In vivo ozone exposure induces antioxidant/stress-related responses in murine lung and skin

Lung and skin are the organs directly exposed to environmental pollution. Ozone (O(3)) is a toxic, oxidant air pollutant, and exposure has been shown to induce antioxidant depletion as well as oxidation of lipids and proteins within the outermost skin layer (stratum corneum) and the lung respiratory tract lining fluids (RTLFs). To further define skin and lung responses to O(3) exposure, SKH-1 hairless mice were exposed to either 0.8 ppm of O(3) (a level occasionally reached in very polluted areas) or ambient air 6 h/day for 6 consecutive days. O(3) exposure resulted in the depletion of alpha-tocopherol in lung and plasma and induction in both skin and lung of heme oxygenase 1, cyclooxygenase 2, and proliferating cell nuclear antigen. O(3)-exposed animals showed a similar extent of upregulation of COX-2 and PCNA in lung and skin, whereas HO-1 was more responsive in skin than in lung (7-fold induction vs. 2-fold induction). In addition to these measures of response to oxidative stress, O(3) exposure led to the activation of nuclear factor kappaB measured as IkappaBalpha phosphorylation in both tissues. We conclude that in this model, O(3) at high pollutant levels is able to affect both lung and skin biology, inducing depletion of alpha-tocopherol and inducing stress-related responses in both skin epidermis and respiratory tract epithelium.     

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

Ozone is so reactive that it can be predicted to be entirely consumed as it passes through the first layer of tissue it contacts at the lung/air interface. This layer includes the lung lining fluid (tracheobronchial surface fluid and alveolar and small airway lining fluid) and, where the lung lining fluid is thin or absent, the membranes of the epithelial cells that line the airways. Therefore, the biochemical changes that follow the inhalation of ozone must be relayed into deeper tissue strata by a cascade of ozonation products. Lipid ozonation products (LOP) are suggested to be the most likely species to act as signal transduction molecules. This is because unsaturated fatty acids are present in the lipids in both the lung lining fluid and in pulmonary cell bilayers, and ozone reacts with unsaturated fatty acids to produce ozone-specific products. Further, lipid ozonation products are finite in number, have structures that are predictable from the Criegee ozonation mechanism, and are small, diffusible, stable (or metastable) molecules. Preliminary data show that individual LOP cause the activation of specific lipases, which trigger the release of endogenous mediators of inflammation.     

Implications of the kynurenine pathway and quinolinic acid in Alzheimer's disease

Summary

Ozone, though not a free radical species, mediates its toxic effects through free radical reactions as a consequence of its high redox potential. Upon inspiration the first physical interface encountered by ozone is a thin layer of aqueous material, the epithelium lining fluid (ELF) which overlays, and is partially derived from, the underlying pulmonary epithelium. ELF is the first physical interface encountered by ozone and the majority of its primary actions are confined to this compartment. ELF contains a range of antioxidants, including the small molecular weight antioxidants: uric acid (UA), ascorbic acid (AH₂) and reduced glutathione (GSH). These compounds are present in large quantities and display high intrinsic reactivities toward ozone, consistent with their role as sacrificial substrates in this setting. In this paper we examine the concept that antioxidants, in ELF, represent the first tier of defence against the oxidizing effects of ozone. Since the concentration of these antioxidants appears to differ between individuals, we propose that these protective substances may dictate, in part, an individual's sensitivity to oxidizing air pollutants such as ozone.     

Ozonation of lysozyme in the presence of oleate in reverse micelles of sodium di-2-ethylhexylsulfosuccinate.

Ozone is shown to react with lysozyme in reverse micelles formed by 0.1 M sodium di-2-ethylhexylsulfosuccinate and 1.2-3 M water (pH 7.4) in isooctane solvent. The reaction of ozone is assessed by the oxidation of tryptophan residues in the protein to N-formylkynurenine. Cosolubilization of oleate in lysozyme-containing reverse micellar solutions at concentrations of 0.5-10 mM results in a progressive inhibition (19% to 82%) of the oxidation of tryptophan residues with a concentration for 50% inhibition around 2 mM. At this concentration of oleate, the magnitude of inhibition is independent of the micelle size and concentration, the overall interfacial area of reverse micelles, and the amount of ozone employed. These findings are discussed in terms of competitive reactions of ozone with unsaturated fatty acids and proteins in the lung lining fluid and in biological membranes.     

A Historical Overview of the Ozone Exposure Problem

Ozone can be found in essentially all locations in the troposphere. Too much exposure of vegetation and humans to this potent oxidizing gas can prove toxic. Reports of human toxicity to ozone first appeared in the 1800's from accidental occupational exposures when ozone was first discovered. Ozone was recognized as damaging field vegetation with a report of altered leaf morphology in grapes in the 1950s. Ozone is the major oxidant component in photochemical smog, and is produced by reactions of volatile organic compounds and oxides of nitrogen with sunlight present. Soon after the inception of the U.S. Environmental Protection Agency (US EPA), the Agency set a general “oxidants” standard (which included ozone) in 1971. A primary standard was created to protect human health and a secondary standard to protect against agricultural losses, ecological damage, and other losses. Ozone concentrations have decreased steadily over the last two decades in some areas of the U.S., but have increased in other areas. Several aspects of ozone exposure need further characterization, including better determination of rural concentrations and the relationship of outdoor to indoor concentrations. Ozone is one of the six criteria air pollutants requiring a formal reexamination of the new findings of effects on health and vegetation on a periodic basis, a process that leads to the publication of an US EPA criteria document. As a result of further study concerning ozone effects, significant changes were made to pollution standards in 1979 and 1997. This toxicant has remained a major air pollutant of concern in the U.S. despite regulation and intense study over several decades.     

Chemical carcinogenesis and toxicity models: Matching complexity to objectives

Mathematical models predicting tissue doses of chemical toxicants can be either highly complex or simple, depending upon the end results needed. As an example of a highly complex mathematical model, the Miller Model of the distribution of reactive gases in human and animal lungs is described. The Miller Model accounts for the convection, the radial and axial diffusion, and the chemical reactions of gases as an inhaled breath passes down the airways. The geometry and physiology of human and animal lungs are used to calculate the convection and diffusion likely in each generation or bifurcating series of airways commencing with the trachea and extending 24 generations in humans. The chemical reactivity of ozone, an air pollutant, is accounted for by simulating second-order chemical reactions with the fluid lining materials of the lung and tissue biological molecules. The flux of ozone into three compartments (pulmonary tissue, overlying liquid layer and capillary blood) in each generation of the lung is calculated to provide molecular doses of ozone reaching each region of the lung. These results of calculated molecular dose are then used to construct dose-response curves for a variety of biological endpoints. A much simpler model is also described which recognizes the saturable or Michaelis-Menten type of kinetics controlling the removal of nickelous ion (nickel) from the lung. This model is used to calculate the chronic lung burden of the human lung for occupational, environmental and cigarette smoking exposure scenarios. In both the complex Miller Model and the simpler nickel lung burden model, the results can be used to calculate molecular doses at the potential site of action of these environmental chemicals and to unify a wide variety of studies. The predictions made are more likely to be valid since multiple investigators using a variety of animal species have participated in generation of the primary data. As a methodology, mathematical modeling based on physiological, physicochemical and anatomical principles provides a means of eliminating non-scientific considerations from the important process of regulating and recognizing toxic or cancer causing chemicals in the human environment.     

Review of the genotoxicity of ozone.

Ozone is a powerful oxidant, reactive to biomolecules. In aqueous solution it decomposes to give hydrogen peroxide, superoxide and hydroxy radicals which can take part in secondary reactions. Ozone is a disinfectant that inactivates both viruses and bacteria. Although other reactions are primarily responsible for the inactivation, cellular DNA is also damaged. Ozone is genotoxic to microorganisms, plants and cell cultures in vitro. The results from in vivo cytogenetic studies with laboratory animals after inhalation exposure are contradictory. Chromosome aberrations in lymphocytes, but not SCEs, have been demonstrated in Chinese hamsters but not in mice. Chromatid deletions were induced in pulmonary macrophages in rats. No cytogenetic effects have been reported for bone marrow cells or spermatocytes. The few experimental and epidemiological studies with human subjects do not allow a conclusion on the cytogenetic effects of ozone in lymphocytes in humans. No life-long cancer studies have been performed with ozone. However, after 4 and 6 months of inhalation exposure, lung adenomas were induced in strain A/J mice, but not in Swiss-Webster mice.     

Uncovering hidden genetic variation in photosynthesis of field‐grown maize under ozone pollution

Ozone is the most damaging air pollutant to crops, currently reducing Midwest US maize production by up to 10%, yet there has been very little effort to adapt germplasm for ozone tolerance. Ozone enters plants through stomata, reacts to form reactive oxygen species in the apoplast and ultimately decreases photosynthetic C gain. In this study, 10 diverse inbred parents were crossed in a half‐diallel design to create 45 F₁ hybrids, which were tested for ozone response in the field using free air concentration enrichment (FACE). Ozone stress increased the heritability of photosynthetic traits and altered genetic correlations among traits. Hybrids from parents Hp301 and NC338 showed greater sensitivity to ozone stress, and disrupted relationships among photosynthetic traits. The physiological responses underlying sensitivity to ozone differed in hybrids from the two parents, suggesting multiple mechanisms of response to oxidative stress. FACE technology was essential to this evaluation because genetic variation in photosynthesis under elevated ozone was not predictable based on performance at ambient ozone. These findings suggest that selection under elevated ozone is needed to identify deleterious alleles in the world's largest commodity crop.     

Depletion of urate in human nasal lavage following in vitro ozone exposure

Ozone, a strong oxidant present in summer smog, is thought to primarily react with antioxidant molecules found in the epithelial lining fluid of the respiratory tract. In humans, as much as 40% of inhaled ozone can be removed in the nasal cavity where the major extracellular antioxidant has been identified as uric acid. The present study was undertaken to examine urate/oxidant interactions in human nasal lavage fluid following in vitro exposure to ozone at concentrations relevant to the U.K. Lavage fluid was collected from 8 volunteers using a modified Foley catheter which permits prolonged contact of isotonic saline with the anterior nasal cavity. Nasal lavage samples in multiwell plates were exposed to ozone at concentrations of 50, 100 and 250 ppb. Samples were removed at intervals from 15 to 240 min following exposure and assayed for uric acid depletion. Uric acid concentrations in the nasal lavage were found to fall from 8.52 (time zero) to 3.99 μM, 0.05 and 0.07 μM after 240 min at 50, 100 and 250 ppb ozone respectively. At a non-environmentally relevant ozone concentration of 1000 ppb, uric acid was completely depleted after 60 min. Regression analysis showed a linear correlation between rate of loss of urate and ozone concentration (R² = 0.97). A novel, non-invasive technique is described to investigate antioxidant compromise and its importance in individual subjects. We conclude that uric acid in nasal lavage samples is scavenged by ozone in a dose and time dependant manner.     

Ozone tolerant maize hybrids maintain Rubisco content and activity during long-term exposure in the field

Ozone pollution is a damaging air pollutant that reduces maize yields equivalently to nutrient deficiency, heat, and aridity stress. Therefore, understanding the physiological and biochemical responses of maize to ozone pollution and identifying traits predictive of ozone tolerance is important. In this study, we examined the physiological, biochemical and yield responses of six maize hybrids to elevated ozone in the field using Free Air Ozone Enrichment. Elevated ozone stress reduced photosynthetic capacity, in vivo and in vitro, decreasing Rubisco content, but not activation state. Contrary to our hypotheses, variation in maize hybrid responses to ozone was not associated with stomatal limitation or antioxidant pools in maize. Rather, tolerance to ozone stress in the hybrid B73 × Mo17 was correlated with maintenance of leaf N content. Sensitive lines showed greater ozone-induced senescence and loss of photosynthetic capacity compared to the tolerant line.     

The role of phytohormone signaling in ozone-induced cell death in plants

Ozone is the main photochemical oxidant that causes leaf damage in many plant species, and can thereby significantly decrease the productivity of crops and forests. When ozone is incorporated into plants, it produces reactive oxygen species (ROS), such as superoxide radicals and hydrogen peroxide. These ROS induce the synthesis of several plant hormones, such as ethylene, salicylic acid, and jasmonic acid. These phytohormones are required for plant growth, development, and defense responses, and regulate the extent of leaf injury in ozone-fumigated plants. Recently, responses to ozone have been studied using genetically modified plants and mutants with altered hormone levels or signaling pathways. These researches have clarified the roles of phytohormones and the complexity of their signaling pathways. The present paper reviews the biosynthesis of the phytohormones ethylene, salicylic acid, and jasmonic acid, their roles in plant responses to ozone, and multiple interactions between these phytohormones in ozone-exposed plants.Key words: cross-talk, ethylene, jasmonic acid, ozone, phytohormones, programmed cell death, salicylic acid, signaling pathways     

ROS perception in Arabidopsis thaliana: the ozone-induced calcium response

Ozone is responsible for more crop losses than any other air pollutant. The changes in gene expression, which occur in plants in response to ozone, have been well characterized, yet little is known about how ozone is perceived or the signal transduction steps that follow. The earliest characterized response to ozone is an elevation in cytosolic-free calcium, which takes place within seconds of exposure. In this study, the calcium response to ozone was investigated in Arabidopsis thaliana seedlings using a variety of fumigation protocols. Ozone elicited distinct calcium responses in the aerial tissue and roots of seedlings. The calcium response in the cotyledons and leaves was biphasic and sensitive to the rate at which the ozone concentration increased. The response in the root was monophasic and insensitive to the rate of increase in ozone concentration. Experiments utilizing inhibitors of antioxidant metabolism demonstrated that the magnitude of the first peak in calcium in the aerial tissues was dependent upon the redox status of the plant. Seedlings were shown to be able to distinguish between ozone and hydrogen peroxide, producing a calcium signal in response to one of these reactive oxygen species (ROS) when they had become refractory to the other. Pre-treatment with ozone altered the calcium response to hydrogen peroxide and vice versa, indicating that the calcium response to a given ROS may reflect the stress history of the plant. These data suggest ROS signalling is more sophisticated than previously realized and raise questions over current models of ozone perception.     

Ecotoxicology of ozone: bioactivation of extracellular ascorbate

The ascorbate pools of the extracellular respiratory lining fluids and the plant apoplast are currently considered as part of the first line of defence against ambient ozone. Ozone is in fact rapidly decomposed by ascorbate, but the only product identified so far (singlet oxygen) is toxic. Peroxy-l-threonic and peroxy-oxalic acids are now derived as further decomposition products on the basis of Criegee-type ozone chemistry. These secondary toxicants may resemble known ozone induced transmitter molecules by participating in signalling events affecting plant and animal innate immunity.     

Ozone enhancement of lower airway allergic inflammation is prevented by gamma-tocopherol

Ozone is a commonly encountered environmental oxidant which has been linked to asthma exacerbation in epidemiological studies. Ozone induces airway inflammation and enhances response to inhaled allergen. It has been suggested that antioxidant therapy may minimize the adverse effects of ozone in asthma. We have previously shown that the antioxidant gamma-tocopherol (gammaT), an isoform of vitamin E, also has anti-inflammatory effects. We employed a Brown Norway rat model of ozone-enhanced allergic responses to test the therapeutic effects of gammaT on O(3)-induced airway inflammation. Ovalbumin (OVA)-sensitized rats were intranasally challenged with 0 or 0.5% OVA on Days 1 and 2, and exposed to 0 or 1 ppm ozone (8 h/day) on Days 4 and 5. Rats were also given 0 or 100 mg/kg gammaT on Days 2 through 5. Pulmonary tissue and bronchoalveolar lavage fluid (BALF) were collected on Day 6. OVA challenge caused increased total cells (267% increase) and eosinophils (4000%) in BALF that was unaffected by ozone exposure. Morphometric evaluation of lung tissue revealed increases in intraepithelial mucosubstances (IM) (300%) and subepithelial eosinophils (400%) in main axial airways. Ozone exposure of allergic rats enhanced IM increases in proximal axial airways (200%), induced cys-leukotrienes, MCP-1, and IL-6 production in BALF, and upregulated expression of IL-5 and IL-13 mRNA. gammaT treatment had no effect on IM increases by allergen, but blocked enhancement by ozone. gammaT attenuated both OVA- or ozone-stimulated eosinophilic infiltration, and increases of BALF cys-leukotrienes, MCP-1, and IL-6, as well as IL-5 and IL-13 mRNA. These data demonstrate broad anti-inflammatory effects of a gammaT and suggest that it may be an effective therapy of allergic airway inflammation.     

Inhalation of ozone induces DNA strand breaks and inflammation in mice

Ozone (O3) is a well-known oxidant pollutant present in photochemical smog. Although ozone is suspected to be a respiratory carcinogen it is not regulated as a carcinogen in most countries.The genotoxic and inflammatory effects of ozone were investigated in female mice exposed to ozone for 90 min. The tail moment in bronchoalveolar lavage (BAL) cells from BALB/c mice was determined by the comet assay as a measure of DNA strand breaks. Within the first 200 min after exposure, the BAL cells from the mice exposed to 1 or 2 ppm ozone had 1.6- and 2.6-fold greater tail moments than unexposed mice. After 200 min there was no effect. It could be ruled out that the effect during the first 200 min was due to major infiltration of lymphocytes or neutrophils. Unexpectedly, ozone had no effect on the content of 8-oxo-deoxyguanosine (8-oxo-dG) in nuclear DNA or on oxidised amino acids in the lung tissue. The mRNA level of the repair enzyme ERCC1 was not increased in the lung tissue. Inflammation was measured by the cytokine mRNA level in lung homogenates. An up to 150-fold induction of interleukin-6 (IL-6) mRNA was detected in the animals exposed to 2 ppm ozone compared to the air-exposed control mice. Also at 1 ppm ozone, the IL-6 mRNA was induced. The large induction of IL-6 mRNA in the lung took place after DNA strand breaks were induced in BAL. This does not support the notion that inflammatory reactions are the cause of DNA damage. To determine whether these exposures were mutagenic, Muta Mice were exposed to 2 ppm ozone, 90 min per day for 5 days. No treatment-related mutations could be detected in the cII transgene.These results indicate that a short episode of ozone exposure at five times the threshold limit value (TLV) in US induces lung inflammatory mediators and DNA damage in the cells in the lumen of the lung. This was not reflected by an induction of mutations in the lung of Muta Mice.     

Oxidative burst and cell death in ozone-exposed plants

The phytotoxic air pollutant ozone spontaneously generates reactive oxygen species (ROS) in the leaf apoplast, provokes hypersensitive response-like lesions and induces defence reactions that significantly overlap with pathogen and other oxidative stress responses. Consequently, ozone has been used as a tool to unravel in planta ROS-induced plant defence and cell death mechanisms. Ozone exposure stimulates an oxidative burst in leaves of sensitive plants, resulting in the generation and accumulation of hydrogen peroxide or superoxide anions in distinct species. Accumulation of these ROS precedes the induction of cell death, and both responses co-occur spatially in the periveinal regions of the leaves. The review summarizes some of the recent results that have been obtained concerning the molecular basis of apoplastic ROS production in monocot and dicot species. Signal molecules, in particular ethylene and salicylic acid, control and potentiate the oxidative burst and subsequent cell death in its initiation and propagation phases while jasmonate leads to lesion containment. Amplification mechanisms that result in the production of excess ROS and hypersensitive cell death are discussed as major factors in ozone sensitivity of plant species and cultivars.