendar (BJH) and Horvath-Kawazoe (HK) methods [21, 22]. Analysis via the HK method afforded information on the distribution of small pores (<2 nm) within each of the membranes, while the BJH method allowed estimation of the larger pores. Combining the two sets of results yielded the pore size distribution profiles shown in Figure 5. Each set of curves show a large peak between 0.5 and 1.5 nm, which can be attributed to the pores between individual nanotubes contained within CNT bundles (interstitial pores). In contrast, significant difference can be seen between the distributions of larger pores that occur between nanotube bundles for the SWNT and MWNT buckypapers. In the case of the SWNT/cipro membrane (Figure 5(a)) a second, well-defined peak is centered at approximately 6 nm which can be attributed to the interbundle pores. For the two MWNT buckypapers, however, it is clear that the corresponding pores are significantly larger. In the case of the MWNT/Trix buckypaper (Figure 5(c)) the distribution of interbundle pores is centered at approximately 23 nm. While there is no corresponding peak in the pore distribution curve for the MWNT/cipro buckypaper (Figure 5(b)), it is still clearly evident that the maxima in the peak distribution are located at >15 nm. Numerical integration of the sets of curves in Figure 5 was performed in order to calculate the average internal pore diameter of the membranes, as well as the percentage contribution of the interbundle pores to the total free volume. The results of this analysis, along with those obtained via application of the BET method  to the original isotherms, are presented in Table 1.
Of particular note is that the average diameter of the internal pores of the two SWNT membranes is significantly lower than that for the corresponding MWNT buckypapers, mirroring what was observed with the surface pores. Furthermore the average internal pore diameters obtained for the two SWNT membranes ( and nm) are generally similar to values reported recently for other buckypapers prepared using the same batch of SWNTs and low molecular mass dispersants . For example, the average internal pore diameter for a SWNT/Trix buckypaper was previously reported to be nm . However, it must be noted that one SWNT buckypaper in the latter study, that was prepared using phthalocyanine tetrasulfonic acid as the dispersant, was shown to possess internal pores with an average diameter of nm, which is comparable to that of the two MWNT membranes in the current study. In contrast to this, there was generally little difference between the average nanotube bundle diameter, internal pore volume, or surface area of SWNT and MWNT membranes in the current study. The one significant exception to this set of general trends was that the surface area of the SWNT/Trix buckypaper was more than two times bigger than that of any of the other materials.
Evidence that ciprofloxacin had been retained in the buckypapers was obtained by microanalysis. The atomic weight percentages of nitrogen and fluorine in a sample of a SWNT/cipro membrane were 2.8% and 1.2%, respectively, while for a MWNT/cipro buckypaper these values were 2.0% and 1.0%, respectively. Both of these elements are present in ciprofloxacin but not in MWNTs or SWNTs. Further evidence in support of incorporation of antibiotic molecules in the buckypapers was obtained using energy dispersive X-ray (EDX) spectroscopy. For example, the EDX spectrum (Figure 6(a)) of a MWNT/cipro membrane showed a peak with weak intensity at ~0.65 keV which is indicative of the presence of fluorine, and is absent from the corresponding spectrum of an MWNT/Trix buckypaper (Figure 6(b)).
The mechanical properties of the four buckypapers were investigated using a tensile test method, and the results obtained summarised in Table 2. Each of the mechanical properties determined from the stress-strain curves fell within a relatively narrow range of values. For example, the tensile strength of the materials was found to vary between and MPa, while the Young’s moduli were in the range GPa. In all cases the mechanical properties of the buckypapers were found to be similar to those reported recently for other buckypapers prepared using the same batch of SWNTs and macrocyclic ligand dispersants . Replacement of Trix by ciprofloxacin in both types of buckypapers generally resulted in a decrease in the mechanical properties of these materials. However, all buckypapers remained intact after being used for the bacterial filtration experiments described later, which typically lasted approximately for 1 h. This suggests that they have sufficient mechanical integrity to allow their use for multiple filtration experiments. Each of the buckypapers containing Trix or cipro was found to be hydrophilic using the sessile drop method, which gave contact angles between and °. Measurement of the electrical conductivity of the buckypapers using a 2-point probe method gave values ranging from to S cm−1, with the values for the materials prepared using SWNTs significantly larger than for those obtained using MWNTs. The conductivities obtained for the two SWNT buckypapers are comparable to those obtained for other membranes prepared using this class of CNTs and low molecular mass dispersants .
3.3. Bacterial Filtration Experiments
The ability of the buckypapers to remove E. coli JM109 was initially investigated by vacuum filtering (at ~200–300 mbar) 50 mL suspensions of the bacterium (in 0.9% (w/v) NaCl) with a final concentration of c.a. 104 cells mL−1. Dilution series produced from the filtrates were plated onto Luria-Bertani (LB) agar and incubated overnight at 37°C. Representative images of E. coli colonies grown from the initial bacterial suspension, and after filtering suspensions across either an MWNT/Trix or SWNT/Trix buckypaper, are shown in Figure 7. The total colony forming units (CFU) for each plate were counted and compared to the CFU for the initial bacterial suspension. The results of this analysis showed that each buckypaper removed >99% of the E. coli present in the initial suspension, demonstrating that they were highly effective for this purpose. In contrast, when the 5 μm PTFE membrane used as a support for preparing the buckypapers was used to filter the same E. coli suspension, only 90% of the bacteria were removed. In order to further facilitate comparison of the relative effectiveness of the different buckypapers, the percentage recoveries () were converted into values of Log Removal using (1):
Table 3 presents the values of Log Removal obtained for the various buckypapers, which suggest that buckypapers containing MWNTs were more effective for filtering E. coli than their SWNT counterparts containing the same dispersant. As anticipated, incorporation of ciprofloxacin instead of Trix into both types of buckypapers reduced the number of viable E. coli in the filtrates. In the case of experiments performed using MWNT/cipro buckypapers, complete removal of bacteria was observed for each of the three samples analysed, suggesting these membranes were the most effective for removal of E. coli.
Further evidence in support of this conclusion was provided by experiments in which the filtrates obtained using MWNT/cipro and SWNT/cipro buckypapers were stained using a combination of propidium iodide (PI) and DAPI and subsequently imaged using fluorescence microscopy. Propidium iodide is internalised only by membrane compromised (i.e., dead) bacterial cells and fluoresces red when excited with high-intensity light. In contrast, DAPI is able to enter all cells and fluoresces blue upon binding to DNA when appropriately excited with light. Figure 8 shows the fluorescence microscopic images obtained of the initial E. coli suspension as well as those of a filtrate obtained after filtering an identical sample of bacteria across a SWNT/cipro buckypaper. The image of the initial bacterial sample (Figure 8(a)) shows, as expected, blue regions attributable to the presence of viable E. coli cells, as well as red regions due to cells that had died as a result of natural attrition. In contrast, the image of the filtrate obtained using an SWNT/cipro buckypaper (Figure 8(b)) shows only a small number of red areas, indicating that some dead bacteria had passed across the membrane. The image of a filtrate obtained using an MWNT/cipro buckypaper did not show either red or blue regions, indicating that no bacterial cells passed across this membrane. This is consistent with the results presented previously that were obtained by counting the CFU, which indicated that the MWNT/cipro buckypaper was the most effective for filtering E. coli.
The general paucity of E. coli present in the filtrates obtained using each of the buckypapers can be attributed largely to rejection of bacteria owing to the greater size of their cells compared to the pores present on the surface and within the membranes and toxicity imparted onto the bacteria through contact with the nanotubes or dispersant molecules. The extent of inactivation of E. coli cells trapped on the surface of the buckypapers was assessed using a fluorescence-based viability assay reported previously . In short, the surfaces of the four membranes were stained using a combination of either PI and SYTO-16 or PI and DAPI, after they had been used to filter the same number of bacterial cells and then imaged using fluorescence microscopy. Like DAPI, SYTO-16 is able to enter all cells. However, it fluoresces green instead of blue upon binding to DNA when excited with light of the appropriate wavelength.
Representative images of each of the four different types buckypapers, after they had been stained as described previously, are shown in Figure 9. Quantitative analysis of the images was performed in accordance with the method outlined by Kang et al. . The results of analysis of the images presented in Figure 9 are presented in Table 4. Inspection of the data shows that there was perhaps a small difference in cell killing efficiency between the two buckypapers prepared using Trix as the dispersant, with the membrane synthesised using SWNTs appearing to be slightly more effective. Of more relevance is that the results show that both the MWNT and SWNT buckypapers displayed higher bactericidal properties when ciprofloxacin was present. For example, in the case of MWNT buckypapers, the percentage of dead bacteria on the membrane surface increased from % for MWNT/Trix to 100% for MWNT/cipro.
aValues determined using one sample only. |
In this paper we have demonstrated that ciprofloxacin can be used to assist the formation of dispersions of SWNTs. Furthermore buckypapers obtained from SWNT/cipro or MWNT/cipro dispersions retain antibiotic molecules after preparation. Analysis of SEM micrographs, and nitrogen adsorption/desorption isotherms, demonstrated that significant differences exist between the surface and internal morphologies of buckypapers prepared from MWNTs and SWNTs. In addition, the data also showed that replacing Trix as the dispersant used during buckypaper preparation by ciprofloxacin had little impact on these characteristics.
Each of the four buckypapers prepared removed more than 99% of the E. coli present in an aqueous suspension. This provides evidence that free-standing buckypaper membranes can be as effective for removing microbial contaminants from water supplies as the composite CNT materials investigated previously [12, 13]. It was somewhat surprising that the overall bacterial filtration efficiency of MWNT buckypapers prepared using either Trix or cipro was greater than that of the corresponding SWNT membranes. This suggests that there is something inherent in the structure of MWNT buckypapers that makes them more suitable for bacterial filtration applications.
Incorporation of ciprofloxacin significantly enhanced the ability of SWNT and MWNT buckypapers to impart bactericidal activity on E. coli. This demonstrates that it is possible to incorporate into buckypapers dispersant molecules with chemical and biological properties designed to improve their effectiveness for particular applications. This added functionality will only exist while the dispersant molecules are retained by the buckypaper. We therefore used absorption spectrophotmetry to monitor the leaching of ciprofloxacin from an MWNT/cipro buckypaper under conditions identical to those used for performing a bacterial filtration experiment. After one hour only 0.3 mg of ciprofloxacin had leached from the buckypaper, which is less than 1% of its total mass. Future experiments are planned which will investigate what, if any, impact the loss of ciprofloxacin has on the efficacy of buckypapers when used multiple times for bacterial filtration experiments. In addition, we also intend to examine the effectiveness of our buckypapers for filtering solutions containing larger numbers of E. coli or different types of both gram-negative and gram-positive bacteria. We believe that these studies could provide insights into the reasons behind the observed difference in bacterial filtration efficiency between MWNT and SWNT membranes presented in this paper.
The authors acknowledge financial support from Australian Institute of Nuclear Science and Engineering (AINSE), Water Quality Research Australia, the New South Wales Environmental Trust, and the Australian Research Council (Centre of Excellence Funding and Future Fellowship to M. in het Panhuis). The authors would like to thank Mr. Tony Romeo for the assistance obtaining SEM images and EDX spectra, Mrs Amanda Skora for the help performing the bacterial filtration experiments, and both Mr Nick Scales and Ms. Ilkay Chironi for the help performing nitrogen adsorption/desorption measurements. Mr Michael A. Ralph is also thanked for the assistance producing some of the images. The authors hereby declare that there is no conflict of interests resulting from the use of the chemicals or the equipment obtained from the nominated suppliers.
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