Air Pollution Measurement Methods and Exposure Assessment Study Notes
Air Pollution Measurement Methods and Exposure Assessment
Introduction
Overview of the lecture on air pollution measurement methods and exposure assessment.
Objectives of the lecture:
Describe the main measurement methods for air pollution.
Understand the strengths and limitations of these methods.
Differentiate exposure from mere concentration measurements.
Practice calculations related to air pollution exposure and concentration.
Module Outline
The course module on Air Quality and Noise, currently in Lecture 7.
Upcoming lecture by Dr. Shannon Lim on dispersion modelling and emissions.
Air Pollution Measurement Methods
Presentation of real-time air quality indices and wind patterns from the IQ Air Earth site using satellite observations and fixed air quality monitoring stations.
Importance of colour scales used to express air quality to the public.
Example: Air quality levels in New Zealand are marked as safe (green).
Impact of COVID-19 on Air Quality
Comparative analysis of air quality data over three years (2019-2021) that show:
A clear drop in pollution levels in 2020 attributed to COVID-19 lockdown and reduced vehicle emissions.
Rebound of pollution levels in 2021 once restrictions were lifted.
Importance for Civil Engineers
Understanding air quality is crucial for civil engineers involved in:
Urban planning.
Transport systems.
Infrastructure projects.
Example of Christchurch: Implementation of low-emission signs led to improved air quality due to effective traffic planning.
Evidence: A clear drop in nitrogen dioxide (NO₂) concentrations post traffic changes on Riccarton Road.
Classification of Measurement Methods
Types of Measurement Methods
Passive vs. Active Methods:
Passive methods require no power (e.g., rainwater collection) and allow pollutants to diffuse naturally.
Active methods involve powered devices (e.g., pumps) to draw air for analysis.
Direct vs. Indirect Methods:
Direct: Measure the actual pollutant concentration (e.g., weighing collected samples).
Indirect: Estimate concentration based on signals from other measurements (e.g., light scattering to infer particulate matter levels).
Reference vs. Sensor-Based Methods
Reference Methods:
Approved by the U.S. Environmental Protection Agency (EPA).
Highly accurate but expensive to install, operate, and maintain. Limited to specific locations.
Sensor-Based Methods:
Less expensive and capable of higher spatial resolution with extensive deployment across cities.
Can be fixed or portable. Suitable for personal exposure assessments.
Fixed Air Quality Monitoring Stations
Functionality of traditional fixed monitoring stations:
Continuous analysis for pollutants (sulfur dioxide, nitrogen oxides, PM) using EPA-approved methods.
High accuracy regulatory-quality data, but limited in number and location.
Example: Auckland has 10 fixed stations measuring various pollutants, crucial for tracking spatial and temporal trends.
Importance of these stations in policy interventions aimed at emission reduction.
Air Quality Guidelines and Standards
Regulatory framework under the Resource Management Act (New Zealand).
Establishes monitoring requirements for areas exceeding national environmental standards.
World Health Organization (WHO) Guidelines:
Revised in 2021, reducing safe pollutant levels based on health research.
Non-legally binding yet serves as benchmarks for air quality management.
Compliance monitoring is facilitated through fixed air quality monitoring stations comparing pollutant concentrations against these standards.
New Measurement Techniques
Passive Sampling Techniques
Passive samplers, like diffusion tubes:
Used to gauge gases (e.g., nitrogen dioxide, volatile organic compounds).
Collect samples through diffusion over a specified exposure time (e.g., two weeks).
Low-Cost Air Pollution Monitoring Technologies
Use of low-cost sensors gaining popularity for air quality monitoring:
Track particulate matter and gases.
Require calibration and regular maintenance for accuracy.
Highlights the community engagement aspect of using low-cost sensors and real-time monitoring systems.
Mobile Air Quality Monitoring
Rise of portable air quality monitors (e.g., blood oxygen monitors, wearable sensors):
Used for citizen science and urban pollution mapping.
Cost-effective, providing real-time data but requires careful calibration.
Filter-Based Sampling
Traditional method using filters for particulate matter:
Measure concentration by comparing filter weight before and after exposure.
Can analyze chemical composition through advanced techniques (e.g., gas chromatography).
Exposure Assessment
Distinction between Concentration and Exposure
Concentration: Level of a pollutant in the air at a given location.
Exposure: Amount of pollutant inhaled by a person, influenced by:
Location and duration spent there.
Activities performed (e.g., indoor air purifier vs. outdoor exposure).
Factors Affecting Exposure
Sources of air pollution:
Indoor sources (cooking, cleaning) vs. outdoor sources (traffic emissions).
Building design, ventilation, and urban planning can mediate exposure levels.
Human factors (age, activity level) impact actual exposure dosage and health responses.
Study Examples on Exposure Assessment
Illustrative diagrams showing how urban layout affects pollution exposure for pedestrians and cyclists.
Differentiation of carbon monoxide uptake across age and weight shows how individual characteristics affect health impacts.
Conclusions
Final thoughts on the importance of understanding both measurement methods and exposure assessment in urban planning.
Encouragement to engage with ongoing air quality studies and monitoring systems for effective policy development.