Elsevier

Toxicology in Vitro

Volume 20, Issue 1, February 2006, Pages 101-108
Toxicology in Vitro

Oxidative stress induction by short time exposure to ozone on THP-1 cells

https://doi.org/10.1016/j.tiv.2005.06.007Get rights and content

Abstract

Ozone is a major component of air pollution mainly formed by photochemical reactions of nitrogen oxides with volatile organic compounds and/or carbon monoxide. Numerous studies have shown the association between ozone exposure with pulmonary injuries. This pollutant is a strong oxidant exerting its biological action either by direct reaction with target molecules or by generating reactive oxygen species which result in its biological effects and its toxicity. In order to study the effects of an induced oxidative stress by ozone on THP-1 cell, a human macrophage-like cell line, we used an in vitro system which has been previously used to study the rapid responses to ozone exposure. Using this system, THP-1 cells were subjected to short time exposure (30 min) followed by different incubation times ranging from 4 to 24 h. Our results show that ozone exposure provokes an alteration of the cell membrane translating an induction of lipid peroxidation resulting in a 3.2-fold increase of thiobarbituric reactive substances (TBARS), an increase by 35% of heme oxygenase-1 (HO-1) expression, and significant modifications of the redox status evaluated by glutathione measurement and of antioxidant enzyme activities in THP-1 cells. Our in vitro model constitutes a very interesting tool for the measurement of ozone effect on rapid modifications induced by this pollutant as well as intracellular modifications due to an oxidative stress.

Introduction

Ozone (O3) is a major component of urban air pollution. Indeed, tropospheric ozone is a secondary pollutant mainly formed by photochemical reactions of nitrogen oxides with volatile organic compounds and/or carbon monoxide (Mustafa, 1990). Several studies have shown a significant negative association between ozone exposure and pulmonary function including the reduction of lung volume parameters (Blomberg et al., 1999), inflammatory response (Scannell et al., 1996), disruption of the epithelial barrier associated with altered vascular permeability (Bhalla, 1999, Bhalla and Gupta, 2000) and the release of toxic and chemotactic mediators (Chang et al., 1998, Klestadt et al., 2002). This pollutant is a powerful oxidant exerting its biological action either by direct reaction with target molecules or via free radicals formed in the process of peroxidation of polyunsaturated fatty acids (PUFA) and oxidation of proteins, amines and thiols (Pryor et al., 1982, Pryor, 1994). Therefore, a consequence of ozone exposure is the induction of oxidative stress which is responsible for the toxicity of this pollutant. The susceptibility to ozone can be estimated by evaluating the antioxidant/stress related response, such as an increase of 8-isoprostane concentration (a lipid peroxidation product of arachidonic acid) in exhaled breath condensate (Corradi et al., 2002, Montuschi et al., 2002). An induction of heat shock/stress protein (HSP) expression has also been observed in lavaged lung cells in guinea pigs (Su and Gordon, 1997), rat and mouse lungs (Wong et al., 1996, Valacchi et al., 2004), and in human alveolar macrophages (Hamilton et al., 1996, Hamilton et al., 1998). Concerning the antioxidant response to ozone, depletion of vitamin E has been reported in mouse lung tissue (Valacchi et al., 2004) and in rat lung, activities of antioxidant enzymes activities (superoxide dismutase, catalase and glutathione peroxidase) are increased after long term ozone exposure (0.7 ppm O3 for five days) (Rahman et al., 1991). To determine the cell specific response to ozone, an in vitro approach using primary culture or established cell lines has proven to be useful, allowing the evaluation of the peroxidative damage induced by ozone on rat alveolar macrophages (Banks et al., 1990) or even the modification of glutathione contents (Rietjens et al., 1985a, Rietjens et al., 1985b).

In order to test the susceptibility of THP-1 cells, a human macrophage-like cell line, to oxidative stress induced by ozone, we submitted these cells to short time exposures (30 min at 0.5 ppm) followed by different incubation times ranging from 4 to 24 h. The system for short time in vitro exposures to low ozone concentrations has been developed previously, allowing the measurement of mobility decrease after intoxication (Laval-Gilly et al., 2000) in order to develop a biosensor to evaluate gases pollutant toxicity. The aim of this study was to determine ozone effects on several typical oxidative markers after short exposure time in our cell model using our in vitro system. The evaluation of the primary response consisted of the determination of lipid peroxidation whereas the delayed response was investigated by the measurement of HO-1 expression, glutathione and linked enzyme activities after exposure. Our results show that ozone exposure provokes an increase of lipid peroxidation and heme oxygenase-1 (HO-1) expression, as well as modifications of the redox status and of antioxidant enzyme activities in THP-1 cells using our in vitro model.

Section snippets

Cell culture

Human monocytic cell line THP-1 (ATCC TIB-202) was grown in RPMI 1640 supplemented with 10% (v/v) heat-inactivated foetal calf serum, 2 mM l-glutamine, 50 U/ml penicillin and 50 μg/ml streptomycin (Invitrogen) in a 5% CO2 humidified atmosphere. The medium was changed every three days, to ensure a constant cell growth (Tsuchiya et al., 1980).

Exposure system to gases

The exposure chambers (EC) were prepared as described previously (Laval-Gilly et al., 2000, Klestadt et al., 2002). Briefly, the ECs were 75 cm2 dishes allowing

Results

The ability to induce oxidative stress in THP-1 cells was first determined by measuring lipid peroxidation products after 30 min of ozone exposure (0.5 ppm). This parameter was also measured for cells exposed to medical air (negative control) and after a treatment by hydrogen peroxide (0.5 mM for 24 h) which is known to induce an oxidative stress as positive control (Fig. 1). No significant difference of TBARs levels were observed between non-exposed cells and cells exposed to medical air which

Discussion

Ozone concentration in urban air can exceed 0.8 ppm in high pollution conditions (e.g. hot sunny climate industrial cities), while normal levels are generally below 0.1 ppm (Mustafa, 1990). Moreover, several studies concerning the ozone effects (from 0.1 ppm to 1 ppm) on different cell types have been realized (Becker et al., 1991, Laval-Gilly et al., 2000, Janic et al., 2003). For example in THP-1 cells, 0.5 ppm of ozone induces a decrease of mobility (Laval-Gilly et al., 2000). In that way it was

Acknowledgment

We thank V. Burgun, J.J. Hascoët and J. Kino for their technical assistances.

References (47)

  • D. Klestadt et al.

    Modification of membrane markers on THP-1 cells after ozone exposure in the presence or absence of fMLP

    Toxicology in Vitro

    (2004)
  • D.L. Laskin et al.

    Role of macrophages and inflammatory mediators in chemically induced toxicity

    Toxicology

    (2001)
  • P. Laval-Gilly et al.

    A new approach to evaluate toxicity of gases on mobile cells in culture

    Journal of Pharmacological and Toxicological Methods

    (2000)
  • P. Montuschi et al.

    Ozone-induced increase in exhaled 8-isoprostane in healthy subjects is resistant to inhaled budesonide

    Free Radical Biology and Medicine

    (2002)
  • I.S. Mudway et al.

    Ozone and the lung: a sensitive issue

    Molecular Aspects of Medicine

    (2000)
  • M.G. Mustafa

    Biochemical basis of ozone toxicity

    Free Radical Biology and Medicine

    (1990)
  • W.A. Pryor

    Mechanisms of radical formation from reactions of ozone with target molecules in the lung

    Free Radical Biology and Medicine

    (1994)
  • W.A. Pryor et al.

    The cascade mechanism to explain ozone toxicity: the role of lipid ozonation products

    Free Radical Biology and Medicine

    (1995)
  • I.M. Rietjens et al.

    The role of glutathione and changes in thiol homeostasis in cultured lung cells exposed to ozone

    Toxicology

    (1985)
  • I.M. Rietjens et al.

    Glutathione pathway enzyme activities and the ozone sensitivity of lung cell populations derived from ozone exposed rats

    Toxicology

    (1985)
  • D. Ritter et al.

    In vitro exposure of isolated cells to native gaseous compounds—development and validation of an optimized system for human lung cells

    Experimental and Toxicologic Pathology

    (2001)
  • F.Q. Schafer et al.

    Redox environment of the cell as viewed through the redox state of the glutathione disulfide/glutathione couple

    Free Radical Biology and Medicine

    (2001)
  • H. Sies et al.

    Glutathione disulfide (GSSG) efflux from cells and tissues

    Methods in Enzymology

    (1984)
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