Key takeaways
- PM1, PM2.5 and PM10 describe particles by aerodynamic size, while TSP covers all suspended particles; each answers a different question about health, nuisance and site control.
- Real-time optical monitors are suited to site management and alerts, while reference or equivalent methods provide data for formal compliance comparisons.
- A network with upwind and downwind locations is needed to separate the site's contribution from background dust, which can be high in Saudi Arabia.
- Alert levels only work when each is tied to a specific mitigation action and a named person responsible for it.
- Applicable limits and reporting obligations depend on the project and its approvals, so confirm them with the competent authority.
Dust monitoring on a construction site is the continuous measurement of airborne particulate matter at and around the site, used to control emissions in real time and to demonstrate compliance with environmental commitments. A well-designed programme measures the right particle sizes, uses methods suited to its purpose, places monitors upwind and downwind, and links alert levels to specific mitigation actions. Without those elements, data is difficult to act on and difficult to defend.
This article explains particle size fractions, measurement methods, network design, alerts and reporting.
Particle size fractions explained
Particulate matter is classified by aerodynamic diameter, measured in micrometres (µm).
| Fraction | Definition | Typical construction sources | Why it matters |
|---|---|---|---|
| TSP | Total suspended particulate, all airborne particles | Earthworks, stockpiles, haul roads, demolition | Visible dust, deposition on property and vegetation, nuisance |
| PM10 | Particles of 10 µm or less | Excavation, crushing, vehicle movement on unpaved surfaces | Inhalable into the upper airways, common regulatory parameter |
| PM2.5 | Particles of 2.5 µm or less | Diesel engines, generators, cutting, fine fraction of earthworks | Penetrates deep into the lungs, closely linked to health effects |
| PM1 | Particles of 1 µm or less | Combustion exhaust, welding fumes | Indicator of combustion sources, very fine fraction |
The fractions are nested: PM1 is part of PM2.5, which is part of PM10, which is part of TSP. Construction activities generate mostly coarse particles, so PM10 and TSP usually respond most clearly to site activity, while PM2.5 and PM1 help identify combustion sources.
Choosing a measurement method
Real-time optical monitors
Optical monitors use light scattering to count and size particles, reporting concentrations at short intervals. Their advantages are immediate data, remote access, low maintenance and suitability for alarms. Their limitation is that readings depend on particle shape, density and humidity, so they are indicative unless corrected against a reference.
Reference and equivalent methods
Reference methods, typically gravimetric sampling onto filters that are weighed in a laboratory, and recognised equivalent methods such as beta attenuation monitors, provide data suited to formal comparison with standards. They are more expensive, need more maintenance, and gravimetric results are not available in real time.
A combined approach
A common and practical approach is to run optical monitors across the network for real-time control, and to co-locate at least one with a reference or equivalent method. This allows a site-specific correction to be applied to the optical data and strengthens the defensibility of the full data set. Confirm which methods are acceptable for compliance purposes on your project with the competent authority.
Designing the monitoring network
Upwind and downwind locations
Saudi Arabia experiences high natural background dust and regional dust events. Monitoring only downwind of the site cannot separate the site’s contribution from background. A defensible network includes:
- At least one upwind location representing incoming background
- Downwind locations at the site boundary facing sensitive receptors
- Additional locations near high-risk activities such as crushing, stockpiles and haul road exits
- A meteorological station recording wind speed and direction, temperature and humidity
Because wind direction changes, locations should be chosen from local wind data, and the upwind and downwind roles of each monitor assigned in the data analysis rather than fixed in advance.
Sensitive receptors
Identify receptors early: homes, schools, hospitals, offices, agricultural land and protected areas. Place boundary monitors on the line between major dust sources and the nearest receptors.
Practical siting
- Keep inlets clear of walls, trees and other obstructions
- Avoid locations directly beside a single dominant source unless that source is the target
- Provide secure power and communications, and protect equipment from damage and theft
- Document each location with coordinates, photographs and reasons for selection
Alert levels tied to mitigation
Alerts are only useful if they trigger action. A tiered approach links each level to a specific response:
| Alert tier | Purpose | Example response |
|---|---|---|
| Advisory | Early warning of rising concentrations | Supervisor checks activities near the monitor, increases water spraying |
| Action | Concentrations approaching the project’s control level | Reduce or relocate high-dust activities, intensify suppression, review wind conditions |
| Stop | Concentrations at or above the control level and attributable to the site | Suspend the contributing activity until levels fall and causes are addressed |
Set alert values according to the project’s environmental management plan, permit conditions and applicable air quality requirements, using averaging periods consistent with those requirements. Confirm current standards with the competent authority rather than relying on general figures. Each alert should notify a named person, and every response should be logged.
Reporting
Regular reports turn data into evidence. A useful monitoring report includes:
- Summary of results for each location and parameter against the project’s control levels
- Wind roses and analysis of upwind and downwind differences
- Record of alerts, investigations and mitigation actions taken
- Notes on regional dust events and data gaps, with reasons
- Calibration, maintenance and data validation records
- Recommendations for adjusting mitigation or the network
Setup checklist
- Monitoring objectives and parameters confirmed (PM10, PM2.5, PM1, TSP)
- Applicable requirements confirmed with the competent authority
- Sensitive receptors and main dust sources mapped
- Upwind, downwind and activity-focused locations selected using wind data
- Optical monitors co-located with a reference or equivalent method where needed
- Meteorological station installed
- Tiered alert levels defined, each with a mitigation response and owner
- Data validation, calibration and reporting procedures documented
How Selorin can help
Selorin’s dust monitoring service covers network design, installation of continuous monitors, alert configuration and periodic reporting, and links to our air quality monitoring and environmental management plans work. Agreeing the monitoring objectives and network layout before mobilisation is usually the most effective place to start.
Frequently asked questions
Should we monitor PM10 or PM2.5 on a construction site?
Usually both, because they serve different purposes. Construction activities generate mainly coarse particles, so PM10 and TSP respond most clearly to earthworks and vehicle movements. PM2.5 is more closely linked to health effects and to combustion sources such as diesel engines. Your environmental management plan or permit conditions may specify which parameters to monitor.
Can optical dust monitors be used for compliance reporting?
Optical monitors are well suited to real-time control and trend analysis, but their readings depend on particle properties and humidity. Whether they are acceptable for compliance purposes depends on the requirements set for the project. Where formal comparison is needed, operators often co-locate an optical monitor with a reference or equivalent method to derive a site-specific correction.
How do we separate our site's dust from desert background dust?
Use paired upwind and downwind monitors with on-site wind speed and direction data. The difference between them, under stable wind conditions, gives an estimate of the site's contribution. Record regional dust events separately so that elevated readings caused by background conditions are not mistaken for site emissions.
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