Journal of Environmental Studies
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Commentary
Semipalatinsk Nuclear Test Site: Morbidity and Mortality in Adjacent Area
Jargin SV*
Department of Pathology, People’s Friendship University of Russia, Russian Federation USSR
*Address for Correspondence:Jargin SV, Department of Pathology, People’s Friendship
University of Russia, Russian Federation USSR. E-mail Id: sjargin@mail.ru
Submission:02 October, 2024
Accepted:28 October, 2024
Published:05 November, 2024
Copyright: © 2024 Jargin SV. This is an open access article
distributed under the Creative Commons Attribution License,
which permits unrestricted use, distribution, and reproduction
in any medium, provided the original work is properly cited.
Keywords:Ionizing Radiation; Semipalatinsk Nuclear Test Site; Lung
Cancer; Cardiovascular Diseases
Abstract
This commentary is focused on morbidity and mortality in the
population residing near the Semipalatinsk Nuclear Test Site. An
explanation for higher detection rates and registered mortality of cancer
and other deceases is the better coverage of exposed populace by
medical examinations and autopsies as well as increased attention
of the residents to their own health. Being informed about benefits
provided by the government, some patients from non-contaminated
territories registered themselves as exposed. The radiation background
in the test site area is normal long-since. Studies of human populations
exposed to low-dose radiation will hardly add reliable information on
dose-effect relationships. Screening effect, selection and ideological
bias will contribute to appearance of new reports on enhanced risks
from anthropogenic elevation of the radiation background, which
would not prove causality. Reliable results can be obtained in lifelong
animal experiments. Numerous publications exaggerating medical
consequences of elevated radiation background appeared after
the Chernobyl accident. Manipulations with statistics have been not
unusual, which should be taken into account by authors of reviews and
meta-analyses. In the beginning, heated interest facilitated foreign aid
and international scientific cooperation. Later on, other motives have
come to the fore: anti-nuclear resentments hindered development of
nuclear power in some countries, thus boosting fossil fuel prices.
Introduction
Since many years we have tried to show that certain scientific
writers and environmental activists act in accordance with the
interests of governments selling fossil fuels [1,2]. The overestimation
of adverse effects of nuclear power production leads to its
strangulation, supporting appeals to eliminate nuclear power plants
(NPPs). The cost of dismantling each NPP may amount to billions of
dollars [3]. The use of atomic energy is on the agenda today due to
increasing needs of the growing humankind. Nuclear energy holds a
promise of an abundant, clean, affordable and almost inexhaustible
source of energy [4]. Fuelled by the Chernobyl accident in 1986,
environmentalist movements mobilized political forces, which made
nuclear energy untenable in some countries [5]. At the same time,
the accident contributed to destabilization of the Soviet society with
subsequent privatization of the state property by the Soviet rulers, so called
nomenklatura.
Among the causes of the Chernobyl disaster was non-compliance
with instructions and safety rules. The number of control rods in the
reactor was about a half of the minimum required for a safe functioning
[6]. An emergency power system had been shut off, which is forbidden
during on-line operation [7]. According to the literature, this was done
to carry out an experiment [6,8], which might be a pretext to cover
sabotage; certainly, not by the control-room personnel but by some
upper management. Most international regimes channel liability to
the person in control of an environmentally damaging activity. In the
case of nuclear pollution, it is the operator of NPP. Persons in control
of the harmful activity should bear the costs of inflicted damage [9].
These days, the single most important consideration against nuclear
facilities is that they are potential war targets. Accordingly, military
threats are arguments against NPPs. Escalation of military conflicts
contributes to boosting fossil fuel prices. This might have been one of
the motives to unleash the Ukraine war [10]. The Chernobyl disaster
has been exploited for the same purpose. Considering vulnerability
of large NPPs during armed conflicts, attention should be directed
to smaller nuclear reactors, which have some economic advantages.
Small reactors can be used also by the military [11].
Focused review:
The overestimation of ecological and medical consequences of
Chernobyl accident and radioactive contaminations in the Urals
were discussed previously [1,2]. A similar tendency has been noticed
in regard to nuclear tests in the former Soviet Union (SU) [12].
The Semipalatinsk Test Site (STS) in today’s Kazakhstan was the
place where 456 nuclear explosions were carried out between 1949
and 1989, including 111 atmospheric tests in the period 1949-1962
[13]. STS was shut down in early 1990s. The villages most affected
by the atmospheric tests were located northeast of STS. The wellknown
cytogenetics expert Yuri Dubrova stated that “according to
the results of numerous studies the doses for the families living in
the Semipalatinsk District of Kazakhstan have been estimated as 0.5
Sv and higher” [14] with reference to the review [15]. However, in
the abstract of the latter review it is written: “The village of Dolon,
in particular, has been identified for many years as the most highly
exposed location in the vicinity of the test site. Previous publications
cited external doses of more than 2 Gy to residents of Dolon while
an expert group assembled by the WHO in 1997 estimated that
external doses were likely to have been less than 0.5 Gy” [15]. Earlier
publications estimated maximum external doses for adult residents
of Dolon at 1.3 Sv [16] or 0.63 Gy (with a remark that integral
exposures at Dolon may have been less than estimated) [17]. Other
experts reported lower doses [18]. Apparently, the single historical
measurement was performed at the axis of the radioactive trace
about 1.5-1.6 km northwest of Dolon, while the width of the cloud
was narrow [19,20]. The dose estimate based on this measurement
is believed to be a maximum rather than average for Dolon residents
[19], while in other villages the doses were much lower. The average
individual dose estimates for townships near STS, received in the
period 1949-1953, have been estimated as follows: Dolon 1600 mGy,
Abai 370, Kainar - 240, Sarzhal - 200, some other villages - 5-20
and Semipalatinsk city ≤ 5.6 mGy. In the period 1971-1990 annual
individual doses in the area were ≤5 mGy [21]. In 2008 the annual
individual dose in the STS compound was 0.073-0.749 mSv and
outside STS - 0.036-0.37 mSv [22], which is a negligible addition
to the natural radiation background (NRB). The worldwide annual
exposures to NRB are generally expected to be in the range 1-10 mSv
but can be higher [23,24]. There are populated areas in the world
where dose rates from the NRB are 10-100-fold higher than the global
average (2.4 mSv/year) with no health risks reliably proven [25].Dubrova et al. stated that individuals, from whom the specimens
for genetic analysis were collected “around the Semipalatinsk nuclear
test site... characterized by the highest effective doses of exposure to
ionizing radiation (>1 Sv)” [26], which is at variance with the dose
comparisons above. Furthermore, Dubrova argued that Jargin [27]
“makes a very serious accusation stating that ‘statistics with unknown
levels of significance’ was used in our publications [14,28]. I would
like to stress that the main result of these two studies, showing
significantly elevated mutation rate in the germline of irradiated
parents, was verified by means of the most conservative statistical test
- Fisher’s exact test” [14]. However, in the letter [27] it was written
that negative correlation between the mutation rate and a paternal
year of birth among inhabitants of Semipalatinsk area is claimed
without providing the value of the correlation coefficient and its level
of significance [26,29]. Considering configuration of diagrams in [29],
this correlation may be insignificant [27]. Nevertheless, a discussion is
led on its basis, e.g.: “Most importantly, this correlation provides the
first experimental evidence for change in human germline-mutation
rate with declining exposure to ionizing radiation and therefore
shows that the Moscow treaty banning nuclear weapon tests in the
atmosphere (August 1963) has been effective in reducing genetic
risk to the affected population” [14]. The above-cited argumentation
from [27] remained unanswered. Moreover, the Fisher’s exact test,
mentioned in the reply by Dubrova [14], is not used for the evaluation
of the level of significance of correlation coefficients.
The tendency to overestimate medical consequences of enhanced
background radiation in the Semipalatinsk area can be exemplified by
the international study [30]. The following was stated in the abstract:
“17 patients (group 1) lived close to the testing area from the childhood
to 1993 and were exposed to the radiation at the year dose 0.1 ber.”
A radiation dose unit “ber” (Biological Equivalent of Rad), used in
Russia, is designated internationally as rem. The annual individual
dose of 0.1 rem (1 mSv) is below the global average for annual doses
from NRB, which is 2.4 mSv. The term “radiogenic carcinoma” was
used for cancers of unknown etiology. Unfounded suppositions
about their rapid growth and “poor prognosis” were made [30]. The
study was based on two sets of tissue specimens from patients with
lung carcinoma: the “exposed” group - 17 cases from the area of
Semipalatinsk, and the control (40 specimens). Cumulative doses were
unknown. The following data are remarkable (from Russian): “The
specific cytogenetical feature of the lung carcinoma in patients from
the area of Semipalatinsk was the neuroendocrine differentiation of
cancer cells in all tumors independently of their histological structure.
We have established it by means of immunohistochemical and
ultrastructural investigations.” At the same time, “no neuroendocrine
differentiation was shown in the control group.” It means that the
marker was found by two methods in 100 % (17/17) of the cases and
in 0 % (0/40) of controls. The extremely high level of significance
(P<0.0001) agrees with the supposition that the “lung cancer in
persons exposed for a long time to radionuclide radiation pollution”
[30] is a distinct entity, different from spontaneous lung carcinoma.
Significant differences between the two groups were found also for
other markers, which additionally enhanced statistical significance
of the difference. It was concluded that “lung carcinoma in patients,
who resided in the area of Semipalatinsk and underwent elevated
radioactivity, can be classified as neuroendocrine carcinoma” [30]. In
the general population, tumors from neuroendocrine cells (small cell
carcinoma and carcinoids) represented at that time 20-30 % of lung
malignancies [31]. The age and sex data in the “exposed” group were
typical for spontaneous cancer possibly caused by cigarette smoking
or industrial air pollution: 15 from 17 patients were 51-70 years old.
Patients with radiation-induced cancer could be younger. In particular,
spontaneous lung cancer is characterized by male predominance due
to cigarette smoking and professional carcinogens. Radiation would
exert a similar effect on both genders. In the “exposed” group there
were 16 males and one female [32]… The designation “radiogenic
carcinoma” and discussion of its supposedly rapid growth and poor
prognosis [30] contributed to exaggeration of medical consequences
of low-dose exposures. Papers of this kind, similarly to those about
Chernobyl and radioactive contaminations in the Urals [1,2], often
have limitations: interpretation of spontaneous diseases as radiationinduced,
indication of dose levels without comparison with the NRB,
conclusions about incidence increase without correct comparisons
with a control. Other studies on STS and Chernobyl by the same
authors [33-36] are characterized by similar limitations. For example,
a discussion of molecular markers of “radiogenic cancer” is led on the
basis of 15 random autopsy and surgical cases of lung cancer from the
areas quite distant from Chernobyl: eight cases were from the Tula
province in Russia [33].
Studies discussed above illustrate the approach persisting until
today. Biased researchers have just gathered experience and learned
to formulate their reports ambiguously to evade criticism. Despite
the low average doses, long-since within limits of NRB, residents of
the Semipalatinsk area are designated as “exposed to radiation” [37-39].
Admittedly, some nuclear tests, conducted from 1949 to 1956,
resulted in non-negligible external doses [40]. However, the last
atmospheric test at STS was performed in 1962, and underground
test in 1989 [41]. After the 1963 Partial Test Ban Treaty, the nuclear
testing was restricted to underground so that, with a few exceptions,
little or no off-site environmental contamination was caused. The
exceptions included cratering events in the period 1965-1968 [41].
To calculate the external cumulative dose, it is generally sufficient to
take into account residence history during the first year following a
nuclear test [40].
The medical and ecological research about STS is associated with
limitations and confounding factors. Studies are not well connected
with each other. Biological specimens were not always properly
stored and labeled, individual migration and residence histories
often unknown [13]. In regard to cancer, the morbidity and mortality
in exposed people were reported to exceed those in control groups
[42]. This problem has been discussed with regard to radioactive
contaminations in Chernobyl and the Urals [1,2]. An explanation
for higher detection rates and mortality from cancer and other
diseases in the exposed populations is the better coverage by medical
examinations (including post mortems) and increased attention of
exposed individuals to their own health: the selection and self-selection
bias. Undiagnosed cancers are often found at autopsies. Besides,
people knew about the Kazakhstani law “Social protection of citizens
who suffered as a result of nuclear tests conducted at the STS” [39];
not surprisingly, some patients from non-contaminated areas have
been falsely registered as exposed. It is feasible under conditions of
corruption. The circumstantial evidence thereof is a marked increase
in the incidence of diseases, unrelated to radiation on the face of it,
in contaminated compared to “clean” territories. For example, the
incidence of tuberculosis in children in the Semipalatinsk province
was 1.5 times higher than in the whole Kazakhstan with a threefold
higher frequency of severe and complicated cases [43]. Remarkably,
the incidence of neoplasia in children of exposed parents was found
to be nearly fourfold higher than among controls: 92.6 vs. 24.7 per
1000 children [44]. At least in part, this was caused by diseased
children brought from non-contaminated areas and registered as
radiation-exposed. Moreover, oncologic patients tend to recollect the
circumstances related to radiation better than healthy controls (recall
bias) [45], thus getting higher dose estimates, contributing to dose effect
correlations.
Several publications discussed the enhanced morbidity and
mortality from cardio- and cerebro-vascular diseases in people
residing near STS [46]. Admittedly, no direct conclusions on cause effect
relationships are made in recent papers [37-39]. When account
was taken of the difference in baseline rates between the exposed
and unexposed groups, no statistically significant dose-response
relationship was observed either for cardiovascular diseases (CVD)
or for stroke [46,47]. This is in agreement with the fact that no dose response
relationship for circulatory diseases among the atomic
bomb survivors in Japan (life span study – LSS) was observed at doses
≤0.5 Gy [46,48,49]. The selection, self-selection and recall bias were
probably active also in LSS, contributing to higher risk estimates.
Furthermore, there are confounding factors preventing
reasonable interpretation of medical statistics from some countries
of the former SU. Like in Russia, CVD mortality in Kazakhstan is
higher compared to West Europe [50]. The causes thereof are known
by anatomic pathologists. Since the Soviet time, the autopsy remained
obligatory for patients dying in hospitals but the quality deteriorated.
Post mortem examinations were often made perfunctorily. The
quality decrease in anatomic pathology during the 1990s coincided
with the increase in the registered CVD mortality. If a cause of death
is not entirely clear, it has been usual to write on a death certificate:
“Ischemic heart disease with cardiac insufficiency” or a similar
formulation. It is known that ill-defined cardiovascular codes from
the International Statistical Classification of Diseases (ICD) are used
in cases with insufficient clinical information. The frequent cause of
cardiovascular death in some countries of the former SU has been
“coronary atherosclerosis”. The nonstandard disease classifications
used in Russia complicated the evaluation of medical statistics
[51]. It has been noted in the recent review that a “diagnosis (by a
physician knowing the patient’s history) could vary with dose” [52].
The tendency that radiation-exposed people are on average more
thoroughly examined was noticed [1,2]. Finally, manipulation with
statistics following official or unofficial directives has been widespread
in Russia [53]. This human factor has remained largely unchanged.
A tendency to over-diagnose CVD is generally known also for
people dying at home and not undergoing post mortem examination.
It can be confirmed by the following: “Increases and decreases
in mortality related to CVD… but not to myocardial infarction,
the proportion of which in Russian CVD mortality is extremely
low” [54]. The diagnosis of myocardial infarction is usually based
on clinical or morphological criteria, while the diagnoses of
ischemic heart disease and coronary atherosclerosis are often used
post mortem without strong evidence. Furthermore, contrary to
myocardial infarction, gross features of ischemic brain infarction
were sometimes mimicked destroying brain tissue using autopsy
knife by a pathologist or postgraduate student not inclined or unable
(for a lack of toxicological tests) to search for the true cause of death
even at university mortuaries let alone peripheral institutions. The
post-mortem diagnosis of stroke has been overused for poisonings,
especially with alcoholic beverages and surrogates [55]. Along with
inadequate treatment of arterial hypertension, this was probably the
cause of higher reported stroke mortality in Russia compared to other
developed countries [56,57].
Dose levels associated with cancer or CVD in animal experiments
and in humans after radiotherapy have been higher than averages
in the cohorts from contaminated areas of the former SU; details
and references are in [1,2]. Results of experiments are generally
not supportive of detrimental effects of low doses, with possible
exception of genetically modified cancer-prone animals. In humans
after radiotherapy, myocardial fibrosis developed after exposures
≥30 Gy. An increased risk of coronary disease has been reported
after radiotherapy with doses 7.6-18.4 Gy [58], which is still much
higher than averages in the exposed cohorts discussed above. In
certain experimental and epidemiological studies, low doses turned
out to be protective against CVD and other adverse effects. There
is considerable evidence in favor of hormesis, summarized in [1,2].
Unrealistic CVD risks at low-dose exposures call in question cancer
risks reported by the same and other researchers. A major part of
the literature about STS is characterized by large volume, abundant
details and mathematical computations, but no clear insight into
medical consequences of contamination. Papers on dosimetry
or retrospective dose estimation contain discourses e.g. about
diets of different ethnic communities, living in or relocated to the
Semipalatinsk area; but provide no clear information on radiation
doses, morbidity and mortality. Along with other ethnic groups,
more than 440,000 Germans were deported to Kazakhstan during
1941-1945 [59] including the subsequently contaminated areas near
STS [46,60].
Mechanisms of damage at low doses remain speculative and the
evidence inconclusive [61,62]. Summarizing the above and previously
published arguments [1,2], the harm caused by anthropogenic
radiation would tend to zero with a dose rate decreasing down to
NRB. The damage and repair are normally in a dynamic balance.
Accordingly, there must be an optimal exposure level, as it is for
many environmental agents: visible and ultraviolet light, various
chemical elements and compounds. Evolutionary adaptation to a
changing environmental factor would lag behind its current value
and correspond to some average from the past. NRB has been
decreasing during the time of life existence on Earth [63]. There are
many substances and physical factors in the environment that are
toxic at some dose level. The lower would be anthropogenic exposure,
the less would be its significance compared to NRB and other factors.
Numerous publications exaggerating medical consequences
of elevated radiation background appeared after the Chernobyl
accident. The motives have been discussed previously [1,2]. In the
beginning, heated interest to Chernobyl facilitated foreign aid and
international scientific cooperation. Radiophobia hindered the
development of nuclear power in many countries, thus boosting fossil
fuel prices. Certain publications apparently served two purposes:
fostering radiophobia [Figure 1,2] by truisms about
radiation-related health risks and, at the same time, obfuscating
real consequences of long-term contaminations in the Urals and
Semipalatinsk areas. It seems that some writers, exaggerating medical
and ecological consequences of the anthropogenic increase in the
radiation background, do not realize that they serve the interests of
fossil fuel producers. Some of them may have good intentions; others
are ideologically biased, serve certain companies or governments.
Today there are no alternatives to nuclear power. The energy carriers
will become increasingly expensive in the long run, contributing to
excessive population growth in fossil fuel producing countries, and
poverty elsewhere. The global development of nuclear energy must be
managed by an international executive based in developed countries.
[64].
Conclusion
Limitations of many publications about STS include lacking
consideration of bias and confounding factors [65]. Some reviews
analyzed together papers of different quality and reliability. The
heterogeneity complicates causal interpretation of results [62,66].
As discussed here and elsewhere, political and economical interests
sometimes overweighed scientific objectivity [1,2]. Dose-effect
relationships should be clarified in experiments with known doses and
dose rates. Animal studies can provide reliable information. Further
work with different species would quantify their radiosensitivity
and enable more precise extrapolations to humans. Studies of
human populations exposed to low-dose ionizing radiation, though
important, will hardly add much reliable information on dose-effect
relationships. Screening effect, selection, self-selection and ideological
bias will contribute to appearance of new reports on enhanced risks
from a moderate anthropogenic increase in the radiation background,
which would not prove causality. Manipulations with statistics have
been not unusual in the former SU [53], which must be taken into
account by authors of reviews and meta-analyses.
Conflicts of interest:
The author has no conflicts of interest to declare.