Biological factor related to Asian sand dust particles contributes to the exacerbation of asthma.

Epidemiologic studies have revealed that Asian sand dust particles (ASDs) can affect respiratory and immune health represented by asthma. Factors responsible for the exacerbation of asthma remain unclear. The fungus Bjerkandera adusta (B.ad) and polycyclic aromatic hydrocarbons such as benzo[a]pyrene (BaP) have been identified in ASDs collected from the atmosphere when an ASD event occurred. We investigated the effects of B.ad and BaP related to ASDs on respiratory and immune systems. Bone marrow-derived antigen-presenting cells (APCs) and splenocytes from atopic prone NC/Nga mice and human airway epithelial cells were exposed to the B.ad or to BaP in the presence and absence of heated-ASDs (H-ASDs). B.ad and BaP in both the presence and absence of H-ASDs increased the expression of cell surface molecules on APCs. H-ASDs alone slightly activated APCs. The expressions induced by B.ad were higher than those induced by BaP in the presence and absence of H-ASDs. There were no remarkable effects on the activation of splenocytes or the proinflammatory responses in airway epithelial cells. These results suggest that B.ad rather than BaP contributes to the exacerbation of asthma regardless of the presence or absence of sand particles, particularly by the activation of the immune system via APCs. Copyright © 2016 John Wiley & Sons, Ltd.

Synergistic effect of carbon nuclei and polyaromatic hydrocarbons on respiratory and immune responses.

Particulate matter with aerodynamic diameter ≤2.5 µm (PM2.5 ) is generally composed of carbon nuclei associated with various organic carbons, metals, ions and biological materials. Among these components, polyaromatic hydrocarbons (PAHs) such as benzo(a)pyrene (BaP) and quinones have detrimental effects on airway epithelial cells and immunodisrupting effects, which leads to the exacerbation of respiratory allergies. The effects of PAHs and the carbon nuclei, separately as well as in combination, remain to be established. We investigated the effects of BaP, 9,10-phenanthroquinone (9,10-PQ), and 1,2-napthoquinone (1,2-NQ) and their combined effects with heated diesel exhaust particle (H-DEP) as carbon nuclei of typical PM2.5 . We exposed human airway epithelial cells (BEAS-2B), murine bone marrow-derived antigen-presenting cells (APCs), and murine splenocytes to BaP, 9,10-PQ, or 1,2-NQ in the presence and absence of H-DEP. Several important inflammatory cytokines and cell surface molecules were measured. PAHs alone did not have apparent cytotoxic effects on BEAS-2B, whereas combined exposure with H-DEP induced noticeable detrimental effects which mainly reflected the action of H-DEP itself. BaP increased CD86 expression as an APC surface molecule regardless of the presence or absence of H-DEP. None of the BaP, 9,10-PQ, or 1,2-NQ exposure alone or their combined exposure with H-DEP resulted in any significant activation of splenocytes. These results suggest that PAHs and carbon nuclei show additive effects, and that BaP with the carbon nuclei may contribute to exacerbations of allergic respiratory diseases including asthma by PM2.5 , especially via antigen-presenting cell activation.

Effects of Components of PM2.5 Collected in Japan on the Respiratory and Immune Systems.

Epidemiologic studies have reported that particulate matter with aerodynamic diameters ≤2.5 µm (PM2.5) affect respiratory diseases, including asthma. The components and/or factors of PM2.5 that contribute to the exacerbation of asthma have not been identified. We investigated the effects of extracts of PM2.5 collected in Japan on the respiratory and immune systems. PM2.5 was collected from an industrial area and an urban area in December 2013. Airway epithelial cells and immune cells were exposed to aqueous or organic extracts of PM2.5. Exposure to extracts from both areas, especially to organic extracts rather than aqueous extracts, caused a pro-inflammatory response via interleukin (IL) 6 production from airway epithelial cells, and it induced the maturation/activation of bone marrow-derived antigen-presenting cells via dendritic and epithelial cell (DEC) 205 and cluster of differentiation (CD) 86 expression and proportional changes in the constitution of the splenocytes. The extracts collected from the industrial area tended to show greater effects than those from the urban area. These results suggest that organic components of PM2.5 affect the respiratory and immune systems. These effects can differ by the collection areas. In addition, IL-6, DEC205, and CD86 can be predictive biomarkers for the respiratory and immune effects of ambient PM2.5.

Effects of air pollution-related heavy metals on the viability and inflammatory responses of human airway epithelial cells.

Various metals produced from human activity are ubiquitously detected in ambient air. The metals may lead to induction and/or exacerbation of respiratory diseases, but the significant metals and factors contributing to such diseases have not been identified. To compare the effects of each metal and different oxidation states of metals on human airway, we examined the viability and production of interleukin (IL)-6 and IL-8 using BEAS-2B cell line, derived from human airway epithelial cells. Airway epithelial cells were exposed to Mn(2+), V(4+), V(5+), Cr(3+), Cr(6+), Zn(2+), Ni(2+), and Pb(2+) at a concentration of 0.5, 5, 50, or 500 µmol/L for 24 hours. Mn and V decreased the cell viability in a concentration-dependent manner, and V(5+) tended to have a greater effect than V(4+). The Cr decreased the cell viability, and (Cr(+6)) at concentrations of 50 and 500 µmol/L was more toxic than (Cr(+3)). Zn at a concentration of 500 µmol/L greatly decreased the cell viability, whereas Ni at the same concentration increased it. Pb produced fewer changes. Mn and Ni at a concentration of 500 µmol/L induced the significant production of IL-6 and IL-8. However, most of the metals including (V(+4), V(+5)), (Cr(+3), Cr(+6)), Zn, and Pb inhibited the production of both IL-6 and IL-8. The present results indicate that various heavy metals have different effects on toxicity and the proinflammatory responses of airway epithelial cells, and those influences also depend on the oxidation states of the metals.

Free advanced glycation end product distribution in blood components and the effect of genetic polymorphisms.

One hypothesis regarding the cause of diabetic complications is that advanced glycation end products (AGEs) bind to the AGE receptor and induce changes in gene expression. However, what AGEs exist in vivo and how individual AGEs are produced and impact body metabolic process to cause diabetes complications are not understood. We developed a new precise method to measure AGEs using LC-MS/MS with a new column and measured 7 free AGEs, including N(6)-carboxymethyllysine (CML), N(6)-(1-carboxyethyl)-l-lysine (CEL) and N5-(5-hydro-5-methyl-4-imidazolon-2-yl)L-ornithine (MG-H1), in human blood components. Blood was obtained from 9 people, and free AGEs were measured in individual blood components with LC-MS/MS before and after a meal. Free CML and CEL were abundant in erythrocytes, with 92% of free CML and 85% of free CEL localized in erythrocytes. In contrast, 60% of free MG-H1 was distributed in the serum. After the meal, free serum MG-H1 increased, but CML and CEL did not. CML and CEL are mainly distributed in erythrocytes and were not affected by the meal, indicating that they are produced in vivo. However, the main source of MG-H1 is the meal. The effect of genetic polymorphisms on AGEs was also investigated. Low activity type aldehyde dehydrogenase 2 (ALDH2) increased the CML concentration in the blood. This is the first observation that shows that the metabolic process of CML and CEL is different from that of MG-H1 and the effect of ALDH2 SNPs on CML.