Skip to main content
International Journal of Nanomedicine logoLink to International Journal of Nanomedicine
. 2015 Nov 4;10:6891–6903. doi: 10.2147/IJN.S91666

Visible-light-responsive ZnCuO nanoparticles: benign photodynamic killers of infectious protozoans

Akhtar Nadhman 1,2,, Samina Nazir 2,, Malik Ihsanullah Khan 1, Attiya Ayub 2,3, Bakhtiar Muhammad 3, Momin Khan 1, Dilawar Farhan Shams 4, Masoom Yasinzai 1,5
PMCID: PMC4639553  PMID: 26604755

Abstract

Human beings suffer from several infectious agents such as viruses, bacteria, and protozoans. Recently, there has been a great interest in developing biocompatible nanostructures to deal with infectious agents. This study investigated benign ZnCuO nanostructures that were visible-light-responsive due to the resident copper in the lattice. The nanostructures were synthesized through a size-controlled hot-injection process, which was adaptable to the surface ligation processes. The nanostructures were then characterized through transmission electron microscopy, X-ray diffraction, diffused reflectance spectroscopy, Rutherford backscattering, and photoluminescence analysis to measure crystallite nature, size, luminescence, composition, and band-gap analyses. Antiprotozoal efficiency of the current nanoparticles revealed the photodynamic killing of Leishmania protozoan, thus acting as efficient metal-based photosensitizers. The crystalline nanoparticles showed good biocompatibility when tested for macrophage toxicity and in hemolysis assays. The study opens a wide avenue for using toxic material in resident nontoxic forms as an effective antiprotozoal treatment.

Keywords: zinc oxide, nanoparticles, doping, photodynamic therapy, Leishmania

Introduction

Researchers and pharmaceutical industries are striving to find alternative treatment options to control outbreaks of infectious diseases caused by pathogens that are resistant to the currently available drugs. Nowadays, it is generally perceived that nanotechnology may change this scenario by introducing new drug delivery systems, and nanomedicines to replace the currently available standard drugs, particularly in situations where parasites and microbes have developed widespread resistance.1,2 Photodynamic therapy (PDT) is a cheap and effective therapy that has been successfully applied for the treatment of topical conditions, such as macular degeneration, skin lesions, cancer,3 and cutaneous leishmaniasis.4 Generally, PDT is a two-step process that involves the delivery of a photosensitizer, followed by its activation with nonthermal light of a specific wavelength to generate reactive oxygen species (ROS). Singlet oxygen moieties are produced frequently in type II reactions of PDT.5 Compared to ground-state oxygen, singlet-state oxygen is highly reactive and very toxic, causing damage to a number of substrates including proteins, nucleic acids (DNA and RNA), lipids, and carbohydrates.6 This highly excited energetic form has received serious consideration because of its physical, chemical, and biological properties. The conversion of ground-state oxygen to this highly activated antiparallel spinning molecule requires overcoming the spin restriction: in the first stage, it has two electrons in the outer shell with a normal spin and in the second stage, it has one electron in an opposite spin and is converted into a highly reactive molecule. Thus, the highly electrophilic characteristic of singlet oxygen and the non-radical nature have increased its capability for stimulating oxidative reactions with macromolecules without the participation of free radicals.7 TiO2 and ZnO are considered potential photosensitizers for PDT due to their unique photo-toxic effect upon irradiation.8,9 The lower cost, nontoxicity, high crystallinity, and being in a similar band to that of TiO2 make ZnO a suitable and cheap alternative.10

A problem that affects the activity of these metal oxides is their large band-gap structure making them UV responsive for electrons-holes generation. Cu and other dopants may enhance the visible light response through reducing the band-gap of such materials.11 Cu doping may help in enhancing the phototoxic activity through dual mode: addition of more electropositive Cu2+ centers can take excited electrons increasing the life-time of holes in valence band of ZnCuO structures. Moreover Cu may induce the visible light sensitivity through narrowing down the conduction band in ZnCuO structures.12

Leishmaniasis caused by Leishmania spp. is a digenetic (heteroxenous) parasitic protozoa of humans and animals.13 The disease occurs in different clinical manifestations, that is, ranging from cutaneous to visceral leishmaniasis. Cutaneous leishmaniasis is caused primarily by Leishmania tropica, and this parasite is different from all others in the Old-World Leishmania complex.14 L. tropica is strictly limited to human beings and the lesions caused by this species may remain for a longer time. The lesions often resemble flattened volcanoes, becoming firmer as they heal and can last for more than 3 years.13

This study focuses on the development of six biocompatible nanoparticles of ZnO doped with different concentrations of Cu (1%, 5%, and 10%, ZnCuO1–ZnCuO3) and 5% N with Cu (1%, 5%, and 10%, ZnCuO4–ZnCuO6, respectively) and their in vitro efficacy against Leishmania parasite. Previously, we had used silver as a dopant15 but it produced a lower ROS, and the half maximal inhibitory concentration (IC50) against Leishmania cells was not efficient as compared to the currently synthesized ZnCuO nanoparticles. In the current study, Cu and Cu–N were selected as dopants as they cause multi-electron reduction of oxygen, which produce a higher quantity of lethal ROS in the immediate environment upon exposure to visible portion of light, and thus were more effective photodynamic killers.

Materials and methods

Ethics

The study was approved by the Research Ethical Committee of Biotechnology Department, Quaid-i-Azam University, Islamabad, Pakistan.

Chemicals and apparatus

Zinc acetate, copper acetate, polyethylene glycol (PEG), ethanol, oleylamine, oleic acid, Ficoll®, Percoll®, trypan blue, sodium azide, mannitol, and penicillin were purchased from Sigma-Aldrich Co. (St Louis, MO, USA); Medium 199 (M199), Roswell Park Memorial Institute (RPMI), sytox green, and 1,3-Diphenylisobenzofuran (DPBF) from Thermo Fisher Scientific (Waltham, MA, USA); fetal bovine serum (FBS) from PAA Laboratories GmbH (Pasching, Austria); streptomycin from Bio Basic Inc. (Markham, ON, Candada); methylene blue and HCl from Merck and Co.

Synthesis

The ZnCuO nanoparticles were synthesized by a modified Masayuki method.16 In a typical reaction, zinc acetate (1 mM), copper acetate (0.01, 0.05, and 0.1 mM corresponding to 1%, 5%, and 10% Cu amount), and oleylamine (5 mM) were added to oleic acid (10 mL) and stirred at 80°C under vacuum for 30 minutes to obtain a clear solution. The solution was heated at 150°C for 60 minutes under nitrogen. The reaction temperature was further raised and kept at 300°C for 1 hour to generate ZnCuO nanostructures. The ZnCuO nanostructures were precipitated by adding ethyl acetate and washed repeatedly with n-hexane and ethanol. Air-dried nanoparticles were annealed in oxygen atmosphere for 6 hours at 600°C to remove oleic acid capping from the synthesized ZnCuO nanostructures. For nitrogen doping, ZnCuO4–ZnCuO6 nanostructures were suspended in 5 mM urea dissolved in 10 mL ethanol and stirred for 3 hours. The resulting suspension was oven dried at 100°C and annealed at 400°C for 4 hours to obtain nitrogen doping in ZnCuO nanostructures. Crystalline ZnCuO1–ZnCuO6 nanoparticles were sonicated in 3 wt% PEG-2000 and incubated for 2 hours to stabilize the nanoparticle surface in biological media toward aggregation. Unbound PEG was removed through centrifugation and washing with ethanol. PEG-bound ZnCuO nanoparticles were air dried for physical characterization.

Characterization of nanostructures

The physical characterization of nanostructures was carried out by transmission electron microscopy, X-ray diffraction analysis, diffused reflectance spectroscopy, and Rutherford backscattering analysis. The crystallite sizes were confirmed through transmission electron microscopy analysis on a JEOL JEM-1010 transmission electron microscope (JEOL, Tokyo, Japan). The crystallite nature of ZnCuO including phases, crystallite structure, and crystalline size was measured on a Shimadzo 6000 X-ray diffraction machine. Analysis was performed using Cu-Kα radiation of λ=1.54 Å at 40 kV and the operating current was set at 30 mA. Diffused reflectance spectroscopy was performed on a LAMBDA 950 PerkinElmer UV/VIS/NIR spectrometer (PerkinElmer Inc., Waltham, MA, USA). Rutherford backscattering was carried out to calculate the percentage composition of nanocrystalline samples. Analysis was executed on a 5UDH-2 Pelletron linear tandem accelerator facility using He2+ beam of energy 2.085 MeV. The incident angle was kept at 0° whereas the backscattering angle was 170°. A solid-state barrier detector was used set at 20 keV resolutions. The data were analyzed via XRUMP 2.0 and SIMNRA 6.06.

Biocompatibility of synthesized nanoparticles

Human macrophages

Human macrophages were isolated by the Ficoll–Gastrografin® method and their biocompatibility was tested and calculated using a previously used method of Nadhman et al.15

Hemolysis assay

Hemolysis assay was carried out by using a modified method of Nederberg et al.17 Briefly, fresh red blood cells (human red blood cells, approved by the review committee of the Biotechnology Department, Quaid-i-Azam University, Islamabad, Pakistan, on February 7, 2014; the subjects also provided informed consent) were washed three to four times with Hank’s buffer salt solution (HBSS). Afterward, 180 μL of red blood cell suspension in HBSS (4% in volume) was placed in 96-well plates and 20 μL of ZnCuO particles were added in different concentrations to each well with one group exposed to sunlight for 15 minutes and another group in dark. Afterward, the plates were incubated for 3 hours at 37°C with 5% CO2. The suspended cells were taken and centrifuged at 1,000× g for 5 minutes. The hemoglobin released was assessed at 576 nm by taking the supernatant in a 96-well plate and read using a microplate reader (BioTek 96-well plate reader; BioTek Instruments Inc., Winooski, VT, USA). The red blood cell suspension in HBSS without nanoparticles was used as a negative control. Triton X-100 (0.1%) was taken as a positive control. The following formula was used to calculate the percentage of hemolysis:

Hemolysis(%)=OD at576nm in the nanoparticle solutionOD at576nm in HBBSOD at576nm in0.1%Triton X-100OD at576nm in HBBS×100 (1)

Dose and time-dependent in vitro anti-leishmanial activity

The L. tropica KWH23 cultures were maintained in M199 supplemented with 10% heat-inactivated FBS, 100 U/mL penicillin, and 100 mg/mL streptomycin at 24°C. The experiments were carried out by our previously used method15 with modifications. Briefly, stock solutions of 1 mg/mL of the different ZnCuO particles were dissolved in deionized water. Leishmania promastigotes were grown in M199 for 7 days at 24°C. The cells (1×106/mL) were suspended in a 96-well microtiter plate. They were then treated with serial concentrations of ZnCuO particles (0.1 ng/mL to 100 μg/mL). The experiments were carried out in four groups. One group each in triplicate was exposed to direct sunlight for 15 minutes, tungsten light (100 W) with an infrared (IR) filter, and dark. The last group containing only L. tropica KWH23 was exposed to direct sunlight without any ZnCuO nanoparticles for the purpose of checking the killing effect of sunlight. The experiments were carried out from mid-September to the end of October, February, and March, respectively, during which time the external temperature was maintained between 22°C and 25°C, favorable for the growth of Leishmania. The external temperature was frequently monitored, and no experiments were performed during cloudy weather. The 96-well plates with clean and clear covered lids were exposed to direct sunlight in all the experiments, and the selected time for such exposure was between 11 am and 12 noon. During this time, the sunlight was located perpendicular against the plates, which is better for more exposure of each well of the 96-well plate. After-ward, the microtiter plates were incubated at 24°C for 3, 12, and 24 hours, respectively, in the dark. The viable cells were counted on neubauer chamber by their motility and also using trypan blue. Their IC50 values were calculated by GraphPad Prism 5 (GraphPad Software, Inc., La Jolla, CA, USA) and also confirmed by SPSS 21 (IBM Corporation, Armonk, NY, USA).

ROS quantification

DPBF solution was prepared by dissolving 0.1 mM DPBF in ethanol. The synthesized nanoparticles were dissolved in a concentration of 10 μg/mL in 2 mL of DPBF solution, taken in sealed quartz cuvette, and exposed to sunlight with an IR filter (400–800 nm) due to the full degradation of DPBF upon exposure to sunlight for 45 seconds. After each 30 seconds, the absorbance was measured by UV 3000 spectrophotometer (O.R.I., Hamburg, Germany) for up to 5 minutes. Methylene blue was used as a standard. Absorbance was measured and corrected for the degradation of DPBF.

For the identification of possible ROS produced, L. tropica KWH23 promastigotes were treated with ZnCuO in two groups and were exposed to sunlight for 15 minutes as in the aforementioned protocol. Sodium azide was added to one group at a concentration of 0.1 mM, and 1 mM mannitol was added to the other group. The cells were incubated at 24°C for 24 hours in the dark. Viable cells were counted by both trypan blue exclusion and motility of Leishmania cells on the neubauer chamber.

Cell internalization studies (inductively coupled plasma atomic emission spectroscopy)

Leishmania cells were taken in 2 mL eppendorf tubes with a higher quantity of Leishmania parasites (2×108 cells/mL)and ZnCuO nanoparticles were added at a concentration of 10 μg/mL. The cells were incubated for 3 hours and after that washed three times with phosphate buffer. The cells were then lyzed by incubating in 1.5 M HCl. Quantification of ZnCuO nanoparticles was carried out by inductively coupled plasma atomic emission spectroscopy (ICP-AES).

Effect on axenic amastigotes and infected macrophages

Axenic amastigotes were cultured in M199 at pH 4.5 and the culture was maintained at 32°C–33°C. The rest of the procedure was the same as previously mentioned in the antileishmanial assay. Human macrophages were cultured in 24-well chamber slides to a cell density of 2×104 cells per well and 24 hours after adhesion and growth on the chamber slides, monolayers with log-phase promastigotes at a range of infection of 1:10 (macrophage/parasite) were infected and incubated at 37°C in 5% CO2 for 5 days. Washing was done until the removal of non-phagocytosed promastigotes, and 0.1 μg/mL of each ZnCuO nanoparticle was administered to each well. One group was exposed to total dark and the other to sunlight for 15 minutes. After 24 hours incubation in dark, chamber slides were fixed and stained with absolute methanol and 4% Giemsa, respectively. The percentage of infected macrophages, as a minimum 100 macrophages per well, was counted and the percent inhibition calculated.

Apoptosis, necrosis, and membrane permeability evaluation

L. tropica KWH23 promastigotes were treated in two groups. One group was exposed to sunlight for 15 minutes and incubated in dark for 24 hours. The second group was incubated in the dark without any exposure to light. Afterward, both the groups were washed with phosphate buffer. The cells were treated with RNAase (1 mg/mL). Both the groups were further divided into two more groups. One of the groups was stained with acridine orange (100 μg/mL) and other group with ethidium bromide (100 μg/mL) mixed with acridine orange (100 μg/mL) in a 3:1 concentration. The increase in fluorescence was checked on a Leica fluorescent microscope with a Canon camera using 485 and 530 nm filters for excitation and emission wavelengths, respectively. Nuclear irregularity was measured by ImageJ software (ImageJ 1.48 free version) using the method of Filippi-Chiela et al.18

To evaluate membrane permeability, the L. tropica KWH23 promastigotes were treated as mentioned earlier and then washed with HBSS. The cells were stained with 1 μM sytox green dye for 15 minutes in dark and then mounted on a slide. The increase in fluorescence was checked on a Leica fluorescent microscope with a Canon camera using 485 and 530 nm filters for excitation and emission wavelengths, respectively. Triton X-100 (0.1%) was used as a control for full permeability.

Temperature measurements of ZnCuO undergoing irradiation

Different concentrations of ZnCuO nanoparticles were added (0.1, 1, and 10 mg/mL) to water, RPMI, and M199 media supplemented with 10% FBS, respectively. No Leishmania cells were added to the media. They were exposed to sunlight for 15 minutes with temperature probe, and the rise in temperature was recorded with Eutech temperature probe at intervals of 1 minute at ambient environment. The control was also exposed to sunlight for 15 minutes without any ZnCuO nanoparticles.

Data processing and statistics

All the experiments were conducted at least three times to confirm their reproducibility and were done each time in triplicate. Statistical analysis was done using SPSS 21 and also with GraphPad Prism 5. The relationship between different parameters was assessed using Pearson’s correlation coefficient (r). Analysis of variance (ANOVA) was used to check significant mean difference with Tukey’s honest significant difference (HSD) for post hoc analysis. Two-way ANOVA was used to determine significant mean and interaction effect, followed by the Holm-Sidak method for multiple pairwise comparisons of the marginal means. P<0.05 and P<0.01 were used to define significant and highly significant results, respectively.

Results and discussion

Characterization of synthesized nanostructures

ZnCuO nanoparticle characterization is provided in the Supplementary material.

Biocompatibility

In the current study, the biocompatibility of the synthesized nanoparticles was carried out on human macrophages because Leishmania attack these cells. Interestingly, ZnCuO particles showed cytotoxic activity at the microgram level against macrophages. Nevertheless, all of the ZnCuO particles showed an improved therapeutic index; lethal concentration, 50% (LC50) for this cell type was a 1,000-fold higher than for Leishmania. This was because of the macrophage capability to cope with ROS as they are produced to act as defensive bullets against pathogens.19 Although, the therapeutic index was higher, it can be elucidated (Figure 1) that increasing the concentration of dopant increased toxicity; for example, the LC50 of non-doped ZnO (ndZnO) was 122±14.52 μg/mL while that of ZnCuO6 was 44±8.90 μg/mL. But according to George et al,20 the cytotoxicity of photocatalytic ndZnO is reduced if its dissolution within culture media is inhibited by doping. However, higher concentrations of dopant might be responsible for the release of dopant ions. In the experiments in dark, the current nanoparticles were found to be toxic at higher concentrations (>200 μg/mL) to these macrophage cells.21

Figure 1.

Figure 1

Biocompatibility of both non-doped ZnO and ZnCuO particles against macrophages.

Notes: Macrophages were treated with synthesized nanoparticles and exposed to sunlight for 15 minutes, then incubated in standard conditions. LC50 and LC90 were calculated by SPSS 21.

Abbreviations: LC50, lethal concentration, 50%; LC90, lethal concentration, 90%.

Furthermore, biocompatibility was also assessed on red blood cells. The cationic agents have major harmful side effects including hemolysis.17 In the current study, different concentrations of the ZnCuO nanoparticles were used to assess the hemolytic activity. Interestingly, after incubation, the ZnCuO nanoparticles have shown little hemolysis at 200 μg/mL, without damaging the membrane of the red blood cells. Moreover, at such concentrations, ZnCuO has successfully damaged the Leishmania surface, as the surface charge of trypanosomatids is highly negative,22 and this might be the reason for the increased uptake of ZnCuO particles by Leishmania (confirmed by ICP-AES), thus increasing the killing and disruption of cell membrane (confirmed by sytox green). However, high concentrations of ZnCuO nanoparticles have shown higher hemolysis (60%–100%) using 500 and 1,000 μg/mL as metal oxides are toxic at higher concentrations.23

Dose and time-dependent in vitro antileishmanial activity

In the current study, the solubility of ndZnO and ZnCuO nanostructures was first tested at different concentrations such as 10, 5, and 1 mg/mL in culture media. It was found that the highest concentrations (10 and 5 mg/mL) of ZnCuO showed some precipitation after 24 hours. The particles were soluble and stable for 36 hours at a concentration of 1 mg/mL in culture media (M199 and RPMI); this is the reason for 1 mg/mL of stock solution being used for these experiments. Leishmania promastigote cells were treated with the serial dilutions of ZnCuO nanoparticles (0.1 ng/mL to 100 μg/mL) in different light conditions, that is, exposing the cells with nanoparticles to direct sunlight, in tungsten light (100 W) with an IR filter and in dark for 15 minutes each. Afterward, the cells were incubated at 24°C for 3, 12, and 24 hours in total dark. The cell killing started from the first hour at 100 and 10 μg/mL of ZnCuO particles. In the first hour, the killing percentage was 20%–25%, while in the second hour, it reached 75%–80% and further to 100% at the third hour after exposure to direct sunlight (Figure 2). Dose-dependent activity of the synthesized nanoparticles showed the IC50 in the μg and ng levels in direct sunlight (Figure 3). In tungsten light with IR filter, 100% killing was achieved after 12 hours at 100 and 10 μg/mL. As for sunlight, the global luminous efficacies (white light proportion) are approximately 105 lm/W for clear skies and for average conditions. Similarly, tungsten light luminous efficiency is approximately 16.7 lm/W (only 2.4% visible region luminosity) for a 100 W bulb.24 Tungsten light is powerful, but a major portion of the emitted radiations from a tungsten source is in the IR region25 and is of little use for the PDT. Therefore, we used the IR filter to filter the IR radiations from a tungsten source. Further, the ZnCuO nanoparticles were activated by the visible region of light as inferred from diffused reflectance spectroscopy and photoluminescence; thus, there was more killing when exposed to direct sunlight than that to tungsten light.

Figure 2.

Figure 2

Time-dependent activity of all the ZnCuO nanoparticles against the promastigotes of Leishmania tropica (mean percent killing of ZnCuO nanoparticles).

Figure 3.

Figure 3

Dose-dependent activity of the synthesized nanoparticles against Leishmania tropica.

Notes: The 96-well plates with transparent, clear, and clean lids were exposed to direct sunlight for 15 minutes with an external temperature of between 22°C and 25°C between 11 am and 12 noon, and afterward incubated in the dark for 24 hours at 24°C.

Abbreviation: nd, non-doped.

Dopants in higher concentration are toxic to cells26 and it was found that there was no killing in dark by the ZnCuO nanoparticles except ZnCuO6 that showed 10% cell killing, which may be the toxicity of a higher dopant concentration. But, in case of other ZnCuO particles, the resident dopant in lattice resulted in decreased toxicity but increased the photo-killing capability of nanoparticles against protozoa.

Based on Figure 4, the best IC50 values were in the order: ZnCuO3>ZnCuO6>ZnCuO5>ZnCuO4>ZnCuO2>ZnCuO1. The bars in Figure 4 represent the confidence intervals of data set, which showed a significant relation (P<0.05) between ZnCuO nanoparticles.

Figure 4.

Figure 4

Statistical comparison of IC50 of ZnCuO particles against Leishmania tropica KWH23 in direct sunlight after 24 hours (bars indicate 95% confidence intervals).

Note: *Indicates no statistical difference at P>0.05.

Abbreviation: IC50, half maximal inhibitory concentration.

However, statistical analysis grouped ZnCuO2 and ZnCuO4 and also ZnCuO5 and ZnCuO6 as having no significant difference (P>0.05 at 95% confidence interval) while both ZnCuO1 and ZnCuO3 were found highly significant (P<0.01 at 95% confidence interval) in comparison with other ZnCuO nanoparticles showing the effect of low and high concentrations of dopant in the ZnO lattice.

ROS quantification and identification

DPBF is a fluorescent dye normally used for the quantification of ROS, especially the singlet oxygen and hydroxyl radicals.27 This dye is sensitive to ROS and rapidly decolorizes. The dye degradation is rate dependent. Furthermore, the dye is also sensitive to sunlight and free oxygen. DPBF was used as a chemical quencher of ROS, and quantification was done using the following equation:

ΦΔZnCuO=ΦMB(kZnCuO/kstandard) (2)

where Φ∆ZnCuO is the quantum yield of semiconductor nanoparticles and Φ∆MB is the quantum yield of methylene blue. The yield from DPBF quenching was more than the normal quencher, ie, methylene blue (quantum yield of 0.52), as in the case of ZnCuO3, the quantum yield was 0.632±0.13. Currently, it was found that the ROS quantum yield by 1% of Cu was 0.24±0.052, while it increased to 0.44±0.1 in the case of 5% of Cu (Figure 5).

Figure 5.

Figure 5

The inverse relation between reactive oxygen species (ROS) and IC50 of ZnCuO particles.

Note: The left side of scale shows the quantum yield of ROS, while the right side scale shows the IC50 of ZnCuO particles against Leishmania promastigotes.

Abbreviation: IC50, half maximal inhibitory concentration.

A highly significant correlation (Pearson’s, r=1) was found among the ROS and IC50, which showed that ROS has an inverse relation with IC50 of nanoparticles (P<0.01), as the more is ROS the less is IC50. ZnO nanoparticles have the capability to produce a lesser amount of ROS28 but having 10% of Cu as impurity in ZnO, it had produced a higher amount of ROS and hence it is required in a lesser quantity to kill the pathogen.

Moreover, to compare the amount of ROS produced by each of the synthesized nanoparticle, a one-way ANOVA was performed, which showed that the effect of nanoparticle type on the production of ROS was significant (P<0.05) (Supplementary material). The pairwise comparison revealed that the difference mainly existed between the nanoparticle used (P<0.05). Meanwhile, the effect with nanoparticle type was present due to a significant difference in ndZnO and ZnCuO nanoparticles to produce ROS (P<0.05). ROS production using ndZnO was significantly lower compared to ZnCuO (P<0.05) as confirmed by the pairwise comparison, portraying the positive effect of dopant in the ZnO lattice.

Essentially, DPBF quenches the singlet oxygen and to some extent the hydroxyl radicals (OH·). In the current study, it was found that ZnCuO nanoparticles produced more of the singlet oxygen. The concentration of these singlet moieties was calculated by introducing quenchers such as sodium azide.29,30 The survival of Leishmania was directly proportional to the scavenging of the particular ROS type. ZnCuO3 was found to produce the maximum amount of singlet oxygen (Figure 6) and it was considered that the significant IC50 value of ZnCuO3 was due to the increase of ROS production especially singlet oxygen.

Figure 6.

Figure 6

Percentage production of reactive oxygen species (ROS) moieties by the ZnCuO nanoparticles using 0.1 mM sodium azide and 1 mM mannitol as singlet oxygen and hydroxyl radical scavengers.

Abbreviation: nd, non-doped.

The production of these moieties started when an equal or high energy light irradiated the nanoparticle surface; it promoted the valence band electrons to the conduction band and produced a hole in the leaving region. Thus, a recombination reaction started producing electron-hole pairs.31 To minimize the recombination reaction, the charge carriers were trapped by the introduction of Cu.32 Thus, it enhanced the photocatalytic activity by producing more ROS due to the surface-to-volume ratio that resulted in more surface oxygen vacancies.33 Moreover, the dopant increased the surface defects, and a space charge layer was formed on the surface, which was beneficial for hindering the combination of photo-induced electron-hole pairs.31,34 But producing excess of hindrance had decreased the ROS yield, for example, in the case of ZnCuO5 and ZnCuO6 particles where the increase in dopant decreased the production of ROS.

The lifetime of singlet oxygen is very short (ie, 3 μs);35 so, it has the capability to react with the available macromolecules such as proteins, lipids, or nucleic acids. Singlet oxygen also has the capability to react with the surrounding water molecules to give rise to further ROS moieties such as hydroxyl radicals, hydroxyl ions, hydrogen peroxide, and superoxide molecules.30 For the hydroxyl radicals, it is also possible that on the surface of nanoparticles, the holes produced in the recombination reaction abstracted electrons from the water molecule through an oxidative process and thus produced hydroxyl radicals.28,36 To compare the total amount of hydroxyl radicals formed by either the recombination reaction on nanoparticle surface or singlet oxygen, a two-way ANOVA was performed. It showed that the effect of the nanoparticle type and singlet oxygen on the production of hydroxyl radical was significant (P<0.05). The hydroxyl radicals produced were 7.8% by ZnCuO3, while 12.6%, 16.6%, 17.8%, 19.4%, and 20.7% were produced by ZnCuO6, ZnCuO2, ZnCuO5, ZnCuO4, and ZnCuO1, respectively particles, respectively. The remaining point percent of ROS were hydroxyl ions and hydrogen peroxide.

Cell internalization studies (ICP-AES)

Delivery of the nanoparticle to the cell is an important aspect of drug delivery. PEG-coated ZnCuO particles have the capability to obtain entry into the cell. In the current study, it was found that PEG containing the ZnCuO nanoparticles were accumulated more inside the Leishmania cells as well as its circulation was also increased.37 The delivery of the nanoparticles was concentration dependent as an increase of dopant increased the entry of ZnCuO particles. In the case of ndZnO, the zinc concentration was 0.98±0.06 μg/mL while that of ZnCuO3 was 1.48±0.28 μg/mL whereas in the control, zinc concentration was 0.023±0.009 μg/mL and the Cu concentration ranged from 0.01 to 0.023 μg/mL while there was no Cu in the control cells (Figure 7). Dopant decreased the dissolution of Zn2+ and thus increased the uptake of Zn.20 Further, the dissolution of these nanoparticles depends on the acidic environment of the lysosomes and calveolar compartments of the cell.38 It is also possible that the cationic nanoparticles enter by electro-migration or electroosmosis in the case of bulk fluid flow across the charged membrane surface.39 Thus, this made these particles more toxic to Leishmania cells.

Figure 7.

Figure 7

ZnCuO nanoparticles internalization in Leishmania cells.

Note: Comparison of Zn (left scale) and Cu (right scale) intake by Leishmania cells (P<0.05).

Abbreviation: nd, non-doped.

Effect on axenic amastigotes and infected macrophages

Axenic amastigote susceptibility was assessed by treating the axenic Leishmania amastigotes with synthesized nanoparticles. In the current study, it was found that the amastigotes were 1–2.5-fold more resistant than the promastigotes. Regarding the infected macrophages, the experiments were carried out in two phases. In the first phase, the experiments were started by incubating the infected macrophages with 0.1 μg/mL of nanoparticles and they were exposed to sunlight for 15 minutes and afterward incubated in dark for 24 hours. The amastigote killing was 55% in the macrophages while the axenic amastigotes were killed 100% at this concentration. In the second phase, the infected macrophage cells were incubated with the nanoparticles and kept in dark for 1–2 hours for the cells to take up the nanoparticles. Afterward, the treated cells were exposed to sunlight for 15 minutes and then incubated in standard conditions. The results were quite remarkable as the amastigote killing reached 100% by all the ZnCuO particles. This increase in amastigote killing was due to the uptake of more ZnCuO molecules, and after exposure to sunlight, it produced more ROS that helped the immune cells to achieve more killing.40 Superior efficacies of the nanoparticles were primarily accredited due to their improved localization in macrophage cells because the PEG coating enhanced the uptake of nanoparticles.41 Furthermore, the negatively charged surface on nanoparticles provided a colloidal dispersion that was helpful to entrap the amastigotes (Figure 8).

Figure 8.

Figure 8

A small cell showing a macrophage infected with amastigotes (purple circles).

Notes: Alteration in nuclear morphology of amastigote occurred in physiological situations and in several processes associated with cell death. These modifications include nuclear condensation and fragmentation observed in apoptosis, decrease in nuclear size, and an increase in nuclear irregularity because of the stress produced by the ZnCuO particles by producing reactive oxygen species (ROS).

Apoptosis, necrosis, and membrane permeability evaluation

Apoptosis is a multistep and complex program cell death pathway, which occurs in every cell.42 Microscopic visualization of staining cells with suitable dye is a primary technique to study the biological mechanisms.43 Upon treatment of Leishmania cells with ZnCuO particles, the cells were treated with apoptotic dye. Acridine orange and ethidium bromide was used for necrosis, as both the dyes attach to nucleic acids in the nucleus upon entry to the cell and emit the respective green and orange colors.44 The Leishmania cells initially started the apoptosis as the chromatin material condensation started with light green nuclei showing early apoptosis in first hour of exposure. The formation of apoptotic bodies by the condensation and fragmentation of cellular bodies, especially in the cytoplasm and nucleus, were the main features of apoptosis (Figure 9).45 The event started by the activation of caspase cascade thus initiated the death receptors that led to the biochemical changes. These changes were initiated by the nucleus shrinkage and condensation of chromatin material, which led to the DNA fragmentation and caused the formation of apoptotic bodies and then to cell death.46 When the cells were exposed for 3 hours or more, ethidium bromide entered the cell indicating the necrosis of cells by emitting an orange color. Upon observation on ImageJ, the cells showed a nuclear irregularity index and many of the Leishmania cells were necrotic and few were apoptotic. In the first hour, more than 90% cells were apoptotic, while in the third hour almost 90% cells were necrotic using 0.1 μg/mL of ZnCuO3.

Figure 9.

Figure 9

Apoptosis and necrosis of Leishmania cells after exposure to ZnCuO3 particles for 1 and 3 hours.

Notes: (A) Bright field image; (B) cell exposure to ZnCuO3 particles at 1 hour; the encircled regions show the formation of apoptotic bodies within the cells with some showing early apoptosis (light green); (C) apoptotic and necrotic cells at 1 hour exposure to ZnCuO3 particles, with 50% of the cells showing necrosis and the remaining show early and late apoptosis; and (D) apoptotic and necrotic cells at 3 hours exposure to ZnCuO3 particles. Almost 90% of the cells show necrosis and the remaining show early and late apoptosis.

For the confirmation of apoptotic dyes to penetrate the membrane, the cell membrane permeability was checked by sytox green dye, which entered the cell upon permeability of cell membrane and attached itself to the nucleic acid and emitted a green fluorescence. Singlet oxygen is lethal to biomembranes, causing oxidation and degradation.47 ZnCuO3-treated Leishmania cells emitted the green fluorescence confirming the permeability of membrane by the ROS produced.

Temperature measurements of ZnCuO undergoing irradiation

These experiments were carried out in water, M199, and RPMI containing 10% FBS, in the absence of Leishmania cells, with different quantities of ndZnO and ZnCuO particles. The results were assessed after each minute by exposing them to direct sunlight. The results showed that increasing the concentration of dopant increased the temperature. The ZnCuO nanoparticles showed a small increase in temperature at 0.1 mg/mL from 0.01°C to 0.057°C (Table 1). The temperature increased from 0.48°C to 0.6°C when 1 mg/mL of each ZnCuO nanoparticles was added in water. However, the temperature increase in M199 and RPMI was in the range of 0.46°C–0.56°C and 0.36°C–0.59°C, respectively. The increase in the temperature was high up to 4.19°C using ZnCuO6 in water, while in RPMI and M199, it was up to 4.10°C and 4.08°C at 10 mg/mL, respectively. Thus, this eliminated the involvement of hyperthermia in the killing of Leishmania cells as the IC50 values were in ng/mL.

Table 1.

Rise in temperature after 15 minutes using different concentrations of ZnCuO nanoparticles and ndZnO nanoparticles

NPs Water
M199
RPMI
0.1 mg/mL (°C) 1 mg/mL (°C) 10 mg/mL (°C) 0.1 mg/mL (°C) 1 mg/mL (°C) 10 mg/mL (°C) 0.1 mg/mL (°C) 1 mg/mL (°C) 10 mg/mL (°C)
ndZnO 0.01±0.002 0.36±0.07 2.7±0.6 0 0.33±0.10 2.4±0.5 0 0.33±0.08 2.3±0.6
ZnCuO1 0.03±0.004 0.48±0.06 2.9±0.8 0.03±0.002 0.40±0.06 3.0±0.7 0 0.36±0.06 3.0±0.7
ZnCuO2 0.037±0.003 0.50±0.05 3.1±0.8 0.031±0.005 0.45±0.06 2.97±0.6 0.021±0.04 0.45±0.065 3.1±0.5
ZnCuO3 0.041±0.006 0.51±0.03 3.1±0.7 0.03±0.005 0.46±0.08 3.06±0.9 0.031±0.06 0.48±0.07 2.79±0.8
ZnCuO4 0.049±0.004 0.53±0.04 3.2±0.7 0.037±0.004 0.50±0.08 3.05±0.9 0.039±0.05 0.51±0.078 3.16±0.4
ZnCuO5 0.056±0.002 0.57±0.03 4.0±0.9 0.043±0.005 0.54±0.07 4.13±1.1 0.045±0.04 0.57±0.09 3.96±0.8
ZnCuO6 0.057±0.006 0.60±0.03 4.19±0.8 0.043±0.007 0.56±0.09 4.08±1.0 0.046±0.06 0.59±0.14 4.10±1

Notes: Nanoparticles were added in water, M199, and RPMI mediums and the rise of temperature was calculated. Data are presented as mean ± standard deviation.

Abbreviations: M199, Medium 199; nd, non-doped; NP, nanoparticle; RPMI, Roswell Park Memorial Institute.

Conclusion

In conclusion, it is elucidated that the ZnCuO nanostructures, especially ZnCuO1 to ZnCuO5, can be used against protozoan diseases such as leishmaniasis because of biocompatibility and better ROS yield. Further, the emission peak existed at 640–690 nm, observed in photoluminescence representing the excitation of the current nanoparticles in visible region, which is very useful for PDT. This visible emission of the ZnCuO nanoparticles will also offer new dimensions to the display materials and their uses in luminescent display. The study showed ZnCuO nanoparticle optimization of dopant for the ROS production and also their use as antileishmanial agents by examining their effects on various cellular parameters of promastigote and amastigote forms. The nanoparticles generated measurable quantities of singlet oxygen. The synthesized particles were found more efficient than conventional molecular PDT agents (based on IC50 values) as they were more effective at lower concentrations to Leishmania parasites. Also, the ZnCuO particles were not toxic to normal cells both in light as well as in dark conditions. The cell-killing ability was only in the presence of visible light by the production of more ROS. These ROS caused oxidative stress, membrane permeability, and induced programmed death of the Leishmania cell. The synthesis of these nanoparticles is highly stable and repeatable. Further investigations are required to elucidate the biocompatibility and biosafety of such particles in vivo.

Acknowledgments

The authors are grateful to Dr Nazma Habib and Professor Akram Shah from the Department of Zoology, University of Peshawar, Pakistan, for providing the strain KWH23 that was acquired in 2010 during Dr Nazma’s PhD program at the London School of Hygiene and Tropical Medicine, London, UK. The authors are also thankful to Dr Turab Ali Abbas (Experimental Physics Laboratory, National Centre for Physics, Islamabad, Pakistan) for providing the Rutherford backscattering analysis facility and the Biosciences Research Center (BRC) (Islamabad, Pakistan) for the fluorescent microscope facility.

Footnotes

Disclosure

The authors report no conflicts of interest in this work.

References

  • 1.Morones JR, Elechiguerra JL, Camacho A, et al. The bactericidal effect of silver nanoparticles. Nanotechnology. 2005;16(10):23–46. doi: 10.1088/0957-4484/16/10/059. [DOI] [PubMed] [Google Scholar]
  • 2.Kim BY, Rutka JT, Chan WC. Nanomedicine. N Engl J Med. 2010;363(25):2434–2443. doi: 10.1056/NEJMra0912273. [DOI] [PubMed] [Google Scholar]
  • 3.Gollnick S, Evans S, Baumann H, et al. Role of cytokines in photodynamic therapy-induced local and systemic inflammation. Br J Cancer. 2003;88(11):1772–1779. doi: 10.1038/sj.bjc.6600864. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 4.Akilov OE, Kosaka S, O’Riordan K, et al. The role of photosensitizer molecular charge and structure on the efficacy of photodynamic therapy against Leishmania parasites. Chem Biol. 2006;13(8):839–847. doi: 10.1016/j.chembiol.2006.06.008. [DOI] [PubMed] [Google Scholar]
  • 5.Agostinis P, Berg K, Cengel KA, et al. Photodynamic therapy of cancer: an update. CA Cancer J Clin. 2011;61(4):250–281. doi: 10.3322/caac.20114. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 6.Brynildsen MP, Winkler JA, Spina CS, MacDonald IC, Collins JJ. Potentiating antibacterial activity by predictably enhancing endogenous microbial ROS production. Nat Biotechnol. 2013;31(2):160–165. doi: 10.1038/nbt.2458. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 7.Agnez-Lima LF, Melo JT, Silva AE, et al. DNA damage by singlet oxygen and cellular protective mechanisms. Mut Res. 2012;751(1):15–28. doi: 10.1016/j.mrrev.2011.12.005. [DOI] [PubMed] [Google Scholar]
  • 8.Zhang S, Yang D, Jing D, et al. Enhanced photodynamic therapy of mixed phase TiO2(B)/anatase nanofibers for killing of HeLa cells. Nano Res. 2014;7(11):1659–1669. [Google Scholar]
  • 9.Arooj S, Nazir S, Nadhman A, et al. Novel ZnO: Ag nanocomposites induce significant oxidative stress in human fibroblast malignant melanoma (Ht144) cells. Beilstein J Nanotechnol. 2015;6(1):570–582. doi: 10.3762/bjnano.6.59. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 10.Hariharan C. Photocatalytic degradation of organic contaminants in water by ZnO nanoparticles: revisited. Applied Catalysis A General. 2006;304:55–61. [Google Scholar]
  • 11.Irie H, Miura S, Kamiya K, Hashimoto K. Efficient visible light-sensitive photocatalysts: Grafting Cu(II) ions onto TiO2 and WO3 photocatalysts. Chem Phys Lett. 2008;457(1–3):202–205. [Google Scholar]
  • 12.Yu H, Irie H, Hashimoto K. Conduction band energy level control of titanium dioxide: toward an efficient visible-light-sensitive photocatalyst. J Am Chem Soc. 2010;132(20):6898–6899. doi: 10.1021/ja101714s. [DOI] [PubMed] [Google Scholar]
  • 13.Jacobson RL. Leishmania tropica (Kinetoplastida: Trypanosomatidae): a perplexing parasite. Folia Parasitol (Praha) 2003;50(4):241–250. doi: 10.14411/fp.2003.042. [DOI] [PubMed] [Google Scholar]
  • 14.Hanafi HA, El-Din el SM, El-Hossary SS, et al. Experimental acquisition, development, and transmission of Leishmania tropica by Phlebotomus duboscqi. Acta Trop. 2013;125(1):37–42. doi: 10.1016/j.actatropica.2012.09.001. [DOI] [PubMed] [Google Scholar]
  • 15.Nadhman A, Nazir S, Khan MI, et al. PEGylated silver doped zinc oxide nanoparticles as novel photosensitizers for photodynamic therapy against Leishmania. Free Radic Biol Med. 2014;77:230–238. doi: 10.1016/j.freeradbiomed.2014.09.005. [DOI] [PubMed] [Google Scholar]
  • 16.Kanehara M, Koike H, Yoshinaga T, Teranishi T. Indium tin oxide nanoparticles with compositionally tunable surface plasmon resonance frequencies in the near-IR region. J Am Chem Soc. 2009;131(49):17736–17737. doi: 10.1021/ja9064415. [DOI] [PubMed] [Google Scholar]
  • 17.Nederberg F, Zhang Y, Tan JP, et al. Biodegradable nanostructures with selective lysis of microbial membranes. Nature Chem. 2011;3(5):409–414. doi: 10.1038/nchem.1012. [DOI] [PubMed] [Google Scholar]
  • 18.Filippi-Chiela EC, Oliveira MM, Jurkovski B, Callegari-Jacques SM, da Silva VD, Lenz G. Nuclear morphometric analysis (NMA): screening of senescence, apoptosis and nuclear irregularities. PLoS One. 2012;7(8):e42522. doi: 10.1371/journal.pone.0042522. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 19.Haidaris C, Bonventre PF. A role for oxygen-dependent mechanisms in killing of Leishmania donovani tissue forms by activated macrophages. J Immunol. 1982;129(2):850–855. [PubMed] [Google Scholar]
  • 20.George S, Pokhrel S, Xia T, et al. Use of a rapid cytotoxicity screening approach to engineer a safer zinc oxide nanoparticle through iron doping. ACS Nano. 2009;4(1):15–29. doi: 10.1021/nn901503q. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 21.Prach M, Stone V, Proudfoot L. Zinc oxide nanoparticles and monocytes: impact of size, charge and solubility on activation status. Toxicol Appl Pharmacol. 2012;266:19–26. doi: 10.1016/j.taap.2012.10.020. [DOI] [PubMed] [Google Scholar]
  • 22.Souto-Padrón T. The surface charge of trypanosomatids. An Acad Bras Cienc. 2002;74(4):649–675. doi: 10.1590/s0001-37652002000400007. [DOI] [PubMed] [Google Scholar]
  • 23.Jeng HA, Swanson J. Toxicity of metal oxide nanoparticles in mammalian cells. J Environ Sci Health A Tox Hazard Subst Environ Eng. 2006;41(12):2699–2711. doi: 10.1080/10934520600966177. [DOI] [PubMed] [Google Scholar]
  • 24.Littlefair PJ. The luminous efficacy of daylight: a review. Lighting Research and Technology. 1985;17(4):162–182. [Google Scholar]
  • 25.MacIsaac D, Kanner G, Anderson G. Basic physics of the incandescent lamp (lightbulb) The Physics Teacher. 1999;37(9):520–525. [Google Scholar]
  • 26.Song L, Connolly M, Fernández-Cruz ML, et al. Species-specific toxicity of copper nanoparticles among mammalian and piscine cell lines. Nanotoxicology. 2014;8(4):383–393. doi: 10.3109/17435390.2013.790997. [DOI] [PubMed] [Google Scholar]
  • 27.Okada Y, Okajima H. Scavenging activity of furan derivatives against hydroxyl radical generated by fenton system. Yakugaku Zasshi. 1998;118(6):226–230. doi: 10.1248/yakushi1947.118.6_226. [DOI] [PubMed] [Google Scholar]
  • 28.Li Y, Zhang W, Niu J, Chen Y. Mechanism of photogenerated reactive oxygen species and correlation with the antibacterial properties of engineered metal-oxide nanoparticles. ACS Nano. 2012;6(6):5164–5173. doi: 10.1021/nn300934k. [DOI] [PubMed] [Google Scholar]
  • 29.Jose GP, Santra S, Mandal SK, Sengupta TK. Singlet oxygen mediated DNA degradation by copper nanoparticles: potential towards cytotoxic effect on cancer cells. J Nanobiotechnol. 2011;9:9. doi: 10.1186/1477-3155-9-9. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 30.Price M, Reiners JJ, Santiago AM, Kessel D. Monitoring singlet oxygen and hydroxyl radical formation with fluorescent probes during photodynamic therapy. Photochem Photobiol. 2009;85(5):1177–1181. doi: 10.1111/j.1751-1097.2009.00555.x. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 31.Mohan R, Krishnamoorthy K, Kim S-J. Enhanced photocatalytic activity of Cu-doped ZnO nanorods. Solid State Commun. 2012;152(5):375–380. [Google Scholar]
  • 32.Wang M, Ren F, Cai G, Liu Y, Shen S, Guo L. Activating ZnO nanorod photoanodes in visible light by Cu ion implantation. Nano Res. 2014;7(3):353–364. [Google Scholar]
  • 33.Xing G, Xing G, Li M, et al. Charge transfer dynamics in Cu-doped ZnO nanowires. Appl Phys Lett. 2011;98(10):102105–102103. [Google Scholar]
  • 34.Huang MH, Wu Y, Feick H, Tran N, Weber E, Yang P. Catalytic growth of zinc oxide nanowires by vapor transport. Adv Mater. 2001;13(2):113–116. [Google Scholar]
  • 35.Hatz S, Lambert JD, Ogilby PR. Measuring the lifetime of singlet oxygen in a single cell: addressing the issue of cell viability. Photochem Photobiol Sci. 2007;6(10):1106–1116. doi: 10.1039/b707313e. [DOI] [PubMed] [Google Scholar]
  • 36.Lin H-F, Liao S-C, Hung S-W. The dc thermal plasma synthesis of ZnO nanoparticles for visible-light photocatalyst. Journal of Photochemistry and Photobiology A: Chemistry. 2005;174(1):82–87. [Google Scholar]
  • 37.Greenwald RB. Poly(ethylene glycol) anticancer drug delivery systems. P R Health Sci J. 2002;21(2):113–121. [PubMed] [Google Scholar]
  • 38.Xia T, Kovochich M, Liong M, et al. Comparison of the mechanism of toxicity of zinc oxide and cerium oxide nanoparticles based on dissolution and oxidative stress properties. ACS Nano. 2008;2(10):2121–2134. doi: 10.1021/nn800511k. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 39.Taveira SF, Lopez RFV. Topical administration of anticancer drugs for skin cancer treatment. In: Porta Caterina AMLa., editor. Skin Cancers – Risk Factors, Prevention and Therapy. Croatia: INTECH Open Access Publisher; 2011. pp. 247–272. [Google Scholar]
  • 40.Allahverdiyev AM, Abamor ES, Bagirova M, et al. Anti-leishmanial effect of silver nanoparticles and their enhanced antiparasitic activity under ultraviolet light. Int J Nanomedicine. 2011;6:2705–2714. doi: 10.2147/IJN.S23883. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 41.Larsen EKU, Nielsen T, Wittenborn T, et al. Accumulation of magnetic iron oxide nanoparticles coated with variably sized polyethylene glycol in murine tumors. Nanoscale. 2012;4(7):2352–2361. doi: 10.1039/c2nr11554a. [DOI] [PubMed] [Google Scholar]
  • 42.Mroz P, Yaroslavsky A, Kharkwal GB, Hamblin MR. Cell death pathways in Photodynamic therapy of cancer. Cancers. 2011;3(2):2516–2539. doi: 10.3390/cancers3022516. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 43.Carpenter AE, Jones TR, Lamprecht MR, et al. CellProfiler: image analysis software for identifying and quantifying cell phenotypes. Genome Biol. 2006;7(10):R100. doi: 10.1186/gb-2006-7-10-r100. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 44.Ribble D, Goldstein NB, Norris DA, Shellman YG. A simple technique for quantifying apoptosis in 96-well plates. BMC Biotechnol. 2005;5(1):12. doi: 10.1186/1472-6750-5-12. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 45.Jimenez-Ruiz A, Alzate JF, MacLeod ET, Luder C, Fasel N, Hurd H. Apoptotic markers in protozoan parasites. Parasit Vectors. 2010;3:104. doi: 10.1186/1756-3305-3-104. [DOI] [PMC free article] [PubMed] [Google Scholar]
  • 46.Savill J, Fadok V. Corpse clearance defines the meaning of cell death. Nature. 2000;407(6805):784–788. doi: 10.1038/35037722. [DOI] [PubMed] [Google Scholar]
  • 47.Bakalova R, Ohba H, Zhelev Z, Ishikawa M, Baba Y. Quantum dots as photosensitizers? Nat Biotechnol. 2004;22(11):1360–1361. doi: 10.1038/nbt1104-1360. [DOI] [PubMed] [Google Scholar]

Articles from International Journal of Nanomedicine are provided here courtesy of Dove Press

RESOURCES