radiation (nuclear industry workers, medical personnel,
medical diagnostic exposure, etc.).
Low-dose risks are assessed for risk-management
purposes by extrapolating the risks observed at higher
doses. This calculation gives an estimate of the risks
entailed by exposure to low doses of ionising radiation.
For these estimates, the prudent hypothesis of a linear
no-threshold relationship between exposure and
the number of deaths from cancer has been adopted
internationally. This hypothesis implies that there is
no dose threshold below which one can assert that
there is no effect. The legitimacy of these estimates and
of this hypothesis nevertheless remains scientifically
controversial, as very large scale studies would be
necessary to further support the hypothesis.
On the basis of the scientific syntheses of UNSCEAR
(see box page 49), the International Commission on
Radiological Protection – ICRP (see publication ICRP 103,
chapter 3, point 1.1.1) has published risk coefficients for
death from cancer due to ionising radiation, showing a
4.1% excess risk per sievert (Sv) for workers and 5.5%
per sievert for the general public.
The evaluation of the risk of lung cancer caused by
radon (radon is a naturally occurring radioactive gas
– a decay product of uranium and of thorium – which
emits alpha particles and is classified by the IARC as a
definite human carcinogen) is based on a large number
of epidemiological studies performed directly in the
home, in France and internationally. These studies have
revealed a linear relationship, even at low exposure
levels (200 becquerels per cubic metre (Bq/m
3
)) over a
period of 20 to 30 years. TheWorld Health Organisation
(WHO) has synthesised the studies and recommends a
maximum annual exposure level of between 100 and
300 Bq/m
3
for the general public. The ICRP
(Publication 115)
compared the risks of lung cancer
observed through studies on uraniumminers with those
observed on the general population and concluded that
there was a very good correlation between the risks
observed in these two conditions of exposure to radon.
The ICRP recommendations confirm those issued by
the WHO which considers that, after tobacco, radon
constitutes the highest risk factor in lung cancer.
In metropolitan France, about 19 million people
spread over some 9,400 municipalities are potentially
exposed to radon. According to InVS (French Health
Monitoring Institute) figures from 2007, between
1,200 and 2,900 deaths from lung cancer can be attributed
each year to radon exposure in the home, that is to say
between 4 and 10% of deaths due to cancer. A national
action plan for managing radon-related risks has been
implemented since 2004 on the initiative of ASN and is
updated periodically (see point 3.2.2).
The latest publication of the International
Agency for Research on Cancer – IARC (2015)
on cancer mortality rate of workers employed
in the nuclear industry*
The publication in 2015 by the WHO (IARC, Lyon,
www.iarc.fr)of the cancer mortality rate for French, American
and British workers employed in the nuclear industry
(fuel preparation, research, electricity production, spent fuel
reprocessing) and having worn personal dosimeters, has provided
greater insight into the external irradiation risks which, although
low, accumulate over the working life. The studied population
included nearly 300,000 workers, of which the French cohort
comprised 59,000 workers from Areva NC, CEA and EDF.
The average monitoring time of these workers was twenty-
seven years. The average dose is 25 mSv cumulated over the
working life (fifteen years on average). The mean annual dose
is less than 2 mSv. 94% of the individuals had a cumulative
total of less than 100 mSv. Among the 6% of individuals whose
cumulative dose exceeded 100 mSv, 75 % started working in
the 1970’s and their mean cumulative dose is 223 mSv.
A first publication in June 2015 showed an increase in the risk
of leukemia as a function of the cumulative dose. A second
publication in October 2015 shows that the risk of cancers
other than leukemias also increases as a function of the
cumulative dose, that is to say about 4% for an increase of
100 mSv.
These results were observed from a total of 66,600 deaths,
of which 19,064 were due to cancers other than leukemias.
From the estimated dose-risk relationship, it appears that the
proportion of deaths that can be attributed to external exposure
to radiation within this population of workers is about 1% of
all the observed 19,064 deaths due to cancers other than
leukemias.
The observed relationship is stable (little heterogeneity between
the countries, small-amplitude variations in the sensitivity
analyses). To evaluate the existence of a potential bias due to
tobacco, lung cancers were excluded from the analysis; this
exclusion had little impact on the risk estimate.
The dose-risk relationship observed is consistent with those
observed in other studies, particularly those of the Hiroshima
and Nagasaki survivors and shows that the risk at low doses
spread over time does not differ from that observed for the
same irradiation dose received in a few seconds.
TO BE NOTED
* The new results concerning the risk of death by cancer other
than leukemia were published in the
British Medical Journal
;
those on the leukemia risk were published in the
Lancet
.
48
CHAPTER 01:
NUCLEAR ACTIVITIES: IONISING RADIATION AND HEALTH AND ENVIRONMENTAL RISKS
ASN report on the state of nuclear safety and radiation protection in France in 2015




