| Literature DB >> 35624694 |
Maud Hemmendinger1, Jean-Jacques Sauvain1, Nancy B Hopf1, Guillaume Suárez1, Irina Guseva Canu1.
Abstract
Exhaled breath condensate (EBC) has attracted substantial interest in the last few years, enabling the assessment of airway inflammation with a non-invasive method. Concentrations of 8-Hydroxydesoxyguanosine (8-OHdG) and 8-isoprostane in EBC have been suggested as candidate biomarkers for lung diseases associated with inflammation and oxidative stress. EBC is a diluted biological matrix and consequently, requires highly sensitive chemical analytic methods (picomolar range) for biomarker quantification. We developed a new liquid chromatography coupled to tandem mass spectrometry method to quantify 8-OHdG and 8-isoprostane in EBC simultaneously. We applied this novel biomarker method in EBC obtained from 10 healthy subjects, 7 asthmatic subjects, and 9 subjects with chronic obstructive pulmonary disease. Both biomarkers were below the limit of detection (LOD) despite the good sensitivity of the chemical analytical method (LOD = 0.5 pg/mL for 8-OHdG; 1 pg/mL for 8-isoprostane). This lack of detection might result from factors affecting EBC collections. These findings are in line with methodological concerns already raised regarding the reliability of EBC collection for quantification of 8-OHdG and 8-isoprostane. Precaution is therefore needed when comparing literature results without considering methodological issues relative to EBC collection and analysis. Loss of analyte during EBC collection procedures still needs to be resolved before using these oxidative stress biomarkers in EBC.Entities:
Keywords: 8-Isoprostane; 8-hydroxy-2′-deoxyguanosine; exhaled breath condensate; liquid chromatography; mass spectrometry; oxidative stress biomarkers
Year: 2022 PMID: 35624694 PMCID: PMC9138069 DOI: 10.3390/antiox11050830
Source DB: PubMed Journal: Antioxidants (Basel) ISSN: 2076-3921
MS transitions and instrumental conditions for 8-OHdG and 8-isoprostane analysis. The vaporizer temperature was 350 °C with the ion transfer tube set at 390 °C. The argon gas pressure was set at 1.5 mTorr.
| Compounds | Polarity | Mass Transitions ( | Spray | Collision | RF Lens (V) |
|---|---|---|---|---|---|
| 8-OHdG | positive | 284 → 140 | 3700 | 28.8 | 37 |
|
| 10 | 37 | |||
| 284 → 243 | 10.2 | 37 | |||
| [15N5]-8-OHdG | positive |
| 3700 | 10 | 40 |
| 8-isoprostane | negative |
| 3400 | 25 | 80 |
| 353 → 291 | 20 | 80 | |||
| 353 → 309 | 20 | 80 | |||
| 8-isoprostane-d4 | negative |
| 3400 | 25 | 78 |
Mass transitions in bold are quantification transitions, others are confirmation transitions.
Summary of participant demographics (n = 26).
| Healthy | Asthmatic | COPD | |
|---|---|---|---|
| Number of subjects (male/female) | 10 (6/4) | 7 (3/4) | 9 (6/3) |
| Age mean years ± SD (range) | 51 ± 5.2 (44–60) | 47 ± 5.2 (40–57) | 54 ± 5.8 (41–60) |
| BMI mean kg/m2 ± SD (range) | 25 ± 3.7 (20–32) | 25 ± 2.4 (22–28) | 24 ± 4.9 (19–34) |
| FEV1/FVC1 ratio | 0.771 ± 0.04 (0.713–0.825) | 0.665 ± 0.04 (0.597–0.697) | 0.611 ± 0.06 (0.501–0.675) |
| Smokers (%) | 30% | 28% | 66% |
SD = standard deviation; BMI = body mass index; COPD = chronic obstructive pulmonary disease; FEV1 = forced expiratory volume in one second; FVC = forced vital capacity.
Figure 1(a,b) Partial chromatogram of a standard injection at 5 pg/mL (left), of the lowest quality check (spiked EBC at 5 pg/mL, middle) and of a typical EBC sample (right), with retention times (RT) for 8-isoprostane and 8-OHdG, respectively. The units of the y-axis are in arbitrary units, counts per second. (a,b) are chromatograms obtained from the same healthy volunteer.
Figure 2Slope signal (not corrected with IS) of the calibrations (minimum of 5 levels) obtained with water and EBC after lyophilization (lyoph) or vacuum concentration, in comparison with standard solutions without any concentration step for the biomarker (a) 8-OHdG and (b) 8-isoprostane, respectively. Error bars correspond to a minimum of two independent repetitions. au= Arbitrary unit; lyoph = lyophilization; standard = non-concentrated standard; H2O lyoph = concentrated standard. * Statistically significant difference (p < 0.05) compared to the standard without the concentration.
Figure 3Effect of using the centrifugal concentrator system on the signal of both analytes in EBC. Bars correspond to standard deviation of three independent repetitions. CCS = centrifugal concentrator system.
Reported concentrations of 8-isoprostane in EBC in literature by validated RIA, GC–MS, and LC–MS methods.
| Reference | Year | Study Group | Analytical Method | Collection Apparatus | Concentration of EBC | Lod | Basal Concentration |
|---|---|---|---|---|---|---|---|
| 2012 | healthy individuals | LC–MS/MS | TurboDeccs | lyophilized | 1 pg/mL |
| |
| 2009 | healthy individuals | LC–MS/MS | Ecoscreen | - | 5 pg/mL |
| |
| 2014 | healthy individuals | affinity sorbant + LC–MS/MS | Ecoscreen | drying under nitrogen | 2.5 pg/mL |
| |
| 1998 | healthy individuals | GC–MS | Teflon-lined tubing (Tygon) | - | 0.02 pg/mL * |
| |
| 2010 | healthy individuals | GC–MS | Ecoscreen | drying under nitrogen | - | 0.19 (0.14–0.29) pg/mL a | |
| 2011 | healthy individuals | GC–MS | Ecoscreen | drying under nitrogen | - | 0.26 (0.2–0.47) pg/mL a | |
| 2012 | healthy individuals | LC–MS/MS | RTube | drying under nitrogen | 0.05–0.1 pg | 0.9 (0.2–1.7) pg/mL d | |
| 2010 | healthy individuals | LC–MS/MS | Ecoscreen | lyophilized | 8 pg/mL | 86.7 (65.8–105.8) pg/mL a | |
| 2017 | healthy individuals | affinity sorbant + LC–MS/MS | Ecoscreen | drying under nitrogen | 1 pg/mL | 3.14 (2.07) pg/mL c | |
| 2021 | healthy individuals | affinity sorbant + LC–MS/MS | Ecoscreen | drying under nitrogen | 1 pg/mL | 3.930 (3.655) pg/mL c | |
| 2010 | healthy individuals | affinity sorbant + LC–MS/MS | Ecoscreen | drying under nitrogen | 1 pg/mL | 4.44 ± 2.01 pg/mL b | |
| 2008 | healthy individuals | affinity sorbant + LC–MS/MS | Ecoscreen | drying under nitrogen | 1 pg/mL | 36 (20–55) pg/mL b | |
| 2016 | healthy ex-smokers | RIA | Ecoscreen | - | 2 pg/mL | 8 (6.0–8.8) pg/mL e | |
| 2000 | healthy individuals | RIA | Ecoscreen | - | 4 pg/mL | 10.8 ± 0.8 pg/mL b | |
| 2008 | healthy individuals | RIA | Ecoscreen | - | 10 pg/mL | 15.5 (11.5–17.0) pg/mL d | |
| 2021 | exposed people to carbon nanotubes | affinity sorbant + LC–MS/MS | Ecoscreen | drying under nitrogen | 1 pg/mL | 5.920 (9.040) pg/mL c | |
| 2017 | exposed people to metal oxidenanoparticles | affinity sorbant + LC–MS/MS | Ecoscreen | drying under nitrogen | 1 pg/mL | 7.13 (8.21) pg/mL c | |
| 2008 | exposed people to asbestos | affinity sorbant + LC–MS/MS | Ecoscreen | drying under nitrogen | 1 pg/mL | 60 (50–70) pg/mL b | |
| 2016 | smokers | RIA | Ecoscreen | - | 2 pg/mL | 11.2 (6.4–18.8) pg/mL e | |
| 2012 | smokers | LC–MS/MS | TurboDeccs | lyophilized | 1 pg/mL | 13–35 pg/mL | |
| 1998 | patients with ALI/ARDS | GC–MS | Teflon-lined tubing (Tygon) | - | 0.02 pg/mL * |
| |
| 2011 | asthma patients | GC–MS | Ecoscreen | drying under nitrogen | - | 0.25 ± 0.12 pg/mL b | |
| 2011 | asthma patients | GC–MS | Ecoscreen | drying under nitrogen | - | 0.32 (0.15–0.3) pg/mL a | |
| 2010 | asthma patients | GC–MS | TurboDeccs | drying under nitrogen | 3.9 pg/mL | 68 (10.3) pg/mL e | |
| 2016 | COPD patients | RIA | Ecoscreen | - | 2 pg/mL | 17.8 (8.8–31.2) pg/mL e |
ALI = and acute lung injury, ARDS = acute respiratory distress syndrome, RIA = radioimmunoassays. a Values are presented as medians (25th–75th percentiles); b Values are presented as mean (±SD); c Values are presented as medians (IQR); d Values are presented as median (range); e Values are presented as mean (±SEM); * LOD obtained from a publication of [30].
Reported EBC concentrations of 8-OHdG in the literature by validated ELISA and LC–MS methods.
| Reference | Year | Study Group | Analytical Method Approach | Collection Apparatus | Concentration of Ebc | Lod | Basal Concentration |
|---|---|---|---|---|---|---|---|
| 2019 | healthy individuals | ELISA kit | TurboDeccs | - | - | 3 pg/mL | |
| 2012 | healthy individuals | LC–MS/MS | EcoScreen | - | 7 pg/mL | 10 (9.0–11.0) pg/mL c | |
| 2016 | healthy individuals | LC–MS/MS | EcoScreen | - | 7 pg/mL | 13 (11.5–14.5) pg/mL c | |
| 2010 | healthy individuals | LC–MS/MS | EcoScreen | - | 7 pg/mL | 14.8 (12.8–19.9) pg/mL a | |
| 2018 | healthy individuals | LC–MS/MS | EcoScreen | - | 7 pg/mL | 18 (15.0–21.0) pg/mL c | |
| 2011 | healthy individuals | ELISA kit | EcoScreen | - | 41 pg/mL | 360 ± 90 pg/mL b | |
| 2017 | exposed welders | ELISA kit | R-tube | - |
| ||
| 2011 | smokers | ELISA kit | EcoScreen | - | 41 pg/mL | 520 ± 150 pg/mL b | |
| 2011 | passive smokers | ELISA kit | EcoScreen | - | 41 pg/mL | 310 ± 100 pg/mL b | |
| 2019 | COPD patients | ELISA kit | TurboDeccs | - | - | 36 pg/ml | |
| 2010 | silica- or asbestos-disorders due to occupational exposure patients | LC–ESI–MS/MS | EcoScreen | - | 7 pg/mL | 46.5 (39.4–49.9) pg/mL a |
a Values are presented as medians (25th–75th percentiles); b Values are presented as mean (±SD); c Values are presented as median (range).