Extracts Of Diesel Exhaust Particles Research Articles

Oxidative-stress potency of organic extracts of diesel exhaust and urban fine particles in rat heart microvessel endothelial cells

Exposure to fine particulate materials is associated with an increase in mortality rate of cardiovascular diseases. Particles deposited in the lung may affect the vascular system both directly (leaching of soluble components from particles) and indirectly (via cytokines and mediators). The present study addressed cytotoxicity and oxidative stress potency of organic extracts of diesel exhaust particles (OE-DEP) and urban fine particles (OE-UFP) in rat heart microvessel endothelial (RHMVE) cells. The LC 50 values of OE-DEP and OE-UFP were calculated to be 17 and 34 μg/ml, respectively, suggesting that OE-DEP was more cytotoxic than OE-UFP. The viability of OE-DEP- and OE-UFP-exposed cells was ameliorated by N-acetyl- l-cysteine (NAC). The cell monolayer was exposed to 0 (control), 1, 3, and 10 μg/ml OE-DEP for 6 h and mRNA levels of antioxidant enzymes such as heme oxygenase-1 (HO-1), thioredoxin peroxidase 2 (TRPO), glutathione S-transferase P subunit (GST-P), and NADPH dehydrogenase (NADPHD) were quantitated by northern analysis. All those mRNA levels increased dose-dependently with OE-DEP and HO-1 mRNA showed the most marked response to OE-DEP. mRNA levels of those antioxidant enzymes and heat shock protein 72 (HSP72) in OE-DEP-exposed cells were higher than those of OE-UFP-exposed cells as compared at the same concentration. The transcription levels of HO-1 and HSP72 in OE-DEP- and OE-UFP-exposed cells were also reduced by NAC. Those results suggest that the organic fraction of particulate materials in the urban air has a potency to cause oxidative stress to endothelial cells and may be implicated in cardiovascular diseases through functional changes of endothelial cells.

Isolation of Nitrophenols from Diesel Exhaust Particles (DEP) as Vasodilatation Compounds

The compounds in diesel exhaust particles (DEP) that are responsible for vasodilatation were isolated and characterized for the first time. From benzene extract of DEP, 2-methyl-4-nitrophenol, 3-methyl-4-nitrophenl and 4-nitrophenol were isolated, and their vasodilatation activities were confirmed. 3-methyl-4-nitrophenol caused dilatation of rat thoracic artery, and the other two nitrophenols, also showed vasodilatation activities.

TOF-SIMS measurements for toxic air pollutants adsorbed on the surface of airborne particles

Three kinds of particulate matter were collected: diesel and gasoline exhaust particles emitted directly from exhaust nozzle, and suspended particulate matter (SPM) near the traffic route. Soxhlet extraction was performed on each sample. By gas-chromatograph–mass spectrometer (GC–MS) analysis of these extracts, di-ethyl phthalate and di- n-butyl phthalate were detected from the extract of SPM and diesel exhaust particles (DEPs). Because these phthalates were sometimes suspected as contamination, time-of-flight secondary ion mass spectrometry (TOF-SIMS) measurements were also performed on the samples collected at the same environment. By comparing obtained spectra, it is clear that these environmental endocrine disrupters (EEDs) were adsorbed on DEP surface. Thus, we concluded that the combination of conventional method and TOF-SIMS measurement is one of the most powerful techniques for analyzing the toxic air pollutants adsorbed on SPM surface.

Diesel Exhaust Particle Extracts and Associated Polycyclic Aromatic Hydrocarbons Inhibit Cox-2-dependent Prostaglandin Synthesis in Murine Macrophages and Fibroblasts

Diesel exhaust particles (DEP) and their organic constituents modulate the immune system and exacerbate allergic airway inflammation. We investigated the role of DEP extract and associated polycyclic aromatic hydrocarbons (PAHs) on prostaglandin synthesis in endotoxin-activated murine macrophages and in mitogen-stimulated fibroblasts. In both macrophages and fibroblasts, DEP extract, phenanthrene, anthracene, phenanthrenequinone, and beta-napthoflavone inhibit prostaglandin production from endogenous arachidonic acid in response to ligand stimulation. However, DEP extract and PAHs do not block ligand induction of cyclooxygenase-2 (COX-2) protein, either in mitogen-stimulated fibroblasts or endotoxin-treated macrophages. Release of total arachidonic acid and total lipid products is not reduced by DEP or PAHs following ligand stimulation of macrophages or fibroblasts. DEP extract and the PAHs inhibit the activity of purified COX-2 enzyme in vitro but do not inhibit COX-1 activity. Thus, DEP and PAHs do not affect ligand-induced COX-2 gene expression, phospholipase activation, or arachidonic acid release in macrophages and fibroblasts but exert their inhibitory effect on prostaglandin production by preferentially blocking COX-2 enzyme activity.

CDNA microarray analysis of gene expression in rat alveolar macrophages in response to organic extract of diesel exhaust particles.

Diesel exhaust particles (DEP) induce pulmonary diseases including asthma and chronic bronchitis. Comprehensive evaluation is required to know the effects of pollutants including DEP on these and other lung diseases. Alveolar macrophages (AM) and epithelial cells are important cellular targets for pollutants such as DEP in the lung. Alveolar macrophages encounter and phagocytose DEP in the alveolar space, and their biological responses have been implicated in DEP-induced pulmonary diseases. Expression profiles of genes induced by DEP in AM will lead to better understanding of the mechanisms involved in pulmonary diseases. To characterize the effect of the DEP extract on AM systematically, we analyzed the gene expression in AM exposed to DEP extract using the Atlas Rat Toxicology Array II. The finding in cDNA microarray was further confirmed by Northern blot analysis. AM were exposed to 10 microg/ml of DEP extract for 6 h in order to elucidate early response to DEP extract in AM. Early response to DEP extract in AM may affect the alteration of gene expression in subsequent responses so that it is important to identify the alteration in early response. In this study, the transcription of 6 genes in the cDNA microarray was significantly elevated by exposure of the AM to DEP extract. These genes were heme oxygenase (HO)-1 and -2, thioredoxin peroxidase 2 (TDPX-2), glutathione S-transferase P subunit (GST-P), NAD(P)H dehydrogenase, and proliferating cell nuclear antigen (PCNA). The antioxidative enzymes such as HO, TDPX-2, GST-P, and NAD(P)H dehydrogenase may play a role in the pulmonary defense against oxidative stress caused by various pollutants including DEP. PCNA may have contributed to the repair of DNA damage and to cell proliferation caused by exposure to these pollutants. Our results suggest that cDNA microarray analysis is a useful tool to investigate the biological responses to pulmonary toxicants.

Chemical constituents of diesel exhaust particles induce IL-4 production and histamine release by human basophils.

An epidemiologic relationship between airway allergic diseases and exposure to atmospheric pollutants has been demonstrated and suggested to be one factor in the increasing prevalence of asthma. Diesel exhaust particles (DEPs) have been shown to participate in the development of allergic airway inflammation, in which the targets include macrophages, B and T cells, epithelial cells, and mast cells. In addition to the adjuvant effect of DEPs on total and allergen-specific IgE production, DEPs also act to induce chemokines and cytokines and may play a key role in primary sensitization. DEPs have been shown to increase local IL-4-containing Kit(+) cells soon after in vivo nasal challenge. The aim of this study was to examine the effects of DEPs on human basophils, a key source of IL-4. Peripheral blood leukocytes from allergic and control subjects were cultured in the presence of organic extracts of DEP (DEPex) with or without allergen. The cultures were analyzed for IL-4-containing cells by using multiparameter flow cytometry, IL-4 secretion with ELISA, and histamine release. Basophils, when exposed in vitro to DEPex, expressed IL-4 and released histamine significantly (P <.01) more than with antigen activation. DEPex did not synergize with allergen in cytokine production and histamine release. DEPex-induced basophil IL-4 expression peaked at 2 hours and persisted through 20 hours, in contrast to allergen-induced IL-4, which was transient. The effect of DEPex on basophil cytokine expression and histamine release was dose dependent and occurred with cells from both allergic and nonallergic subjects. DEPex induced IL-4 expression and histamine release in highly enriched basophil populations, suggesting it acts directly on basophils. Other peripheral blood leukocytes, including T cells, did not contribute to this cytokine expression. Preincubation with N-acetylcysteine completely abrogated DEPex-driven basophil IL-4 expression. Basophils are a direct target for DEPex, inducing IL-4 expression and histamine release in an IgE-allergen independent fashion. N-acetylcysteine inhibition of DEPex-driven IL-4 expression provides evidence that generation of reactive oxygen species is required for the effects observed. The capability of DEPex to activate basophils in both allergic and nonallergic subjects suggests a potential role of this pollutant in the increasing prevalence of allergic diseases.

Effect of diesel exhaust particle extracts on induction of oral tolerance in mice.

We examined the effect of diesel exhaust particle (DEP) extracts on oral tolerance in mice. For this examination, a single DEP sample was consecutively extracted with hexane (HEX-DEP), benzene (BEN-DEP), dichloromethane (DIC-DEP), methanol (MET-DEP), and 1 M ammonia (AMM-DEP). Residues unextracted (UNE-DEP) with the last extraction solvent 1 M ammonia were also used to test their ability to induce oral tolerance. To immunize mice, hen egg lysozyme (HEL) emulsified with an equal volume of CFA was injected sc (day 0). Oral tolerance was induced by feeding 10 mg HEL on days -5, -4, -3, -2, and -1. DEP, each DEP extract, and UNE-DEP were intranasally administered immediately after each feeding of HEL. The results showed that oral administration of HEL markedly suppressed production of anti-HEL IgG antibodies as well as proliferative responses of spleen cells to HEL. The suppression of anti-HEL IgG antibody production and the cell proliferation by the oral antigen was significantly blocked by DEP, DIC-, AMM-, and UNE-DEP. Neither HEX-, BEN-, nor MET-DEP modulated the orally induced suppression of these immune responses. When the levels of anti-HEL IgG2a antibodies and IFN-gamma (Th1 responses) and anti-HEL IgG1 antibodies and IL-4 (Th2 responses) were determined, DEP and DIC-DEP diminished the suppression of both Th1 and Th2 responses observed following oral administration of HEL. In contrast, UNE- and AMM-DEP prevented the reduction of Th1 but not Th2, and Th2 but not Th1 oral tolerance, respectively. Thus, UNE-DEP appears to contain compounds that block induction of Th1 but not Th2 oral tolerance, whereas AMM-DEP have compounds that abrogate induction of Th2 but not Th1 oral tolerance. DIC-DEP, as well as DEP, appear to contain components that block induction of both Th1 and Th2 oral tolerance. As oral tolerance is thought to play a critical role in preventing Th1 as well as Th2 food allergy, the blockade of oral tolerance by these DEP extracts suggests that DEP may contain compounds different in hydrophobicity associated with the cause of such adverse immunologic responses to food proteins.

Activation of the mouse heme oxygenase-1 gene by 15-deoxy-Delta(12,14)-prostaglandin J(2) is mediated by the stress response elements and transcription factor Nrf2.

The mechanism of heme oxygenase-1 (ho-1) gene activation by 15-deoxy-Delta(12,14)-prostaglandin J(2) (15d-PGJ(2)) was examined. 15d-PGJ(2) stimulated expression of HO-1 mRNA and protein and of a mouse ho-1 gene promoter/luciferase fusion construct (HO15luc) in a dose-dependent manner in mouse hepatoma (Hepa) cells. HO15luc expression was not effected by troglitazone, a peroxisome proliferator-activated receptor-gamma (PPAR-gamma) ligand, but induction by 15d-PGJ(2) was abrogated by the antioxidant N-acetylcysteine. The primary 15d-PGJ(2) responsive sequences were localized to a 5' distal enhancer (E1) and identified as the stress-response element, previously shown to mediate ho-1 activation by several agents, including heme and heavy metals. Treatment of Hepa cells with 15d-PGJ(2) stimulated stress-response element-binding activity as judged by electrophoretic mobility shift assays. Antibody "supershift" experiments identified NF-E2 related factor 2 (Nrf2), but not Fos, Jun, or activating transcription factor/cyclic AMP response element binding protein transcription factors, within the 15d-PGJ(2)-induced complexes. Similarly, a dominant-negative mutant of Nrf2, but not of c-Jun or c-Fos, abrogated 15d-PGJ(2)-stimulated E1 transcription activity. Finally, prior induction of HO-1 in RAW264.7 mouse macrophages by 15d-PGJ(2) attenuated cell death caused by diesel exhaust particle extracts. These results demonstrate that induction of mouse HO-1 expression by 15d-PGJ(2) is independent of PPAR-gamma but dependent on oxidative stress, is regulated by the oxidative stress-activated transcription factor Nrf2, and provides cytoprotective activity.

Estrogenic Activities of Chemicals in Diesel Exhaust Particles.

In a previous study, we focused on estrogenic activity of the hexane extract of diesel exhaust particles (DEP). The extract of hexane was first fractionated to acidic, phenolic and neutral portions according to their chemical properties, of which the neutral fraction was fractionated by column chromatography on silica gel. The chemical structures of compounds in these fractions were then analyzed. It was found that the neutral fraction of the hexane extract of DEP contains dibenzothiophene derivatives, one of which, 4,6-dimethyldibenzothiophene, possesses estrogenic activity.

Effects of diesel exhaust particle extracts on Th1 and Th2 immune responses in mice.

The present study was undertaken to investigate the effects of extracts of diesel exhaust particles (DEP) on Th1 and Th2 immune responses. In order to separate compounds from DEP different in hydrophobicity, a single DEP sample was consecutively extracted with hexane (HEX-DEP), benzene (BEN-DEP), dichloromethane (DIC-DEP), methanol (MET-DEP), and 1M ammonia (AMM-DEP). The last unextracted residue (UNE-DEP) was also used to test its effect on immune responses. To immunize mice, hen egg lysozyme (HEL) was injected i.p. (day 0). Varying doses of DEP, each DEP extract, and UNE-DEP were intranasally administered every 2 days from days 0 to 18. Anti-HEL IgG2a antibodies in sera and IFN-&#x03B3; secreted from spleen cells were measured as an indicator of Th1 immune responses, while anti-HEL IgG1 antibodies and IL-4 as that of Th2 responses. The results showed that treatment with DEP and DIC-DEP increased both Th1 and Th2 responses to HEL. UNE-DEP facilitated Th1 but not Th2 responses, while MET- and AMM-DEP administration was followed by enhancement of Th2 but not Th1 responses. Neither HEX- nor BEN-DEP modulated Th1 as well as Th2 responses. These results suggest that DEP contain various compounds different in hydrophobicity which may affect both Th1 and Th2, Th1 but not Th2, and Th2 but not Th1 immune responses.

Diesel exhaust particles induce an inflammatory response in airway epithelial cells: involvement of reactive oxygen species.

Epidemiological studies have shown that high particulate air pollution is associated with an increase in hospital admissions for respiratory diseases and with an exacerbation of asthma symptoms [8]. In urban areas, traffic appears to be the main source of particulate airborne pollutants. Diesel engine powered cars, which produce the most abundant components of PM2.5 (Particulate Matter 2.5 µm), are suspected to be responsible for this exacerbation of respiratory diseases but their real impact on health has not been fully elucidated. Recent experimental studies have emphasized the role of diesel exhaust particles (DEP) in the development of an inflammatory response. Nasal challenges of humans with DEP result in the local increase in IgE and cytokine production [7]. In vitro studies have shown that airway epithelial cells, one of the main cellular targets of DEP, directly participate in this inflammatory response [2]. Indeed, cultured human nasal and bronchial epithelial cells exposed to DEP released in a time and dose dependent process, proinflammatory cytokines such as GM-CSF and IL-8 known to be involved in allergic diseases [3]. This increased release of GM-CSF has been shown to be subsequent to transcription [4]. Since airway epithelial cells can be effectors of the inflammatory response, it is necessary to investigate the cellular and molecular mechanisms leading to this response and to determine the respective role of DEP components in these mechanisms. DEP are composed of a carbonaceous core with adsorbed organic compounds (polyaromatic hydrocarbons (PAH), nitroaromatic hydrocarbons, quinones, aldehydes and aliphatic hydrocarbons) which could represent up to 60% of the mass of the particle depending on the vehicle and the fuel composition. The cellular and molecular events induced by DEP were investigated using a model of bronchial epithelial cells, the human bronchial epithelial cell line (16HBE 14 o-) and standard reference DEP (SRM 1650). The effects of native DEP were compared to those induced by the organic extracts of DEP (OE-DEP) obtained by extraction of DEP with dichloromethan and by the carbonaceous core represented either by carbon black particles or stripped DEP (sDEP) recovered after extraction. DEP trigger MAPK Erk 1/2 signalling pathways as a specific inhibitor of this pathway (PD 98059) clearly reduced the DEP-induced GM-CSF release. Moreover the phosphorylated form of Erk 1/2

Effect of Diesel Exhaust Particle Extracts on Collagen-induced Arthritis in Mice

We investigated the effect of diesel exhaust particles (DEP) extracts on collagen-induced arthritis (CIA) in mice. For this study, a single DEP sample was consecutively extracted with hexane (HEX-DEP), benzene (BEN-DEP), dichloromethane (DIC-DEP), methanol (MET-DEP), and 1 u M ammonia (AMM-DEP) in that order. Residues unextracted with the last extraction solvent 1 u M ammonia (UNE-DEP) were also used for experiments. To induce CIA, mice were immunized with type II collagen (CII) and 21 days later given a booster injection. DEP, each DEP extract, and UNE-DEP were intranasally administered every two days over a period of 20 days, commencing on the day of immunization. The results showed that treatment of mice with DEP, DIC-DEP, and UNE-DEP augmented both the incidence and the severity of CIA. DEP and DIC-DEP increased production of anti-CII IgG, IgG2a, and IgG1 antibodies as well as secretion of IFN- n and IL-4. Treatment with UNE-DEP resulted in an increase in antigen-specific IgG, IgG2a, and IFN- n but neither IgG1 nor IL-4. AMM-DEP failed to affect CIA as well as production of IgG2a and IFN- n, although significant increases in anti-CII IgG1 and IL-4 were observed in the treatment group. HEX-DEP, BEN-DEP, and MET-DEP had no effects on CIA and production of antibodies and cytokines examined. Thus, DEP and DIC-DEP appear to contain compounds, which enhance both Th1 and Th2 responses, while UNE-DEP and AMM-DEP to contain chemicals, which augment Th1 and Th2 alone, respectively. Th1- but not Th2-modulating compounds from DEP, DIC-DEP, and UNE-DEP seem to influence CIA.

USE OF A STRATIFIED OXIDATIVE STRESS MODEL TO STUDY THE BIOLOGICAL EFFECTS OF AMBIENT CONCENTRATED AND DIESEL EXHAUST PARTICULATE MATTER

Although several epidemiological studies have shown a positive relationship between exposure to ambient air particulate matter (PM) and adverse health effects in humans, there is still a fundamental lack of understanding of the most toxic particle components and the biological mechanisms through which they act. Since our studies on the biological effects of diesel exhaust particles (DEP) have highlighted the role of reactive oxygen species (ROS), catalyzed by organic chemical compounds, we set out to establish whether this constitutes an oxidative stress model that can be used to study the biological effects of ambient coarse and fine PM. We demonstrate that organic DEP extracts induce a stratified oxidative stress response, leading to heme oxygenase 1 (HO-1) expression at normal GSH/ GSSG ratios, proceed to Jun kinase activation and interleukin 8 (IL-8) production at intermediary oxidative stress levels, and culminate in cellular apoptosis in parallel with a sharp decline in GSH/GSSG ratios. We demonstrate that ambient concentrated air particulates, collected with a particle concentrator and a liquid impinger, mimic the effects of organic DEP extracts at lower oxidative stress levels. While fine PM consistently induced HO-1 expression in all most of the samples collected over a 9-mo survey period, coarse particulates were effective at inducing that effect during fall and winter. Moreover, HO-1 expression was positively correlated to the higher organic carbon (OC) and polyaromatic hydrocarbons (PAHs) content of fine versus coarse PM, as well as the rise in PAH content that occurs in coarse PM during the winter months. Although coarse and fine PM lead to a decrease in cellular glutathione (GSH)/GSSG ratios, oxidative stress did not increase to cytotoxic levels. Taken together, these data demonstrate that it is possible to use the stratified oxidative stress model developed for DEP to interpret the biological effects of coarse and fine PM. This work has important implications for the selection of relevant biological endpoints for in vivo studies.

Estrogenic and anti-estrogenic activities of two types of diesel exhaust particles

In an earlier study using a recombinant yeast screen we found that a suspension of diesel exhaust particles (DEP) and some extracts of DEP are not estrogenic but possess anti-estrogenic activity. In the present study, estrogenic and anti-estrogenic activities of two types of DEP, type-1 (old type) and type-2 (new type) were compared. Whole DEP of both types were found to possess estrogenic and anti-estrogenic activities. The DEP were serially extracted with organic solvents and then with 1 M ammonia and 1 M HCl. In type-2 DEP, the ratio of dry weight of a hexane extract was higher than those of methanol and ammonia extracts, which were lower than those in type-1 DEP. In the hexane extract, estrogenic activity was found in both types of DEP. In the benzene and dichloromethane extracts, estrogenic and anti-estrogenic activities were found in both types of DEP. In the methanol extract, estrogenic activity was found in type-2 DEP, and extracts of both types decreased the activity of estrogen. Anti-estrogenic activity was found in extracts of ammonia and HCl from both types of DEP. It was found that both type-1 and type-2 DEP possess estrogenic and anti-estrogenic activities.

Induction of cytochrome P450 1B1 in lung, liver and kidney of rats exposed to diesel exhaust.

We have shown previously that diesel exhaust particle (DEP) extracts (DEPE) and 1-nitropyrene were genotoxically activated by human cytochrome P450 1B1 in SOS/umu assay. In this study, the in vivo induction of P450 family 1 enzymes in rats by exposure to diesel exhaust was investigated with regard to mRNA levels, P450 enzyme content, drug oxidation activities in the microsomes and umu gene expression of typical P450 substrates and DEPE itself catalyzed by the microsomes. Male Fischer 344 rats (4 weeks old) were exposed to 0.3 and 3.0 mg/m(3) DEP for 12 h per day for 4 weeks; the former dose corresponded to the typical daily airborne particle concentration. The levels of mRNA of rat P450 1B1 and P450 1A1 in the lung and liver were significantly increased 1.1-1.4-fold by exposure to 0.3 mg/m(3) DEP. Diesel exhaust particle extracts induced umu gene expression in Salmonella typhimurium TA1535/pSK1002 in the absence of a functional P450 system and were further activated by human recombinant P450 1B1. Using an O-acetyltransferase overexpressing Salmonella strain, genotoxic activation of P450 1B1 marker chemicals (1-nitropyrene, 1-aminopyrene and DEPE) by lung, liver and kidney microsomes was increased 1.7-4.2-, 1.4-1.5- and 1.0-1.3-fold, respectively, by exposure to 0.3 mg/m(3) DEP. Activation of 3-amino-1,4-dimethyl-5H-pyrido [4,3-b]indole (Trp-P-1; marker for P450 1A1) by lung microsomes and the P450 1A2 content in liver microsomes were slightly increased by exposure to 3.0 mg/m(3) DEP. This is the first report to suggest that typical daily contaminant levels (0.3 mg particle/m(3)) of diesel exhaust can induce P450 1B1 in rats and that the induced P450 1B1 may catalyze the genotoxic activation of DEP.

Organic compounds from diesel exhaust particles elicit a proinflammatory response in human airway epithelial cells and induce cytochrome p450 1A1 expression.

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)-kappaB 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-kappaB 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-kappaB 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.

Genotoxic effects of carbon black particles, diesel exhaust particles, and urban air particulates and their extracts on a human alveolar epithelial cell line (A549) and a human monocytic cell line (THP-1).

The possible genotoxicity of small particulate matter has been under investigation for the last 10 years. Diesel exhaust particles (DEP) are considered as "probably carcinogenic" (IARC group 2A) and a number of studies show genotoxic effects of urban particulate matter (UPM). Carbon black (CB) is carcinogenic in rats. In this study the cytotoxic and genotoxic potency of these three particle types was investigated by exposing human cells (A549 and THP-1 cell lines) in vitro to CB, DEP (SRM 1650, NIST), and UPM (SRM 1648, NIST) for 48 hr. Cytotoxicity was assessed using the Alamar Blue assay, whereas genotoxicity was assessed using the single-cell gel electrophoresis (comet assay). The particles were characterized with regard to their mean diameter in tissue culture medium (CB 100 nm, DEP 400 nm, UPM 2 microm), their total carbon content (CB 99%, DEP 85%, UPM 15%), and their acid-soluble metal composition (UPM >> CB approximately DEP). The concentrations ranged from 16 ng/ml to 16 microg/ml for cytotoxicity tests and from 16 ng/ml to 1.6 microg/ml for genotoxicity tests. In both assays, paraquat was used as a reference chemical. The CB, DEP, and UPM particles showed no significant cytotoxicity. However, all three particles were able to cause significant DNA damage, although to a different extent in the two cell lines. The genotoxicity of washed particles and dichloromethane extracts was also investigated. In THP-1 cells CB washed particles and DEP extracts caused significant DNA damage. This difference in effect may be related to differences in size, structure, and composition of the particles. These results suggest that CB, DEP, and UPM are able to cause DNA damage and, therefore, may contribute to the causation of lung cancer. More detailed studies on influence of size, structure, and composition of the particles are needed.

Diesel exhaust particle-induced cell death of human leukemic promyelocytic cells HL-60 and their variant cells HL-NR6.

The cytotoxicity of diesel exhaust particles (DEPs) toward human leukemic promyelocytic cells HL-60 was examined. DEPs were toxic and cytotoxicity increased in a dose-dependent manner. All cells died with 750 microg/ml DEPs in culture media. Apoptosis occurred in HL-60 cells exposed to DEPs. The cytotoxicity of DEP extracts with organic solvents was much lower than those of DEPs and organic solvent-washed residual DEPs. HL-NR6 cells, an HL-60 variant cell line, having higher superoxide dismutase and catalase activities than HL-60 cells, were more resistant to DEP cytotoxicity. When preincubated with the fluorescent probe diacetoxymethyl 6-carboxy-2',7'-dichlorodihydrofluorescinate diacetate and then exposed to DEPs, HL-60 cells emitted green fluorescence under blue illumination, indicating that reactive oxygen species were generated within the cells. The DEP cytotoxicity correlated inversely with the cellular concentration of reduced glutathione (GSH), which had been attenuated with L-buthionine-(R,S)-sulfoximine, a gamma-glutamylcysteine synthetase inhibitor, and was lowered with ethyl reduced glutathionate, a GSH carrier across biomembranes. Further, DEPs themselves decreased the cellular concentration of GSH in a dose-dependent manner. The alpha-tocopherol model compound 2,2,5,7,8-pentamethylchroman-6-ol decreased DEP cytotoxicity, while alpha-tocopherol had no effect. In addition, quinacrine, an endocytosis inhibitor, decreased DEP cytotoxicity. These results show that DEPs are cytotoxic and suggest that the cytotoxicity results from generation of reactive oxygen species by DEPs which have been incorporated into cells.

Bioactivation of diesel exhaust particle extracts and their major nitrated polycyclic aromatic hydrocarbon components, 1-nitropyrene and dinitropyrenes, by human cytochromes P450 1A1, 1A2, and 1B1

The genotoxicities of four samples of diesel exhaust particle (DEP) extracts (DEPE) and nine nitroarenes found in DEPE were investigated after activation catalyzed by human cytochrome P450 (P450) family 1 enzymes co-expressed with NADPH-cytochrome P450 reductase (NPR) in Escherichia coli membranes. The DEPE samples induced umu gene expression in Salmonella typhimurium TA1535/pSK1002 without any P450 system and were further activated by human P450 1B1/NPR membranes. Moderate activation of the DEPE sample by P450 1A2/NPR membranes was also observed, but not by either P450 1A1/NPR or NPR membranes. 1-Nitropyrene (1-NP) was strongly activated by human P450 1B1/NPR membranes. 1,8-Dinitropyrene (1,8-DNP) was most highly activated by P450 1A1 and 1B1 systems for the three DNPs tested. In contrast, 1,3-DNP was inactivated by P450 1A1/NPR, 1A2/NPR, and 1B1/NPR systems and slightly activated by NPR membranes. 2-Nitrofluoranthene (2-NF) and 3-nitrofluoranthene (3-NF) showed activities similar to 1-NP after bioactivation by P450 1B1/NPR membranes. However, the genotoxicities of 6-nitrochrysene, 7-nitrobenz[ a]anthracene, and 6-nitrobenzo[ a]pyrene were all weak in the present assay system. Apparent genotoxic activities of DEPE were very low compared with standard nitroarenes in the presence of P450s, possibly because unknown component(s) of DEPE had inhibitory effects on the bioactivation of 1-NP and 1,8-DNP catalyzed by human P450 1B1. These results suggest that environmental chemicals existing in airborne DEP, in addition to 1-NP, 1,6-DNP, 1,8-DNP, 2-NF, and 3-NF, can be activated by human P450 1B1. Biological actions of air pollutants such as nitroarenes to human extrahepatic tissues may be of concern in tissues in which P450 1B1 is expressed.

Pollution and the immune response: atopic diseases--are we too dirty or too clean?

The effect of pollutants on the immune system has filled tomes and is almost always controversial whether the topic is disinfectants in drinking water or particulates and lung cancer. Even whether outdoor and indoor air quality is improving or declining has been a source of considerable investigation, consultation and often litigation. Few areas, however, yield so much uncertainty and debate as the role of airborne pollutants in atopy. Atopy is defined as an immunoglobulin E- (IgE) mediated allergic response to environmental antigens and can be manifested as rhinitis, asthma or atopic dermatitis. While there is some debate over whether there has been a real increase in atopy over the last decades, it is indisputable that there has been a dramatic change over the last 200 years. While isolated cases of anaphylaxis had been noted before, allergies were unheard of until the early 19th century. Only 54 years after the first description of hay fever in England in 1819, it was considered an epidemic and a clear association with urbanization had been reported.1 What aspect of urbanization is involved has been much debated. There has been much discussion amongst both experimental immunologists and epidemiologists over whether pollutants are responsible for increased allergic sensitization and/or severity.2,3 In the last few years new studies have supported an alternative explanation, namely the decline in infectious diseases in industrialized countries.4,5 Does this ‘hygiene theory’ toll the death knell for the ‘pollution theory’? In this review I will argue that there is a compelling case to be made for both theories and that even this is not the entire picture.