Recent studies have suggested a link between particulate matter (PM) exposure and increased mortality and morbidity associated with pulmonary and cardiovascular diseases; accumulating evidences point to a new role for air pollution in CNS diseases. The purpose of our study is to investigate PM10sum effects on lungs and extra pulmonary tissues. Milano PM10sum has been intratracheally instilled into BALB/c mice. Broncho Alveolar Lavage fluid, lung parenchyma, heart and brain were screened for markers of inflammation (cell counts, cytokines, ET-1, HO-1, MPO, iNOS), cytotoxicity (LDH, ALP, Hsp70, Caspase8-p18, Caspase3-p17) for a putative pro-carcinogenic marker (Cyp1B1) and for TLR4 pathway activation. Brain was also investigated for CD68, TNF-α, GFAP. In blood, cell counts were performed while plasma was screened for endothelial activation (sP-selectin, ET-1) and for inflammation markers (TNF-α, MIP-2, IL-1β, MPO). Genes up-regulation (HMOX1, Cyp1B1, IL-1β, MIP-2, MPO) and miR-21 have been investigated in lungs and blood. Inflammation in the respiratory tract of PM10sum-treated mice has been confirmed in BALf and lung parenchyma by increased PMNs percentage, increased ET-1, MPO and cytokines levels. A systemic spreading of lung inflammation in PM10sum-treated mice has been related to the increased blood total cell count and neutrophils percentage, as well as to increased blood MPO. The blood-endothelium interface activation has been confirmed by significant increases of plasma ET-1 and sP-selectin. Furthermore PM10sum induced heart endothelial activation and PAHs metabolism, proved by increased ET-1 and Cyp1B1 levels. Moreover, PM10sum causes an increase in brain HO-1 and ET-1. These results state the translocation of inflammation mediators, ultrafine particles, LPS, metals associated to PM10sum, from lungs to bloodstream, thus triggering a systemic reaction, mainly involving heart and brain. Our results provided additional insight into the toxicity of PM10sum and could facilitate shedding light on mechanisms underlying the development of urban air pollution related diseases.
Citation: Farina F, Sancini G, Battaglia C, Tinaglia V, Mantecca P, et al. (2013) Milano Summer Particulate Matter (PM10) Triggers Lung Inflammation and Extra Pulmonary Adverse Events in Mice. PLoS ONE 8(2): e56636. doi:10.1371/journal.pone.0056636
Editor: Michelle L. Block, Virginia Commonwealth University, United States of America
Received: October 18, 2012; Accepted: January 11, 2013; Published: February 25, 2013
Copyright: © 2013 Farina et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original author and source are credited.
Funding: This research has received a financial support by the CARIPLO Foundation to the project TOSCA “Toxicity of particulate matter and marker of risk”. Francesca Farina obtained a grant for this project. The funders had no role in study design, data collection and analysis, decision to publish, or preparation of the manuscript.
Competing interests: The authors have declared that no competing interests exist.
Short term exposure to a high amount of PM10 (particles ≤10 µm in aerodynamic diameter, including fine and ultrafine particles) leads to higher hospitalization rates for cardiovascular diseases, increases risk for myocardial infarction and ischemic stroke , even 24 h after peak of pollution . Different possible mechanisms have been hypothesized to explain the systemic effect of PM inhalation , : on one hand, the inhaled PM may trigger the direct release of pro-oxidative and/or pro-inflammatory mediators from lungs into systemic circulation and, on the other hand, ultrafine PM may actively translocate from lungs into the bloodstream thus exerting extra pulmonary toxicity.
Convincing evidences indicate that PM10 causes the most severe effects on human health because of the broad range of miscellaneous toxic compounds present in this PM fraction , , such as transition metals, endotoxins  and ultrafine components, which could mediate the adverse effects in a mechanism called the “ultrafine hypothesis” .
Brain is another potential target of the inhaled PM: it is known that inhaled nanosized particles can penetrate lungs, deposit in extra pulmonary tissues and cross the blood-brain barrier (BBB), possibly already compromised by the PM triggered systemic inflammation .
Our previous investigations  demonstrated that summer PM10 (PM10sum) induced more severe lung inflammation than winter PM10 (PM10win) after a single intratracheal instillation in mice, and suggested a link between pro-inflammogenic potential of PM10sum and its Gram-negative bacteria content . The greater LPS amount associated to PM10sum (60,5 EU/mg)  could induce in lungs a condition that might trigger a systemic toxic reaction, so that the aim of the present study is to broaden the analysis of Milano PM10sum-induced toxicity, not only in the respiratory tract but also in extra pulmonary districts. To disclose the systemic toxicity of Milano PM10sum, we here analysed different pro-inflammatory and cytotoxic markers, both at RNA as well as at protein level, in BALB/c mice broncho-alveolar lavage fluid (BALf), lungs, blood, heart and brain, 24 hours after the last of three intratracheal instillations of PM10sum. Finally we evaluated the microRNA miR-21, recently proposed as a new marker of inflammation which is up-regulated by LPS in many cells types, including macrophages .
Materials and Methods
Male BALB/c mice (7–8 weeks old) were purchased from Harlan; food and water were administered ad libitum. Mice were housed in plastic cages under controlled environmental conditions (temperature 19–21°C, humidity 40–70%, lights on 7 a.m.−7 p.m.). “Animal use and care procedures were approved by the Institutional Animal Care and Use Committee of the University of Milano-Bicocca and complied with guidelines set by Italian Ministry of Health (DL 116/92); invasive procedures have been performed under anesthesia and all efforts were made to minimize suffering.”
PM Sources and Characterization
Atmospheric PM10sum was collected during summer 2008 at Torre Sarca, an urban site in Milano, as described in previous papers . The chemical characterization of PM10 collected during summer 2008 doesn’t differ from the PM10 collected in summer 2006 and 2007 . Particles were recovered from filters by sequential sonications (four cycles of 20 min each) in sterile water; detached particles were dried into a desiccator and weighed. Particles’ suspensions were prepared as follow: just before the intratracheal instillation, PM10sum aliquots were properly diluted in sterile saline, sonicated, vortexed and then immediately instilled in mice.
A single intratracheal instillation of 100 µg of PM10sum raised pulmonary inflammation within 3 hours; 24 h after the single instillation all the inflammatory markers basically turned to sham levels, and only differential cell count and Hsp70 reverted 1 week later .
The aim of this study is to disclose the pulmonary short-term effects and extra-pulmonary translocation of PM10sum collected in Milano urban centre. Similar investigations have been previously based on very high PM exposure rate both in case of whole chamber PM exposure , , , , , ,  and in single or repeated intratracheal instillations , , , , , .
It is well known that larger particles in the lungs are rapidly phagocytised by AMs while smaller particles enter the blood capillaries ; moreover, pulmonary inflammation plays a key role in enhancing the extra-pulmonary translocation of particles, as confirmed by the evidence that particles translocation is markedly increased following LPS treatment . We have previously reported that LPS concentration is particularly high in PM10sum collected in Milano (60 EU/mg)  and that PM10sum sub-fraction contains about 60% of fine and ultrafine particles . Our treatment scheme has been designed to lengthen the PM10sum triggered pro-inflammatory effects within lungs, in order to prove the translocation of inflammatory mediators, cytokines, ultrafine particles, LPS and/or PM associated metals from lungs toward the bloodstream. We started from the PM dose proposed by Happo et al. , who instilled in mice a cumulative dose of 0.82 mg/animal of coarse PM, and we reduced the cumulative dose to 0.3 mg/animal of PM10sum within the same time points. Indeed, the PM dose here used is not directly correlated to human urban exposures, but it has been determined as the lowest dose which induces a sustained lung inflammatory response in PM10sum exposed mice.
It must be taken into account that not all the particles intratracheally instilled are able to reach the alveoli, as some are quickly removed by the muco-ciliar clearance system or phagocited by alveolar macrophages. Finally, we used healthy BALB/c mice, preventing additional variability to response due to pre-existing disease. In any case, no signs of PM10sum lung overloading have been reported as clearly demonstrated by histological and biochemical investigations.
Intratracheal PM10sum Instillation
Animal testing was carried out by intratracheally instilling 3 mice for each experimental group and the experiment was replicated twice, for a total of 6 sham and 6 PM10sum-treated mice. For RNA and miRNA analysis, additional 5 sham and 5 PM10sum-treated mice were considered.
Male BALB/c mice were briefly exposed to a mixture of 2.5% isoflurane (Flurane) anesthetic gas and kept under anaesthesia for the whole instillation procedure (about 5 minutes). Intratracheal instillation with 100 µg of PM10sum in 100 µl of isotonic saline solution or 100 µl of isotonic saline solution (sham) has been achieved by means of MicroSprayer® Aerosolizer system (MicroSprayer® Aerosolizer- Model IA-1C and FMJ-250 High Pressure Syringe, Penn Century, USA; validated by Bivas-Benita , as described in Mantecca et al. ,  and in Farina et al. . The intratracheal instillation was performed on days 0, 3, and 6, for a total of three instillations, as previously described , .
Bronchoalveolar Lavage Fluid Analysis
24 h after the last instillation, mice from each experimental group (sham and PM10sum-treated) were euthanized with an anesthetic mixture overdose (Tiletamine/Zolazepam-Xylazine and Flurane). The PM adverse effects were assessed 24 h after the last treatment of repeated dosing of particulate since the greatest and prolonged inflammation does occur within this time point . The Broncho Alveolar Lavage Fluid (BALf), pellets and supernatants have been collected as described in Mantecca et al. ,  and in Farina et al. .
The analysis of pro-inflammatory cytokines and chemokines released in the BALf was performed by DuoSet ELISA kits for TNF-α, MIP-2 and IL-1β(R&D Systems, Minneapolis, MN) according to the manufacturer’s protocols.
The following biochemical analysis were performed on cell-free BALf supernatants. The commercially available kits for ALP (DALP-250 QuantiChrom Alkaline Phosphatase Assay Kit, Gentaur Molecular) and LDH (DLDH-100 QuantiChrom Lactate Dehydrogenase Kit, Gentaur Molecular) were employed according to the manufacturer’s instructions.
30 µg of BALf proteins of sham and PM10sum-treated mice were loaded on SDS-PAGE, submitted to electrophoresis followed by Western blot, and tested for MPO and Hsp70 (anti-MPO 1:200, anti-Hsp70 1:200, Santa Cruz), according to the procedures below described.
Lung, Heart and Brain Parenchyma Analysis
Lungs of sham and PM10sum-treated mice were quickly excised from the chest and washed in ice cold isotonic saline solution. Left lung from sham and PM10sum-treated mice was dissected and submitted to histological and immunohystochemical analysis, while right lung was submitted to immunoblotting analysis. For proteins detection and quantification, organs were minced at 4°C, briefly homogenized for 30 seconds at 11000 rpm with Ultra-Turrax T25 basic (IKA WERKE), sonicated for 30 seconds and then suspended in NaCl 0.9%. Samples were submitted to trichloroacetic acid (TCA) precipitation according to the procedure described in Farina et al. . The pellets were suspended in water and protein amounts measured by BCA method (Sigma Aldrich, USA).
Thereafter, lung, heart and brain homogenates of sham and PM10sum-treated mice were loaded on SDS-PAGE and submitted to electrophoresis, followed by Western blot, according to the procedures described in Farina et al. . Lung parenchyma was assessed with specific antibodies for MPO, ET-1, HO-1, Cyp1B1, iNOS, Hsp70, Caspase8-p18 and Caspase3-p17 (all 1:200, Santa Cruz). The activation of TLR4 pathway has been studied by investigating the phosphorylation of IRAK-1, TAK1 and IKBα (all 1:200, Abcam). Heart homogenates were incubated with specific antibodies for MPO, HO-1, Hsp70, Cyp1B1, ET-1 Caspase8-p18 and Caspase3-p17 (all 1:200, Santa Cruz) and brain homogenates were evaluated with specific antibodies for ET-1, HO-1, soluble and membrane bound TNF-α, Hsp70, Cyp1B1, CD68, GFAP, Caspase8-p18 and Caspase3-p17 (all 1:200, Santa Cruz).
Then, blots were incubated for 1.5 h with horseradish peroxidase-conjugated anti-rabbit IgG (1:5000) or anti-goat IgG (1:2000) diluted in PBS-Tween20/milk or in TBS-Tween20/BSA. Proteins were detected by ECL by means of the SuperSignal detection kit (Pierce, Rockford, IL). Immunoblot bands were analyzed and the optical density (OD) quantified by KODAK (Kodak Image Station 2000R); all the data have been normalized to β-actin (1:1500, Sigma) and each protein in PM10-treated group has been normalized to the respective sham group.
Lung Histological Analysis
At the end of BAL procedure, the left lung from sham and PM10sum-treated mice was excised and immediately formalin fixed and processed for histology. Briefly, after being preserved for 24 h in the fixative, tissue samples were rinsed in distilled water, dehydrated in an ethanol series from 70% to 100% and embedded in Bio-plast tissue embedding medium. For each sham and PM10sum exposed lung sample, 7.0 µm serial sections were cut by a rotary microtome, mounted on slides and stained with Mayer’s haemalaun and alcoholic eosin.
The immunohistochemical localization of HO-1 in lung tissues was performed by an indirect immunochemical method using a rabbit anti-HO-1 polyclonal antibody (Santa Cruz), and the peroxidase-based Vectastain Elite ABC Kit (Vectastain Laboratories) following the procedure reported in Mantecca et al. .
Samples were qualitatively screened by means of Zeiss Axioplan microscope at a magnification of 40× and images were taken using Zeiss AxioCam MRc5 digital camera interfaced with the Axiovision Real 4.6 software. Figure panels were prepared using Adobe Photoshop.
Blood of sham and PM10sum-treated mice was collected by means of intracardiac puncture with the appropriate anticoagulant (EDTA, Na-citrate). Total cells count and neutrophils percentage were performed as previously described . Plasma was obtained after two centrifugation, the first at 2000 g for 20 minutes and the second at 10000 g for 10 minutes at 4°C to completely remove platelets. Plasma samples have been then submitted to sP-Selectin quantification (Quantikine Mouse sP-selectin, R&D Systems) and cytokines analysis (TNF-α, MIP-2 and IL-1β; R&D Systems, Minneapolis, MN), following manufacturer’s procedures. Immunoblot assays of MPO and ET-1 (all 1:200, Santa Cruz) were performed according to previously described protocols; all the data have been normalized to albumin. Each protein of PM10sum-treated group has been normalized to the respective sham group.
RNA e miRNA Expression Analysis
5 sham and 5 PM10sum-treated mice were considered for RNA analysis. Lungs, not submitted to BAL procedure (called “no-BAL”), have been excised, suspended in an appropriate volume of RNA Later and submitted to total RNA extraction. Aliquots of lung and heart parenchyma from all the 5 sham and 5 PM10sum-treated mice were submitted to immunoblot analysis. Total RNA was extracted from tissues using the miRNeasy extraction kit (Qiagen, Hilden, Germany), according to the manufacturer’s instructions. Blood sample collection and RNA extraction were carried out using the Mouse RiboPure™-Blood RNA Isolation kit (Ambion, Life Technologies, Carlsbad, CA, USA), following the manufacturer’s instructions. After elution in RNase free-water, RNA samples were quantified by ND-1000 spectrophotometer (NanoDrop Technologies, Wilmington, DE, USA). RNA quality was checked by microcapillary electrophoresis with 2100 BioAnalyzer (Agilent Technologies, Santa Clara, CA, USA). Total RNA integrity was assessed on the basis of the RIN (RNA Integrity Number) factor and presence of low molecular weight RNA molecules (including 5S rRNA and small RNAs) was verified. RNA samples were stored at −80°C until use.
Quantitative PCR (QPCR) reactions for microRNAs was performed by use of TaqMan® MicroRNA Reverse Transcription (RT) kit (Applied Biosystems, Life Technologies, Inc. Carlsbad, CA, USA) and of specific miRNA primers provided with TaqMan® microRNA assays, according to the manufacturer’s protocol. Starting from 10 ng of total RNA for each assay, RT reactions were performed by means of Applied Biosystems 7900 Thermocycler machine. Quantitative microRNA expression analysis was carried out for miR-21 (Assay ID, 000397, Applied Biosystems) normalized against U6snRNA (Assay ID, 001973, Applied Biosystems) taken as endogenous control. For gene expression analysis, we performed QPCR starting from 1 µg of total RNA using the High Capacity cDNA Reverse Transcription kit (Applied Biosystems) and gene-specific primers provided with TaqMan® Gene Expression Assays. Specifically, QPCR analysis were carried out for HMOX1 (Assay ID Mm00516005_m1), Cyp1B1 (Assay ID Mm00487229_m1), IL-1β (Assay ID Mm01336189_m1), MIP-2 (Assay ID Mm00436450_m1) and MPO (Assay ID Mm00447886_m1) genes. All data have been normalized versus glyceraldehyde-3-phosphate dehydrogenase (GAPDH, Assay ID Mm99999915_g1) gene taken as endogenous control. Reactions were run in triplicate on the Applied Biosystems 7900HT Fast Real-Time PCR System machine. Ct values were calculated using the SDS software version 2.3 (Applied Biosystems), by applying automatic baseline and standard threshold settings. We applied the 2−ΔΔCt method (Applied Biosystems User Bulletin No. 2) to obtain a relative quantification of miRNA and gene expression levels.
For each cytological and biochemical parameter measured in sham and PM10sum treated mice the means ± standard error (s.e.) were calculated. Statistical differences were confirmed by U Mann-Withney test. To test the tendency toward increase or decrease of the cytological and biochemical parameters, linear regressions were carried out. Statistical differences were considered to be significant at the 95% or 99% level (p<0.05 or p<0.01).
Total cell count confirmed no differences between sham and PM10sum-treated mice, 24 h after the last PM10sum intratracheal instillation (Tab. 1, A). On the contrary, differential cell count disclosed a significant decrease of AMs percentage and a significant increase of PMNs percentage (99% neutrophils) in treated mice (Tab. 1, A). A significant increase of IL-1β and MIP-2 concentrations were evident in the BALf of PM10sum-treated mice in comparison to sham, though in presence of unchanged concentration of TNF-α (Tab. 1, A). Lactate Dehydrogenase (LDH) and Alkaline Phosphatase (ALP) activities were analyzed in the BALf as markers of cytotoxicity. LDH activity was significantly increased in PM10sum-treated mice (Tab. 1, A), while no difference was detected in ALP activity (Tab. 1, A). Finally, PM10sum-treatment induced a significant increase in both MPO and Hsp70 levels (Fig. 1, A and Tab. 1, B).
Western blottings displaying proteins in BALf (A), lung (B), heart (C), brain (D) and plasma (E) in sham and PM10sum-treated mice, 24 h after the third intratracheal instillation. Reported blots are representative of 6 sham and 6 PM10sum-treated mice; densitometry analyses are reported in Tab.1.
Lung Genes Expression Analysis
PM10sum-treatment induced a significant MIP-2 up-regulation while no significant changes were found for HMOX1, Cyp1B1, IL-1β and MPO; an induction of miR-21 in the lung tissues of PM10sum-treated mice was evidenced during miRNA gene expression analysis (Tab. 2).
Lung, Heart and Brain Protein Analyses
ET-1, a potent regulator of the vascular tone, was significantly higher in the lungs of PM10sum-treated mice in comparison to sham (Fig. 1, B and Tab. 3, A). Moreover a significant increase in HO-1 and Hsp70 levels (Fig. 1, B and Tab. 3, A), both involved in the protection against protein unfolding, as well as in the inflammation and oxidative stress, were observed in the lungs of PM10sum-treated mice. The level of Cyp1B1, a cytochrome of the P450 superfamily involved in the activation of many xenobiotics and in PAHs metabolism, significantly decreased 24 h after the last PM10sum intratracheal instillation (Fig. 1, B and Tab. 3, A). iNOS, MPO, Caspase8-p18 and Caspase3-p17 showed no differences between sham and PM10sum-treated mice (Tab. 3, A). TLR4 pathway was not activated as no increases of the IRAK1, TAK1 and IKBα phosphorylation were detected (Tab. 3, A).
Heart tissues of PM10sum-treated mice disclosed significant increases of ET-1, Cyp1B1 and Hsp70 levels (Fig. 1, C and Tab. 3, B). MPO, HO-1, Caspase8-p18 and Caspase3-p17 shown no differences between sham and PM10sum treated mice (Tab. 3, B).
In the brain of PM10sum-treated mice, ET-1 and HO-1 levels were significantly increased (Fig. 1, D and Tab. 3, C); Cyp1B1, CD68, soluble and membrane bound TNF-α, Hsp-70, GFAP, Caspase8-p18, Caspase3-p17 were basically unchanged comparing sham and PM10sum-treated mice (Tab. 3, C).
Blood and Plasma Analysis
Gene expression analysis evidenced no up-regulation of HMOX1 or IL-1β in blood RNA of PM10sum-treated mice, compared to sham, together with no induction of miR-21 (Tab. 4).
Blood and plasma of sham and PM10sum-treated mice were analysed for pro-inflammatory and pro-trombogenic markers. Total cell count, neutrophils percentage and sP-selectin concentration, a marker of the activated platelet/endothelium interface, were significantly increased 24 h after the last intratracheal instillation of PM10sum (Tab. 5, A). The cytokines analyses in the plasma of sham and PM10sum-trated mice, performed by ELISA assay, were under the kit detection limits.
Despite the relatively high cumulative dose of PM10sum instilled, there were no signs of pulmonary overloading with particles; moreover, only few free particles and no large particle aggregates were seen in the BALf or lung tissue of treated mice.
As evidenced by the histological lung analysis, when compared to sham (Fig. 2, A–B) PM10sum has induced inflammatory cell recruitment in the connective surrounding the terminal bronchioles and the proximal alveolar sacs (Fig. 2, C–D). Lungs instilled with PM10sum showed extended inflammatory infiltrate and particles engulfed by alveolar macrophages (Fig. 2, C–D). These histological evaluations have supported the cytological and biochemical assays on BALf. Immunohistochemical detection of HO-1 in the lungs of PM10sum-treated mice has confirmed the biochemical analyses, (Fig. 3, A–D). HO-1 induction appeared to be distributed along both airways and the respiratory tract, particularly well distinguishable within the epithelium of distal bronchioles (Fig. 3, C–D).
Histology of lung tissue 24 h after the third intratracheal instillation. (A, B): lung parenchyma of sham mice, showing bronchiolar and alveolar epithelia; (C, D): PM10sum-treated lung parenchyma, showing inflammatory cells recruitment and AMs infiltration (arrows) in the connective surrounding terminal bronchioles and proximal alveolar sacs. Each figure represents the status evidenced examining 6 sham and 6 PM10sum-treated mice. A and C bars = 150 µm; B and D bars = 50 µm.
Immunohistochemical analyses of HO-1 expression in lung tissue 24 h after the third intratracheal instillation; the brown color reflects the site and intensity of HO-1 expression. (A): lung of sham mice; in the box, a control of the immunohistochemical reaction specificity, where the primary antibody has been avoided, in a PM10sum instilled mouse; (B): alveolar and peribronchiolar spaces in the lung of a sham mouse; (C, D): alveolar and peribronchiolar spaces in lungs of PM10sum-treated mice. Each figure represents the status evidenced examining 6 sham and 6 PM10sum-treated mice. A bar = 150 µm; B–D bars = 50 µm.
Prolonged or persistent exposure to PM is supposed to exert heavy adverse effects on cell homeostasis mediated by a direct particles cell interaction within the district that PM reaches (lung, myocardial or neuronal tissues), or by the induction of a chronic inflammation, resulting in a general systemic inflammation and sustained oxidative stress status .
In order to enhance the translocation of PM10sum we tested the threshold able to lengthen the PM10sum pro-inflammatory effects within lungs of our BALB/c mice. Previous published reports of particles exposures that do not yield significant alterations in markers of lung inflammation , , but do show significant changes in the expression of makers of inflammation and endothelial activation in extra-pulmonary tissues, are basically related to engine combustion derived particles. Indeed the translocation of these fine particles might be quick enough to directly exert systemic adverse effects even without overt pulmonary effects.
Inflammatory Response Elicited by PM10sum in Respiratory and Cardiovascular Systems
Lungs are the primary site of exposure to PM. In the BALf from healthy mice, the alveolar macrophages are the most numerous cells (>90%) and an influx of neutrophils is a sensitive indicator of inflammatory reaction , , . After three PM10sum intratracheal instillations, differential cell count evidenced a significant decrease of AMs percentage and a significant increase of PMNs percentage. A compensatory effect between the infiltration of PMNs and the extra-pulmonary migration of AMs is supposed to take place, thus explaining the absence of difference of the total cell count between sham and PM10sum-treated mice, as previously described .
Comparing to a single exposition , three repeated intratracheal instillations of PM10sum showed a lower PMNs percentage and a higher AMs percentage in the BALf of treated mice, confirming that the acute inflammatory status is still sustained but not heavily exacerbated, considering that the lung clearance mechanisms are still working.
24 h after a single PM10sum instillation, TNF-α concentration significantly increased in the BALf of treated mice ; nevertheless, 24 h after the last of three PM10sum instillations in a week (cumulative dose of 0.3 mg/mice/week), TNF-α concentration was basically unchanged comparing to sham. Moreover, histological findings have not shown signs of lung particle overloading. All together these observations claim for a mild ongoing lung inflammation triggered by PM10sum treatment scheme. This perfectly agree with the data coming from the extra-pulmonary translocation of lung administered particles both in humans and rodents , , , , , , , .
Several chemoattractants derived from macrophages and epithelial cells might be responsible for neutrophils recruitment in the lung, in particular IL-1β . 24 h after PM10sum treatment, the significant increase of IL-1β concentration in the BALf together with neutrophils infiltration suggests an ongoing and persistent lung inflammation . Indeed, the finding of increased MIP-2 lung mRNA and BALf MIP-2 concentration observed after 24 h in PM10sum-treated mice is in agreement with the quick induction in MIP-2 mRNA observed in rat lungs after in-vivo stimulation with IL-1β .
The increased MPO level in the BALf of PM10sum-treated mice perfectly correlates with lung neutrophils infiltration: indeed, MPO is an inflammatory marker released by degranulation of activated neutrophils promoted by IL-1β ,  and its activity increases after PM exposure .
The pro-inflammatory effect of PM with high LPS amount on lungs of treated mice has been already described . It is known that mediators produced in the lungs are able to translocate into the bloodstream  thus we analysed the presence of inflammatory markers also in blood and heart tissue of sham and PM10sum-treated mice.
The lack of increase in circulating cytokines after acute particles exposure might reflect that the PM induced inflammation is still localized (i.e. confined to the lungs); however, after repeated PM-exposure, the inflammatory cytokines released from lungs may have enough time to enter the systemic circulation and become detectable . Indeed, the increased total cell number, neutrophilia and high MPO levels, that we found in blood and plasma of PM10sum-treated mice, support the hypothesis of a systemic reaction and confirm the huge pro-inflammatory effect of PM10sum.
Endothelial Activation in Lungs and Cardiovascular System
An increase of vasoactive mediators may occur within the lungs and the systemic circulation both in presence or absence of lung inflammation . Previous studies have shown that PM exposure is associated with an increases in ET-1 level in-vivo and in-vitro , .
In the lung parenchyma, the ET-1 expression in macrophages as well as in endothelial and epithelial cells is stimulated by cytokines, LPS, air pollutant and ozone , ; ET-1 could promote acute lung injury, inducing cytokines production and activating neutrophils, releasing oxygen radicals . Indeed, the increased ET-1, that we found in the lungs of PM10sum-treated mice, once more confirms an ongoing lung inflammation linked to PM10sum exposure.
In the heart, ET-1 is synthesized by cardiomyocytes, fibroblasts, and endothelial cells; moreover, ET-1 directly stimulates cardiac fibroblasts to produce extracellular matrix proteins thus promoting myocardial fibrosis . The ET-1 expression has increased in cardiac tissue of rats daily exposed to diesel exhaust particles and to urban particulate matter . Confirming previous findings, the high ET-1 level observed in the heart of our PM10sum-treated mice strengthens the evidences of cardiac adverse effects elicited by PM10sum exposure.
A significant increase of ET-1 and sP-selectin were observed in plasma of PM10sum-treated mice. As previously discussed, lung cells may release ET-1 into the systemic circulation after PM exposure, as well as the vascular ET system may be up-regulated after PM exposure , . Increased levels of circulating ET-1 may trigger arterial vasoconstriction and influence the inflammatory response by promoting the recruitment of leukocytes into vessel walls . High ET-1 within the plasma correlates with acute coronary risk in concomitance to PM exposure .
Many data indicate that platelet adhesion to the endothelium is an event preceding the development of atherosclerotic lesions , contributing to the final stages of cardiovascular diseases . sP-selectin is a marker of activated interface blood-vasculature ; the significant increase in sP-selectin plasma concentration of PM10sum-treated mice suggested a systemic endothelial activation induced by PM10sum, which might be related to the high rate of cardiovascular hospitalization following PM10 exposure peak.
Finally, high MPO levels that we found in blood of PM10sum-treated mice could be related to an heavy endothelial dysfunction, as discussed by Brook et al. . The increase of MPO could be potentially harmful, due to the generation of hypochlorous acid, a compound toxic on bacteria and also onto host cells .
PM10sum Cytotoxic Effect in Lungs and Heart
A significant increase of LDH activity in the BALf was observed 24 h after the PM10sum third intratracheal instillation. However, this evidence was not supported by any changes in ALP activity, a specific marker of damage of type I pneumocytes and of proliferation of type II pneumocytes . The direct cytotoxic damage induced by PM10sum might be basically related to AMs and only marginally to pneumocytes, as previously we described for winter PM ; it is possible to hypothesize that the damage produced by repeated PM intratracheal instillations is a consequence of the amounts of metals and PAHs still associated to PM10sum.
The lung parenchyma necrosis and inflammation could explain the increase of Hsp70 levels that we found in the BALf after PM10sum instillation. Hsp70 might increase in the extracellular milieu, where it acts as a cytokine to human monocytes , after two events: an active release from epithelial cells or from mononuclear cells and a passive release when cells undergo necrosis .
Finally, in both lungs and heart, 24 h after the last PM10sum-treatment, the initiator Caspase 8 and the effector Caspase 3 were not active, despite the presence of pro-apoptotic inducers such as cytokines and hypochlorous acid, eventually produced by MPO in the BALf and blood, suggesting the existence of an on-going protection mechanism.
HO-1 and Hsp70 Induced Protection in Lung and Heart Parenchyma
HO-1 was significantly higher in the lungs of PM10sum-treated mice thus indicating the existence of a protection mechanism against oxidative stress and inflammation. In the lung parenchyma, HO-1 is expressed in various cells, including type II pneumocytes and AMs . Its role is to catabolize the heme group from the cytosol, thus generating CO, biliverdin (converted to bilirubin) and Fe2+ thus playing a protective role against inflammation and oxidative stress . Moreover, it has been hypothesized the existence of a post-translational down-regulation of cytochromes following the induction of HO-1, possibly related to a decrease in the heme group bioavailability . Consistently with this observations, we found a significant decrease in Cyp1B1 levels in the lung parenchyma of PM10sum-treated mice.
On the contrary, the absence of a significant increase of HO-1 in the heart of PM10sum-treated mice allows the increase of Cyp1B1, thus suggesting that soluble molecules PM-related could reach the heart parenchyma through the bloodstream.
Oxidative stress, LPS, cytokines, ER stress and protein unfolding induced by PM exposure, might promote the expression of heat shock proteins, such as Hsp70 or Hsp90 ; in particular, the intracellular Hsp70 has the ability to protect cells and tissues limiting the amount of inflammatory mediators . In both lung and heart parenchyma, Hsp70 showed a significant increase 24 h after the last PM10sum instillation, suggesting that the active protection system is not only related to the induction of HO-1. Graff et al.  demonstrated that the treatment of rat ventricular myocytes with Zn and V induced small but significant increases in the expression of Hsp70. Taking into account that Zn and V are soluble components PM-related and have the potential to be absorbed into the bloodstream and transported to the heart , , we hypothesize that these two metals could be in part accountable of the Hsp70 increase that we observed in PM10sum-treated mice.
Finally, both Hsp70 and HO-1, are important apoptotic inhibitors ,  which might thus explaining the absence of apoptosis cascade activation that we found in lungs and heart parenchyma of PM10sum treated mice.
In order to advance our studies on the PM10sum toxic effects, we considered a new class of molecules, miRNAs. In particular, according to literature, miR-21 is one of the miRNAs induced in mice lungs by exposure to LPS  and is involved in negative regulation of the signalling pathway of TLR-2  and TLR-4 , thus playing a key role in orchestrating the inflammatory process induced by LPS. Moschos et al.  and Sheedy et al.  have hypothesized that miR-21 might be involved in the resolution rather than in the induction of inflammation. So, increased miR21 levels that we found in the lungs of PM10sum-treated mice could be considered a marker of inflammatory status associated to an ongoing protection reaction. Consistent with this observation, the TLR4 pathway was not activated in the lungs of PM10sum-treated mice.
PM10sum Toxicity on Brain
The BBB endothelial cells play an essential role in maintaining brain homeostasis, actively transporting nutrients, and limiting the entrance to harmful components such as LPS and cytokines . In healthy brain, the endothelial cells express very low levels of adhesion molecules required for leukocyte migration , and expression of ET-1 increases BBB permeability in-vivo . Guo et al.  proposed that elevated plasma levels of ET-1, induced by PM10 exposure in-vivo, may promote ET-1 penetration within the brain either by active transport or by passive diffusion across a permeabilized BBB. The high ET-1 levels that we found in the brains of PM10sum-treated mice suggest a compromised BBB function , therefore allowing the translocation of smallest particles and/or of their soluble components within brain. It has been disclosed that ET-1 is a key factor in the development of PM10-mediated brain endothelial injury.
A possible mechanism by which PM exerts its toxic effect on brain cells has been proposed by Block et al. : it is supposed that particles might initiate the phagocytic activity of microglia, leading to the neurotoxic production of extracellular superoxide. As neurons are particularly vulnerable to oxidative damage, the ROS production can lead to neuron death. In our investigations, PM10sum-treatment causes an increase in brain HO-1 levels, probably as a consequence of oxidative stress induction.
The chronic induction of HO-1 can have both beneficial and detrimental effects on cellular metabolism. While exists plenty of evidence for the HO-1-mediated neuro-protection, a growing literature attesting the neuro-endangering effects of HO-1 activity is also at hand . Fe2+ produced by HO-1 can catalyze the production of free radicals through the Fenton’s chemistry, thus acting as a cytotoxic and oxidative stress inducer. Indeed, the excessive cellular amounts of free Fe2+ heme-derived resulting from HO-1 over-activity and dysregulation of iron metabolism  may be related to the pathogenesis of neuro-degenerative disorders .
Finally, it must be noted that the intratracheal administration route for PM has completely avoided the particles transport along the olfactory nerve. Alterations in the nasal mucosa, olfactory bulb, cortical and sub-cortical brain structures have been described in healthy dogs exposed to high levels of ambient air pollutants ; in addition, brain biomarkers of oxidative stress and tissue injury have been observed in mice exposed to concentrated ambient particles . Indeed, it is possible that ET-1 and HO-1 increased levels in the brain of our PM10sum-treated mice could be attenuated, while PM nasal inhalation could induce higher oxidative stress and endothelial activation in some regions of the central nervous system.
A repeated exposure of PM10sum in BALB/c mice leads to the induction of lungs inflammation, associated to cytokine production, PMNs infiltration and endothelium activation. Translocation of mediators, cytokines, ultrafine particles, LPS and/or metals associated to PM10sum from lungs to bloodstream triggers systemic adverse effects, involving heart and brain. The activation of endothelium/platelets interface that we found in PM10 exposed mice could explain the associations between short-term induced changes by inhalable particles and cardiovascular hospital admissions. Our results confirm the systemic toxic effect triggered by PM10sum mainly involving the respiratory and cardiovascular system in an inflammatory and pro-coagulant reaction, thus intending a correlation between PM exposure and cardiovascular diseases. However, lungs and heart might activate some putative protection mechanisms against inflammation and/or cytotoxicity thus supporting that compensatory mechanisms may occur within sub acute PM exposure.
PM10sum promotes brain endothelial activation and oxidative stress induction. In recent years, increasing evidences indicates Alzheimer and other neurodegenerative diseases at least partially mediated by oxidative stress and impaired BBB functions.
These findings may contribute to the knowledge of the interplay between PM exposure and cardiovascular diseases, the chronic oxidative stress generation and the development of neurodegenerative diseases. Future investigations should address the effects of lifetime air pollution exposure and aging related to the neuroinflammation and to the neurotoxicity.
Authors thank the researchers of the Atmospheric Chemistry group directed by Prof. E. Bolzacchini, operating in the POLARIS Research Center, Department of Environmental Science, University of Milano Bicocca, for their precious contribution in PM sampling and chemical characterization. Thanks to Prof. A. Pesci, Azienda Ospedaliera San Gerardo, Monza, for his precious contribution in microscope analyses. Valentina Tinaglia is recipient of PhD fellowship from Scuola di Dottorato di Medicina Molecolare, Università degli Studi di Milano. We thank Maria Carla Proverbio (Università degli Studi di Milano) for technical assistance with gene expression analysis.
Conceived and designed the experiments: FF GS PP. Performed the experiments: FF GS CB VT PM. Analyzed the data: FF GS CB PP. Contributed reagents/materials/analysis tools: GS PP CB PM MC. Wrote the paper: FF GS PP MC.
- 1. Schicker B, Kuhn M, Fehr R, Asmis LM, Karagiannidis C, et al. (2009) Particulate matter inhalation during hay storing activity induces systemic inflammation and platelet aggregation. Eur J Appl Physiol 105: 771–778. doi: 10.1007/s00421-008-0962-9
- 2. Brook RD, Franklin B, Cascio W, Hong Y, Howard G, et al. (2004) Air pollution and cardiovascular disease: a statement for healthcare professionals from the expert panel on population and prevention science of the American heart association. Circulation 109: 2655–2671. doi: 10.1161/01.cir.0000128587.30041.c8
- 3. Franchini M, Mannucci PM (2009) Particulate Air Pollution and cardiovascular risk: short-term and long-term effects. Thieme Medical Publishers Semin Thromb Hemost 35(7): 665–70. doi: 10.1055/s-0029-1242720
- 4. Schwarze PE, Øvrevik J, Låg M, Refsnes M, Nafstad P, et al. (2006) Particulate matter properties and health effects: consistency of epidemiological and toxicological studies. Hum Exp Toxicol 25: 559–579. doi: 10.1177/096032706072520
- 5. MacNee W, Donaldson K (2003) Mechanism of lung injury caused by PM10 and ultrafine particles with special reference to COPD. Eur Respir J 21(40): 47s–51s. doi: 10.1183/09031936.03.00403203
- 6. Utell MJ, Frampton MW (2000) Acute health effects of ambient air pollution: the ultrafine particle hypothesis. J Aerosol Med 13(4): 355–59. doi: 10.1089/jam.2000.13.355
- 7. Oberdoster G, Utell MJ (2002) Ultrafine particles in the urban air: to the respiratory tract – and beyond? Environ Health Perspect 110(8): 440–441. doi: 10.1289/ehp.110-a440
- 8. Farina F, Sancini G, Mantecca P, Gallinotti D, Camatini M, et al. (2011) The acute toxic effects of particulate matter in mouse lung are related to size and season of collection. Toxicol Lett 202: 209–217. doi: 10.1016/j.toxlet.2011.01.031
- 9. Franzetti A, Gandolfi I, Gaspari E, Ambrosini R, Bestetti G (2011) Seasonal variability of bacteria in fine and coarse urban air particulate matter. Appl Microbiol Biotechnol 90(2): 745–53. doi: 10.1007/s00253-010-3048-7
- 10. Camatini M, Corvaja V, Pezzolato E, Mantecca P, Gualtieri M (2012) PM10-biogenic fraction drives the seasonal variation of proinflammatory response in A549 cells. Environmental Toxicology 27(2): 63–73. doi: 10.1002/tox.20611
- 11. Sheedy FJ, Palsson-McDermott E, Hennessy EJ, Martin C, O’Leary JJ, et al. (2010) Negative regulation of TLR4 via targeting of the proinflammatory tumor suppressor PDCD4 by the microRNA miR-21. Nature Immunology 11: 141–147. doi: 10.1038/ni.1828
- 12. Gualtieri M, Mantecca P, Corvaja V, Longhin E, Perrone MG, et al. (2009) Winter fine particulate matter from Milan induces morphological and functional alterations in human pulmonary epithelial cells (A549). Toxicol Lett 188(1): 52–62. doi: 10.1016/j.toxlet.2009.03.003
- 13. Oberdörster G, Sharp Z, Atudorei V, Elder A, Gelein R, et al. (2004) Translocation of inhaled ultrafine particles to the brain. Inhal Toxicol 16(6–7): 437–45. doi: 10.1080/08958370490439597
- 14. Gunnison A, Chen LC (2005) Effects of subchronic exposures to concentrated ambient particles (CAPs) in mice. VI. Gene expression in heart and lung tissue. Inhal Toxicol 17(4–5): 225–33. doi: 10.1080/08958370590912851
- 15. Araujo JA, Barajas B, Kleinman M, Wang X, Bennett BJ, et al. (2008) Ambient particulate pollutants in the ultrafine range promote early atherosclerosis and systemic oxidative stress. Circ Res 102(5): 589–96. doi: 10.1161/circresaha.107.164970
- 16. Graff DW, Cascio WE, Rappold A, Zhou H, Huang YC, et al. (2009) Exposure to concentrated coarse air pollution particles causes mild cardiopulmonary effects in healthy young adults. Environ Health Perspect 117(7): 1089–94. doi: 10.1289/ehp0900558
- 17. Samet JM, Rappold A, Graff D, Cascio WE, Berntsen JH, et al. (2009) Concentrated ambient ultrafine particle exposure induces cardiac changes in young healthy volunteers. Am J Respir Crit Care Med 179(11): 1034–42. doi: 10.1164/rccm.200807-1043oc
- 18. Kreyling WG, Hirn S, Schleh C (2010) Nanoparticles in the lung. Nat Biotechnol 28(12): 1275–6. doi: 10.1038/nbt.1735
- 19. Hasegawa G, Hirano M, Ishihara Y (2011) Differential gene expression associated with inflammation and blood pressure regulation induced by concentrated ambient particle exposure. Inhal Toxicol 23(14): 897–905. doi: 10.3109/08958378.2011.625058
- 20. Chen J, Tan M, Nemmar A, Song W, Dong M, et al. (2006) Quantification of extrapulmonary translocation of intratracheal-instilled particles in vivo in rats: effect of lipopolysaccharide. Toxicology 222(3): 195–201. doi: 10.1016/j.tox.2006.02.016
- 21. Cao Q, Zhang S, Dong C, Song W (2007) Pulmonary responses to fine particles: differences between the spontaneously hypertensive rats and Wistar Kyoto rats. Toxicol Lett 171(3): 126–37. doi: 10.1016/j.toxlet.2007.05.007
- 22. Naota M, Shimada A, Morita T, Inoue K, Takano H (2009) Translocation pathway of the intratracheally instilled C60 fullerene from the lung into the blood circulation in the mouse: possible association of diffusion and caveolae-mediated pinocytosis. Toxicol Pathol 37(4): 456–62. doi: 10.1177/0192623309335059
- 23. Emmerechts J, Alfaro-Moreno E, Vanaudenaerde BM, Nemery B, Hoylaerts MF (2010) Short-term exposure to particulate matter induces arterial but not venous thrombosis in healthy mice. J Thromb Haemost (12): 2651–61. doi: 10.1111/j.1538-7836.2010.04081.x
- 24. Happo MS, Salonen RO, Hälinen AI, Jalava PI, Pennanen AS, et al. (2010) Inflammation and tissue damage in mouse lung by single and repeated dosing of urban air coarse and fine particles collected from six European cities. Inhal Toxicol 22(5): 402–16. doi: 10.3109/08958370903527908
- 25. Saunders V, Breysse P, Clark J, Sproles A, Davila M, et al. (2010) Particulate matter-induced airway hyperresponsiveness is lymphocyte dependent. Environ Health Perspect 118(5): 640–6. doi: 10.1289/ehp.0901461
- 26. Perrone MG, Larsen BR, Ferrero L, Sangiorgi G, De Gennaro G, et al. (2012) Sources of high PM2.5 concentrations in Milan, Northern Italy: molecular marker data and CMB modelling. Sci Total Environ 414: 343–55. doi: 10.1016/j.scitotenv.2011.11.026
- 27. Bivas-Benita M, Zwier R, Junginger HE, Borchard G (2005) Non-invasive pulmonary aerosol delivery in mice by the endotracheal route. Eur J Pharm Biopharm 61(3): 214–8. doi: 10.1016/j.ejpb.2005.04.009
- 28. Mantecca P, Sancini G, Moschini E, Farina F, Gualtieri M, et al. (2009) Lung toxicity induced by intratracheal instillation of size-fractionated tire particles. Toxicol Lett 189: 206–214. doi: 10.1016/j.toxlet.2009.05.023
- 29. Mantecca P, Farina F, Moschini E, Gallinotti D, Gualtieri M, et al. (2010) Comparative acute lung inflammation induced by atmospheric PM and size-fractionated tire particles. Toxicol Lett 198: 244–254. doi: 10.1016/j.toxlet.2010.07.002
- 30. Pope CA III, Dockery DW (2006) Health effects of fine particulate air pollution: lines that connect. J Air Waste Manag Assoc 56: 709–742. doi: 10.1080/10473289.2006.10464485
- 31. Lund AK, Lucero JA, Lucas S, Madden MC, McDonald JD, et al. (2009) Vehicular emissions induce vascular MMP-9 expression and activity via endothelin-1 mediated pathways. Arterioscler Thromb Vasc Biol 29: 511–517. doi: 10.1161/atvbaha.108.176107
- 32. Campen MJ, Lund AK, Knuckles TL, Conklin DJ, Bishop B, et al. (2010) Inhaled diesel emissions alter atherosclerotic plaque composition in ApoE−/− mice. Toxicol Appl Pharmacol 242: 310–317. doi: 10.1016/j.taap.2009.10.021
- 33. Henderson RF (2005) Use of bronchoalveolar lavage to detect respiratory tract toxicity of inhaled material. Exp Toxicol Pathol 57: 155–159. doi: 10.1016/j.etp.2005.05.004
- 34. Xu WB, Haddad EB, Tsukagoshi H, Adcock I, Barnes PJ, et al. (1995) Induction of macrophage inflammatory protein 2 gene expression by interleukin 1 beta in rat lung. Thorax. 50(11): 1136–1140. doi: 10.1136/thx.50.11.1136
- 35. Guo L, Zhu N, Guo Z, Li G, Chen C, et al. (2012) Particulate matter (PM10) exposure induces endothelial dysfunction and inflammation in rat brain. Journal of Hazardous Materials 213–214: 28–37. doi: 10.1016/j.jhazmat.2012.01.034
- 36. Dularay B, Dieppe PA, Elson CJ (1990) Depressed degranulation response of synovial fluid polymorphonuclear leucocytes from patients with rheumatoid arthritis to IgG aggregates. Clin Exp Immunol 79(2): 195–201. doi: 10.1111/j.1365-2249.1990.tb05178.x
- 37. Shah KB, Kop WJ, Christenson RH, Diercks DB, Kuo D, et al. (2009) Lack of diagnostic and prognostic utility of circulating plasma myeloperoxidase concentrations in patients presenting with dyspnea. Clin Chem 55(1): 59–67. doi: 10.1373/clinchem.2008.108159
- 38. Brook RD, Rajagopalan S, Pope CA III, Brook JR, Bhatnagar A, et al. (2010) Particulate matter air pollution and cardiovascular disease: an update to the scientific statement from the American Heart Association. Circulation 121: 2331–2378. doi: 10.1161/cir.0b013e3181dbece1
- 39. Gilmour MI, McGee J, Duvall RM, Dailey L, Daniels M, et al.. (2007) Comparative Toxicity of Size-Fractionated Airborne Particulate Matter Obtained from Different Cities in the United States. Inhalation Toxicology (Suppl. 1): 7–16.
- 40. Kido T, Tamagawa E, Bai N, Suda K, Yang HH, et al. (2011) Particulate matter induces translocation of IL-6 from the lung to the systemic circulation. Am J Respir Cell Mol Biol 44(2): 197–204. doi: 10.1165/rcmb.2009-0427oc
- 41. MohanKumar SMJ, Campbell A, Block M, Veronesi B (2008) Particulate matter, oxidative stress and neurotoxicity. NeuroToxicology 29(3): 479–488. doi: 10.1016/j.neuro.2007.12.004
- 42. Chauhan V, Breznan D, Thomson E, Karthikeyan S, Vincent R (2005) Effects of ambient air particles on the endothelin system in human pulmonary epithelial cells (A549). Cell Biol. Toxicol 21: 191–205. doi: 10.1007/s10565-005-0162-x
- 43. Calderón-Garcidueñas L, Franco-Lira M, Torres-Jardon R, Henríquez-Roldán C, Barragan Mejía G, et al. (2007) Pediatric respiratory and systemic effects of chronic air pollution exposure: nose, lung, heart, and brain pathology. Toxicol Pathol 35: 1–9. doi: 10.1080/01926230601059985
- 44. Fagan KA, McMurtry IF, Rodman DM (2001) Role of endothelin-1 in lung disease. Respir Res 2(2): 90–101. doi: 10.1186/rr44
- 45. Thomson E, Kumarathasan P, Goegan P, Aubin RA, Vincent R (2005) Differential regulation of the lung endothelin system by urban particulate matter and ozone. Toxicol Sci 88: 103–113. doi: 10.1093/toxsci/kfi272
- 46. Khimji AK, Rockey DC (2010) Endothelin–biology and disease. Cell Signal 22(11): 1615–25. doi: 10.1016/j.cellsig.2010.05.002
- 47. Langrish JP, Lundbäck M, Mills NL, Johnston NR, Webb DJ, et al. (2009) Air Pollution and Endothelin. Contribution of Endothelin 1 to the Vascular Effects of Diesel Exhaust Inhalation in Humans. Hypertension 54: 910–915. doi: 10.1161/hypertensionaha.109.135947
- 48. Kang YJ, Li Y, Zhou Z, Roberts AM, Cai L, et al. (2002) Elevation of serum endothelins and cardiotoxicity induced by particulate matter (PM2.5) in rats with acute myocardial infarction. Cardiovasc Toxicol 2(4): 253–61. doi: 10.1385/ct:2:4:253
- 49. Stow LR, Jacobs ME, Wingo CS, Cain BD (2011) Endothelin-1 gene regulation. The FASEB Journal 25(1): 16–28. doi: 10.1096/fj.10-161612
- 50. van Eeden SF, Yeung A, Quinlam K, Hogg JC (2005) Systemic response to ambient particulate matter: relevance to chronic obstructive pulmonary disease. Proc Am Thorac Soc 2(1): 61–7. doi: 10.1513/pats.200406-035ms
- 51. Massberg S, Brand K, Gruner S, et al. (2002) A critical role of platelet adhesion in the initiation of atherosclerotic lesion formation. J Exp Med 196: 887–96. doi: 10.1084/jem.20012044
- 52. Weinberger I, Fuchs J, Davidson E, Rotenberg Z (1992) Circulating aggregated platelets, number of platelets per aggregate, and platelet size during acute myocardial infarction. Am J Cardiol 70: 981–983. doi: 10.1016/0002-9149(92)90347-2
- 53. Burger PC, Wagner DD (2003) Platelet P-selectin facilitates atherosclerotic lesion development. Blood 101: 2661–2666. doi: 10.1182/blood-2002-07-2209
- 54. Fehrenbach H (2001) Alveolar epithelial type II cell: defender of the alveolus revisited. Respir Res 2: 33–46.
- 55. Asea A, Kraeft SK, Kurt-Jones EA, Stevenson MA, Chen LB, et al. (2000) HSP70 stimulates cytokine production through a CD14-dependant pathway, demonstrating its dual role as a chaperone and cytokine. Nat Med 6(4): 435–42.
- 56. Svensson PA, Asea A, Englund MCO, Bausero MA, Jernas M, et al. (2006) Major role of HSP70 as a paracrine inducer of cytokine production in human oxidized LDL treated macrophages. Atherosclerosis 185(1): 32–38. doi: 10.1016/j.atherosclerosis.2005.05.007
- 57. Fredenburgh LE, Perrella MA, Mitsialis SA (2007) The Role of Heme Oxygenase-1 in Pulmonary Disease. Am J Resp Cell Mol Biol 36(2): 158–165. doi: 10.1165/rcmb.2006-0331tr
- 58. Choi BM, Pae HO, Chung HT (2003) Nitric oxide priming protects nitric oxide-mediated apoptosis via heme oxygenase-1 induction. Free Rad Biol Med 34: 1136–1145. doi: 10.1016/s0891-5849(03)00064-9
- 59. Bessette EE, Fasco MJ, Pentecost BT, Reilly A, Kaminsky LS (2009) Investigations of the posttranslational mechanism of arsenite-mediated downregulation of human cytochrome P4501A1 levels: the role of heme oxygenase-1. J Biochem Mol Toxicol 23(3): 222–32. doi: 10.1002/jbt.20283
- 60. Watterson TL, Hamilton B, Martin R, Coulombe RA (2009) Urban Particulate Matter Causes ER Stress and the Unfolded Protein Response in Human Lung Cells. Toxicological Sciences 112: 111–122. doi: 10.1093/toxsci/kfp186
- 61. Jacquier-Sarlin MR, Fuller K, Dinh-Xuan AT, Richard MJ, Polla BS (1994) Protective effects of hsp70 in inflammation. Experientia 50: 1031–1048. doi: 10.1007/bf01923458
- 62. Graff DW, Cascio WE, Brackhan JA, Devlin RB (2004) Metal particulate matter components affect gene expression and beat frequency of neonata rat ventricular myocytes. Environmental Health Perspectives 112(7): 792–798. doi: 10.1289/txg.6865
- 63. Bourotte CLM, Sanchez-Ccoyllo OR, Forti MC, Melfi AJ (2011) Chemical composition of atmospheric particulate matter soluble fraction and meteorological variables in Sao Paulo state, Brazil. Revista Brasileira de Meteorologia 26(3): 419–432. doi: 10.1590/s0102-77862011000300008
- 64. Kang J, Yun YD, Nakano K, Nagai N (2005) Expression of Hsp70 in Acute Lung Injury Induced by Lipopolysaccharide. Journal of Hard Tissue Biology 14: 1. doi: 10.2485/jhtb.14.28
- 65. Reiter TA, Demple B (2005) Carbon monoxide mediates protection against nitric oxide toxicity in HeLa cells. Free Rad Biol Med 39: 1075–1088. doi: 10.1016/j.freeradbiomed.2005.05.023
- 66. Moschos SA, Williams AE, Perry MM, Birrell MA, Belvisi MG, et al. (2007) Expression profiling in vivo demonstrates rapid changes in lung microRNA levels following lipopolysaccharide-induced inflammation but not in the anti-inflammatory action of glucocorticoids. BMC Genomics 8: 240. doi: 10.1186/1471-2164-8-240
- 67. Case SR, Martin RJ, Jiang D, Minor MN, Chu HW (2011) MicroRNA-21 inhibits toll-like receptor 2 agonist-induced lung inflammation in mice. Exp Lung Res 37(8): 500–508. doi: 10.3109/01902148.2011.596895
- 68. Reijerkerk A, Lakeman KA, Drexhage JA, van Het Hof B, van Wijck Y, et al. (2012) Brain endothelial barrier passage by monocytes is controlled by the endothelin system. J Neurochem 121(5): 730–7. doi: 10.1111/j.1471-4159.2011.07393.x
- 69. Lossinsky AS, Shivers RR (2004) Structural pathways for macromolecular and cellular transport across the blood brain barrier during inflammatory conditions. Histol Histopath 19: 535–64.
- 70. Block ML, Hong JS (2005) Microglia and inflammation-mediated neurodegeneration: multiple triggers with a common mechanism. Progress in Neurobiology 76: 77–98. doi: 10.1016/j.pneurobio.2005.06.004
- 71. Schipper HM (2004) Heme oxygenase-1: transducer of pathological brain iron sequestration under oxidative stress. Ann N Y Acad Sci 1012: 84–93. doi: 10.1196/annals.1306.007
- 72. Gozzelino R, Jeney V, Soares MP (2010) Mechanisms of Cell Protection by Heme Oxygenase-1. Annual Review of Pharmacology and Toxicology 50: 323–354. doi: 10.1146/annurev.pharmtox.010909.105600
- 73. Nader A, Attallah K (2008) Pharmacological and Clinical Aspects of Heme Oxygenase. Pharmacological Reviews 60(1): 79–127. doi: 10.1124/pr.107.07104
- 74. Calderon-Garciduenas L, Azzarelli B, Acuna H, Garcia R, Gambling TM, et al. (2002) Air pollution and brain damage. Toxicologic Pathology 30(3): 373–389. doi: 10.1080/01926230252929954
- 75. Campbell A, Oldham M, Becaria A, Bondy SC, Meacher D, et al. (2005) Particulate matter in polluted air may increase biomarkers of inflammation in mouse brain. NeuroToxicology 26: 133–140. doi: 10.1016/j.neuro.2004.08.003