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      Genotoxicity effect of methyl-tertiary butyl ether on rat lymphocytes using comet assay

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          Abstract

           Dear Editor, Methyl-tertiary butyl ether (MTBE), an oxygenated compound, is added to gasoline in order to reduce air pollutants. MTBE alters enzyme activity or mRNA levels of antioxidant enzymes (Elovaara et al., 2007[11]; Khalili et al., 2015[12]; Badr et al., 2016[1]; Badr and Saadat 2016[3], 2018[2]) and oncogenes (Zhou et al., 1999[14]). It has been reported that elevation of cancer incidence is associated with exposure to MTBE (Belpoggi et al., 1995[4]). Therefore, its usage has been limited in several countries. However, it is still used in several Middle East countries. In many countries, people are exposed to very low levels of MTBE by drinking contaminated water (Brown 1997[6]). In a majority of previous reports, researchers have investigated the effects of high or very high doses of MTBE on experimental animals (de Peyster et al., 2014[9]; Dongmei et al., 2009[10]; Khalili et al, 2015[12]; Badr et al., 2016[1]). It should be noted that low levels of MTBE significantly alter the gene expression levels of GSTs (Badr and Saadat 2018[2]). Although many investigations concerning genotoxicity of MTBE and its metabolites have been carried out, the potential risk of human mutagenicity, is still a matter of debate among toxicologists (Bogen et al., 2015[5]). The purpose of the present experiment is to examine the potential of MTBE at low doses in inducing DNA damage condition using alkaline comet assay. A total of 24 adult Wistar male rats (180-200 g) were purchased from the animal house of Shiraz University of Medical Sciences (Iran). Animals were housed in plastic cages under standard animal house conditions with a 12 h light/dark cycle and a temperature of 25 ± 2 °C, received standard pellet food, and tap water was available ad libitum. After acclimation period (10 days), the animals were randomly divided into four equal experimental groups. Group 1 (control) was treated with distilled water and groups 2, 3 and 4 received 5, 10 and 20 mg/kg/day MTBE in distilled water, respectively. The treatments were done through oral gavage for 30 consecutive days. At the end of the exposure period, animals were anesthetized with ether and blood samples were obtained from their heart. Lymphocytes were separated by density centrifugation at 1000×g for 30 min at the room temperature over a layer of Ficoll and then the cell suspension was adjusted to 104-106 cells/ml. For positive control, 50 μL of the cell suspension obtained from untreated rat was mixed with 1 μM H2O2 and incubated for 5 min at 4 °C. The comet assay was performed under alkaline conditions as described previously (Olive and Banáth, 2006[13]) with some modifications. Thereafter, images of 50 randomly chosen cells were taken per sample with Nikon fluorescence microscope, and then, indices of cellular DNA damage were measured using TriTek CometScore V 2.0 software. Indices of DNA damage were the tail length (TL), tail DNA percent (TD), and tail moment (TM). Statistical analysis indicated that the TL, TD and TM indices in the positive controls which were treated with 1 μM H2O2 showed maximum levels of DNA damage, while the control group revealed very low DNA damage. One-way analysis of variance demonstrated that there were significant statistical differences between the experimental groups for the LT (F=31.19; df=3, 20; P<0.001), TD (F=22.22; df=3, 20; P<0.001), and TM (F=20.35; df=3, 20; P<0.001) indices. The post hoc Duncan test revealed that the means of the study indices were significantly increased in the groups that received 10 and 20 mg/kg/day MTBE compared with the control levels (Figure 1(Fig. 1)). Pearson correlation analysis revealed that there were significant positive correlations between MTBE concentrations and the TL (r=+0.882, df=22, P<0.001), TD (r=+0.851, df=22, P<0.001) and TM (r=+0.852, df=22, P<0.001) indices. It means that the amount of DNA damage increases as a function of MTBE concentration. MTBE has been recently reported to induce chromosomal aberration in bone marrow cells of rats, orally administered with this chemical at high concentration (Darwish and Mosallam 2019[8]). A significant increase in the extent of DNA damage was observed in human lymphocytes treated with MTBE at low doses (Chen et al., 2008[7]). Our present findings indicate that MTBE can induce DNA strand breaks even at low doses under in vivo condition. Considering that MTBE is metabolized to the known weak carcinogens, tert-butanol and formaldehyde (Belpoggi et al., 1995[4]), and in order to find the real association between low levels of MTBE and possible alterations in incidence rates of human cancers, further research in this field is required. Acknowledgement This work was supported by the Shiraz University (97GCU2M1741), Iran. Conflict of interest None.

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          Most cited references13

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          Assessment of genotoxicity of methyl-tert-butyl ether, benzene, toluene, ethylbenzene, and xylene to human lymphocytes using comet assay.

          Methyl-tert-butyl ether (MTBE) is a gasoline oxygenate and antiknock additive substituting for lead alkyls currently in use worldwide. Benzene, toluene, ethylbenzene, and xylene (BTEX) are volatile monoaromatic hydrocarbons which are commonly found together in crude petroleum and petroleum products such as gasoline. The aim of this study is to evaluate the genotoxic effects of these tested chemicals in human lymphocytes. Using the alkaline comet assay, we showed that all of the tested chemicals induce DNA damage in isolated human lymphocytes. This effect could follow from the induction of DNA strands breaks. The neutral version of the test revealed that MTBE, benzene, and xylenes induce DNA double-strand breaks at 200 microM. Apart from MTBE, the spin traps, 5,5-dimethyl-pyrroline-N-oxide (DMPO) and N-tert-butyl-alpha-phenylnitrone (PBN) can decrease the level of DNA damage in BTEX at 200 microM. This indicated that DNA damage could result from the participation of free radicals in DNA-damaging effect, which was further supported by the fact that post-treatment of formamidopyrimidine-DNA glycosylase (Fpg), enzyme recognizing oxidized DNA purines, gave rise to a significant increase in the extent of DNA damage in cells treated with benzene, and xylene at 200 microM. The results obtained suggested that MTBE and BTEX could induce a variety type of DNA damage such as single-strand breaks (SSBs), double-strand breaks (DSBs), and oxidative base modification.
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            Methyl-tertiary-butyl ether (MTBE)--a gasoline additive--causes testicular and lymphohaematopoietic cancers in rats.

            In the framework of a series of experiments conducted to evaluate the carcinogenic effects of oxygenated gasoline additives, MTBE was analyzed in an oral lifetime carcinogenicity study using 8-week-old male and female Sprague-Dawley rats. These experiments were part of a large research project on gasoline carcinogenicity performed at the Bentivoglio (BT) Castle Cancer Research Center of the Ramazzini Foundation and of the Bologna Institute of Oncology, MTBE, dissolved in oil, was administered by stomach tube at the doses of 1000, 250, or 0 mg/kg b.w., once daily, four days weekly, for 104 weeks. The animals were maintained until natural death. The last animal died 166 weeks after the start of the experiment, i.e., at 174 weeks of age. Under the tested experimental conditions, MTBE was shown to cause an increase in Leydig interstitial cell tumors of the testes and a dose-related increase in lymphomas and leukemias in female rats.
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              Atmospheric and potable water exposures to methyl tert-butyl ether (MTBE).

              S L Brown (1997)
              This paper presents information on the ways in which people can be exposed to methyl tert-butyl ether (MTBE) via air and water and on the distribution of doses that can result from those exposures. Data on concentrations of MTBE in air were complied for 15 different occupational, commuting, or residential exposure categories, and concentrations in potable water were complied from five states in the MTBE-using areas of the United States. Based on these concentrations and characteristics of the exposed populations, average daily and lifetime average doses were estimated. Both the concentration data and several of the population characteristics were estimated as distributions rather than as point values so that the numbers of people exposed at various levels could be estimated. Arithmetic mean occupational doses via air were in the range of 0.1 to 1.0 mg/kg-day, while doses from residential exposures, commuting, and refueling were in the range of 0.0004 to 0.006 mg/kg-day. Lifetime doses for workers were in the range 0.01 to 0.1 mg/kg-day. The cumulative dose distribution for the entire population of the MTBE-using regions of the United States was estimated by combining the distributions of doses and the numbers of people in each exposure category. In the MTBE-using areas, arithmetic mean doses via air were estimated to be 0.0053 and 0.00185 mg/kg-day for the chronic and lifetime cases, respectively. Approximately 98.5% of the population living in MTBE-using regions uses water with concentrations affected only by atmospheric deposition, if at all, and too low to be detected with current methods (< 2 micrograms/liter). The remaining population uses water with an estimated geometric mean concentration of 0.36 microgram/liter, an arithmetic mean concentration of 49 micrograms/l, and a 95th percentile concentration of 64 micrograms/liter. Doses via ingestion, inhalation, and dermal absorption were included. The estimated arithmetic mean dose for the population exposed via water was 1.4 x 10(-3) mg/kg-day.
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                Author and article information

                Journal
                EXCLI J
                EXCLI J
                EXCLI J
                EXCLI Journal
                Leibniz Research Centre for Working Environment and Human Factors
                1611-2156
                25 May 2020
                2020
                : 19
                : 668-670
                Affiliations
                [1 ]Department of Biology, College of Sciences, Shiraz University, Shiraz 71467-13565, Iran
                Author notes
                *To whom correspondence should be addressed: Mostafa Saadat, Department of Biology, College of Sciences, Shiraz University, Shiraz 71467-13565, Iran; Fax: +98-71-32280926, E-mail: saadat@ 123456shirazu.ac.ir
                Article
                2020-1214 Doc668
                7290103
                1e82b759-c56e-4935-b382-15eeb9cb1c56
                Copyright © 2020 Alishahi et al.

                This is an Open Access article distributed under the terms of the Creative Commons Attribution Licence ( http://creativecommons.org/licenses/by/4.0/) You are free to copy, distribute and transmit the work, provided the original author and source are credited.

                History
                : 13 March 2020
                : 13 May 2020
                Categories
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