Particulate

Particulates or atmospheric particulate matter (see below for other names) are microscopic particles of solid or liquid matter suspended in the air. The term aerosol refers to the particulate/air mixture, as opposed to the particulate matter alone, though it is sometimes defined as a subset of aerosol terminology. Sources of particulate matter can be natural or anthropogenic. They have impacts on climate and precipitation that adversely affect human health, in ways additional to direct inhalation.

PM_2.5 and PM₁₀ compared with a human hair in a graphic from the Environmental Protection Agency

Types, and size distribution in micrometres (μm), of atmospheric particulate matter

Types of atmospheric particles include suspended particulate matter; thoracic and respirable particles; inhalable coarse particles, designated PM₁₀, which are coarse particles with a diameter of 10 micrometers (μm) or less; fine particles, designated PM_2.5, with a diameter of 2.5 μm or less;ultrafine particles, with a diameter of 100 nm or less; and soot.

Airborne particulate matter is a Group 1 carcinogen. Particulates are the most harmful form (other than ultra-fines) of air pollution as they can penetrate deep into the lungs and brain from blood streams, causing health problems such as heart disease, lung disease, cancer and preterm birth. There is no safe level of particulates. Worldwide, exposure to PM_2.5 contributed to 4.1 million deaths from heart disease, stroke, lung cancer, chronic lung disease, and respiratory infections in 2016. Overall, ambient particulate matter is one of the leading risk factor for premature death globally.

Sources

Particulate emission when using modern electrical power tool during home broadband installation, Tai Po, Hong Kong

Excavator (a type of heavy equipment commonly used at construction sites and roadworks) demolishing the remnants of the pre-war Postal Train 0880Station (Dworzec Pocztowy) at Jerozolimskie Avenue, Poland

Human activities generate significant amounts of particulates. For example:

• Burning of fossil fuels (e.g., aircraft),joss paper, waste,firecrackers and biomass including wood and crop residue.
• Construction (including activities of building rehabilitation/ refurbishment or demolition).
• Renovation.
• Roadworks, diesel exhausts of the heavy equipments used, emission from the production of building materials, etc.
• Dusty materials that are not cleaned up or properly covered (e.g., in construction sites, landfills and ceramics production facilities; ashes left from burning or wildfires).
• Metalworking (e.g., welding).
• Woodworking.
• Glass reprocessing.
• Industries.
• Cooking (frying, boiling, grilling).
• Agricultural activities (e.g., ploughing and soil tilling).
• Power plants.
• Waste incineration.
• Road dust from tyre and road wear and road dust from unpaved road.
• Wet cooling towers in cooling systems.
• Various industrial processes such as mining,smelting and oil refining.
• Disasters (both natural or caused by humans, e.g., wildfires, earthquakes, wars, and September 11 attacks, etc.).
• Microplastics (gaining attention as a type of airborne PM).

Some types of dust, e.g., ashes, soot, paint, glass, plastic and dust from certain man-made fibres, which are brittle and break easily (can fragment and "proliferate"), can pose greater threats and irritations to humans. Those with sharp edges may be even more problematic. The number, shapes, stickiness, etc. of particulates may also be altered by different meteorological conditions.

Human-made (anthropogenic) aerosols account for about 10 percent of the total mass of aerosols in the atmosphere as estimated in 2010. The remaining 90 percent comes from natural sources such as volcanoes, dust storms, forest and grassland fires, living vegetation and sea spray, emitting particulates such as volcanic ash, desert dust, soot and sea salt.

Domestic combustion and wood smoke

In the United Kingdom domestic combustion is the largest single source of PM_2.5 and PM₁₀ annually, with domestic wood burning in both closed stoves and open fires responsible for 38% of PM_2.5 in 2019. To tackle the problem some new laws were introduced since 2021. In some towns and cities in New South Wales wood smoke may be responsible for 60% of fine particle air pollution in the winter.

There are a few ways to reduce wood smoke, e.g., buying the right wood heater and maintaining it well, choosing the right firewood and burning it the right way. There are also regulations in some countries where people can report smoke pollution to the local council.

Composition

Global aerosols portrait produced by a GEOS-5 simulation at a 10-km resolution, August 2006 - April 2007.
Red/orange: desert (mineral) dust
Blue: sea salt
Green: smoke
White: sulfate particles

The composition and toxicity of aerosols, including particles, depends on their source and atmospheric chemistry and varies widely. Wind-blown mineral dust tends to be made of mineral oxides and other material blown from the Earth's crust; this particulate is light-absorbing. Sea salt is considered the second-largest contributor in the global aerosol budget, and consists mainly of sodium chloride originated from sea spray; other constituents of atmospheric sea salt reflect the composition of sea water, and thus include magnesium, sulfate, calcium, potassium, and others. In addition, sea spray aerosols may contain organic compounds like fatty acids and sugars, which influence their chemistry.

Some secondary particles derive from the oxidation of primary gases such as sulfur and nitrogen oxides into sulfuric acid (liquid) and nitric acid (gaseous) or from biogenic emissions. The precursors for these aerosols—i.e. the gases from which they originate—may have an anthropogenic origin (from biomass and fossil fuel combustion) as well as a natural biogenic origin. In the presence of ammonia, secondary aerosols often take the form of ammonium salts; i.e. ammonium sulfate and ammonium nitrate (both can be dry or in aqueous solution); in the absence of ammonia, secondary compounds take an acidic form as sulfuric acid (liquid aerosol droplets) and nitric acid (atmospheric gas).

Secondary sulfate and nitrate aerosols are strong light-scatterers. This is mainly because the presence of sulfate and nitrate causes the aerosols to increase to a size that scatters light effectively.

Organic matter (OM) found in aerosols can be either primary or secondary, the latter part deriving from the oxidation of volatile organic compounds (VOCs); organic material in the atmosphere may either be biogenic or anthropogenic. Organic matter influences the atmospheric radiation field by both scattering and absorption. Some aerosols are predicted to include strongly light-absorbing material and are thought to yield large positive radiative forcing. Some secondary organic aerosols (SOAs) resulting from combustion products of internal combustion engines, have been identified as a danger to health. Particulate toxicity has been found to vary by region and source contribution which affects the particles chemical composition.

The chemical composition of the aerosol directly affects how it interacts with solar radiation. The chemical constituents within the aerosol change the overall refractive index. The refractive index will determine how much light is scattered and absorbed.

The composition of particulate matter that generally causes visual effects, haze, consists of sulfur dioxide, nitrogen oxides, carbon monoxide, mineral dust, and organic matter. The particles are hygroscopic due to the presence of sulfur, and SO₂ is converted to sulfate when high humidity and low temperatures are present. This causes reduced visibility and red-orange-yellow colors.

Size distribution

False-color maps are based on data from the Moderate Resolution Imaging Spectroradiometer (MODIS) on NASA's Terra satellite. Green: aerosol plumes dominated by larger particles. Red: aerosol plumes dominated by small particles. Yellow: plumes in which large and small aerosol particles are intermingling. Gray: the sensor did not collect data.

Human-produced aerosols such as particle pollution tend to have a smaller radius than aerosol particles of natural origin (such as windblown dust). The false-color maps in the map of distribution of aerosol particles on the right show where there are natural aerosols, human pollution, or a mixture of both, monthly.

Smaller aerosols in the North

The size distribution time series shows that in the planet's most southerly latitudes, nearly all the aerosols are large, but in the high northern latitudes, smaller aerosols are very abundant. Most of the Southern Hemisphere is covered by the ocean, where the largest source of aerosols is natural sea salt from dried sea spray. Because the land is concentrated in the Northern Hemisphere, the amount of small aerosols from fires and human activities is greater there than in the Southern Hemisphere. Overland, patches of large-radius aerosols appear over deserts and arid regions, most prominently, the Sahara Desert in North Africa and the Arabian Peninsula, where dust storms are common. Places where human-triggered or natural fire activity is common (land-clearing fires in the Amazon from August–October, for example, or lightning-triggered fires in the forests of northern Canada in Northern Hemisphere summer) are dominated by smaller aerosols. Human-produced (fossil fuel) pollution is largely responsible for the areas of small aerosols over developed areas such as the eastern United States and Europe, especially in their summer.^{[better source needed]}

Satellite measurements of aerosols, called aerosol optical thickness, are based on the fact that the particles change the way the atmosphere reflects and absorbs visible and infrared light. As shown in this page, an optical thickness of less than 0.1 (palest yellow) indicates a crystal clear sky with maximum visibility, whereas a value of 1 (reddish-brown) indicates very hazy conditions.^{[better source needed]}

Deposition processes

In general, the smaller and lighter a particle is, the longer it will stay in the air. Larger particles (greater than 10 micrometers in diameter) tend to settle to the ground by gravity in a matter of hours. The smallest particles (less than 1 micrometer) can stay in the atmosphere for weeks and are mostly removed by precipitation. There are evidence that aerosols can "travel across the ocean". For example, in September 2017 wildfires burning across the western United States and Canada, and the smoke was found to have arrived over the United Kingdom and northern France in three days, as shown by satellite images.Diesel particulate matter is highest near the source of emission. Any information regarding DPM and the atmosphere, flora, height, and distance from major sources is useful to determine health effects.

Control

Technologies

Fabric filters Hepa effect: without (outdoor) and with filter (indoor)

Particulate matter emissions are highly regulated in most industrialized countries. Due to environmental concerns, most industries are required to operate some kind of dust collection system. These systems include inertial collectors (cyclonic separators), fabric filter collectors (baghouses), electrostatic filters used in facemasks,wet scrubbers, and electrostatic precipitators.

Cyclonic separators are useful for removing large, coarse particles and are often employed as a first step or "pre-cleaner" to other more efficient collectors. Well-designed cyclonic separators can be very efficient in removing even fine particulates, and may be operated continuously without requiring frequent shutdowns for maintenance.^{[citation needed]}

Fabric filters or baghouses are the most commonly employed in general industry. They work by forcing dust-laden air through a bag-shaped fabric filter leaving the particulate to collect on the outer surface of the bag and allowing the now clean air to pass through to either be exhausted into the atmosphere or in some cases recirculated into the facility. Common fabrics include polyester and fiberglass and common fabric coatings include PTFE (commonly known as Teflon). The excess dust buildup is then cleaned from the bags and removed from the collector.

Substantial amount of construction dust emitted and rising up from a building under rehabilitation on a Saturday afternoon, Treasure Garden, Tai Po, Hong Kong. The rehabilitation scheme is subsidised by the government and contract like this can worth up to a hundred million. People are living inside the building throughout the whole period of the renovation work, which usually lasts for over a year, and it can be foretold that the residents' exposure to construction dust is even more serious than the occupational exposure of the workers. The possible presence of asbestos and lead paint dust is also worth worrying. This type of rehabilitation works are very common (over 3000 buildings in the first 6 years of the scheme), especially in some older districts. With such a large amount of dust emitted, it was obvious that neither water was being sprayed nor dust extraction device was in use, which was a violation of the local law.

Wet scrubbers pass the dirty air through a scrubbing solution (usually a mixture of water and other compounds) allowing the particulate to attach to the liquid molecules. Electrostatic precipitators electrically charge the dirty air as it passes through. The now charged air then passes through large electrostatic plates which attract the charged particle in the airstream collecting them and leaving the now clean air to be exhausted or recirculated.

Measures

For general building construction, some places that have acknowledged the possible health risks of construction dust for decades legally require the relevant contractor to adopt effective dust control measures, although inspections, fines and imprisonments are rare in recent years (for example, two prosecutions with a total fines of HK$6,000 in Hong Kong in the year 2021).

Some of the mandatory dust control measures include load, unload, handle, transfer, store or dispose of cement or dry pulverized fuel ash in a completely enclosed system or facility, and fit any vent or exhaust with an effective fabric filter or equivalent air pollution control system or equipment, enclose the scaffolding of the building with dust screens, use impervious sheeting to enclose both material hoist and debris chute, wet debris with water before it is dumped into a debris chute, have water sprayed on the facade surface before and during grinding work, use grinder equipped with vacuum cleaner for facade grinding work, spray water continuously on the surface for any pneumatic or power-driven drilling, cutting, polishing or other mechanical breaking operation that causes dust emission, unless there is the operation of an effective dust extraction and filtering device, provide hoarding of not less than 2.4 m in height along the whole length of the site boundary, have hard paving on open area and wash every vehicle that leaves the construction sites. Use of automatic sprinkler equipment, automatic carwash equipment and installation of video surveillance system for the pollution control facilities and retain the videos for one month for future inspections.

Besides removing particulates from the source of pollution, they may also be cleaned in the open air (e.g. smog tower, moss wall, and water truck), while other control measures employ the use of barriers.

Measurement

Particulates have been measured in increasingly sophisticated ways since air pollution was first systematically studied in the early 20th century. The earliest methods included relatively crude Ringelmann charts, which were grey-shaded cards against which emissions from smokestacks could be visually compared, and deposit gauges, which collected the soot deposited in a particular location so it could be weighed. Automated, modern methods of measuring particulates include optical photodetectors, tapered element oscillating microbalances, and Aethalometers. Besides measuring the total mass of particles per unit volume of air (particle mass concentration), sometimes it is more useful to measure the total number of particles per unit volume of air (). This can be done by using a condensation particle counter (CPC).

To measure the atomic composition of particulate samples, techniques such as X-ray spectrometry can be used.

Climate effects

Aerosols have a cooling effect that is small compared to the radiative forcing (warming effect) of greenhouse gases.

Atmospheric aerosols affect the climate of the Earth by changing the amount of incoming solar radiation and outgoing terrestrial longwave radiation retained in the Earth's system. This occurs through several distinct mechanisms which are split into direct, indirect and semi-direct aerosol effects. The aerosol climate effects are the biggest source of uncertainty in future climate predictions. The Intergovernmental Panel on Climate Change (IPCC) stated in 2001:

While the radiative forcing due to greenhouse gases may be determined to a reasonably high degree of accuracy... the uncertainties relating to aerosol radiative forcings remain large, and rely to a large extent on the estimates from global modeling studies that are difficult to verify at the present time.

Aerosol radiative

Global aerosol optical thickness. The aerosol scale (yellow to dark reddish-brown) indicates the relative amount of particles that absorb sunlight.

Average monthly aerosol amounts around the world, observations from the Moderate Resolution Imaging Spectroradiometer (MODIS) on NASA's Terra satellite.

Direct

Particulates in the air causing shades of orange, yellow, pink, and grey in Mumbai during sunset

Italian city polluted by particulates and optic air detector (laser)

The direct aerosol effect consists of any direct interaction of radiation with atmospheric aerosols, such as absorption or scattering. It affects both short and longwave radiation to produce a net negative radiative forcing. The magnitude of the resultant radiative forcing due to the direct effect of an aerosol is dependent on the albedo of the underlying surface, as this affects the net amount of radiation absorbed or scattered to space. For example, if a highly scattering aerosol is above a surface of low albedo it has a greater radiative forcing than if it was above a surface of high albedo. The converse is true of absorbing aerosol, with the greatest radiative forcing arising from a highly absorbing aerosol over a surface of high albedo. The direct aerosol effect is a first-order effect and is therefore classified as a radiative forcing by the IPCC. The interaction of an aerosol with radiation is quantified by the single-scattering albedo (SSA), the ratio of scattering alone to scattering plus absorption (extinction) of radiation by a particle. The SSA tends to unity if scattering dominates, with relatively little absorption, and decreases as absorption increases, becoming zero for infinite absorption. For example, the sea-salt aerosol has an SSA of 1, as a sea-salt particle only scatters, whereas soot has an SSA of 0.23, showing that it is a major atmospheric aerosol absorber.^{[citation needed]}

Indirect

The Indirect aerosol effect consists of any change to the Earth's radiative budget due to the modification of clouds by atmospheric aerosols and consists of several distinct effects. Cloud droplets form onto pre-existing aerosol particles, known as cloud condensation nuclei (CCN). Droplets condensing around human-produced aerosols such as found in particulate pollution tend to be smaller and more numerous than those forming around aerosol particles of natural origin (such as windblown dust).

For any given meteorological conditions, an increase in CCN leads to an increase in the number of cloud droplets. This leads to more scattering of shortwave radiation i.e. an increase in the albedo of the cloud, known as the cloud albedo effect, First indirect effect or Twomey effect. Evidence supporting the cloud albedo effect has been observed from the effects of ship exhaust plumes and biomass burning on cloud albedo compared to ambient clouds. The Cloud albedo aerosol effect is a first order effect and therefore classified as a radiative forcing by the IPCC.

An increase in cloud droplet number due to the introduction of aerosol acts to reduce the cloud droplet size, as the same amount of water is divided into more droplets. This has the effect of suppressing precipitation, increasing the cloud lifetime, known as the cloud lifetime aerosol effect, second indirect effect or Albrecht effect. This has been observed as the suppression of drizzle in ship exhaust plume compared to ambient clouds, and inhibited precipitation in biomass burning plumes. This cloud lifetime effect is classified as a climate feedback (rather than a radiative forcing) by the IPCC due to the interdependence between it and the hydrological cycle. However, it has previously been classified as a negative radiative forcing.

Semi-direct

The Semi-direct effect concerns any radiative effect caused by absorbing atmospheric aerosol such as soot, apart from direct scattering and absorption, which is classified as the direct effect. It encompasses many individual mechanisms, and in general is more poorly defined and understood than the direct and indirect aerosol effects. For instance, if absorbing aerosols are present in a layer aloft in the atmosphere, they can heat surrounding air which inhibits the condensation of water vapour, resulting in less cloud formation. Additionally, heating a layer of the atmosphere relative to the surface results in a more stable atmosphere due to the inhibition of atmospheric convection. This inhibits the convective uplift of moisture, which in turn reduces cloud formation. The heating of the atmosphere aloft also leads to a cooling of the surface, resulting in less evaporation of surface water. The effects described here all lead to a reduction in cloud cover i.e. an increase in planetary albedo. The semi-direct effect classified as a climate feedback) by the IPCC due to the interdependence between it and the hydrological cycle. However, it has previously been classified as a negative radiative forcing.

Specific aerosol roles

Sulfate

Sulfate aerosols are mostly inorganic sulfur compounds like SO²⁻
₄, HSO⁻
₄ and H
₂SO⁻
₄, which are mainly produced when sulfur dioxide reacts with water vapor to form gaseous sulfuric acid and various salts (often through an oxidation reaction in the clouds), which are then thought to experience hygroscopic growth and coagulation and then shrink through evaporation. Some of them are biogenic (typically produced via atmospheric chemical reactions with dimethyl sulfide from mostly marine plankton) or geological via volcanoes or weather-driven from wildfires and other natural combustion events, but in the recent decades anthropogenic sulfate aerosols produced through combustion of fossil fuels with a high sulfur content, primarily coal and certain less-refined fuels, like aviation and bunker fuel, had dominated. By 1990, global human-caused emissions of sulfur into the atmosphere became "at least as large" as all natural emissions of sulfur-containing compounds combined, and were at least 10 times more numerous than the natural aerosols in the most polluted regions of Europe and North America, where they accounted for 25% or more of all air pollution. This led to acid rain, and also contributed to heart and lung conditions and even the risk of preterm birth and low birth weight. Sulfate pollution also has a complex relationship with NOx pollution and ozone, reducing the also harmful ground-level ozone, yet capable of damaging the stratospheric ozone layer as well.

Stratospheric sulfates from volcanic emissions cause transient cooling; the purple line showing sustained cooling is from tropospheric sulfate pollution.

Once the problem became clear, the efforts to remove this pollution through flue-gas desulfurization measures and other pollution controls were largely successful, reducing their prevalence by 53% and causing healthcare savings valued at $50 billion annually in the United States alone. Yet, around the same time, research had shown that sulfate aerosols were affecting both the visible light received by the Earth and its surface temperature, and as the so-called global dimming) began to reverse in the 1990s in line with the reduced anthropogenic sulfate pollution, climate change accelerated. As of 2021, state-of-the-art CMIP6 models estimate that total cooling from the currently present aerosols is between 0.1 °C (0.18 °F) to 0.7 °C (1.3 °F); the IPCC Sixth Assessment Report uses the best estimate of 0.5 °C (0.90 °F), with the uncertainty mainly caused by contradictory research on the impacts of aerosols of clouds. Some are certain that they cool the planet, though, and this led to solar geoengineering proposals known as stratospheric aerosol injection, which seeks to replicate and enhance the cooling from sulfate pollution while minimizing the negative effects on health through deploying in the stratosphere, where only a fraction of the current sulfur pollution would be needed to avoid multiple degrees of warming, but the assessment of costs and benefits remains incomplete, even with hundreds of studies into the subject completed by the early 2020s.

Black carbon

Black carbon (BC) or elemental carbon (EC), often called soot, is composed of pure carbon clusters, skeleton balls and fullerenes, and is one of the most important absorbing aerosol species in the atmosphere. It should be distinguished from organic carbon (OC): clustered or aggregated organic molecules on their own or permeating an EC buckyball. Black carbon from fossil fuels is estimated by the IPCC in the Fourth Assessment Report of the IPCC, 4AR, to contribute a global mean radiative forcing of +0.2 W/m² (was +0.1 W/m² in the Second Assessment Report of the IPCC, SAR), with a range +0.1 to +0.4 W/m². A study published in 2013 however, states that "the best estimate for the industrial-era (1750 to 2005) direct radiative forcing of atmospheric black carbon is +0.71 W/m² with 90% uncertainty bounds of (+0.08, +1.27) W/m²" with "total direct forcing by all-black carbon sources, without subtracting the preindustrial background, is estimated as +0.88 (+0.17, +1.48) W/m²".

Instances

Solar radiation reduction due to volcanic eruptions

Volcanoes are a large natural source of aerosol and have been linked to changes in the Earth's climate often with consequences for the human population. Eruptions linked to changes in climate include the 1600 eruption of Huaynaputina which was linked to the Russian famine of 1601–1603, leading to the deaths of two million, and the 1991 eruption of Mount Pinatubo which caused a global cooling of approximately 0.5 °C lasting several years. Research tracking the effect of light-scattering aerosols in the stratosphere during 2000 and 2010 and comparing its pattern to volcanic activity show a close correlation. Simulations of the effect of anthropogenic particles showed little influence at present levels.

Aerosols are also thought to affect weather and climate on a regional scale. The failure of the Indian monsoon has been linked to the suppression of evaporation of water from the Indian Ocean due to the semi-direct effect of anthropogenic aerosol.

Recent studies of the Sahel drought and major increases since 1967 in rainfall in Australia over the Northern Territory, Kimberley, Pilbara and around the Nullarbor Plain have led some scientists to conclude that the aerosol haze over South and East Asia has been steadily shifting tropical rainfall in both hemispheres southward.

Health effects

Air pollution measurement station in Emden, Germany

Size, shape, and solubility matter

Size

The size of particulate matter (PM) is a key determinant of its potential to cause health problems. Particles of different sizes deposit in different regions of the respiratory tract, leading to various health effects. The particles are grouped by sizes:

• Coarse particles (PM₁₀), with diameters between 2.5 and 10 micrometers, are inhalable and can deposit in the upper airways, including the nose, throat, and bronchi. Exposure to PM₁₀ is associated with respiratory diseases (such as aggravation of asthma, bronchitis, and rhinosinusitis), cardiovascular effects (such as increased risk of heart attacks and arrhythmias due to systemic inflammation).
• Fine particles (PM_2.5), with diameters less than 2.5 micrometers, can penetrate deep into the lungs, reaching the bronchioles and alveoli. They are associated with chronic rhinosinusitis (PM_2.5 particles can deposit in the nasal passages and sinuses, leading to inflammation and chronic rhinosinusitis), respiratory diseases (exacerbation of asthma and COPD due to deep lung penetration), and cardiovascular diseases from systemic inflammation and oxidative stress.
• Ultrafine particles (PM_0.1), with diameters less than 0.1 micrometers (100 nanometers), can enter the bloodstream and reach other organs, including the heart and brain. Health effects include neurological effects (potential contribution to neurodegenerative diseases such as Alzheimer's due to particles crossing the blood-brain barrier), cardiovascular effects such as promotion of atherosclerosis and increased risk of heart attacks.

Mechanisms of health effects

Particles can cause health effects through several mechanisms: inflammation in the respiratory tract oxidative stress via reactive oxygen species, leading to cellular damage, and systemic effects, such as translocation of ultrafine particles into circulation affects organs beyond the lungs.

Outcomes

Exposure to particulate matter is linked to various diseases across body systems, such as respiratory system (asthma, chronic obstructive pulmonary disease (COPD), lung cancer, and rhinosinusitis), cardiovascular system (heart attacks, hypertension, arrhythmias, and atherosclerosis), nervous system (cognitive decline and neurodegenerative diseases), metabolic system (diabetes and metabolic syndrome due to inflammatory pathways).

Threshold Concentrations and Guidelines

The World Health Organization (WHO) provides guidelines to limit exposure:

• PM₁₀: Annual mean not to exceed 15 μg/m³; 24-hour mean not to exceed 45 μg/m³.
• PM_2.5: Annual mean not to exceed 5 μg/m³; 24-hour mean not to exceed 15 μg/m³.
• Exposure above these levels increases the risk of adverse health effects.

Solubility

The site and extent of absorption of inhaled gases and vapors are determined by their solubility in water. Absorption is also dependent upon air flow rates and the partial pressure of the gases in the inspired air. The fate of a specific contaminant is dependent upon the form in which it exists (aerosol or particulate). Inhalation also depends upon the breathing rate of the subject.

Shape

Another complexity not entirely documented is how the shape of PM can affect health, except for the needle-like shape of asbestos fibres which can lodge in the lungs. Geometrically angular shapes have more surface area than rounder shapes, which in turn affects the binding capacity of the particle to other, possibly more dangerous substances.^{[citation needed]} The table below lists the colours and shapes of some common atmospheric particulates:

Type of particulate	Color	Shape
Portland cement	Gray	Irregular
Smolder smoke	White	Spherical
Soot	Black	Fractal aggregate
Water droplets	White	Spherical
Loess	Yellow Brown	Irregular
Lokon volcanic ash	Dark Brown	Irregular
Sahara sand (Libya)	Brown	Irregular

Scanning electronic microscopy of particulates

• Scanning electron microscopy of glass powder originated from glass bottles
• Scanning electron microscopy of cement
• Scanning electron microscopy of mortar glass powder (10%) which seems to have fibre-like structure
• Scanning electron microscopy of white asbestos with needle-like shape fibre

Composition, quantity, and duration

Worker in a cloud of concrete dust

Composition of particles can vary greatly depending on their sources and how they are produced. For example, dust emitted from the burning of vegetation would be different from those emitted from the burning of incense paper or construction waste. Particles emitted from fuel combustion are not the same as those emitted from waste combustion. The particulate matter generated from the fire of a recycling yard or a ship full of scrap metal may contain more toxic substances than other types of burning.

Different types of building activities produce different kinds of dust too. The composition of PM generated from cutting or mixing concrete made with Portland Cement would be different from those generated from cutting or mixing concrete made with different types of slag (e.g. GGBFS, EAF slag), fly ash or even EAF dust (EAFD), while EFAD, slag and fly ash are likely to be more toxic as they contain heavy metals. Besides slag cement that is sold and used as an environmental friendly product, fake (adulterated) cement, where different types of slag, fly ash or other unknown substances are added, is also very common in some places due to the much lower production cost. To address to the quality and toxicity problems, some places are starting to ban the use of EAF slag in cement used in buildings. Composition of welding fumes varies a lot as well and it depends on the metals in the material being welded, the composition of the coatings, electrode, etc., and hence a lot of health problems (e.g., lead poisoning, metal Fume Fever, cancers, nausea, irritation, kidney and liver damage, central nervous system problems, asthma, pneumonia, etc.) can be resulted from the different types of toxic emissions.

Studies have found that blood lead levels of people in China are highly correlated to ambient PM_2.5 concentration as well as top soil lead content, indicating that air and soil (e.g., by the inhalation of resuspended soil particles, consuming of contaminated crops or water, etc.) are important sources of lead exposure.

Besides composition, quantity and duration of exposure are also important, since they would affect the triggering and severity of a disease. Particles that get into indoor would directly affect indoor air quality. Possible secondary contamination, similar to third-hand smoke, is also of concern.

Since construction and refurbishment projects are prominent sources of particulate matter, it implicates that such projects, which are very common in some places, should be avoided in health facilities that already commenced and under operation as far as possible. For inevitable projects, better plannings and mitigation measures regarding PM emission should be introduced. Use of power tools, heavy equipments, diesel fuels and potentially toxic building materials (e.g. concrete, metals, solder, paint, etc.) should be strictly monitored to ensure that patients who are there seeking for disease treatments or chances to survive are not adversely affected.

Health problems

Deaths from air pollution compared to other common causes

Air quality information on PM₁₀ displayed in Katowice, Poland

The effects of inhaling particulate matter that have been widely studied in humans and animals include COVID-19,asthma, lung cancer, respiratory diseases like silicosis, cardiovascular disease, premature delivery, birth defects, low birth weight, developmental disorders, neurodegenerative disorders mental disorders, and premature death. Outdoor fine particulates with diameter less than 2.5 microns accounts for 4.2 million annual deaths worldwide, and more than 103 million disability-adjusted life-years lost, making it the fifth leading risk factor for death. Air pollution has also been linked to a range of other psychosocial problems. Particulates may cause tissue damage by entering organs directly, or indirectly by systemic inflammation. Adverse effects may occur even at exposure levels lower than published air quality standards deemed safe.

Anthropogenic fine particulates as main hazard

Increased levels of fine particles in the air as a result of anthropogenic particulate air pollution "is consistently and independently related to the most serious effects, including lung cancer and other cardiopulmonary mortality". The association between a large number of deaths and other health problems and particulate pollution was first demonstrated in the early 1970s and has been reproduced many times since. PM pollution is estimated to cause 22,000–52,000 deaths per year in the United States (from 2000) contributed to ~370,000 premature deaths in Europe during 2005. and 3.22 million deaths globally in 2010 per the global burden of disease collaboration. A study by the European Environment Agency estimates that 307,000 people have died prematurely in 2019 due to fine particle pollution in the 27 EU member states.

A study in 2000 conducted in the U.S. explored how fine particulate matter may be more harmful than coarse particulate matter. The study was based on six different cities. They found that deaths and hospital visits that were caused by particulate matter in the air were primarily due to fine particulate matter. Similarly, a 1987 study of American air pollution data found that fine particles and sulfates, as opposed to coarser particles, most consistently and significantly correlated to total annual mortality rates in standard metropolitan statistical areas.

A study published in 2022 in GeoHealth concluded that eliminating energy-related fossil fuel emissions in the United States would prevent 46,900–59,400 premature deaths each year and provide $537–678 billion in benefits from avoided PM_2.5-related illness and death.

Infertility, pregnancy, and birth defects

Higher rates of infertility have been correlated with exposure to particulates. Maternal PM_2.5 exposure during pregnancy is also associated with high blood pressure in children.

Inhalation of PM_2.5 – PM₁₀ is associated with elevated risk of adverse pregnancy outcomes, such as low birth weight. Exposure to PM_2.5 has been associated with greater reductions in birth weight than exposure to PM₁₀. PM exposure can cause inflammation, oxidative stress, endocrine disruption, and impaired oxygen transport access to the placenta, all of which are mechanisms for heightening the risk of low birth weight. Overall epidemiologic and toxicological evidence suggests that a causal relationship exists between long-term exposures to PM_2.5 and developmental outcomes (i.e. low birth weight). Studies investigating the significance of trimester-specific exposure have proven to be inconclusive, and results of international studies have been inconsistent in drawing associations of prenatal particulate matter exposure and low birth weight. As perinatal outcomes have been associated with lifelong health and exposure to particulate matter is widespread, this issue is of critical public health importance.

Cardiovascular and respiratory disease

PM_2.5 leads to high plaque deposits in arteries, causing vascular inflammation and atherosclerosis – a hardening of the arteries that reduces elasticity, which can lead to heart attacks and other cardiovascular problems. A 2014 meta analysis reported that long term exposure to particulate matter is linked to coronary events. The study included 11 cohorts participating in the European Study of Cohorts for Air Pollution Effects (ESCAPE) with 100,166 participants, followed for an average of 11.5 years. An increase in estimated annual exposure to PM 2.5 of just 5 μg/m³ was linked with a 13% increased risk of heart attacks. Not only affecting human cells and tissues, PM also impacts bacteria which cause disease in humans.Biofilm formation, antibiotic tolerance, and colonisation of both Staphylococcus aureus and Streptococcus pneumoniae was altered by black carbon exposure.

The largest US study on acute health effects of coarse particle pollution between 2.5 and 10 micrometers in diameter was published 2008 and found an association with hospital admissions for cardiovascular diseases but no evidence of an association with the number of hospital admissions for respiratory diseases. After taking into account fine particle levels (PM_2.5 and less), the association with coarse particles remained but was no longer statistically significant, which means the effect is due to the subsection of fine particles.

The Mongolian government agency recorded a 45% increase in the rate of respiratory illness in the past five years (reported in 2011). Bronchial asthma, chronic obstructive pulmonary disease, and interstitial pneumonia were the most common ailments treated by area hospitals. Levels of premature death, chronic bronchitis, and cardiovascular disease are increasing at a rapid rate.

Cognitive hazards and mental health

The effects of air pollution and particulate matter on cognitive performance has become an active area of research.

Air pollution may increase the risk of developmental disorders (e.g., autism), neurodegenerative disorders, mental disorders, and suicide, although studies on the link between depression and some air pollutants are not consistent. At least one study has identified "the abundant presence in the human brain of magnetite nanoparticles that match precisely the high-temperature magnetite nanospheres, formed by combustion and/or friction-derived heating, which are prolific in urban, airborne particulate matter (PM)."

Particulates also appear to have a role in the pathogenesis of Alzheimer's disease and premature brain aging. There is increasing evidence to suggest a correlation between PM_2.5 exposure and the prevalence of neurodegenerative diseases such as Alzheimer's. Several epidemiological studies have suggested a link between PM_2.5 exposure and cognitive decline, particularly in the development of neurodegenerative diseases such as Alzheimer's.

Using geospatial analytical techniques, "NIEHS-funded researchers were able to confirm a strong association between cases of Parkinson's disease and fine particulate matter (known as PM_2.5) across the U.S. In the study, regions of the country with a high rate of Parkinson's disease were associated generally with higher levels of PM_2.5, of which sources include motor vehicles, wildfires, and power plants." While the exact mechanisms behind the link between PM_2.5 exposure and cognitive decline are not fully understood, research suggests that the fine particles may be able to enter the brain through the olfactory nerve and cause inflammation and oxidative stress, which can damage brain cells and contribute to the development of neurodegenerative diseases.

Increased death

The World Health Organization (WHO) estimated in 2005 that "... fine particulate air pollution (PM(2.5)), causes about 3% of mortality from cardiopulmonary disease, about 5% of mortality from cancer of the trachea, bronchus, and lung, and about 1% of mortality from acute respiratory infections in children under 5 years, worldwide." A 2011 study concluded that traffic exhaust is the single most serious preventable cause of heart attack in the general public, the cause of 7.4% of all attacks.

Particulate matter studies in Bangkok, Thailand from 2008 indicated a 1.9% increased risk of dying from cardiovascular disease, and 1.0% risk of all disease for every 10 micrograms per cubic meter. Levels averaged 65 in 1996, 68 in 2002, and 52 in 2004. Decreasing levels may be attributed to conversions of diesel to natural gas combustion as well as improved regulations.

Racial disparities

There have been many studies linking race to increased proximity to particulate matter, and thus susceptibility to adverse health effects of long term exposure. A U.S. study showed that "the proportions of Black residents in a tract was linked to higher asthma rates". Many scholars link this disproportionality to racial housing segregation and their respective inequalities in "toxic exposures". This reality is made worse by the finding that "health care occurs in the context of broader historic and contemporary social and economic inequality and persistent racial and ethnic discrimination in many sectors of American life". Residential proximity to particulate emitting facilities increases exposure to PM 2.5 which is linked to increased morbidity and mortality rates. Multiple studies confirm the burden of PM emissions is higher among non-White and poverty ridden populations, though some say that income does not drive these differences. This correlation between race and housing related health repercussions stems from a longstanding environmental justice problem linked to the practice of historic redlining. An example of these factors contextualized is an area of Southeastern Louisiana, colloquially dubbed 'Cancer Alley' for its high concentration of cancer related deaths due to neighboring chemical plants. Cancer Alley being a majority African American community, with the neighborhood nearest to the plant being 90% Black, perpetuates the scientific narrative that Black populations are located disproportionately closer to areas of high PM output than White populations. A 2020 article relates the long-term health effects of living in high PM concentrations to increased risk, spread, and mortality rates from the SARS-CoV-2 or COVID-19, and faults a history of racism for this outcome.

Wildfire smoke risk

In regions where wildfires are persistent the risk of particulate exposure increased. Smoke from wildfires may impact sensitive groups such as the elderly, children, pregnant women, and people with lung, and cardiovascular disease. It was found that in the 2008 wildfire season in California, the particulate matter was much more toxic to human lungs, as increased neutrophil infiltrate, cell influx and edema was observed versus particulate matter from ambient air. Furthermore, particulate matter from wildfires have been linked to be a triggering factor of acute coronary events such as ischemic heart disease. Wildfires also have been associated with increased emergency department visits due to particulate matter exposure, as well as an increased risk of asthma related events. A link between PM_2.5 from wildfires and increased risk of hospitalizations for cardiopulmonary diseases has been discovered. Evidence also suggest wildfire smoke reduces mental performance.

Energy industry knowledge and response to adverse health effects

Deaths caused by accidents and air pollution from fossil fuel use in power plants exceed those caused by production of renewable energy.

Major energy companies understood at least since the 1960s that use of their products causes widespread adverse health effects and death but continued aggressive political lobbying in the United States and elsewhere against clean air regulation and launched major corporate propaganda campaigns to sow doubt regarding the causative link between the burning of fossil fuels and major risks to human life. Internal company memoranda reveal that energy industry scientists and executives knew that air pollutants created by fossil fuels lodge deep in human lung tissue, and cause birth defects in children of oil industry workers. The industry memos acknowledge that automobiles "are by far the greatest sources of air pollution" and also that air pollution causes adverse health effects and lodges toxins, including carcinogens, "deep into the lungs which would otherwise be removed in the throat".

In response to mounting public concern, the industry eventually created the Global Climate Coalition, an industry lobby group, to derail governments' attempts to regulate air pollution and to create confusion in the public mind about the necessity of such regulation. Similar lobbying and corporate public relations efforts were undertaken by the American Petroleum Institute, a trade association of the oil and gas industry, and the climate change denier private think tank, The Heartland Institute. "The response from fossil-fuel interests has been from the same playbook – first they know, then they scheme, then they deny and then they delay. They've fallen back on delay, subtle forms of propaganda and the undermining of regulation," said Geoffrey Supran, a Harvard University researcher of the history of fossil-fuel companies and climate change. These efforts have been compared, by policy analysts such as Carroll Muffett of the Center for International Environmental Law, to the tobacco industry strategy of lobbying and corporate propaganda campaigns to create doubt regarding the causal connection between cigarette smoking and cancer and to forestall its regulation. In addition, industry-funded advocates, when appointed to senior government positions in the United States, have revised scientific findings showing the deadly effects of air pollution and have rolled back its regulation.

Effects on vegetation

Particulate matter can clog stomatal openings of plants and interfere with photosynthesis functions. In this manner, high particulate matter concentrations in the atmosphere can lead to growth stunting or mortality in some plant species.^{[citation needed]}

Regulation

Most governments have created regulations both for the emissions allowed from certain types of pollution sources (motor vehicles, industrial emissions etc.) and for the ambient concentration of particulates. The IARC and WHO designate particulates a Group 1 carcinogen. Particulates are the deadliest form of air pollution due to their ability to penetrate deep into the lungs and blood streams unfiltered, causing respiratory diseases, heart attacks, and premature death. In 2013, the ESCAPE study involving 312,944 people in nine European countries revealed that there was no safe level of particulates and that for every increase of 10 μg/m³ in PM₁₀, the lung cancer rate rose 22%. For PM_2.5 there was a 36% increase in lung cancer per 10 μg/m³. In a 2014 meta-analysis of 18 studies globally including the ESCAPE data, for every increase of 10 μg/m³ in PM_2.5, the lung cancer rate rose 9%.

Limits / standards set by governments

Country/ Region	PM2.5 (μg⁄m^3)		PM10 (μg⁄m^3)		No. of exceedances allowed per year
	Yearly avg.	Daily avg. (24-hour)	Yearly avg.	Daily avg (24-hour)
Australia	8	25	25	50	None
China	35	75	70	150	None
European Union	25	None	40	50	PM2.5: None; PM10: 35
Hong Kong	35	75	50	100	PM2.5: 9; PM10: 9
Japan	15	35	None	100	None
South Korea	15	35	50	100	None
Taiwan	15	35	50	100	None
United Kingdom	20	50	40		35
United States	9	35	None	150	PM2.5: Not applicable; PM10: 1
World Health Organization	5	15	15	45	3–4

Canada

In Canada the standard for particulate matter is set nationally by the federal-provincial Canadian Council of Ministers of the Environment (CCME). Jurisdictions (provinces and territories) may set more stringent standards. The CCME standard for particulate matter 2.5 (PM_2.5) as of 2015 is 28 μg/m³ (calculated using the 3-year average of the annual 98th percentile of the daily 24-hr average concentrations) and 10 μg/m³ (3-year average of annual mean). PM_2.5 standards will increase in stringency in 2020.

European Union

The European Union has established the European emission standards, which include limits for particulates in the air:

European Air Quality Index	Good	Fair	Moderate	Poor	Very poor	Extremely poor
Particles less than 2.5μm (PM2,5)	0–10 μg/m^3	10–20 μg/m^3	20–25 μg/m^3	25–50 μg/m^3	50–75 μg/m^3	75–800 μg/m^3
Particles less than 10μm (PM10)	0–20 μg/m^3	20–40 μg/m^3	40–50 μg/m^3	50–100 μg/m^3	100–150 μg/m^3	150–1200 μg/m^3

United Kingdom

To mitigate the problem of wood burning, starting from May 2021, traditional house coal (bituminous coal) and wet wood, two of the most polluting fuels, can no longer be sold. Wood sold in volumes of less than 2m³ must be certified as 'Ready to Burn', which means it has a moisture content of 20% or less. Manufactured solid fuels must also be certified as 'Ready to Burn' to ensure they meet sulphur and smoke emission limits. Starting from January 2022, all new wood burning stoves have to meet new EcoDesign standards (Ecodesign stoves produce 450 times more toxic air pollution than gas central heating. Older stoves, which are now banned from sale, produce 3,700 times more).

In 2023, the amount of smoke that burners in "smoke control areas" - most England's towns and cities - can emit per hour is reduced from 5g to 3g. Violation will result in an on-the-spot fine of up to £300. Those who do not comply may even get a criminal record.

United States

Air quality trends in the United States. Blue area shows the range of the middle 80% of monitoring sites.

The United States Environmental Protection Agency (EPA) has set standards for PM₁₀ and PM_2.5 concentrations. (See National Ambient Air Quality Standards.)

California

Air quality trends in the western United States. Blue area shows the range of the middle 80% of monitoring sites.

In October 2008, the Department of Toxic Substances Control (DTSC), within the California Environmental Protection Agency, announced its intent to request information regarding analytical test methods, fate and transport in the environment, and other relevant information from manufacturers of carbon nanotubes. DTSC is exercising its authority under the California Health and Safety Code, Chapter 699, sections 57018–57020. These sections were added as a result of the adoption of Assembly Bill AB 289 (2006). They are intended to make information on the fate and transport, detection and analysis, and other information on chemicals more available. The law places the responsibility to provide this information to the department on those who manufacture or import the chemicals.

On 22 January 2009, a formal information request letter was sent to manufacturers who produce or import carbon nanotubes in California, or who may export carbon nanotubes into the State. This letter constitutes the first formal implementation of the authorities placed into statute by AB 289 and is directed to manufacturers of carbon nanotubes, both industry, and academia within the State, and to manufacturers outside California who export carbon nanotubes to California. This request for information must be met by the manufacturers within one year. DTSC is waiting for the upcoming 22 January 2010 deadline for responses to the data call-in.

The California Nano Industry Network and DTSC hosted a full-day symposium on 16 November 2009 in Sacramento, California. This symposium provided an opportunity to hear from nanotechnology industry experts and discuss future regulatory considerations in California.

DTSC is expanding the Specific Chemical Information Call-in to members of the nanometal oxides, the latest information can be found on their website.

Colorado

Air quality trends in the southwestern United States. Blue area shows the range of the middle 80% of monitoring sites.

Key points in the Colorado Plan include reducing emission levels and solutions by sector. Agriculture, transportation, green electricity, and renewable energy research are the main concepts and goals in this plan. Political programs such as mandatory vehicle emissions testing and the prohibition of smoking indoors are actions taken by local government to create public awareness and participation in cleaner air. The location of Denver next to the Rocky Mountains and wide expanse of plains makes the metro area of Colorado's capital city a likely place for smog and visible air pollution.^{[citation needed]}

Affected areas

Difference between levels of PM_2.5 in the air in 2019 and 2022 among 70 capital cities

To analyse the air pollution trend, 480 cities around the world (Ukraine excluded) was mapped by air experts to calculate the average PM_2.5 level of the first nine months of 2019 against that of 2022. Average levels of PM_2.5 were measured using aqicn.org's World Air Quality Index data, and a formula developed by AirNow was used to convert the PM_2.5 figure into micrograms per cubic meter of air (μg⁄m³) values.

Among the 70 capital cities investigated, Baghdad, Iraq is the worst performing one, with PM_2.5 levels going up +31.6 μg/m³. Ulan Bator (Ulaanbaatar), the capital city of Mongolia, is performing the best, with PM_2.5 levels dropping by −23.4 μg/m³. Previously it was as one of the most polluted capital cities in the world. An air quality improvement plan in 2017 appears to be showing positive results.

Out of the 480 cities, Dammam in Saudi Arabia is performing the worst with PM_2.5 levels going up +111.1 μg/m³. The city is a significant center for the Saudi oil industry and home to both the largest airport in the world and the largest port in the Persian Gulf. It is currently the most polluted city surveyed.

In Europe, the worst performing cities are located in Spain. They are Salamanca and Palma, with PM_2.5 levels increase by +5.1 μg/m³ and +3.7 μg/m³ respectively. The best performing city is Skopje, the capital city of North Macedonia, with PM_2.5 levels dropping by −12.4 μg/m³. It was once the most polluted capital city in Europe and still has a long way to go to achieve clean air.

In the U.S., Salt Lake City, Utah and Miami, Florida are the two cities with the highest PM_2.5 level increases (+1.8 μg/m³). Salt Lake City suffers from a weather event known as 'inversion'. Located in a valley, cooler, polluted air is trapped close to ground level under the warmer air above when inversion occurs. On the other hand, Omaha, Nebraska is performing the best and has a decrease of −1.1 μg/m³ in PM_2.5 levels.

The cleanest city in this report is Zürich, Switzerland with PM_2.5 levels of just 0.5 μg/m³, placed first in both 2019 and 2022. The second cleanest city is Perth, with 1.7 μg/m³ and PM_2.5 levels dropping by −6.2 μg/m³ since 2019. Of the top ten cleanest cities, five are from Australia. They are Hobart, Wollongong, Launceston, Sydney and Perth. Honolulu is the only U.S. city in the top ten list, ranking tenth with levels of 4 μg/m³, with a tiny increase since 2019.

Almost all of the top ten most polluted cities are in the Middle East and Asia. The worst is Dammam in Saudi Arabia with a PM_2.5 level of 155 μg/m³. Lahore in Pakistan is the second worst with 98.1 μg/m³. The third is Dubai, home to the world's tallest building. In the bottom ten are three cities from India, Muzaffarnagar, Delhi and New Delhi. Here is a list of the 30 most polluted cities by PM_2.5, Jan to Sep 2022:

City	Country / Region	1st 9 months average PM2.5 (μg⁄m^3)
		2022	2019
Dammam	Saudi Arabia	155	43.9
Lahore	Pakistan	98.1	64.6
Dubai	United Arab Emirates	97.7	47.5
Baghdad	Iraq	60.5	29
Dhaka	Bangladesh	55.3	48.7
Muzaffarnagar	India	53.9	60.5
Delhi	India	51.6	59.8
Oaxaca	Mexico	51.1	13.5
New Delhi	India	50.1	54.2
Manama	Bahrain	48	43.4
Patna	India	47.9	53.5
Peshawar	Pakistan	47	46.7
Ghāziābād	India	46.6	56.9
Lucknow	India	46.4	54.1
Hawalli	Kuwait	46.2	40.4
Hapur	India	45.7	53.3
Chandigarh	India	44.9	39.7
Jaipur	India	43.5	40.6
Kampala	Uganda	42.9	48.3
Khorramshahr	Iran	42	30
Pokhara	Nepal	41.8	18.2
Abu Dhabi	United Arab Emirates	40.2	44.7
Xi'an	China	36.6	40
Xuchang	China	36.4	41.4
Xinxiang	China	36.3	46.4
Anyang	China	36.1	45.9
Shijiazhuang	China	36	44.9
Taiyuan	China	35.9	39.2
East London	South Africa	35.9	7.1
Gandhinagar	India	35.5	42.9

There are limits to the above survey. For example, not every city in the world is covered, and that the number of monitoring stations for each city would not be the same. The data is for reference only.

Australia

PM₁₀ pollution in coal mining areas in Australia such as the Latrobe Valley in Victoria and the Hunter Region in New South Wales significantly increased during 2004 to 2014. Although the increase did not significantly add to non-attainment statistics the rate of increase has risen each year during 2010 to 2014.

China

Some cities in Northern China and South Asia have had concentrations above 200 μg/m³. The PM levels in Chinese cities were extreme between 2010 and 2014, reaching an all-time high in Beijing on 12 January 2013, of 993 μg/m³, but has been improving thanks to clean air actions.

To monitor the air quality of south China, the U.S. Consulate Guangzhou set a PM_2.5 and PM₁₀ monitor on Shamian Island in Guangzhou and displays readings on its official website and social platforms.

Europe

Concentration of PM₁₀ in Europe, 2005

Italy

Concentration of PM_2,5 (European Air Quality Index) during time slot in a city in Italy 2019–2020

South Korea

As of 2017, South Korea has the worst air pollution among the developed nations in the OECD (Organization for Economic Cooperation and Development). According to a study conducted by NASA and NIER, 52% of PM_2.5 measured in Olympic Park, Seoul in May and June 2016 came from local emissions. The rest was trans-boundary pollution coming from China's Shandong Province (22%), North Korea (9%), Beijing (7%), [[Shanghai (5%), and a combined 5% from China's Liaoning Province, Japan and the West Sea. In December 2017, the environmental ministers from South Korea and China signed the China-Korea Environmental Cooperation Plan (2018–22), a five-year plan to jointly solve issues in the air, water, soil and waste. An environmental cooperation centre was also launched in 2018 to aid cooperation.

Thailand

Air quality of Thailand is getting worse in 2023, which is described as a "post-COVID back-to-normal situation". In addition to the capital Bangkok, air quality in Chiang Mai, a popular tourist destination, is also deteriorating. Chiang Mai was listed as the most polluted city in a live ranking by a Swiss air quality company on 27 March 2023. The ranking includes data from about 100 world cities for which measured PM_2.5 data is available.

Ulaanbaatar

Mongolia's capital city Ulaanbaatar has an annual average mean temperature of about 0 °C, making it the world's coldest capital city. About 40% of the population lives in apartments, 80% of which are supplied with central heating systems from three combined heat and power plants. In 2007, the power plants consumed almost 3.4 million tons of coal. The pollution control technology is in poor condition. ^{[citation needed]}

The other 60% of the population reside in shantytowns (Ger districts), which have developed due to the country's new market economy and the very cold winter seasons. The poor in these districts cook and heat their wood houses with indoor stoves fueled by wood or coal. The resulting air pollution is characterized by raised sulfur dioxide and nitrogen oxide levels and very high concentrations of airborne particles and particulate matter (PM). Annual seasonal average particulate matter concentrations have been recorded as high as 279 μg/m³ (micrograms per cubic meter).^{[citation needed]} The World Health Organization's recommended annual mean PM₁₀ level is 20 μg/m³, which means that Ulaanbaatar's PM₁₀ annual mean levels are 14 times higher than recommended.^{[citation needed]}

During the winter months, in particular, the air pollution obscures the air, affecting the visibility in the city to such an extent that airplanes on some occasions are prevented from landing at the airport.

In addition to stack emissions, another source unaccounted for in the emission inventory is fly ash from ash ponds, the final disposal place for fly ash that has been collected in settling tanks. Ash ponds are continually eroded by wind during the winter.

United States

• U.S. counties violating national PM_2.5 standards, June 2018
• U.S. counties violating national PM₁₀ standards, June 2018

From the "State of Air 2022" report compiled by the American Lung Association using data from the U.S. Environmental Protection Agency from 2018 to 2020, California cities are the most polluted cities (by PM_2.5) in the U.S. while the East Coast is cleaner.

However, another study has come up with a very different conclusion. According to Forbes, a travel insurance comparison site InsureMyTrip conducted a survey of 50 U.S. cities in 2020 and ranked them by cleanliness with criteria like hand sanitizer demand, cleanliness of restaurants, quantity of recycling collectors, satisfaction of garbage disposal, electric vehicle market share and pollution. On their top ten cleanest cities list, seven are from California, including Long Beach (No. 1), San Diego (No. 2), Sacramento (No. 3), San Jose (No. 6), Oakland (No. 7), Bakersfield (No. 9), and San Francisco (No. 10). The discrepancies maybe due to the differences in data choice, calculation methods, definitions of "cleanliness" and a large variation of air quality across the same state, etc. This again shows that one need to be very careful when drawing conclusions from the many air quality rankings available on the internet.

In mid-2023, air quality in eastern U.S. lowered significantly as particulates from Canada's wildfires blew down. According to NASA, some of the fires were ignited by lightning.

See also

• Air filter
• Air quality index | Air quality law
• ASTDR
• Bioaerosol
• Black carbon
• CCN (Cloud condensation nuclei)
• Chip formation
• Cleanroom
• Contamination control
• Criteria air contaminants
• Dust
• Exposure assessment | Exposure science
• Fertilizer | Pesticides
• Fog | Pea soup fog
• Fugitive dust
• Heavy industry
• List of least polluted cities by particulate matter concentration
• List of most polluted cities by particulate matter concentration
• Metal swarf | Sawdust
• NIEHS
• Non-exhaust emissions
• Occupational dust exposure
• Respirator
• Recycling
• Scrubber
• Suspended solids

Health effects:

• Health effects of coal ash
• Health effects of pesticides
• Health impact of asbestos
• Health impacts of sawdust

Health-related:

• Asthmagen
• Atherosclerosis
• Chronic obstructive pulmonary disease
• Exercise-induced bronchoconstriction
• Pneumoconiosis
• Pulmonary emphysema
• Pulmonary fibrosis

Other names

• atmospheric aerosol particles
• particulate matter (PM)
• suspended particulate matter (SPM)

Notes

1. PM₁₀ limit since 1 January 2005
2. PM_2.5 limit since 1 January 2015
3. Since 1 January 2014
4. PM₁₀ referred to as Suspended Particulate Matter
5. PM_2.5 limit since 21 September 2009
6. PM₁₀ limit since 4 December 2006
7. PM_2.5 limit since 27 March 2018
8. annual limit since 2024
9. daily limit since 2007
10. annual limit removed in 2006
11. daily limit since 1987
12. 3-year average of annual 98th percentile

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