Physico-chemical properties and biological effects of diesel and biomass particles

Diesel combustion and solid biomass burning are the major sources of ultrafine particles (UFP) in urbanized areas. Cardiovascular and pulmonary diseases, including lung cancer, are possible outcomes of combustion particles exposure, but differences in particles properties seem to influence their bio...

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Veröffentlicht in:Environmental pollution (1987) 2016-08, Vol.215, p.366-375
Hauptverfasser: Longhin, Eleonora, Gualtieri, Maurizio, Capasso, Laura, Bengalli, Rossella, Mollerup, Steen, Holme, Jørn A., Øvrevik, Johan, Casadei, Simone, Di Benedetto, Cristiano, Parenti, Paolo, Camatini, Marina
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container_end_page 375
container_issue
container_start_page 366
container_title Environmental pollution (1987)
container_volume 215
creator Longhin, Eleonora
Gualtieri, Maurizio
Capasso, Laura
Bengalli, Rossella
Mollerup, Steen
Holme, Jørn A.
Øvrevik, Johan
Casadei, Simone
Di Benedetto, Cristiano
Parenti, Paolo
Camatini, Marina
description Diesel combustion and solid biomass burning are the major sources of ultrafine particles (UFP) in urbanized areas. Cardiovascular and pulmonary diseases, including lung cancer, are possible outcomes of combustion particles exposure, but differences in particles properties seem to influence their biological effects. Here the physico-chemical properties and biological effects of diesel and biomass particles, produced under controlled laboratory conditions, have been characterized. Diesel UFP were sampled from a Euro 4 light duty vehicle without DPF fuelled by commercial diesel and run over a chassis dyno. Biomass UFP were collected from a modern automatic 25 kW boiler propelled by prime quality spruce pellet. Transmission electron microscopy (TEM) and scanning electron microscopy (SEM) images of both diesel and biomass samples showed aggregates of soot particles, but in biomass samples ash particles were also present. Chemical characterization showed that metals and PAHs total content was higher in diesel samples compared to biomass ones. Human bronchial epithelial (HBEC3) cells were exposed to particles for up to 2 weeks. Changes in the expression of genes involved in xenobiotic metabolism were observed after exposure to both UFP already after 24 h. However, only diesel particles modulated the expression of genes involved in inflammation, oxidative stress and epithelial-to-mesenchymal transition (EMT), increased the release of inflammatory mediators and caused phenotypical alterations, mostly after two weeks of exposure. These results show that diesel UFP affected cellular processes involved in lung and cardiovascular diseases and cancer. Biomass particles exerted low biological activity compared to diesel UFP. This evidence emphasizes that the study of different emission sources contribution to ambient PM toxicity may have a fundamental role in the development of more effective strategies for air quality improvement. •Diesel particles exposure induce significant alterations in bronchial HBEC3 cells.•Xenobiotic metabolism and oxidative stress pathways are modulated.•Sub-chronic exposure conditions show significant pro-inflammatory effects.•Epithelial-mesenchymal transition genes, cell morphology and migration are affected.•Biomass particles exposed cells show minor effects also after sub-chronic exposure. Diesel more than biomass UFP induce gene expression changes, inflammatory mediators release and phenotypical alterations. These effects were mostly observ
doi_str_mv 10.1016/j.envpol.2016.05.015
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Cardiovascular and pulmonary diseases, including lung cancer, are possible outcomes of combustion particles exposure, but differences in particles properties seem to influence their biological effects. Here the physico-chemical properties and biological effects of diesel and biomass particles, produced under controlled laboratory conditions, have been characterized. Diesel UFP were sampled from a Euro 4 light duty vehicle without DPF fuelled by commercial diesel and run over a chassis dyno. Biomass UFP were collected from a modern automatic 25 kW boiler propelled by prime quality spruce pellet. Transmission electron microscopy (TEM) and scanning electron microscopy (SEM) images of both diesel and biomass samples showed aggregates of soot particles, but in biomass samples ash particles were also present. Chemical characterization showed that metals and PAHs total content was higher in diesel samples compared to biomass ones. Human bronchial epithelial (HBEC3) cells were exposed to particles for up to 2 weeks. Changes in the expression of genes involved in xenobiotic metabolism were observed after exposure to both UFP already after 24 h. However, only diesel particles modulated the expression of genes involved in inflammation, oxidative stress and epithelial-to-mesenchymal transition (EMT), increased the release of inflammatory mediators and caused phenotypical alterations, mostly after two weeks of exposure. These results show that diesel UFP affected cellular processes involved in lung and cardiovascular diseases and cancer. Biomass particles exerted low biological activity compared to diesel UFP. This evidence emphasizes that the study of different emission sources contribution to ambient PM toxicity may have a fundamental role in the development of more effective strategies for air quality improvement. •Diesel particles exposure induce significant alterations in bronchial HBEC3 cells.•Xenobiotic metabolism and oxidative stress pathways are modulated.•Sub-chronic exposure conditions show significant pro-inflammatory effects.•Epithelial-mesenchymal transition genes, cell morphology and migration are affected.•Biomass particles exposed cells show minor effects also after sub-chronic exposure. Diesel more than biomass UFP induce gene expression changes, inflammatory mediators release and phenotypical alterations. 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Human bronchial epithelial (HBEC3) cells were exposed to particles for up to 2 weeks. Changes in the expression of genes involved in xenobiotic metabolism were observed after exposure to both UFP already after 24 h. However, only diesel particles modulated the expression of genes involved in inflammation, oxidative stress and epithelial-to-mesenchymal transition (EMT), increased the release of inflammatory mediators and caused phenotypical alterations, mostly after two weeks of exposure. These results show that diesel UFP affected cellular processes involved in lung and cardiovascular diseases and cancer. Biomass particles exerted low biological activity compared to diesel UFP. 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Cardiovascular and pulmonary diseases, including lung cancer, are possible outcomes of combustion particles exposure, but differences in particles properties seem to influence their biological effects. Here the physico-chemical properties and biological effects of diesel and biomass particles, produced under controlled laboratory conditions, have been characterized. Diesel UFP were sampled from a Euro 4 light duty vehicle without DPF fuelled by commercial diesel and run over a chassis dyno. Biomass UFP were collected from a modern automatic 25 kW boiler propelled by prime quality spruce pellet. Transmission electron microscopy (TEM) and scanning electron microscopy (SEM) images of both diesel and biomass samples showed aggregates of soot particles, but in biomass samples ash particles were also present. Chemical characterization showed that metals and PAHs total content was higher in diesel samples compared to biomass ones. Human bronchial epithelial (HBEC3) cells were exposed to particles for up to 2 weeks. Changes in the expression of genes involved in xenobiotic metabolism were observed after exposure to both UFP already after 24 h. However, only diesel particles modulated the expression of genes involved in inflammation, oxidative stress and epithelial-to-mesenchymal transition (EMT), increased the release of inflammatory mediators and caused phenotypical alterations, mostly after two weeks of exposure. These results show that diesel UFP affected cellular processes involved in lung and cardiovascular diseases and cancer. Biomass particles exerted low biological activity compared to diesel UFP. This evidence emphasizes that the study of different emission sources contribution to ambient PM toxicity may have a fundamental role in the development of more effective strategies for air quality improvement. •Diesel particles exposure induce significant alterations in bronchial HBEC3 cells.•Xenobiotic metabolism and oxidative stress pathways are modulated.•Sub-chronic exposure conditions show significant pro-inflammatory effects.•Epithelial-mesenchymal transition genes, cell morphology and migration are affected.•Biomass particles exposed cells show minor effects also after sub-chronic exposure. Diesel more than biomass UFP induce gene expression changes, inflammatory mediators release and phenotypical alterations. These effects were mostly observed after sub-chronic exposure.</abstract><cop>England</cop><pub>Elsevier Ltd</pub><pmid>27194366</pmid><doi>10.1016/j.envpol.2016.05.015</doi><tpages>10</tpages></addata></record>
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subjects Air Pollutants - adverse effects
Air Pollutants - analysis
Biofuels
Biomass
Cells, Cultured
Chemical characterization
Diesel
Environmental Exposure - adverse effects
Environmental Exposure - analysis
Fossil Fuels
Heating - methods
Humans
Inflammation - etiology
Inflammation - genetics
Inflammation - metabolism
In vitro toxicology
Lung - cytology
Lung - drug effects
Lung - metabolism
Metals - adverse effects
Metals - analysis
Oxidative Stress - drug effects
Oxidative Stress - genetics
Particle Size
Particulate Matter - adverse effects
Particulate Matter - chemistry
Polycyclic Aromatic Hydrocarbons - adverse effects
Polycyclic Aromatic Hydrocarbons - analysis
Respiratory Mucosa - cytology
Respiratory Mucosa - drug effects
Respiratory Mucosa - metabolism
Soot - adverse effects
Soot - chemistry
Ultrafine particles
Vehicle Emissions - analysis
Xenobiotics - metabolism
title Physico-chemical properties and biological effects of diesel and biomass particles
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