scholarly journals Particulate Matter from Both Heavy Fuel Oil and Diesel Fuel Shipping Emissions Show Strong Biological Effects on Human Lung Cells at Realistic and Comparable In Vitro Exposure Conditions

PLoS ONE ◽  
2015 ◽  
Vol 10 (6) ◽  
pp. e0126536 ◽  
Author(s):  
Sebastian Oeder ◽  
Tamara Kanashova ◽  
Olli Sippula ◽  
Sean C. Sapcariu ◽  
Thorsten Streibel ◽  
...  
Chemosphere ◽  
2015 ◽  
Vol 128 ◽  
pp. 321-326 ◽  
Author(s):  
Faye F. Liu ◽  
Cheng Peng ◽  
Jack C. Ng

Cancers ◽  
2021 ◽  
Vol 13 (4) ◽  
pp. 750
Author(s):  
Werner E. G. Müller ◽  
Meik Neufurth ◽  
Shunfeng Wang ◽  
Heinz C. Schröder ◽  
Xiaohong Wang

The anti-cancer antitumor antibiotic bleomycin(s) (BLM) induces athyminic sites in DNA after its activation, a process that results in strand splitting. Here, using A549 human lung cells or BEAS-2B cells lunc cells, we show that the cell toxicity of BLM can be suppressed by addition of inorganic polyphosphate (polyP), a physiological polymer that accumulates and is released from platelets. BLM at a concentration of 20 µg ml−1 causes a decrease in cell viability (by ~70%), accompanied by an increased DNA damage and chromatin expansion (by amazingly 6-fold). Importantly, the BLM-caused effects on cell growth and DNA integrity are substantially suppressed by polyP. In parallel, the enlargement of the nuclei/chromatin in BLM-treated cells (diameter, 20–25 µm) is normalized to ~12 µm after co-incubation of the cells with BLM and polyP. A sequential application of the drugs (BLM for 3 days, followed by an exposure to polyP) does not cause this normalization. During co-incubation of BLM with polyP the gene for the BLM hydrolase is upregulated. It is concluded that by upregulating this enzyme polyP prevents the toxic side effects of BLM. These data might also contribute to an application of BLM in COVID-19 patients, since polyP inhibits binding of SARS-CoV-2 to cellular ACE2.


1989 ◽  
pp. 103-117
Author(s):  
C. C. Harris ◽  
J. C. Willey ◽  
N. Matsukura ◽  
J. F. Lechner ◽  
M. Miyashita ◽  
...  

2011 ◽  
Vol 86 (1) ◽  
pp. 121-135 ◽  
Author(s):  
Todd L. Watterson ◽  
Brett Hamilton ◽  
Randy S. Martin ◽  
Roger A. Coulombe

2017 ◽  
Vol 280 ◽  
pp. S212
Author(s):  
Hang Nguyen ◽  
Kenneth Sexton ◽  
Lisa Smeester ◽  
Kjersti Marie Aagaard ◽  
Cynthia Do Shope ◽  
...  

CHEST Journal ◽  
1983 ◽  
Vol 83 (5) ◽  
pp. 81S-82 ◽  
Author(s):  
A. G. Leitch ◽  
R. A. Lewis ◽  
E. J. Corey ◽  
K. F. Austen

2012 ◽  
Vol 12 (2) ◽  
pp. 5065-5105 ◽  
Author(s):  
S. Ebersviller ◽  
K . Lichtveld ◽  
K. G. Sexton ◽  
J. Zavala ◽  
Y-H. Lin ◽  
...  

Abstract. This is the first of a three-part study designed to demonstrate dynamic entanglements among gaseous organic compounds (VOC), particulate matter (PM), and their subsequent potential biological effects. We study these entanglements in increasingly complex VOC and PM mixtures in urban-like conditions in a large outdoor chamber. To the traditional chemical and physical characterizations of gas and PM, we added new measurements of gas-only- and PM-only-biological effects, using cultured human lung cells as model indicators. These biological effects are assessed here as increases in cellular damage or expressed irritation (i.e., cellular toxic effects) from cells exposed to chamber air relative to cells exposed to clean air. The exposure systems permit gas-only- or PM-only-exposures from the same air stream containing both gases and PM in equilibria, i.e., there are no extractive operations prior to cell exposure. Our simple experiments in this part of the study were designed to eliminate many competing atmospheric processes to reduce ambiguity in our results. Simple volatile and semi-volatile organic gases that have inherent cellular toxic properties were tested individually for biological effect in the dark (at constant humidity). Airborne mixtures were then created with each compound and PM that has no inherent cellular toxic properties for another cellular exposure. Acrolein and p-tolualdehyde were used as model VOCs and mineral oil aerosol (MOA) was selected as a surrogate for organic-containing PM. MOA is appropriately complex in composition to represent ambient PM, and it exhibits no inherent cellular toxic effects and thus did not contribute any biological detrimental effects on its own. Chemical measurements, combined with the responses of our biological exposures, clearly demonstrate that gas-phase pollutants can modify the composition of PM (and its resulting detrimental effects on lung cells) – even if the gas-phase pollutants are not considered likely to partition to the condensed phase: the VOC-modified-PM showed significantly more damage and inflammation to lung cells than did the original PM. Because gases and PM are transported and deposited differently within the atmosphere and the lungs, these results have significant consequences. For example, current US policies for research and regulation of PM do not recognize this "effect modification" phenomena (NAS, 2004). These results present an unambiguous demonstration that – even in these simple mixtures – physical and thermal interactions alone can cause a modification of the distribution of species among the phases of airborne pollution mixtures and can result in a non-toxic phase becoming toxic due to atmospheric thermal processes only. Subsequent work extends the simple results reported here to systems with photochemical transformations of complex urban mixtures and to systems with diesel exhaust produced by different fuels.


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