Can be solid or liquid particles, usually defined in terms of PM10 and PM2.5 where the subscript refers to the diameter of the particle in microns
Particulate Matter
Some particles, such as dust, dirt, soot, or smoke, are large or dark enough to be seen with the naked eye
Reduces visibility in the atmosphere
Causes health problems related to the respiratory system and circulatory system
Relative sizes of particles in air
PM10
PM2.5
Total Suspended Particulate Matter (TSP)
High-volume samplers measured PM by TSP, usually less than 25-50 μg/m3, concentrations measured usually around 260 μg/m3
Based on research in the 1960s and 1970s, the human respiratory system was found to be affected by PM that was finer than what high-volume samplers measured
PM10 standard
A new standard based on PM10 was established using a 24-hour concentration of 150 μg/m3
Respiratory effects: Irritation of the respiratory tract, asthma exacerbation, bronchitis, emphysema, and other respiratory diseases
Cardiovascular effects: Increased risk of heart attacks, strokes, and cardiovascular mortality
Adverse pregnancy outcomes: Increased risk of low birth weight, preterm birth, and infant mortality
Other health effects: Impaired lung function, increased susceptibility to infections, and exacerbation of existing health conditions
Environmental Impacts of PM
Air quality degradation: Reduction in visibility and formation of haze
Ecosystem damage: Deposition of particles on soil and water bodies, affecting plant and aquatic life
Climate change: Particles can act as cloud condensation nuclei, influencing cloud formation and precipitation patterns
WHO benchmarks for PM
PM2.5: 10 µg/m³ annual mean, 25 µg/m³ 24-hour mean
PM10: 20 µg/m³ annual mean, 50 µg/m³ 24-hour mean
Primary standards for PM regulation
Set with the intent to protect public health, particularly the health of sensitive populations such as children, the elderly, and those with asthma
Secondary standards for PM regulation
Meant to protect public welfare and the environment, limit occurrences of decreased visibility and avoid damage to animals, crops, vegetation, and buildings
Air Quality Index (AQI)
Numerical scale to communicate the health risks associated with PM pollution
AQI Levels of Health Concern
Good (0-50)
Moderate (51-100)
Unhealthy for Sensitive Groups (101-150)
Unhealthy (151-200)
Very Unhealthy (201-300)
Hazardous (301-500)
Measurement and Monitoring of Particulate Matter
Monitoring stations equipped with instruments such as particulate matter samplers and optical sensors
Measurement of PM concentrations in terms of mass concentration (µg/m³) or particle count (particles/cm³)
Computation of Air Quality Index (AQI) to communicate the health risks associated with PM pollution
Methods of PM Measurement
Gravimetric method: collecting PM on filters and weighing them to determine mass concentration
Optical methods: Using light scattering or absorption to estimate particle concentration
Direct-reading instruments: Providing real-time measurements of PM concentrations
Instruments used for PM monitoring
Beta Attenuation Mass (BAM) Monitor
Annual PM2.5 Monitoring by Region (2023)
Annual PM10 Monitoring by Region (2023)
Region 10 PM10 Monitoring (Feb. 2023)
Metro Manila AQI based on PM10 & PM2.5 (3/19/24 @8pm)
Philippines' Air Quality Index (AQI) Rose 3x Higher Than the Safe Level (4/30/23)
Regulatory Standards and Guidelines
DENR Standards (RA 8749)
World Health Organization (WHO) Air Quality Guidelines
United States Environmental Protection Agency (EPA) National Ambient Air Quality Standards
Mitigation Strategies
Implementation of emission control measures (e.g., vehicle emission standards, industrial regulations)
Promotion of clean energy sources and technologies
Urban planning measures to reduce exposure to PM pollution (e.g., green spaces, pedestrian zones)
Public awareness and education campaigns on the health effects of PM pollution and ways to reduce exposure
Challenges and Future Directions
Ensuring the accuracy and reliability of monitoring data
Addressing emerging pollutants and sources of PM pollution
Integrating PM monitoring with other environmental monitoring efforts
Promoting research and innovation in PM measurement technologies
Estimating and Monitoring Non-CO2 Greenhouse Gas Emissions from Field Burning of Crop Residues
Jose Hermis P. Patricio
Professor, CMU-CFES
Outline
Overview of agricultural residue burning
Importance of addressing the issue
Environmental and health impacts
Estimating greenhouse gas emissions from burning of agricultural wastes
Monitoring techniques
Management strategies
Land Area for Agriculture
Leading Cropsin PH
Given this, the country's agriculture sector is expectedly generating every year significant amount of wastes called crop residues (rice, corn and sugarcane)
Sugarcane residues constitute about 11% of the world's agricultural waste (Crutzen and Andreae, 1990)
Wetland rice cultivated in the Phils. under a moderate level of management produced between 0.6 and 0.9 tonnes of straw per tonne of grain (Ponnamperuma, 1984)
Corn residues in the Philippines is produced at a rate of 4,731.92 kg ha-1 (DAP, nd)
Burning of Agri Residues
Common agricultural practice in the Philippines, particularly after harvest seasons
Primarily conducted to clear fields quickly for the next planting cycle
Main crops associated with residue burning include rice, sugarcane, corn, and other crops
Typically occurs in rural areas where agriculture is a major livelihood
Regulatory efforts exist to control burning, but enforcement can be challenging due to socioeconomic factors and limited resources
Burning of Agri Residues
Causes significant air pollution, emitting pollutants such as particulate matter, carbon monoxide, and volatile organic compounds
Leads to health issues, including respiratory problems, particularly among vulnerable populations such as children and the elderly
Contributes to environmental degradation, soil erosion, loss of biodiversity, and greenhouse gas emissions
However, the practice of field burning crop residues leads to the production not only of CO2 but also non-CO2 GHG and their precursors such as carbon monoxide (CO), methane (CH4), nitrous oxide (N2O) and nitrogen oxide (NOx)
Estimating GHG Emissions from Burning of Agricultural Residues
1. Total Carbon Released from Burning Agricultural Residues
2. Calculate GHG emissions
Total Carbon Released from Burning Agricultural Residues
Data required: Amount of crops produced with residues that are commonly burned, Ratio of residue to crop product, Fraction of residue burned, Dry matter content of residue, Fraction oxidized in burning, and Carbon content of the residue