Sources of Carbon Monoxide
- Carbon monoxide is produced by the incomplete
combustion of organic substances or those that are
essentially just carbon, such as coke. Complete
combustion, in the presence of sufficient oxygen, leads
to production of carbon dioxide, whereas if there is a
slight deficiency of oxygen some carbon monoxide is
formed. Thus most combustion processes produce some
carbon monoxide, depending on the efficiency of the
process and the availability of oxygen. From the point of
view of human health, some forms of exposure to carbon
monoxide are particularly important. For example, in some
industrial processes and in coal mines, pockets of high
concentrations of carbon monoxide may occur and cause
serious health effects. In the home, gas cookers,
paraffin heaters and bottled gas heaters operating in
poorly ventilated rooms, or badly installed or maintained
flued gas, oil or solid fuel heaters may cause high
levels of carbon monoxide in the air, leading to
lassitude, unconsciousness or even death. In suicide bids
the role of the carbon monoxide contained either in town
gas, prior to the introduction of natural gas, or in
motor car exhaust gases is well known; as are the dangers
of carbon monoxide to those, including fire fighters,
involved in fires in buildings or other confined
spaces.
- Apart from the major accidental and domestic sources
of comparatively high levels of carbon monoxide, the most
important general exposures of individuals to the gas
come from cigarettes and vehicles. Cigarettes are mainly
responsible for exposure of smokers, although some
passive exposure of others will occur from inhalation of
other people's smoke indoors. The amount of carbon
monoxide in the blood of a regular smoker is considerably
greater than that which can be obtained by breathing air
in even heavily polluted streets (see
Table 1), and therefore, the recommended Air Quality
Standard for carbon monoxide aims to limit the exposure
of non-smokers. For non-smokers, the main source of
outdoor exposure to carbon monoxide is general pollution
of the atmosphere by vehicle exhausts. As far as total
exposure is concerned, again for non-smokers, indoor
sources can account for a larger proportion than
traffic.
Table 1 Average blood
carboxyhaemoglobin* (COHb) levels in persons exposed to
carbon monoxide
|
|
COHb%
|
|
Non-smokers
|
Smokers
|
|
Calculated values:
|
|
|
|
Rural background exposure
|
0.5**
|
-
|
|
Urban exposure to 10 ppm***
|
1.0
|
-
|
|
Urban exposure to 25 ppm***
|
2.7
|
-
|
|
|
|
Measured values****
|
|
|
|
Urban background exposure
|
0.8
|
3.5
|
|
Point-duty police (after 3 hours in busy
street)
|
1.9
|
3.6
|
|
Others on foot in busy streets
|
1.2
|
-
|
|
Cyclists (city streets)
|
1.7
|
-
|
|
Motorists
|
1.8
|
-
|
|
Staff in parking garages
|
2.4
|
5.0
|
|
Staff in customs sheds, ferries
|
1.3
|
4.2
|
|
*
|
The absorption of carbon monoxide results in the
formation of carboxyhaemoglobin in the blood.
|
|
**
|
This represents the background value due to the
natural formation of carbon monoxide in the
body.
|
|
***
|
These values are estimated from Figure 4 (see
page 22), on the assumption that the individual is
undertaking light activity whilst continuously
exposed to the stated concentration of carbon
monoxide for a period of 8 hours. In reality, such
exposures are unlikely to occur in ambient air
since the measured value would vary depending both
on the individual and the circumstances of
exposure. The concentration of 25 parts per million
(ppm) is not exceeded in ambient air nowadays in
the United Kingdom.
|
|
****
|
Adapted from Lawther and Commins, 1970. Values
of blood COHb measured in the 1960s in groups of
between 5-165 persons. Levels of carbon monoxide in
urban areas in the United Kingdom have decreased
significantly since then and levels of COHb in
blood are expected to be lower nowadays.
|
- Combustion systems in vehicles are normally designed
to operate most efficiently when there is just enough air
to oxidise the carbon in the fuel. When the engine is
cold or badly tuned, or when the engine is idling or
moving slowly, it will depart from this optimal condition
and produce more carbon monoxide.Thus it might be
anticipated that levels of the gas in the ambient air
would be highest close to busy roads in cities,
especially when traffic flow is reduced as in rush hours.
Atmospheric conditions, such as the periods of cold still
air occurring at times in winter, may of course prevent
the dispersal of this and other gases, leading to higher
concentrations. Carbon monoxide emitted by motor vehicles
in urban areas is normally rapidly dispersed away from
roads and then is destroyed by photochemical reaction
over a period of months.
- In the United Kingdom, it has been estimated that
some 6.7 million tonnes of carbon monoxide are emitted
into the atmosphere each year, and that 87% of this comes
from petrol-engined vehicles. The relative contributions
of different sources are shown in Table
2. In line with the increase in traffic, there has
been an increase in these emissions of approximately 50%
from the 1970 values (see Figure 1). Recently, there has
been evidence of a decline in vehicle emissions,
following increasingly strict European Community
directives. Improved engine design, with fuel injection
and engine management systems, the introduction of
catalytic converters, and the adoption of emission
standards in the annual MOT test will reduce levels
further, although this favourable trend will be opposed
by any increases in traffic.
Table 2 Estimated United Kingdom
emissions of carbon monoxide by emission source, 1990-92,
thousand tonnes per year*
|
Source
|
1990
|
1991
|
1992
|
Percentage of total in 1992**
|
|
Road transport:
Petrol
Diesel
|
6,152
157
|
6,140
164
|
5,865
164
|
87
2
|
|
Power stations
|
50
|
47
|
45
|
1
|
|
Domestic
|
286
|
293
|
258
|
4
|
|
Commercial/public service
|
8
|
8
|
7
|
-
|
|
Refineries
|
1
|
1
|
2
|
-
|
|
Iron and steel
|
28
|
26
|
25
|
-
|
|
Other industrial combustion
|
41
|
42
|
42
|
1
|
|
Extraction and distillation of fossil fuels
|
33
|
35
|
36
|
1
|
|
Waste treatment and disposal
|
220
|
220
|
220
|
3
|
|
Railways
|
12
|
12
|
12
|
-
|
|
Aircraft
|
11
|
11
|
11
|
-
|
|
Shipping
|
20
|
20
|
19
|
-
|
|
Agriculture
|
1
|
1
|
1
|
-
|
|
Total
|
7,020
|
7,021
|
6,708
|
100
|
* Figures rounded tothe
nearest 1,000tonnes.
** Figures rounded to the nearest
1%.
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Published 29 October 1998
Expert Panel on Air Quality Standards
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