Literature DB >> 24673907

Genotoxicity of titanium dioxide nanoparticles.

Tao Chen1, Jian Yan2, Yan Li2.   

Abstract

Titanium dioxide nanoparticles (TiO(2)-NPs, <100 nm) are increasingly being used in pharmaceuticals and cosmetics due to the unique properties derived from their small sizes. However, their large surface-area to mass ratio and high redox potential may negatively impact human health and the environment. TiO(2)-NPs can cause inflammation, pulmonary damage, fibrosis, and lung tumors and they are possibly carcinogenic to humans. Because cancer is a disease involving mutation, there are a large number of studies on the genotoxicity of TiO(2)-NPs. In this article, we review the results that have been reported in the literature, with a focus on data generated from the standard genotoxicity assays. The data include genotoxicity results from the Ames test, in vitro and in vivo Comet assay, in vitro and in vivo micronucleus assay, sister chromatid exchange assay, mammalian cell hypoxanthine-guanine phosphoribosyl transferase gene assay, the wing somatic mutation and recombination assay, and the mouse phosphatidylinositol glycan, class A gene assay. Inconsistent results have been found in these assays, with both positive and negative responses being reported. The in vitro systems for assessing the genotoxicity of TiO(2)-NPs have generated a greater number of positive results than the in vivo systems, and tests for DNA and chromosome damage have produced more positive results than the assays measuring gene mutation. Nearly all tests for measuring the mutagenicity of TiO(2)-NPs were negative. The current data indicate that the genotoxicity of TiO(2)-NPs is mediated mainly through the generation of oxidative stress in cells.
Copyright © 2014. Published by Elsevier B.V.

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Keywords:  Ames test; Carcinogenicity; Class A gene; Comet; Genotoxicity; Hypoxanthine-guanine phosphoribosyl transferase gene; Micronucleus; Phosphatidylinositol glycan; Sister chromatid exchange; Titanium dioxide nanoparticles; Wing point mutation

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Year:  2014        PMID: 24673907      PMCID: PMC9359145          DOI: 10.1016/j.jfda.2014.01.008

Source DB:  PubMed          Journal:  J Food Drug Anal            Impact factor:   6.157


1. Introduction

Titanium dioxide (TiO2) is the naturally occurring oxide of titanium. It has several different crystalline structures. Rutile is the most common natural form of TiO2, whereas anatase and brookite are two more rare polymorphs. TiO2 has been used widely in pigments, accounting for 70% of the total production volume of pigments worldwide. It provides whiteness and opacity to products such as paints, plastics, papers, inks, foods, and toothpastes. It can also be found in pharmaceuticals and cosmetic products such as sunblock [1] due to its photocatalytic, biocidal, and/or antiproliferative properties [2]. Until recently, the use had been limited to coarse and fine (both diameters > 100 nm) TiO2 particles. Coarse and fine particles of TiO2 have been investigated and declared biologically inert in humans and animals [3,4]. More recently, TiO2 nanoparticles (TiO2-NPs, <100 nm) have increasingly been used in pharmaceuticals and cosmetics due to the unique properties derived from their small sizes [5,6]. These new applications of TiO2-NPs, however, call into question their biological inertness. TiO2-NPs have a large surface-area to mass ratio [7] and a high redox potential, which can cause undesirable effects on human health and the environment. Recent studies have revealed that exposure to TiO2-NPs can cause inflammation, pulmonary damage, fibrosis, and lung tumors in rodents [7-9]. TiO2-NPs are possibly carcinogenic to humans (Group 2B) based on sufficient evidence in experimental animals and inadequate evidence from epidemiology studies, according to a report from the International Agency for Research on Cancer [10]. The National Institute for Occupational Safety and Health (NIOSH) [11] also concluded that TiO2-NPs were a potential occupational carcinogen, acting through a secondary genotoxicity mechanism primarily related to particle size and surface area. Genotoxicity data are important for nanotechnology regulation and risk assessment. Recently, the genotoxicity of TiO2-NPs has been intensively studied due to their carcinogenicity. Although a large number of reports on the genotoxicity of TiO2-NPs and its underlying mechanisms have been published, there has been no review article specific to the genotoxicity of TiO2-NPs. The purpose of this review is to present up-to-date knowledge regarding the genotoxicity of TiO2-NPs, with a focus on results from standard genotoxicity assays.

2. In vitro studies

Results on genotoxicity studies on TiO2-NPs were identified through Medline database searches. The data from the studies using the standard genotoxicity assays including the Ames test, Comet assay, micronucleus assay, sister chromatid exchange (SCE) assay, andmammalian cell gene mutation assay, are summarized in Table 1.
Table 1

In vitro studies on genotoxicity of titanium dioxide nanoparticles.

Size and crystalline structureDoseTest systemResultAuthor and Reference
Ames test
23 nm; 84% anatase and 16% rutile1–100 μg/mLA modified fluctuation test procedure for the Ames testPositiveJomini et al, 2012 [14]
5.7 nm; 86% anatase and 14% brookite1–100 μg/mLA modified fluctuation test procedure for the Ames testPositiveJomini et al, 2012 [14]
23 nm; 84% anatase and 16% rutile1–100 μg/mLFluctuation Ames testNegativeJomini et al, 2012 [14]
5.7 nm; 86% anatase and 14% brookite1–100 μg/mLFluctuation Ames testNegativeJomini et al, 2012 [14]
10 × 50 nm; rutile in T-LiteUp to 5 mg/plateAmes testNegativeLandsiedel et al, 2010 [15]
10 nm; anatase5 mg/plateAmes testNegativeWoodruff et al, 2012 [16]
Comet assay
<25 nm; anatase50 μg/mL and 100 μg/mLBottlenose dolphin leukocytesPositiveBernardeschi et al, 2010 [17]
21 nm; 80%/20% anatase/rutile150 mg/mLAGS human gastric epithelial cell linePositiveBotelho et al, 2013 [18]
2.3 nm100 μg/mLWith or without Fpg and End III in Human peripheral blood lymphocytes and cultured human embryonic kidney cells (HEK293)PositiveDemir et al, 2013a [19]
50 nm25 μg/mLHuman lymphocytesPositiveGhosh et al, 2013 [21]
14 nm; anatase50 μg/mLSyrian hamster embryo cellsPositiveGuichard et al, 2012 [22]
25 nm; 80%/20% anatase/rutile10 μg/mL, 25 μg/mL, and 50 μg/mLSyrian hamster embryo cellsPositiveGuichard et al, 2012 [22]
5.9 nm; anatase100 mg/mLChinese hamster lung fibroblast cellsPositiveHamzeh and Sunahara, 2013 [23]
34.1 nm; 83% anatase and 17% rutile100 mg/mLChinese hamster lung fibroblast cellsPositiveHamzeh and Sunahara, 2013 [23]
1.5 nm; rutile100 mg/mLChinese hamster lung fibroblast cellsPositiveHamzeh and Sunahara, 2013 [23]
Varying sizes 12–140 nm; anatase or rutile100 μg/mLA549 human lung carcinoma cellsPositiveJugan et al, 2012 [24]
7 nm anatase or 10 nm rutile0.5–256 μg/mLHuman hepatoblastoma C3A cellsPositiveKermanizadeh et al, 2012 [25]
27.5 nm; 86% anatase/14% rutile20–100 μg/mLHuman bronchial epithelial cellPositivePrasad et al, 2013 [26]
30 nm20 μg/mLHuman amnion epithelial (WISH) cellsPositiveSaquib et al, 2012 [27]
10 nm; anatase0.8–80 μg/mLHuman epidermal cells (A431)PositiveShukla et al, 2011 [29]
30–70 nm1–80 μg/mLHepG2 cellsPositiveShukla et al, 2013 [28]
<100 nm3μM, 5 μM, and 10 μMHuman peripheral blood lymphocytesPositiveTurkez 2011 [30]
25 nm anatase; 25 nm 80% anatase and 20% rutile80 μg/mL, 120 μg/mL, and 150 μg/mLHuman SHSY5Y neuronal cellsPositiveValdiglesias et al, 2013 [31]
<100 nm anataseUp to 50 μg/cm2Human lung fibroblasts and human bronchial fibroblastsNegativeBhattacharya et al, 2009 [32]
62 nm; rutileUp to 50 μg/mLSyrian hamster embryo cellsNegativeGuichard et al, 2012 [22]
15–30 nm; anatase20–200 μg/mLHuman peripheral blood lymphocytesNegativeHackenberg et al, 2011 [33]
1–10 nm; polyacrylate-coated100 mg/mLChinese hamster lung fibroblast cellsNegativeHamzeh and Sunahara, 2013 [23]
10 × 50 nm; rutile in T-LiteUp to 600 μg/mL for 4 h exposure and up to 150 μg/mL for 24 h exposureV79 cellsNegativeLandsiedel et al, 2010 [15]
10 nm; anataseUp to 40 μg/mLChinese hamster ovary cells (CHO-K1)NegativeWang et al, 2011 [34]
10 nm; anataseUp to 200 μg/mLTK6 human lymphocytesNegativeWoodruff et al, 2012 [16]
Micronucleus assay
20 nm0.5 μg/mL and 1 μg/mLChinese hamster ovary cellsPositiveDi Virgilio et al, 2010 [35]
27.5 nm; 86% anatase/14% rutile20–100 μg/mLHuman bronchial epithelial cellPositivePrasad et al, 2013 [26]
≤20 nm1.0 μg/cm2Syrian hamster embryo cellsPositiveRahman et al, 2002 [36]
30–70 nm1–80 μg/mLHepG2 cellsPositiveShukla et al, 2013 [28]
10 nm; anatase0.8–80 μg/mLHuman epidermal cells (A431)PositiveShukla et al, 2011 [29]
<25 nm10 and 50 μg/mLHuman lung cancer cells (A549)PositiveSrivastava et al, 2011 [37]; Srivastava et al, 2013 [38]
21 nm; anatase;5–125 μg/mLHuman lymphocytesPositiveTavares et al, 2013 [39]
22 nm; hydrophobic rutile5–125 μg/mLHuman lymphocytesPositiveTavares et al, 2013 [39]
19 nm; hydrophilic rutile5–125 μg/mLHuman lymphocytesPositiveTavares et al, 2013 [39]
<100 nm3 μM, 5 μM, and 10 μMHuman peripheral blood lymphocytesPositiveTurkez, 2008 [30]; Turkez, 2011 [51]
25 nm; anatase80 μg/mL, 120 μg/mL, and 150 μg/mLHuman SHSY5Y neuronal cellsPositiveValdiglesias et al, 2013 [31]
25 nm; 80% anatase and 20% rutile80 μg/mL, 120 μg/mL, and 150 μg/mLHuman SHSY5Y neuronal cellsPositiveValdiglesias et al, 2013 [31]
25 nm; 80% anatase and 20% rutileUp to 50 μg/mLSyrian hamster embryo cellsNegativeGuichard et al, 2012 [22]
14 nm; anataseUp to 50 μg/mLSyrian hamster embryo cellsNegativeGuichard et al, 2012 [22]
62 nm; rutileUp to 50 μg/mLSyrian hamster embryo cellsNegativeGuichard et al, 2012 [22]
20 nm; 85% anatase and 15% rutileUp to 250 μg/mLHuman lymphocytesNegativeTavares et al, 2013 [39]
Sister chromatid exchange assay
20 nm1–5 μg/mLChinese hamster ovary cellsPositiveDi Virgilio et al, 2010 [35]
<100 nm3μM, 5 μM and 10μMHuman peripheral blood lymphocytesPositiveTurkez, 2008 [30]; Turkez, 2011 [51]
Hprt mutation assay
10 nm; anataseUp to 40 μg/mLHprt mutation assay in Chinese hamster ovary cells (CHO-K1)NegativeWang et al, 2011 [34]

2.1. Ames test

The Ames test is formally called the Salmonella typhimurium reversion assay. This test is used worldwide as an initial screen to determine the mutagenic potential of agents and the assay identifies point mutagens [12,13]. Four different types of TiO2-NPs have been evaluated by the Ames assay and all of them were negative in the standard mutation assay. However, two showed positive responses when evaluated with a modified fluctuation test procedure (Table 1). Jomini et al [14] used the standard fluctuation test and a modified fluctuation test procedure with the S. typhimurium strains TA97, TA98, TA100, and TA102 to measure the mutagenic potential of two types of TiO2-NPs. The test was negative when the normal assay was used. However, when they applied a simple pre-exposure of bacteria to the NPs in a low ionic strength solution (NaCl, 10 mM) at a pH below the nanoparticles isoelectric points (pH 5.5), the results were positive. They concluded that a simple pre-exposure step in a low ionic-strength solution, at a pH below the nanoparticle isoelectric points (NaCl, 10 mM, pH 5.5) could increase bacterial uptake of the nanoparticles and improve the accuracy of the test. In another two tests, TiO2-NPs were negative in different Salmonella strains. Landsiedel et al [15] evaluated several TiO2-NPs used for sunscreen products using Ames test. S. typhimurium TA1535, TA100, TA1537, TA98, and TA102 were treated with the NPs at 20–5000 μg/plate both with or without metabolic activation. No mutagenicity was found. In the other study, the bacteria were preincubated with eight different concentrations of 10 nm anatase TiO2-NPs up to 5000 μg/plate. No mutation induction was found. Analyses with transmission electron microscopy and energy-dispersive X-ray spectroscopy show that the TiO2-NPs are not able to enter the bacterial cells [16].

2.2. Comet assay

The Comet assay is a method for measuring DNA strand breaks in eukaryotic cells. The Comet assay is also called the single-cell gel electrophoresis assay due to its working principle. After treatment, single cell suspensions are embedded in agarose on a microscope slide and lysed. Electrophoresis at high pH results in structures resembling comets when observed by fluorescence microscopy. The intensity of the comet tail relative to the head is proportional to the number of DNA breaks. For detecting oxidative DNA damage, cells embedded in agarose on microscope slides can be further treated with nucleases such as formamidopyrimidine DNA-glycosylase (Fpg), endonuclease III (Endo III), and 8-hydroxyguanine DNA-glycosylase to generate secondary DNA breaks at the sites with oxidative DNA adducts. The Comet assay has been widely used to assess genotoxicity of nanomaterials due to its sensitivity and simplicity. The results from in vitro Comet assays on TiO2-NPs are summarized in Table 1. Among 24 Comet assay tests, 17 of them showed positive responses to treatments of different types of TiO2-NPs (Table 1). Bottlenose dolphin leukocytes were treated with smaller than 25 nm anatase TiO2-NPs and the Comet assay was performed to measure the genotoxicity of the NPs. The results showed that the NPs were genotoxic for the cells after exposure to concentrations of 50 μg/mL and 100 μg/mL for 24 hours and 48 hours, respectively [17]. AGS human gastric epithelial cells treated with 21 nm TiO2-NPs caused DNA damage. The tail intensity increased 1.88-fold in 150 mg/mL of TiO2-NPs treated cells compared to the control cells [18]. Human peripheral blood lymphocytes and cultured human embryonic kidney (HEK293) cells were treated with 1 μg/mL, 10 μg/mL, and 100 μg/mL of 2.3 nm TiO2-NPs and the DNA breaks were measured using the Comet assay with or without the Fpg and Endo III enzymes. The 100 μg/mL of TiO2-NPs significantly increase the DNA damage with or without the Fpg and Endo III enzymes in both the cell lines [19]. The Comet assays were conducted using human bronchial epithelial BEAS 2B cells to evaluate genotoxicity of <25 nm uncoated anatase TiO2-NPs and 10 × 40 nm SiO2-coated rutile TiO2-NPs. The results showed that both the two types of TiO2-NPs induced DNA breaks [20]. DNA fragmentation was induced by TiO2-NPs in human lymphocytes at a concentration of 25 μg/mL [21]. Guichard et al [22] compared genotoxicity of nanosized and non-nanosized anatase and rutile TiO2 particles in Syrian hamster embryo (SHE) cells. Although TiO2-NPs in both forms induced higher cytotoxicity than their bulk counterparts after 72 hours of exposure, the anatase NPs induced similar levels of DNA damage in the Comet assay after 24 hours of exposure as the bulk particles. Chinese hamster lung fibroblast cells were treated with 100 mg/mL of 5.9 nm anatase, 34.1 nm 83% anatase and 17% rutile mixture, and 1.5 nm rutile TiO2-NPs, respectively. DNA double strand breaks were measured using the Comet assay. All types of the NPs were positive in the test [23]. Jugan et al [24] evaluated genotoxicity of varying sizes of NPs in A549 human lung carcinoma cells and found that they were genotoxic when assayed with the Comet assay. Following 4 hours’ exposure of the human hepatoblastoma C3A cells to sublethal levels of the TiO2-NPs, DNA damage measured by the Comet assay was significantly induced [25]. Prasad et al [26] evaluated effects of TiO2-NP agglomeration on their genotoxicity using three different nanoparticle-treatment media. They found that TiO2-NPs induced similar amounts of DNA damage measured by the Comet assay in all three media, independent of the amount of agglomeration, cellular interaction, or cell-cycle changes [26]. Human amnion epithelial (WISH) cells were exposed to varying concentrations of 30 nm TiO2-NPs for 6 hours. The comet results exhibited a significant induction of DNA damage at 20 μg/mL of the particles [27]. TiO2-NPs (30–70 nm) induced significant oxidative DNA damage in HepG2 cells measured with the Fpg-Comet assay even at 1 μg/mL [28]. Human epidermal cells (A431) were treated with 50 nm anatase TiO2-NPs at doses 0.008–80 μg/mL. The treatment resulted in a significant DNA damage in the cells [29]. Human peripheral blood lymphocytes were treated with 3 μM, 5 μM, and 10 μM TiO2-NPs (<100 nm). DNA damage measured using the Comet assay was increased by the treatment and addition of ascorbic acid prevented the induction [30]. Two types of TiO2-NPs, 25-nm anatase and 25 nm with 80% anatase and 20% rutile, were used for the treatment of human SHSY5Y neuronal cells. The Comet assay was conducted after treatment for 3 hours or 6 hours of the two types of particles. Positive results were obtained for both types of NP [31]. Seven out of 24 Comet assay tests gave negative responses to TiO2-NPs (Table 1). TiO2-NPs (anatase, <100 nm) did not induce DNA-breakage measured by the Comet assay in human lung fibroblasts and human bronchial fibroblasts [32]. Guichard et al [22] found that 60-nm rutile TiO2-NPs did not increase DNA damage after 24 hours of exposure to SHE cells at concentrations up to 50 μg/mL. Human peripheral blood lymphocytes from 10 male donors were exposed to 15–30 nm anatase TiO2-NPs at concentrations 20 μg/mL, 50 μg/mL, 100 μg/mL, and 200 μg/mL for 24 hours. Although the NPs were detected in the cytoplasm and nucleus of the lymphocytes, they did not induce genotoxicity in the cells measured with the Comet assay [33]. Landsiedel et al [15] treated V79 cells with 10 nm × 50 nm rutile TiO2-NPs at concentrations up to 600 μg/mL for 4 hours and up to 150 μg/mL for 24 hours’ exposure in T-Lite and measured the DNA damage with the Comet assay. The result was negative for the test. Chinese hamster lung fibroblast cells were treated with 1–10 nm polyacrylate-coated TiO2-NPs and the Comet assay was performed. The NPs were negative in the test [23]. Chinese hamster ovary cells (CHO–K1) were exposed to < 25 nm anatase TiO2-NPs at concentrations 0 μg/mL, 10 μg/mL, 20 μg/ mL, or 40 μg/mL for 60 days. Immediately after the treatment, the alkaline Comet assay was performed and the result was negative [34]. The genotoxicity of 10 nm anatase TiO2-NPs was assessed with the Comet assay. TK6 cells were treated with 0–200 μg/mL TiO2-NPs for 24 hours. Although the TK6 cells did take up the particles, no significant induction of DNA breakage or oxidative DNA damage was observed in the treated cells using the standard alkaline assay or the EndoIII and 8-hydroxyguanine DNA-glycosylase-modified assay [16].

2.3. Micronucleus assay

The micronucleus test measures damage to the chromosomes and mitotic apparatus of cells. An increase in the frequency of micronucleated cells is an indication of induced chromosome damage. Studies on 16 types of TiO2-NPs using the micronucleus assay are summarized in Table 1. Twelve of them were positive in the test, and four were negative. Genotoxic effects of 20 nm TiO2-NPs were evaluated using Chinese hamster ovary (CHO-K1) cells. Micronucleus frequencies were significantly increased by 0.5 μg/mL and 1 μg/mL of the NPs [35]. Human bronchial epithelial BEAS 2B cells were treated with smaller than 25 nm uncoated anatase TiO2-NPs and 10 nm × 40 nm SiO2-coated rutile TiO2-NPs, respectively. Although the uncoated TiO2-NPs increased the micronucleus frequency, the SiO2-coated NPs did not [20]. Guichard et al [22] found that none of the TiO2-NPs or TiO2 bulk particles showed significant induction of micronuclei formation after 24 hours’ exposure of these particles to SHE cells. Prasad et al [26] found that TiO2-NPs induced micronuclei only in a medium that facilitated the lowest amount of agglomeration, the greatest amount of NP-cellular interaction, and the highest population of cells accumulating in S phase. The genotoxic potential of ≤20 nm TiO2-NPs was assessed in SHE cells. The cells were treated with 1.0 μg/cm2 of the particles for 12 hours, 24 hours, 48 hours, 66 hours, and 72 hours. The micronucleus frequencies were increased by the treatment in a time-dependent manner [36]. HepG2 cells were treated with low doses of 30–70 nm TiO2-NPs and a significant increase in the micronucleus frequency was observed in the treated cells [28]. Human epidermal cells (A431) were treated with 50 nm anatase TiO2-NPs at doses of 0.008–80 μg/mL. The treatment resulted in significant chromosome alteration at doses 0.8–80 μg/mL [29]. Human lung cancer cells, A549, were treated with 10 μg/mL and 50 μg/mL of TiO2-NPs for 24 hours. Micronucleus assay was conducted to determine the genotoxicity of the particles and there was a positive response in the micronucleus induction for both of the treatment concentrations [37,38]. Tavares et al [39] evaluated genotoxicity of different types of TiO2-NPs using in vitro micronucleus assay in human lymphocytes. They found that 21 nm anatase TiO2-NPs at 125 μg/mL dose, 22 nm hydrophobic rutile TiO2-NPs at 5 μg/mL and 45 μg/mL doses, and 19 nm hydrophilic rutile TiO2-NPs at 15 μg/mL and 45 μg/mL doses significantly increased the frequencies of micronucleated binucleated cells except for 20 nm uncoated 15% rutile and 85% anatase TiO2-NPs. Human peripheral blood lymphocytes were treated with 3 μM, 5 μM, and 10 μMTiO2-NPs (<100 nm). A positive response of TiO2-NPs in micronucleus assay was found and the addition of ascorbic acid decreased the micronucleus induction [30]. Human SHSY5Y neuronal cells were treated with 25 nm anatase TiO2-NPs and 25 nm TiO2-NPs with 80% anatase and 20% rutile. Results from the micronucleus test showed that both types of the TiO2-NPs induced a dose-dependent micronucleus formation after 6 hours’ exposure [31].

2.4. SCE assay

The SCE assay is a short-term test for the detection of reciprocal exchanges of DNA between two sister chromatids of a duplicating chromosome. A positive response of this assay indicates certain types of chromosome damage. Only two studies on SCE analysis of TiO2-NPs have been reported (Table 1). Genotoxic effects of 20 nm TiO2-NPs were evaluated by conducting SCE assay in Chinese hamster ovary (CHO–K1) cells. SCE frequencies were significantly increased by 1–5 μg/ mL of the TiO2-NPs [35]. In the second study, human peripheral blood lymphocytes were treated with 3 μM, 5 μM, and 10 μM TiO2-NPs (<100 nm). The SCE assay was conducted and the genotoxicity of the NPs tested was positive. Addition of ascorbic acid resulted in decreasing the SCE frequencies [30].

2.5. Mammalian cell mutation assay

The in vitro mammalian cell mutation assays detect gene mutations induced by test agents. The most commonly-used genes for measurement of mutations are the thymidine kinase and hypoxanthine-guanine phosphoribosyl transferase (Hprt) genes. The mutation tests detect different spectra of mutational events. Only one in vitro mammalian cells mutation study was found (Table 1). The Hprt gene mutation assay was conducted on chronically exposed cells for 60 days to 0–40 μg/mL < 25 nm anatase TiO2-NPs. The results showed no mutation induction [34].

3. In vivo studies

The in vivo genotoxicity of TiO2-NPs has been investigated in several studies (Table 2) using the in vivo Comet assay, micronucleus assay, wing somatic mutation and recombination assay, and phosphatidylinositol glycan, class A gene (Piga) mutation assay.
Table 2

In vivo studies on genotoxicity of titanium dioxide nanoparticles.

Size and crystalline structureDoseTest systemResultReference
In vivo Comet assay
33 nm40–1000 mg/kgCBAB6F1 mice were gavaged daily for 7 d, and their bone marrow, liver and brain were assayedPositive in bone marrow and liver; negative in brainSycheva et al, 2011 [40]
21 nm; 75% anatase and 25% rutile500 mg/kgMice were exposed via drinking water for 5 d, and their blood cells were used for the assayPositiveTrouiller et al, 2009 [41]
80 nm; 74% anatase and 26% brookiteUp to 28.5 mg/m3Rats were exposed via inhalation for 5 d, 4 h/d and their lung cells were assayedNegativeLindberg et al, 2012 [42]
10 × 50 nm; rutile in T-Lite10 mg/kgRats were exposed by inhalation, and their lung cells were assayedNegativeLandsiedel et al, 2010 [15]
5 nm; anataseUp to 5 mg/kgIntratracheally exposure to male Sprague–Dawley rats, and the lung cells was assayedNegativeNaya et al, 2012 [43]
Micronucleus assay
21 nm; 75% anatase and 25% rutile500 mg/kgMice were exposed via drinking water for 5 d. The mouse blood cells were testedPositiveTrouiller et al, 2009 [41]
80 nm; 74% anatase and 26% brookiteUp to 28.5 mg/m3Rats were exposed via inhalation for 5 d, 4 h/d. The peripheral blood polychromatic erythrocytes were testedNegativeLindberg et al, 2012 [42]
10 nm; anataseThree daily dose of 50 mg/kgIntravenously exposure to male B6C3F1 mice; the blood cells was assayedNegativeSadiq et al, 2012 [44]
40 nm; anataseUp to 1387 mg/kgOne dose intravenous injection to mice, and the blood cells were assayedNegativeXu et al, 2013 [45]
Mutation assay
2.3 nm; anataseFed, 0.1–10 mMDrosophila melanogaster, the wing somatic mutation and recombination assayNegativeDemir et al, 2013b [46]
10 nm; anataseThree daily dose of 50 mg/kgIntravenously exposure to male B6C3F1 mice and Pig-a mutation assay in blood cells was conductedNegativeSadiq et al, 2012 [44]

3.1. The in vivo Comet assay

Five studies have been performed using the in vivo Comet assay in different tissues. Two showed positive responses to TiO2-NP treatment. CBAB6F1 mice were treated via gavage with 33 nm TiO2-NPs at doses of 40 mg/kg, 200 mg/kg, and 1000 mg/kg body weight, daily for 7 days. Genotoxic effects in brain, liver, and bone marrow were evaluated by the Comet assay. The NPs induced DNA damage in bone marrow and liver, but not in the brain [40]. In the other positive comet study, mice were treated through drinking water containing a 21-nm mixture of 75% anatase and 25% rutile TiO2-NPs and DNA damage measured by the Comet assay in the blood cells. DNA strand breaks were significantly increased by 500 mg/kg TiO2-NPs [41]. In the first negative study, rats were exposed by inhalation with T-Lite SF containing 79–89% TiO2-NP (10 nm × 50 nm rutile) and T-Lite Max containing 69–73% TiO2-NPs, used as UV protecting agents in sunscreens, and genotoxicity of the particles were investigated in the lung by the in vivo Comet assay. No DNA damage was found in the lung [15]. C57BL/6J mice were treated with freshly generated TiO2-NPs (74% anatase, 26% brookite at approximately 80 nm in size) for 5 days, 4 hours/day by inhalation at doses of 0.8 mg/m3, 7.2 mg/m3, and 28.5 mg/m3. DNA damage was assessed by the Comet assay in lung epithelial alveolar type II and Clara cells sampled immediately following the exposure. Although a dose-dependent deposition of Ti in lung tissue was seen, no significant effect was observed on the level of DNA damage in lung epithelial cells [42]. The genotoxicity of 5 nm anatase TiO2-NPs was evaluated using the Comet assay after a single or repeated intratracheal instillation at doses of 1.0 mg/kg or 5.0 mg/kg body weight or 0.2 mg/kg or 1.0 mg/kg body weight once a week for 5 weeks. The lung cells were used for the assay and there was no increase in % tail DNA in any of the treatment groups [43].

3.2. The in vivo micronucleus assay

Four in vivo micronucleus tests of TiO2-NPs have been reported: one was positive and three of them were negative. C57BL/6J mice were treated with NPs and micronuclei were analyzed in peripheral blood polychromatic erythrocytes (PCEs) collected 48 hours after the last exposure. No significant effect on micronucleated PCEs was observed [42]. In vivo micronucleus assay was conducted to evaluate the genotoxicity of 10 nm TiO2 anatase NPs in mice. B6C3F1 mice were treated intravenously for 3 consecutive days with 0.5 mg/kg, 5.0 mg/kg, and 50 mg/kg TiO2-NPs. The mouse blood was assayed and no induction of micronuclei was found although the NPs reached the bone marrow and induced cytotoxicity [44]. Finally, there was no induction of micronuclei in the PCE of mice 14 days after a single intravenous injection of different doses of 40 nm anatase TiO2-NPs [45].

3.3. In vivo mutation assay

Two studies have been reported on the mutagenicity of TiO2-NPs in vivo and both of them had negative results. Drosophila melanogaster third instar larvae were fed with the medium containing 0.1–10 mM TiO2-NPs and the SMART assay was conducted. The results showed no significant increases in the frequency of all measured spots, indicating that these NPs were not able to induce mutations or recombination [46]. The Pig-a mutation assay was performed at different sampling times after mice were treated with different doses of 10 nm anatase TiO2-NPs. The NPs did not increase mutant frequency in the gene at any time point or dose [44].

4. Mechanisms underlying the genotoxicity of TiO2-NPs

4.1. Oxidative stress

A number of studies suggest that TiO2-NPs induce toxicity via oxidative stress due to their relatively large surface area and greater reactive activity than bulk TiO2 particles. Jugan et al [24] found that TiO2-NPs caused an early intracellular accumulation of reactive oxygen species (ROS) and that addition of glutathione significantly reduced the ROS, suggesting that this molecular antioxidant detoxified ROS overproduction caused by TiO2-NPs. Evidence for the induction of oxidative damage to DNA was also gained from the measurement of the level of 8-oxo-7,8-dihydro-2′-deoxyguanosine [24]. TiO2-NPs induced a significant reduction in mitochondrial dehydrogenase activity in human lymphocytes, resulting in the generation of ROS and an alteration of mitochondrial membrane potential [21]. Bhattacharya et al [32] showed that TiO2-NPs were able to generate free radicals and induce indirect genotoxicity mainly by DNA-adduct formation. However, Jugan et al [24] reported that if experiments were processed in the dark to avoid any photocatalytic effects on TiO2-NPs, ROS accumulation decreased, suggesting that TiO2-NPs generated ROS in cells via photocatalysis.

4.2. Size, structure, and agglomeration effects

Smaller TiO2-NPs were more genotoxic than larger TiO2-NPs, regardless of their crystalline phases. It is likely that the smaller the NPs are, the easier for them to enter cells and accumulate inside the cells, both in the cytoplasm and the nucleus [47]. Some studies show that anatase NPs induce more deleterious effects than rutile NPs because of the photocatalytic properties of anatase TiO2. TiO2-NPs forming large agglomerates induced DNA damage in different cell lines, whereas NPs that formed smaller agglomerates (200 nm) had no effect on genotoxicity [48].

4.3. Effects on DNA repair, proliferation, and apoptosis

Evidence indicates that TiO2-NPs can impair cellular DNA repair, by inactivation of both the NER and BER pathways. The inactivation could result from structural modification of NER and BER proteins by oxidation caused by TiO2-NPs induced ROS accumulation. Protein oxidation/reduction has been regarded as a critical mechanism for the modulation of repair pathway. Botelho et al [18] reported that 21 nm TiO2-NPs increased oxidative stress and cell proliferation, and decreased apoptosis in the AGS human gastric epithelial cell line. Huang et al [49] showed that short-term exposure to TiO2-NPs enhanced cell proliferation, survival, ERK signaling activation, and ROS production in cultured fibroblasts whereas long-term exposure to TiO2-NPs not only increased cell survival and growth but also increased the numbers of multinucleated cells and micronuclei. Their results suggest that long-term exposure to TiO2-NPs disturbs cell cycle progression and genome segregation, leading to chromosomal instability and cell transformation.

5. Conclusions

As with many other nanomaterials, controversial results have been reported on the genotoxicity of TiO2-NPs. A large number of tests on TiO2-NPs have been conducted and many have detected positive responses. However, there remain clear inconsistencies in the reported results. The conflicting results reported from different studies could have arisen from inconsistencies in characteristics of the test materials, such as size, shape, and crystalline structure. The different results may also have been a function of the different test systems and different genotoxicity endpoints that have been employed. Generally, in vitro systems for assessing genotoxicity of TiO2-NPs generated more positive results than the in vivo systems, whereas DNA and chromosome damage tests generated more positive results than the assays measuring gene mutations. Nearly all tests for the mutagenicity of TiO2-NPs were negative, except for a few studies using the Ames test, which has been suggested to be unsuitable for detecting the genotoxicity of nanoparticles [50]. The available evidence indicates that TiO2-NPs induce genotoxicity mainly via generating oxidative stress in cells. The ROS generation is dependent on the size, structure, and aggregation of the TiO2-NPs. The oxidative stress produced by the NPs could affect DNA repair, cell cycle progression, cell proliferation, and apoptosis by affecting protein structure.
  49 in total

1.  Impact of agglomeration and different dispersions of titanium dioxide nanoparticles on the human related in vitro cytotoxicity and genotoxicity.

Authors:  Zuzana Magdolenova; Dagmar Bilaničová; Giulio Pojana; Lise M Fjellsbø; Alexandra Hudecova; Katarina Hasplova; Antonio Marcomini; Maria Dusinska
Journal:  J Environ Monit       Date:  2012-01-25

2.  Determination of TiO2, ZrO2, and Al2O3 nanoparticles on genotoxic responses in human peripheral blood lymphocytes and cultured embyronic kidney cells.

Authors:  Eşref Demir; Durmuş Burgucu; Fatma Turna; Sezgin Aksakal; Bülent Kaya
Journal:  J Toxicol Environ Health A       Date:  2013

3.  In vitro toxicity of respirable-size particles of diatomaceous earth and crystalline silica compared with asbestos and titanium dioxide.

Authors:  G A Hart; T W Hesterberg
Journal:  J Occup Environ Med       Date:  1998-01       Impact factor: 2.162

4.  Cytotoxicity and genotoxicity of nanosized and microsized titanium dioxide and iron oxide particles in Syrian hamster embryo cells.

Authors:  Yves Guichard; Julien Schmit; Christian Darne; Laurent Gaté; Michèle Goutet; Davy Rousset; Olivier Rastoix; Richard Wrobel; Olivier Witschger; Aurélie Martin; Vanessa Fierro; Stéphane Binet
Journal:  Ann Occup Hyg       Date:  2012-03-26

5.  Modifications of the bacterial reverse mutation test reveals mutagenicity of TiO(2) nanoparticles and byproducts from a sunscreen TiO(2)-based nanocomposite.

Authors:  Stéphane Jomini; Jérôme Labille; Pascale Bauda; Christophe Pagnout
Journal:  Toxicol Lett       Date:  2012-09-28       Impact factor: 4.372

6.  Investigation of genotoxic and cytotoxic effects of micro- and nanosized titanium dioxide in six organs of mice in vivo.

Authors:  Lyudmila P Sycheva; Vjacheslav S Zhurkov; Valentina V Iurchenko; Natalia O Daugel-Dauge; Maria A Kovalenko; Elena K Krivtsova; Andrey D Durnev
Journal:  Mutat Res       Date:  2011-08-17       Impact factor: 2.433

7.  Effect of treatment media on the agglomeration of titanium dioxide nanoparticles: impact on genotoxicity, cellular interaction, and cell cycle.

Authors:  Raju Y Prasad; Kathleen Wallace; Kaitlin M Daniel; Alan H Tennant; Robert M Zucker; Jenna Strickland; Kevin Dreher; Andrew D Kligerman; Carl F Blackman; David M Demarini
Journal:  ACS Nano       Date:  2013-02-15       Impact factor: 15.881

8.  In vivo genotoxicity assessment of titanium, zirconium and aluminium nanoparticles, and their microparticulated forms, in Drosophila.

Authors:  Eşref Demir; Fatma Turna; Gerard Vales; Bülent Kaya; Amadeu Creus; Ricard Marcos
Journal:  Chemosphere       Date:  2013-10-03       Impact factor: 7.086

9.  Cytotoxicity, pro-oxidant effects and antioxidant depletion in rat lung alveolar macrophages exposed to ultrafine titanium dioxide.

Authors:  F Afaq; P Abidi; R Matin; Q Rahman
Journal:  J Appl Toxicol       Date:  1998 Sep-Oct       Impact factor: 3.446

10.  Genotoxicity evaluation of nanosized titanium dioxide, synthetic amorphous silica and multi-walled carbon nanotubes in human lymphocytes.

Authors:  Ana M Tavares; Henriqueta Louro; Susana Antunes; Stephanie Quarré; Sophie Simar; Pieter-Jan De Temmerman; Eveline Verleysen; Jan Mast; Keld A Jensen; Hannu Norppa; Fabrice Nesslany; Maria João Silva
Journal:  Toxicol In Vitro       Date:  2013-06-27       Impact factor: 3.500

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  32 in total

1.  CeO2 nanoparticle fate in environmental conditions and toxicity on a freshwater predator species: a microcosm study.

Authors:  Agathe Bour; Florence Mouchet; Stéphanie Cadarsi; Jérôme Silvestre; David Baqué; Laury Gauthier; Eric Pinelli
Journal:  Environ Sci Pollut Res Int       Date:  2017-06-05       Impact factor: 4.223

Review 2.  The impact of nanomaterial characteristics on inhalation toxicity.

Authors:  Frank S Bierkandt; Lars Leibrock; Sandra Wagener; Peter Laux; Andreas Luch
Journal:  Toxicol Res (Camb)       Date:  2018-02-01       Impact factor: 3.524

Review 3.  Subchronic and chronic toxicity evaluation of inorganic nanoparticles for delivery applications.

Authors:  Raziye Mohammadpour; Marina A Dobrovolskaia; Darwin L Cheney; Khaled F Greish; Hamidreza Ghandehari
Journal:  Adv Drug Deliv Rev       Date:  2019-07-08       Impact factor: 15.470

4.  Aspirin and paracetamol removal using a commercial micro-sized TiO2 catalyst in deionized and tap water.

Authors:  Claudia L Bianchi; Benedetta Sacchi; Carlo Pirola; Francesco Demartin; Giuseppina Cerrato; Sara Morandi; Valentino Capucci
Journal:  Environ Sci Pollut Res Int       Date:  2016-10-21       Impact factor: 4.223

5.  Titanium dioxide nanoparticles: an in vitro study of DNA binding, chromosome aberration assay, and comet assay.

Authors:  Suhani Patel; Palak Patel; Sonal R Bakshi
Journal:  Cytotechnology       Date:  2017-01-03       Impact factor: 2.058

6.  The Protective Effects of Vitamins A and E on Titanium Dioxide Nanoparticles (nTiO2)-Induced Oxidative Stress in the Spleen Tissues of Male Wistar Rats.

Authors:  Mozhgan Afshari-Kaveh; Roghayeh Abbasalipourkabir; Alireza Nourian; Nasrin Ziamajidi
Journal:  Biol Trace Elem Res       Date:  2020-11-18       Impact factor: 3.738

7.  Drosophila as a Suitable In Vivo Model in the Safety Assessment of Nanomaterials.

Authors:  Eşref Demir; Fatma Turna Demir; Ricard Marcos
Journal:  Adv Exp Med Biol       Date:  2022       Impact factor: 2.622

Review 8.  Mechanisms of immune response to inorganic nanoparticles and their degradation products.

Authors:  Raziye Mohammapdour; Hamidreza Ghandehari
Journal:  Adv Drug Deliv Rev       Date:  2021-11-02       Impact factor: 15.470

9.  Profiling Non-Coding RNA Changes Associated with 16 Different Engineered Nanomaterials in a Mouse Airway Exposure Model.

Authors:  Joseph Ndika; Piia Karisola; Pia Kinaret; Marit Ilves; Harri Alenius
Journal:  Cells       Date:  2021-05-01       Impact factor: 6.600

10.  Moroccan Bee Bread Improves Biochemical and Histological Changes of the Brain, Liver, and Kidneys Induced by Titanium Dioxide Nanoparticles.

Authors:  Meryem Bakour; Nawal Hammas; Hassan Laaroussi; Driss Ousaaid; Hinde El Fatemi; Abderrazak Aboulghazi; Najoua Soulo; Badiaa Lyoussi
Journal:  Biomed Res Int       Date:  2021-06-23       Impact factor: 3.411

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