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Abstract |
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Diesel exhaust particles (DEP) are known to enhance inflammatory responses in human volunteers. In cultured human
bronchial epithelial (16HBE) cells, they induce the release of
proinflammatory cytokines after triggering transduction pathways, including nuclear factor (NF)-
B activation and mitogen-activated protein kinase (MAPK) phosphorylation. This study
compares the effects of native DEP (nDEP), organic extracts
of DEP (OE-DEP), and carbonaceous particles, represented by
stripped DEP (sDEP) and carbon black particles (CB), in order
to clarify their respective roles. OE-DEP and nDEP induce granulocyte macrophage colony-stimulating factor (GM-CSF) release,
NF-
B activation, and MAPK phosphorylation. The carbonaceous core generally induces less intense effects. Reactive oxygen species are produced in 16HBE cells and are involved in
GM-CSF release and in the stimulation of NF-
B DNA binding by nDEP and OE-DEP. We demonstrate, for the first time, in
airway epithelial cells in vitro that nDEP induce the expression
of the CYP1A1, a cytochrome P450 specifically involved in
polycyclic aromatic hydrocarbons metabolism, thereby demonstrating the critical role of organic compounds in the DEP-induced proinflammatory response. Understanding the respective contributions of DEP components in these effects is
important for vehicle manufacturers in order to improve their
exhaust gas post-treatment technologies. In conclusion, the
DEP-induced inflammatory response in airway epithelial cells mainly involves organic compounds such as PAH, which induce CYP1A1 gene expression.
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Introduction |
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Air pollution is now an important issue for human health in industrialized countries. Both gaseous and particulate emissions resulting from motor vehicle traffic contribute to this phenomenon. Epidemiologic studies suggested that exposure to air pollutants generated by petrol- and diesel-burning engines worsens the symptoms of lung diseases such as asthma and rhinitis (1, 2). Among the various environmental factors, diesel exhaust particles (DEP) must be taken into account as they are considered to be among the most abundant components of particulate matter with an aerodynamic diameter < 2.5 µm (PM 2.5), but their real impact on air quality has not been fully elucidated. In vivo experiments have revealed that nasal challenges of humans by DEP result in a local increase in immunoglobulin (Ig) E and cytokine production (3). DEP can therefore induce inflammation of the respiratory tract, but the cellular events and the physicochemical characteristics of DEP involved in the induction of this effect are still unclear.
DEP are composed of carbonaceous particles with adsorbed and condensed hydrocarbons and sulfur (6). This
organic fraction could represent up to 60% of the total mass
of the particle in the absence of an exhaust gas treatment
system and contains polycyclic aromatic hydrocarbons
(PAH). The small size of DEP allows their penetration
into the lung and their potential accumulation at the bronchiolar and alveolar levels. However, airway epithelial cells
and alveolar macrophages remove most of the particles by mucociliary clearance and phagocytosis, respectively. Macrophages and epithelial cells are therefore the first cell
types encountering DEP, which could initiate the inflammatory response. In vitro investigations have shown that
both cell types released cytokines involved in inflammation when exposed to DEP (7). We have previously shown that native DEP are taken up by airway epithelial
cells and stimulate the release of proinflammatory cytokines interleukin (IL)-8, IL-1
, and granulocyte macrophage colony-stimulating factor (GM-CSF), which are involved in allergic diseases (11). This process occurs at
noncytotoxic concentrations and involves the regulation of
gene expression. Reverse transcriptase/polymerase chain
reaction studies have shown that DEP-induced GM-CSF
release is accompanied by an increase of the GM-CSF
messenger RNA (mRNA) level in human bronchial epithelial (16HBE) cells (12) and by the activation of nuclear
factor (NF)-
B (13, 14), a transcription factor known to
regulate the gene expression of many proinflammatory cytokines such as the GM-CSF (15). DEP also trigger signaling pathways in epithelial cells such as the phosphorylation of mitogen-activated protein kinase (MAPK) Erk 1/2
and p38 (14, 16). However, the DEP properties responsible for these events have not yet been identified. One hypothesis is that reactive oxygen species (ROS) could explain the cellular and molecular effects triggered after DEP exposure (17).
In the present study, to clarify the contribution of each
component of DEP in the induction of the inflammatory
response, we systematically compared the effects induced
by native DEP (nDEP) with those induced by organic extracts of DEP (OE-DEP) and the carbonaceous core, represented either by stripped DEP (sDEP) or by carbon
black particles (CB). This comparison was performed in
16HBE cells on the various DEP-induced cellular events,
such as GM-CSF release, NF-
B activation, and MAPK
phosphorylation. The involvement of ROS in the effects
induced by each component was also analyzed. In addition, we investigated the expression of the CYP1A1 gene,
which is responsible for PAH metabolism.
We present evidence that, even if the carbonaceous
core is not totally devoid of effect, organic compounds are
the main contributors to the DEP-induced GM-CSF release, I
B degradation, NF-
B DNA binding, and MAPK
Erk1/2 phosphorylation. ROS are involved in the effects
induced by organic compounds and nDEP. We also demonstrated, for the first time, that nDEP induce CYP1A1
gene expression.
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Materials and Methods |
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Reagents
Diesel particulate matter SRM 1650 was purchased from the National Institute of Standards and Technology (Gaithersburg, MD) and are characterized by a 20.2 ± 0.4% of dichloromethane extractable mass and 1.33 ± 0.35 µg/g of benzo(a)pyrene (BaP). CB (FR103, 95 nm diameter) was obtained from Degussa (Frankfurt, Germany). Stock solutions of particles were prepared by suspension in a 0.04% (wt/vol) solution of dipalmitoylphosphatidylcholine (DPPC) in distilled water and by ultrasonication twice for 5 min at maximum power (100 W) (Vibra-cell; Bioblock Scientific, Illkirch, France). Particles were used at 10 µg/cm2. Concentrations are expressed in µg/cm2 because particles rapidly sediment onto the culture. DEP were extracted by dichloromethane in a soxhlet apparatus, and the extract obtained was dried, then redissolved in dimethyl sulfoxide. The collected particles were extracted a second time to ensure total extraction. Benzo(a)pyrene, a typical PAH present on DEP, was tested at 250, 50, and 0.25 µg/ml in comparison with OE-DEP at 15 µg/ml. It was used at 250 µg/ml in the CYP1A1 experiments as a positive control. All chemicals were purchased from Sigma (Saint Quentin Fallavier, France) except when otherwise specified.
Cell Culture and Stimulation
An SV-40 large T antigen transformed human airway epithelial cell line, 16HBE14o- (16HBE), kindly provided by Dr. D. C. Gruenert (18) (Colchester, VT), was cultured in Dulbecco's modified Eagle's medium-nutrient mixture F12 Ham (DMEM/F12) (GIBCO BRL, Cergy Pontoise, France) supplemented with penicillin (100 U/ml), streptomycin (100 µg/ml), glutamine (1%), fungizone (0.125 µg/ml; GIBCO BRL), and ultroserG (2%; GIBCO BRL). Cells were cultured on collagen (type I, 4 µg/cm2). At the time of treatment, ultroserG was not added to DMEM/F12. Cultures were incubated in humidified 95% air with 5% CO2 at 37°C. Different inhibitors and antioxidants were tested on the 16HBE cells. The antioxidants dimethylthiourea (DMTU) and N-acetylcysteine (NAC) were dissolved in water and used at 10 and 10 mM, respectively. PD98059, an MAPK/extracellular regulated kinase kinase inhibitor (Tebu, Le Perray-en-Yvelines, France), and SB203580, a p38 kinase inhibitor (Calbiochem, Meudon, France), were prepared in DMSO and used at 10 and 1 µM, respectively. The antioxidants and inhibitors were used for a 1-h pretreatment and were kept in the culture medium during treatment of the cells. DMSO at 0.1% was added to the control and to the samples when necessary.
GM-CSF Assay
After 24 h of treatment, the supernatants of subconfluent cells of
the 16HBE cell line cultured in 12-well dishes were centrifuged before being frozen at
80°C until use. The GM-CSF concentration released into the culture supernatant was measured with the
human GM-CSF enzyme-linked immunosorbent assay kit (Amersham Life Science, Les Ulis, France).
Electrophoretic Mobility Shift Assay
After treatment, nuclear extracts were isolated from subconfluent 16HBE cells (3 × 106) cultured in 25-cm2 flasks as described
by Staal and coworkers (19). Briefly, cells were washed and removed by scraping in Tris-buffered saline (TBS) (25 mM Tris-HCl, 136 mM NaCl, 2.7 mM KCl, pH 7.4), and pelleted. The pellets were resuspended in 400 µl of ice-cold hypoosmotic buffer
(10 mM Hepes, 10 mM KCl, 2 mM MgCl2, 0.1 mM ethylenediaminetetraacetic acid [EDTA], pH 7.8) supplemented with 0.5 mM
dithiothreitol (DTT), 0.5 mM phenylmethylsulfonylfluoride
(PMSF), 1 µg/ml antipain, 0.3 µg/ml leupeptin, 0.5 µg/ml pepstatin. Nuclei were spun down at 16,000 × g for 30 s after the addition of a 10% Nonidet P-40 solution, then resuspended in 40 µl of
a hyperosmotic buffer (50 mM Hepes, 50 mM KCl, 300 mM
NaCl, 0.1 mM EDTA, 10% glycerol, pH 7.8) supplemented with
0.5 mM DTT, 0.5 mM PMSF, 1 µg/ml antipain, 0.3 µg/ml leupeptin, 0.5 µg/ml pepstatin. Nuclear proteins were extracted, incubating the nuclear suspension for 30 min at 4°C, with a slow rotation followed by a 16,000 × g centrifugation for 10 min. The
supernatants that contain the nuclear extracts were stored at
80°C until used. They were complexed with radiolabeled double-stranded oligonucleotides containing a consensus NF-
B site
(Promega, Lyon, France) and loaded onto 5% polyacrylamide gel as described by Baeza-Squiban and associates (13).
Western Blot Analysis
Total proteins were collected by scraping the 16HBE cell cultures (3 × 106, 25-cm2 flask) supplemented with solubilization
buffer (pH 7.4, 0.06 M Tris, 3% sodium dodecyl sulfate [SDS],
5%
-mercaptoethanol, 10% glycerol, 1 mM PMSF), boiled, and
run on 12% SDS-polyacrylamide gel electrophoresis gels at 150 V. Prestained molecular-mass markers (Bio-Rad, Hercules, CA)
were run on adjacent lanes. Samples were normalized for protein
contents before loading with the Bicinchoninique Acid (BCA) kit
(Pierce, Rockford, IL). Electrophoresed proteins were electroblotted onto nitrocellulose membrane, and the blots were blocked
with 5% milk in TBS, pH 7.6 (0.02 M Tris, 0.135 M NaCl) containing 0.1% Tween-20. The membranes were incubated for 2 h
with the primary antibody in 1% milk in TBS-0.1% Tween-20. Polyclonal rabbit antibodies against phospho-Erk 1/2, Erk 1/2, and phospho-p38 (New England Biolabs, Beverly, MA) were used
at a dilution of 1/2,000. The mouse monoclonal antibody 10B
against I
B
was kindly provided by Dr. R. Hay (Edinburgh,
UK) and used at a dilution of 1/100. The rabbit polyclonal antibody against
-tubulin (Sigma) was used as an internal reference
to control equal protein loading. Horseradish peroxidase-conjugated antirabbit or mouse IgG was used as a secondary antibody
(New England Biolabs) at a dilution of 1/5,000. Bands were detected with chemiluminescence reagents and film according to
the manufacturer's instructions (NEN, Boston, MA).
RNA Isolation and Northern Blot Analysis
Total cellular RNA was isolated from subconfluent cells (10 × 106), cultured in 75-cm2 flasks, by using Tri Reagent according to the manufacturer's instructions. The amount of RNA in aqueous solution was determined by absorbance at 260 nm. Equal amounts (30 µg) of total cellular RNA were size separated by 0.65 M formaldehyde-agarose (0.8%) gel electrophoresis and transferred onto Hybond-Plus membranes (Amersham Life Science) using 10× saline sodium citrate (SSC) buffer (1×: 150 mM NaCl, 15 mM sodium citrate). The blot was then baked for 2 h at 80°C and hybridized to specific probes. The blots were prehybridized at 65°C in Rapid Hybrid solution (Amersham Life Science) and hybridized overnight at 65°C with 1 to 5 × 107 cpm/ml of 32P-labeled complementary DNAs (cDNAs). Probes were synthesized from cDNAs with the Megaprime DNA labeling kit (Amersham Life Science) according to the manufacturer's instructions. After hybridization, the blots were washed for 30 min at 65°C with 2× SSC, then 1× SSC, and then 0.5× SSC, in the presence of 0.1% SDS. The membranes were exposed and the radioactivity was quantified with a PhosphorImager and ImageQuant software (Molecular Dynamics, Sunnyvale, CA).
The cDNA probe of the CYP1A1 gene was a generous gift from Dr. I. De Waziers (Paris, France) (20).
Dichlorofluorescein Staining
Dichlorofluorescein-diacetate (DCFH-DA) is a nonfluorescent compound that enters the cells and is trapped by removal of the diacetate group. Upon interaction with peroxides, dichlorofluorescein (DCF) is converted into a fluorescent product. 16HBE cells cultured in 12-well dishes (1 × 106) were incubated with DCFH-DA (20 µM) in Hanks' balanced salt solution (HBSS) for 20 min at 37°C in the dark. DCFH-DA was removed and the cells were then washed with HBSS and treated. Cells were collected by trypsination. Propidium iodide (3 µg/ml) was added to the samples, which were then immediately subjected to flow cytometric analysis.
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Results |
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Role of Organic Compounds in DEP-Induced GM-CSF Release
GM-CSF release was used as a biomarker of the proinflammatory response induced by DEP in 16HBE cells (12) in order to determine which component of nDEP is the most critical one for this response. For this purpose, nDEP- induced GM-CSF release was compared with that induced by OE-DEP, BaP, one of the numerous DEP organic compounds used as a model of PAH, sDEP, and CB that were used as surrogates of the carbonaceous core of DEP, which are known to be endocyted to the same extent as nDEP (11).
The various types of particles were used at 10 µg/cm2. At this concentration, nDEP are not cytotoxic and clearly induce a GM-CSF release (11, 12). nDEP and sDEP from standard reference DEP (SRM 1650), and CB exhibited different activities after 24 h of treatment (Figure 1). nDEP induced a 4.7-fold increase in GM-CSF release compared with the control, whereas sDEP had a lower but significant effect and CB had no effect, suggesting a role of organic compounds in this response. OE-DEP tested at 15 µg/ml, which is in the range of the concentration of organic compounds present on 10 µg/cm2 of DEP, induced a marked increase of GM-CSF release (3.7 fold), suggesting their participation in the induction of this proinflammatory response. Their effect was compared with that of BaP. BaP at 50 and 0.25 ng/ml had a slight but significant effect on GM-CSF release, which became stronger at 250 ng/ml, but always remained lower than that induced by OE-DEP.
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These data highlight the role of organic compounds in DEP-induced GM-CSF release.
Role of Organic Compounds on DEP-Induced
NF-
B Activation
nDEP-induced GM-CSF release in 16HBE cells has been
previously shown to be associated with increased GM-CSF
gene transcription (12), and nDEP has been shown to induce a time- and dose-dependent increase in NF-
B DNA
binding (13, 14). The contribution of organic compounds
to NF-
B activation was investigated by studying both degradation of the inhibitory subunit I
B
by Western blot and NF-
B DNA binding by electrophoretic mobility shift
assay (EMSA). In the cytoplasm of nonstimulated cells,
NF-
B binds to I
B and is maintained in an inactive form.
I
B degradation after stimulation allows translocation of
NF-
B to the nucleus and its subsequent binding to DNA.
A kinetic study of the degradation of I
B
(Figure 2) was
performed in 16HBE cells with or without treatment by either nDEP or OE-DEP. Western blot of total cellular proteins was performed using a specific antibody against
I
B
(Mouse antibody [Mab] 10) or a control antibody
against
-tubulin and revealed that nDEP induced I
B
degradation after 2 to 4 h of exposure. OE-DEP also induced a similar I
B degradation.
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The time-course study of NF-
B DNA binding induced
by nDEP and OE-DEP revealed that the kinetics of activation of NF-
B DNA binding was different for these
compounds (Figure 3). Indeed, whereas OE-DEP activated
NF-
B DNA binding after only 1 h of exposure, the nDEP
effect clearly increased after 2 and 4 h of treatment. The
carbonaceous core could play a role in this response as an increase of NF-
B DNA binding was observed with CB (Figure 3) and with sDEP (data not shown). Taken together,
these findings suggest that the organic compounds play an
important but not exclusive role in NF-
B activation.
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DEP-Induced CYP1A1 mRNA Level
The prevalent role of organic compounds in the DEP-induced effects could be owing to their PAH content, known to induce the CYP1A1 gene. The relative amount of the CYP1A1 mRNA was determined by Northern blot analysis of total RNA from 16HBE cells with or without treatment by nDEP (10 µg/cm2), OE-DEP (15 µg/ml), sDEP (10 µg/cm2), or BaP (250 µg/ml). The CYP1A1 mRNA level was markedly increased in nDEP- and OE-DEP-treated cells in comparison with their respective control cells (Figure 4). This increase was slightly lower than that with the positive control BaP. sDEP had a very weak effect. The faint band observed could represent the effect of a small amount of PAH that could not be extracted from the DEP. It is likely that the induced CYP1A1 contributes to the metabolism of these PAH.
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Involvement of ROS in a DEP-Induced Effect
Because the metabolism of organic compounds may lead
to the production of ROS and because NF-
B is a redox-sensitive transcription factor (19), we investigated whether
ROS were involved in the nDEP- or OE-DEP-induced effects. For this purpose, we studied the effect of radical
scavengers DMTU (10 mM) and NAC (10 mM). GM-CSF
release induced by nDEP, OE-DEP, and CB in 16HBE
cells was markedly decreased by DMTU and NAC (Figure
5A). A similar degree of inhibition was observed for nDEP
and extracts. NF-
B DNA binding induced by nDEP or
OE-DEP was attenuated by DMTU (Figure 5B). However,
the DMTU appeared to be less effective on OE-DEP- induced NF-
B DNA binding than on nDEP-induced
NF-
B DNA binding, suggesting that other pathways could
be involved in NF-
B activation.
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nDEP and OE-DEP Induced ROS Production
Because nDEP- and OE-DEP-induced GM-CSF release
and NF-
B activation were inhibited by antioxidants, ROS
generation was measured using the DCFH-DA probe,
which yields a fluorescent product by interaction with peroxides. Treatment of 16HBE cells with nDEP and OE-DEP generated a 4.6- and 4.7-fold increase, respectively, in the mean intensity of DCF fluorescence after 4 h of exposure (Table 1).
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DEP-Induced MAPK Activation
To study the signal transduction pathways triggered by nDEP, OE-DEP, and sDEP, we investigated the effect of Erk1/2 and p38 inhibitors (PD98059 [10 µM] and SB203580 [1 µM], respectively) on GM-CSF release, and the phosphorylation of Erk1/2 and p38 after various treatment times (30 min, 2 h, and 4 h). GM-CSF release induced by nDEP and OE-DEP was markedly decreased by PD98059 (Figure 6A). In contrast, SB203580 had no effect on nDEP-induced GM-CSF release, but slightly reduced OE-DEP-induced GM-CSF release.
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nDEP triggered Erk1/2 phosphorylation (Figure 6B) in a time-dependent manner (30 min up to 4 h). The increased Erk1/2 phosphorylation induced by OE-DEP appeared to be always lower than that induced by nDEP, but was higher than that induced by sDEP at 2 and 4 h of exposure. Increased p38 phosphorylation (Figure 6C) was already detected after 30 min of treatment with nDEP, OE-DEP, or sDEP, increased after 2 h, and decreased after 4 h of treatment. nDEP and OE-DEP therefore appeared to mainly induce phosphorylation of both MAPK Erk1/2 and p38, whereas sDEP predominantly induced p38 phosphorylation.
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Discussion |
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To clarify the properties of DEP associated with inflammatory effects, a systematic comparison of the cellular effects induced by nDEP, OE-DEP, and sDEP or CB was
performed on a human bronchial epithelial cell line, the
16HBE cell line. For this purpose, different molecular targets, typical of DEP-induced inflammatory response, were
studied (i.e., GM-CSF release, I
B degradation, NF-
B
DNA binding, and MAPK activation).
In the present report, we demonstrated the critical contribution of organic compounds to DEP-induced effects: (1) OE-DEP always induced approximately the same response as nDEP; (2) sDEP and CB, used as surrogates of carbonaceous core, exerted either no effect or markedly reduced effects; (3) BaP, a typical PAH present in DEP, is able to induce the same type of responses as OE-DEP.
Because OE-DEP caused the greatest effect in the nDEP-induced responses, it is possible that organic compounds could be desorbed from DEP to become bioavailable for the cells. This might occur in cells after the phagocytosis of DEP (11), as an aqueous solution of DPPC, a phospholipid used to prepare the DEP suspension, had no extraction effect on the PAH adsorbed onto the surface of the particles (11). In the present study, we show for the first time in human bronchial epithelial cells that nDEP and OE-DEP can rapidly induce the expression of the CYP1A1 gene, which could be related to the desorption of PAH from nDEP and their metabolism. Our experiment clarifies the experiments conducted by Sato and colleagues (21), who recently reported the induction of the CYP1A1 gene in the lung homogenates of Big Blue rats exposed, by inhalation, to whole DEP fumes. CYP1A1 induction is dependent on the binding of PAH to the aryl hydrocarbon receptor (AhR) in the cytosol. This complex translocates to the nucleus and associates with the AhR nuclear translocator, resulting in an active transcription factor that binds to the promoter of the CYP1A1 gene (22). Extracts of DEP have been shown to act as activators of the AhR (23) in murine hepatoma or human breast cancer cells.
Time-course studies demonstrated different kinetics of
action for nDEP and OE-DEP: OE-DEP seemed to activate NF-
B earlier than did nDEP. This result tends to
highlight the different behaviors of organic compounds
that are either immediately available (OE-DEP), or require desorption after phagocytosis (nDEP). In this latter case, the carbonaceous core could be considered mostly as
a vector allowing the entry of organic compounds into the
cells and their slow diffusion leading to sustained stimulation of the cells, as nDEP-induced NF-
B DNA binding
started later but was more persistent than that induced by
OE-DEP. However, the carbonaceous core is not completely devoid of effects: although the effects induced by
the carbonaceous core are fairly low compared with those
induced by nDEP, they are not negligible, suggesting that
they could act in combination with organic compounds. In
particular, the markedly increased phosphorylation of p38
induced by sDEP revealed that the carbonaceous core
could trigger a specific signaling pathway. Various studies
have also emphasized the potential role of carbon black in
inflammation, particularly when occuring as ultrafine particles (24).
This study also demonstrated the involvement of ROS in nDEP- and OE-DEP-induced effects, by the use of antioxidant molecules and direct measurement of peroxides using the fluorescent probe DCFH, confirming experiments performed in a human alveolar macrophage cell line (25). DEP have been shown to generate ROS, leading to the transcription of antioxidant genes (such as heme oxygenase-1 [HO-1]), which are regulated by the antioxidant responsive element (26, 27). The main generation of ROS could proceed from organic compounds contained in DEP that could produce ROS (1) immediately by oxidation- reduction cycling of quinones or quinonelike compounds or (2) subsequently after metabolization of PAH. The catalytic activities of cytochrome P450 are known to produce ROS directly and also generate biologic reactive intermediates, including quinones, which produce ROS by redox cycling (28). These two different mechanisms could induce two waves of ROS production. ROS generation could also proceed, to a lesser extent, from the carbonaceous core. CB exhibit oxidative properties as they deplete the antioxidant defenses in the epithelial lining fluid (29) and induce DNA strand scission in plasmidic DNA (30).
MAPK pathways are triggered by many extracellular
stimuli such as environmental stresses. They could interact
with the regulation of the activity of transcription factors
such as NF-
B (31) and they could be involved in the
transduction of oxidative stress to the gene-regulating machinery of the cell (32). Erk, Sapk/JNK, and p38 are the
three major MAPK described today. PD98059, an inhibitor of the Erk pathway, significantly reduces GM-CSF release induced by nDEP or OE-DEP. However, PD98059
has been described as an AhR antagonist (33), suggesting
that its inhibitory action could be owing to the inhibition
of DEP metabolism. Nevertheless, a marked increase in
the phosphorylated form of Erk1/2 was shown with nDEP
and OE-DEP. Although the p38 inhibitor induced little or
no reduction of nDEP- or OE-DEP-induced GM-CSF release, nDEP, OE-DEP, and sDEP markedly induced p38
phosphorylation. In another human bronchial epithelial
cell line (BEAS-2B), only p38 phosphorylation was observed with nDEP (16). This discrepancy with our results could either reflect cell-specific responses or be owing to
the shorter kinetics as this study was only conducted over
2 h, whereas Erk phosphorylation was most striking after 4 h
of exposure in our experiment.
The involvement of organic compounds in DEP-induced cellular effects will require additional characterization of the organic components: either quinones or PAH or both, as they are DEP components known to have toxicologic effects. A possible role of quinones in the DEP-induced oxidative effects has already been suggested (27, 34). Because DEP-PAH are possibly desorbed and further bioactivated by the induced CYP1A1 gene, they may generate oxygenated PAH, including quinones. Quinones could therefore be the key molecules in the DEP-induced effects. Because of their ability to generate ROS, they could participate in the regulation of many genes controlled by redox-sensitive transcription factors. Li and coworkers (27) recently reported that HO-1 expression, induced by OE-DEP in macrophages, essentially involved the polar extracted fraction of DEP, which contained quinones and oxygenated PAH.
In conclusion, we have shown that the DEP-induced inflammatory response in 16HBE cells mainly involves organic compounds such as PAH, which induce CYP1A1 gene expression. However, the carbonaceous core also exhibits a slight effect. Understanding the respective contributions of the various components of DEP in its cellular effects is important to vehicle manufacturers so that they are able to improve their exhaust gas post-treatment technologies. In addition, the present determination of the cellular signaling pathways triggered by DEP and the involvement of ROS in these events could provide new insight into therapeutic strategies.
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Footnotes |
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Address correspondence to: Véronique Bonvallot, Laboratoire de Cytophysiologie et Toxicologie Cellulaire, Université Paris VII Denis Diderot, Tour 53-54 E3, case 70-73, 2, place Jussieu, 75251 Paris cedex 05, France. E-mail: bonvallot{at}paris7.jussieu.fr
(Received in original form January 26, 2001 and in revised form May 9, 2001).
Abbreviations: aryl hydrocarbon receptor, AhR; carbon black particles, CB; benzo(a)pyrene, BaP; dichlorofluorescein, DCF; dichlorofluorescein diacetate, DCFH-DA; diesel exhaust particles, DEP; dimethylsulfoxide, DMSO; dimethylthiourea, DMTU; dipalmitoylphosphatidylcholine, DPPC; electrophoresis mobility shift assay, EMSA; granulocyte macrophage colony-stimulating factor, GM-CSF; Hanks' balanced salt solution, HBSS; human bronchial epithelial, HBE; inhibitor
B, I
B; messenger RNA, mRNA;
mitogen-activated protein kinase, MAPK; N-acetylcysteine, NAC; native
diesel exhaust particles, nDEP; nuclear factor
B, NF-
B; organic extract of
diesel exhaust particles, OE-DEP; phenylmethylsulfonylfluoride, PMSF;
polycyclic aromatic hydrocarbons, PAH; reactive oxygen species, ROS;
stripped diesel exhaust particles, sDEP; sodium dodecyl sulfate, SDS; standard error, SE; saline sodium citrate, SSC; Tris-buffered saline, TBS.
Acknowledgments:
The authors wish to acknowledge Renault (DIMAT) for performing DEP extraction, Dr. D.C. Gruenert for the human bronchial cell line,
and Dr. R. Hay for the mouse antibody against I
B
. They thank Christiane
Guennou, Mireille Legrand, and Arulraj Nadaradjane for their excellent technical help. This study was supported by grant 235 from Renault (DIMAT), grant
BOU 9536 from Ademe, grants 97034 and PR99/022000/010 from Primequal, and
a grant from Caisse d'Assurance Maladie des Professions Libérales Provinces.
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