Particulate matter and coal dust
Airborne Particles
Airborne particles––also known as particulate matter (PM), particulates, or aerosols––refer to any mixture of solids and liquid droplets in the atmosphere. Particles can be directly emitted into the air or formed through chemical reactions of gaseous pollutants.
Particles are often distinguished by their size. The terms PM1, PM2.5, and PM10 are common ways particles are described, measured, and regulated, with the number indicating the diameter of the particles in micrometers. Particles can also be discussed in the terms of very-fine (PM1), fine (PM2.5), and coarse (PM10) particles, with PM10 generally referring to as dust. Particle size, composition, and shape affect how particles are regulated under the U.S. Clean Air Act and their health impacts.
Coal Dust
Coal dust is a type of particulate matter that contains coal. Coal dust particles tend to be larger in size, including PM2.5 and PM10, as well as even bigger PM that is visible with the unaided eye.[1] Coal dust is lost from the atmosphere through settling and deposition, leaving black dust films on outdoor and indoor surfaces. Coal dust contains toxic heavy metals that have serious health impacts at ambient concentrations and exposures below the U.S. Environmental Protection Agency National Ambient Air Quality Standards (NAAQS).
Coal Dust Emissions
Coal dust is produced through physical processes that wear on the brittle coal rocks during mining, transport, and storage to generate coal particles that are then uplifted to the atmosphere and carried by winds. There are various physical disturbances that can unsettle coal particles and uplift them into the air. The distance traveled by the coal dust emissions depends on the size of particles, with smaller particles generally reaching farther distances, and the conditions in the atmosphere. Physical disturbances influencing coal dust emissions and downwind impacts include weather and wind patterns and the transporting and handling of coal.
Wind and weather disturbances
In Southeast Newport News, coal is stored in large open piles, and these stockpiles are susceptible to wind erosion with coal particles easily becoming airborne. The wind speeds over the coal piles influence the coal dust emissions and transport downwind, with higher wind speeds associated with higher airborne particle concentrations. As wind speeds increase, atmospheric particulate matter in the air increases, and there is an overall increase in dust fluxes to the atmosphere of particulates such as coal.[2] The direction of airborne dust travel is determined by the wind direction. Higher particulate matter and black carbon concentrations have been observed in the neighboring community when winds blow from of the Curtis Bay coal export terminal.[3]
Rain events are associated with lower airborne coal dust concentrations, as the water droplets reduce both dust emissions and force airborne particles out of the air and back to the surface through a process called wet deposition. This is similar to the use of water sprayers for wet dust suppression.
- Relative humidity influences coal dust particle size, with higher humidity associated with larger particle matter as the dust particles clump together.
- Lower humidity may increase the concentration of fine dust particles which penetrate more deeply into lungs and cells, posing a serious public health concern.
- The Virginia Air Pollution Control Board conducted a study published in January 1987 which determined the mathematical formula (Equation 1.1) for the “Effective wind forces” (Kt) on the coal piles at the terminal in Newport News, which is influenced by:
- SP = wind speed
- T = temperature
- RH = relative humidity
- P = air density
- μ = air viscosity
This model was used to predict the emissions of coal dust based on these various conditions, and how to optimize wet dust suppression with sprayers.
Coal transporting and handling disturbances
Transportation of coal: The transport of coal in uncovered open-top rail cars results in significant amounts of coal dust being emitted into the air by the jostling of the rail cars or due to wind and weather. Along the transportation route, coal dust can blow over residential and agriculture areas, polluting the air, crops, and waterways. The company BNSF has conducted studies that indicate 500 lbs to 1 ton of coal can escape from a single coal car during travel along a railway.
Coal handling: Loading and unloading piles of coal from rail cars into coal piles can unsettle dust particles which get released into the air.
- Equipment at the terminal which manages and moves coal piles, such as bulldozers and conveyor belts, can release coal dust into the air.
- The transfer of coal onto ships at the port can similarly unsettle dust particles.
- In June 1989, Virginia's Department of Air Pollution Control Board set limits on the emissions from each ship unloading operation, each conveyor belt, the bucket elevator, silo airslides, and the truck loadout system to 0.3 lbs/hr for both particulate matter and PM10 for each respective coal handling operation.
- In July 1994, this emission limit was increased to 1.6 lb/hr.
Evidence of Atmospheric Coal Particulate Deposition
In a study conducted at the Lambert’s Point Docks, sample soils were collected to examine the extent of particulate coal and the associated Arsenic deposition to local soils. The amount of particulate coal that occurs in the surface soil samples (4cm depth) of the study area averaged 7.1 weight% and an associated mean Arsenic value of 13.3 mg/kg. There was a decrease in the amount of particulate coal with increasing distance from Lambert’s Point Dock. There was also an increase in the amount of particulate coal eastward of Lambert’s Point Dock (the prevailing wind direction for the region is from the west). These results indicate that much of the Hampton Roads region of Southeastern Virginia has experienced atmospheric deposition of particulate coal, along with As concentration, originating from the Lambert’s Point Docks.
- Another study by William Joseph Bounds, Old Dominion University, sought to determine the distribution of coal dust added to the local soils by the coal shipping processors occurring at Lamberts Point Docks. These results indicated substantial levels of coal dust within the soils of the study area, with coal levels ranging from 3.2 weight% to 19.9 weight%. Additionally, arsenic levels ranged from undetectable levels to 17.4 mg/kg in these coal samples.
- July 2017, The Virginia Department of Health examined potential public health implications of particulate matter measuring 10 microns (PM10) and less generated by the Norfolk Southern’s Coal Pier at Lambert’s Point coal terminal. Monitors located at Hampton Roads Sanitary Department facility (north of coal piers) and east of the pier administration building collected an average of 14.46 and 17.58 µg/m3, respectively. The study detected a PM10 concentration below the NAAQS PM10 standard (150 µg/m3), claiming it is not expected to harm people’s health. It’s important to address that there is an apparent gap between residential local scientific knowledge and the results of this study.
- Tidewater Air Monitoring Evaluation (TAME) project is an ongoing Virginia Department of Environmental Quality 18-month investigation to study atmospheric toxic metals and particulates at Lambert’s Point and East End communities. They hope to study and reduce the potential health risks associated with dust coming from nearby coal storage and transportation facilities. If you live in Lambert's Point or the Southeast communities and would like to host a sensor, please contact John Brandt at john.brandt@deq.virginia.gov or (757) 407-2341.
- Have not been able to locate data and/or research on coal particulate air pollution in adjacent communities.
Documents
- Viney P. Aneja, Priya R. Pillai, Aaron Isherwood, Peter Morgan & SaurabhP. Aneja (2016): Particulate matter pollution in the coal-producing regions of the Appalachian Mountains: Integrated ground-based measurements and satellite analysis, Journal of the Air & Waste Management Association. October 12, 2019.
- Coal Dust Residues on Homes in Southeast Newport News, 2024–2025 Photographs
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Coal Dust Residues
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Coal Dust Residues
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Coal Dust Residues
References
- ↑ Li, et al., Experimental Research of Particle Size and Size Dispersity on the Explosibility Characteristics of Coal Dust, Powder Technology, 292, 290–297, 2016.
- ↑ Deng et al., Characteristics of atmospheric dustfall fluxes and particle size in an open pit coal mining area and surrounding areas, Scientific Reports, 15, 9597, doi:10.1038/s41598-025-94161-4, 2025.
- ↑ Deanes et al., Relation of wind direction and coal terminal activity patterns with air pollution burden in a community bordering a coal export terminal, Curtis Bay, Maryland, USA, Air Quality, Atmosphere & Health, 18, 2805–2821, 2025.