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A 2011 review of studies addressing childhood leukaemia following exposure to ionizing radiation, including both diagnostic exposure and natural background exposure from [[radon]], concluded that existing risk factors, excess [[relative risk]] per sievert (ERR/Sv), is "broadly applicable" to low dose or low dose-rate exposure, "although the uncertainties associated with this estimate are considerable". The study also notes that "epidemiological studies have been unable, in general, to detect the influence of natural background radiation upon the risk of childhood leukaemia"<ref>{{cite journal | vauthors = Wakeford R | title = The risk of childhood leukaemia following exposure to ionising radiation--a review | journal = Journal of Radiological Protection | volume = 33 | issue = 1 | pages = 1–25 | date = March 2013 | pmid = 23296257 | doi = 10.1088/0952-4746/33/1/1 | bibcode = 2013JRP....33....1W | s2cid = 41245977 }}</ref>
A 2011 review of studies addressing childhood leukaemia following exposure to ionizing radiation, including both diagnostic exposure and natural background exposure from [[radon]], concluded that existing risk factors, excess [[relative risk]] per sievert (ERR/Sv), is "broadly applicable" to low dose or low dose-rate exposure, "although the uncertainties associated with this estimate are considerable". The study also notes that "epidemiological studies have been unable, in general, to detect the influence of natural background radiation upon the risk of childhood leukaemia"<ref>{{cite journal | vauthors = Wakeford R | title = The risk of childhood leukaemia following exposure to ionising radiation--a review | journal = Journal of Radiological Protection | volume = 33 | issue = 1 | pages = 1–25 | date = March 2013 | pmid = 23296257 | doi = 10.1088/0952-4746/33/1/1 | bibcode = 2013JRP....33....1W | s2cid = 41245977 }}</ref>

The U.S average background radiation dose from cosmic rays, radionuclides in soil and rock, from the food we eat, and indoor radon, is 3 mSv/year or 240 mSv per 80-year lifetime. Using the BEIR VII risk of 0.000114 per mSv implies a lifetime risk from background radiation of 240 x 0.000114 = 0.027 or 2.7%. This is substantially greater than EPA’s incremental lifetime cancer incidence risk goal of 10<sup>-6</sup>, and a substantial fraction of the inherent U.S. cancer incidence risk of approximately 42%. If the EPA and medical community truly believed that 2.7% is the cancer risk from background radiation, then it should proclaim that to the world, and watch Amazon’s sales of lead-lined clothing skyrocket.<ref>{{Cite web |last=Rutherford |first=Phil |date=September 10, 2007 |title=Linear No Threshold Model of Radiation Risk |url=https://www.etec.energy.gov/Library/Main/Radiation_Risk_LNT_Rev_A.pdf |url-status=live |access-date=November 19, 2023 |website=Department of Energy}}</ref> The LNT model of radiation risk together with EPA’s reliance on 10<sup>-6</sup> as a de facto “safe” limit for incremental lifetime cancer incidence risk, leads to some wildly implausible inferences. A 10<sup>-6</sup> increased cancer risk would be incurred by drinking an additional 0.4 teaspoons of orange juice each day for 30 years, due to its radioactive potassium-40 content. 10<sup>-6</sup> is the difference in radiation risk between the feet and head of a 6-foot person due to the difference in cosmic ray exposure. 10<sup>-6</sup> is the additional non-radiation fatal risk from driving an extra 1 mile per year for 30 years.<ref>{{Cite web |last=Rutherford |first=Phil |date=January 27, 2010 |title=Radiation Risks in Everyday Life |url=https://www.philrutherford.com/Conf_Papers/Radiation_Risks_in_Everyday_Life_Rev_1A.pdf |url-status=live |access-date=November 19, 2023 |website=Phil Rutherford Consulting}}</ref><ref>{{Cite web |last=Rutherford |first=Phil |date=November 18, 2018 |title=Linear No Threshold (LNT) Model of Radiation Risk |url=https://www.philrutherford.com/Radiation_Risk/Linear_No_Threshold.pdf |url-status=live |access-date=November 19, 2023 |website=Phil Rutherford Consulting}}</ref>


Several expert scientific panels have been convened on the accuracy of the LNT model at low dosage, and various organizations and bodies have stated their positions on this topic:
Several expert scientific panels have been convened on the accuracy of the LNT model at low dosage, and various organizations and bodies have stated their positions on this topic:

Revision as of 23:29, 19 November 2023

Different assumptions on the extrapolation of the cancer risk vs. radiation dose to low-dose levels, given a known risk at a high dose:
(A) supra-linearity, (B) linear
(C) linear-quadratic, (D) hormesis

The linear no-threshold model (LNT) is a dose-response model used in radiation protection to estimate stochastic health effects such as radiation-induced cancer, genetic mutations and teratogenic effects on the human body due to exposure to ionizing radiation.[1] The model statistically extrapolates effects of radiation from very high doses (where they are observable) into very low doses, where no biological effects may be observed. The LNT model lies at a foundation of a postulate that all exposure to ionizing radiation is harmful, regardless of how low the dose is, and that the effect is cumulative over lifetime.

The LNT model is commonly used by regulatory bodies as a basis for formulating public health policies that set regulatory dose limits to protect against the effects of radiation. The model has also been used in the assessment of cancer risks of mutagenic chemicals. The validity of the LNT model, however, is disputed, and other significant models exist: the threshold model, which assumes that very small exposures are harmless, the radiation hormesis model, which says that radiation at very small doses can be beneficial, and the supra-linear model based on observational data.[2] Whenever the cancer risk is estimated from real data at low doses, and not from extrapolation of observations at high doses, the supra-linear model is verified.[3] It has been argued that the LNT model may have created an irrational fear of radiation.[1][4]

Different organizations take different approaches to the LNT model. For example, the US Nuclear Regulatory Commission and United States Environmental Protection Agency endorse the model, while a number of other bodies deprecate it.[5] One of the organizations for establishing recommendations on radiation protection guidelines internationally, the United Nations Scientific Committee on the Effects of Atomic Radiation (UNSCEAR) that previously supported the LNT model, no longer supports the model for very low radiation doses.[6]

Introduction

Stochastic health effects are those that occur by chance, and whose probability is proportional to the dose, but whose severity is independent of the dose.[7] The LNT model assumes there is no lower threshold at which stochastic effects start, and assumes a linear relationship between dose and the stochastic health risk. In other words, LNT assumes that radiation has the potential to cause harm at any dose level, however small, and the sum of several very small exposures is just as likely to cause a stochastic health effect as a single larger exposure of equal dose value.[1] In contrast, deterministic health effects are radiation-induced effects such as acute radiation syndrome, which are caused by tissue damage. Deterministic effects reliably occur above a threshold dose and their severity increases with dose.[8] Because of the inherent differences, LNT is not a model for deterministic effects, which are instead characterized by other types of dose-response relationships.

LNT is a common model to calculate the probability of radiation-induced cancer both at high doses where epidemiology studies support its application, but controversially, also at low doses, which is a dose region that has a lower predictive statistical confidence.[1] Nonetheless, regulatory bodies, such as the Nuclear Regulatory Commission (NRC), commonly use LNT as a basis for regulatory dose limits to protect against stochastic health effects, as found in many public health policies. Whether the LNT model describes the reality for small-dose exposures is disputed, and challenges to the LNT model used by NRC for setting radiation protection regulations were submitted.[4] NRC rejected the petitions in 2021 because "they fail to present an adequate basis supporting the request to discontinue use of the LNT model".[9]

The LNT model opposes two competing schools of thought: the threshold model, which assumes that very small exposures are harmless, and the radiation hormesis model, which claims that radiation at very small doses can be beneficial. A 2016 peer-reviewed meta-analysis rejected the LNT on the basis of a lack of empirical evidence supporting it, and that it ignores biological effects, especially the self-correcting mechanisms in DNA which are effective up to a certain level of mutagenic agent.[1] Because the current data is inconclusive, scientists disagree on which model should be used. Pending any definitive answer to these questions, the LNT model is applied through the precautionary principle. The model is sometimes used to quantify the cancerous effect of collective doses of low-level radioactive contaminations, which may produce estimates of excess deaths at levels that may have had zero deaths or saved lives in the two other models. Such practice has been criticized by the International Commission on Radiological Protection since 2007.[5][1]

The LNT model is sometimes applied to other cancer hazards such as polychlorinated biphenyls in drinking water.[10]

Origins

Increased Risk of Solid Cancer with Dose for A-bomb survivors, from BEIR report. Notably, this exposure pathway occurred from essentially a massive spike or pulse of radiation, a result of the brief instant that the bomb exploded, which while somewhat similar to the environment of a CT scan, is wholly unlike the low dose rate of living in a contaminated area such as Chernobyl, where the dose rate is orders of magnitude smaller. LNT does not consider dose rate and is an unsubstantiated one size fits all approach based solely on total absorbed dose. When the two environments and cell effects are vastly different. Likewise, it has also been pointed out that bomb survivors inhaled carcinogenic benzopyrene from the burning cities, yet this is not factored in.[11]

The association of exposure to radiation with cancer had been observed as early as 1902, six years after the discovery of X-rays by Wilhelm Röntgen and radioactivity by Henri Becquerel.[12] In 1927, Hermann Muller demonstrated that radiation may cause genetic mutation.[13] He also suggested mutation as a cause of cancer.[14] Gilbert N. Lewis and Alex Olson, based on Muller's discovery of the effect of radiation on mutation, proposed a mechanism for biological evolution in 1928, suggesting that genomic mutation was induced by cosmic and terrestrial radiation and first introduced the idea that such mutation may occur proportionally to the dose of radiation.[15] Various laboratories, including Muller's, then demonstrated the apparent linear dose response of mutation frequency.[16] Muller, who received a Nobel Prize for his work on the mutagenic effect of radiation in 1946, asserted in his Nobel lecture, The Production of Mutation, that mutation frequency is "directly and simply proportional to the dose of irradiation applied" and that there is "no threshold dose".[17]

The early studies were based on higher levels of radiation that made it hard to establish the safety of low level of radiation. Indeed, many early scientists believed that there may be a tolerance level, and that low doses of radiation may not be harmful.[12] A later study in 1955 on mice exposed to low dose of radiation suggests that they may outlive control animals.[18] The interest in the effects of radiation intensified after the dropping of atomic bombs on Hiroshima and Nagasaki, and studies were conducted on the survivors. Although compelling evidence on the effect of low dosage of radiation was hard to come by, by the late 1940s, the idea of LNT became more popular due to its mathematical simplicity. In 1954, the National Council on Radiation Protection and Measurements (NCRP) introduced the concept of maximum permissible dose. In 1958, the United Nations Scientific Committee on the Effects of Atomic Radiation (UNSCEAR) assessed the LNT model and a threshold model, but noted the difficulty in acquiring "reliable information about the correlation between small doses and their effects either in individuals or in large populations". The United States Congress Joint Committee on Atomic Energy (JCAE) similarly could not establish if there is a threshold or "safe" level for exposure; nevertheless, it introduced the concept of "As Low As Reasonably Achievable" (ALARA). ALARA would become a fundamental principle in radiation protection policy that implicitly accepts the validity of LNT. In 1959, the United States Federal Radiation Council (FRC) supported the concept of the LNT extrapolation down to the low dose region in its first report.[12]

By the 1970s, the LNT model had become accepted as the standard in radiation protection practice by a number of bodies.[12] In 1972, the first report of National Academy of Sciences (NAS) Biological Effects of Ionizing Radiation (BEIR), an expert panel who reviewed available peer reviewed literature, supported the LNT model on pragmatic grounds, noting that while "dose-effect relationship for x rays and gamma rays may not be a linear function", the "use of linear extrapolation . . . may be justified on pragmatic grounds as a basis for risk estimation." In its seventh report of 2006, NAS BEIR VII writes, "the committee concludes that the preponderance of information indicates that there will be some risk, even at low doses".[19]

Radiation precautions and public policy

See also: Health effects of sun exposure

Radiation precautions have led to sunlight being listed as a carcinogen at all sun exposure rates, due to the ultraviolet component of sunlight, with no safe level of sunlight exposure being suggested, following the precautionary LNT model. According to a 2007 study submitted by the University of Ottawa to the Department of Health and Human Services in Washington, D.C., there is not enough information to determine a safe level of sun exposure.[20]

If a particular dose of radiation is found to produce one extra case of a type of cancer in every thousand people exposed, LNT projects that one thousandth of this dose will produce one extra case in every million people so exposed, and that one millionth of the original dose will produce one extra case in every billion people exposed. The conclusion is that any given dose equivalent of radiation will produce the same number of cancers, no matter how thinly it is spread. This allows the summation by dosimeters of all radiation exposure, without taking into consideration dose levels or dose rates.[21]

The model is simple to apply: a quantity of radiation can be translated into a number of deaths without any adjustment for the distribution of exposure, including the distribution of exposure within a single exposed individual. For example, a hot particle embedded in an organ (such as lung) results in a very high dose in the cells directly adjacent to the hot particle, but a much lower whole-organ and whole-body dose. Thus, even if a safe low dose threshold was found to exist at cellular level for radiation-induced mutagenesis, the threshold would not exist for environmental pollution with hot particles, and could not be safely assumed to exist when the distribution of dose is unknown.

The linear no-threshold model is used to extrapolate the expected number of extra deaths caused by exposure to environmental radiation, and it therefore has a great impact on public policy. The model is used to translate any radiation release, like that from a "dirty bomb", into a number of lives lost, while any reduction in radiation exposure, for example as a consequence of radon detection, is translated into a number of lives saved. When the doses are very low, at natural background levels, in the absence of evidence, the model predicts via extrapolation, new cancers only in a very small fraction of the population, but for a large population, the number of lives is extrapolated into hundreds or thousands, and this can sway public policy.

A linear model has long been used in health physics to set maximum acceptable radiation exposures.

The United States-based National Council on Radiation Protection and Measurements (NCRP), a body commissioned by the United States Congress, recently released a report written by the national experts in the field which states that radiation's effects should be considered to be proportional to the dose an individual receives, regardless of how small the dose is.

A 1958 analysis of two decades of research on the mutation rate of 1 million lab mice showed that six major hypotheses about ionizing radiation and gene mutation were not supported by data.[22] Its data was used in 1972 by the Biological Effects of Ionizing Radiation I committee to support the LNT model. However, it has been claimed that the data contained a fundamental error that was not revealed to the committee, and would not support the LNT model on the issue of mutations and may suggest a threshold dose rate under which radiation does not produce any mutations.[23][24]

Fieldwork

The LNT model and the alternatives to it each have plausible mechanisms that could bring them about, but definitive conclusions are hard to make given the difficulty of doing longitudinal studies involving large cohorts over long periods.

A 2003 review of the various studies published in the authoritative Proceedings of the National Academy of Sciences concludes that "given our current state of knowledge, the most reasonable assumption is that the cancer risks from low doses of x- or gamma-rays decrease linearly with decreasing dose."[25]

A 2005 study[26] of Ramsar, Iran (a region with very high levels of natural background radiation) showed that lung cancer incidence was lower in the high-radiation area than in seven surrounding regions with lower levels of natural background radiation. A fuller epidemiological study[27] of the same region showed no difference in mortality for males, and a statistically insignificant increase for females.

A 2009 study by researchers that looks at Swedish children exposed to fallout from Chernobyl while they were fetuses between 8 and 25 weeks gestation concluded that the reduction in IQ at very low doses was greater than expected, given a simple LNT model for radiation damage, indicating that the LNT model may be too conservative when it comes to neurological damage.[28] However, in medical journals, studies detail that in Sweden in the year of the Chernobyl accident, the birth rate both increased and shifted to those of "higher maternal age" in 1986.[29] More advanced maternal age in Swedish mothers was linked with a reduction in offspring IQ in a paper published in 2013.[30] Neurological damage has a different biology than cancer.

In a 2009 study,[31] cancer rates among UK radiation workers were found to increase with higher recorded occupational radiation doses. The doses examined varied between 0 and 500 millisieverts (mSv) received over their working lives. These results exclude the possibilities of no increase in risk or that the risk is 2-3 times that for A-bomb survivors with a confidence level of 90%. The cancer risk for these radiation workers was still less than the average for persons in the UK due to the healthy worker effect.

A 2009 study focusing on the naturally high background radiation region of Karunagappalli, India concluded: "our cancer incidence study, together with previously reported cancer mortality studies in the HBR area of Yangjiang, China, suggests it is unlikely that estimates of risk at low doses are substantially greater than currently believed."[32] A 2011 meta-analysis further concluded that the "Total whole body radiation doses received over 70 years from the natural environment high background radiation areas in Kerala, India and Yanjiang, China are much smaller than [the non-tumour dose, "defined as the highest dose of radiation at which no statistically significant tumour increase was observed above the control level"] for the respective dose-rates in each district."[33]

In 2011 an in vitro time-lapse study of the cellular response to low doses of radiation showed a strongly non-linear response of certain cellular repair mechanisms called radiation-induced foci (RIF). The study found that low doses of radiation prompted higher rates of RIF formation than high doses, and that after low-dose exposure RIF continued to form after the radiation had ended.[34]

In 2012 a historical cohort study of over 175,000 patients without previous cancer who were examined with CT head scans in UK between 1985 and 2002 was published.[35] The study, which investigated leukaemia and brain cancer, indicated a linear dose response in the low dose region and had qualitative estimates of risk that were in agreement with the Life Span Study (Epidemiology data for low-linear energy transfer radiation).

In 2013 a data linkage study of 11 million Australians with over 680,000 people exposed to CT scans between 1985 and 2005 was published.[36] The study confirmed the results of the 2012 UK study for leukaemia and brain cancer but also investigated other cancer types. The authors conclude that their results were generally consistent with the linear no threshold model.

However, these were disputed by a 2014 French study of 67,274 patients that took into account cancer-predisposing factors among those scanned. It concluded that taking these factors into account, there is no significant excess risk from CT scans.[37]

In 2016 Jeffry A. Siegel summarised the debate between supporters and opponents of LNT as based partially in conflict between statistical and experimental inference:[1]

Epidemiological studies that claim to confirm LNT either neglect experimental and/or observational discoveries at the cellular, tissue, and organismal levels, or mention them only to distort or dismiss them. The appearance of validity in these studies rests on circular reasoning, cherry picking, faulty experimental design, and/or misleading inferences from weak statistical evidence. In contrast, studies based on biological discoveries demonstrate the reality of hormesis: the stimulation of biological responses that defend the organism against damage from environmental agents. Normal metabolic processes are far more damaging than all but the most extreme exposures to radiation. However, evolution has provided all extant plants and animals with defenses that repair such damage or remove the damaged cells, conferring on the organism even greater ability to defend against subsequent damage.

— Siegel JA, Epidemiology Without Biology: False Paradigms, Unfounded Assumptions, and Specious Statistics in Radiation Science

A 2021 study based on whole-genome sequencing of children of parents employed as liquidators in Chernobyl indicated no trans-generational genetic effects of exposure of parents to ionizing radiation.[38]

Controversy

The LNT model has been contested by a number of scientists.[1] It has been claimed that the early proponent of the model Hermann Joseph Muller intentionally ignored an early study that did not support the LNT model when he gave his 1946 Nobel Prize address advocating the model.[39]

In very high dose radiation therapy, it was known at the time that radiation can cause a physiological increase in the rate of pregnancy anomalies; however, human exposure data and animal testing suggests that the "malformation of organs appears to be a deterministic effect with a threshold dose", below which no rate increase is observed.[40] A review in 1999 on the link between the Chernobyl accident and teratology (birth defects) concludes that "there is no substantive proof regarding radiation‐induced teratogenic effects from the Chernobyl accident".[40] It is argued that the human body has defense mechanisms, such as DNA repair and programmed cell death, that would protect it against carcinogenesis due to low-dose exposures of carcinogens.[41]

Ramsar, located in Iran, is often quoted as being a counter example to LNT. Based on preliminary results, it was considered as having the highest natural background radiation levels on Earth, several times higher than the ICRP-recommended radiation dose limits for radiation workers, whilst the local population did not seem to have any ill effects.[42] However, the population of the high-radiation districts is small (about 1800 inhabitants) and only receive an average of 6 millisieverts per year,[43] so cancer epidemiology data are too imprecise to draw any conclusions.[44] On the other hand, there may be non-cancer effects from the background radiation such as chromosomal aberrations.[45]

At the same time in Germany and Austria, some of the most radiophobic countries, people attend "radon spas" where they voluntarily expose themselves to low-level radiation of radon for its alleged health benefits.[46]

A 2011 research of the cellular repair mechanisms support the evidence against the linear no-threshold model.[34] According to its authors, this study published in the Proceedings of the National Academy of Sciences of the United States of America "casts considerable doubt on the general assumption that risk to ionizing radiation is proportional to dose".

A 2011 review of studies addressing childhood leukaemia following exposure to ionizing radiation, including both diagnostic exposure and natural background exposure from radon, concluded that existing risk factors, excess relative risk per sievert (ERR/Sv), is "broadly applicable" to low dose or low dose-rate exposure, "although the uncertainties associated with this estimate are considerable". The study also notes that "epidemiological studies have been unable, in general, to detect the influence of natural background radiation upon the risk of childhood leukaemia"[47]

The U.S average background radiation dose from cosmic rays, radionuclides in soil and rock, from the food we eat, and indoor radon, is 3 mSv/year or 240 mSv per 80-year lifetime. Using the BEIR VII risk of 0.000114 per mSv implies a lifetime risk from background radiation of 240 x 0.000114 = 0.027 or 2.7%. This is substantially greater than EPA’s incremental lifetime cancer incidence risk goal of 10-6, and a substantial fraction of the inherent U.S. cancer incidence risk of approximately 42%. If the EPA and medical community truly believed that 2.7% is the cancer risk from background radiation, then it should proclaim that to the world, and watch Amazon’s sales of lead-lined clothing skyrocket.[48] The LNT model of radiation risk together with EPA’s reliance on 10-6 as a de facto “safe” limit for incremental lifetime cancer incidence risk, leads to some wildly implausible inferences. A 10-6 increased cancer risk would be incurred by drinking an additional 0.4 teaspoons of orange juice each day for 30 years, due to its radioactive potassium-40 content. 10-6 is the difference in radiation risk between the feet and head of a 6-foot person due to the difference in cosmic ray exposure. 10-6 is the additional non-radiation fatal risk from driving an extra 1 mile per year for 30 years.[49][50]

Several expert scientific panels have been convened on the accuracy of the LNT model at low dosage, and various organizations and bodies have stated their positions on this topic:

Support
  • The US Nuclear Regulatory Commission:[51]

    Based upon the current state of science, the NRC concludes that the actual level of risk associated with low doses of radiation remains uncertain and some studies, such as the INWORKS study, show there is at least some risk from low doses of radiation. Moreover, the current state of science does not provide compelling evidence of a threshold, as highlighted by the fact that no national or international authoritative scientific advisory bodies have concluded that such evidence exists. Therefore, based upon the stated positions of the aforementioned advisory bodies; the comments and recommendations of NCI, NIOSH, and the EPA; the October 28, 2015, recommendation of the ACMUI; and its own professional and technical judgment, the NRC has determined that the LNT model continues to provide a sound regulatory basis for minimizing the risk of unnecessary radiation exposure to both members of the public and occupational workers. Consequently, the NRC will retain the dose limits for occupational workers and members of the public in 10 CFR part 20 radiation protection regulations.

The NRC upheld the LNT model in 2021 as a "sound regulatory basis for minimizing the risk of unnecessary radiation exposure to both members of the public and radiation workers" following challenges to the dose limit requirements contained in its regulations.[9]
  • In 2004 the United States National Research Council (part of the National Academy of Sciences) supported the linear no threshold model and stated regarding Radiation hormesis:[52]

    The assumption that any stimulatory hormetic effects from low doses of ionizing radiation will have a significant health benefit to humans that exceeds potential detrimental effects from the radiation exposure is unwarranted at this time.

  • In 2005 the United States National Academies' National Research Council published its comprehensive meta-analysis of low-dose radiation research BEIR VII, Phase 2. In its press release the Academies stated:[53]

The scientific research base shows that there is no threshold of exposure below which low levels of ionizing radiation can be demonstrated to be harmless or beneficial.

  • The National Council on Radiation Protection and Measurements (a body commissioned by the United States Congress).[54] endorsed the LNT model in a 2001 report that attempted to survey existing literature critical of the model.
  • The United States Environmental Protection Agency endorses the LNT model in its 2011 report on radiogenic cancer risk:[55]

    Underlying the risk models is a large body of epidemiological and radiobiological data. In general, results from both lines of research are consistent with a linear, no-threshold dose (LNT) response model in which the risk of inducing a cancer in an irradiated tissue by low doses of radiation is proportional to the dose to that tissue

UNSCEAR notably reversed its earlier support on the LNT model in 2014 for doses at levels equivalent to or lower than natural background levels (see below).

Oppose

A number of organisations disagree with using the Linear no-threshold model to estimate risk from environmental and occupational low-level radiation exposure:

  • The French Academy of Sciences (Académie des Sciences) and the National Academy of Medicine (Académie Nationale de Médecine) published a report in 2005 (at the same time as BEIR VII report in the United States) that rejected the linear no-threshold model in favor of a threshold dose response and a significantly reduced risk at low radiation exposure:[56][57]

In conclusion, this report raises doubts on the validity of using LNT for evaluating the carcinogenic risk of low doses (< 100 mSv) and even more for very low doses (< 10 mSv). The LNT concept can be a useful pragmatic tool for assessing rules in radioprotection for doses above 10 mSv; however since it is not based on biological concepts of our current knowledge, it should not be used without precaution for assessing by extrapolation the risks associated with low and even more so, with very low doses (< 10 mSv), especially for benefit-risk assessments imposed on radiologists by the European directive 97-43.

Due to large statistical uncertainties, epidemiological studies have not provided consistent estimates of radiation risk for effective doses less than 100 mSv. Underlying dose-response relationships at molecular levels appear mainly nonlinear. The low incidence of biological effects from exposure to radiation compared to the natural background incidence of the same effects limits the applicability of radiation risk coefficients at effective doses less than 100 mSv (NCRP 2012).

The references to 100 mSv in this position statement should not be construed as implying that health effects are well established for doses exceeding 100 mSv. Considerable uncertainties remain for stochastic effects of radiation exposure between 100 mSv and 1,000 mSv, depending upon the population exposed, the rate of exposure, the organs and tissues affected, and other variables. In addition, it is worth noting that epidemiological studies generally do not take into account the dose that occupationally or medically exposed persons incur as natural background; thus, the references to 100 mSv in this position statement should generally be interpreted as 100 mSv above natural background dose.

The Health Physics Society (in the United States) has published a documentary series on the origins of the LNT model.[59]
  • The American Nuclear Society concurred with the Health Physics Society's position that:[60]

    There is substantial and convincing scientific evidence for health risks at high dose. Below 10 rem or 100 mSv (which includes occupational and environmental exposures) risks of health effects are either too small to be observed or are non-existent.

However, it recommended further research on the Linear No Threshold Hypothesis before making adjustments to current radiation protection guidelines derived from the LNT model.
  • UNSCEAR, which supported the LNT model in its previous reports on radiogenic cancer risk,[61] has adjusted its position in its 2012 report and stated:[6][62]

The Scientific Committee does not recommend multiplying very low doses by large numbers of individuals to estimate numbers of radiation-induced health effects within a population exposed to incremental doses at levels equivalent to or lower than natural background levels.

Mental health effects

Further information: Radiophobia

It has been argued that the LNT model had caused an irrational fear of radiation, whose observable effects are much more significant than non-observable effects postulated by LNT.[1] In the wake of the 1986 Chernobyl accident in Ukraine, Europe-wide anxieties were fomented in pregnant mothers over the perception enforced by the LNT model that their children would be born with a higher rate of mutations.[63] As far afield as the country of Switzerland, hundreds of excess induced abortions were performed on the healthy unborn, out of this no-threshold fear.[64] Following the accident however, studies of data sets approaching a million births in the EUROCAT database, divided into "exposed" and control groups were assessed in 1999. As no Chernobyl impacts were detected, the researchers conclude "in retrospect the widespread fear in the population about the possible effects of exposure on the unborn was not justified".[65] Despite studies from Germany and Turkey, the only robust evidence of negative pregnancy outcomes that transpired after the accident were these elective abortion indirect effects, in Greece, Denmark, Italy etc., due to the anxieties created.[66]

The consequences of low-level radiation are often more psychological than radiological. Because damage from very-low-level radiation cannot be detected, people exposed to it are left in anguished uncertainty about what will happen to them. Many believe they have been fundamentally contaminated for life and may refuse to have children for fear of birth defects. They may be shunned by others in their community who fear a sort of mysterious contagion.[67]

Forced evacuation from a radiation or nuclear accident may lead to social isolation, anxiety, depression, psychosomatic medical problems, reckless behavior, or suicide. Such was the outcome of the 1986 Chernobyl nuclear disaster in Ukraine. A comprehensive 2005 study concluded that "the mental health impact of Chernobyl is the largest public health problem unleashed by the accident to date".[67] Frank N. von Hippel, a U.S. scientist, commented on the 2011 Fukushima nuclear disaster, saying that "fear of ionizing radiation could have long-term psychological effects on a large portion of the population in the contaminated areas".[68]

Such great psychological danger does not accompany other materials that put people at risk of cancer and other deadly illness. Visceral fear is not widely aroused by, for example, the daily emissions from coal burning, although as a National Academy of Sciences study found, this causes 10,000 premature deaths a year in the US. It is "only nuclear radiation that bears a huge psychological burden – for it carries a unique historical legacy".[67]

See also

References

  1. ^ a b c d e f g h i Sacks B, Meyerson G, Siegel JA (1 June 2016). "Epidemiology Without Biology: False Paradigms, Unfounded Assumptions, and Specious Statistics in Radiation Science (with Commentaries by Inge Schmitz-Feuerhake and Christopher Busby and a Reply by the Authors)". Biological Theory. 11 (2): 69–101. doi:10.1007/s13752-016-0244-4. PMC 4917595. PMID 27398078.
  2. ^ "Preventing Breast Cancer Second Edition: 1996".
  3. ^ Corcos D, Bleyer A (2020). "Epidemiologic Signatures in Cancer". N Engl J Med. 382 (1): 96–97. doi:10.1056/NEJMc1914747. PMID 31875513. S2CID 209481963.
  4. ^ a b Emshwiller JR, Fields G (13 August 2016). "Is a Little Radiation So Bad?". Wall Street Journal.
  5. ^ a b "The 2007 Recommendations of the International Commission on Radiological Protection". International Commission on Radiological Protection. 2007.
  6. ^ a b "UNSCEAR Fifty-Ninth Session 21–25 May 2012" (PDF). 14 August 2012. Archived from the original (PDF) on 5 August 2013. Retrieved 3 February 2013.
  7. ^ "Stochastic effects". Health Physics Society.
  8. ^ Christensen DM, Iddins CJ, Sugarman SL (February 2014). "Ionizing radiation injuries and illnesses". Emergency Medicine Clinics of North America. 32 (1): 245–65. doi:10.1016/j.emc.2013.10.002. PMID 24275177.
  9. ^ a b "Linear No-Threshold Model and Standards for Protection Against Radiation". Federal Register.
  10. ^ Consumer Factsheet on: polychlorinated biphenyls US Environmental Protection Agency.
  11. ^ Tubiana M, Feinendegen LE, Yang C, Kaminski JM (April 2009). "The linear no-threshold relationship is inconsistent with radiation biologic and experimental data". Radiology. 251 (1): 13–22. doi:10.1148/radiol.2511080671. PMC 2663584. PMID 19332842.
  12. ^ a b c d Kathren RL (December 2002). "Historical Development of the Linear Nonthreshold Dose-Response Model as Applied to Radiation". University of New Hampshire Law Review. 1 (1).
  13. ^ Muller HJ (July 1927). "Artificial Transmutation of the Gene" (PDF). Science. 66 (1699): 84–7. Bibcode:1927Sci....66...84M. doi:10.1126/science.66.1699.84. PMID 17802387.
  14. ^ Crow JF, Abrahamson S (December 1997). "Seventy years ago: mutation becomes experimental". Genetics. 147 (4): 1491–6. doi:10.1093/genetics/147.4.1491. PMC 1208325. PMID 9409815.
  15. ^ Calabrese, Edward J. (March 2019). "The linear No-Threshold (LNT) dose response model: A comprehensive assessment of its historical and scientific foundations". Chem Biol Interact. 301: 6–25. doi:10.1016/j.cbi.2018.11.020. PMID 30763547. S2CID 73431487.
  16. ^ Oliver, C. P. (10 January 1930). "The Effect of Varying the Duration of X-Ray Treatment Upon the Frequency of Mutation". Science. 71 (1828): 44–46. Bibcode:1930Sci....71...44O. doi:10.1126/science.71.1828.44. PMID 17806621.
  17. ^ "Hermann J. Muller - Nobel Lecture". Nobel Prize. 12 December 1946.
  18. ^ Lorenz E, Hollcroft JW, Miller E, Congdon CC, Schweisthal R (February 1955). "Long-term effects of acute and chronic irradiation in mice. I. Survival and tumor incidence following chronic irradiation of 0.11 r per day". Journal of the National Cancer Institute. 15 (4): 1049–58. doi:10.1093/jnci/15.4.1049. PMID 13233949.
  19. ^ "Beir VII: Health Risks from Exposure to Low Levels of Ionizing Radiation" (PDF). The National Academy.
  20. ^ Cranney A, Horsley T, O'Donnell S, Weiler H, Puil L, Ooi D, et al. (August 2007). "Effectiveness and safety of vitamin D in relation to bone health". Evidence Report/Technology Assessment (158): 1–235. PMC 4781354. PMID 18088161.
  21. ^ "Radiation Standards: Scientific Basis Inconclusive, and EPA and NRC Disagreement Continues" (PDF). United States General Accounting Office. June 2000. Archived from the original (PDF) on 5 December 2001. In the absence of more conclusive data, scientists have assumed that even the smallest radiation exposure carries a risk.
  22. ^ Russell WL, Russell LB, Kelly EM (December 1958). "Radiation dose rate and mutation frequency". Science. 128 (3338): 1546–50. Bibcode:1958Sci...128.1546R. doi:10.1126/science.128.3338.1546. PMID 13615306. S2CID 23227290.
  23. ^ University of Massachusetts Amherst (23 January 2017). "Calabrese says mistake led to adopting the LNT model in toxicology". Phys.org.
  24. ^ Calabrese EJ (April 2017). "The threshold vs LNT showdown: Dose rate findings exposed flaws in the LNT model part 2. How a mistake led BEIR I to adopt LNT". Environmental Research. 154: 452–458. Bibcode:2017ER....154..452C. doi:10.1016/j.envres.2016.11.024. PMID 27974149. S2CID 9383412.
  25. ^ Brenner DJ, Doll R, Goodhead DT, Hall EJ, Land CE, Little JB, et al. (November 2003). "Cancer risks attributable to low doses of ionizing radiation: assessing what we really know". Proceedings of the National Academy of Sciences of the United States of America. 100 (24): 13761–6. Bibcode:2003PNAS..10013761B. doi:10.1073/pnas.2235592100. PMC 283495. PMID 14610281.
  26. ^ Mortazavi SM, Ghiassi-Nejad M, Rezaiean M (2005). "Cancer risk due to exposure to high levels of natural radon in the inhabitants of Ramsar, Iran". International Congress Series. 1276: 436–437. doi:10.1016/j.ics.2004.12.012.
  27. ^ Mosavi-Jarrahi A, Mohagheghi M, Akiba S, Yazdizadeh B, Motamedi N, Monfared AS (2005). "Mortality and morbidity from cancer in the population exposed to high level of natural radiation area in Ramsar, Iran". International Congress Series. 1276: 106–109. doi:10.1016/j.ics.2004.11.109.
  28. ^ Almond D, Edlund L, Palme M (2009). "Chernobyl's Subclinical Legacy: Prenatal Exposure to Radioactive Fallout and School Outcomes in Sweden" (PDF). Quarterly Journal of Economics. 124 (4): 1729–1772. doi:10.1162/qjec.2009.124.4.1729.
  29. ^ Odlind V, Ericson A (1991). "Incidence of legal abortion in Sweden after the Chernobyl accident". Biomedicine & Pharmacotherapy. 45 (6): 225–8. doi:10.1016/0753-3322(91)90021-k. PMID 1912377.
  30. ^ Myrskylä M, Silventoinen K, Tynelius P, Rasmussen F (April 2013). "Is later better or worse? Association of advanced parental age with offspring cognitive ability among half a million young Swedish men". American Journal of Epidemiology. 177 (7): 649–55. doi:10.1093/aje/kws237. PMID 23467498.
  31. ^ Muirhead CR, O'Hagan JA, Haylock RG, Phillipson MA, Willcock T, Berridge GL, Zhang W (January 2009). "Mortality and cancer incidence following occupational radiation exposure: third analysis of the National Registry for Radiation Workers". British Journal of Cancer. 100 (1): 206–12. doi:10.1038/sj.bjc.6604825. PMC 2634664. PMID 19127272.
  32. ^ Nair RR, Rajan B, Akiba S, Jayalekshmi P, Nair MK, Gangadharan P, et al. (January 2009). "Background radiation and cancer incidence in Kerala, India-Karanagappally cohort study". Health Physics. 96 (1): 55–66. doi:10.1097/01.HP.0000327646.54923.11. PMID 19066487. S2CID 24657628.
  33. ^ Tanooka H (July 2011). "Meta-analysis of non-tumour doses for radiation-induced cancer on the basis of dose-rate". International Journal of Radiation Biology. 87 (7): 645–52. doi:10.3109/09553002.2010.545862. PMC 3116717. PMID 21250929.
  34. ^ a b Neumaier T, Swenson J, Pham C, Polyzos A, Lo AT, Yang P, et al. (January 2012). "Evidence for formation of DNA repair centers and dose-response nonlinearity in human cells". Proceedings of the National Academy of Sciences of the United States of America. 109 (2): 443–8. Bibcode:2012PNAS..109..443N. doi:10.1073/pnas.1117849108. PMC 3258602. PMID 22184222.
  35. ^ Pearce MS, Salotti JA, Little MP, McHugh K, Lee C, Kim KP, et al. (August 2012). "Radiation exposure from CT scans in childhood and subsequent risk of leukaemia and brain tumours: a retrospective cohort study". Lancet. 380 (9840): 499–505. doi:10.1016/S0140-6736(12)60815-0. PMC 3418594. PMID 22681860.
  36. ^ Mathews JD, Forsythe AV, Brady Z, Butler MW, Goergen SK, Byrnes GB, et al. (May 2013). "Cancer risk in 680,000 people exposed to computed tomography scans in childhood or adolescence: data linkage study of 11 million Australians". BMJ. 346: f2360. doi:10.1136/bmj.f2360. PMC 3660619. PMID 23694687.
  37. ^ Journy, N; Rehel, J-L; Ducou Le Point, H; Lee, C; Brisse, H; Chateil, J-F; Caer-Lorho, S; Laurier, D; Bernier, M-O (14 October 2014). "Are the studies on cancer risk from CT scans biased by indication? Elements of answer from a large-scale cohort study in France". British Journal of Cancer. 112 (1): 185–193. doi:10.1038/bjc.2014.526. PMC 4453597. PMID 25314057.
  38. ^ Yeager, Meredith; Machiela, Mitchell J.; Kothiyal, Prachi; Dean, Michael; Bodelon, Clara; Suman, Shalabh; Wang, Mingyi; Mirabello, Lisa; Nelson, Chase W.; Zhou, Weiyin; Palmer, Cameron (14 May 2021). "Lack of transgenerational effects of ionizing radiation exposure from the Chernobyl accident". Science. 372 (6543): 725–729. Bibcode:2021Sci...372..725Y. doi:10.1126/science.abg2365. ISSN 0036-8075. PMC 9398532. PMID 33888597. S2CID 233371673.
  39. ^ Calabrese EJ (December 2011). "Muller's Nobel lecture on dose-response for ionizing radiation: ideology or science?" (PDF). Archives of Toxicology. 85 (12): 1495–8. doi:10.1007/s00204-011-0728-8. PMID 21717110. S2CID 4708210.
  40. ^ a b Castronovo FP (August 1999). "Teratogen update: radiation and Chernobyl". Teratology. 60 (2): 100–6. doi:10.1002/(sici)1096-9926(199908)60:2<100::aid-tera14>3.3.co;2-8. PMID 10440782.
  41. ^ Schachtman NA. "The Mythology of Linear No-Threshold Cancer Causation". nathan@schachtmanlaw.com.
  42. ^ Mortazavi SM. "High Background Radiation Areas of Ramsar, Iran". Retrieved 4 September 2011.
  43. ^ Sohrabi M, Babapouran M (2005). "New public dose assessment from internal and external exposures in low- and elevated-level natural radiation areas of Ramsar, Iran". International Congress Series. 1276: 169–174. doi:10.1016/j.ics.2004.11.102.
  44. ^ Mosavi-Jarrahi A, Mohagheghi M, Akiba S, Yazdizadeh B, Motamedi N, Monfared AS (2005). "Mortality and morbidity from cancer in the population exposed to high level of natural radiation area in Ramsar, Iran". International Congress Series. 1276: 106–109. doi:10.1016/j.ics.2004.11.109.
  45. ^ Zakeri F, Rajabpour MR, Haeri SA, Kanda R, Hayata I, Nakamura S, et al. (November 2011). "Chromosome aberrations in peripheral blood lymphocytes of individuals living in high background radiation areas of Ramsar, Iran". Radiation and Environmental Biophysics. 50 (4): 571–8. doi:10.1007/s00411-011-0381-x. PMID 21894441. S2CID 26006420.
  46. ^ Kabat G. "In Germany And Austria, Visits To Radon Health Spas Are Covered By Health Insurance". Forbes. Retrieved 19 March 2021.
  47. ^ Wakeford R (March 2013). "The risk of childhood leukaemia following exposure to ionising radiation--a review". Journal of Radiological Protection. 33 (1): 1–25. Bibcode:2013JRP....33....1W. doi:10.1088/0952-4746/33/1/1. PMID 23296257. S2CID 41245977.
  48. ^ Rutherford, Phil (10 September 2007). "Linear No Threshold Model of Radiation Risk" (PDF). Department of Energy. Retrieved 19 November 2023.{{cite web}}: CS1 maint: url-status (link)
  49. ^ Rutherford, Phil (27 January 2010). "Radiation Risks in Everyday Life" (PDF). Phil Rutherford Consulting. Retrieved 19 November 2023.{{cite web}}: CS1 maint: url-status (link)
  50. ^ Rutherford, Phil (18 November 2018). "Linear No Threshold (LNT) Model of Radiation Risk" (PDF). Phil Rutherford Consulting. Retrieved 19 November 2023.{{cite web}}: CS1 maint: url-status (link)
  51. ^ "Petition for Rulemaking; Denial: Linear No-Threshold Model and Standards for Protection Against Radiation". Nuclear Regulatory Commission. 16 August 2021. Retrieved 2 August 2021.
  52. ^ National Research Council. (2006). "Hormesis and Epidemiology". Health Risks from Exposure to Low Levels of Ionizing Radiation: BEIR VII Phase 2. Washington, DC: The National Academies Press. p. 335. doi:10.17226/11340. ISBN 978-0-309-09156-5.
  53. ^ "Low Levels of Ionizing Radiation May Cause Harm". News Release. National Academies of Sciences. 29 June 2005.
  54. ^ NCRP report. Ncrppublications.org. Retrieved on 5 May 2012.
  55. ^ U.S. Environmental Protection Agency (April 2011). "EPA Radiogenic Cancer Risk Models and Projections for the U.S. Population" (PDF). EPA. Retrieved 15 November 2011.
  56. ^ Heyes GJ, Mill AJ, Charles MW (1 October 2006). "Authors' reply". British Journal of Radiology. 79 (946): 855–857. doi:10.1259/bjr/52126615.
  57. ^ Tubiana M, Aurengo A, Averbeck D, Bonnin A, Le Guen B, Masse R, Monier R, Valleron AJ, De Vathaire F (30 March 2005). "Dose-effect relationships and estimation of the carcinogenic effects of low doses of ionizing radiation" (PDF). Academy of Medicine (Paris) and Academy of Science (Paris) Joint Report. Archived from the original (PDF) on 25 July 2011. Retrieved 27 March 2008.
  58. ^ Health Physics Society, 2019. Radiation Risk in Perspective PS010-4 [1]
  59. ^ "The History of the Linear No-Threshold (LNT) Model Episode Guide". Health Physics Society.
  60. ^ "Health Effects of Low-Level Radiation" (PDF). Position Statement #41. The American Nuclear Society. 2001.
  61. ^ UNSCEAR 2000 REPORT Vol. II: Sources and Effects of Ionizing Radiation: Annex G: Biological effects at low radiation doses. page 160, paragraph 541. Available online at [2].
  62. ^ UNSCEAR United Nations (31 December 2015). Sources, Effects and Risks of Ionizing Radiation, United Nations Scientific Committee on the Effects of Atomic Radiation (UNSCEAR) 2012 Report: Report to the General Assembly, with Scientific Annexes A and B. ISBN 9789210577984.
  63. ^ Kasperson RE, Stallen PJ (1991). Communicating Risks to the Public: International Perspectives. Berlin: Springer Science and Media. pp. 160–2. ISBN 978-0-7923-0601-6.
  64. ^ Perucchi M, Domenighetti G (December 1990). "The Chernobyl accident and induced abortions: only one-way information". Scandinavian Journal of Work, Environment & Health. 16 (6): 443–4. doi:10.5271/sjweh.1761. PMID 2284594.
  65. ^ Dolk H, Nichols R (October 1999). "Evaluation of the impact of Chernobyl on the prevalence of congenital anomalies in 16 regions of Europe. EUROCAT Working Group". International Journal of Epidemiology. 28 (5): 941–8. doi:10.1093/ije/28.5.941. PMID 10597995.
  66. ^ Little J (April 1993). "The Chernobyl accident, congenital anomalies and other reproductive outcomes". Paediatric and Perinatal Epidemiology. 7 (2): 121–51. doi:10.1111/j.1365-3016.1993.tb00388.x. PMID 8516187.
  67. ^ a b c Revkin AC (10 March 2012). "Nuclear Risk and Fear, from Hiroshima to Fukushima". New York Times.
  68. ^ von Hippel FN (September–October 2011). "The radiological and psychological consequences of the Fukushima Daiichi accident". Bulletin of the Atomic Scientists. 67 (5): 27–36. Bibcode:2011BuAtS..67e..27V. doi:10.1177/0096340211421588. S2CID 218769799.
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