Cytochrome P450 2B1 immunoreactivity in bronchiolar and alveolar epithelial cells after exposure of rats to ozone

CAR and PXR expression and inducibility of CYP2B and CYP3A activities in rat and rabbit lungs

Several CYP enzymes are expressed in the lung of mammals but studies on their regulation have been rather neglected. In this study, the CAR and PXR expression and the inducibility of CYP 2B and CYP 3A isoforms in the lung rats and rabbits were investigated. Rats were treated with phenobarbital, clotrimazole or a mixture of dexametasone plus pregnenolone 16alpha-carbonitrile, whereas rabbits were treated with phenobarbital or rifampicin. A low constitutive expression of CAR mRNA was demonstrated by RT-PCR analysis in the lung of rat but not in rabbit. Phenobarbital treatment did not change the CAR expression profiles and did not induce in either rats and rabbits the pulmonary CYP 2B isoforms, as judged by western blot analysis and the marker pentoxyresorufin O-dealkylase and 7-ethoxy-4-trifluoroethylcoumarin O-deethylase activities. On the contrary, these marker activities were strongly induced by phenobarbital in the liver of both species. A low constitutive level of PXR mRNA was also detected by RT-PCR in the lung of rabbit but not in rat. However, also in this case, their expressions were not altered by the administration of strong CYP 3A inducers such as clotrimazole or a mixture of dexametasone plus pregnenolone 16alpha-carbonitrile for the rat and rifampicin or phenobarbital for the rabbit. For the first time, it was demonstrated by RT-PCR that rat lung expresses CYP 3A2, 3A9, 3A18 and 3A23 whereas the rabbit lung expresses the CYP 3A6, the only CYP 3A isoform identified in the rabbit so far. However, notwithstanding the differences observed in the constitutive presence of PXR and CYP 3A transcripts in both species, the above mentioned treatments did not affect in their lungs, unlike their livers, neither the anti-rat 3A immunoreactive proteins nor the CYP 3A marker 7-benzyloxyquinoline O-debenzylase and the 6beta-testosterone hydroxylase activities. The results obtained indicate that the role of CAR and PXR in the lung of rat and rabbit is different from that observed in the liver or other extrahepatic tissues where the induction of the CYP 2B and CYP 3A isoforms is regulated by these receptors.

Respiratory tract toxicity of inhaled hydrogen sulfide in Fischer-344 rats, Sprague–Dawley rats, and B6C3F1 mice following subchronic (90-day) exposure

The goal of this study was to characterize the toxicity of hydrogen sulfide (H2S), including nasal and pulmonary effects, in adult male and female Fischer-344 and Sprague-Dawley rats and B6C3F1 mice. Animals underwent whole-body exposure to 0, 10, 30, or 80 ppm H2S for 6 h/day for at least 90 days. Exposure to 80 ppm H2S was associated with reduced feed consumption during either the first exposure week (rats) or throughout the 90-day exposure (mice). Male Fischer-344 rats, female Sprague-Dawley rats, and female B6C3F1 mice exposed to 80 ppm H2S had depressed terminal body weights when compared with air-exposed controls. Subchronic H2S inhalation did not result in toxicologically relevant alterations in hematological indices, serum chemistries, or gross pathology. Histologic evaluation of the nose showed an exposure-related increased incidence of olfactory neuronal loss (ONL) and rhinitis. ONL occurred following exposure to > or =30 ppm H2S in both sexes of all experimental groups, with one exception, male Sprague-Dawley rats demonstrated ONL following exposure to 80 ppm H2S only. A 100% incidence of rhinitis was found in the male and female B6C3F1 mice exposed to 80 ppm H2S. In the lung, exposure to H2S was associated with bronchiolar epithelial hypertrophy and hyperplasia in male and female Sprague-Dawley rats following exposure to > or =30 ppm H2S and in male Fischer-344 rats exposed to 80 ppm H2S. Our results confirm that the rodent nose, and less so the lung, are highly sensitive to H2S-induced toxicity, with 10 ppm representing the NOAEL for ONL following subchronic inhalation.

Effects of paving asphalt fume exposure on genotoxic and mutagenic activities in the rat lung

Asphalt fumes are complex mixtures of aerosols and vapors containing various organic compounds, including polycyclic aromatic hydrocarbons (PAHs). Previously, we have demonstrated that inhalation exposure of rats to asphalt fumes resulted in dose-dependent induction of CYP1A1 with concomitant down-regulation of CYP2B1 and increased phase II enzyme quinone reductase activity in the rat lung. In the present study, the potential genotoxic effects of asphalt fume exposure due to altered lung microsomal enzymes were studied. Rats were exposed to air or asphalt fume generated under road paving conditions at various concentrations and sacrificed the next day. Alveolar macrophages (AM) were obtained by bronchoalveolar lavage and examined for DNA damage using the comet assay. To evaluate the systemic genotoxic effect of asphalt fume, micronuclei formation in bone marrow polychromatic erythrocytes (PCEs) was monitored. Lung S9 from various exposure groups was isolated from tissue homogenates and characterized for metabolic activity in activating 2-aminoanthracene (2-AA) and benzo[a]pyrene (BaP) mutagenicity using the Ames test with Salmonella typhimurium YG1024 and YG1029. This study showed that the paving asphalt fumes significantly induced DNA damage in AM, as revealed by DNA migration in the comet assay, in a dose-dependent manner, whereas the micronuclei formation in bone marrow PCEs was not detected even at a very high exposure level (1733 mg h/m3). The conversion of 2-AA to mutagens in the Ames test required lung S9-mediated metabolic activation in a dose-dependent manner. In comparison to the controls, lung S9 from rats exposed to asphalt fume at a total exposure level of 479+/-33 mg h/m3 did not significantly enhance 2-AA mutagenicity with either S. typhimurium YG1024 or YG1029. At a higher total asphalt fume exposure level (1150+/-63 mg h/m3), S9 significantly increased the mutagenicity of 2-AA as compared to the control. However, S9 from asphalt fume-exposed rats did not significantly activate the mutagenicity of BaP in the Ames test. These results show that asphalt fume exposure, which significantly altered both phases I and II metabolic enzymes in lung microsomes, is genotoxic to AM and enhances the metabolic activation of certain mutagens through altered S9 content.

The dual effect of the particulate and organic components of diesel exhaust particles on the alteration of pulmonary immune/inflammatory responses and metabolic enzymes

Exposure to diesel exhaust particles (DEP) is an environmental and occupational health concern. This review examines the cellular actions of the organic and the particulate components of DEP in the development of various lung diseases. Both the organic and the particulate components cause oxidant lung injury. The particulate component is known to induce alveolar epithelial damage, alter thiol levels in alveolar macrophages (AM) and lymphocytes, and activate AM in the production of reactive oxygen species (ROS) and pro-inflammatory cytokines. The organic component, on the other hand, is shown to generate intracellular ROS, leading to a variety of cellular responses including apoptosis. There are a number of differences between the biological actions exerted by these two components. The organic component is responsible for DEP induction of cytochrome P450 family 1 enzymes that are critical to the polycyclic aromatic hydrocarbons (PAH) and nitro-PAH metabolism in the lung as well as in the liver. The particulate component, on the other hand, causes a sustained down-regulation of CYP2B1 in the rat lung. The significance of this effect on pulmonary metabolism of xenobiotics and endobiotics remains to be seen, but may prove to be an important factor governing the interplay of the pulmonary metabolic and inflammatory systems. Long-term exposures to various particles including DEP, carbon black (CB), TiO2, and washed DEP devoid of the organic content, have been shown to produce similar tumorigenic responses in rodents. There is a lack of correlation between tumor development and DEP chemical-derived DNA adduct formation. But the organic component has been shown to generate ROS that produce 8-hydroxydeoxyguanosine (8-OHdG) in cell culture. The organic, but not the particulate, component of DEP suppresses the production of pro-inflammatory cytokines by AM and the development of Th1 cell-mediated immunity. The mechanism for this effect is not yet clear, but may involve the induction of heme oxygenase-1 (HO-1), a cellular genetic response to oxidative stress. Both the organic and the particulate components of DEP enhance respiratory allergic sensitization. Part of the DEP effects may be due to a depletion of glutathione in lymphocytes. The organic component, which is shown to induce IL-4 and IL-10 productions, may skew the immunity toward Th2 response, whereas the particulate component may stimulate both the Th1 and Th2 responses. In conclusion, the literature shows that the particulate and organic components of DEP exhibit different biological actions but both involve the induction of cellular oxidative stress. Together, these effects inhibit cell-mediated immunity toward infectious agents, exacerbate respiratory allergy, cause DNA damage, and under long-term exposure, induce the development of lung tumors.

Immunohistochemical evidence for the expression and induction of paraoxonase in rat liver, kidney, lung and brain tissue. Implications for its physiological role

Studies on the localization of paraoxonases (PON's) are of interest because of its involvement in both the detoxication of activated organophosphorus pesticides and in the prevention of peroxidative damage to phospholipids and cholesteryl-esters in LDL and HDL particles and cell membranes during the atherogenic process. In the present study, we have investigated the cellular localization of PON1 by immunohistochemistry in different rat tissues. The protein was mainly detected in the endothelial lining of every tissue studied (liver, kidney, lung and brain). Besides, it was found in hepatocytes from the centrolobular region of the liver, in the glomeruli and basal pole of the proximal convoluted tubule of the kidney, in cells from bronchiolar epithelium and type I pneumocytes of the lung, and in leptomeningeal cells, ependymal cells and ventricular side of choroid plexus cells of the brain. However, neurons and glia lacked immunostaining. After 3-methylcholanthrene induction an increase in the intensity of immunostaining was observed in the same areas, as well as an additional staining in midzonal hepatocytes. On the basis of the tissue distribution observed for PON1, it is proposed that this enzyme might have a function related to the inactivation of oxidative stress by-products (either at a cellular level or blood-vessel wall) and other environmental chemicals. At present it has not yet been established whether the paraoxonase detected in the various tissues is truly a product of the PON1 gene or could represent products of the PON2 or PON3 genes.

Cell-specific loss of cytochrome P450 2B1 in rat lung following treatment with pneumotoxic and non-pneumotoxic trialkylphosphorothioates

This study was designed to test the hypothesis that the reduction in cytochrome P450 (CYP) 2B1 content and activity of rat lung microsomes, following dosing with pneumotoxic trimethylphosphorothioates, results from damage to specific cell types. Of the lung cells exhibiting immunolabelling for CYP2B1, only type I cells showed signs of susceptibility to the pneumotoxins O,O.S-trimethylphosphorothioate and O,S,S-trimethylphosphorodithioate. While most type I cells became necrotic, type II and Clara cells showed no signs of injury, despite their gradual loss of CYP2B1, as detected by immunogold labelling. This loss of labelling was accompanied by a 75% reduction in the immunoreactive CYP2B1 content and an 85% reduction in pentoxyresorufin O-dealkylase activity in lung microsomes. In contrast, the non-pneumotoxic analogue O,O,S-trimethylphosphorodithioate, differing from O,O,S-trimethylphosphorothioate by only the presence of a P = S rather than a P = O moiety, caused an even more rapid fall in pulmonary pentoxyresorufin O-dealkylase activity, but only a slight reduction in the microsomal content of CYP2B1. The recovery of this activity began within 12 hr of dosing. O,O,S-Trimethylphosphorodithioate, which acts as a suicidal inhibitor of pulmonary CYP2B1, did not cause any detectable lung injury or increase in cell division. These results are consistent with the initial reduction in both enzyme content and activity caused by the P = O - containing pneumotoxins resulting, almost entirely, from death of type I cells. Subsequent reductions that occur long after clearance of the toxin may be exacerbated by the onset of mitosis in Clara and type II cells.

Interactions between cytochrome P-450 activities and ozone-induced modulatory effects on endothelial permeability in rabbit lungs: influence of gender

The effects of rabbit exposure to ozone (O(3)) (0.4 ppm for 4 h) on two different cytochrome P-450 (CYP450)-dependent activities were investigated. In turn, the role of CYP450 in the inhibitory effect of O(3) on acetylcholine (ACh)-evoked increase in endothelial permeability was also assessed. Immediately after the period of exposure, rabbits of both sexes were sacrificed and their lungs were extracted. Some lungs were used for preparation of microsomes and measurement of 7-ethoxyresorufin O-deethylase (EROD) and parathion oxidase activities. Other rabbit lungs were isolated and recirculatingly blood-free perfused. Arterial, venous pressures, and lung weight were continuously recorded. Capillary pressure was measured by applying the double occlusion method. Capillary filtration coefficient (K(f,c)) was evaluated by measuring the amount of fluid filtering through the endothelium when vascular pressures were suddenly increased. Dose-response curves to ACh were constructed in air- or O(3)-exposed rabbits. Some animals were pretreated with piperonyl butoxide (PBO), a well-known inhibitor of CYP450. O(3) significantly reduced both EROD and parathion oxidase lung microsomal activities in females, while it had no effect in males. Exposure to O(3) strongly inhibited the ACh-induced increase in K(f,c). Pretreatment with PBO reversed the modulatory effect of O(3) on endothelial permeability in male rabbits, but not in females. It was concluded (1) that inhibition of 2 different CYP450-dependent activities after exposure to 0.4 ppm O(3) for 4 h appears to be a gender-dependent phenomenon, and (2) that CYP450 is probably involved in the O(3)-evoked inhibitory mechanism against ACh-induced increase in endothelial permeability, but only in males.

Cytochrome P450 2E1 in rat tracheobronchial airways: response to ozone exposure

The distal trachea and centriacinus of the lung are primary sites of acute injury during short-term ozone exposure; long-term exposure yields cells in these areas that are resistant to high doses of oxidant gases. Epithelial cells located in primary sites for ozone injury are also targets for chemicals that undergo cytochrome P450 (CYP)-dependent activation. These studies were designed to compare the effects of ozone exposure on pulmonary CYP2E1 in susceptible and nonsusceptible sites within the airway tree of lung. CYP2E1 activity was measured in well-defined regions of airways using p-nitrophenol, a CYP2E1-selective substrate, with HPLC/ electrochemical detection of the p-nitrocatechol. Alterations in distribution of CYP2E1 were evaluated by immunohistochemistry. CYP2E1 activities were highest in the distal bronchioles and minor daughter airways but were much lower in the lobar bronchi/ major daughter airways and trachea. Immediately after short-term ozone exposures (8 h, 1 ppm), CYP2E1 activities were elevated only in the lobar bronchi/major daughter airways. These activities remained above the filtered air control at 1 day but returned to control levels by 2 days. Immunohistochemical assessment of CYP2E1 protein in ozone and filtered air-exposed animals was consistent with the activity measurements. After long-term ozone exposures (90 days, 1 ppm), CYP2E1 activities were decreased in the major and minor daughter airways. These studies indicate that CYP2E1 activities vary substantially by airway level. However, ozone exposure only results in minimal alterations in activity with varying concentration of ozone, length of exposure, and time after exposure in any of the lung subcompartments examined.

Inhibitory effect of sex steroids on guinea-pig airway smooth muscle contractions

We assessed the possible inhibition of airway smooth muscle contraction by progesterone and pregnanolones (5 alpha and 5 beta-reduced). Progesterone and 5 beta-pregnanolone prevented histamine- or carbachol-induced contraction in isolated guinea-pig trachea and potency was related to their respective chemical structure; progesterone was the most potent inhibitor in a concentration-dependent manner. The steroids also exhibited calcium antagonist activities in this tissue as assessed by their action on calcium entry in depolarized preparations; this event involved the immediate blockade of the extracellular calcium influx in the muscle cell membrane, indicating a nongenomic action. Classical GABAA antagonists did not block the progesterone response, implying no involvement of the GABAA-receptor complex. Our results suggest a bronchodilating effect induced by sex steroids, and probably by other related compounds, before the genomic mechanisms take place. This nongenomic action of steroids could have potential therapeutic usefulness in the treatment of asthma.