Justification of an Air Quality Standard for Carbon
Monoxide
- It is clear from the foregoing that the highest exposures in the
ambient outdoor air likely to be experienced by non-smokers will occur
from peak concentrations close to heavy motor traffic, especially
during cold still conditions in winter. Regular smokers are unlikely
ever to be affected by such conditions, since their blood levels of
carboxyhaemoglobin are already higher than can be reached by breathing
polluted outdoor air (see Table 1),
and therefore the recommendation for an Air Quality Standard for carbon
monoxide is intended to limit exposure of non-smokers. After reviewing
the large amount of evidence on the health effects of carbon monoxide,
the Panel have concluded that the people most susceptible to exposure
to carbon monoxide are those with angina and disease of the coronary
arteries. The evidence suggests that the lowest level of carboxyhaemoglobin
at which effects can be detected in such people lies between 3 and
4%. The Panel have therefore concluded that ambient atmospheric concentrations
of carbon monoxide should be such that the concentration of carboxyhaemoglobin
in the blood of people breathing that air over a prolonged period
should not exceed 2.5%, thus allowing a safety margin.
- It is possible to relate blood carboxyhaemoglobin
levels to atmospheric concentrations of carbon monoxide
by use of mathematical formulae. This relationship shows
that carboxyhaemoglobin concentrations would be kept
below 2.5% when breathing the following concentrations of
carbon monoxide at maximum levels of activity:
10 ppm for 8 hours
25 ppm for 1 hour
50 ppm for 30 minutes
87 ppm for 15 minutes.
- It is apparent from the results of air monitoring
referred to above that an 8-hour standard provides the
tightest control. The Panel therefore recommend an Air
Quality Standard for carbon monoxide in the United
Kingdom of 10 ppm. In order to ensure that maximum
concentrations are not missed by arbitary averaging
periods, we recommend that a running 2
8-hour average be used for the Standard.
2 Running
8-hour average carbon monoxide concentrations are calculated
by first calculating the hourly average carbon monoxide
concentrations over fixed periods from 00.00 to 00.59
onwards. These averages are then taken consecutively in
groups of eight and the 8-hour averages are calculated for
00.00 - 07.59, 01.00 - 08.59 etc onwards.
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Published 29 October 1998
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