Augmentation of arginase 1 expression by exposure to air pollution exacerbates the airways hyperresponsiveness in murine models of asthma
© North et al; licensee BioMed Central Ltd. 2011
Received: 20 August 2010
Accepted: 3 February 2011
Published: 1 December 2011
Arginase overexpression contributes to airways hyperresponsiveness (AHR) in asthma. Arginase expression is further augmented in cigarette smoking asthmatics, suggesting that it may be upregulated by environmental pollution. Thus, we hypothesize that arginase contributes to the exacerbation of respiratory symptoms following exposure to air pollution, and that pharmacologic inhibition of arginase would abrogate the pollution-induced AHR.
To investigate the role of arginase in the air pollution-induced exacerbation of airways responsiveness, we employed two murine models of allergic airways inflammation. Mice were sensitized to ovalbumin (OVA) and challenged with nebulized PBS (OVA/PBS) or OVA (OVA/OVA) for three consecutive days (sub-acute model) or 12 weeks (chronic model), which exhibit inflammatory cell influx and remodeling/AHR, respectively. Twenty-four hours after the final challenge, mice were exposed to concentrated ambient fine particles plus ozone (CAP+O3), or HEPA-filtered air (FA), for 4 hours. After the CAP+O3 exposures, mice underwent tracheal cannulation and were treated with an aerosolized arginase inhibitor (S-boronoethyl-L-cysteine; BEC) or vehicle, immediately before determination of respiratory function and methacholine-responsiveness using the flexiVent®. Lungs were then collected for comparison of arginase activity, protein expression, and immunohistochemical localization.
Compared to FA, arginase activity was significantly augmented in the lungs of CAP+O3-exposed OVA/OVA mice in both the sub-acute and chronic models. Western blotting and immunohistochemical staining revealed that the increased activity was due to arginase 1 expression in the area surrounding the airways in both models. Arginase inhibition significantly reduced the CAP+O3-induced increase in AHR in both models.
This study demonstrates that arginase is upregulated following environmental exposures in murine models of asthma, and contributes to the pollution-induced exacerbation of airways responsiveness. Thus arginase may be a therapeutic target to protect susceptible populations against the adverse health effects of air pollution, such as fine particles and ozone, which are two of the major contributors to smog.
Epidemiological studies have described a relationship between ambient levels of air pollution, and respiratory admissions to hospitals [1, 2]. It has become increasingly imperative to determine the biological effects of urban air pollutants, as they pose a serious risk to public health and continue to present an enormous and increasing health and economic burden [3, 4]. Investigations of the health impact of air pollution using controlled human exposures have demonstrated acute cardiopulmonary effects in both healthy subjects and asthmatics [5–7]. Fine particulate matter, with an aerodynamic diameter of less than 2.5 μm, has been specifically associated with increased mortality, pulmonary inflammation and oxidative stress [8–10]. Ozone (O3) exposure has also been associated with asthma-related hospital visits . Fine particulate matter and O3 typically occur together in urban settings . Therefore, it is important to understand the combined effects of these criteria air pollutants on cardiopulmonary disease. In particular, the role of these pollutants in asthma exacerbations remains to be fully understood.
Studies of gene-environment interactions have focused on the role of oxidative stress-responsive genes and air pollution exposures in asthma [12, 13]. However, the mechanism(s) linking exposure to air pollution and asthma exacerbation remains unclear. The metabolism of L-arginine plays an important homeostatic role in the airways, through synthesis of the bronchodilating molecule, nitric oxide (NO), from L-arginine, by the nitric oxide synthase (NOS) isozymes . The arginase isozymes (arginases 1 and 2), convert L-arginine into L-ornithine and urea, and thus compete with the NOS isozymes for substrate . We and others have shown that arginase expression is upregulated in human asthma [16–18] and that the arginase isozymes play a functional role in the airways hyperresponsiveness (AHR) in animal models of asthma, using ovalbumin (OVA) [16, 17, 19, 20], Aspergillus fumigatus , trimellitic anhydride exposure , and more recently house dust mite . We have previously demonstrated that the AHR in a chronic murine model of allergic airways inflammation to OVA is due to arginase 1 overexpression . Furthermore, single nucleotide polymorphisms of arginase 1 have been specifically associated with responsiveness to bronchodilators, and L-arginine bioavailability can impact airflow in asthma [23, 24].
The arginase pathway has not previously been examined as a potential mechanism underlying the air pollution-induced exacerbation of asthma symptoms. However, arginase has been shown to be further upregulated in smoking asthmatics who are regularly and voluntarily exposed to high levels of particulate matter . Furthermore, there is evidence to support uncoupling of the endothelial NOS in the vasculature following exposure to diesel exhaust , and dysfunction of endothelial-dependent vasorelaxation following exposure to second-hand tobacco smoke , likely as a consequence of a reduction in the bioavailability of L-arginine or tetrahydrobiopterin for the NOS pathway. Thus, it is plausible that dysregulation of L-arginine metabolism as a consequence of air pollution-induced upregulation of pulmonary arginase could contribute to the exacerbation of respiratory symptoms in susceptible asthmatics. We tested the hypothesis that arginase expression is augmented in response to exposures to environmental air pollutants, using two independent murine models of allergic airways inflammation; sub-acute and chronic models that mimic the inflammatory response and airways remodeling/AHR, respectively [28–31]. We demonstrate further upregulation of arginase following exposure to air pollution and attenuation of the pollution-induced AHR following treatment with an arginase inhibitor in both murine models of allergic airways inflammation.
Sub-acute and chronic models of allergic airways inflammation
Air Pollution Exposures
CAP and ozone exposure levels for the sub-acute and chronic models
CAP (μg/m3) a
553 ± 79
1.80 ± 0.07
456 ± 44
1.79 ± 0.04
Pulmonary Function Testing and Arginase Inhibition
Following the CAP+O3 or HEPA FA exposures, mice were anesthetized with ketamine (50 mg/kg i.p., Bioniche, Belleville, ON)/xylazine (10 mg/kg i.p., Bayer Inc., Toronto, ON) for measurement of in vivo airways responsiveness to methacholine using the flexiVent® system (SciReq Inc., Montréal QC) . The arginase inhibitor, S-boronoethyl L-cysteine (BEC; 40 μg/g body weight) or the PBS vehicle were nebulized directly into the airways after establishment of baseline resistance parameters, and allowed to equilibrate for 15 minutes prior to pulmonary function testing, in randomly selected mice from each model. We have previously found this dose to be effective in inhibiting arginase in acute and chronic murine models of asthma [16, 20]. Respiratory mechanics were assessed using the linear first-order single compartment model, which provides resistance of the total respiratory system (R), and the constant phase model, which utilizes forced oscillation to differentiate between airways resistance (RN) and peripheral tissue damping (G) [30, 37, 38]. Following pulmonary function testing, bronchoalveolar lavage (BAL) was performed in a subset of mice, for assessment of inflammation and 8-isoprostane as a marker of oxidative stress. All remaining lungs were harvested for protein analysis or immunohistochemical staining.
Arginase activity and isozyme expression
Total arginase activity testing and Western blotting for arginases 1 and 2 were performed as described previously . Semi-quantitative assessment of the Western blots was conducted using a Bio-Rad Fluor-S MultiImager with the Bio-Rad Quantity One 4.3.0 software package (Bio-Rad Laboratories, Hercules, CA). Densitometry was performed using GelEval v1.22 (FrogDance Software, Dundee UK).
Inflammation and Assessment of Immunohistochemical Localization of Arginase 1
Differential cell counts were performed on cytospin slides (Shandon, Thermo Scientific, Waltham, MA), stained with DiffQuick (Dade Behring Inc., Newark, NJ). Differential cell counts were performed under a light microscope, by counting more than 300 cells per slide. Immunohistochemical staining of BAL cells and histological sections was performed using standard protocols at the Toronto Centre for Phenogenomics Pathology Core Facility, as previously described . Goat anti-arginase 1 primary (sc-18351) and donkey anti-goat secondary (sc-2042) antibodies were purchased from Santa Cruz Biotechnologies (Santa Cruz, CA). For immunohistochemical counts of arginase 1-positive macrophages, macrophages were identified based on size and morphology using a hematoxylin counterstain. Lungs were collected for immunohistochemical staining and inflated to a pressure of 20 cmH2O with 10% neutral buffered formalin (Sigma, Mississauga ON) . For immunohistochemical analyses of tissue arginase 1 expression, slides were visualized on a Leica inverted microscope and images were captured using a micropublisher RTV 5.0 camera with QCapture image capture software (Quorum Technologies Inc., Guelph, ON).
Oxidative Stress Marker
As a marker of oxidative stress, 8-isoprostane levels (8-iso-prostaglandin F2α) were measured in BAL fluid using an enzyme immunoassay kit (8-Isoprostane EIA Kit. Item No. 516351, Cayman Chemical Company, Ann Arbor, MI), according to the manufacturer's instructions and standardized to protein concentration in the BAL, as determined by Bradford assay (BioRad, Hercules, CA).
Statistical analyses were performed independently on the data from the sub-acute and chronic models. Specific respiratory measurements (R, RN, G), arginase activity and Western blotting densitometry data were analyzed using one-way ANOVA with Bonferroni's multiple comparison post-hoc test. BAL differential cell counts were analyzed using the non-parametric Kruskal-Wallis test with Dunn's Multiple Comparison post-hoc test, as some cell types were not observed in the OVA/PBS controls (i.e., eosinophils). Dose-response curves were compared using the F-test, with the null hypothesis that the data from all groups could be modelled by the same curve, and using two-way ANOVA with Bonferroni's post-hoc test. Correlations between exposure parameters and protein expression were determined by Spearman's test. P-values < 0.05 were considered significant. All statistical analyses were performed using GraphPad Prism 4.0c.
Arginase activity and expression
We used Western blotting to determine the contribution of the arginase isozymes to the increased total arginase activity. Arginase 1 expression was significantly increased in lungs from FA-exposed OVA/OVA mice in both models, relative to their respective OVA/PBS controls (Figure 2C & 2D). Following exposure to CAP+O3, OVA/OVA mice in the sub-acute and chronic models exhibited further significant increases in pulmonary arginase 1 expression, relative to the FA exposed OVA/OVA controls (2.6- and 1.7-fold, respectively). Interestingly, in the sub-acute model, the pulmonary expression of arginase 1 correlated directly with CAP exposure levels at concentrations lower than 565 μg/m3 (Spearman ρ = 0.622, P = 0.013; linear regression r2 = 0.32; n = 15 mice from 11 independent exposure days) (Figure 2E), suggesting that the CAP-induced increase in expression of arginase 1 was dose-dependent. At exposure levels above 565 μg/m3 we observed no further increase in arginase 1 expression, indicating a plateau in the response at higher levels. As the ozone exposures were fixed at the target concentration of 2 ppm, there was no correlation with protein expression. While pulmonary arginase 2 protein expression was increased significantly in the sub-acute model OVA/OVA mice under FA conditions, it was not further augmented by CAP+O3 exposure. No significant increases in arginase 2 protein expression were observed in the chronic model mice, regardless of whether they were exposed to FA or CAP+O3.
Localization of increased arginase 1 expression
As arginase 1 is known to be expressed in alternatively-activated macrophages , we investigated arginase 1 expression in BAL cells using immunohistochemistry. We did not observe any change in the proportion of arginase 1-positive macrophages in the immunostained BAL slides from the CAP+O3-exposed OVA/PBS or OVA/OVA mice compared to their respective FA controls (Figure 3B). Thus, the increase in arginase 1 expression in the CAP+O3-exposed mice was not due to an increased proportion of alternatively-activated macrophages infiltrating the lung.
Effects of air pollution on methacholine responsiveness
Arginase inhibition abrogates the CAP+O3-induced AHR
After determining that exposure to CAP+O3 resulted in exacerbation of methacholine responsiveness in mice with pre-existing allergic airways inflammation, paralleling the up-regulation of pulmonary arginase 1, we administered the arginase inhibitor, BEC, or vehicle control (PBS) to randomly selected sub-groups of mice following the CAP+O3 exposures in both the sub-acute and chronic models. The maximum total respiratory resistance (RMax) was significantly increased in OVA/OVA mice vs. OVA/PBS from both models after the CAP+O3 exposure (Figure 5C and 5D). After treatment with BEC, the RMax values in the CAP+O3-exposed OVA/OVA mice was significantly attenuated compared with the PBS-treated controls (i.e., CAP+O3-exposed OVA/OVA mice), and were indistinguishable from the RMax for the OVA/PBS controls. Thus, treatment with the arginase inhibitor completely reversed the CAP+O3-induced exacerbation of symptoms in the OVA/OVA mice.
Oxidative Stress Due to CAP+O3Exposures
8-isoprostane levels in BAL samples from the sub-acute and chronic OVA-model mice exposed to filtered air or CAP+O3.
Filtered Air a
7.9 ± 3.6
9.7 ± 4.1
42.5 ± 11.4#
67.4 ± 22.4#
19.0 ± 3.3
36.8 ± 5.0*
65.7 ± 16.0#
83.0 ± 17.0#
This study demonstrated that the increased arginase activity in the lungs of mice from both sub-acute and chronic models of allergic airways inflammation was further augmented by exposure to CAP+O3, and that this was primarily driven by arginase 1. We also determined that the up-regulation of arginase 1 in the lung was not related to increased influx of macrophages. Finally, we demonstrated that induction of AHR by CAP+O3 was specific to the mice with pre-existing allergic airways inflammation, and that local delivery of an arginase inhibitor after exposure, significantly reduced the CAP+O3-induced AHR in both models; thus providing further support for the potential of targeting this pathway therapeutically in asthma.
Arginase induction by CAP+O3
There is increasing evidence to support the role of arginase in the pathophysiology of asthma, and that further up-regulation of arginase likely results in worsening of asthma symptoms [15–19]. The sub-acute model mice in the present study, challenged with ovalbumin daily for three days, exhibited significantly lower arginase 1 expression and airways responsiveness, compared to the acute OVA-model mice reported in our previous study, in which we employed seven consecutive daily challenges . Thus, increased arginase 1 expression is directly associated with the increasing airways responsiveness in these murine models (P = 0.002, Spearman ρ = 0.522). We speculate that there is a critical threshold of arginase induction, at which the increased arginase activity exhibits physiological effects. Air pollution is known to contribute to asthma exacerbations [41–43]. Increased levels of particulate matter and ozone have been associated with increased oxidative stress and decreased pulmonary function in children with asthma . Increased arginase protein expression has been observed in smokers with asthma , but it is not known whether arginase plays a role in air pollution-induced exacerbations of respiratory symptoms. In this study we demonstrated further augmentation of arginase activity and arginase 1 expression in the airways of our OVA-sensitized and -challenged mice following exposure to CAP+O3.
Arginase 1 protein expression in blood serum has recently been associated with markers of oxidative stress in a healthy human population , and augmented arginase activity correlates with indices of oxidative stress (i.e., malondialdehyde and protein carbonylation levels) in platelets and plasma from patients with chronic obstructive pulmonary disease exposed to wood smoke . Arginase 1 has also been reported to be induced in isolated coronary arterioles following one hour of ex vivo exposure to hydrogen peroxide-induced oxidative stress . Thengchaisri et al. also demonstrated changes in smooth muscle function in response to increased oxidative stress, and demonstrated that arginase inhibition restored the hydrogen peroxide-impaired vasodilation . However, in our model we only observed an increase in arginase 1 in mice that were previously sensitized and challenged with ovalbumin; while, we observed increases in 8-isoprostane levels in the BAL samples from all mice exposed to CAP+O3 regardless of the presence or absence of airways inflammation. This may be due to differences in experimental procedures, as Thengchaisri et al. exposed isolated coronary arterioles to hydrogen peroxide ex vivo , while we examined the whole lung following in vivo acute CAP+O3 exposure. Alternatively, toll-like receptors, the hallmark regulators of the innate immune response to bacterial, viral, and parasitic components, have recently been shown to upregulate arginase 1 via an alternative promoter region . It is highly likely that some of these biologic exposures are relevant to our CAP exposures. Further work is necessary to elucidate the mechanisms underlying the upregulation of arginase 1 in response to environmental stimuli in the presence of an inflammatory response.
While we did not investigate the effects of long-term pollution exposure in these models, our findings raise the interesting question of whether continued exposures would result in chronic upregulation of arginase, and lead to remodeling of the airways. Increased airway wall remodeling has been observed by Dai et al., following exposure of rat tracheal explants to Ottawa urban air particles . Diesel exhaust particles can also potentiate airways remodeling in a house dust mite murine model of allergic airways inflammation  that is known to exhibit augmented arginase expression . Thus, arginase may be induced as part of the host response to cell damage by air pollution, as it is known to be involved in cell growth and wound healing . As the metabolic pathways downstream of arginase are related to cellular proliferation and collagen biosynthesis, it is likely that augmented arginase expression contributes to airways remodeling in asthma . The role of L-arginine metabolism in the effects of chronic air pollution exposure, and the effects of concomitant inhibition of arginase represent future avenues for investigation.
Functional improvement of airways hyperresponsiveness with arginase inhibition
Although the arginase pathway has been shown to be functionally involved in the development of AHR in vivo following allergen challenges with ovalbumin [16, 19, 20, 53] and house dust mite , it was not clear whether this pathway would be functionally important in the exacerbation of AHR induced by air pollution. In this investigation we used two mouse models of asthma, which exhibit the inflammatory changes, remodeling and moderate AHR as symptoms of allergic airways disease; while the OVA/OVA mice in the sub-acute model did not exhibit AHR to methacholine, those in the chronic model did exhibit moderate AHR, which was consistent with our previous report . We further demonstrated exacerbation of the AHR in the chronic model and the development of AHR in the sub-acute model after exposure to air pollution. In both murine models we demonstrated an increase in the maximum total lung resistance following air pollution exposure, and that inhibition of arginase, post-exposure, blocked this effect. We also examined the contribution of the airways and peripheral tissue to the net response. Using a sub-acute model of allergic airways inflammation, Tomioka et al. previously demonstrated that the effects of allergic inflammation in this model were more pronounced in the lung periphery and thus affected peripheral lung mechanics more strongly than conducting airways mechanics . However, it was not known how the added challenge of a CAP+O3 exposure would affect peripheral lung mechanics in the sub-acute model. Our data suggest that CAP+O3 exposure specifically aggravated peripheral lung responsiveness to methacholine in the OVA/OVA mice in this sub-acute model. Arginase inhibition with BEC completely abrogated the augmented GMax, strongly suggesting a role for arginase in the functional exacerbation of peripheral AHR by air pollution in the sub-acute model.
The particles we employed were derived from the ambient air in Toronto, Ontario, and particles within a specific size range (0.1-2.5 μm) were concentrated, representing real-world particles. We examined the effects of concentrated ambient particles and ozone, as these pollutants have been shown to be associated with increased asthma exacerbations in humans, and because concomitant exposures have been shown to increase respiratory resistance in mice, thus allowing our study to examine the biological mechanisms responsible for these effects [1, 2, 11, 54]. Murine models present several limitations, as no animal model exhibits all of the clinical features of human asthma [30, 55–57]. However, our sub-acute model exhibits airways inflammation and our chronic model recapitulates airways remodeling and mild hyperresponsiveness, all of which are important features of human asthma [28, 58], and mice in both models exhibited an even greater degree of airways hyperresponsiveness following air pollution exposures. Asthmatics as a group represent a potential susceptible population that would be more significantly affected by air pollution than those who do not have underlying respiratory disease. Our results support this idea, as we did not observe increased airways responsiveness in the control mice, but demonstrated an increase in mice with pre-existing allergic airways inflammation.
While the doses of particulate matter and ozone employed in this study are high, similar doses have been shown to be useful for studying acute mechanisms of air pollution induced AHR in the setting of allergic airways inflammation and healthy controls [33–35]. Exposure to high levels of ozone can induce pulmonary edema and lung injury [35, 59]. While OVA/PBS control mice that were exposed concurrent with the OVA/OVA mice in our study did not exhibit any alterations in inflammatory cell counts or profiles in bronchoalveolar lavage samples obtained immediately after CAP+O3 exposures, the possibility remains that our findings could be due solely to the high-level exposures. Interestingly, the OVA/PBS mice exposed to CAP+O3 exhibited a slight increase in methacholine responsiveness compared with FA. Similarly, the OVA/OVA mice exposed to CAP+O3 that were treated with BEC exhibited a similar increase of methacholine responsiveness, suggesting that pathways unrelated to arginase induction, such as edema, could contribute to this non-significant increase. Thus, further investigations will be necessary to determine whether the pathways activated by acute high-level exposures are similar to those activated after chronic exposures to lower levels of particulate matter and ozone.
The chronic model offers the ability to study exacerbation of established disease, in a model that recapitulates more of the features of chronic human asthma, including remodeling, collagen deposition, smooth muscle hypertrophy, and mild AHR [16, 28, 60–62]. Furthermore, we have previously shown that the chronic model exhibits alterations in the profile of L-arginine-related protein expression that are most similar to those of human asthma . In the chronic model OVA/OVA mice, we found that both central airways resistance and peripheral tissue damping contributed to the pulmonary response to CAP+O3 exposure. However only central airways resistance was attenuated by BEC, suggesting that arginase-independent effects, such as lung edema or the accumulation of endogenous NOS inhibitors (i.e., ADMA)[63, 64], may also be induced by exposure to air pollution and contribute to AHR. While we observed a correlation between CAP exposures and arginase induction in OVA-sensitized and -challenged mice, future studies should assess the dose-effects of air pollutants and corroborate the findings with additional model allergens.
Arginase activity and arginase 1 expression are upregulated following environmental exposures in both sub-acute and chronic murine models of allergic asthma. Pollution-induced AHR is attenuated by arginase inhibition in both models. Thus, induction of arginase 1 is likely a key step in the short-term response to air pollution and inhibition may represent a therapeutic target to treat or prevent environmental pollution-induced exacerbations of allergic airways disease.
concentrated ambient particles
half-maximal effective concentration
peripheral tissue damping
nitric oxide synthase
phosphate buffered saline
total resistance of the respiratory system
resistance of the central airways.
The authors thank Dr. Mingyao Liu for thoughtful comments on the manuscript. The authors thank Mike Fila and Mary Speck for assistance with exposures, and input on the design of the exposure system, respectively. The authors thank Dr. Jeffrey R. Brook, Ministry of Environment, for the constituent analysis and helpful comments. This study was supported by the AllerGen NCE, the National Sanitarium Association, and the Keenan Research Centre of the Li Ka Shing Knowledge Institute of St. Michael's Hospital. MN is a recipient of a CIHR Doctoral Award.
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