Particulates, alternatively referred to as particulate matter (PM), aerosols or
fine particles, are tiny particles of solid or liquid suspended in a gas. They range in size from less than 10
nanometres to more than 100 micrometres in diameter. The
notation PM10 is used to describe particles of 10 micrometres or less and PM2.5 represents particles less
than 2.5 micrometres in aerodynamic diameter; other numeric values may also be used. This range of sizes represent scales from a
gathering of a few molecules to the size where the particles no longer can be carried by the
gas. Sources of particulate matter can be anthropogenic or natural.
Some particulates occur naturally, originating from volcanoes, dust storms, forest and grassland fires,
living vegetation, and sea spray. Human activities, such as the burning of fossil fuels also generate aerosols. Averaged over the globe, anthropogenic aerosols—those made by
human activities—currently account for about 10 percent of the total amount of aerosols in our atmosphere.
Sources
Aerosol pollution over Northern India and Bangladesh - Photo:
NASA
There are both natural and human sources of atmospheric particulates. The biggest natural sources are dust, volcanoes, and forest fires. Sea spray is also a large source of particles though most of these fall back to
the ocean close to where they were emitted. The biggest human sources of particles are combustion sources, mainly the burning of
fuels in internal combustion engines in automobiles and power plants, and wind blown dust from
construction sites and other land areas where the water or vegetation has been removed.
Some of these particles are emitted directly to the atmosphere (primary emissions) and some are emitted as gases and form particles in the atmosphere (secondary
emissions).
- "In Europe and the United States, particulate emissions from vehicles are expected to decline over the next decade. For
example, by 2005, the European Union will introduce more stringent standards for particulate emissions from light duty vehicles
of 0.025 grams per kilometer [0.04 grams per mile].
- The state of California is implementing an even more restrictive standard in 2004, allowing only 0.006 grams per kilometer
[0.01 grams per mile] of particulate emissions. Even if the California standard were introduced worldwide, says Jacobson, diesel
cars may still warm the climate more than gasoline cars over 13 to 54 years. New particle traps being introduced by some European
automobile manufacturers in their diesel cars appear to reduce black carbon emissions to
0.003 grams per kilometer [0.005 grams per mile], even below the California standard." [1]
BlueTec is one technology developed to reduce particulate emissions from Diesel engines in
order to meet strigent Californian standards.
Composition
The composition of aerosol particles depends on their source. Wind-blown mineral dust
[2] tends to be
made of mineral oxides and other material blown from the Earth's
crust; this aerosol is light-absorbing. Sea salt [3] 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,
etc. In addition, sea spray aerosols may contains organic compounds, which influence their chemistry. Sea salt does not
absorb.
Secondary particles derive from the oxidation of primary gases such as sulfur and nitrogen oxides into sulfuric acid (liquid) and nitric acid (gaseous). The precursors for
these aerosols, i.e. the gases from which they originate, may have an anthropogenic origin (from fossil fuel combustion) and 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.
[4] This is mainly
because the presence of sulphate and nitrate causes the aerosols to increase to a size that scatters light effectively.
Organic matter (OM) can be either primary or secondary, the latter part deriving
from the oxidation of VOCs; organic material in the atmosphere may either be
biogenic or anthropogenic. Organic matter influences the atmospheric radiation field by both scattering and absorption. Another important aerosol type is constitude of elemental carbon (EC, also known as black carbon, BC): this aerosol
type includes strongly light-absorbing material and is thought to yield large positive radiative forcing. Organic matter and elemental carbon together constitute the carbonaceous fraction of aerosols.ii [5]
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.
Removal 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 whereas the smallest particles (less than 1
micrometer) can stay in the atmosphere for weeks and are mostly removed by precipitation.
Radiative forcing from aerosols
Solar radiation reduction due to volcanic eruptions
Aerosols, natural and anthropogenic, can affect the climate by changing the way
radiation is transmitted through the atmosphere. Direct observations of the
effects of aerosols are quite limited so any attempt to estimate their global effect necessarily involves the use of computer
models. The Intergovernmental Panel on Climate Change, IPCC,
says: 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 modelling studies that are difficult to verify at the present time [6].
A graphic showing the contributions (at 2000, relative to pre-industrial) and uncertainties of various forcings is available
here.
Sulphate aerosol
Sulphate aerosol has two main effects, direct and indirect. The direct effect, via albedo, is
to cool the planet: the IPCC's best estimate of the
radiative forcing is -0.4 watts per square meter with a
range of -0.2 to -0.8 W/m² [7] but there are substantial uncertainties. The effect varies strongly geographically, with most cooling believed to
be at and downwind of major industrial centres. Modern climate models attempting to deal
with the attribution of recent climate change need to include
sulfate forcing, which appears to account (at least partly) for the slight drop in global temperature in the middle of the 20th
century. The indirect effect (via the aerosol acting as cloud condensation nuclei, CCN, and thereby modifying the cloud properties) is more uncertain but is believed to be a
cooling.
Black carbon
Black carbon (BC), or Carbon Black, or Elemental Carbon (EC), often called soot, is
composed of pure carbon clusters, skeleton balls and buckyballs, 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. BC from fossil fuels is estimated by the IPCC in the
Fourth Assessment Report of the IPCC, TAR, 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.
All aerosols both absorb and scatter solar and terrestrial radiation. If
a substance absorbs a significant amount of radiation, as well as scattering, we call it absorbing. This is quantified in 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, 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.
Health effects
The effects of inhaling particulate matter has been widely studied in humans and animals and include asthma, lung cancer, cardiovascular issues, and premature death. The size of the particle is a main determinant of where in the respiratory tract the particle will come to
rest when inhaled. Larger particles are generally filtered in the nose and throat and do not cause problems, but particulate
matter smaller than about 10 micrometres, referred to as PM10, can settle in the bronchi and lungs and cause health problems. The 10 micrometer size does not represent a strict boundary between respirable and
non-respirable particles, but has been agreed upon for monitoring of airborne particulate matter by most regulatory agencies.
Similarly, particles smaller than 2.5 micrometres, PM2.5, tend to penetrate into the gas-exchange regions of
the lung, and very small particles (< 100 nanometers) may pass through the lungs to affect other organs. In particular, a
study published in the Journal of the American Medical Association indicates that PM2.5 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 [1]. Researchers suggest that even short-term exposure at elevated concentrations could significantly
contribute to heart disease.
There is also evidence that particles smaller than 100 nanometres can pass through cell membranes. For example, particles may
migrate into the brain. It has been suggested that particulate matter can cause similar brain damage as that found in
Alzheimer patients. Particles emitted from modern diesel engines (commonly referred to as Diesel Particulate
Matter, or DPM) are typically in the size range of 100 nanometres (0.1 micrometres). In addition, these
soot particles also carry carcinogenic components like
benzopyrenes adsorbed on their surface. It is becoming increasingly clear that the
legislative limits for engines, which are in terms of emitted mass, are not a proper measure of the health hazard. One particle
of 10 µm diameter has approximately the same mass as 1 million particles of 100 nm diameter, but it is clearly much less
hazardous, as it probably never enters the human body - and if it does, it is quickly removed. Proposals for new regulations
exist in some countries, with suggestions to limit the particle surface area or the particle number.
The large number of deaths and other health problems associated with particulate pollution was first demonstrated in the early
1970s [2] 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) [3] and 200,000 deaths per year in Europe).
Regulation
Due to the health effects of particulate matter, maximum standards have been set by various governments. Many urban areas in the U.S. and Europe still frequently violate the particulate standards, though urban air on
these continents has gotten cleaner, on average, with respect to particulates over the last quarter of the 20th
century.[citation needed]
United States
The United States Environmental Protection Agency (EPA)
sets standards for PM10 and PM2.5 concentrations in urban air. (See National Ambient Air Quality Standards.) EPA regulates primary particulate
emissions and precursors to secondary emissions (NOx, sulfur, and ammonia).
EU legislation
In directives 1999/30/EC and 96/62/EC, the European Commission has set limits for PM10 in the air:
|
Phase 1
from 1 January 2005
|
Phase 2¹
from 1 January 2010
|
| Yearly average |
40 µg/m³ |
20 µg/m³ |
Daily average (24-hour)
allowed number of exceedences per year.
|
50 µg/m³
35
|
50 µg/m³
7
|
¹ indicative value.
Affected areas
| Most Polluted World Cities by PM[4] |
Particulate matter,
μg/m3 (2004) |
City |
| 169 |
Cairo, Egypt |
| 161 |
Beijing, China |
| 150 |
Delhi, India |
| 128 |
Kolkata, India (Calcutta) |
| 125 |
Taiyuan, China |
| 123 |
Chongqing, China |
| 109 |
Kanpur, India |
| 109 |
Lucknow, India |
| 104 |
Jakarta, Indonesia |
| 101 |
Shenyang, China |
The most concentrated particulate matter pollution tends to be in densely populated metropolitan areas in developing
countries. The primary cause is the burning of fossil fuels by transportation and industrial sources.
U.S. counties violating national PM
2.5 standards, roughly correlated with population density.
U.S. counties violating national PM
10 standards.
Aerosol science
The field of aerosol science and technology has grown in response to the need to
understand and control natural and manmade aerosols.
References
- ^ Pope, Arden C; et al. (2002). "Cancer, cardiopulmonary mortality, and long-term exposure to fine
particulate air pollution". J. Amer. Med. Assoc. 287: 1132-1141.
- ^ Lave, Lester B.; Eugene P. Seskin
(1973). "An Analysis of the Association Between U.S. Mortality and Air Pollution". J. Amer. Statistical Association
68: 342.
- ^ Mokdad, Ali H.; et al. (2004).
"Actual Causes of Death in the United States, 2000". J. Amer. Med. Assoc. 291 (10): 1238.
- ^ http://siteresources.worldbank.org/DATASTATISTICS/Resources/table3_13.pdf
Further Reading
See also
External links
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