Characterisation and seasonal variations of particles in the atmosphere of rural, urban and industrial areas: Organic compounds.

Atmospheric aerosol samples (PM2.5-0.3, i.e., atmospheric particles ranging from 0.3 to 2.5µm) were collected during two periods: spring-summer 2008 and autumn-winter 2008-2009, using high volume samplers equipped with cascade impactors. Two sites located in the Northern France were compared in this study: a highly industrialised city (Dunkirk) and a rural site (Rubrouck). Physicochemical analysis of particulate matter (PM) was undertaken to propose parameters that could be used to distinguish the various sources and to exhibit seasonal variations but also to provide knowledge of chemical element composition for the interpretation of future toxicological studies. The study showed that PM2.5-0.3 concentration in the atmosphere of the rural area remains stable along the year and was significantly lower than in the urban or industrial ones, for which concentrations increase during winter. High concentrations of polycyclic aromatic hydrocarbons (PAHs), dioxins, furans and dioxin like polychlorinated biphenyls (DL-PCBs), generated by industrial activities, traffic and municipal wastes incineration were detected in the samples. Specific criteria like Carbon Preference Index (CPI) and Combustion PAHs/Total PAHs ratio (CPAHs/TPAHs) were used to identify the possible sources of atmospheric pollution. They revealed that paraffins are mainly emitted by biogenic sources in spring-summer whereas as in the case of PAHs, they have numerous anthropogenic emission sources in autumn-winter (mainly from traffic and domestic heating).

Comparison between ultrafine and fine particulate matter collected in Lebanon: Chemical characterization, in vitro cytotoxic effects and metabolizing enzymes gene expression in human bronchial epithelial cells.

During the last few years, the induction of toxicological mechanisms by atmospheric ultrafine particles (UFP) has become one of the most studied topics in toxicology and a subject of huge debates. Fine particles (FP) and UFP collected at urban and rural sites in Lebanon were studied for their chemical composition and toxicological effects. UFP were found more enriched in trace elements, secondary inorganic ions, total carbon and organic compounds than FP. For toxicological analysis, BEAS-2B cells were exposed for 24, 48 and 72 h to increasing concentrations of FP, water-UFP suspension (UFPw) and UFP organic extract (UFPorg). Our findings showed that UFP caused earlier alterations of mitochondrial metabolism and membrane integrity from the lowest concentrations. Moreover, a significant induction of CYP1A1, CYP1B1 and AhRR genes expression was showed after cells exposure to UFPorg and to a lesser extent to UFPw and FP samples.

Genotoxic potential of Polycyclic Aromatic Hydrocarbons-coated onto airborne Particulate Matter (PM 2.5) in human lung epithelial A549 cells.

To improve the knowledge of the underlying mechanisms of action involved in air pollution Particulate Matter (PM)-induced toxicity in human lungs, with a particular interest of the crucial role played by coated-organic chemicals, we were interested in the metabolic activation of Polycyclic Aromatic Hydrocarbons (PAH)-coated onto air pollution PM, and, thereafter, the formation of PAH-DNA adducts in a human lung epithelial cell model (A549 cell line). Cells were exposed to Dunkerque city's PM(2.5) at its Lethal Concentrations at 10% and 50% (i.e. LC(10)=23.72 microg/mL or 6.33 microg/cm2, and LC(50)=118.60 microg/mL or 31.63 microg/cm2), and the study of Cytochrome P450 (CYP) 1A1 gene expression (i.e. RT-PCR) and protein activity (i.e. EROD activity), and the formation of PAH-DNA adducts (i.e. 32P-postlabeling), were investigated after 24, 48, and/or 72 h. PAH, PolyChlorinated Dibenzo-p-Dioxins and -Furans (PCDD/F), Dioxin-Like PolyChlorinated Biphenyls (DLPCB), and PolyChlorinated Biphenyls (PCB)-coated onto collected PM were determined (i.e. GC/MS and HRGC/HRMS, respectively), Negative (i.e. TiO2 or desorbed PM, dPM; EqLC10=19.42 microg/mL or 5.18 microg/cm2, and EqLC50=97.13 microg/mL or 25.90 microg/cm2), and positive (i.e. benzo(a)pyrene; 1 microM) controls were included in the experimental design. Statistically significant increases of CYP1A1 gene expression and protein activity were observed in A549 cells, 24, 48 and 72 h after their exposure to dPM, suggesting thereby that the employed outgassing method was not efficient enough to remove total PAH. Both the CYP1A1 gene expression and EROD activity were highly induced 24, 48 and 72 h after cell exposure to PM. However, only very low levels of PAH-DNA adducts, also not reliably quantifiable, were reported 72 h after cell exposure to dPM, and, particularly, PM. The relatively low levels of PAH together with the presence of PCDD/F, DLPCB, and PCB-coated onto Dunkerque City's PM 2.5 could notably contribute to explain the borderline detection of PAH-DNA adducts in dPM and/or PM-exposed A549 cells. Hence, remaining very low doses of PAH in dPM or relatively low doses of PAH-coated onto PM were involved in enzymatic induction, a key feature in PAH-toxicity, but failed to show a clear genotoxicity in this in vitro study. We also concluded that, in the human lung epithelial cell model we used, and in the experimental conditions we chose, bulky-DNA adduct formation was apparently not a major factor involved in the Dunkerque City's PM 2.5-induced toxicity.

Detection of polycyclic aromatic hydrocarbon levels in milk collected near potential contamination sources.

Polycyclic aromatic hydrocarbons (PAHs), mainly formed by incomplete anthropogenic organic matter combustion, are ubiquitous in the environment. To assess milk PAH contamination sources, milk samples were collected from the tank milk at farms located near potential contaminating emission sources such as cementworks, steelworks, and motorways. PAH analyses were carried out by gas chromatography coupled to mass spectrometry. Eight PAHs were identified in milk: naphthalene, acenaphthylene, acenaphthene, fluorene, anthracene, fluoranthene, pyrene, and benzo[a]anthracene. For all potential contaminating sources, these eight PAHs were detected with similar profiles and at low concentrations except for fluorene and naphthalene, for which source-molecule interaction is pointed out.