- ICH GCP
- US Clinical Trials Registry
- Clinical Trial NCT03104387
Health Effects of Occupational Exposure to Combustion Particles - a Study on Volunteers Performing as Train Conductors (BioTrack)
Effects of Diesel Combustion Generated Air Pollution on Cardiovascular Function and Oxidatively Damaged DNA in Healthy Volunteers
Ambient air pollution is a complex mixture of gaseous pollutants and particulate matter (PM). PM has a recognized important role in human health. There is a strong scientific consensus on the independent association of PM and adverse cardiovascular and respiratory effects, as well as cancer. It is reasonable to expect that the smaller particles (ultrafine particles, UFP) may have an enhanced toxicity relative to other PM size fractions, due to physical properties and potential to translocation beyond the lung.
A recent Danish report concluded that train conductors on a working day, and in two specific diesel engine trains, are exposed to higher concentrations of diesel exhaust than by constant stay in a busy street. Indeed, the average exposure for train conductors on such engines was around 100,000-150,000 UFP per cm3 as compared with around 40,000 per cm3 on a busy street in Copenhagen [1]. The aim of this study is to investigate if this occupational exposure is associated with vascular and respiratory impairment and DNA damage.
Study Overview
Status
Conditions
Intervention / Treatment
Study Type
Enrollment (Actual)
Phase
- Not Applicable
Contacts and Locations
Study Locations
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Copenhagen, Denmark
- University of Copenhagen
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Participation Criteria
Eligibility Criteria
Ages Eligible for Study
Accepts Healthy Volunteers
Genders Eligible for Study
Description
Inclusion Criteria:
- Healthy volunteers
- Legally competent subjects
Exclusion Criteria:
- Current smokers
- Pregnancy
- Alcohol and drug abuse
- Prescriptionary use of anti-inflammatory or cardiovascular medication
Study Plan
How is the study designed?
Design Details
- Primary Purpose: BASIC_SCIENCE
- Allocation: RANDOMIZED
- Interventional Model: CROSSOVER
- Masking: NONE
Arms and Interventions
Participant Group / Arm |
Intervention / Treatment |
|---|---|
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EXPERIMENTAL: Diesel train - exposure scenario
The same study person will be exposed to two different scenarios, at different times and for three consecutive days.
It will be a lag time of 2 weeks between each exposure scenario.
The "exposure" scenario is defined as a workday (6 hours) on the diesel ME-driven model regional train.
The Diesel Train Scenario is performed twice.
After the scenario completion (on the third day in defined train routes) the vascular function, lung function, blood and urine samplings are performed.
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Exposure to air with high level of ultrafine particles (Diesel train)
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SHAM_COMPARATOR: Electric train - low exposure scenario
The same study person will be exposed to two different scenarios, at different times and for three consecutive days.
It will be a lag time of 2 weeks between each exposure scenario.
The "low exposure" scenario is defined as a workday (6 hours) on the electric train.
The Diesel Train Scenario is performed twice.
After the scenario completion (on the third day in defined train routes) the vascular function, lung function, blood and urine samplings are performed.
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Exposure to air with low level of ultrafine particles (Electric train)
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What is the study measuring?
Primary Outcome Measures
Outcome Measure |
Measure Description |
Time Frame |
|---|---|---|
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Reactive hyperemia index measured by peripheral arterial tonometry
Time Frame: Peripheral arterial tonometry is assessed after each exposure scenario (on the third day after 6 hours on defined train routes per day)
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The primary outcome will be measured in the form of post-ischemic variation followed by the measurement of the vasomotor function after the administration of nitroglycerin, to allow the investigation of the endothelium independent vasodilatation.
The portable device EndoPAT 2000 will be used (Itamar Medical Ltd, Israel) [2-6].
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Peripheral arterial tonometry is assessed after each exposure scenario (on the third day after 6 hours on defined train routes per day)
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Heart rate variability
Time Frame: Assessed after each exposure scenario (on the third day after 6 hours on defined train routes per day)
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Heart rate variability is measured with the EndoPAT 2000 device during baseline recording.
It includes time domain measures (SDNN, pNN50 and RMSSD), high (HF) and low frequency (LF) components as well as LF/HF ratio, based on measurements over 5 minutes.
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Assessed after each exposure scenario (on the third day after 6 hours on defined train routes per day)
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DNA damage in peripheral blood mononuclear cells
Time Frame: Blood is sampled, prepared and stored after each exposure scenario (on the third day after 6 hours on defined train routes per day). Analysis is performed after sample collection completion.
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The levels of strand breaks and formamidopyrimidine-DNA-glycosylase (FPG) sites are measured with the single cell gel electrophoresis assay (comet assay) [7-13]
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Blood is sampled, prepared and stored after each exposure scenario (on the third day after 6 hours on defined train routes per day). Analysis is performed after sample collection completion.
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Secondary Outcome Measures
Outcome Measure |
Measure Description |
Time Frame |
|---|---|---|
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Lung function
Time Frame: The lung function is assessed after each exposure scenario (on the third day after 6 hours on defined train routes per day)
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The lung function is measured with EasyOne 2001 spirometer device (Switzerland).
Lung function measurements includes forced vital capacity (FVC), forced expiratory volume after 1 second (FEV1), peak expiratory flow (PEF) and FEV1/FVC.
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The lung function is assessed after each exposure scenario (on the third day after 6 hours on defined train routes per day)
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Systemic inflammatory markers
Time Frame: Blood is sampled, prepared and stored after each exposure scenario (on the third day after 6 hours on defined train routes per day). Analysis is performed after sample collection completion.
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Acute phase reactants, pro-inflammatory cytokines and cell adhesion molecules
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Blood is sampled, prepared and stored after each exposure scenario (on the third day after 6 hours on defined train routes per day). Analysis is performed after sample collection completion.
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Urinary excretion of 1-hydroxypyrene
Time Frame: Morning urine is sampled, prepared and stored after each exposure scenario (on the morning of the third day after two days with 6 hours on defined train routes). Analysis is performed after sample collection completion.
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The urinary biomarker of exposure to polycyclic aromatic hydrocarbons, 1-hydroxypyrene, is measured with reverse-phase HPLC and standardized for diuresis with the concentration of creatinine
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Morning urine is sampled, prepared and stored after each exposure scenario (on the morning of the third day after two days with 6 hours on defined train routes). Analysis is performed after sample collection completion.
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Serum/plasma bioactivity
Time Frame: Blood is sampled, prepared and serum is stored after each exposure scenario (on the third day after 6 hours on defined train routes per day). Analysis is performed after sample collection completion.
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To assess the potential effects on vascular and endothelial function [14, 15]
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Blood is sampled, prepared and serum is stored after each exposure scenario (on the third day after 6 hours on defined train routes per day). Analysis is performed after sample collection completion.
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Other Outcome Measures
Outcome Measure |
Measure Description |
Time Frame |
|---|---|---|
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Augmentation index
Time Frame: Assessed after each exposure scenario (on the third day after 6 hours on defined train routes per day)
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Measured with the EndoPAT 2000 device during baseline recording.
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Assessed after each exposure scenario (on the third day after 6 hours on defined train routes per day)
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Blood pressure
Time Frame: Assessed after each exposure scenario (on the third day after 6 hours on defined train routes per day)
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Measured with an aneroid sphygmomanometer.
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Assessed after each exposure scenario (on the third day after 6 hours on defined train routes per day)
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Heart rate
Time Frame: Assessed after each exposure scenario (on the third day after 6 hours on defined train routes per day)
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Measured with the EndoPAT 2000 device during baseline recording.
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Assessed after each exposure scenario (on the third day after 6 hours on defined train routes per day)
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Collaborators and Investigators
Sponsor
Investigators
- Principal Investigator: Peter Moller, PhD, University of Copenhagen
Publications and helpful links
General Publications
- Karottki G, Loft S. Rapport vedroerende maaling af udsaettelse for ultrafine partikler blandt ansatte i DSB, 1-48, 2015.
- Brauner EV, Forchhammer L, Moller P, Barregard L, Gunnarsen L, Afshari A, Wahlin P, Glasius M, Dragsted LO, Basu S, Raaschou-Nielsen O, Loft S. Indoor particles affect vascular function in the aged: an air filtration-based intervention study. Am J Respir Crit Care Med. 2008 Feb 15;177(4):419-25. doi: 10.1164/rccm.200704-632OC. Epub 2007 Oct 11.
- Olsen Y, Karottki DG, Jensen DM, Beko G, Kjeldsen BU, Clausen G, Hersoug LG, Holst GJ, Wierzbicka A, Sigsgaard T, Linneberg A, Moller P, Loft S. Vascular and lung function related to ultrafine and fine particles exposure assessed by personal and indoor monitoring: a cross-sectional study. Environ Health. 2014 Dec 15;13:112. doi: 10.1186/1476-069X-13-112.
- Karottki DG, Spilak M, Frederiksen M, Gunnarsen L, Brauner EV, Kolarik B, Andersen ZJ, Sigsgaard T, Barregard L, Strandberg B, Sallsten G, Moller P, Loft S. An indoor air filtration study in homes of elderly: cardiovascular and respiratory effects of exposure to particulate matter. Environ Health. 2013 Dec 28;12:116. doi: 10.1186/1476-069X-12-116.
- Hemmingsen JG, Rissler J, Lykkesfeldt J, Sallsten G, Kristiansen J, Moller P P, Loft S. Controlled exposure to particulate matter from urban street air is associated with decreased vasodilation and heart rate variability in overweight and older adults. Part Fibre Toxicol. 2015 Mar 19;12:6. doi: 10.1186/s12989-015-0081-9.
- Brauner EV, Moller P, Barregard L, Dragsted LO, Glasius M, Wahlin P, Vinzents P, Raaschou-Nielsen O, Loft S. Exposure to ambient concentrations of particulate air pollution does not influence vascular function or inflammatory pathways in young healthy individuals. Part Fibre Toxicol. 2008 Oct 6;5:13. doi: 10.1186/1743-8977-5-13.
- Forchhammer L, Moller P, Riddervold IS, Bonlokke J, Massling A, Sigsgaard T, Loft S. Controlled human wood smoke exposure: oxidative stress, inflammation and microvascular function. Part Fibre Toxicol. 2012 Mar 27;9:7. doi: 10.1186/1743-8977-9-7.
- Brauner EV, Forchhammer L, Moller P, Simonsen J, Glasius M, Wahlin P, Raaschou-Nielsen O, Loft S. Exposure to ultrafine particles from ambient air and oxidative stress-induced DNA damage. Environ Health Perspect. 2007 Aug;115(8):1177-82. doi: 10.1289/ehp.9984.
- Danielsen PH, Brauner EV, Barregard L, Sallsten G, Wallin M, Olinski R, Rozalski R, Moller P, Loft S. Oxidatively damaged DNA and its repair after experimental exposure to wood smoke in healthy humans. Mutat Res. 2008 Jul 3;642(1-2):37-42. doi: 10.1016/j.mrfmmm.2008.04.001. Epub 2008 Apr 14.
- Hemmingsen JG, Jantzen K, Moller P, Loft S. No oxidative stress or DNA damage in peripheral blood mononuclear cells after exposure to particles from urban street air in overweight elderly. Mutagenesis. 2015 Sep;30(5):635-42. doi: 10.1093/mutage/gev027. Epub 2015 Apr 22.
- Moller P, Danielsen PH, Karottki DG, Jantzen K, Roursgaard M, Klingberg H, Jensen DM, Christophersen DV, Hemmingsen JG, Cao Y, Loft S. Oxidative stress and inflammation generated DNA damage by exposure to air pollution particles. Mutat Res Rev Mutat Res. 2014 Oct-Dec;762:133-66. doi: 10.1016/j.mrrev.2014.09.001. Epub 2014 Sep 16.
- Moller P, Hemmingsen JG, Jensen DM, Danielsen PH, Karottki DG, Jantzen K, Roursgaard M, Cao Y, Kermanizadeh A, Klingberg H, Christophersen DV, Hersoug LG, Loft S. Applications of the comet assay in particle toxicology: air pollution and engineered nanomaterials exposure. Mutagenesis. 2015 Jan;30(1):67-83. doi: 10.1093/mutage/geu035.
- Moller P, Loft S. Oxidative damage to DNA and lipids as biomarkers of exposure to air pollution. Environ Health Perspect. 2010 Aug;118(8):1126-36. doi: 10.1289/ehp.0901725. Epub 2010 Apr 27.
- Aragon M, Erdely A, Bishop L, Salmen R, Weaver J, Liu J, Hall P, Eye T, Kodali V, Zeidler-Erdely P, Stafflinger JE, Ottens AK, Campen MJ. MMP-9-Dependent Serum-Borne Bioactivity Caused by Multiwalled Carbon Nanotube Exposure Induces Vascular Dysfunction via the CD36 Scavenger Receptor. Toxicol Sci. 2016 Apr;150(2):488-98. doi: 10.1093/toxsci/kfw015. Epub 2016 Jan 21.
- Aragon MJ, Chrobak I, Brower J, Roldan L, Fredenburgh LE, McDonald JD, Campen MJ. Inflammatory and Vasoactive Effects of Serum Following Inhalation of Varied Complex Mixtures. Cardiovasc Toxicol. 2016 Apr;16(2):163-71. doi: 10.1007/s12012-015-9325-z.
- Andersen MHG, Frederiksen M, Saber AT, Wils RS, Fonseca AS, Koponen IK, Johannesson S, Roursgaard M, Loft S, Moller P, Vogel U. Health effects of exposure to diesel exhaust in diesel-powered trains. Part Fibre Toxicol. 2019 Jun 11;16(1):21. doi: 10.1186/s12989-019-0306-4.
Study record dates
Study Major Dates
Study Start (ACTUAL)
Primary Completion (ACTUAL)
Study Completion (ACTUAL)
Study Registration Dates
First Submitted
First Submitted That Met QC Criteria
First Posted (ACTUAL)
Study Record Updates
Last Update Posted (ACTUAL)
Last Update Submitted That Met QC Criteria
Last Verified
More Information
Terms related to this study
Keywords
Other Study ID Numbers
- H-16033227 (OTHER: Danish Committee on Health Research Ethics for the Capital Region)
- No grant number (Other Grant/Funding Number: The Swedish Society of Spinal Surgeons)
- 2015-57-0121 case SUND-2016-80 (OTHER: Danish Data Protection Agency)
Plan for Individual participant data (IPD)
Plan to Share Individual Participant Data (IPD)?
Drug and device information, study documents
Studies a U.S. FDA-regulated drug product
Studies a U.S. FDA-regulated device product
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