Open access peer-reviewed chapter

Biodegradable Chitosan Matrix Composite Reinforced with Titanium Dioxide for Biocidal Applications

By Johnny López Calero, Zuleika Oquendo Berríos and Oscar M. Suarez

Submitted: September 24th 2018Reviewed: January 14th 2019Published: February 15th 2019

DOI: 10.5772/intechopen.84397

Downloaded: 148

Abstract

Access to drinkable water is increasingly difficult in developing nations. According to the World Health Organization, more than 1.2 billion people lack access to this resource. The scientific community has risen to the challenge by developing innovating methods to purify water. In this context, a chitosan/titanium dioxide biocomposite represents an appealing, economically viable solution to remove oils, heavy metals, and pathogen colonies from contaminated waters. The present chapter reports the study of a chitosan film matrix impregnated with nanoparticles, which was capable of expressing antibacterial properties when exposed to UV light. Several techniques allowed characterizing the biocomposite uniformity, corroborating the crystal structure and assessing the bonding type of this biocomposite mixture. Antibacterial tests with Escherichia coli (Gram-negative) and Staphylococcus aureus (Gram-positive) were completed via growth curve analysis and the Kirby-Bauer technique. The results of this encompassing study revealed that bacterial growth was reduced by more than 50%. Optical microscopy, Fourier-transform infrared spectroscopy, and X-ray diffraction helped to characterize this biocomposite film. This chapter discusses how a novel and biodegradable film represents a better antibacterial material that is able to eliminate pathogens cost-effectively.

Keywords

  • chitosan
  • titanium dioxide
  • anatase
  • Escherichia coli
  • Staphylococcus aureus
  • composite
  • biocide

1. Introduction

The widespread use of antibiotics has promoted the dissemination of multidrug resistance (MDR) genes in bacteria, whereas nanoparticles (NPs) have proven to be effective when dealing with this bacteria type [1]. Superbugs (i.e., bacteria which are resistant to nearly all antibiotics) have evolved due to the abuse, misuse, and negligence of antibiotics. They are capable of transferring their resistance by mechanisms as plasmid [2], transposon [3], and integrons [4]. This means that just one superbug can render an infection nearly untreatable. Antibiotics target mainly three areas inside bacteria: the cell wall, the translational machinery, and the DNA replication system. Superbugs can develop genes capable of resisting the effect of antibiotics, ranging from the expression of enzymes and modification of cell components all the way to the creation of efflux pumps [5]. For example, enzymes such as β-lactamase [6] could alter the chemical structure of the antibiotics, leaving them inactive. Meanwhile, cell components such as ribosomes [7] offer resistance and efflux pump work by removing antibiotics from the inside of a cell and maintaining a safe environment for which the bacteria can grow normally.

Furthermore, NPs work differently when it comes to dealing with bacteria; this makes any antibiotic resistance ineffective against NPs. The NP antimicrobial mechanism falls into three categories: oxidative stress induction [8], metal ion release [9], and nonoxidative [10]. These mechanisms all work toward producing bacterial cell death.

Nanoparticles, as nanostructured materials, can be defined as three-dimensional materials with dimensions in the nanoscale (1–100 nm). As many studies suggest, they offer an array of antibacterial properties against Gram-negative and Gram-positive bacteria, such as E. coli and S. aureus, respectively. For example, zinc oxide (ZnO) NPs are capable of inhibiting the growth of S. aureus, while silver NPs demonstrate antimicrobial activity against E. coli [11].

As mentioned above, there are three main mechanisms by which NPs produce apoptosis. One can summarize the entire process as follows: first, the disruption of bacterial cell membrane occurs, followed by (whenever possible) the production of reactive oxygen species (ROS), which induces the penetration of the bacterial cell to disrupt the intracellular mechanism needed by the bacteria to function properly. NPs can produce ROS by different mechanisms, but, in the scientific community, the photocatalytic hypothesis is most widely accepted.

MDR genes have proliferated to such an extent that they become a challenge for the existing resources to counteract them. Accordingly, investigations related to antibacterial materials have become mandatory to protect human lives.

Prior research demonstrated that separately chitosan and TiO2 (anatase polymorph) possess antibacterial properties under ultraviolet light irradiation. This characteristic can clean water sources, which represents one of the main vectors used by bacteria to infect the human body.

Water has become a precious resource, causing the access to fresh and clean water to become a critical matter at a global scale. Nowadays, innovative methods must offer clean, fresh, and purified water. As mentioned above, in this context, chitosan and TiO2 biocomposites could be an economically viable alternative to resolve this problem by removing oils, heavy metals, and pathogen colonies.

2. Bacteria

Because of their incidence in global health, this study centered on two types of bacteria: a Gram-negative and a Gram-positive one. Details of them are provided in the next sections.

2.1 Escherichia coli

Escherichia coli (E. coli) is a Gram-negative, rod-shaped, facultative anaerobic bacterium, as shown in Figure 1. The cell wall consists of an outer membrane with lipopolysaccharide and peptidoglycan along with a plasma membrane. A good analogy is that this type of bacteria bears both an outer and an inner skin that offer double protection against foreign agents. Theodor Escherich first described this microorganism in 1885, making it one of the most studied bacteria in the world. E. coli strains colonized the gastrointestinal tract of humans and animals as a normal flora [12]. Despite this, some strains have evolved into a pathogenic E. coli. This bacterium acquires virulence factors through transposons, bacteriophages, plasmids, and other pathogenicity islands. One can categorize E. coli as a pathogen, according to the pathogenicity mechanisms and clinical symptom serogroups or through virulence factors [12].

Figure 1.

Optical image of E. coli stained using Gram’s method.

There is a variety of foods and environmental sources for the E. coli to grow that are resistant to a breadth of antimicrobial drugs, usually used in medicine and agriculture. Their particular resistance to antibiotics is of great importance, because these are Gram-negative pathogens commonly found in humans. For instance, there are different sources of contamination of vegetables, such as poor water treatment and the presence of fertilizers used during cultivation. Similarly, water or food contaminated with wastes can infect animals. Another vector of contamination is via meat products as a result of improper handling and processing or lack of hygiene [13].

There are numerous serotypes in enterohemorrhagic E. coli (EHEC) that are frequently associated with human diseases such as O26:H11, O91:H21, O111:H8, O157:NM, and O157:H7 [12]. E. coli O157:H7 is the most common isolated serotype of E. coli. It has been frequently isolated from people in the United States, Japan, and the United Kingdom. The E. coli O157:H7 is also a common food-related pathogen leading to major worldwide health problems. This enterohemorrhagic pathogen can cause different clinical symptoms ranging from diarrhea to death.

2.2 Staphylococcus aureus

Staphylococcus aureus (S. aureus) is also a common bacterium in the human body. This Gram-positive bacterium possesses a cell wall bearing only a thick peptidoglycan layer followed by a plasma membrane, as shown in Figure 2. It is present in the mucous membranes (nose) and in the skin [14]; 30% of healthy adults have these bacteria in the nose, and about 30% has it in the skin [15]. These percentages are increased in people who work in hospitals. S. aureus is spread by contact with infected people or by contact with contaminated objects.

Figure 2.

Optical image of S. aureus stained using Gram’s method.

Some common infections caused by S. aureus are:

  • Pneumonia that causes fever, shortness of breath, and cough, causing abscesses in the lungs and accumulation of pus

  • Toxic epidermal necrolysis: infection that causes detachment of large amounts of skin

  • Blood flow infection that produces high and persistent fever and shock

  • Osteomyelitis: infection of the bones that can reach the bone through the bloodstream or can spread through the surrounding tissue

UV radiation can inhibit the bacteria growth. This is commonly used in medicine to sterilize surgical instruments. UV radiation kills the bacterium by disrupting its reproduction mechanism [16].

3. Chitin and chitosan overview

In recent years, the use of biopolymers has increased due to their broader application in cosmetics, pharmaceuticals, food industry, biomedical, agriculture, and environmental products. Chitin was discovered in 1811 by Braconnot and chitosan, in 1859, by Rouget [17]. Chitin is made of N-acetyl-D-glucosamine monomer units linked with β(1,4) glycosidic linkage, whereas chitosan is the deacetylated form of chitin [18]. In addition, chitosan presents a rigid crystalline structure due to inter- and intramolecular hydrogen bonds as a result of the amine and hydroxyl groups [18].

Chitosan is a long chain of hydrophilic polysaccharide with a chemical formula of β(1–4) 2-asetamide-2-deoxy-D-glucopyranose. Chitosan is also known to be a natural polymer with similar molecular structure as cellulose; however it varies in the C-2 chain where the hydroxyl group in cellulose is replaced by amine (NH2). Chitosan is used to inhibit biofouling, being nontoxic and biocompatible, and also possesses inherent antimicrobial properties [19].

Chitin can be extracted from the exoskeletons of crustaceans and fungi by a two-step chemical processing: demineralization and deproteinization [20]. A wide variety of chemical processes allow preparing chitosan: solution casting, dipping and spray coating, compression molding, blending, layer-by-layer, and 3D printing [21].

Chitin along with chitosan is considered the most abundant natural polysaccharides after cellulose. Due to the abundance of waste of shrimps, crabs, and other crustacean exoskeletons, chitin and chitosan are both a cost-effective and abundance product. As polymers, they can be shaped as membranes, films, nanofibers, capsules, tablets, microspheres, pastes, gels, powders, filaments, granules, sponges, and hydrogels. Biomedical uses of chitosan and chitin include drug delivery systems, tissue engineering, and wound healing, as a result of their extensive biocompatibility and biodegradability. For instance, chitosan can be degraded in vertebrates mainly by lysozyme and certain bacterial enzymes in the colon [22]. Moreover, chitosan presents a high in vivo biocompatibility and biodegradability with minimal inflammation and body reaction when applied as tissue [23]. Moreover, the film adhesion on tissue can induce the proliferation of fibroblasts, indicating high biocompatibility [23]. Despite the great biological properties, such as biocompatibility, nonimmunogenicity, antibacterial, and anti-tumorigenicity, there is a lack of sufficient knowledge on the regenerative mechanism of this biopolymer [24]. Another advantage is their functionalization, especially in the hydrophilic group, hydrophobic group, cationic group, targeting ligand, thiol group, and amino acid. This can lead to various gene therapy applications by improving their solubility, toxicity, buffering capacity, escapes in endosome, cellular uptake, genetic material release, transfection efficiency, and silencing efficiency [17]. Chitosan is also known for its anti-inflammatory effects on in vivo tissue applications, which can be applied to inhibit growths of Gram-positive and Gram-negative bacteria. Acting alone, chitosan has shown much promise in wastewater treatment, as it can be used in the removal of dyes, odor, organic pollutants, and inorganic heavy metal ions from industrial wastewater [21]. It can also be applied as an antifouling material used on boat paint because of its prevention on bacteria formation [25]. A problem is that parameters such as molecular weight of chitosan, acetic acid concentration, sterilization process, thickness of the matrix, pH of the medium, and cell parameters (i.e., age, concentration, and bacteria type) led to important differences on microbial growth [18].

4. Titanium dioxide

Titanium dioxide has many commercially available applications in the food industry as a food additive, in the cosmetic industry as a makeup additive and sunscreen, and in the health industry as a drug delivery system [26]. It has also been used as a treatment of wastewater to remove pollutants [27]. Pure titanium dioxide when exposed to ultraviolet light (wavelength less than 400 nm) becomes a photocatalytic material [28]. This is largely dependent on particle size, shape, surface characteristics, and the dioxide crystal structure [29]. Different TiO2 crystal structures (viz., anatase, rutile, and brookite) have different photocatalytic properties [29]. Sayes et al. demonstrated that the anatase polymorph is more reactive under ultraviolet light (UV) [30], which renders it more cytotoxic. Furthermore, Blinova et al. stated that pure anatase induces apoptosis but does not generate ROS, while rutile does initiate cell death through the formation of ROS [31]. Davis et al. proposed that anatase particles under 100 nm have a strong UV absorption [32].

Nevertheless, TiO2 is a proven photocatalytic material under UV light. When this energy is greater than the band gap, i.e., 3.06 eV for rutile and 3.23 eV for anatase [33], the electrons in the valence band (VB) are excited to the conductive band (CB), producing a corresponding hole in the valence band and highly reactive reactants (e and h+) on the TiO2 surface, as shown in Figure 3.

Figure 3.

Schematic illustration for the photocatalytic reaction of TiO2.

The electrons and holes react with water and air to form the highly chemical active ROS. There are four main and common ROS: superoxide radical (O2−), hydroxyl radical (OH), hydrogen peroxide (H2O2), and singlet oxygen (O) [34]. They range from less acute (O2− and H2O2) to more acute (O2− and O) [34]. Not all NPs can produce ROS, and even if they could, many do not produce them all. For example, calcium oxide (CaO) and magnesium oxide (MgO) NPs can only produce O2− [34]. ZnO can generate H2O2 and OH but not O2− [34], while TiO2 and copper oxide (CuO) NPs can produce all four types of ROS [34]. For the sake of simplicity, the present work focuses only on TiO2 irradiated with UV light and is used as a ROS source.

Such ROS production induced by the irradiation of TiO2 with UV light is shown in the following equations. Eq. (1) describes the energy absorption and the photocatalytic reaction. Eqs. (2)(4) depict the photocatalytic redox pathways involved in the generation of an O2− and an OH at the reaction between the holes with H2O and the electrons with O2− [35]. Eqs. (5), (6) describe the generation of H2O2 by reductive and oxidative pathways, respectively.

TiO2+energyeCB+hVB+E1
O2+eCBO2E2
H2O+hVB+OH+H+E3
OH+hVB+OHE4
O2+2H++eCBH2O2E5
2hVB++2H2OH2O2+2H+E6

4.1 Oxidative stress

The ROS formation is an oxidative stress mechanism due to the generation of an imbalance between the production of free radicals and the ability of the cell to counteract. Different bacteria have particular ways to protect themselves to some degree against ROS. However, any overproduction of this species initiates a systematic failure that starts by damaging the cell component and ends with the cell death. Human cells are not exempt from the effect of ROS [36], due to their self-production in the mitochondria.

In bacteria the reactive oxygen species attack the cell membrane and proteins, affecting the interaction between deoxyribonucleic acid (DNA) and cell and increasing the gene expression for oxidative proteins [37]. Several studies found that the expression of two oxidative stress genes (catalase Kat A and alkyl hydroperoxide reductase, Ahp C) and a general stress response gene (chaperon protein, DNA K) rose by 52, 7, and 17 times, respectively, as revealed by real-time polymerase chain reaction (RT-PCR) [38].

Negatively charged O2− and OH can exist on the cell surface and cannot penetrate the intracellular regions of the bacteria because of the negative charge barrier; conversely, hydrogen peroxide [39] can easily pass through. Therefore, NPs that produce all ROS have a higher opportunity as a broad-spectrum biocide. Furthermore, there exists evidence that TiO2 increases the membrane permeability of a bacterial cell, which allows ROS to enter and start the cell death process [40].

5. Methodology

5.1 Materials

For the production of the biocomposite, the following materials were used: chitosan powder (coarse ground flakes, deacetylated chitin, poly(D-glucosamine) CAS number: 9012-76-4), acetic acid (glacial ACS reagent (2.5 L, RABA0010–2.5D1)), and TiO2 (anatase polymorph) purchased from Sigma Aldrich® now Millipore Sigma® (22 nm, nanocrystalline colloidal paste for transparent films, >95% anatase by x-ray diffraction, 60–65% porosity, specific surface area 65–75 m2, pH <1, #798495).

To test the antibacterial properties of this renewable biocomposite, E. coli (ACTC 25922) and S. aureus (ATCC25923), provided by the Biology Department at the University of Puerto Rico—Mayagüez (UPRM), were used. The bacterial medium used to grow them was the Miller’s Luria Broth (LB, CAS number: 91079–40-2, tryptone 10 g/L, yeasts 5 g/L, and sodium chloride 10 g/L), provided by Research Product International (RPI). An in-house Millipore filter provided the necessary deionized water. To provide aseptic conditions and for disinfection, common Lysol® diluted in distilled water was used. The use of protective gear, i.e., face masks, laboratory coats, gloves, and safety glasses, was mandatory throughout the entire experimental work. Laboratories in the UPRM Biology Building and Stéfani Building hosted the present research.

5.2 Chitosan/TiO2 film production

Following the procedure for polymer solution casting, we measured and mixed chitosan powder with acetic acid and deionized water following this schedule: a mechanical agitator for 1.5 h, a sonicator for 1 h, and a magnetic agitator for another 1 h. The TiO2 powder (anatase polymorph) was added in increments of 0.5 wt% to reach each target concentration and to prepare four different mixtures of TiO2 and chitosan. These mixtures were left inside an oven at 55°C for 48 hrs to be then utilized and characterized. Figure 4 shows the as-produced films ready to be tested.

Figure 4.

Films as extracted from the oven. (A) 0.0% TiO2, (B) 0.5% TiO2, (C) 1.0% TiO2, and (D) 1.5% TiO2.

5.3 Bacteria medium preparation for growth curve analysis

In this protocol, we prepared the bacterial medium of Luria broth (LB) nearly 24 h before each experiment. All laboratory glassware was autoclaved for 15 minutes before use. One liter of water was mixed with 10 g of LB assisted by a magnetic agitator. After obtaining a visually homogenous mixture, we divided it in three groups of laboratory plastic tubes, namely, control, E. coli, and S. aureus, and autoclaved a second time for 15 minutes. Each bacteria medium was left overnight inside a fume hood under UV light. Two master solutions were separated from the group, incubated with the bacteria, and left inside a shaker at 200 rpm and 37.0°C for almost 6 h. We followed this entire procedure twice per experiment to produce enough samples to be tested with and without UV.

6. Characterization

6.1 Growth curve analysis

Growth curve analysis (GCA) allowed assessing the effect of the ROS generated from the TiO2 upon UV irradiation. As mentioned, we tested two bacteria: E. coli and S. aureus. We removed the bacterial media from the hood (protocol described previously) and mixed them with the films impregnated with TiO2 in laboratory plastic tubes as shown in Table 1.

Number of laboratory tubes
GroupS. aureusE. coliControlTiO2UV
Day 1333YesYes
333NoYes
Day 2333NoNo
333YesNo

Table 1.

The number of laboratory plastic tubes used and how the groups were organized.

A spectrophotometer allowed measuring the optical density (OD) of each master solution for each bacterium so that one could extract a fixed amount of volume (aliquot) from the solution for each bacterium. This aliquot was then added and mixed to each laboratory plastic tube with the bacteria medium and biocomposite film, as mentioned above. To know exactly how much volume was needed, Eq. [7] was used. Eq. [7] related the volume needed (V2) of aliquot to add to each plastic tube. C1, C2, and V1 are the concentration of the plastic tube, the concentration in the master solution, and volume of medium already in the plastic tube (20 mL), respectively. The concentration was obtained from the OD measurement.

V2=C1V1C2E7

Table 1 presents the three groups formed, i.e., the control group with only the composite films and the medium without bacteria, the group with E. coli and films with bacteria medium, and the group with S. aureus and films with bacteria medium.

After the three groups were ready, we measured the OD after the first 20 minutes three times (20, 40, and 60 minutes) of the mix preparation, then after 40 minutes three times (100, 140, and 180 minutes), and, finally, after an hour five times (240, 300, 360, 420, and 480 minutes).

During the wait time, i.e., between measurements, the test tubes remained inside the shaker under optimal conditions for bacterial growth. It is important to understand that we completed this entire process twice. As UV light irradiated the samples, we covered the shaker with a black box to block any other light source. Figures 5 and 6 show how the films without any UV irradiation affected the bacteria growth.

Figure 5.

S. aureus exposed for 8 h to the chitosan films impregnated with TiO2, without UV irradiation. The upper curves indicate the presence of bacteria, while the bottom ones indicate lower bacteria content.

Figure 6.

E. coli exposed for 8 h to the chitosan films impregnated with TiO2, without UV irradiation. The upper curves indicate the presence of bacteria, while the bottom ones indicate lower bacteria content.

Figures 5 and 6 prove the negligible antibacterial capacity of the films without photoactivation (no UV light). As we can observe in both Figures 5 and 6, the samples with bacteria grow normally (if we compared the sample with only bacteria with the samples of bacteria and films), while the samples without bacteria stay constant (0.0 absorbance) until close to the end of the experiment. The samples are either grouped on the top (samples with bacteria) or in the bottom (samples without bacteria). On the other hand, Figures 7 and 8 (obtained for S. aureus and E. coli, respectively) have shown that the effect of photoactivated films becomes apparent. The growth rate reduction is attributed to the effects of the ROS liberated from TiO2 when exposed to energy from the UV light.

Figure 7.

S. aureus exposed for 8 h to the chitosan films impregnated with TiO2, with UV irradiation.

Figure 8.

E. coli exposed for 8 h to the chitosan films impregnated with TiO2, with UV irradiation.

Figures 7 and 8 display a difference in the bacteria growth on the films photoactivated by UV. Further, Figures 9 and 10 (obtained for S. aureus and E. coli, respectively) evince the difference in growth percent of the bacteria exposed to the films after the growth rate stabilized at the end of the experiment. As observed in these two figures, the celling line corresponds to the normal growth of the bacteria. The bars represent the growth rate of each bacterium exposed to the different concentrations of TiO2 in the films. Figures 11 and 12 show the same bacteria groups exposed to the same level of TiO2 but this time with UV light.

Figure 9.

Growth percent of S. aureus exposed for 8 h to the biocomposite films made of chitosan and TiO2.

Figure 10.

Growth percent of E. coli exposed for 8 h to the biocomposite films made of chitosan and TiO2.

Figure 11.

Growth percentage of S. aureus exposed for 8 h to the biocomposite films made of chitosan and TiO2 with UV light.

Figure 12.

Growth percentage of E. coli exposed for 8 h to the biocomposite films made of chitosan and TiO2 with UV light.

As observed in Figures 9 and 10, the celling line is the normal growth of the bacteria. The bars are the bacteria exposed to the different concentrations of TiO2 in the films. Figures 11 and 12 (obtained for S. aureus and E. coli, respectively) show the same bacteria groups exposed to the same concentration of TiO2 but this time with UV light.

Figures 11 and 12 demonstrate how the exposure of the films to the UV light did affect the bacteria growth. One can say that the UV light alone is detrimental to the bacteria but the experiments with only UV exposure did not affect the growth rate significantly.

6.2 Inhibition ring analysis

This analysis, also known as the Kirby-Bauer (KB) method, helps determine the susceptibility to solutions or drugs of isolated microorganisms, i.e., in our case E. coli and S. aureus. We cut the films as circular pieces using a paper perforator so that all pieces had the same diameter. These were then exposed to UV irradiation for different times. The best results were obtained on films exposed to UV light for 168 h, as shown in Figures 13 and 14. When the UV exposure was over, we placed the films over the bacteria in the Petri dishes. Afterward, the bacteria would grow forming a ring along the chitosan piece with NPs. We measured the area of this ring as a measure of the biocidal potential of the biocomposite. In other words, a larger ring area represented better antibacterial properties of the material.

Figure 13.

Area of inhibition ring for S. aureus after films are exposed for 168 h to UV light. Each bar was a different data point of the same plate taken continuously every 24 h.

Figure 14.

Area of inhibition ring of E. coli after films are exposed for 168 h to UV light. Each bar was a different data point of the same plate taken continuously every 24 h.

Figure 13 shows four groups of S. aureus. Each group was exposed to a different film with different TiO2 concentrations. The horizontal axis corresponds to the time elapsed after the films were placed over the bacteria. Naturally, at 0.00 h there was no inhibition ring yet since the films had just been placed on the bacteria.

Similar to Figure 13, Figure 14 has the bacteria E. coli exposed to different concentrations of TiO2. The very first point after the films were placed was without inhibition rings yet. Here the optimal TiO2 concentration was 1.0% and not 1.5%, which was to be expected due to the double membrane that the E. coli possesses.

6.3 Fourier-transform infrared (FTIR)

The Fourier-transform infrared (FTIR) spectroscopy helps identify functional groups in a molecule. In our case, we used it to identify the chemical bonds present and how they degraded after UV exposure. As it is well-known, UV irradiation degrades the covalent bonds in polymers, rendering them brittle after a prolonged time under UV light.

In that context, FTIR spectroscopy, as a chemical analytical technique, helps measure the infrared intensity as a function of the wavelength (or wave number) of light. Based upon said wave number, infrared light can be categorized as far infrared, mid infrared, and near infrared for use in polymer science, organic synthesis, petrochemical engineering, food analysis, and even pharmaceutical industries [41, 42]. Figures 1518 show the results from four films after the UV exposure. Even more, by using the transmittance percent, we can detect the difference among films before and after such UV exposure.

Figure 15.

FTIR spectrum of the 0.0% TiO2 film after the UV exposure (blue line) for 24 h and without UV exposure (black line).

Figure 16.

FTIR spectrum of the 0.5% TiO2 film after the UV exposure (blue line) for 24 h and without any exposure (black line).

Figure 17.

FTIR spectrum of the 1.0% TiO2 film after the UV exposure (blue line) for 24 h and without any exposure (black line).

Figure 18.

FTIR spectrum of the 1.5% TiO2 film after the UV exposure (blue line) for 24 h and without any exposure (black line).

The characteristic bands of 3400, 3000, 1080, and 1030 cm−1 were assigned to the stretching vibration of O▬H groups, C▬H group, C▬N groups, and C▬O▬C groups, respectively. The band at 1618 cm−1 was attributed to the bending vibration of N-H.

A transmittance increment becomes evident after the UV light exposure on the films according to our results in Figures 1518. The breakdown of the covalent bonds in the polymer reveals the degradation. Each valley is a different bond that when degraded absorbs less energy.

6.4 X-ray diffraction (XRD)

X-ray diffraction (XRD) is a phase identification tool in crystal materials [43]. In the present study, XRD analysis allowed confirming the crystalline nature of the TiO2 used, identifying it as the anatase polymorph. A comparison between two diffraction patterns is in Figure 19. Further, this XRD analysis revealed that during the entire synthesis, process of the films (described in Section 5.2) did not affect the original anatase polymorph of the TiO2. In effect, via Figure 19, we can conclude this because each peak (reflected by specific indexed crystallographic planes) aligns almost perfectly with the anatase pattern. This is an important finding since any formation of the two other polymorphs or even the amorphous alternative would have resulted in a loss of the photocatalytic capacity of the dioxide.

Figure 19.

XRD analysis diffraction of the TiO2 used in the research, compared to pattern of anatase.

6.5 Scanning electron microscopy (SEM)

Scanning electron microscopy (SEM) helped acquire information about the external morphology (texture) of the films [44]. In this research, SEM confirmed the adequate TiO2 dispersion within the chitosan matrix. Figure 20 shows the 0.0% and 0.5% films with two (2) different positions and angle for each sample. Figure 21 reveals analogous information for the films 1.0 and 1.5%. As the amount of NPs increased, the uniformity was maintained.

Figure 20.

SEM images of the films containing 0.0% TiO2 (A, B) and 0.5% TiO2 (C, D).

Figure 21.

SEM images of the films containing 1.0% TiO2 (A, B) and 1.5% TiO2 (D, C).

For each film, multiple shots were taken at different angles and positions within the films. Figures 20 and 21 present the most typical configurations of the particle dispersion. Figure 20 A and B shows the surface of the chitosan without NPs. SEM analysis in overall showed a uniform distribution of TiO2 nanoparticle clots over the chitosan film as no large aggregate was observed. No phase separation was evident, as the TiO2 content increased.

7. Discussion

As a whole, the results in Figures 5 through 12 prove clearly that the biocomposite film made of chitosan and TiO2 NPs can be photoactivated. Once the films containing NPs have produced ROS, they are capable of reducing significantly the amount and growth rate of bacteria. Two different tests (viz., the growth curve analysis and the Kirby-Bauer technique) present incontrovertible evidence that when the bacteria are exposed to the photoactivated biocomposites, their growth pattern is affected, and the end amount is lower. We already mentioned that the reviewed literature proved that the main mechanism affecting the bacteria growth is the production of ROS rendered by the TiO2 upon UV light irradiation. However, in order for these ROS to be effective (in sufficient concentration), the correct polymorph of TiO2 is needed, i.e., anatase. For this reason, we selected this dioxide NPs, seeking to obtain more ROS, as mentioned in Section 4 of this chapter. Nonetheless, it is well-known that different processing conditions (involving temperature) of titanium dioxide can lead to a phase change. Thanks to the XRD characterization, we were able to confirm that the crystal structure used throughout this research was anatase and that the synthesis process of the biocomposite films did not change its crystal structure.

During the said process, the mixing methods used to disperse uniformly the TiO2 NPs in the chitosan could have caused clots and agglomeration of the particles. This was the only reason to use a SEM (secondary imaging mode) to acquire the images shown in Section 6.5. The technique allowed scrutinizing the entire film exposed surface from different angles. This extensive survey did not evince any large clots or even lumps of NPs on the surface of the films. These images also proved that the attachment of the NPs onto the chitosan films was efficacious. In effect, as the TiO2 content increased more, film surface was uniformly covered by the NPs, and no detachment occurred.

To reveal the interaction between TiO2 and chitosan before and after UV irradiation, as already presented in Section 6.3, we acquired a set of FTIR spectra. Due to the addition of oxygen atoms from the TiO2 NPs, one can observe a more intense peak from the O-H bond in Figures 1618. Along that line, as the UV light photoactivated the TiO2, the spectral data revealed a smaller intensity from this bond (O▬H) after the UV irradiation. Finally, the bond nigh 3000 cm−1 (C▬H) indicates a degradation of the chitosan polymer as this peak decreases. This could result in a more brittle substrate to hold the nanoparticles, which should be taken into consideration in upcoming applications of the composite.

In closing, even with the rise of superbugs and the decline in effectiveness of antibiotics, innovated materials like nanoparticles show a promising future as the next generation of antimicrobial. In this context, our chitosan/TiO2 biocomposite films can represent an economic option when compared to other materials for similar applications, such as activated carbon, capable of reducing the bacteria present in water. The synthesis process is reproducible and very economical, creating a technology with ample potential application.

8. Conclusions

This chapter presents an appealing alternative of a novel antibacterial material. The use of chitosan was due to its versatility, its abundance in nature, and excellent biocompatibility and nontoxicity. Through a straightforward technique, TiO2 nanoparticles dispersed onto a chitosan matrix permitted formulating a renewable and biodegradable composite film capable of excellent antibacterial properties when exposed to UV light.

The synthesis process used did not affect the crystal structure of the dioxide, which remains anatase polymorph. X-ray diffraction characterization confirmed such anatase structure.

Chitosan demonstrated to be a very good selection as a matrix able to hold in place the TiO2 nanoparticles. Incorporation of TiO2 nanoparticles onto the chitosan film via solution casting method produced the chitosan/TiO2 biocomposite films. The immobilized TiO2 exhibited good distribution in the chitosan film, as demonstrated via secondary electron microscopy. From those observations, one can infer that chitosan provides an excellent substrate to immobilize TiO2 nanoparticles. Electron microscopy also demonstrated that the nanostructured TiO2 particles dispersed homogeneously within the polymer matrix without obvious aggregation even at the highest TiO2 content, i.e., 1.5% wt.

Under UV light, TiO2 proved effective against E. coli and S. aureus. This is due to the generation of ROS from the UV excitement of the TiO2. The growth curve analysis demonstrated that the growth rate of bacteria was affected, as evidenced by the Kirby-Bauer technique. In the present experimental conditions, the best effect came from biocomposites containing 1.5% wt TiO2.

The irradiation with UV light affected the chitosan covalent bonds, as revealed by the Fourier-transform infrared spectroscopy. From the spectra of chitosan with TiO2, one could infer that more oxygen molecules were present. The degradation of the bond at 3000 cm−1 (C▬H) demonstrated that extensive UV light irradiation is detrimental to the biopolymer, compromising its integrity in actual applications.

The research presented for the synthesis of the films is an effective way to immobilize TiO2 while retaining the structure of the stronger photocatalytic polymorph.

Acknowledgments

This material is based upon work supported by the National Science Foundation under grants No. 0851449 and 1345156 (CREST Program). The authors would like to thank Ms. Barbara Sanchez along with the UPRM Biology Department for the use of their facilities. Professor Matias Cafaro provided insightful comments for the completion of this research.

Conflict of interest

The authors declare no conflict of interest.

Notes/thanks/other declarations

Most of the work completed in the laboratory was with the assistance of the following undergraduate students: Amanda Quintero, Yamalis Lopez, Christian McRobert, Katyria Torres, Kenneth Serrano, Karimar Amador, Ariana Torres, Luis Orta, Genesis Reyes, Luis Olmo, Karla Romero, and Edwin Ramos.

© 2019 The Author(s). Licensee IntechOpen. This chapter is distributed under the terms of the Creative Commons Attribution 3.0 License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited.

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Johnny López Calero, Zuleika Oquendo Berríos and Oscar M. Suarez (February 15th 2019). Biodegradable Chitosan Matrix Composite Reinforced with Titanium Dioxide for Biocidal Applications, Renewable and Sustainable Composites, António B. Pereira and Fábio A. O. Fernandes, IntechOpen, DOI: 10.5772/intechopen.84397. Available from:

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