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Douglas Booker | NAQTS
Routes To Clean Air | 30th October 2018
Vehicle Interior Air Quality
Who We Are
National Air Quality Testing Services (NAQTS) is a social business, founded in 2015, that is
passionate about improving the quality of life. We seek to improve awareness of air
quality through widespread public and commercial monitoring using our holistic, high-
quality, air pollution monitoring technology: the NAQTS V2000.
Our technology incorporates the latest developments in low-cost sensor technologies,
alongside a regulatory grade Condensation Particle Counter, Thermal Desorption tubes,
and other environmental measurements. The NAQTS V2000 is a portable air quality
monitoring station designed to be easy-to-use for high-volume, lower-cost air quality
measurements.
Based in UK (Lancaster University Environment Centre and Cardiff), Ann Arbor, Michigan,
USA, and Guangzhou, China.
Lancaster University
Co-located with Lancaster Environment Centre (LEC) one of the largest multi-
disciplinary environment centres in the world
It combines an academic university department with a number of businesses
PhD Projects:
• Energy Efficiency & IAQ
• Particulate Matter Mitigation
• IAQ & Environmental Justice
International Projects:
• Intra-urban air pollution exposure
prediction: a smart platform and
applications using a land-use regression
model
NAQTS Air Quality Bench
PN - CPC with 20:1 pre-dilution (IPA, d50 15nm)
CO, NO2, NO – Electrochemical
CO, NO2, VOCs – Metal Oxide
VOCs – Metal Oxide
CO2 – NDIR
T, P, RH – BME280
Vibration – 3D accelerometer and 3D Gyro
Suitable for OEM applications
NAQTS V2000
• Ultrafine Particles
• Carbon Monoxide
• Carbon Dioxide
• Nitrogen Dioxide
• Volatile Organic Compounds
• Temperature
• Pressure
• Relative Humidity
• Noise
“Holistic understanding of air quality”
Ultrafine Particles
• Huge spatial/temporal variability in UFP
concentrations
• Limited number of controlled human
exposure and toxicological studies that
examined UFPs
• No ambient UFP legislation
Condensation Particle Counter (CPC)
Regulatory grade PN: ISO
27891
CPC with 20:1 pre-dilution
(IPA, d50 15nm)
Electrochemical
Using state-of-the-art
transimpedance amplifier
(LMP9100) for flexibility for
set-up and calibration
Electrochemical sensors used
in conjunction with metal
oxide sensors to address
cross-interferences
(orthogonal calibration
methodology)
Metal Oxide
NDIR
Auto Baseline algorithm used for long-term
sampling (400ppm CO2)
Can be fitted with sampling manifold adapter
Gas Metrology
Easy, low cost
calibration using
typical
automotive gas
bottles, e.g. 16%
CO2 Quad Blend
(CO, HC, NO),
and NO2 through
the integrated
diluter
Applications of the NAQTS V2000
CITIZEN SCIENCE - INDOOR:OUTDOOR AIR QUALITY
Air quality toolkit for citizen science measurements. Capturing
real-time pollution levels during school drop off/pick up times, as
well as levels of student exposure in the classroom
INDOOR AIR QUALITY & ENERGY EFFICIENCY
Developing models for assisting building design and modification
whilst ensuring energy efficiency and good indoor air quality.
AIR QUALITY MAPPING
Routine mobile monitoring for measuring time-integrated
concentrations at high spatial resolution
OCCUPATIONAL HEALTH AND SAFETY
Evaluation of exposure to nanomaterials
VEHICLE INTERIOR AIR QUALITY
Air Quality, Noise, and Vibration
Data on in-cabin comfort from 100s of vehicles per year
Applications of the NAQTS V2000
CITIZEN SCIENCE - INDOOR:OUTDOOR AIR QUALITY
Air quality toolkit for citizen science measurements. Capturing
real-time pollution levels during school drop off/pick up times, as
well as levels of student exposure in the classroom
INDOOR AIR QUALITY & ENERGY EFFICIENCY
Developing models for assisting building design and modification
whilst ensuring energy efficiency and good indoor air quality.
AIR QUALITY MAPPING
Routine mobile monitoring for measuring time-integrated
concentrations at high spatial resolution
OCCUPATIONAL HEALTH AND SAFETY
Evaluation of exposure to nanomaterials
VEHICLE INTERIOR AIR QUALITY
Air Quality, Noise, and Vibration
Data on in-cabin comfort from 100s of vehicles per year
Vehicle Interior Air Quality
101 minutes per day in vehicles (Dong et al. 2004)
Immediate proximity to significant pollutant
sources (other vehicles), plus in urban areas, high
outdoor concentrations
Simultaneous indoor and outdoor measurements
Vehicle Interior Air Quality
Key questions:
1. How much ambient air pollution is
coming into the vehicle?
2. What are the in-vehicle sources of
air pollution? (Müller et al. 2011)
How much ambient air pollution is coming into the vehicle?
Ultrafine Particles – Ingress Ratio
The data from these
four vehicles shows
the heterogeneity
of Ingress Ratios
24-99% with
recirculation mode
off
5-17% with
recirculation mode
on
Ultrafine Particles – Ingress Ratio
CO2 – Stuffiness Factor
An inherent tradeoff
between protecting
passengers from
ambient ingress, and
adequate ventilation
CO2 – Stuffiness Factor
Cabin Filtration Efficiency
Indoor 4620
Outdoor 6989
Filtration
Efficiency
34%
Cabin Filtration Efficiency
Indoor 650
Outdoor 12,053
Filtration
Efficiency
95%
Air Changes Per Hour (ACH)
”Fresh Air” 40 ACH
Recirculation 0.5 ACH
CO2 >2000ppm impairs
cognitive function
“Fresh Air” Recirculation
What are the in-vehicle sources of air pollution?
Volatile Organic Compounds (VOCs), responsible for
the “new car smell”, can be emitted from an array of
interior parts and components: the dashboard,
interior panels, flooring materials, and many others.
Within the confined space of a vehicle, VOCs emitted
from these components may reach levels that are
potentially harmful to human occupants, causing
symptoms such as nausea, allergies, fatigue, stinging
eyes, and headaches.
Beyond affecting drivers’ and passengers’ well-being
and comfort, such symptoms may have also
consequences on safe driving
Regulatory Context
Who is setting standards?
• Automobile Associations (JAMA, ACEA, TÜV Rhineland
Group etc.)
• Manufacturers (GM, BMW, VW, etc.)
• ISO (ISO 12219-1 – ISO 12219-7)
Monitoring techniques?
• Environmental Chambers (BMW GS97014-3, ISO 12219-3 -
ISO 12219-5)
• Bag method (TSM0508G, ISO 12219-2)
• TD GC-MS (PB VWL 709; VDA 278)
What are they monitoring?
• Interior materials (GMW15634)
• Full vehicle (GMW15654, ISO 12219-1)
Move towards harmonisation…
“Shall include provisions and
harmonized test procedures for the
measurement of interior VOCs taking
into account existing standards”
Experimental Set-Up (Static Baseline)
Hydrophobic TnxTA/Cg1
Integrated into NAQTS V2000
Top 20 peaks, Semi-quantitative (spiked with d8-
Toluene, d6-benzene and d4-dichlorobenzene)
Tested inside Emissions Analytics’ Stokenchurch Emissions Lab
Agilent GC-MS, samples run on full scan mode Thermal Desorption
Experimental Set-Up (Real World Driving)
Thermal DesorptionAgilent GC-MS, samples run on full scan mode
Tested dynamically on RDE-type route (Geofencing –
Urban, Rural, Highway etc.) at same time as indoor-
outdoor research to see VOCs ingress
Hydrophobic TnxTA/Cg1
Top 20 peaks, Semi-quantitative (spiked with d8-
Toluene, d6-benzene and d4-dichlorobenzene)
Integrated into NAQTS V2000
VW Golf (2011)
Renault Clio (2016)
Mercedes C220 (2005)
Ford Focus (2009)
Ford Focus (2015)
Fiat Punto (2008)
German Saloon (2017)
Mini Cooper (2006)
Comparisons - TVOCs
Comparisons - TVOCs
Health Effects
• <200 µg/m³ - No
irritation or discomfort
• 200-3000 µg/m³ -
Irritation and discomfort
possible
• 3000-25000 µg/m³-
Discomfort expected
and headache possible
• >25000 µg/m³ - toxic
Comparisons II - Speciation
Comparisons II - Speciation
3 µg/m³
Carcinogen (Group 1)
Comparisons II - Speciation
15 µg/m³
23 µg/m³
8.4 µg/m³
5.5 µg/m³
Comparisons II - Speciation
Carcinogen (Group 2A)
20 µg/m³
14 µg/m³
19 µg/m³
How do you communicate these results to
the general public?
Vehicle manufacturers beginning to differentiate
themselves based on VIAQ, we need more independent
research to inform the consumer.
Complicated subject matter + general public aversion
to analytical chemistry
“You can literally survive a military grade bio attack by
sitting in your car” - TESLA
Mobile Air Quality Monitoring
Routine mobile monitoring for measuring
time-integrated concentrations at high spatial
resolution
4-5 orders of magnitude improvements in
spatial resolution than current central site
monitoring stations
NAQTS V2000 Can be mounted on the vehicle, or
placed inside with a sample tube to outside
Air Quality Mapping
2 year project in Guangzhou (megacity)
Land-use regression model combining: mobile air
quality monitoring, fixed site stations,
meteorological, land-use, traffic volume, POI data
etc.
Will map UFP and other pollutants
Developing an app to predict air pollution
exposure
When combined with cellular GPS data, rich
“personal exposure analytics” become possible
Case study to demonstrate feasibility of a low-cost
air quality monitoring network
Potential for expansion: >150 cities in China with a
population of >1 million
Mapping the Air Quality in Lancaster
Lancaster is a small city of 138,000
people in the North-West of England
Over a period of 1 week, particle
number concentrations were recorded
every second over a 20-mile route
during evening rush hour
(5:30/7:00pm)
0 – 5 000 5 001 – 8 000 8 001 – 15 000 15 001 – 50 000 50 000+
0
1000
2000
3000
4000
5000
6000
7000
8000
9000
City centre Residential Rural Overall
ParticleNumber
Concentration(#/cm3)
Mapping the Air Quality in Lancaster
Mapping the Air Quality in Lancaster
Air Quality ”hotspots” change in space and time!
Mapping the Air Quality in Lancaster
Conclusions
This case study represents a small data set, however, Emissions Analytics
are using NAQTS’ air quality monitoring technology to gather data on
VIAQ for 100s of vehicles per year. Moreover, this will be extended to
include other pollutants such as NO2 and CO.
• An inherent tradeoff between protecting passengers from ambient
ingress, and adequate ventilation
• Huge influence of passenger habit on dose. By driver education, and
automation of HVAC controls, exposure to UFPs can be reduced
significantly
• Heterogeneity of VIAQ across the fleet, both in terms of ambient
ingress, and interior emissions
• We need more independent research to inform the consumer.
www.naqts.com@NAQTS
Thank you for listening.
Any questions?

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Vehicle Interior Air Quality Monitoring and Mapping

  • 1. Douglas Booker | NAQTS Routes To Clean Air | 30th October 2018 Vehicle Interior Air Quality
  • 2. Who We Are National Air Quality Testing Services (NAQTS) is a social business, founded in 2015, that is passionate about improving the quality of life. We seek to improve awareness of air quality through widespread public and commercial monitoring using our holistic, high- quality, air pollution monitoring technology: the NAQTS V2000. Our technology incorporates the latest developments in low-cost sensor technologies, alongside a regulatory grade Condensation Particle Counter, Thermal Desorption tubes, and other environmental measurements. The NAQTS V2000 is a portable air quality monitoring station designed to be easy-to-use for high-volume, lower-cost air quality measurements. Based in UK (Lancaster University Environment Centre and Cardiff), Ann Arbor, Michigan, USA, and Guangzhou, China.
  • 3. Lancaster University Co-located with Lancaster Environment Centre (LEC) one of the largest multi- disciplinary environment centres in the world It combines an academic university department with a number of businesses PhD Projects: • Energy Efficiency & IAQ • Particulate Matter Mitigation • IAQ & Environmental Justice International Projects: • Intra-urban air pollution exposure prediction: a smart platform and applications using a land-use regression model
  • 4. NAQTS Air Quality Bench PN - CPC with 20:1 pre-dilution (IPA, d50 15nm) CO, NO2, NO – Electrochemical CO, NO2, VOCs – Metal Oxide VOCs – Metal Oxide CO2 – NDIR T, P, RH – BME280 Vibration – 3D accelerometer and 3D Gyro Suitable for OEM applications
  • 5. NAQTS V2000 • Ultrafine Particles • Carbon Monoxide • Carbon Dioxide • Nitrogen Dioxide • Volatile Organic Compounds • Temperature • Pressure • Relative Humidity • Noise “Holistic understanding of air quality”
  • 6. Ultrafine Particles • Huge spatial/temporal variability in UFP concentrations • Limited number of controlled human exposure and toxicological studies that examined UFPs • No ambient UFP legislation
  • 7. Condensation Particle Counter (CPC) Regulatory grade PN: ISO 27891 CPC with 20:1 pre-dilution (IPA, d50 15nm)
  • 8. Electrochemical Using state-of-the-art transimpedance amplifier (LMP9100) for flexibility for set-up and calibration Electrochemical sensors used in conjunction with metal oxide sensors to address cross-interferences (orthogonal calibration methodology)
  • 10. NDIR Auto Baseline algorithm used for long-term sampling (400ppm CO2) Can be fitted with sampling manifold adapter
  • 11. Gas Metrology Easy, low cost calibration using typical automotive gas bottles, e.g. 16% CO2 Quad Blend (CO, HC, NO), and NO2 through the integrated diluter
  • 12. Applications of the NAQTS V2000 CITIZEN SCIENCE - INDOOR:OUTDOOR AIR QUALITY Air quality toolkit for citizen science measurements. Capturing real-time pollution levels during school drop off/pick up times, as well as levels of student exposure in the classroom INDOOR AIR QUALITY & ENERGY EFFICIENCY Developing models for assisting building design and modification whilst ensuring energy efficiency and good indoor air quality. AIR QUALITY MAPPING Routine mobile monitoring for measuring time-integrated concentrations at high spatial resolution OCCUPATIONAL HEALTH AND SAFETY Evaluation of exposure to nanomaterials VEHICLE INTERIOR AIR QUALITY Air Quality, Noise, and Vibration Data on in-cabin comfort from 100s of vehicles per year
  • 13. Applications of the NAQTS V2000 CITIZEN SCIENCE - INDOOR:OUTDOOR AIR QUALITY Air quality toolkit for citizen science measurements. Capturing real-time pollution levels during school drop off/pick up times, as well as levels of student exposure in the classroom INDOOR AIR QUALITY & ENERGY EFFICIENCY Developing models for assisting building design and modification whilst ensuring energy efficiency and good indoor air quality. AIR QUALITY MAPPING Routine mobile monitoring for measuring time-integrated concentrations at high spatial resolution OCCUPATIONAL HEALTH AND SAFETY Evaluation of exposure to nanomaterials VEHICLE INTERIOR AIR QUALITY Air Quality, Noise, and Vibration Data on in-cabin comfort from 100s of vehicles per year
  • 14. Vehicle Interior Air Quality 101 minutes per day in vehicles (Dong et al. 2004) Immediate proximity to significant pollutant sources (other vehicles), plus in urban areas, high outdoor concentrations Simultaneous indoor and outdoor measurements
  • 15. Vehicle Interior Air Quality Key questions: 1. How much ambient air pollution is coming into the vehicle? 2. What are the in-vehicle sources of air pollution? (Müller et al. 2011)
  • 16. How much ambient air pollution is coming into the vehicle?
  • 17. Ultrafine Particles – Ingress Ratio
  • 18. The data from these four vehicles shows the heterogeneity of Ingress Ratios 24-99% with recirculation mode off 5-17% with recirculation mode on Ultrafine Particles – Ingress Ratio
  • 20. An inherent tradeoff between protecting passengers from ambient ingress, and adequate ventilation CO2 – Stuffiness Factor
  • 21. Cabin Filtration Efficiency Indoor 4620 Outdoor 6989 Filtration Efficiency 34%
  • 22. Cabin Filtration Efficiency Indoor 650 Outdoor 12,053 Filtration Efficiency 95%
  • 23. Air Changes Per Hour (ACH) ”Fresh Air” 40 ACH Recirculation 0.5 ACH CO2 >2000ppm impairs cognitive function “Fresh Air” Recirculation
  • 24.
  • 25. What are the in-vehicle sources of air pollution? Volatile Organic Compounds (VOCs), responsible for the “new car smell”, can be emitted from an array of interior parts and components: the dashboard, interior panels, flooring materials, and many others. Within the confined space of a vehicle, VOCs emitted from these components may reach levels that are potentially harmful to human occupants, causing symptoms such as nausea, allergies, fatigue, stinging eyes, and headaches. Beyond affecting drivers’ and passengers’ well-being and comfort, such symptoms may have also consequences on safe driving
  • 26. Regulatory Context Who is setting standards? • Automobile Associations (JAMA, ACEA, TÜV Rhineland Group etc.) • Manufacturers (GM, BMW, VW, etc.) • ISO (ISO 12219-1 – ISO 12219-7) Monitoring techniques? • Environmental Chambers (BMW GS97014-3, ISO 12219-3 - ISO 12219-5) • Bag method (TSM0508G, ISO 12219-2) • TD GC-MS (PB VWL 709; VDA 278) What are they monitoring? • Interior materials (GMW15634) • Full vehicle (GMW15654, ISO 12219-1) Move towards harmonisation… “Shall include provisions and harmonized test procedures for the measurement of interior VOCs taking into account existing standards”
  • 27. Experimental Set-Up (Static Baseline) Hydrophobic TnxTA/Cg1 Integrated into NAQTS V2000 Top 20 peaks, Semi-quantitative (spiked with d8- Toluene, d6-benzene and d4-dichlorobenzene) Tested inside Emissions Analytics’ Stokenchurch Emissions Lab Agilent GC-MS, samples run on full scan mode Thermal Desorption
  • 28. Experimental Set-Up (Real World Driving) Thermal DesorptionAgilent GC-MS, samples run on full scan mode Tested dynamically on RDE-type route (Geofencing – Urban, Rural, Highway etc.) at same time as indoor- outdoor research to see VOCs ingress Hydrophobic TnxTA/Cg1 Top 20 peaks, Semi-quantitative (spiked with d8- Toluene, d6-benzene and d4-dichlorobenzene) Integrated into NAQTS V2000
  • 38. Comparisons - TVOCs Health Effects • <200 µg/m³ - No irritation or discomfort • 200-3000 µg/m³ - Irritation and discomfort possible • 3000-25000 µg/m³- Discomfort expected and headache possible • >25000 µg/m³ - toxic
  • 39. Comparisons II - Speciation
  • 40. Comparisons II - Speciation 3 µg/m³ Carcinogen (Group 1)
  • 41. Comparisons II - Speciation 15 µg/m³ 23 µg/m³ 8.4 µg/m³ 5.5 µg/m³
  • 42. Comparisons II - Speciation Carcinogen (Group 2A) 20 µg/m³ 14 µg/m³ 19 µg/m³
  • 43. How do you communicate these results to the general public? Vehicle manufacturers beginning to differentiate themselves based on VIAQ, we need more independent research to inform the consumer. Complicated subject matter + general public aversion to analytical chemistry “You can literally survive a military grade bio attack by sitting in your car” - TESLA
  • 44. Mobile Air Quality Monitoring Routine mobile monitoring for measuring time-integrated concentrations at high spatial resolution 4-5 orders of magnitude improvements in spatial resolution than current central site monitoring stations NAQTS V2000 Can be mounted on the vehicle, or placed inside with a sample tube to outside
  • 45. Air Quality Mapping 2 year project in Guangzhou (megacity) Land-use regression model combining: mobile air quality monitoring, fixed site stations, meteorological, land-use, traffic volume, POI data etc. Will map UFP and other pollutants Developing an app to predict air pollution exposure When combined with cellular GPS data, rich “personal exposure analytics” become possible Case study to demonstrate feasibility of a low-cost air quality monitoring network Potential for expansion: >150 cities in China with a population of >1 million
  • 46. Mapping the Air Quality in Lancaster Lancaster is a small city of 138,000 people in the North-West of England Over a period of 1 week, particle number concentrations were recorded every second over a 20-mile route during evening rush hour (5:30/7:00pm) 0 – 5 000 5 001 – 8 000 8 001 – 15 000 15 001 – 50 000 50 000+ 0 1000 2000 3000 4000 5000 6000 7000 8000 9000 City centre Residential Rural Overall ParticleNumber Concentration(#/cm3)
  • 47. Mapping the Air Quality in Lancaster
  • 48. Mapping the Air Quality in Lancaster
  • 49. Air Quality ”hotspots” change in space and time! Mapping the Air Quality in Lancaster
  • 50. Conclusions This case study represents a small data set, however, Emissions Analytics are using NAQTS’ air quality monitoring technology to gather data on VIAQ for 100s of vehicles per year. Moreover, this will be extended to include other pollutants such as NO2 and CO. • An inherent tradeoff between protecting passengers from ambient ingress, and adequate ventilation • Huge influence of passenger habit on dose. By driver education, and automation of HVAC controls, exposure to UFPs can be reduced significantly • Heterogeneity of VIAQ across the fleet, both in terms of ambient ingress, and interior emissions • We need more independent research to inform the consumer.
  • 51. www.naqts.com@NAQTS Thank you for listening. Any questions?