Literature DB >> 35516620

A titanium dioxide/nitrogen-doped graphene quantum dot nanocomposite to mitigate cytotoxicity: synthesis, characterisation, and cell viability evaluation.

Pravena Ramachandran1, Chong Yew Lee2, Ruey-An Doong3, Chern Ein Oon4, Nguyen Thi Kim Thanh5, Hooi Ling Lee1.   

Abstract

Titanium dioxide nanoparticles (TiO2 NPs) have attracted tremendous interest owing to their unique physicochemical properties. However, the cytotoxic effect of TiO2 NPs remains an obstacle for their wide-scale applications, particularly in drug delivery systems and cancer therapies. In this study, the more biocompatible nitrogen-doped graphene quantum dots (N-GQDs) were successfully incorporated onto the surface of the TiO2 NPs resulting in a N-GQDs/TiO2 nanocomposites (NCs). The effects of the nanocomposite on the viability of the breast cancer cell line (MDA-MB-231) was evaluated. The N-GQDs and N-GQDs/TiO2 NCs were synthesised using a one- and two-pot hydrothermal method, respectively while the TiO2 NPs were fabricated using microwave-assisted synthesis in the aqueous phase. The synthesised compounds were characterised using Fourier transform infrared (FTIR) spectroscopy, high-resolution transmission electron microscopy (HRTEM), field emission scanning electron microscopy (FESEM) and UV-visible spectrophotometry. The cell viability of the MDA-MB-231 cell line was determined using a CellTiter 96® AQueous One Solution Cell Proliferation (MTS) assay. The obtained results indicated that a monodispersed solution of N-GQDs with particle size 4.40 ± 1.5 nm emitted intense blue luminescence in aqueous media. The HRTEM images clearly showed that the TiO2 particles (11.46 ± 2.8 nm) are square shaped. Meanwhile, TiO2 particles were located on the 2D graphene nanosheet surface in N-GQDs/TiO2 NCs (9.16 ± 2.4 nm). N-GQDs and N-GQDs/TiO2 NCs were not toxic to the breast cancer cells at 0.1 mg mL-1 and below. At higher concentrations (0.5 and 1 mg mL-1), the nanocomposite was significantly less cytotoxic compared to the pristine TiO2. In conclusion, this nanocomposite with reduced cytotoxicity warrants further exploration as a new TiO2-based nanomaterial for biomedical applications, especially as an anti-cancer strategy. This journal is © The Royal Society of Chemistry.

Entities:  

Year:  2020        PMID: 35516620      PMCID: PMC9054499          DOI: 10.1039/d0ra02907f

Source DB:  PubMed          Journal:  RSC Adv        ISSN: 2046-2069            Impact factor:   4.036


Introduction

With the current growth of the nanotechnology sector, extensive production of engineered NPs and their diverse application in industrial and pharmaceutical fields are rapidly expanding. Among the existing nanoparticles, TiO2 NPs have gained interest because of their physicochemical properties which make them appropriate materials in heterogeneous catalysis, cosmetic products, self-cleaning surfaces, pharmaceutical applications, water splitting and photoelectrochemical conversion.[1] Titanium dioxide (TiO2) resembles the group of transition metal oxides. TiO2 is an n-type semiconductor, has high chemical and physical stability, potent antimicrobial properties, low toxicity, low cost and excellent photocatalytic properties which are related to the electron–hole pair generation process.[2] Therefore, the photoexcited electrons and holes can be utilised to liberate reactive oxygen species (ROS).[3,4] The ROS produced are essential in degrading organic contaminants and germs, and for biomedical applications such as photodynamic and sonodynamic therapy in cancer treatment.[5] Despite the various traits, this metal oxide has also attracted much attention as an active agent since it involves directly in photosimulation in photodynamic application, in contrast with passive nanoparticles such as silica, polyacrylamide, and gold which require conjugation with photosensitive agents.[6,7] Although TiO2 NPs have great prospect in various fields, its application could be limited by the toxicity issue.[8] Generally, TiO2 particles in bulk have been considered biologically inert, while toxicity of nanoscale particles remains unclear.[9] As such, International Agency for Research on Cancer (IARC) has classified TiO2 NPs as a group 2B carcinogen.[10] One of the promising strategies to overcome this toxicity issue is via surface modification by fabricating semiconductor heterojunctions. For example, the materials can be incorporated with additional components including transition metals (Cu, Zn and Fe),[11,12] noble metals (Ag, Pt and Pd)[13,14] and other semiconductors (CdS, CdSe and NiO).[15-17] Most of conventional transition metals, semiconductors and noble metals are unstable or induce toxicity leading to environmental issues and impeding their benefits except Fe metal, since the excited electrons in conduction band is taken up by Fe3+. Thus, it promotes recombination of e−/h+ pair and reduces superoxide that lower the toxicity of TiO2 NPs.[18] Meanwhile, loading with noble metals such as Pt is considered to be more effective due to their anti-cancer activity,[14] but the high cost of the metal restricts their application. Alternatively, the utilisation of nanostructure carbonaceous materials (carbon nanotube, graphene and graphene oxide) to modify TiO2 NPs has created great interest in researchers. Besides having excellent absorption capacity, efficient charge separation properties and have good biocompatibility, N-GQDs inherit unique properties of both graphene and quantum dots.[19] In addition, heteroatom doping (N atom) of GQDs results in high quantum yield, good stability and higher catalytic activity by tuning their electrochemical properties.[20] Moreover, its large surface area-to-volume ratio with delocalised electrons increases drug loading efficiency through their π–π stacking interactions which has been widely used to deliver drug molecules to cells.[21] Furthermore, versatile characteristics and low toxicity of N-GQDs have resulted in wide-scale applications such as electrocatalysis,[22] optoelectronic devices,[23] fluorescent sensors,[24] hydrogen storage,[25] including tissue engineering, biosensing, molecular imaging, drug and gene delivery.[21,26] Various conventional methods such as sol–gel technique,[27] chemical vapour deposition,[28] solvothermal[29] and sonochemical method[30] are applied to synthesise metal TiO2 NPs. Among these methods, hydrothermal is one of the best-performing methods to synthesise mesoporous TiO2. However, this method is generally time-consuming and cumbersome.[31] Microwave heating is an alternative method to produce TiO2 in short time with less energy usage. As compared to traditional heating method, microwave heating is simultaneous, selective and rapid which leads to molecular homogeneity and thus results in greater production efficiency and uniform products with better properties.[32] Although microwave-assisted synthesis efficient, very limited reports are on aqueous phase synthesis have been documented. Recent efforts on fabricating N-GQDs using electrochemical, liquid exfoliation, electron beam lithography, acid exfoliation and solvothermal cutting are not satisfactory owing to complex preparation procedure, time-consuming and require expensive equipment.[33] Hence, in this context, a facile bottom-up hydrothermal method has been considered as a good candidate to prepare N-GQDs. Similarly, TiO2 based N-GQDs nanocomposite is usually prepared via facile physical mixing of TiO2 NPs and N-GQDs followed by hydrothermal route synthesis, meanwhile in this work, a simple and easy two pot hydrothermal method was employed to synthesise this nanocomposite.[34] In this study, N-GQDs and N-GQDs/TiO2 NCs are synthesised using hydrothermal method. Meanwhile, TiO2 NPs are fabricated using microwave-assisted hydrothermal method in aqueous phase. Their potential cytotoxicity was studied using MDA-MB-231 cells as a model cancer cell line.

Experimental

Materials

Citric acid-1-hydrate (Bendosen, Laboratory Chemicals), ethylenediamine (QREC, Grade AR, (Asia) Sdn. Bhd, Malaysia), titanium(iv) tetraisopropoxide, TTIP ≥97% purity (Sigma-Aldrich, Co., USA), hydrochloric acid (HCl, 37%, QREC, Grade AR, (Asia) Sdn. Bhd, Malaysia), purchased pure anatase, ≥99% (Sigma-Aldrich, Co., USA). Dulbecco's modified eagle's medium (DMEM) and penicillin–streptomycin mixed solution (Nacalai Tesque, Japan), fetal bovine serum (FBS) (TICO Europe, Netherlands), phosphate buffered saline (Sigma-Aldrich, Co., Germany), Trypsin–EDTA (GibcoTM, Life Technologies, Canada) and CellTiter 96® AQueous One Solution Cell Proliferation Assay (MTS, Promega, USA) were purchased. All reagents were used as purchased and without further purification.

Synthesis of N-GQDs

The N-GQDs were synthesised via hydrothermal method with citric acid (CA) and ethylenediamine (EDA) used as carbon and nitrogen precursors, respectively. The synthesis was carried out based on the previous study[35] with some modifications. 1 mol of CA and 1 mol of EDA were dissolved in 5 mL of ultrapure water and stirred to form a clear solution. The solution was then transferred into a 20 mL Teflon-lined stainless-steel autoclave followed by hydrothermal treatment at 180 °C for 4 h. The as-received black-brown transparent solution was centrifuged at 5000 rpm for 5 min. Then, the final product was dialyzed in 1 kDa dialysis bag for 24 h to remove the unreacted chemicals and preserved in dark at 4 °C for further use. The stability of the synthesised N-GQDs were studied for the period of two months using UV-vis spectroscopy. The absorbance of the similar concentration sample was taken every 2 weeks once.

Synthesis of TiO2 NPs

The TiO2 NPs were fabricated by adding 2 mL TTIP in 50 mL of distilled water with continuous stirring to form a homogeneous solution. The pH of the solution was adjusted to pH 1.3 by slowly adding 37% hydrochloric acid with constant stirring for 30 min and then transferred to a 100 mL sealed vessel made of high-purity TFM (modified Teflon) placed in a commercial microwave digestion system (Multiwave 3000 Antor Paar, Austria). This equipment was programmed at 600 W of power for 20 min. The resulting precipitate was centrifuged at 8500 rpm for 10 min, followed by several cycles of washing with distilled water and finally dried in an oven at 50 °C. The dried as-obtained powder was further calcined in air at 500 °C for 2 h to obtain TiO2 NPs.

Synthesis of N-GQDs/TiO2 NCs

The N-GQDs/TiO2 NCs were synthesised via two-pot hydrothermal technique. Initially, 3 mL of TTIP was added into 50 mL distilled water under magnetic stirring for 30 min. The solution was then treated by a hydrothermal method in Teflon-lined stainless-steel autoclave (100 mL) at 160 °C for 24 h. After cooling to room temperature, the obtained precipitates were carefully washed with distilled water and centrifuged at a rotation speed of 8500 rpm for 10 min. Then 50 mL of distilled water was added to the sol under magnetic stirring. The entire process was followed using the same procedure used for the synthesis of N-GQDs. Both citric acid and ethylenediamine were added simultaneously to the solution. The solution was further magnetically stirred for 30 min. Following this, the reaction was carried out by heating in a closed hydrothermal system at 180 °C for 4 h. The resulting composites were recovered by centrifugation (15 min, 5000 rpm), washed with distilled water and dried under vacuum oven at 60 °C overnight.

Characterisations

Fourier Transform Infrared (FTIR) spectrum of the as-synthesized sample was recorded by the KBr method on PerkinElmer System 2000 FT-IR in the range of 500–4000 cm−1, ATR method on PerkinElmer FT-NIR Spectrometer Frontier. The morphology and size distribution of the product were determined using field emission scanning electron microscope (FESEM) (Leo Supra 50 VP Field Emission SEM) and HRTEM (FEI Titan Krios FEG at 300 kV). Further optical characterisation was carried out via UV-visible spectroscopy (PerkinElmer Lambda 35) at 200–400 nm of wavelength range to determine the light absorption of synthesised nanomaterials. Dynamic light scattering (DLS) measurements acquired using Malvern Zetasizer Nano ZS to measure hydrodynamic size and zeta potential of the products in cell culture medium with different percentage of FBS.

Cell culture

Human breast epithelial cancer cell line (MDA-MB-231) was obtained from Dr Chern Ein Oon (INFORMM, USM). Cells were cultured in DMEM medium supplemented with 10% FBS and 1% penicillin–streptomycin, incubated at 37 °C with 5% CO2.

Nanoparticle preparation and exposure to cells

The N-GQDs, autoclave TiO2 NPs and N-GQDs/TiO2 NCs were individually suspended in DMEM medium at a concentration of 1.0 mg mL−1. Both TiO2 NPs and N-GQDs/TiO2 NCs were dispersed by sonication for 15 min directly prior to dilution to ensure an even distribution of the nanoparticles without agglomeration. The resulting solutions of TiO2 NPs, N-GQDs/TiO2 NCs and N-GQDs were diluted to different concentrations (0.01, 0.05, 0.1, and 0.5 mg mL−1) before exposure to cells.

Cytotoxicity assay

Cytotoxicity of the synthesised products were assessed using MTS assay following the manufacturer's protocol. Briefly, the cells in 96-well plates (10 000 cells per well) were treated with medium containing various doses of N-GQDs, TiO2 NPs and N-GQDs/TiO2 NCs and incubated for 48 h. After the exposure time completed, MTS solution was added and incubated for 4 h. Then, the plates were placed on a Multiskan Go UV microplate reader (ThermoFisher Scientific, US) and the absorbance of the solution were read 490 nm. The cell viability was calculated according to the following eqn (1):

Statistical analysis

Data are expressed as the mean ± standard deviation (SD). The statistically significant differences of cell viability (p < 0.05) were analysed using ANOVA by GraphPad Prism 5.0 software, California.

Results and discussion

Fourier-transform infrared spectroscopy (FTIR)

The overlay FTIR spectra of N-GQDs, pristine TiO2 NPs, N-GQDs/TiO2 NCs and pure anatase was employed to exhibit characteristics changes in the functional groups and different types chemical bonds in the synthesised nanomaterials, as shown in Fig. 1. As for N-GQDs, a broad absorption band around 3353 cm−1 is due to the stretching vibration of the O–H. The stretching vibration peaks of C–H was at 2943 cm−1 and a vibrational absorption peak found at 1648 cm−1 is corresponded to the CO in the carboxyl group, while the peak at 1531 cm−1 and 1220 cm−1 belongs to the bending vibrations of CC and C–O, respectively.[34] The two peaks at 3103 and 1381 cm−1 can be ascribed to N–H bending vibration and C–N in-plane bending vibration, respectively. The spectrum exhibits successful anchoring of N-functionalization in the lattice of GQDs.[36]
Fig. 1

Overlay of FT-IR spectra for N-GQDs, TiO2 NPs, N-GQDs/TiO2 NCs and anatase TiO2.

Besides, the FT-IR spectra of pristine TiO2 NPs, N-GQDs/TiO2 NCs and pure anatase showed that major broad absorption band between 3300 to 3400 cm−1 and weak vibrational band around 1630 cm−1 ascribed to O–H stretching and bending of H2O molecules, indicating the absorption of water molecules in the samples. The absorbance peaks at 591, 627 and 687 cm−1 correspond to Ti–O–Ti vibrations of pristine TiO2 NPs, N-GQDs/TiO2 NCs and pure anatase TiO2 NPs, respectively.[37] In the case of N-GQDs/TiO2 NCs, the characteristic vibration at 627 cm−1 becomes broader compared with pristine TiO2 NPs and pure anatase. This could be attributed to the combination of Ti–O–Ti and Ti–O–C vibrations.[38] The bond breaking of –OH group in TTIP and the C–O group in N-GQDs during the hydrothermal reaction has resulted in the bond formation of Ti–O–C.[39] Besides, there are stretching vibration peaks of C–H at 2398 cm−1 and C–N vibrations of amine group at 1376 cm−1 for N-GQDs/TiO2 NCs, which confirms the successful incorporation of N-GQDs with TiO2.[40]

UV-visible (UV-vis) spectroscopy

The UV-vis absorption spectrum of N-GQDs, pristine TiO2 NPs, N-GQDs/TiO2 NCs are is shown in Fig. 2. From the UV-vis spectrum of N-GQDs, two typical peaks at 240 nm and 344 nm were observed. The peak at 240 nm is assigned to the π–π* transition of the aromatic sp2 domains, resulting in almost no photoluminescence. Meanwhile, peak at 344 nm corresponds to n–π* transition of CO and C–N in N-substituted aromatic heterocycles, leading to strong photoluminescence emission.[24] Moreover, based on inset of Fig. 2, N-GQDs exhibited excellent stability for the period of two months as the differences in the absorbance was insignificant and consistent with concentration of 0.0348 g mL−1. Besides, as shown in Fig. 2, absorption edge of pristine TiO2 NPs is 434 nm, which indicates the visible region. However, compared with those of the pristine TiO2 NPs, the absorption edge thresholds of the N-GQDs/TiO2 NCs are distinctly red-shifted towards the near infrared (NIR) region (775 nm). The NIR light absorption of TiO2 NPs has been effectively enhanced by the surface modification with N-GQDs.
Fig. 2

Overlay of UV-vis spectra for N-GQDs, TiO2 NPS and N-GQDs/TiO2 NCs.

Size, structure and morphology analysis

High-resolution transmission electron microscope (HRTEM)

The morphology and structure of the N-GQDs were confirmed by HRTEM. The HRTEM image reveals the presence of lattice fringes which correspond to the high crystalline quality of N-GQDs. From low-magnification HRTEM image (Fig. 3a), it can be seen that the N-GQDs consists of 2-D sheets. Based on Fig. 3b, spherical quantum dots are observed which distributed reasonably uniform in size with the diameter 4.40 ± 1.5 nm without apparent agglomeration. The high-magnification images disclosed the crystalline nature of the quantum dots with prominent lattice fringes of 0.346 nm (Fig. 3c), 0.246 nm (Fig. 3d), and 0.216 nm (Fig. 3e), that indicates the basal plane spacing (002), in-plane lattice constant (d = 0.246) and in-plane lattice spacing (100) of graphite, respectively.[41] These lattice parameters were calculated from the Fast Fourier Transform (FFT) image of selected area, as shown in inset of Fig. 3(c, d and e), respectively. It is worth to take note that the obtained basal plane spacing (0.346 nm) is slightly higher as compared with bulk graphite (0.336 nm).[42] This is mainly due the presence of nitrogen doping atoms that enlarged the basal plane distance of N-GQDs. Besides, hexagonal structure of the dots can be observed from the selected area of FFT image (inset of Fig. 3f), further justifies the graphene structure.
Fig. 3

(a–f) HRTEM images of N-GQDs. The insets show FFT image corresponding to the selected area, (g) particle-size distribution of N-GQDs.

HRTEM images of TiO2 NPs (Fig. 4a and b) exhibited that particles irregular square-shaped with an average particle size of 11.46 ± 2.8 nm (inset of Fig. 4a). The interplanar d-spacings calculated from the lattice fringes correspond to the 0.351, 0.233, 0.185, and 0.171 nm plane of anatase TiO2, as depicted in Fig. 4c–e. The rings in the SAED pattern (Fig. 4f) shows the typical diffuse polycrystalline pattern of anatase phase of TiO2 with the main planes identifies in (101), (004), (105) and (200) where the first ring showed well-defined concentric circle and followed by others with similar intensity.[43]
Fig. 4

(a–e) HRTEM images (f) SAED pattern. The insets show FFT image corresponding to the selected area and particle-size distribution of TiO2 NPs.

After the incorporation of N-GQDs in TiO2, a brown coloured powder was obtained and the corresponding HRTEM images as shown in Fig. 5. The HRTEM image (Fig. 5a and b) clearly showed that TiO2 particles were located on the 2D graphene nanosheets surface in a considerably uniform distribution, despite the dark area indicates that some TiO2 NPs were agglomerated on the graphene surface.[44] There were indistinct changes observed in the morphology of TiO2 in the N-GQDs/TiO2 NCs (9.16 ± 2.4 nm) with agglomeration as compared to that of synthesised TiO2 NPs. The lattice spacing of 0.351 nm (Fig. 5c) corresponds to the interplanar separation of (101) plane of TiO2, while the lattice parameter of 0.245 nm (Fig. 5d) is consistent with the in-plane lattice constant of graphene.[41,43]
Fig. 5

(a–d) HRTEM images. The insets show particle-size distribution of N-GQDs/TiO2 NCs.

Field emission scanning electron microscope (FESEM)

FESEM was employed to study the surface morphology of synthesised TiO2 NPs and N-GQDs/TiO2 NCs. Fig. 6 shows the FESEM images of nanoparticles and nanocomposite obtained at higher magnification. It can be observed both the TiO2 NPs were grown with agglomerated spherical morphology due to the higher surface area while –COOH group on the surface of N-GQDs helps to bind TiO2 NPs onto N-GQDs and thus results in less agglomeration. As for N-GQDs/TiO2 NCs, the presence of graphene was not observed wherein the TiO2 NPs could be seen clearly. This might be due to the higher concentration of TiO2 in the nanocomposite and thus the spherical shaped agglomerates completely cover the graphene sheets.[44]
Fig. 6

FESEM images of (a & b) TiO2 NPs and (c & d) N-GQDs/TiO2 NCs.

Possible formation mechanism of N-GQDs

The N-GQDs were synthesised using bottom-up approach which contains ionisation, condensation, polymerisation and carbonisation (graphitisation) as shown in Fig. 7.[45] In this reaction, CA acts as a carbon source while EDA acts as both nitrogen source and catalyst. The reaction was carried out by first ionising the precursors in an aqueous media followed by condensation of CA and EDA to form polymer-like quantum dots. As the reaction temperature evolved from low to high, polymerisation changed into N-doped carbogenic carbon dots, and followed the graphitisation to form N-GQDs. The condensation reaction led to the formation of N atoms bonded with C in five membered-ring structures, referred to as pyrrolic N. With increasing reaction time, pyrrolic N is gradually transformed into graphitic and pyridinic N. Pyridinic N originates from the N atoms that are bonded with C in six membered-ring while graphitic N indicates that N atoms bonded with 3 neighbour C atoms.[4]
Fig. 7

Reaction mechanism of N-GQDs using citric acid and ethylenediamine.

Possible formation mechanism of TiO2 NPs

Generally, there are two stages in the formation of nanocrystals: nucleation and growth (Fig. 8). As for microwave assisted synthesis, the reaction starts with the heating of mixture to the reaction temperature for the specified duration. This assist in the formation of abundant crystal nuclei. As the nucleation process begins, the system developed into growth stage immediately, which leads to the rapid growth of existing clusters, no additional nuclei are formed. Then, the clusters are assembled into aggregated nanocrystalline.[46] The rapid heating rate of microwave-assisted synthesis greatly shorten the overall nucleation and growth processes. In the case of TiO2 NPs, titanium isopropoxide underwent the hydrolysis and condensation processes which occurs upon microwave irradiation. Initially, titanium isopropoxide undergone hydrolysis process in an aqueous media and titanium hydroxides (Ti(OH)4) formed as an intermediate (eqn (2)). Usually, Ti(OH)4 is unstable and thus, condensation process of Ti(OH)4 occurred and formed amorphous hydrous oxide precipitates (TiO2·xH2O) as stated in eqn (3). The TiO2·xH2O precipitates were then calcined at 500 °C (eqn (4)). During the calcination process, water molecules were removed and anatase crystalline TiO2 NPs formed.[47,48] The interaction between microwave power and solvent affects the growth of the particles after the nucleation of initial particles. This is primarily due to the dielectric properties of the solvent which ensure efficient heating and ability of the solvent to convert electromagnetic energy into heat under the microwave field.[49] This heating characteristic is determined by dissipation factor (loss tangent, tan δ). Water has moderate (tan δ = 0.157) microwave absorbing capacity.[50] Thus, microwave power interacts with water to form spherical or square-shaped mesoporous TiO2 NPs aggregates. The homogenous and rapid dielectric heating of microwave results in high degree of crystallisation of the nanoparticles.
Fig. 8

Schematic illustration of the TiO2 aggregates formation process.

Hydrolysis: Condensation: Crystallisation via calcination:

Possible formation mechanism of Ti–O–C bond of N-GQDs/TiO2 NCs

In the formation of Ti–O–C bonds of N-GQDs/TiO2 NCs, the residual carboxylic acid functional group of N-GQDs will bind with surface hydroxyl group of TiO2 NPs during the hydrothermal process.[51] The oxygen and Ti atoms of TiO2 surface were incompletely coordinated and hence, they have partial charge on the surface. Thus, it will attract and bind (chemisorbed) with water molecules in the aqueous solution and moisture in the air. The water molecules then dissociate, leaving a hydroxyl group bound to the surface metal ions known as terminal OH (eqn (5)). Similarly, the electronegative oxygen atom hydrogen bonded to the hydrogen atom of water to form bridge OH (eqn (6)).[52] Upon the addition of N-GQDs precursors, the surface hydroxyl groups of TiO2 will interact with –COOH group on N-GQDs and led to the formation of Ti–O–C bonds and release water molecules as shown in Fig. 9.
Fig. 9

Chemical synthesis process of N-GQDs/TiO2 NCs.

Characterisation of N-GQDs, TiO2 NPs and N-GQDs/TiO2 NCs in cell culture treatment

Hydrodynamic size and zeta potential of NPs and NCs in deionized water (DI water) and culture medium was determined to understand the distribution of nanomaterial cell culture environment and their interaction with biological substrates. Based on Table 1, dispersing these nanomaterials in DMEM without any dispersing agent resulted in slightly higher hydrodynamic size as compared to DI water. This is probably due to high ionic strengths in cell culture medium causes van der Waals forces to dominate whereby leading to bind of particles together.[53] Agglomerated particles often have higher toxicity than well dispersed particles, thus it is not recommended to investigate biological effects of agglomerated NPs.[54] To improve the dispersion of these nanomaterials, FBS as a dispersing agent were employed to medium in different concentration. Upon the addition of FBS, decrease in hydrodynamic size of particles were observed for all the synthesised products. This is due to the formation of a protein corona around the particles following the rapid binding of the serum in the medium to the NPs.[55] This protein corona provides steric hindrance and electrostatic repulsion between particles, thus, resulted in better dispersion.[56,57] Meanwhile, there is a decrease in the hydrodynamic size of particles as the concentration decreases. This effect arises due to the electrical double-layer surrounding charged particles in the medium. As the concentration decreases, the counterion clouds that charge-compensate the charged surface of nanoparticles extend the double-layer interaction to long–range interaction. Thus, electrostatic repulsion dominates to form stable nanoparticle suspension as the van der Waals attraction is relatively weak at long–range interaction.[57] Consistent with these results, the measured zeta potential value for all the synthesised NPs except N-GQDs in DI water indicated positive surface charge while negative surface charge of particles was observed in complete culture medium. The difference the surface charge could be attributed to the formation of negatively charged protein corona on the surface of these synthesised nanomaterials.[12] Meanwhile, the highly water-soluble N-GQDs has negative surface charge in both DI water and complete culture medium, which indicated good stability and anionic in nature. When comparing NPs in medium containing 5% and 1% FBS, insignificant difference in the hydrodynamic size and zeta potential value were observed. Thus, in this study, 1% FBS stabilised medium is used to achieve highly dispersed NPs suspension, which is suitable for cellular penetration based on literature.

Dispersing parameters of N-GQDs, TiO2 NPs, N-GQDs/TiO2 NCs in cell culture medium (mean ± SD, n = 3). The nanomaterials were dispersed in water or medium with or without FBS (5 or 1%, v/v), then sonicated, vortexed and hydrodynamic size and zeta potential were measured

Medium (concentration of nanomaterials)N-GQDsTiO2 NPsN-GQDs/TiO2 NCs
Hydrodynamic diameter (nm)Zeta potential (mV)Hydrodynamic diameter (nm)Zeta potential (mV)Hydrodynamic diameter (nm)Zeta potential (mV)
DI water (1.0 mg mL−1)31.1 ± 6.3−17.2 ± 1.3289.4 ± 4.814.4 ± 2.7253.5 ± 4.816.4 ± 1.7
Medium (1.0 mg mL−1)44.3 ± 5.3−13.7 ± 2.1753.9 ± 5.7−10.7 ± 0.8739.9 ± 3.7−11.2 ± 0.3
Medium + 5% FBS (1.0 mg mL−1)14.8 ± 4.7−31.7 ± 1.588.9 ± 2.5−19.6 ± 1.980.5 ± 5.6−21.1 ± 1.5
Medium + 1% FBS (1.0 mg mL−1)16.7 ± 6.5−25.2 ± 1.893.7 ± 4.3−17.4 ± 1.586.8 ± 4.3−18.9 ± 0.7
Medium + 1% FBS (0.5 mg mL−1)13.8 ± 3.2−27.5 ± 1.056.9 ± 5.1−20.8 ± 0.752.3 ± 5.3−19.7 ± 1.4
Medium + 1% FBS (0.1 mg mL−1)11.8 ± 5.2−30.0 ± 2.751.1 ± 3.3−21.5 ± 1.649.2 ± 4.5−23.2 ± 2.1

In vitro cytotoxicity assessment of N-GQDs, TiO2 NPs and N-GQDs/TiO2 NCs using the MDA-MB-231 breast cancer cell line

The in vitro toxicity assay was assessed using MDA-MB-231 cells at different concentration of N-GQDs, TiO2 NPs and N-GQD/TiO2 NCs (0.01, 0.05, 0.1, 0.5 and 1.0 mg mL−1) for 48 h. Based on Fig. 10a, after 48 h exposure of N-GQDs, the viability decreases slightly, resulting in 83% viable cells at 0.5 mg mL−1 and further decreased to 78% at 1.0 mg mL−1. There was no growth inhibitory effect observed at lower concentrations (0.05–0.1 mg mL−1) after 48 h post treatment. The obtained results corroborate with existing literature which claimed that doping GQDs with heteroatoms such as nitrogen and boron allow higher cell viability because it is biologically safe. Even though there is still no direct comparative toxicity study on GQDs and N-GQDs, generally GQDs demonstrated cell viability above 80% at a much higher administration dose of 200 μg mL−1.[58,59] Meanwhile, HeLa cells was demonstrated to be close to 95% viable even at higher concentration of 2.0 mg mL−1 of boron doped GQDs, suggesting that toxicity not higher than GQDs.[59] Furthermore, the study on cytotoxicity of N-GQDs and graphene oxide (GO) for red blood cells has denoted N-GQDs has lower toxicity than GO. GO induce haemolysis at concentration above 50 μg mL−1, in contrast, N-GQDs did not result in any haemolysis even the concentration of N-GQDs was as high as 200 μg mL−1.[60] Generally, N-GQDs are primarily internalised through cell endocytosis. They have been reported to enter cell membrane by diffusion to enter the nucleus, rendering direct contact with both the genetic materials and proteins in the cell.[61] At higher concentration of N-GQDs, these interactions could distort the morphology of the cytoplasm and nucleus which may alter gene expression, particularly those related to cell death. These results clearly indicated N-GQDs exhibit less toxicity and excellent biocompatibility at lower concentration, and thus it can be utilised in biomedical applications.
Fig. 10

Cell viability of MDA-MB-231 breast cancer cells post treatment with N-GQDs, TiO2 NPs and N-GQDs/TiO2 NCs (a) low concentration and (b) high concentration. Data represented are mean ± SD of two identical experiments made in three replicates. Significant difference as compared to TiO2 NPs **(p < 0.01), ***(p < 0.001).

As shown in Fig. 10b, the cytotoxicity effect was significantly higher in the MDA-MB-231 cells cultured 48 h post treatment. As compared to control group, cells cultured in medium containing 0.5 and 1.0 mg mL−1 TiO2 NPs showed a 28 and 33% decrease in viability respectively following 48 h exposure. As for the lower concentrations of nanoparticles (0.05–0.1 mg mL−1), the differences in cell viability were non-significant when compared to higher concentrations (0.5 and 1.0 mg mL−1). These observations were in good agreement with other reports denoting that pure TiO2 NPs induce low toxicity in different types of human cells.[9,62,63] Specific characteristics of nanoparticles, for example size, crystallinity, composition are regarded as important parameters in determining the toxicity.[13] As the size of the particles approaches nanoscale, the surface area and reactivity increase dramatically which lead to adverse biological effects.[64] As for crystallinity, due to wider absorption gap and smaller electron effective mass of anatase which results in greater generation of ROS than rutile TiO2. The HRTEM of TiO2 NPs reveals the particles were in nanoscopic scale. Apart from that, metallic components of nanoparticles can cause different effects in human body. For instance, cadmium from cadmium selenide (CdSe) is a toxic metal while titanium is non-toxic and harmless metal. TiO2 NPs are insoluble, resulting in low toxicity as compared with soluble nanoparticles (ZnO, Fe2O3 and Ca3(PO4)2) which are highly toxic. For instance, the toxicity of ZnO NPs could be related to release of toxic Zn2+ which can cause cell death through breakdown of the mitochondrial membrane potential.[65] Based on the results in Fig. 10b, N-GQD/TiO2 NCs showed small decrease in cell viability except at the highest concentrations (0.5 and 1.0 mg mL−1) tested after 48 h incubation and thus, inducing low biological effects. The viability trend significantly increased as compared to TiO2 NPs at 0.5 (p < 0.01) and 1.0 mg mL−1 (p < 0.001), since the toxicity level of TiO2 NPs is more prominent as compared with the nanocomposite. This due to the particle size of the TiO2 in the nanocomposite (9.16 ± 2.4 nm) differs slightly as that of synthesised TiO2 NPs (11.46 ± 2.8 nm), since size of the particle is one of the important parameters in inducing toxicity.[66] Besides, the good biocompatibility properties of N-GQDs helps to reduce the toxicity of TiO2 NPs. It can be concluded that surface-modification using N-GQDs has no influence on inducing additional toxicity, besides it helps to lower the toxicity effects of TiO2 NPs.

Conclusions

In this study, N-GQDs and N-GQDs/TiO2 NCs have been successfully synthesised through one and two-pot hydrothermal reaction, respectively, while TiO2 NPs was synthesised using microwave-assisted reaction. Based on HRTEM, the average diameter of spherical-shaped N-GQDs was 4.40 ± 1.5 nm, while TiO2 NPs were irregular square-shaped with 11.46 ± 2.8 nm diameter. Upon incorporating N-GQDs into TiO2 NPs, the size of the particles does not differ dramatically (9.16 ± 2.4 nm) and the TiO2 NPs were located on the 2D graphene nanosheets surface in a considerably uniform distribution. Based on the result presented, the effect of nanoparticles on MDA-MB-231 cells shows a concentration-dependent decrease, and as the dosage of the nanoparticles increases, the cell viability decreases. Moreover, conjugating N-GQDs reduces the toxicity effect of pristine TiO2 NPs while remaining the size of the particles. This approach addresses the toxicity effect of pristine TiO2 NPs without altering its unique properties by remaining the nano-scale size of the particles.

Conflicts of interest

There are no conflicts to declare.
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