Mutation Research/Genetic Toxicology and Environmental Mutagenesis
Genotoxic effects of silver nanoparticles stimulated by oxidative stress in human normal bronchial epithelial (BEAS-2B) cells
Highlights
► Genotoxic potential of Ag-NPs and the role of oxidative stress in BEAS-2B cells. ► Ag-NPs increase DNA breakage and MN formation. ► ROS generated by Ag-NPs stimulate genotoxic effects.
Introduction
Nanomaterials are defined by the U.S. National Nanotechnology Initiative as materials that are 1–100 nm in size in at least one dimension. In recent years, nanotechnology has been involved in the creation and manipulation of materials at nanoscale levels to generate products that exhibit novel properties [1]. In particular, nanoparticles have been proposed for the treatment of many diseases that require a constant drug concentration in the blood or specific drug targeting of cells or organs [2], [3]. With the development of nanotechnology, the size effects of particles have gradually been considered to be important. However, although the novel properties of nanomaterials are impressive from a physicochemical viewpoint, there are concerns about their possible adverse effects on biological systems. Nanoparticles may be more toxic than larger particles of the same substance because of their larger surface area and enhanced chemical reactivity [4]. Moreover, some nanoparticles readily travel throughout the body, deposit in target organs, penetrate cell membranes, lodge in mitochondria, and may trigger injurious responses [5], [6], [7].
Silver (Ag) is a naturally occurring element that has been widely used for thousands of years in applications such as jewellery, utensils, monetary currency, dental alloys, photography, and even explosives [8]. In addition, Ag is widely known as a catalyst, oxidizing methanol to formaldehyde and ethylene to ethylene oxide [9]. Strong growth is projected in the silver nanoparticles (Ag-NPs) market in the coming years [10]. This increasing use of Ag-NPs necessitated a health and environmental risk assessment [10], [11]. In particular, because pulmonary exposure to Ag-NPs occurs during handling of Ag-NPs, it was necessary to evaluate the toxic response in the respiratory tract. The results of 90-day inhalation studies with Ag-NPs indicated that lungs and liver are the major target tissues for Ag-NPs accumulation [12], [13]. It was recently reported that exposure of human lung epithelial cells to metal-containing nanoparticles generated reactive oxygen species (ROS), which can lead to oxidative stress and cellular damage [14]. Barillet et al. [15] reported that silicon carbide nanoparticles induced genotoxicity and oxidative stress in A549 lung epithelial cells. In addition, Kim et al. [16] reported that Ag-NPs induced oxidative stress-dependent toxicity in human liver cells. However, there is no report on the genotoxic effects of Ag-NPs or the role of oxidative stress in these effects in normal lung epithelial cells. Therefore, we examined the genotoxic potential of Ag-NPs and the role of oxidative stress in their effects in a human normal bronchial epithelial (BEAS-2B) cell line.
We purchased Ag nanopowder (<100 nm) and completely dispersed them in experimental medium by sonication. After this process, the Ag-NPs solution was filtrated using a membrane filter; the Ag-NPs were then physically characterized. First, prior to their genotoxic evaluation, the uptake of Ag-NPs was characterized along with their effects on cellular adhesion and their surface distribution. Second, in order to evaluate the genotoxic potential of Ag-NPs in human pulmonary exposure, cultured human lung cells (BEAS-2B cells) were used in the comet assay and the in vitro micronucleus (MN) assay. Third, we identified the genetic toxicity related to ROS generation by Ag-NPs. To measure ROS generation, an oxidative stress assay of intracellular oxidation of 2′,7′-dichlorofluorescein-diacetate (DCFH-DA) was performed [1], [17]. In addition, specific bacterial enzymes, formamidopyrimidine DNA glycosylase (FPG) and endonuclease III (Endo III), were used to measure oxidized purine and oxidized pyrimidine in the modified comet assay (Comet assay interest group website; http://cometassay.com/). To determine whether the genotoxic effect of Ag-NPs was stimulated by ROS, BEAS-2B cells were co-treated with both Ag-NPs (10 μg/ml) and scavengers [mannitol (Man), OH radical scavenger; catalase (CAT) and sodium selenite (SS), H2O2 radical scavengers; superoxide dismutase (SOD), superoxide radical scavenger] in the comet assay and the cytokinesis-block MN (CBMN) assay.
Section snippets
Ag-NPs preparation
Ag-NPs (Sigma–Aldrich, St. Louis, MO, USA) were homogenously dispersed in bronchial-epithelial growth medium (BEGM; Clonetics Corp., Walkersville, MD, USA) by sonication for 30 min (Bioruptor UCD-200T, Cosmobio Corp., Japan), and filtered through a cellulose membrane (pore size 200 nm, Advantec, Toyo Toshi Kaisha, Japan). Ag-NPs were serially diluted to 0.01, 0.1, 1, and 10 μg/ml and incubated with the BEAS-2B cell line.
Characterization of Ag-NPs
The size and shape of Ag-NPs were characterized by using a scanning electron
Characterization and intracellular localization of Ag-NPs
In genotoxicity studies, Ag-NPs were characterized by SEM, TEM, and DLS, which showed spherical aggregates that were about 58.9 nm in size (Fig. 1). In SEM and TEM analysis, the single particle size of Ag-NPs was 100 nm or less (Fig. 1A and B), while the size distribution of Ag-NPs by DLS ranged from 43 to 260 nm (Fig. 1C). As shown in Fig. 2B and C, they existed as aggregates wrapped with an endocytic vesicle within the cytoplasm and nucleus of BEAS-2B cells that were treated with Ag-NPs for 24 h.
The genotoxicity of Ag-NPs in BEAS-2B cells
Discussion
There are no standardized testing methods for the genotoxicity of nanoparticles [24], [25]. In the review by Landsiedel et al. [25], the comet assay and MN assay were more sensitive and frequently used to confirm the genotoxicity of nanoparticles than the well-known Ames test in bacterial systems. The Ames tests on nanoparticles (e.g., TiO2, ZnO, SWCNT) were predominantly negative, possibly due to penetration problems of the nanoparticles through the bacterial cell wall [25]. Therefore,
Conflict of interest statement
None.
Acknowledgments
This study was supported by the Eco-Technopia-21 project of the Korea Ministry of the Environment and the National Research Foundation of Korea Grant funded by the Korean Government (MEST).
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S.M. Oh and K.H. Chung contributed equally.