Correlation between formamidopyrimidine DNA glycosylase (Fpg)-sensitive sites determined by a comet assay, increased MDA, and decreased glutathione during long exposure to thinner inhalation
Introduction
Thinners are chemical mixtures containing toluene, benzene, acetone, methanol, hexanes, and other substances. They are widely used as industrial solvents and have potential for abuse inhalation, which is a public health problem in Mexico. Data from the Mexican Survey on Addiction showed that inhaled solvents were the second most frequently used drugs among street children and teenagers (Medina-Mora et al., 2003). Glue and thinner sniffing are the most common forms of thinner abuse due to their accessibility and low cost (Villatoro et al., 2002).
Thinner sniffing causes damage to the brain, kidney, liver, lung, and reproductive system. Oxidative stress is a possible mechanism for tissue damage in individuals and animals exposed to thinner fumes. In one report, toluene increased the intensity of chemiluminescence, indicating activation of free radical processes in brain (Burmistrov et al., 2001). Increased lipid peroxidation, depletion of glutathione (GSH), and a neuroprotective effect of melatonin have been observed in brain after thinner exposure (Baydas et al., 2003). In lung, thinner inhalation caused increased lipid peroxidation, decreased superoxide dismutase activity, and GSH depletion (Zengin et al., 1998). In the plasma of people who abused inhalants, lipid peroxidation increased, and GSH levels decreased (Halifeoglu et al., 2000, Dündaröz et al., 2003).
However, the effect of thinner inhalation on DNA has not been studied. Toluene is the principal component of most thinners (accounting for 60–70% of thinner volume). Toluene is mainly metabolized to benzoic acid, but minor toluene metabolism is responsible for the toxic effects of thinner. A minor pathway of toluene metabolism yields toluene epoxide(s), which rearranges to cresol; cresol, in turn, is hydroxylated to form methylhydroquinone and methylbenzoquinone. These quinones, during redox processes generate reactive oxygen species (ROS) that can cause “oxidative stress” and oxidative DNA damage (Murata et al., 1999). The minor toluene metabolite p-cresol can also induce DNA damage by direct alkylation. Enzymatic oxidation of p-cresol results in the formation of a quinone methide, which reacts with DNA. The resulting DNA adducts have been proposed as specific biomarkers for toluene exposure in humans (Gaikwad and Bodell, 2003).
The aim of this project was to examine DNA damage in lymphocytes of rats exposed to thinner fumes over a period of 16 weeks. We examined lymphocytes, because they are routinely used to monitor DNA damage in human populations and can be obtained easily and repeatedly from the same animals during the course of exposure. We combined single cell gel electrophoresis (comet assay), a simple and sensitive technique to detect DNA damage, with a restriction enzyme formamidopyrimidine glycoslyase (Fpg), which recognizes oxidized purines (products of DNA oxidation) and some alkylated DNA products (Cadet et al., 2003, Tudek et al., 1998). In addition, we assessed two oxidative stress biomarkers (GSH and malondialdehyde (MDA)) used in previous studies that showed oxidative stress effects of thinner inhalation. We established the interrelationships between GSH depletion, MDA increase, and DNA damage. Overall, our analysis demonstrated a high correlation between the levels of these two biomarkers of oxidative stress and the number of Fpg-sensitive sites in DNA induced by thinner inhalation. Thus, we suggest that DNA damage detected by the Fpg enzyme corresponds, at least in part, to oxidative DNA damage. In addition, we showed that the comet assay, in combination with the enzyme Fpg, can be used as a rapid test for biomonitoring exposure to organic solvents.
Section snippets
Chemicals
The repair endonuclease Fpg was obtained from New England Bio-Labs, and DAPI from Vectashield. Histopaque 1077 and all other compounds were purchased from the Sigma Chemical Company.
Animals and experimental design
Four-week-old male (weighing 100–120 g) Sprague–Dawley rats from the animal facility of the Instituto de Neurobiología, UNAM were housed in polycarbonate cages. All rats were maintained in accordance with the guide for the Care and Use of Laboratory Animals. We used common thinner (Petroquimica Pemex) composed of 63%
Results
A significant difference in body weight was seen between the thinner treatment and control groups. The control group gained 340 g, and the thinner-exposed group gained only 219 g (64.4%) during the 16 weeks of thinner inhalation (Fig. 1).
Lymphocytes from three rats exposed to thinner inhalation and three control rats were analyzed by the alkaline version of the comet assay in the absence of Fpg treatment. DNA damage observed in this assay corresponds to alkali-labile sites (ALS), single-stranded
Discussion
Our conditions of thinner exposure induced tissue damage as reported previously (Cárabez et al., 1998). Moreover, rats exposed to thinner inhalation showed a smaller body weight gain compared with control rats. A possible effect of toluene on appetite suppression has been suggested (Morón et al., 2004).
We find no significant DNA single strand or double strand breaks with the comet assay under alkaline conditions (p-value = 0.1213 by Mann–Whitney U-test); therefore, under our conditions, thinner
Acknowledgements
We would like to recognize the assistance of Martín Garcia, Pilar Galarza, Nydia Hernández, Dr. Dorothy Pless, Dr. Magda Giordano, and Nancy Hernández. We thank Dr. M. Díaz-Muñoz for critical comments on the manuscript.
We are particularly grateful to Dr. Sylvie Sauvaigo from CEA, Grenoble France for helpful advice. This work was supported in part by PAPIIT IN208-003-3.
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