Skip to main page content
U.S. flag

An official website of the United States government

Dot gov

The .gov means it’s official.
Federal government websites often end in .gov or .mil. Before sharing sensitive information, make sure you’re on a federal government site.

Https

The site is secure.
The https:// ensures that you are connecting to the official website and that any information you provide is encrypted and transmitted securely.

Access keys NCBI Homepage MyNCBI Homepage Main Content Main Navigation
. 2018 Mar 1:342:99-107.
doi: 10.1016/j.taap.2018.01.024. Epub 2018 Jan 31.

Investigating mitochondrial dysfunction in human lung cells exposed to redox-active PM components

Affiliations

Investigating mitochondrial dysfunction in human lung cells exposed to redox-active PM components

Katelyn S Lavrich et al. Toxicol Appl Pharmacol. .

Abstract

Exposure to ambient particulate matter (PM) causes cardiopulmonary morbidity and mortality through mechanisms that involve oxidative stress. 1,2-naphthoquinone (1,2-NQ) is a ubiquitous component of PM and a potent redox-active electrophile. We previously reported that 1,2-NQ increases mitochondrial H2O2 production through an unidentified mechanism. We sought to characterize the effects of 1,2-NQ exposure on mitochondrial respiration as a source of H2O2 in human airway epithelial cells. We measured the effects of acute exposure to 1,2-NQ on oxygen consumption rate (OCR) in the human bronchial epithelial cell line BEAS-2B and mitochondrial preparations using extracellular flux analysis. Complex-specific assays and NADPH depletion by glucose deprivation distinguished between mitochondrial and non-mitochondrial oxygen utilization. 1,2-NQ exposure of BEAS cells caused a rapid, marked dose-dependent increase in OCR that was independent of mitochondrial respiration, exceeded the OCR observed after mitochondrial uncoupling, and remained sensitive to NADPH depletion, implicating extra-mitochondrial redox cycling processes. Similar effects were observed with the environmentally relevant redox-cycling quinones 1,4-naphthoquinone and 9,10-phenanthrenequinone, but not with quinones that do not redox cycle, such as 1,4-benzoquinone. In mitochondrial preparations, 1,2-NQ caused a decrease in Complex I-linked substrate oxidation, suggesting impairment of pyruvate utilization or transport, a novel mechanism of mitochondrial inhibition by an environmental exposure. This study also highlights the methodological utility and challenges in the use of extracellular flux analysis to elucidate the mechanisms of action of redox-active electrophiles present in ambient air.

Keywords: Air pollution; Bioenergetics; Extracellular flux; Mitochondria; Quinones.

PubMed Disclaimer

Conflict of interest statement

Conflict of Interest

The authors declare they have no actual or potential competing financial interests.

Figures

Figure 1
Figure 1. 1,2-NQ increases basal Oxygen Consumption Rate (OCR, pmol/min)
Bioenergetic effects of 1,2-NQ on BEAS cells were measured using the Cell Mito Stress Test on a XFe96 analyzer. An acute injection of 1,2-NQ was followed by additions of 1 uM oligomycin, 0.25 uM FCCP, and 1 uM antimycin A and rotenone at the indicated times. Data displayed as mean +/− SEM, n ≥ 10. One-sided error bars are used for clarity.
Figure 2
Figure 2. 1,2-NQ-induced OCR increases are independent of mitochondrial electron transport
A. BEAS cells were treated with 1 uM antimycin A and 1 uM rotenone for 13 min prior to addition of DMSO (vehicle), the indicated concentration of 1,2-NQ, or 0.25 uM FCCP. B. The change in OCR after acute injection was calculated from rotenone/antimycin A-pretreated baseline, mean +/− SEM, n = 3, * indicates significant difference from the pretreated baseline (p < 0.05).
Figure 3
Figure 3. Exposure to environmentally relevant redox-cycling quinones increases OCR
BEAS cells were treated with DMSO (vehicle), the indicated concentrations of 1,2-NQ, 1,4-NQ, 9,10-PQ, BQ, or 0.25 uM FCCP following a baseline OCR collection period of 18 min on the extracellular flux analyzer. Shown is the change in OCR at 6 min of exposure relative to basal value. * indicates the compound-induced OCR is significantly different from baseline OCR (p<0.05). For 1,2-NQ (3-50 uM), n ≥ 11. For 1,4-NQ, n ≥ 7. For 9,10-PQ (3-50 uM), n ≥ 6. For 100 uM of all quinones, n=3. For BQ, n =3. For FCCP, n = 4. Data displayed as mean +/− SEM.
Figure 4
Figure 4. Glucose starvation blunts quinone-induced increase in OCR
BEAS cells were starved of glucose (open bars) or provided with 10 mM glucose (closed bars) 2 hours prior to start of assay. BEAS cells were treated with DMSO (vehicle), the indicated concentrations of 1,2-NQ, 1,4-NQ, 9,10-PQ, BQ, or 0.25 uM FCCP following a baseline OCR collection period of 18 min on the extracellular flux analyzer. Shown is the change in OCR relative to basal value, * indicates the compound-induced OCR was significantly (p<0.05) different from baseline OCR. # indicates a significant (p<0.05) difference between glucose starved and supplemented groups. Data displayed as mean +/− SEM. For DMSO, 1,2-NQ and 1,4-NQ, n ≥ 4. For 9,10-PQ and FCCP, n = 3.
Figure 5
Figure 5. Exposure to redox cycling quinones induces H2O2 production
BEAS cells were exposed to DMSO (vehicle) or the indicated concentrations of 1,2-NQ, 1,4-NQ, 9,10-PQ, BQ, or H2O2 for 18 min. H2O2 was measured in apical media as fluorescence at excitation λ= 545 nm, emission λ= 590 nm following a 30 min incubation in the presence of HRP and Amplex Red. n = 3, mean +/− SEM.
Figure 6
Figure 6. Mitochondrial preparations show a diminished 1,2-NQ-induced OCR increase
All values shown as a change from basal OCR observed immediately after addition of DMSO or the indicated concentration of 1,2-NQ. All values were normalized to the mass of mitochondrial protein in each preparation. * indicates the change in OCR was significantly (p<0.05) different from DMSO treatment within each preparation. # indicates the change in OCR was statistically different (p<0.05) between mitochondrial preparations. For intact cells, n ≥ 11; for permeabilized cells, n ≥ 13; for isolated mitochondria, n = 5. Data shown as mean +/− SEM.
Figure 7
Figure 7. 1,2-NQ impairs Complex I-linked respiration in permeabilized cells
A. BEAS cells were permeabilized with XF PMP and treated as indicated with buffer, DMSO,1,2-NQ, 1,4-NQ, 9,10-PQ, BQ for 10 min, followed by an injection of 10 mM pyruvate/2 mM malate or 10 mM glutamate/10 mM malate, in a buffer containing 4 mM ADP, and mitochondrial respiration was measured as OCR. * indicates activity was significantly (p<0.05) different from buffer control. # indicates a significant (p<0.05) difference between glutamate and pyruvate supplementation. For 1,2-NQ, 1,4-NQ, Buffer, and DMSO, n ≥ 4. For 9,10-PQ and BQ, n ≥ 3. B. Complex II-linked mitochondrial respiration measured by OCR after addition of 10 mM succinate/4 mM ADP/2 uM rotenone. BEAS cells were permeabilized with XF PMP and treated as indicated with DMSO,1,2-NQ, 1,4-NQ, 9,10-PQ, BQ for 10 min, and substrate oxidation was measured as OCR. * indicates activity was significantly (p<0.05) different from buffer control. For DMSO and 1,2-NQ, n = 4. For 1,4-NQ and BQ, n = 3. C. BEAS cells were treated with 10 uM or 50 uM 1,2-NQ for 15 min and Complex I activity was assayed as the NADH-dependent reduction of a chromophore over 30 min. * indicates activity was significantly (p<0.05) different from media control, n = 3. Data shown as mean +/− SEM.

References

    1. Alves CA, Barbosa C, Rocha S, Calvo A, Nunes T, Cerqueira M, Pio C, Karanasiou A, Querol X. Elements and polycyclic aromatic hydrocarbons in exhaust particles emitted by light-duty vehicles. Environmental Science and Pollution Research. 2015;22:11526–11542. - PubMed
    1. Brand MD. The sites and topology of mitochondrial superoxide production. Experimental Gerontology. 2010;45:466–472. - PMC - PubMed
    1. Brand MD, Nicholls DG. Assessing mitochondrial dysfunction in cells. Biochemical Journal. 2011;435:297–312. - PMC - PubMed
    1. Cheng WY, Currier J, Bromberg PA, Silbajoris R, Simmons SO, Samet JM. Linking oxidative events to inflammatory and adaptive gene expression induced by exposure to an organic particulate matter component. Environmental Health Perspectives. 2012;120:267. - PMC - PubMed
    1. Cho AK, Di Stefano E, You Y, Rodriguez CE, Schmitz DA, Kumagai Y, Miguel AH, Eiguren-Fernandez A, Kobayashi T, Avol E. Determination of four quinones in diesel exhaust particles, SRM, 1649a, and atmospheric PM2. 5 special issue of aerosol science and technology on findings from the fine particulate matter supersites program. Aerosol Science and Technology. 2004;38:68–81.

Publication types

MeSH terms