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J Appl Physiol 83: 707-711, 1997;
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Journal of Applied Physiology
Vol. 83, No. 3, pp. 707-711, September 1997
ENVIRONMENT

In vivo exposure to ozone produces an increase in a 72-kDa heat shock protein in guinea pigs

Wei Yi Su and Terry Gordon

Institute of Environmental Medicine, New York University Medical Center, Tuxedo, New York 10987

ABSTRACT
INTRODUCTION
MATERIALS AND METHODS
RESULTS
DISCUSSION
ACKNOWLEDGEMENTS
FOOTNOTES
REFERENCES


ABSTRACT

Su, Wei Yi, and Terry Gordon. In vivo exposure to ozone produces an increase in a 72-kDa heat shock protein in guinea pigs. J. Appl. Physiol. 83(3): 707-711, 1997.---Although several lines of evidence have suggested that oxidizing agents can induce heat shock proteins (HSPs) in vitro, little is known about the induction of HSPs during in vivo exposure to oxidants. Guinea pigs were exposed to ozone for 6 h and euthanized up to 72 h later. Proteins from lavage cells and lung tissue were characterized by immunoblotting with 72- and 73/72-kDa HSP monoclonal antibodies. Although 73-kDa HSP was expressed constituitively in lung tissue, it was not affected by ozone. In contrast, 72-kDa HSP was significantly increased in lavage cells and lung tissue of animals exposed to 0.4 and 0.66 parts/million of ozone. Both heat treatment and arsenite induced 72-kDa HSP in cultured alveolar macrophages. The increase in 72-kDa HSP in the lavage cell pellet peaked at 24 h after ozone, whereas the influx of polymorphonuclear leukocytes peaked at 4 h. Examination of the induction of HSPs by ozone may provide clues to the development of ozone tolerance in humans and animals.

tolerance; adaptation; lung; macrophage


INTRODUCTION

THE HEAT SHOCK or stress response is a conserved physiological response of cells to injury. This response is characterized by the de novo synthesis of so-called heat shock/stress proteins (HSPs), which are categorized by their apparent molecular weight on polyacrylamide electrophoresis gels (20, 23). The term HSP 70 family is often used in the literature to collectively address a group of gene products that is induced by heat and other stress-inducing agents and has been widely studied (20, 22, 26). In most mammals, 73-kDa HSP is constituitively expressed, whereas 72-kDa HSP, an inducible form, is present at a much lower level in primates under normal conditions. A variety of stress-inducing agents, including heat, transition metals, and amino acid analogs, has been reported to activate 72-kDa HSP expression (3). Another broadly defined inducer of 72-kDa HSP is oxidative stress, which encompasses many chemical and physical agents such as hydrogen peroxide (15), hydroxyquinoline (3), ischemia-reperfusion (6), anoxia-reoxygenation (6), and gamma irradiation (13).

A function for 72-kDa HSP has been proposed under both physiological and pathological conditions. Transient expression during development suggests a role in cell differentiation and proliferation (9). There is also in vitro evidence that 72-kDa HSP is involved in the onset of adaptation or tolerance to heat and other environmental stresses. The phenomenon of HSPs in adaptation/tolerance is defined originally from the finding that the treatment of organisms with a sublethal dose of heat confers on them a resistance to a subsequent exposure to a normally lethal temperature. It is now understood that 72-kDa HSP binds to proteins to prevent denaturation and to facilitate their recovery after stress (5). More recent studies with transgenic animal models and transfection of cells in vitro have demonstrated the effects that overexpression of 72-kDa HSP confers on animal or cell resistance to subsequent stress condition (14, 19). Similarly, inhibition of 72-kDa HSP results in an increased sensitivity to heat (8). Therefore, these studies suggest a clear role for HSP 70 as a protective mechanism in cells responding to environmental stresses.

Ozone is a ubiquitous environmental pollutant, and acute exposure to this oxidant gas causes a number of concentration-dependent alterations in the mammalian respiratory tract. The sequelae of the oxidative stress produced by ozone include lipid peroxidation, generation of free radicals, and alterations in antioxidants (10). Pryor and Church (16, 17) have demonstrated that aldehydes, hydrogen peroxide, organic radicals, and hydroxyl radical are among the toxic mediators generated by ozone. Interestingly, some of these reactive oxygen species have been shown to elicit a heat shock response in cells and animals. More specifically, hydrogen peroxide and the hydroxyl radical are strong inducers of 72-kDa HSP in cells and animals. Given that hydrogen peroxide and the hydroxyl radical are present in the process of ozone-initiated oxidative stress, it is reasonable to propose that in vivo ozone exposure may also elicit 72-kDa HSP expression in the lung. On the basis of the understanding of the role of HSPs in the development of tolerance/adaptation in a spectrum ranging from bacteria to mammal, we speculate that HSP 70 could play an important role in ozone-induced tolerance. To explore these possible mechanisms, we examined whether in vivo ozone exposure induces HSP 72/73 in the respiratory tract of the guinea pig.


MATERIALS AND METHODS

Animals and exposure. Male, viral antibody-free Hartley guinea pigs (Charles River Breeding Laboratories, Kingston, NY), weighing 300-400 g, were housed in polycarbonate cages (within isolation units supplied with high-efficiency particulate-filtered air) in a temperature- and humidity-controlled room. Food and water were provided ad libitum.

Ozone was generated by passing ultrapure 0.5% oxygen-balance argon through an ozone generator (Ozonizer model 25, Erwin Sander). Exposures were conducted in a 56-liter Plexiglas chamber with guinea pigs separated by oxidant-resistant wire caging. Ozone concentrations were monitored continuously with an ozone monitor (model 8810, Monitor Labs, San Diego, CA). The ozone monitor was calibrated with a US Environmental Protection Agency-traceable ozone calibrator (model 8850, Monitor Labs). Temperature and humidity were checked periodically with a probe-type thermo/hygrometer (Omega, Stanford, CT).

Guinea pigs were exposed to 0.2, 0.4, or 0.66 parts/million (ppm) ozone for 6 h. Animals were euthanized at 0, 4, 24, 48, and 72 h after exposure for a time-course study and at 24 h for a dose-response study. Control guinea pigs were exposed under identical conditions to air filtered with activated charcoal and a high-efficiency particulate air filter. The lungs of naive (i.e., unexposed) animals were lavaged to collect cells for examining the in vitro response to heat shock and sodium arsenite.

Sample collection. Guinea pigs were anesthetized by injection of ketamine (100 mg/kg im) and xylazine (15 mg/kg im) and exsanguinated by transecting the aorta and vena cava. The diaphragm was incised, and the lungs were allowed to collapse. The lungs were lavaged in situ with six volumes of phosphate-buffered saline without Ca and Mg (GIBCO-BRL, Bethesda, MD). For each animal, the six recovered lavage samples were pooled, and aliquots were taken for total cell count and for cell differential slides prepared by cytocentrifugation. Cells were stained with Giemsa (Sigma Chemical, St. Louis, MO), and at least 200 cells/animal were counted by light microscopy (×1,000 oil-immersion lens). After the lavage procedure, two pieces of tissue were cut from the peripheral region of both sides of the lung and frozen at -70°C. For each animal, both pieces of lung tissue were pooled together and homogenized.

Gel electrophoresis and Western blotting of 72- and 73-kDa HSP. Lavaged cells (n = 4 at each time point and dose) and lung tissue (n = 4 at each time point and dose, except n = 2 at the 48- and 72-h time points) were lysed in Laemmli buffer (tissue sections were first homogenized manually in a glass-Teflon homogenizer) and solubilized by sonicating and boiling for 5 min. The cell and tissue lysates were centrifuged at 2,000 g for 5 min, and the supernatants were stored at -70°C. Protein concentrations of all samples were determined by the Lowry microprotein assay kit (Sigma Chemical) with bovine serum albumin as the standard. An equal amount of protein (40 µg/lane) for each sample was separated by a discontinuous gel electrophoresis system (Bio-Rad, Richmond, CA) with 4% stacking and 7.5% sodium dodecyl sulfate-polyacrylamide gel elctrophoresis (SDS-PAGE) gels by using piperazine diacrylamide. Prestained protein markers were used to monitor the efficiency of transfer of proteins from the polyacrylamide gel to a nitrocellulose membrane (Bio-Rad). The membranes were immunoblotted for 1 h with monoclonal antibodies C92 or N27 (1:1,000). The monoclonal antibodies recognizing the inducible 72-kDa HSP (C92) or the HSP 72/73 (N27) were a gift (Dr. W. J. Welch, University of California, San Francisco; Ref. 24) or purchased from StressGen (Vancouver, BC). The HSP immunoreactive antibodies were visualized by using a goat anti-mouse immunoglobulin G as secondary antibody conjugated with alkaline phosphatase (Organon Teknika, West Chester, PA) by using 5-bromo-4-chloro-3-indoyl phosphate/nitroblue tetrazolium (Sigma Chemical) as the substrate. To quantify the relative HSP expression, blots were scanned (HP ScanJet IIcx, Hewlett-Packard) and quantified with imaging software (BandLeader 2.0, Tel Aviv, Israel). Band densities of protein samples from air-exposed animals were defined as 100%. At least three samples were assessed for each group.

In vitro treatment of alveolar macrophages. Alveolar macrophages were collected by lung lavage (as described above) and purified by adherence for 1 h, followed by washing with sterile, pyrogen-free phosphate-buffered saline (GIBCO). Macrophages (2 × 106) were cultured with RPMI-1640 (GIBCO) in 37-mm petri dishes and treated with 5, 20, 60, 100, or 200 µM sodium arsenite (Sigma Chemical) for 3 h or heated for 20 min at 44°C. After treatment, the cells were incubated at 37°C for 18 h (arsenite-treated cells were first washed). Cells were lysed in Laemmli buffer, and proteins from cell lysates were separated by SDS-PAGE and immunoblotted by using the anti-HSP 72 antibody as described above. Total cell protein was also visualized by silver staining of an identical SDS-PAGE gel that was run in parallel with the gel used for Western blotting.

Statistics. Data are means ± SE. Statistical differences among groups were analyzed with a one-factor analysis of variance. A Dunnett's two-tailed test was used in a post hoc analysis comparing values from ozone groups to the values from the air group. A P value <=  0.05 was considered statistically significant.


RESULTS

The effect of ozone on the in vivo expression of 72- and 73-kDa HSP was assessed in lavage cells and in lung tissue. Western blot analysis demonstrated that 72-kDa HSP protein expression was barely detectable in the lavage cell pellet or lung tissue of air-exposed animals. Exposure to ozone had a dose-dependent and time-dependent effect on 72-kDa HSP expression in both the lavage cell pellet and lung tissue. At 0 and 4 h, 72-kDa HSP was increased (50 and 245%, respectively, P < 0.05) in the lavage cell lysate of animals exposed to 0.66 ppm ozone for 6 h (Fig. 1). Induction of 72-kDa HSP in the lavage cells reached a peak at 24 h (366% increase) and returned to near-control values by 48 h after ozone exposure. Exposure to 0.4 and 0.66 ppm, but not 0.2 ppm, ozone induced significant increases in the 72-kDa HSP in the cell lysate (Fig. 2). In lung tissue, 72-kDa HSP was also significantly increased at 24 h (192%) after exposure to 0.66 ppm ozone, and this enhanced 72-kDa HSP expression in lung tissue appeared to last longer than that in cell lysates (Fig. 3). The level of 72-kDa HSP in lung tissue of ozone-exposed animals was still higher than control values at 72 h after exposure. As in the lavage cell lysates, a concentration-response relationship was observed for 72-kDa HSP in lung tissue (Fig. 4). Unlike the effect of ozone on 72-kDa HSP, there were no significant changes in 73-kDa HSP in either lavaged cell lysates or lung tissue at any postexposure time or ozone concentration (data not shown).


Fig. 1. Temporal induction of 72-kDa heat shock protein (HSP; bottom) in lavage cells of guinea pigs exposed to 0.66 parts/million (ppm) ozone for 6 h. Values are means ± SE. Air, high-efficiency particulate air. Proteins were analyzed by sodium dodecyl sulfate-polyacrylamide gel electrophoresis (SDS-PAGE) and Western blot (top) with monocolonal antibody (MAb) to 72-kDa HSP and semiquantified by scanning of band density. Each lane represents an individual animal. * Significantly different, P <=  0.05.
[View Larger Version of this Image (42K GIF file)]


Fig. 2. Bottom: effect of ozone concentration on 72-kDa HSP induction in lavage cells. Values are means ± SE. Top: samples (each lane represents an individual animal) collected at 24 h after exposure to 0.2-0.66 ppm ozone for 6 h. * Significantly different, P <= 0.05.
[View Larger Version of this Image (38K GIF file)]


Fig. 3. Bottom: temporal induction of 72-kDa HSP in lung tissue of guinea pigs exposed to 0.66 ppm ozone for 6 h. Values are means ± SE. Top: samples (each lane represents an individual animal) analyzed by Western blot with MAb to 72-kDa HSP. * Significantly different, P <=  0.05.
[View Larger Version of this Image (30K GIF file)]


Fig. 4. Bottom: effect of ozone concentration on 72-kDa HSP induction in lung tissue. Values are means ± SE. Top: samples (each lane represents an individual animal) collected at 24 h after exposure to 0.2-0.66 ppm ozone for 6 h. * Significantly different, P <= 0.05.
[View Larger Version of this Image (35K GIF file)]

Guinea pig alveolar macrophages treated in vitro with sodium arsenite showed a concentration-dependent induction of 72-kDa HSP in the range of 5 to 200 µM (Fig. 5, bottom). Heat treatment of alveolar macrophages at 44°C for 20 min also produced an increase in 72-kDa HSP expression. The induction of a 72-kDa protein by arsenite in macrophages was even detectable on SDS-PAGE gels visualized with a silver stain (Fig. 5, top).


Fig. 5. Induction of 72-kDa HSP in guinea pig alveolar macrophages in vitro by either heat (44°C, 20 min) or arsenite (5-200 µM). Top: SDS-PAGE gel visualized with silver staining. Arrow, induction of a protein band at 72 kDa (72). Bottom: immunoblot of gel run in parallel with top gel.
[View Larger Version of this Image (72K GIF file)]

As shown in Fig. 6, polymorphonuclear leukocytes (PMNs) in lavage fluid peaked at 4 h and returned to near control levels at 24 and 48 h after ozone exposure. Monocytes/macrophages were the major cell population and comprised >84% of the total lavage cells at all time points except at 4 h after exposure (42% of total lavage cells).


Fig. 6. Cellular profile in lavage fluid of guinea pigs exposed for 6 h to 0.66 ppm ozone. Lavage cells were prepared by cytocentrifugation and stained with Giemsa. At least 200 cells/animal were counted under light microscopy (×1,000). PMNs, polymorphonuclear leukocytes. * Significantly different, P <=  0.05.
[View Larger Version of this Image (24K GIF file)]


DISCUSSION

The present study has shown that exposure to ozone can induce the expression of a member of the HSP 70 family in an in vivo animal model. Levels of the 72-kDa HSP form were significantly induced by exposure to ozone in a dose- and time-dependent manner. Although 73-kDa HSP was constituitively expressed in all guinea pig lungs examined, it was not altered by exposure to ozone.

The mechanism underlying the induction of 72-kDa HSP by in vivo exposure to ozone is not known, but we speculate that oxidative stress may play a role. Hydrogen peroxide and hydroxy radical have been reported to induce members of the HSP 70 family in macrophages and other cells (15). Other oxidative stressors such as hydroxyquinoline (3), ischemia-reperfusion (14), anoxia-reoxygenation (6), and gamma irradiation (13) have also been reported to induce the expression of HSPs in vivo or in vitro. Thus states of imbalance in oxidants/antioxidants may underlie the observed inductions in the HSP 70 family of gene products. We speculate that oxidative stress produced by ozone may be responsible for the observed 72-kDa HSP induction in guinea pig lung. Ozone is thought to exert its toxic effects either by interacting directly with cell membranes or generating secondary products that are often more reactive than ozone itself. Moreover, hydrogen peroxide, hydroxy radical, superoxide radical, and an array of ozonides are among the secondary products generated by resident and transient respiratory cells activated by ozone exposure (16, 17). Thus oxidative stress originated from activated pulmonary inflammatory cells may participate in the induction of HSPs. This indirect induction of 72-kDa HSP by ozone-initiated inflammation may be critical because direct exposure of alveolar macrophages and transformed human airway epithelial cells to ozone in vitro does not elicit HSP induction (4, 21).

On repeated exposure, the mammalian respiratory tract is known to acquire tolerance to some of the adverse effects typically observed after a single exposure to ozone. Although changes in levels of antioxidants occurring after ozone exposure may contribute to the development of ozone-induced adaptation, we hypothesize that 72-kDa HSP may also play a role. In addition to the lines of research that have provided strong evidence that members of the HSP 70 gene family are essential for homeostasis of cellular environment (5), many in vitro studies suggest that HSP 70 may be important for protection of cellular function during environmental stress. For example, expression of HSP 70 by transfection of rat fibroblasts or by microinjection into Chinese hamster ovary cells confers heat resistance to these cells (12). Competitive inhibition of HSP 70 gene products also causes thermosensitivity in Chinese hamster ovary cells (8). Comparatively few studies have examined the role of HSPs in the development of tolerance in vivo. Ribeiro et al. (18) have reported that induction of HSP 70 by sodium arsenite in rat lung protects rats against sepsis. Plumier et al. (14) have demonstrated that overexpression of human HSP 70 in transgenic mice significantly improves the recovery from ischemic myocardial injury. These observations provide convincing evidence that an increased level of HSP 70 expression is correlated with the acquisition of resistance to environmental stress. Thus the increased level of 72-kDa HSP expression observed in the present study may be indicative of an adaptive response to protect the respiratory tract from repeated exposure to ozone.

The quick induction and the pattern of 72-kDa HSP production in the lavage cells of ozone-exposed animals are compatible with the features of development of adaptation to ozone, which have been characterized as being quick in onset and short lasting (2, 7, 25). The peak induction of 72-kDa HSP in the lavage cell pellet occurred at 24 h after ozone exposure. Expression of 72-kDa HSP in the lavage cell pellet returned to near-baseline values by 72 h after exposure. The finding of a small elevation in 72-kDa HSP in lung tissue at 72 h, but not in the lavage cell pellet, suggests a difference in kinetics in these two compartments. The rapid decline of HSP expression in the cell pellet may have resulted from a more rapid turnover of 72-kDa HSP in that cell population. The macrophages, PMNs, lymphocytes, and eosinophils present as free cells in the alveolar spaces have a shorter half-life than epithelial lining cells and vascular endothelial cells in the lung. The transient nature of these free cells may be responsible for the more rapid decline in the lavage cell pellet.

This study did not identify the cell type(s) responsible for the increase in 72-kDa HSP in the lavage cell pellet. Although PMNs were significantly increased after exposure, the major infiltration of neutrophils was observed at 4 h after exposure, whereas the peak induction in 72-kDa HSP occurred at 24 h. Despite the fact that this temporal difference does not exclude the possible contribution of PMNs, it is likely that other lavage cells are involved in the induction of 72-kDa HSP by ozone. As visualized on silver-stained gels, in vitro treatment of alveolar macrophages with heat or sodium arsenite confirmed that 72-kDa HSP is the major stress protein produced by macrophages. Although this may provide indirect evidence that macrophages play an important role in the increased expression of 72-kDa HSP in the lavage cell pellet of ozone-exposed animals, immunohistochemical studies at the light or electron microscopic level would be more appropriate in determining the relative contribution of macrophages, PMNs, and eosinophils.

As demonstrated in primates by Welch and Suhan (24), a low-level expression of 72-kDa HSP, the inducible form of the HSP 70 gene family, was observed in guinea pig lung. Blake et al. (1) have speculated that HSP 70 might play an important role in the homeostasis of lung cells. An alternate explanation of its low-level expression in lung tissue may be that the respiratory system is under constant "stress" during its direct interaction with the outside environment, even though this interaction is part of its normal physiological condition. In the present study, the additional environmental stress produced by the in vivo exposure to an oxidant gas such as ozone led to an induction of 72-kDa HSP in lavage cells (4.6-fold) and in lung tissue (2.9-fold). Examination of the induction of HSPs by in vivo ozone exposure may provide clues to the development of tolerance in ozone-exposed human subjects and animals.


ACKNOWLEDGEMENTS

The authors thank Dr. W. J. Welsh of the University of California, San Francisco, for the generous gift of antibodies and Dr. C. Miller for expert advice in protein electrophoresis.


FOOTNOTES

   This work was supported by National Institute of Environmental Health Sciences Grants ES-00260 and ES-04947. T. Gordon is the recipient of a Research Career Development Award from the National Institute of Environmental Health Science (ES-0256).

   Present address of W. Y. Su: Pulmonary Toxicology Branch, Environmental Protection Agency, Mail Drop-82, Research Triangle Park, NC 27711.

Address for reprint requests: T. Gordon, Dept. of Environmental Medicine, New York Univ. School of Medicine, Long Meadow Rd., Tuxedo, NY 10987.

Received 26 July 1996; accepted in final form 23 April 1997.


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