Abstract
Genotoxic effects of indium tin oxide (ITO) were investigated on root cells of Allium cepa by employing both Allium and Comet assays. A. cepa roots were treated with the aqueous dispersions of ITO at 5 different concentrations (12.5, 25, 50, 75, and 100 ppm) for 4 h. Exposure of ITO significantly increased mitotic index, and total chromosomal aberrations by the Allium test. While chromosome laggards, stickiness, disturbed anaphase–telophase and anaphase bridges were observed in anaphase–telophase cells, c-metaphase and binuclear cells were observed in other cells. A significant increase in DNA damage was also observed at all concentrations of ITO by the Comet assay. These results indicate that ITO exhibits genotoxic activity in A. cepa root meristematic cells.
Keywords: Allium test, Chromosome aberration, Comet assay, DNA damage
Introduction
ITO, composed of Indium (III) oxide (In2O3, 90 %) and tin (IV) oxide (SnO2, 10 %), is used for liquid crystal display (LCDs), electrochromic displays, flat panel displays, field emission displays, touch or laptop computer screens, cell phones, energy conserving architectural windows, defogging aircraft and automobile windows, heat-reflecting coatings to increase light bulb efficiency, gas sensors, antistatic window coatings, wear resistant layers on glass, nanowires and nanorods because of its unique properties of high electrical conductivity, transparency and mechanical resistance (Copra and Das 1983; Lee et al. 1997; Alam and Cameron 2002; Patel et al. 2003; Homma et al. 2003; Jang et al. 2005; Elangovan and Ramamurthi 2005; Li et al. 2005; Lison et al. 2009). Nakajima et al. (2008) showed that indium caused tail malformations in rat fetuses by caudal hypoplasia probably due to excessive cell loss by increased apoptosis in the tailbud at the early postimplantation stage. ITO also caused chronic pulmonary toxicity when repeated intratracheal instillations were given to hamsters (Tanaka et al. 2010). Incidences of bronchiolo-alveolar adenomas and carcinomas, bronchiolo-alveolar hyperplasia, alveolar proteinosis and infiltrations of alveolar macrophages and inflammatory cells were significantly increased after inhalation exposure of rats to ITO aerosol (Nagano et al. 2011). Lison et al. (2009) found that ITO particles represent a new toxicological entity which has the potential to generate high amounts of ROS and induce lung toxicity in experimental animals, including inflammatory and genotoxic effects. Studies of workers exposure showed that ITO induced occupational lung disease and the risk of interstitial lung damage (Homma et al. 2003, 2005; Chonan et al. 2007; Hamaguchi et al. 2008). Surfactant protein A, and surfactant protein D levels, sensitive markers of interstitial lung disease, were elevated significantly in the workers with moderately high indium exposure (Liu et al. 2012).
Higher plants (Vicia faba, Tradescantia paludosa, Pisum sativum, Hordeum vulgare, Crepis capillaries, Nicotiana tabacum and Allium cepa etc.) are highly reliable bioassays with a high sensitivity in general toxicity studies. Among them, A. cepa anaphase–telophase test is used for studying the effects of different compounds on chromosome and cell division because of its properties such as simplicity, speed, economics, large size and small number of chromosomes, good correlation with other test systems etc. (Fiskesjö 1985, 1988; Grant 1999; Rank 2003; Saxena et al. 2005; Konuk et al. 2007; Liman et al. 2010, 2012).
Comet assay is routinely used for detecting strand breaks in the DNA of single cells due to its high sensitivity, simplicity, speed, low cost, requirement of relatively small number of cells and versatility (Singh et al. 1998; Tice et al. 2000; Duez et al. 2003; Collins 2004; Olive and Banath 2006; Gichner et al. 2009). Apart from Allium test, root meristem cells of A. cepa are also used in different laboratories for detecting DNA damage by Comet assay which is faster, simpler and independent of mitosis (Seth et al. 2008; Chakraborty et al. 2009; Gichner et al. 2009; Ghosh et al. 2010; Liman et al. 2011; Türkoğlu 2012).
The objective of this study was to investigate the effects of ITO on MI (mitotic index), mitotic phases, CAs (chromosome abberations) by Allium test and DNA damage by Comet assay in the root meristem cells of A. cepa.
Materials and methods
Organism
Allium cepa (2n = 16) onion bulbs, 25–30 mm diameter, without any treatment, were purchased from a local supermarket.
Chemicals
Indium tin oxide (CAS No. 50926-11-9, nano powder, <50 nm particle size, In2O3, 90 %; SnO2, 10 %), methyl methanesulfonate (MMS, CAS No. 67-27-3), normal melting point agarose (NMPA), low melting point agarose (LMPA), di-sodium salt of ethylene diamine tetra acetic acid (EDTA), Tris buffer, ethidium bromide (EtBr), Trizma base, Tris HCl, Triton X-100 and SDS were purchased from Sigma Aldrich (Munich, Germany).
Allium cepa anaphase–telophase test
ITO was suspended directly in distilled water and dispersed by ultrasonic vibration (130 W, 20 kHz) for 30 min to prepare five required dispersions (12.5, 25, 50, 75, and 100 ppm). All concentrations were selected arbitrarily. Prior to initiating the test, the outer scales of the bulbs and the dry bottom plate were removed without destroying the root primordia. Six healthy onion bulbs were grown in the dark at room temperature (~21 °C ± 4 °C) for 24 h. After this time, they were treated with different concentrations of ITO for 4 h. The root tips (4–5 mm) were collected and immediately fixed in aceto:alcohol (1:3) for 24 h. They were then transferred to 70 % ethyl alcohol and stored at 4 °C until use. Fixation and staining of the root tip cells were carried out as reported earlier (Liman 2013).
Slides were randomly coded and scored blindly. The MI and the frequencies of CAs were carried out according to Saxena et al. (2005). In order to obtain MI, 5,000–6,000 cells (1,000 cells in each of the five slides) were observed for each sample. MI is calculated as: MI = total number of dividing cells/total cell number × 100. In chromosome aberration test, 100 cells in anaphase or telophase were examined for CAs per slide if possible. Types of aberrations scored included disturbed anaphase–telophase, chromosome laggards, stickiness and anaphase bridges.
Application of the Comet assay (single cell gel electrophoresis)
Root meristem cells of A. cepa were exposed to similar concentrations of ITO as used for cytogenetic analysis. 20–30 seedlings were placed in a petri dish kept on ice and spread with 500 μL of ice-cold Tris-MgCl2 buffer (0.2 M Tris, pH 7.5; 4 mM MgCl2-6H2O; 0.5 % w/v Triton X-100). The roots were immediately chopped with a fresh razor blade and isolated root nuclei were collected in the buffer. Each microscope slide was pre-coated with a layer of 1 % NMPA and thoroughly dried at room temperature. Next, 100 μL of 0.8 % LMPA at 37 °C was mixed with 20 μL of the nuclear suspension and dropped on top of the first layer. The slides were allowed to solidify for 5 min on an ice-cooled tray and were then immersed in ice-cold lysing solution (1 M NaCl; 30 mM NaOH, 0.5 % w/v SDS, pH 12.3) for 1 h. Subsequent to lysing, the slides were placed in a horizontal gel electrophoresis chamber and the DNA was allowed to unwind for 1 h in the electrophoretic buffer, containing 30 mM NaOH and 1.5 mM EDTA at pH > 12.3. Electrophoresis was then conducted for 20 min at 25 V (1 V cm−1) in the chamber cooled on ice. Following electrophoresis, the slides were rinsed three times with cold distilled water for neutralization and stained with 60 μL EtBr (20 μg ml−1) and covered with a cover slip (Rucińska et al. 2004). Fifty comets (50 comets/slide) were scored visually as belonging to one of five classes (0—undamaged, 1—mild damage, 2—moderate damage, 3—severe damage, 4—complete damage) using a fluorescence microscope (Collins 2004). Thus, the total score for 50 comets could range from 0 (all undamaged) to 200 (all damaged). The percentage of damaged cells was calculated and statistically analyzed. Arbitrary Unit used to express the extent of DNA damage was calculated as follows Eq. 1):
| 1 |
where Ni = Number of cells in i degree; i = degree of damage (0, 1, 2, 3, 4).
Statistical analysis
The MI, mitotic phases and CAs (expressed as percents) and comet scores were presented as mean ± standard deviation. The levels of significance in different treatment groups were analyzed using the Duncan multiple range tests by using SPSS 18.0 version for Windows software. p < 0.05 was set as statistical significance.
Results and discussion
The Allium test was carried out for detecting genotoxic effects and DNA damage of Indium tin oxide. The effect of ITO on MI and mitotic phases in the root meristematic cells of A. cepa treated for 4 h is summarized in Table 1. At all concentrations used in the incubations of root increased MI was observed compared to negative control. The highest values were obtained with 100 ppm of ITO (25.1 ± 0.75), and the lowest one with 10 ppm of MMS (15.83 ± 1.48). The increase of MI showed statistically significant results (p < 0.05) in all concentrations. MI increased in a dose dependent manner (r = 0.599, p < 0.01). The cytotoxicity levels of an agent can be determined by the increase or decrease in the MI (Fernandes et al. 2007). MIs lower than the negative control may indicate that the growth and development of exposed organisms have been affected by the test compounds. On the other hand, MIs above those of the negative control may be result of the induction of increased cell division, which may characterize an event detrimental to cells, leading to uncontrolled proliferation and even tumor formation (Hoshina 2002) or could be a consequence of delayed mitosis (Tkalec et al. 2009) The increased cell proliferation activity can be the consequence of a reduction of the time necessary for DNA repair (Evseeva et al. 2005). The characteristic effect caused by the tested preparations of ITO was a decrease of prophase index (especially at 100 ppm) and metaphase index (except at 75 and 100 ppm), simultaneous increase of anaphase (except at 12.5 ppm) and telophase index (except at 25 ppm) when compared to control. Some of the increased and decreased phase indices showed statistically significant results (p < 0.05). This may indicate an alteration of the cell cycle with more cells entering and exiting mitosis than in the controls. According to Hasegawa et al. (2012), ITO may affect cytosolic signal transduction elements to interfere with the homeostatic regulatory system, causing abnormal cell proliferation.
Table 1.
The effects of ITO on mitotic index and mitotic phase in A. cepa root meristem cells
| Concentration (ppm) | CCN | Mitotic Index ± SD | Mitotic phases (%) ± Standard deviation (SD)* | ||||
|---|---|---|---|---|---|---|---|
| Prophase | Metaphase | Anaphase | Telophase | ||||
| Control | – | 5,181 | 18.96 ± 1.06a | 78.78 ± 2.46a | 9.15 ± 1.91ad | 4.98 ± 1.92a | 7.09 ± 1.94a |
| MMS | 10 | 5,231 | 15.83 ± 1.48b | 77.91 ± 0.87ab | 19.81 ± 0.56b | 0.96 ± 0.29b | 1.32 ± 0.16b |
| Indium tin oxide | 12.5 | 5,263 | 23.32 ± 1.15c | 77.39 ± 1.12ab | 7.09 ± 1.19c | 4.74 ± 1.67a | 10.78 ± 1.43c |
| 25 | 5,295 | 23.63 ± 0.7cd | 76.69 ± 0.8b | 8.25 ± 1.36ac | 8.26 ± 0.95cd | 6.8 ± 0.94a | |
| 50 | 5,248 | 23.72 ± 0.3cd | 78.08 ± 1.26ab | 7.42 ± 1.13c | 6.64 ± 0.9c | 7.86 ± 0.55ad | |
| 75 | 5,201 | 24.69 ± 1.43cd | 73.41 ± 1.23c | 10.62 ± 1.14de | 8.76 ± 1.32d | 7.21 ± 1.59a | |
| 100 | 5,182 | 25.1 ± 0.75d | 68.65 ± 0.54d | 11.82 ± 0.87e | 10.39 ± 0.84e | 9.14 ± 0.69d | |
CCN counting cell number
* Means with the same letter do not differ statistically at the level of 0.05
In the A. cepa anaphase–telophase chromosome aberration test to investigate the genotoxic potential of the ITO conducted with root meristematic cells of A. cepa is shown in Table 2. Four types of aberrations (especially chromosome laggards, stickiness, disturbed anaphase–telophase and anaphase bridges) were observed in anaphase–telophase cells. The effect of ITO concentrations on CA was significantly different (p < 0.05) compared to the negative control and higher than MMS at 75 and 100 ppm of ITO. Total aberrations for ITO was found in a dose dependent manner (r = 0.852, p < 0.01). Among above aberrations, disturbed anaphase–telophase and chromosome laggards (especially at 75 and 100 ppm) could occur by the effect of ITO on microtubule formations (Amer and Ali 1986; Kumari et al. 2009). Such spindle malfunctioning may arise due to inhibition of tubulin polymerization (Kuriyama and Sakai 1974) or could be changes in the cytoskeleton proteins after incubation with ITO (Kwee et al. 2001; Tkalec et al. 2009). Chromosome laggards at anaphase may due to the failure of the chromosomes or acentric chromosome fragments to move to either of the pole and may cause delayed prophase and/or metaphase and lead to an increased mitotic index (Evseeva et al. 2005). Stickiness (especially at 25 ppm), a chromatid type of aberration, indicates highly irreversible type of toxic effect of ITO, and its occurrences during the study could be due to sub-chromatid linkage between chromosomes and probably leads to cell death (Chauhan et al. 1986; Ajay and Sarbhoy 1988; Kovalchuk et al. 1998; Barbério et al. 2011). Anaphase bridges indicating structural chromosomal mutations could happen during the translocation of unequal chromatid exchange or can be due to dicentric chromosome presence due to the breakage and fusion of chromosomes and chromatids, or due to less active replication enzymes (Badr et al. 1992; El-Ghamery et al. 2000; Luo et al. 2004). In addition to these anomalies, other anomalies (especially c-metaphase and binuclear cell) were also observed. While the lowest anomalies were observed with 0.08 ± 0.03 % at the 100 ppm for ITO, the highest one was observed with 2.93 ± 0.41 % at the 10 ppm of MMS. Statistically significant (p < 0.05) frequencies of other anomalies were recorded for 25 and 50 ppm for ITO. C-metaphase, a possibly reversible effect, might occur due to disturbed microtubules by ITO or an imbalance of the proteins responsible for the structure of nuclear chromatin and can result in multinuclear cells (Fiskesjö 1988; Shahin and El-Amoodi 1991; Odeigah et al. 1997; Kurás et al. 2006; Fernandes et al. 2007). Binuclear cells might occur as a result of inhibition of cell plate formation or even mitotic irregularities (Grant 1978). Such anomalies in interphases may lead to the induction of cell death process (Leme and Marin-Morales 2008). Unlike our results, Asakura et al. (2009) showed that indium was not genotoxic by chromosomal aberration tests in cultured mammalian cells because average particle size of indium (45 μm) was larger than cell size. It was found that ITO particles induced an increased frequency of micronuclei in type II pneumocytes in vivo but not in lung epithelial cells in vitro, suggesting the preponderance of a secondary genotoxic mechanism (Lison et al. 2009). ITO also increased mutation in rat alveolar type II cells (Driscoll et al. 1997) and carcinogenicity in male and female rats (Nagano et al. 2011). Indium chloride also induced micronuclei formation (Takagi et al. 2011; Lin et al. 2011).
Table 2.
Percentage of chromosome aberrations of ITO at different times and concentrations obtained for the A. cepa anaphase telophase test
| Concentration (ppm) | Anaphase–telophase anomalies % | Other anomalies % | ||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|
| CCN | DAT | CL | S | AB | TA ± SD* | CCN | CM | BNC | p | TA ± SD* | ||
| Control | – | 500 | 6.2 | 6.8 | 9.6 | 1.2 | 23.8 ± 3.03a | 5,181 | 0.06 | 0.06 | – | 0.12 ± 0.05a |
| MMS | 10 | 139 | 3.8 | 39.67 | 0.63 | – | 44.1 ± 2.62bd | 5,202 | 2.93 | – | – | 2.93 ± 0.41b |
| Indium tin oxide | 12.5 | 500 | 3.8 | 18.8 | 7.4 | 1.8 | 31.8 ± 4.32c | 5,263 | 0.23 | 0.02 | – | 0.25 ± 0.08ac |
| 25 | 500 | 6.2 | 17.4 | 11.2 | 1 | 35.8 ± 2.58c | 5,295 | 0.4 | 0.02 | 0.02 | 0.44 ± 0.1c | |
| 50 | 500 | 8.2 | 24 | 3.4 | 4.6 | 40.2 ± 3.11d | 5,248 | 0.34 | 0.08 | – | 0.42 ± 0.13c | |
| 75 | 500 | 6 | 27.8 | 8.4 | 2.2 | 44.4 ± 3.57bd | 5,201 | 0.27 | 0.06 | – | 0.33 ± 0.19ac | |
| 100 | 500 | 4.4 | 28.6 | 8 | 4.2 | 45.2 ± 2.28b | 5,182 | 0.08 | – | – | 0.08 ± 0.03a | |
SD standard deviation
* Means with the same letter do not differ statistically at the level of 0.05
CCN counting cell numbers, DAT disturbed anaphase–telophase, CL chromosome laggards, S stickiness, AB anaphase bridge, TA total anomalies, CM C-metaphase, BNC binuclear cell, P polyploidy
Due the ability of the Comet assay to detect low levels of DNA damage in different cell types, the Comet assay represents a powerful tool with which to identify DNA damage. Results obtained from the Comet assay are summarized in Table 3. Results of the chromosomal aberrations and MI show a good correlation with that of the Comet assay. As it can be seen, exposure of ITO increased the DNA damage at all concentrations in a dose dependent manner (r = 0.923, p < 0.01). Comet assay results showed that DNA damage was significantly higher at all concentrations of ITO compared to negative control. While the highest genotoxic activity was observed in the positive control (130 ± 3.46), the lowest one was observed in the negative control (34 ± 5.29). The DNA damaging activity of ITO could be associated with the generation of free radicals. Free radicals from ITO are most probably generated at reactive sites caused by the introduction of substitutional Sn in the overall crystal structure, where electron density is high (Fan and Goodenough 1977). ITO showed the capacity to cause a rupture of C–H bonds, with the consequent release of carbon centered radicals (Lison et al. 2009). ITO showed mutagenic activities via generating DNA damage (Emerit et al. 2001), or bind to nucleoprotein, nucleotide or functional proteins owing to longer contact time (Hasegawa et al. 2012). Gottschling et al. (2001) suggested that indium phosphide-induced oxidative stress may play an important role in the pulmonary carcinogenesis of indium phosphide. Bustamente et al. (1997) found that Indium can induce apoptosis and necrosis in T lymphocytes in a dose-dependent manner.
Table 3.
Detection of DNA damage in nuclei of A. cepa root meristem cells exposure to ITO using the Comet assay
| Compounds | Concentration (ppm) | DNA Damage (Arbitrary Unit ± SD)* |
|---|---|---|
| Negative control | – | 34 ± 5.29a |
| MMS | 10 | 130 ± 3.46b |
| Indium tin oxide | 12.5 | 50 ± 4c |
| 25 | 56.66 ± 2.3d | |
| 50 | 95.33 ± 4.08e | |
| 75 | 100.66 ± 4.16ef | |
| 100 | 104 ± 2f |
SD standard deviation
* Means with the same letter do not differ statistically at the level of 0.05
Conclusions
As a result, ITO has a genotoxic effect by increasing CAs and DNA damage and it also induced cell division by increasing the MI in A. cepa root meristematic cells. Therefore further studies should be conducted to better understand the molecular mechanisms involved in the genotoxicity of ITO. It is essential to pay much greater attention to indium compounds.
References
- Ajay KL, Sarbhoy R. Cytogenetic studies on the effect of some chlorinated pesticides. Cytologia. 1988;53:427–436. doi: 10.1508/cytologia.53.427. [DOI] [Google Scholar]
- Alam MJ, Cameron DC. Investigation of annealing effects on sol–gel deposited indium tin oxide thin films in different atmospheres. Thin Solid Films. 2002;420–421:76–82. doi: 10.1016/S0040-6090(02)00737-X. [DOI] [Google Scholar]
- Amer SM, Ali EM. Cytological effects of pesticides. XVII. Effect of the insecticide dichlorvas on root mitosis of Vicia faba. Cytologia. 1986;51:21–25. doi: 10.1508/cytologia.51.21. [DOI] [Google Scholar]
- Asakura K, Satoh H, Chiba M, Okamoto M, Serizawa K, Nakano M, Omae K. Genotoxicity studies of heavy metals: lead bismuth indium silver and antimony. J Occup Health. 2009;51:498–512. doi: 10.1539/joh.L9080. [DOI] [PubMed] [Google Scholar]
- Badr A, Ghareeb A, El-Din HM. Cytotoxicity of some pesticides in mitotic cells of V. faba roots. Egypt J Appl Sci. 1992;7:457–468. [Google Scholar]
- Barbério A, Voltolini JC, Mello MLS. Standardization of bulb and root sample sizes for the Allium cepa test. Ecotoxicology. 2011;20:927–935. doi: 10.1007/s10646-011-0602-8. [DOI] [PubMed] [Google Scholar]
- Bustamante J, Dock L, Vahter M, Fowler B, Orrenius S (1997) The semiconductor elements arsenic and indium induce apoptosis in rat thymocytes. Toxicology 118:129–136 [DOI] [PubMed]
- Chakraborty R, Mukherjee AK, Mukherjee A. Evaluation of genotoxicity of coal fly ash in Allium cepa root cells by combining comet assay with the Allium test. Environ Monit Assess. 2009;153:351–357. doi: 10.1007/s10661-008-0361-z. [DOI] [PubMed] [Google Scholar]
- Chauhan LKS, Dikshith TSS, Sundararaman V. Effect of deltamethrin on plant cells. Icytological effects on the root meristem cells of Allium cepa. Mutat Res. 1986;171:25–30. doi: 10.1016/0165-1218(86)90005-4. [DOI] [Google Scholar]
- Chonan T, Taguchi O, Omae K. Interstitial pulmonary disorders in indium-processing workers. Eur Respir J. 2007;29:317–324. doi: 10.1183/09031936.00020306. [DOI] [PubMed] [Google Scholar]
- Collins AR. The comet assay for DNA damage and repair: principles applications and limitations. Mol Biotechnol. 2004;26:249–261. doi: 10.1385/MB:26:3:249. [DOI] [PubMed] [Google Scholar]
- Copra KL, Das SR (1983) Thin film solar cell Plenum. New York, p 321
- Driscoll KE, Deyo LC, Carter JM, Howard BW, Hassenbein DG, Bertram TA. Effects of particle exposure and particle-elicited inflammatory cells on mutation in rat alveolar epithelial cells. Carcinogenesis. 1997;18:423–430. doi: 10.1093/carcin/18.2.423. [DOI] [PubMed] [Google Scholar]
- Duez P, Dehon G, Kumps A, Dubois J. Statistics of the comet assay: a key to discriminate between genotoxic effects. Mutagenesis. 2003;18:159–166. doi: 10.1093/mutage/18.2.159. [DOI] [PubMed] [Google Scholar]
- Elangovan E, Ramamurthi K. Studies on micro-structural and electrical properties of spray-deposited fluorine-doped tin oxide thin films from low-cost precursor. Thin Solid Films. 2005;476:231–236. doi: 10.1016/j.tsf.2004.09.022. [DOI] [Google Scholar]
- El-Ghamery AA, El-Nahas AI, Mansour MM. The action of atrazine herbicide as an indicator of cell division on chromosomes and nucleic acid content in root meristems of Allium cepa and Vicia faba. Cytologia. 2000;65:277–287. doi: 10.1508/cytologia.65.277. [DOI] [Google Scholar]
- Emerit J, Beaumont C, Trivin F. Iron metabolism free radicals and oxidative injury. Biomed Pharmacother. 2001;55:333–339. doi: 10.1016/S0753-3322(01)00068-3. [DOI] [PubMed] [Google Scholar]
- Evseeva TI, Geras’kin SA, Shuktomova II, Taskaev AI. Genotoxicity and cytotoxicity assay of water sampled from the underground nuclear explosion site in the north of the Perm region (Russia) J Environ Radioact. 2005;80:59–74. doi: 10.1016/j.jenvrad.2004.08.014. [DOI] [PubMed] [Google Scholar]
- Fan JCC, Goodenough JB. X-ray photoemission spectroscopy studies of Sn-doped indium-oxide films. J Appl Phys. 1977;48:3524–3531. doi: 10.1063/1.324149. [DOI] [Google Scholar]
- Fernandes TCC, Mazzeo DEC, Marin-Morales MA. Mechanism of micronuclei formation in polyploidizated cells of Allium cepa exposed to trifluralin herbicide. Pestic Biochem Phys. 2007;88:252–259. doi: 10.1016/j.pestbp.2006.12.003. [DOI] [Google Scholar]
- Fiskesjö G. The Allium test as standard in environmental monitoring. Hereditas. 1985;102:99–112. doi: 10.1111/j.1601-5223.1985.tb00471.x. [DOI] [PubMed] [Google Scholar]
- Fiskesjö G. The Allium test-an alternative in environmental studies: the relative toxicity of metal ions. Mutat Res. 1988;197:243–260. doi: 10.1016/0027-5107(88)90096-6. [DOI] [PubMed] [Google Scholar]
- Ghosh M, Paul J, Sinha S, Mukherjee A. Comparative evaluation of promutagens o-PDA m-PDA and MH for genotoxic response in root cells of Allium cepa L. Nucleus. 2010;53:45–50. doi: 10.1007/s13237-010-0005-x. [DOI] [Google Scholar]
- Gichner T, Znidar I, Wagner ED, Plewa MJ. The use of higher plants in the Comet assay. In: Dhawan A, Anderson D, editors. The Comet assay in toxicology. UK: Royal Society of Chemistry; 2009. pp. 98–119. [Google Scholar]
- Gottschling BC, Maronpot RR, Hailey JR, Peddada S, Moomaw CR, Klaunig JE, Nyska A. The role of oxidative stress in indium phosphide-induced lung carcinogenesis in rats. Toxicol Sci. 2001;64:28–40. doi: 10.1093/toxsci/64.1.28. [DOI] [PubMed] [Google Scholar]
- Grant WF. Chromosome aberrations in plants as a monitoring system. Environ Health Perspect. 1978;27:37–43. doi: 10.1289/ehp.782737. [DOI] [PMC free article] [PubMed] [Google Scholar]
- Grant WF. Higher plant assays for the detection of chromosomal aberrations and gene mutations—a brief historical background on their use for screening and monitoring environmental chemicals. Mutat Res-Fund Mol Mech. 1999;426:107–112. doi: 10.1016/S0027-5107(99)00050-0. [DOI] [PubMed] [Google Scholar]
- Hamaguchi T, Omae K, Takebayashi T, Kikuchi Y, Yoshioka N, Nishiwaki Y, Tanaka A, Hirata M, Taguchi O, Chonan T. Exposure to hardly soluble indium compounds in ITO production and recycling plants is a new risk for interstitial lung damage. Occup Environ Med. 2008;65:51–55. doi: 10.1136/oem.2006.029124. [DOI] [PubMed] [Google Scholar]
- Hasegawa G, Shimonaka M, Ishihara Y. Differential genotoxicity of chemical properties and particle size of rare metal and metal oxide nanoparticles. J Appl Toxicol. 2012;32:72–80. doi: 10.1002/jat.1719. [DOI] [PubMed] [Google Scholar]
- Homma T, Ueno T, Sekizawa K, Tanaka A, Hirata M. Interstitial pneumonia developed in a worker dealing with particles containing indium-tin oxide. J Occup Health. 2003;45:137–139. doi: 10.1539/joh.45.137. [DOI] [PubMed] [Google Scholar]
- Homma S, Miyamoto A, Sakamoto S. Pulmonary fibrosis in an individual occupationally exposed to inhaled indium–tin oxide. Eur Respir J. 2005;25:200–204. doi: 10.1183/09031936.04.10012704. [DOI] [PubMed] [Google Scholar]
- Hoshina MM (2002) Evaluation of a possible contamination of the waters of the Claro River-Municipality of Rio Claro part of the Corumbataí River Basin with the mutagenicity tests using Allium cepa. State University of São Paulo Rio Claro Sp. (in Portuguese)
- Jang HS, Kim DH, Lee HR, Lee SY. Field emission from cone-like single crystalline indium tin oxide nanorods. Mater Lett. 2005;59:1526–1529. doi: 10.1016/j.matlet.2004.12.051. [DOI] [Google Scholar]
- Konuk M, Liman R, Cigerci IH. Determination of genotoxic effect of boron on Allium cepa root meristematic cells. Pak J Bot. 2007;39:73–79. [Google Scholar]
- Kovalchuk O, Arkhipov I, Telyuk A, Hohn P, Kovalchuk L. The Allium cepa chromosome aberration test reliably measures genotoxicity of soils of inhabited areas In the Ukraine contaminated by the Chernobyl accident. Mutat Res. 1998;415:47–57. doi: 10.1016/S1383-5718(98)00053-9. [DOI] [PubMed] [Google Scholar]
- Kumari M, Mukherjee A, Chandrasekaran N. Genotoxicity of silver nanoparticles in Allium cepa. Sci Total Environ. 2009;407:5243–5246. doi: 10.1016/j.scitotenv.2009.06.024. [DOI] [PubMed] [Google Scholar]
- Kurás M, Nowakowska J, Sliwinska E, Pilarski R, Ilasz R, Tykarska T, Zobel A, Gulewicz K. Changes in chromosome structure mitotic activity and nuclear DNA content from cells of Allium test induced by bark water extract of Uncaria tomentosa (Willd.) DC. J Ethnopharmacol. 2006;107:211–221. doi: 10.1016/j.jep.2006.03.018. [DOI] [PubMed] [Google Scholar]
- Kuriyama R, Sakai H. Role of tubulin-Sh groups in polymerization to microtubules. Functional-Sh groups in tubulin for polymerization. J Biochem. 1974;76:651–654. doi: 10.1093/oxfordjournals.jbchem.a130609. [DOI] [PubMed] [Google Scholar]
- Kwee S, Raskmark P, Velizarov S. Changes in cellular proteins due to environmental non-ionizing radiation. I. Heat-shock proteins. Electro-Magnetobiol. 2001;20:141–152. [Google Scholar]
- Lee H, Kim IG, Cho SW, Lee SH. Effect of process parameters on the characteristics of indium tin oxide thin film for flat panel display application. Thin Solid Films. 1997;302:25–30. doi: 10.1016/S0040-6090(96)09581-8. [DOI] [Google Scholar]
- Leme DM, Marin-Morales MA. Chromosome aberration and micronucleus frequencies in Allium cepa cells exposed to petroleum polluted water—a case study. Mutat Res-Fund Mol Mech. 2008;650:80–86. doi: 10.1016/j.mrgentox.2007.10.006. [DOI] [PubMed] [Google Scholar]
- Li D, Haneda H, Hishita S, Ohashi N, Labhsetwar NK. Fluorine-doped TiO2 powders prepared by spray pyrolysis and their improved photocatalytic activity for decomposition of gas-phase acetaldehyde. J Fluorine Chem. 2005;126:67–77. [Google Scholar]
- Liman R. Genotoxic effects of Bismuth (III) oxide nanoparticles by Allium and Comet assay. Chemosphere. 2013;93:269–273. doi: 10.1016/j.chemosphere.2013.04.076. [DOI] [PubMed] [Google Scholar]
- Liman R, Akyıl D, Eren Y, Konuk M. Testing of the mutagenicity and genotoxicity of metolcarb by using both Ames/Salmonella and Allium Test. Chemosphere. 2010;80:1056–1061. doi: 10.1016/j.chemosphere.2010.05.011. [DOI] [PubMed] [Google Scholar]
- Liman R, Cigerci IH, Akyıl D, Eren Y, Konuk M. Determination of genotoxicity of fenaminosulf by Allium and Comet tests. Pestic Biochem Phys. 2011;99:61–64. doi: 10.1016/j.pestbp.2010.10.006. [DOI] [Google Scholar]
- Liman R, Gökçe UG, Akyıl D, Eren Y, Konuk M. Evaluation of genotoxic and mutagenic effects of aqueous extract from aerial parts of Linaria genistifolia subsp. genistifolia. Rev Bras Farmacogn. 2012;22:541–548. [Google Scholar]
- Lin RH, Yang ML, Li YC, Chang HM, Kuan YH (2011) Indium chloride-induced micronuclei via reactive oxygen species in Chinese hamster lung fibroblast V79 cells. Environ Toxicol 28:595–600. doi:10.1002/tox.20755 [DOI] [PubMed]
- Lison D, Laloy J, Corazzari I, Muller J, Rabolli V, Panin N, Huaux F, Fenoglio I, Fubini B. Sintered indium-tin-oxide (ITO) particles: a new pneumotoxic entity. Toxicol Sci. 2009;108:472–481. doi: 10.1093/toxsci/kfp014. [DOI] [PubMed] [Google Scholar]
- Liu HH, Chen CY, Chen GI, Lee LH, Chen HL. Relationship between indium exposure and oxidative damage in workers in indium tin oxide production plants. Int Arch Occup Environ Health. 2012;85:447–453. doi: 10.1007/s00420-011-0688-6. [DOI] [PubMed] [Google Scholar]
- Luo LZ, Werner KM, Gollin SM, Saunders WS. Cigarette smoke induces anaphase bridges and genomic imbalances in normal cells. Mutat Res-Fund Mol Mech. 2004;554:375–385. doi: 10.1016/j.mrfmmm.2004.06.031. [DOI] [PubMed] [Google Scholar]
- Nagano K, Nishizawa T, Umeda Y, Kasai T, Noguchi T, Gotoh K, Ikawa N, Eitaki Y, Kawasumi Y, Yamauchi T, Arito H, Fukushima S. Inhalation carcinogenicity and chronic toxicity of indium-tin oxide in rats and mice. J Occup Health. 2011;53:175–187. doi: 10.1539/joh.10-0057-OA. [DOI] [PubMed] [Google Scholar]
- Nakajima M, Mitsunaga K, Nakazawa K, Usami M. In vivo/in vitro study in rat embryos on indium-caused tail malformations. Reprod Toxicol. 2008;25:426–432. doi: 10.1016/j.reprotox.2008.04.008. [DOI] [PubMed] [Google Scholar]
- Odeigah PGC, Nurudeen O, Amund OO. Genotoxicity of oil field wastewater in Nigeria. Hereditas. 1997;126:161–167. doi: 10.1111/j.1601-5223.1997.00161.x. [DOI] [Google Scholar]
- Olive PL, Banath JP. The comet assay: a method to measure DNA damage in individual cells. Nat Protoc. 2006;1:23–29. doi: 10.1038/nprot.2006.5. [DOI] [PubMed] [Google Scholar]
- Patel NG, Patel PD, Vaishnav VS. Indium tin oxide (ITO) thin film gas sensor for detection of methanol at room temperature. Sensor Actuat B-Chem. 2003;96:180–189. doi: 10.1016/S0925-4005(03)00524-0. [DOI] [Google Scholar]
- Rank J. The method of allium anaphase–telophase chromosome aberration assay. Ekologija. 2003;1:38–42. [Google Scholar]
- Rucińska R, Sobkowiak R, Gwóźdź EA. Genotoxicity of lead in lupin root cells as evaluated by the comet assay. Cell Mol Biol Lett. 2004;9:519–528. [PubMed] [Google Scholar]
- Saxena PN, Chauhan LKS, Gupta SK. Cytogenetic effects of commercial formulation of cypermethrin in root meristem cells of Allium sativum: spectroscopic basis of chromosome damage. Toxicology. 2005;216:244–252. doi: 10.1016/j.tox.2005.08.008. [DOI] [PubMed] [Google Scholar]
- Seth CS, Misra V, Chauhan LKS, Singh RR. Genotoxicity of cadmium on root meristem cells of Allium cepa: cytogenetic and Comet assay approach. Ecotoxicol Environ Safe. 2008;71:711–716. doi: 10.1016/j.ecoenv.2008.02.003. [DOI] [PubMed] [Google Scholar]
- Shahin SA, El-Amoodi KHH. Induction of numerical chromosomal aberrations during DNA synthesis using fungicides nimrod and rubigan-4 in root tips of Vicia faba L. Mutat Res-Genet Toxicol. 1991;261:169–176. doi: 10.1016/0165-1218(91)90064-S. [DOI] [PubMed] [Google Scholar]
- Singh NP, McCoy MT, Tice RR, Schneider EL. A simple technique for quantitation of low levels of DNA damage in individual cells. Exp Cell Res. 1998;175:184–191. doi: 10.1016/0014-4827(88)90265-0. [DOI] [PubMed] [Google Scholar]
- Takagi R, Suzuki Y, Seki Y, Ikehata M, Kajihara C, Shimizu H, Yanagisawa H. Indium chloride-induced micronuclei in in vivo and in vitro experimental systems. J Occup Health. 2011;53:102–109. doi: 10.1539/joh.L9142. [DOI] [PubMed] [Google Scholar]
- Tanaka A, Hirata M, Homma T, Kiyohara Y. Chronic pulmonary toxicity study of indium–tin oxide and indium oxide following intratracheal instillations into the lungs of hamsters. J Occup Health. 2010;52:14–22. doi: 10.1539/joh.L9097. [DOI] [PubMed] [Google Scholar]
- Tice RR, Agurell E, Anderson D, Burlinson B, Hartmann A, Kobayashi H, Miyamae Y, Rojas YF, Ryu E, Sasaki JC. Single cell gel/comet assay: guidelines for in vitro and in vivo genetic toxicology testing. Environ Mol Mutagen. 2000;35:206–221. doi: 10.1002/(SICI)1098-2280(2000)35:3<206::AID-EM8>3.0.CO;2-J. [DOI] [PubMed] [Google Scholar]
- Tkalec M, Malaric K, Pavlica M, Pevalek-Kozlina B, Vidakovic-Cifrek Z. Effects of radiofrequency electromagnetic fields on seed germination and root meristematic cells of Allium cepa L. Mutat Res-Fund Mol Mech. 2009;672:76–81. doi: 10.1016/j.mrgentox.2008.09.022. [DOI] [PubMed] [Google Scholar]
- Türkoğlu Ş. Determination of genotoxic effects of chlorfenvinphos and fenbuconazole in Allium cepa root cells by mitotic activity chromosome aberration DNA content and comet assay. Pestic Biochem Phys. 2012;103:224–230. doi: 10.1016/j.pestbp.2012.06.001. [DOI] [PubMed] [Google Scholar]
