Interactive effects of cerium oxide and diesel exhaust nanoparticles on inducing pulmonary fibrosis.

Cerium compounds have been used as a fuel-borne catalyst to lower the generation of diesel exhaust particles (DEPs), but are emitted as cerium oxide nanoparticles (CeO2) along with DEP in the diesel exhaust. The present study investigates the effects of the combined exposure to DEP and CeO2 on the pulmonary system in a rat model. Specific pathogen-free male Sprague-Dawley rats were exposed to CeO2 and/or DEP via a single intratracheal instillation and were sacrificed at various time points post-exposure. This investigation demonstrated that CeO2 induces a sustained inflammatory response, whereas DEP elicits a switch of the pulmonary immune response from Th1 to Th2. Both CeO2 and DEP activated AM and lymphocyte secretion of the proinflammatory cytokines IL-12 and IFN-γ, respectively. However, only DEP enhanced the anti-inflammatory cytokine IL-10 production in response to ex vivo LPS or Concanavalin A challenge that was not affected by the presence of CeO2, suggesting that DEP suppresses host defense capability by inducing the Th2 immunity. The micrographs of lymph nodes show that the particle clumps in DEP+CeO2 were significantly larger than CeO2 or DEP, exhibiting dense clumps continuous throughout the lymph nodes. Morphometric analysis demonstrates that the localization of collagen in the lung tissue after DEP+CeO2 reflects the combination of DEP-exposure plus CeO2-exposure. At 4 weeks post-exposure, the histological features demonstrated that CeO2 induced lung phospholipidosis and fibrosis. DEP induced lung granulomas that were not significantly affected by the presence of CeO2 in the combined exposure. Using CeO2 as diesel fuel catalyst may cause health concerns.

Induction of pulmonary fibrosis by cerium oxide nanoparticles.

Cerium compounds have been used as a diesel engine catalyst to lower the mass of diesel exhaust particles, but are emitted as cerium oxide (CeO(2)) nanoparticles in the diesel exhaust. In a previous study, we have demonstrated a wide range of CeO(2)-induced lung responses including sustained pulmonary inflammation and cellular signaling that could lead to pulmonary fibrosis. In this study, we investigated the fibrogenic responses induced by CeO(2) in a rat model at various time points up to 84 days post-exposure. Male Sprague Dawley rats were exposed to CeO(2) by a single intratracheal instillation. Alveolar macrophages (AM) were isolated by bronchial alveolar lavage (BAL). AM-mediated cellular responses, osteopontin (OPN) and transform growth factor (TGF)-ß1 in the fibrotic process were investigated. The results showed that CeO(2) exposure significantly increased fibrotic cytokine TGF-ß1 and OPN production by AM above controls. The collagen degradation enzymes, matrix metalloproteinase (MMP)-2 and -9 and the tissue inhibitor of MMP were markedly increased in the BAL fluid at 1 day- and subsequently declined at 28 days after exposure, but remained much higher than the controls. CeO(2) induced elevated phospholipids in BAL fluid and increased hydroxyproline content in lung tissue in a dose- and time-dependent manner. Immunohistochemical analysis showed MMP-2, MMP-9 and MMP-10 expressions in fibrotic regions. Morphological analysis noted increased collagen fibers in the lungs exposed to a single dose of 3.5mg/kg CeO(2) and euthanized at 28 days post-exposure. Collectively, our studies show that CeO(2) induced fibrotic lung injury in rats, suggesting it may cause potential health effects.

Cerium oxide nanoparticle-induced pulmonary inflammation and alveolar macrophage functional change in rats.

The use of cerium compounds as diesel fuel catalyst results in the emission of cerium oxide nanoparticles (CeO2) in the exhaust. This study characterized the potential effects of CeO2 exposure on lung toxicity. Male Sprague Dawley rats were exposed to CeO2 by a single intratracheal instillation at 0.15, 0.5, 1, 3.5 or 7 mg/kg body weight. At 1 day after exposure, CeO2 significantly reduced NO production, but increased IL-12 production, by alveolar macrophages (AM) in response to ex vivo lipopolysacchride (LPS) challenge, and caused AM apoptosis, through activation of caspases 9 and 3. CeO2 exposure markedly increased suppressor of cytokine signaling-1 at 1-day and elevated arginase-1 at 28-day post exposure in lung cells, while osteopontin was significantly elevated in lung tissue at both time points. CeO2 induced inflammation, cytotoxicity, air/blood barrier damage, and phospholipidosis with enlarged AM. Thus, CeO2 induced lung inflammation and injury in lungs which may lead to fibrosis.

Reactive oxygen species- and nitric oxide-mediated lung inflammation and mitochondrial dysfunction in wild-type and iNOS-deficient mice exposed to diesel exhaust particles.

Pulmonary responses to diesel exhaust particles (DEP) exposure are mediated through enhanced production of reactive oxygen species (ROS) and nitric oxide (NO) by alveolar macrophages (AM). The current study examined the differential roles of ROS and NO in DEP-induced lung injury using C57B/6J wild-type (WT) and inducible NO synthase knockout (iNOS KO) mice. Mice exposed by pharyngeal aspiration to DEP or carbon black particles (CB) (35 mg/kg) showed an inflammatory profile that included neutrophil infiltration, increased lactate dehydrogenase (LDH) activity, and elevated albumin content in bronchoalveolar lavage fluid (BALF) at 1, 3, and 7 d postexposure. The organic extract of DEP (DEPE) did not induce an inflammatory response. Comparing WT to iNOS KO mice, the results show that NO enhanced DEP-induced neutrophils infiltration and plasma albumin content in BALF and upregulated the production of the pro-inflammatory cytokine interleukin 12 (IL-12) by AM. DEP-exposed AM from iNOS KO mice displayed diminished production of IL-12 and, in response to ex vivo lipopolysaccharide (LPS) challenge, decreased production of IL-12 but increased production of IL-10 when compared to cells from WT mice. DEP, CB, but not DEPE, induced DNA damage and mitochondria dysfunction in AM, however, that is independent of cellular production of NO. These results demonstrate that DEP-induced immune/inflammatory responses in mice are regulated by both ROS- and NO-mediated pathways. NO did not affect ROS-mediated mitochondrial dysfunction and DNA damage but upregulated IL-12 and provided a counterbalance to the ROS-mediated adaptive stress response that downregulates IL-12 and upregulates IL-10.

Role of mitochondria in silica-induced apoptosis of alveolar macrophages: inhibition of apoptosis by rhodamine 6G and N-acetyl-L-cysteine.

Induction of apoptosis by silica in alveolar macrophages (AM) may be a critical step in silica-induced lung injury and pulmonary fibrosis. This study investigated the mechanism(s) through which silica induces apoptosis in AM and their production of proinflammatory cytokines. Using N-acetyl-L-cysteine (NAC) for glutathione (GSH) synthesis and removal of reactive oxygen species (ROS), and rhodamine 6G (R6G) to inhibit the mitochondrial-dependent function, this study found that silica-induced apoptosis of rat AM in primary culture is mitochondria dependent and exhibits a mechanism involving ROS generation, increased mitochondrial release of cytochrome c, and the activation of caspase 9, but not caspase 8, activity. Silica-induced apoptosis was accompanied by a lowering of intracellular and mitochondrial GSH (mGSH) and was blocked by pretreatment of cells with NAC or R6G. When cells were exposed to silica and then treated with either NAC or R6G, silica-induced apoptosis was not affected by the blocking agent. In addition, R6G, which inhibited cellular ATP production and mitochondrial ROS generation, had no effect on apoptosis induced by exogenous hydrogen peroxide or superoxide. Pretreatment of cells with NAC or R6G also inhibited silica-induced production of interleukin (IL)-1beta and tumor necrosis factor (TNF)-alpha, but the inhibition of these cytokines with agents known to block their secretion did not protect cells from silica-induced apoptosis. Data indicate that silica-induced apoptosis is mediated through mitochondrial generation of ROS, which may be inhibited by pretreatment of cells with R6G that prevents ROS generation, or with NAC that maintains a high level of mGSH. The secretion of IL-1beta and TNF-alpha by silica-exposed AM was markedly inhibited by NAC and R6G, suggesting that the production of these cytokines is also ROS dependent.

Suppression of phagocytic and bactericidal functions of rat alveolar macrophages by the organic component of diesel exhaust particles.

Exposure to diesel exhaust particles (DEP) was shown to increase the susceptibility of the lung to bacterial infection in rats. In this study, the effects of DEP on alveolar macrophage (AM) phagocytic and bactericidal functions and cytokine secretion by AM and lymphocytes in response to Listeria monocytogenes infection were investigated in vitro and the roles of different DEP components in these processes were compared. Exposure to DEP or the organic extracts of DEP (eDEP) significantly decreased the phagocytosis and killing of L. monocytogenes by AM obtained from normal rats. Washed DEP (wDEP) also decreased AM phagocytosis and bacterial killing to a lesser extent, whereas carbon black (CB) reduced AM phagocytosis but had no significant effect on AM bactericidal activity. DEP or eDEP concentration-dependently suppressed L. monocytogenes-induced secretion of tumor necrosis factor-alpha, interleukin (IL)-1beta, and IL-12 by AM and of IL-2 and interferon-gamma by lymphocytes obtained from L. monocytogenes-infected rats, but augmented the AM secretion of IL-10. wDEP or CB, however, exerted little or no effect on these L. monocytogenes-induced cytokines. These results provide direct evidence that DEP, through the actions of organic components, suppresses AM phagocytic and bactericidal functions in vitro. Inhibition of AM phagocytic function and alterations of AM and lymphocyte cytokine secretion by DEP and DEP organic compounds may be implicated in the diminished AM bactericidal activity and the lymphatic arm of the host immune system, thus resulting in an suppressed pulmonary clearance of L. monocytogenes and an increased susceptibility of the lung to bacterial infection.

Cooperation of the inducible nitric oxide synthase and cytochrome P450 1A1 in mediating lung inflammation and mutagenicity induced by diesel exhaust particles.

Diesel exhaust particles (DEPs) have been shown to activate oxidant generation by alveolar macrophages (AMs), alter xenobiotic metabolic pathways, and modify the balance of pro-antiinflammatory cytokines. In this study we investigated the role of nitric oxide (NO) in DEP-mediated and DEP organic extract (DEPE) -mediated inflammatory responses and evaluated the interaction of inducible NO synthase (iNOS) and cytochrome P450 1A1 (CYP1A1). Male Sprague-Dawley rats were intratracheally (IT) instilled with saline, DEPs (35 mg/kg), or DEPEs (equivalent to 35 mg DEP/kg), with or without further treatment with an iNOS inhibitor, aminoguanidine (AG; 100 mg/kg), by intraperitoneal injection 30 min before and 3, 6, and 9 hr after IT exposure. At 1 day postexposure, both DEPs and DEPEs induced iNOS expression and NO production by AMs. AG significantly lowered DEP- and DEPE-induced iNOS activity but not the protein level while attenuating DEPE- but not DEP-mediated pulmonary inflammation, airway damage, and oxidant generation by AMs. DEP or DEPE exposure resulted in elevated secretion of both interleukin (IL) -12 and IL-10 by AMs. AG significantly reduced DEP- and DEPE-activated AMs in IL-12 production. In comparison, AG inhibited IL-10 production by DEPE-exposed AMs but markedly increased its production by DEP-exposed AMs, suggesting that NO differentially regulates the pro- and antiinflammatory cytokine balance in the lung. Both DEPs and DEPEs induced CYP1A1 expression. AG strongly inhibited CYP1A1 activity and lung S9 activity-dependent 2-aminoanthracene mutagenicity. These studies show that NO plays a major role in DEPE-induced lung inflammation and CYP-dependent mutagen activation but a lesser role in particulate-induced inflammatory damage.

Silica-induced apoptosis in alveolar macrophages: evidence of in vivo thiol depletion and the activation of mitochondrial pathway.

Studies have shown that silica induces apoptosis through mechanisms that also regulate the inflammatory responses of lung cells to silica exposure. Although implicated in cell culture studies, the major in vivo pathway through which silica induces apoptosis has not been characterized. The present study is to study the role of mitochondria in silica-induced oxidative stress and apoptosis in vivo. Rats were intratracheally instilled with saline or silica (20 mg/kg) and sacrificed at 3 days post-exposure unless otherwise specified. Alveolar macrophages (AM) were harvested by bronchoalveolar lavage and measured for apoptosis and secretion of inflammatory mediators in the presence or absence of appropriate inhibitors. Concurrent studies were carried out to determine the presence of intracellular reactive oxygen species (ROS) via confocal microscopy, mitochondrial trans-membrane potential by flow cytometry, mitochondrial release of cytochrome c, and the activation of caspase activities in AM by Western blot analysis. Silica was shown to induce elevated levels of intracellular ROS, resulting in a marked decrease in intracellular glutathione (GSH) and cysteine and a sustained presence of apoptotic AM in silica-exposed rats up to two weeks post-exposure. The apoptotic AM were characterized by decreased mitochondrial trans-membrane potential, increased mitochondrial release of cytochrome c, activated caspase 9 (but not caspase 8) and caspase 3 activities, and PARP degradation, comparing to cells from the saline control. Silica induced AM production of IL-1 and TNF-alpha, which may be inhibited by ex vivo treatment of cells with N-acetylcysteine (NAC) or microtubule modifiers such as tetrandrine and taxol. NAC was shown to prevent intracellular GSH depletion and silica-induced production of IL-1beta and TNF-alpha but not apoptosis in AM from silica-exposed rats. These results show that silica-induced apoptosis is mediated through the mitochondrial pathway but not through cellular production of inflammatory cytokines, ROS generation, however, induces both apoptosis and cellular secretion of inflammatory mediators.

Effect of diesel exhaust particles on allergic reactions and airway responsiveness in ovalbumin-sensitized brown Norway rats.

We have previously demonstrated that exposure to diesel exhaust particles (DEP) prior to ovalbumin (OVA) sensitization in rats reduced OVA-induced airway inflammation. In the present study, Brown Norway rats were first sensitized to OVA (42.3 +/- 5.7 mg/m3) for 30 min on days 1, 8, and 15, then exposed to filtered air or DEP (22.7 +/- 2.5 mg/m3) for 4 h/day on days 24-28, and challenged with OVA on day 29. Airway responsiveness was examined on day 30, and animals were sacrificed on day 31. Ovalbumin sensitization and challenge resulted in a significant infiltration of neutrophils, lymphocytes, and eosinophils into the lung, elevated presence of CD4+ and CD8+ T lymphocytes in lung draining lymph nodes, and increased production of serum OVA-specific immunoglobulin (Ig)E and IgG. Diesel exhaust particles pre-exposure augmented OVA-induced production of allergen-specific IgE and IgG and pulmonary inflammation characterized by marked increases in T lymphocytes and infiltration of eosinophils after OVA challenge, whereas DEP alone did not have these effects. Although OVA-sensitized rats showed modest response to methacholine challenge, it was the combined DEP and OVA exposure that produced significant airway hyperresponsiveness in this animal model. The effect of DEP pre-exposure on OVA-induced immune responses correlated with an interactive effect of DEP with OVA on increased production of reactive oxygen species (ROS) and nitric oxide (NO) by alveolar macrophages (AM) and alveolar type II (ATII) cells, NO levels in bronchoalveolar lavage fluid, the induction of inducible NO synthase expression in AM and ATII cells, and a depletion of total intracellular glutathione (GSH) in AM and lymphocytes. These results show that DEP pre-exposure exacerbates the allergic responses to the subsequent challenge with OVA in OVA-sensitized rats. This DEP effect may be, at least partially, attributed to the elevated generation of ROS in AM and ATII cells, a depletion of GSH in AM and lymphocytes, and an increase in AM and ATII cell production of NO.

Sustained effect of inhaled diesel exhaust particles on T-lymphocyte-mediated immune responses against Listeria monocytogenes.

Studies have shown that exposure to diesel exhaust particles (DEP) suppresses pulmonary host defense against bacterial infection. The present study was carried out to characterize whether DEP exposure exerts a sustained effect in which inhaled DEP increase the susceptibility of the lung to bacterial infection occurring at a later time. Brown Norway rats were exposed to filtered air or DEP by inhalation at a dose of 21.2 +/- 2.3 mg/m3, 4 h/day for 5 days, and intratracheally instilled with saline or 100,000 Listeria monocytogenes (Listeria) 7 days after the final DEP exposure. Bacterial growth and cellular responses to DEP and Listeria exposures were examined at 3 and 7 days post-infection. The results showed that inhaled DEP prolonged the growth of bacteria, administered 7 days post DEP exposure, in the lung as compared to the air-exposed controls. Pulmonary responses to Listeria infection were characterized by increased production of interleukin (IL)-1beta, tumor necrosis factor (TNF)-alpha, IL-12, and IL-10 by alveolar macrophages (AM) and increased presence of T lymphocytes and their CD4+ and CD8+ subsets in lung draining lymph nodes that secreted elevated levels of IL-2, IL-6, IL-10, and interferon (IFN)-gamma. Diesel exhaust particles were found to inhibit Listeria-induced production of IL-1beta and TNF-alpha, which are responsible for the innate immunity, and IL-12, which initiates the development of T helper (Th)1 responses, but enhance Listeria-induced AM production of IL-10, which prolongs Listeria survival in these phagocytes. The dual action of DEP on AM production of IL-12 and IL-10 correlated with an inhibition of the development of bacteria-specific T lymphocytes by DEP. Cytokine production by lymphocytes from DEP- and Listeria-exposed rats showed a marked decrease in the production of IL-2, IL-10, and IFN-gamma compared to Listeria infection alone, suggesting either that DEP inhibit the production of cytokines by lymphocytes or that these lymphocytes contained T-cell subsets that are different from those of Listeria infection alone and less effective in mediating Th1 immune responses. This study demonstrates that inhaled DEP, after a 7-day resting period, increase the susceptibility of the lung to bacterial infection occurring at a later time by inhibiting macrophage immune function and suppressing the development of T-cell-mediated immune responses. The results support the epidemiological observations that exposure to DEP may be responsible for the pulmonary health effects on humans.

Exposure of brown Norway rats to diesel exhaust particles prior to ovalbumin (OVA) sensitization elicits IgE adjuvant activity but attenuates OVA-induced airway inflammation.

Exposure to diesel exhaust particles (DEP) during the sensitization process has been shown to increase antigen-specific IgE production and aggravate allergic airway inflammation in human and animal models. In this study, we evaluated the effect of short-term DEP exposure on ovalbumin (OVA)-mediated responses using a post-sensitization model. Brown Norway rats were first exposed to filtered air or DEP (20.6 +/- 2.7 mg/m3) for 4 h/day for five consecutive days. One day after the final air or DEP exposure (day 1), rats were sensitized with aerosolized OVA (40.5 +/- 6.3 mg/m3), and then again on days 8 and 15, challenged with OVA on day 29, and sacrificed on days 9 or 30, 24 h after the second OVA exposure or the final OVA challenge, respectively. Control animals received aerosolized saline instead of OVA. DEP were shown to elicit an adjuvant effect on the production of antigen-specific IgE and IgG on day 30. At both time points, no significant airway inflammatory responses and lung injury were found for DEP exposure alone. However, the OVA-induced inflammatory cell infiltration, acellular lactate dehydrogenase activity and albumin content in bronchoalveolar lavage (BAL) fluid, and numbers of T cells and their CD4+ and CD8+ subsets in lung-draining lymph nodes were markedly reduced by DEP on day 30 compared with the air-plus-OVA exposure group. The OVA-induced nitric oxide (NO) in the BAL fluid and production of NO, interleukin (IL)-10, and IL-12 by alveolar macrophages (AM) were also significantly lowered by DEP on day 30 as well as day 9. DEP or OVA alone decreased intracellular glutathione (GSH) in AM and lymphocytes on days 9 and 30. The combined DEP and OVA exposure resulted in further depletion of GSH in both cell types. These results show that short-term DEP exposure prior to sensitization had a delayed effect on enhancement of the sensitization in terms of allergen-specific IgE and IgG production, but caused an attenuation of the allergen-induced airway inflammatory responses.

Roles of reactive oxygen species and heme oxygenase-1 in modulation of alveolar macrophage-mediated pulmonary immune responses to Listeria monocytogenes by diesel exhaust particles.

Diesel exhaust particles (DEP) have been shown to suppress alveolar macrophage (AM)-mediated pulmonary immune responses to Listeria monocytogenes in vivo. In this study, effects of DEP-derived reactive oxygen species (ROS) and heme oxygenase (HO)-1 on AM-mediated immune responses to L. monocytogenes were investigated. Brown Norway rats were intratracheally inoculated with 100,000 L. monocytogenes, and AM were isolated at 7 days post-infection. Exposure to DEP or their organic extract (eDEP), but not the washed DEP (wDEP) or carbon black, increased intracellular ROS and HO-1 expression in AM. Induction of ROS and HO-1 by eDEP was partially reversed by alpha-naphthoflavone, a cytochrome P450 1A1 inhibitor, and totally blocked by N-acetylcysteine. In addition, exposure to eDEP, but not wDEP, inhibited lipopolysacchride-stimulated secretion of tumor necrosis factor-alpha (TNF-alpha) and interleukin-12 (IL-12), but augmented production of IL-10 by AM. Kinetic studies showed that modulation of cytokines by eDEP was preceded by ROS and HO-1 induction. Furthermore, pretreatment of AM with superoxide dismutase (SOD) or zinc protoporphrin IX (Znpp), which attenuated eDEP-induced HO-1 expression/activity, substantially inhibited eDEP effect on IL-10. Finally, direct stimulation with pyrogallol (PYR), a superoxide donor, upregulated HO-1 and IL-10 but decreased secretion of IL-12 in L. monocytogenes-infected AM. These results show that DEP, through eDEP-mediated ROS, induce HO-1 expression and IL-10 production and at the same time inhibit AM production of TNF-alpha and IL-12 to dampen the host immune responses. The results also suggest that HO-1 may play an important role in regulating production of IL-10 by DEP-exposed and L. monocytogenes-infected AM.

Effect of diesel exhaust particulate (DEP) on immune responses: contributions of particulate versus organic soluble components.

The effect of diesel exhaust particulate (DEP) exposure on innate, cellular and humoral pulmonary immunity was studied using high-dose, acute-exposure rat, mouse, and cell culture models. DEP consists of a complex mixture of petrochemical-derived organics adsorbed onto elemental carbon particles. DEP is a major component of particulate urban air pollution and a health concern in both urban and occupational environments. The alveolar macrophage is considered a key cellular component in pulmonary innate immunity. DEP and DEP organic extracts have been found to suppress alveolar macrophage function as demonstrated by reduced production of cytokines (interleukin-1 [IL-1], tumor necrosis factor- alpha [TNF- alpha]) and reactive oxygen species (ROS) in response to a variety of agents, including lipopolysaccharide (LPS), interferon- gamma (IFN- gamma), and bacteria. Fractionation of DEP organic extract suggests that this activity was predominately in polyaromatic-containing and more polar (resin) fractions. Organic-stripped DEP did not alter these innate pulmonary immune responses. DEP also depressed pulmonary clearance of Listeria monocytogenes and Bacillus Calmette-Guerin (BCG). The contribution of the organic component of DEP is less well defined with respect to acquired and humoral immunity. Indeed, both DEP and carbon black enhanced humoral immune responses (specific immunoglobulin [Ig] E and IgG) in an ovalbumin-sensitized rat model. It is concluded that both the particulate and adsorbed organics may contribute to DEP-mediated immune alterations.

Suppression of cell-mediated immune responses to listeria infection by repeated exposure to diesel exhaust particles in brown Norway rats.

Diesel exhaust particles (DEP) have been shown to alter pulmonary immune responses to bacterial infection. Exposure of rats to 100 mg/m(3) DEP for 4 h was found to aggravate Listeria monocytogenes(Listeria) infection at 3 days postinfection, but the bacteria were largely cleared at 7 days postinfection due to the development of a strong T cell-mediated immunity. In the present study, we examined the effects of repeated DEP exposure at lower doses on pulmonary responses to bacterial infection. Brown Norway rats were exposed to DEP by inhalation at 20.62 +/- 1.31 mg/m 3 for 4 h/day for 5 days, followed by intratracheal inoculation with 100,000 Listeria at 2 h after the last DEP exposure. DEP-exposed rats showed a significant increase in lung bacterial load at both 3 and 7 days postinfection. The repeated DEP exposure was shown to suppress both the innate, orchestrated by alveolar macrophages (AM), and T cell-mediated responses to Listeria. DEP inhibited AM production of interleukin- (IL-) 1beta, tumor necrosis factor- (TNF-) alpha, and IL-12 but enhanced Listeria-induced AM production of IL-10, which has been shown to prolong the survival of intracellular pathogens such as Listeria. DEP exposure also suppressed the development of bacteria-specific lymphocytes from lung-draining lymph nodes, as indicated by the decreased numbers of T lymphocytes and their CD4(+) and CD8(+) subsets. Furthermore, the DEP exposure markedly inhibited the Listeria-induced lymphocyte secretion of IL-2 at day 7, IL-10 at days 3 and 7, and interferon- (IFN-) gamma at days 3 to 10 postinfection when compared to air-exposed controls. These results show a sustained pattern of downregulation of T cell-mediated immune responses by repeated low-dose DEP exposure, which is different from the results of a single high-dose exposure where the acute effect of DEP aggravated bacteria infection but triggered a strong T cell-mediated immunity.

Effect of asphalt fume inhalation exposure at simulated road paving conditions prior to bacterial infection on lung defense responses in rats.

Asphalt fume inhalation has been suspected of affecting immune function in exposed workers. The objective of this study was to evaluate the effect of asphalt exposure on lung immune responses in rats using a bacterial infectivity model. Pathogen-free male Sprague-Dawley rats were exposed by inhalation to asphalt fumes (72.6 +/- 4.95 mg/m3) or filtered air for 6 h/day for 5 days. One day after the final asphalt exposure, rats were intratracheally inoculated with 5 x 10(5) Listeria monocytogenes. At 0 (prior to bacterial inoculation), 3, and 7 days after L. monocytogenes instillation, the lungs of each animal were divided. Bronchoalveolar lavage (BAL) was performed on right lungs. The recovered BAL cells were then differentiated and counted, and alveolar macrophage (AM) function was determined. Albumin and lactate dehydrogenase (LDH), two indices of lung injury, were measured in the acellular BAL fluid. To assess bacterial clearance, the left lungs were removed, homogenized, and bacterial colony-forming units (CFUs) were counted. In addition, lung-draining lymph nodes were removed, and lymphocyte phenotype and lymphocyte-induced cytokine production were examined. Asphalt fume exposure did not cause lung injury or inflammation in rats in the absence of infection. Infection induced elevations in AMs, neutrophils (PMNs), albumin, and LDH. Importantly, no significant differences were seen when comparing the asphalt group with the air and nonexposed naive groups at any time before or after infection. Also, asphalt fume inhalation exposure did not affect the rate of pulmonary clearance of L. monocytogenes or AM production of reactive oxygen and nitrogen species. However, asphalt-related increases in lymphocyte secretion of interferon (IFN)-gamma, interleukin (IL)-6, and IL-10 were observed at different times after bacterial infection, whereas the total number of lymph-node cells and the percentage of CD4+ and CD8+ cells were not significantly different among the treatment groups. Despite the asphalt-induced changes observed in lymphokine secretion, adaptive immune function seemed to function properly in lung defense against bacterial infection. Because innate nonspecific lung responses and pulmonary clearance of L. monocytogenes were unaffected by asphalt fume exposure, lung defenses were sufficient to control the infection. It was concluded that acute inhalation of asphalt fumes at a high concentration had a minimal effect on lung immune responses to infection in rats.

Alteration of pulmonary immunity to Listeria monocytogenes by diesel exhaust particles (DEPs). II. Effects of DEPs on T-cell-mediated immune responses in rats.

Previously, we showed that diesel exhaust particles (DEPs) suppressed pulmonary clearance of Listeria monocytogenes (Listeria) and inhibited the phagocytosis of alveolar macrophages and their response to Listeria in the secretion of interleukin (IL)-1 beta, tumor necrosis factor alpha, and IL-12. In this report we examined the effects of DEPs and/or Listeria on T-cell development and secretion of IL-2, IL-6, and interferon (IFN)-gamma. We exposed Brown Norway rats to clean air or DEPs at 50 or 100 mg/m3 for 4 hr by nose-only inhalation and inoculated with 100,000 Listeria. Lymphocytes in the lung-draining lymph nodes were isolated at 3 and 7 days postexposure, analyzed for CD4+ and CD8+ cells, and measured for cytokine production in response to concanavalin A or heat-killed L. monocytogenes. Listeria infection induced lymphocyte production of IL-6. At 7 days postinfection, lymphocytes from Listeria-infected rats showed significant increases in CD4+ and CD8+ cell counts and the CD8+/CD4+ ratio and exhibited increased production of IFN-gamma and IL-2 receptor expression compared with the noninfected control. These results suggest an immune response that involves the action of IL-6 on T-cell activation, yielding Listeria-specific CD8+ cells. DEP exposure alone enhanced lymphocyte production of both IL-2 and IL-6 but inhibited lymphocyte secretion of IFN-gamma. In rats exposed to 100 mg/m3 DEPs and Listeria, a 10-fold increase occurred in pulmonary bacterial count at 3 days postinfection when compared with the Listeria-only exposure group. The isolated lymphocytes showed a significant increase in the CD4+ and CD8+ cell counts and the CD8+/CD4+ ratio and exhibited increased IL-2 responsiveness and increased capacity in the secretion of IL-2, IL-6, and IFN-gamma. This T-cell immune response was sufficient to allow the Brown Norway rats to clear the bacteria at 7 days postinfection and overcome the down-regulation of the innate immunity by the acute DEP exposure.

Alteration of pulmonary immunity to Listeria monocytogenes by diesel exhaust particles (DEPs). I. Effects of DEPs on early pulmonary responses.

It has been hypothesized that diesel exhaust particles (DEPs) aggravate pulmonary bacterial infection by both innate and cell-mediated immune mechanisms. To test this hypothesis, we investigated the effects of DEP exposure on the functions of alveolar macrophages (AMs) and lymphocytes from lung-draining lymph nodes using a rat Listeria monocytogenes infection model. In the present study, we focused on the effects of DEP exposure on AM functions, including phagocytic activity and secretion of proinflammatory cytokines. The Listeria infection model was characterized by an increase in neutrophil count, albumin content, and acellular lactate dehydrogenase activity in the bronchoalveolar lavage (BAL) fluid at 3 and 7 days postinfection. Short-term DEP inhalation (50 and 100 mg/m(3), 4 hr) resulted in a dose-dependent suppression of lung clearance of Listeria, with the highest bacteria count occurring at day 3. This aggravated bacterial infection was consistent with the inhibitory effect of DEPs on macrophage functions. DEPs suppressed phagocytosis and Listeria-induced basal secretion of interleukin-1ss (IL-1ss) and IL-12 by AMs in a dose-dependent manner. The amount of IL-1ss and IL-12 in the BAL fluid was also reduced by DEP exposure. In addition, DEPs decreased Listeria-induced lipopolysaccharide-stimulated secretion of tumor necrosis factor-alpha (TNF-alpha), IL-1ss, and IL-12 from AMs. These results suggest that DEPs retard bacterial clearance by inhibiting AM phagocytosis and weaken the innate immunity by inhibiting AM secretion of IL-1ss and TNF-alpha. DEPs may also suppress cell-mediated immunity by inhibiting AM secretion of IL-12, a key cytokine for the initiation of T helper type 1 cell development in Listeria infection.

Transport and utilization of arginine and arginine-containing peptides by rat alveolar macrophages.

PURPOSE: To demonstrate that rat alveolar macrophages (AM) exhibited the PepT1-like transporter for the uptake of arginine (Arg)-containing small peptides and utilized these peptides as direct substrates for nitric oxide (NO) production. NO is an important mediator that, on one hand, protects the lung from bacteria infection and, on the other hand, augments inflammatory lung injury. METHOD: The uptake of small peptides by rat AM was evaluated using fluorescein isothiocyanate (FITC)-labeled (*) peptides (Arg-Lys*, Gly-Sar-Lys*, and beta-Ala-Lys*), high-performance liquid chromatography (HPLC) analysis of potential peptide degradation, and known inhibitors of Arg and PepT1 transport. NO production by AM through Arg and Arg-containing peptides was studied with and without inhibition by transport inhibitors. The presence of PepT1-like transporter on AM was evaluated using anti-PepT1 antisera and Western blot analysis. The substrate specificity of Arg-Gly and Arg-Gly-Asp was determined using purified inducible NO synthase (iNOS). The availability of Arg-containing peptides in the lung was determined by HPLC analysis of bronchoalveolar lavage (BAL) fluid. RESULTS: The FITC-labeled peptides were internalized by AM without degradation. The uptake of Arg-Lys*, beta-Ala-Lys*, and Gly-Sar-Lys* was blocked (approximately 50%) by cephradine (an inhibitor of PepT1 for peptide transport) but not by Lys (an inhibitor on cationic amino acid transporter 2B for Arg transport). The NO production by AM through Arg-containing peptides was significantly blocked only by PepT1 inhibitors and by an anti-PepT1 antibody in a dose-dependent manner. These inhibitors had no effect on the AM production of NO using Arg as a substrate. Arg-Gly and Arg-Gly-Asp were found to be direct substrates for iNOS with similar Km and Vmax values to those of Arg. But, the production of NO by AM using these peptides as substrates was 2-fold higher than using Arg as a substrate. Both Arg-Gly and Arg-Gly-Asp were found in the BAL fluid. The presence of a PepT1-like transporter on AM was confirmed by Western blotting. CONCLUSION: This study shows that AM exhibit PepT1-like transporter for small peptide uptake. Arginine-containing peptides, through the PepT1 transporter system, can serve as direct substrates of iNOS for the production of NO by AM.

The effect of diesel exhaust particles (DEP) and carbon black (CB) on thiol changes in pulmonary ovalbumin allergic sensitized Brown Norway rats.

Brown Norway rats were exposed by intratracheal instillation of saline, carbon black (CB), or diesel exhaust particles (DEP) (5 mg/kg) on day 1, followed by exposure to ovalbumin (OVA, 90 mg/m(3)) or saline for 30 minutes on days 1, 8, 15, and 29. Animals were sacrificed on day 30. The DEP, CB, or OVA exposure alone did not result in abnormal levels of inflammatory cells, lactate dehydrogenase (LDH), or total protein in the lavage fluid. In combined OVA-DEP or OVA-CB exposure, however, these markers were significantly increased. The adjuvant effect of CB and DEP on OVA sensitization was evidenced by the marked increases in serum OVA-specific IgG (5.6-fold) and IgE (3.5-4 fold) levels, and the increase in interleukin-4 (IL-4) mRNA levels in lung tissue. The OVA exposure markedly reduced glutathione (GSH) levels in both cell types. In combined DEP-OVA exposure, the level of GSH in lymphocytes was further decreased, indicating a possible interactive effect between DEP and OVA exposures. These results show that both DEP and CB augmented OVA-induced allergic sensitization, and that particle composition of DEP may not be a critical factor for the adjuvant effect. OVA exposure causes significant depletion of intracellular GSH in lymphocytes, which may play a key role in OVA-mediated immune responses.

Alteration of intracellular cysteine and glutathione levels in alveolar macrophages and lymphocytes by diesel exhaust particle exposure.

The purpose of this study was to characterize the effects of diesel exhaust particles (DEP) on thiol regulation in alveolar macrophages (AM) and lymphocytes. We obtained AM and lymph node (thymic and tracheal) cells (LNC) (at different time points) from rats exposed intratracheally to DEP (5 mg/kg) or saline, and measured inflammatory markers, thiol levels, and glutathione reductase (GSH-R) activity. DEP exposure produced significant increases in neutrophils, lactate dehydrogenase, total protein, and albumin content in the lavage fluid. AM from DEP-exposed rats showed a time-dependent increase in intracellular cysteine (CYSH) and GSH. In LNC the intracellular GSH reached peak level by 24 hr, declining toward control levels by 72 hr after exposure. LNC-CYSH and AM-CYSH and GSH were increased at both 24 and 72 hr. Both Sprague-Dawley and Brown Norway rats showed similar trends of responses to DEP exposure as per measurement of the inflammatory markers and thiol changes. AM and, to a lesser degree, LNC were both active in cystine uptake. The DEP exposure stimulated GSH-R activity and increased the conversion of cystine to CYSH in both cell types. The intracellular level of GSH in DEP-exposed AM was moderately increased compared with the saline control, and was further augmented when cells were incubated with cystine. In contrast, the intracellular level of GSH in DEP-exposed LNC was significantly reduced despite the increased CYSH level and GSH-R activity when these cells were cultured for 16 hr. DEP absorbed 23-31% of CYSH, cystine, and GSH, and only 8% of glutathione disulfide when incubated in cell free media. These results indicate that DEP exposure caused lung inflammation and affected thiol levels in both AM and LNC.