Non-targeted and delayed effects of exposure to ionizing radiation: II. Radiation-induced genomic instability and bystander effects in vivo,clastogenic factors and transgenerational effects

The goal of this review is to summarize the evidence for non-targeted and delayed effects of exposure to ionizing radiation in vivo. Currently, human health risks associated with radiation exposures are based primarily on the assumption that the detrimental effects of radiation occur in irradiated cells. Over the years a number of non-targeted effects of radiation exposure in vivo have been described that challenge this concept. These include radiation-induced genomic instability, bystander effects, clastogenic factors produced in plasma from irradiated individuals that can cause chromosomal damage when cultured with nonirradiated cells, and transgenerational effects of parental irradiation that can manifest in the progeny. These effects pose new challenges to evaluating the risk(s) associated with radiation exposure and understanding radiation-induced carcinogenesis.     

Non-targeted and delayed effects of exposure to ionizing radiation: I. Radiation-induced genomic instability and bystander effects in vitro

A long-standing dogma in the radiation sciences is that energy from radiation must be deposited in the cell nucleus to elicit a biological effect. A number of non-targeted, delayed effects of ionizing radiation have been described that challenge this dogma and pose new challenges to evaluating potential hazards associated with radiation exposure. These effects include induced genomic instability and non-targeted bystander effects. The in vitro evidence for non-targeted effects in radiation biology will be reviewed, but the question as to how one extrapolates from these in vitro observations to the risk of radiation-induced adverse health effects such as cancer remains open.     

Radiation injury: some aspects of the oncogenic effects.

The late effects or irradiation stem from cell killing, mutation, and malignant transformation. Cancer is the major somatic late effect of exposure to low dose levels of radiation, and estimates of risk of cancer in man after irradiation are based entirely on human experience. The data for dose-response relationships for the induction of tumors by external irradiation in man have been obtained from a single exposure or a small number of exposures delivered at high dose rates. In contrast, exposure to environmental irradiation is mainly protracted over a long period of time and is delivered at a low dose rate. As yet no allowance has been made for the effect of protraction of the exposure time in estimating the risk of cancer, although an adjustment has been made in the case of estimates of genetic risk. Incidence of tumors has been the only parameter used for risk estimates, but latent period and degree of malignancy, which are probably both dose and dose-rate dependent, influence the nature of the risk from radiation. As the knowledge about the effects of low-level radiation has been accumulated and assimilated over the last 70 years, so has the concern for reasonable standards of safety. There are still problems in the estimation of radiation risks, but at least many of the relevant questions can now be framed. The problems of estimating risks for chemical carcinogens are clearly greater, but the experience gained from radiation studies should help in the design of the necessary experiments.     

Interrelationships amongst radiation-induced genomic instability, bystander effects, and the adaptive response

Over the past two decades, our understanding of radiation biology has undergone a fundamental shift in paradigms away from deterministic "hit-effect" relationships and towards complex ongoing "cellular responses". These responses include now familiar, but still poorly understood, phenomena associated with radiation exposure such as bystander effects, genomic instability, and adaptive responses. All three have been observed at very low doses, and at time points far removed from the initial radiation exposure, and are extremely relevant for linear extrapolation to low doses; the adaptive response is particularly relevant when exposure is spread over a period of time. These are precisely the circumstances that are most relevant to understanding cancer risk associated with environmental and occupational radiation exposures. This review will provide a synthesis of the known, and proposed, interrelationships amongst low-dose cellular responses to radiation. It also will examine the potential importance of non-targeted cellular responses to ionizing radiation in setting acceptable exposure limits especially to low-LET radiations.     

Relationships between satellite association and the occurrence of non-disjunction in man.

It has been reported that there is an increased incidence of Down's syndrome among the children of parents who have been exposed to ionizing radiations for radiodiagnostic or radiotherapeutic reasons. Work with Drosophila, mice and human lymphocytes has shown that irradiation with X- or gamma-rays induces aneuploidy, presumably by non-disjunction. It has been suggested that in man the frequency of satellite association (s.a.) of acrocentric chromosomes may be involved in the causation of chromosomal non-disjunction. In the present work the effects of radiation on s.a. have, therefore, been investigated. The frequency of s.a. between acrocentric chromosomes was determined after the exposure of human blood from normal and chromosomally abnormal individuals to various small doses of Co-60 gamma-rays. The criteria of Zang and Back were used for the evaluation of s.a. complexes. No effects of radiation on the frequency of s.a. were apparent within the dose range investigated. The same result was obtained when s.a. was evaluated using the silver-staining technique in which physical connections between the associating satellites may be observed and the association complexes evaluated directly. The effects of other radiation sources have also been investigated.     

Principal inferences from studies of radiobiological effects for radiation protection purposes

The most recent Recommendations (Publication 103) issued by the International Commission for Radiological Protection (ICRP) are based on the data that have been published since 1990 up to now. The basic task of the ICRP Committee 1 was to formulate the key implications of studies on radiobiological effects for the purposes of radiological protection. Presented in the paper are the new achievements in the field of biology, radiobiology and radiation epidemiology which were taken into account by the ICRP in the process of Publication 103 preparation. The Recommendations provide present-day values of weighting factors for radiation exposure and tissue weighting factors, as well as radiation detriment and radiogenic risk factors for cancer and genetic diseases. Also considered are tissue reactions to radiation exposure, consequences of in utero exposure and the risks of developing non-cancer diseases for exposed individuals. It should be noted that the key inferences and recommendations are to a considerable degree related to biological effects accounted for by acute and chronic exposure to ionizing radiation in the range of small doses (up to 100 mSv).     

Non-targeted bystander effects induced by ionizing radiation

Radiation-induced bystander effects refer to those responses occurring in cells that were not subject to energy deposition events following ionizing radiation. These bystander cells may have been neighbors of irradiated cells, or physically separated but subject to soluble secreted signals from irradiated cells. Bystander effects have been observed in vitro and in vivo and for various radiation qualities. In tribute to an old friend and colleague, Anthony V. Carrano, who would have said "well what are the critical questions that should be addressed, and so what?", we review the evidence for non-targeted radiation-induced bystander effects with emphasis on prevailing questions in this rapidly developing research field, and the potential significance of bystander effects in evaluating the detrimental health effects of radiation exposure.     

Biological low-dose radiation effects.

It is theorized that biological responses to ionizing radiation in the low dose range are determined according to a doubly dichotomous pattern. Energy depositions fall into 2 categories: events at thermal energy levels where they may be experienced by cells as rates even at background exposure conditions, and events at energy levels of the order of 10-100 eV where damage to DNA may be caused. Variations in background exposure intensity may or may not lead preemptively to changes in the cell's capacity for response to radiation damage. High-level energy depositions lead post hoc to an initial stabilizing reaction largely leading to the fixation of the initial DNA damage, and to a subsequent restorative or palliative repair process. This model entails reinterpretation of some experimental results. The model has implications for the relationship between scientific analysis of low-dose effects and the regulatory needs for simplicity and homogeneity in risk evaluation. This represents a new challenge for the acceptability of radiation protection norms.     

Psychophysiological indicators for children using mobile phones. Communication 1. Current state of the problem

An overview of the epidemiological and experimental evidence for exposure of humans and animals to electromagnetic radiation produced by mobile phones is provided. The effects of mobile phone radiation on the child's body are considered in detail. It has been shown that the children's organism is more sensitive to this kind of exposure than the adult one.     

Nontargeted effects of ionizing radiation: implications for low-dose exposures

The traditional thinking has been that the biological effects of ionizing radiation occur in irradiated cells as a consequence of the DNA damage they incur. This implies that: 1) biological effects occur only in irratiated cells, 2) radiation traversal through the nucleus of the cell is a prerequisite to produce a biological response, and 3) DNA is the target molecule in the cell. Evidence has been emerging, however, for non-DNA targeted effects of radiation; that is, effects including mutations, chromosomal aberrations, and changes in gene expression which occur in cells that in themselves receive no radiation exposure. Two of these phenomena will be described in this paper. The first is radiation-induced genomic instability whereby biological effects, including elevated frequencies of mutations and chromosomal aberrations, arise in the distant descendants of irradiated cells. The second phenomenon has been termed the "bystander effect", whereby in a mixed population of irradiated and nonirradiated cells, biological effects arise in those cells that receive no radiation exposure. The damage signals are transmitted from cell to cell through gap junction channels, and the genetic effects observed in bystander cells appear to result from an upregulation of oxidative stress. The possible influence of these non-targeted effects of radiation of the respounse to low-dose exposures is discussed.     

Sex-specific microRNAome deregulation in the shielded bystander spleen of cranially exposed mice

The bystander effect is a phenomenon that occurs when exposed cells signal distress to their naïve, unexposed neighbors. It is now accepted as a ubiquitous consequence of radiation exposure. It is well documented to occur in cultured cells, 3D tissue models, and in organs and organisms. Notwithstanding, the exact mechanisms of the bystander effect remain unclear. Recent studies hinted that bystander effects may, in part, be distinct in males and females, and possibly mediated via short non-coding RNAs, specifically, microRNAs. MicroRNAs are small, abundant, and capable of regulating the expression of a wide variety of targets. Yet, their roles in bystander effects have not been analyzed in detail. The mechanisms behind sex differences observed in in vivo bystander effects also remain to be uncovered. We hypothesized that the radiation-induced expression of microRNAs in exposed and bystander tissue may be distinct in males and females. Using a well-establish bystander mouse model when the animal’s head is exposed, while the body is completely protected by a medical-grade shield, we have for the first time shown that radiation exposure triggers a significant and sex-specific deregulation of the microRNAome in the non-exposed bystander spleen. The altered miRNA levels were paralleled by sex-specific changes in the levels of the miRNA processing enzyme Dicer and components of the RNA-induced silencing complex (RISC). Sterilization of animals resulted in drastic microRNAome alterations and significantly affected radiation and bystander miRNA responses. Our data may provide a roadmap for further analysis of the role of microRNAome in genotoxic stress responses and may help us explain sex specificity of radiation-induced carcinogenesis.     

Two types of X-ray-induced radioresistance in mice: Presence of 4 dose ranges with distinct biological effects

Preirradiation with 0.05 Gy of X rays 2 months before a second exposure to a mid-lethal dose significantly enhanced the survival rate in both female and male ICR strain mice. The radioresistance was observed between 2–2.5 months after exposure to 0.05 Gy. It did not appear within 1.5 months, and disappeared after 3 months. This radioresistance was induced only by whole-body preirradiation (not by partial irradiation of the head or the trunk). On the other hand, preirradiation with 0.30 Gy as well as 0.50 Gy resulted in radioresistance 2 weeks later, but not 2 months later. The radioresistance was induced by whole-body preirradiation or partial preirradiation of the trunk. No radioresistance was evident after exposure of intermediate preirradiation doses of 0.15 and 0.20 Gy administered before 2 months and 2–5 weeks, respectively. The present and previous results show that the biological effects of ionizing radiation may be distinguished with the following four radiation dose ranges; (1) below 0.025 Gy: no radioresistance after 2 months; (2) 0.05–0.10 Gy: significant radioresistance after 2–2.5 months; (3) 0.20 Gy: no radioresistance after 2–5 weeks; and (4) 0.30–0.50 Gy or more: significant radioresistance after 2 weeks. These results conflict with previous findings of the biological effects of ionizing radiation in which the radiation hazard increases in relation to increasing accumulated doses. Some stimulation, in addition to adaptation, by low dose irradiation may have occurred.     

New photo-induced effects of reactivation and protection of yeast cells under lethal UVB radiation

Brief exposure of yeasts to low-intensity monochromatic light (400–730 nm) has revealed the effects of photoreactivation and photoprotection of the cells inactivated by medium wave UVB radiation (290–320 nm). The red spectral region with a maximum at 680 nm has been found to be the most active in the initiation of photoreactivation and photoprotection. It has been noted that, according to the regularities investigated, these processes differ fundamentally from the known processes of enzymatic photoreactivation and photoprotection, which have a spectral response limited by, respectively, blue (<450 nm) and near (<380 nm) UV light. The data obtained make possible to consider the observed effects of photoreactivation and photo-protection as the manifestation of functioning of some light-dependent defense system capable of increasing the resistance of cells to UVB radiation.     

Radiation-induced bystander effects in the Atlantic salmon (salmo salar L.) following mixed exposure to copper and aluminum combined with low-dose gamma radiation

Very little is known about the combined effects of low doses of heavy metals and radiation. However, such “multiple stressor” exposure is the reality in the environment. In the work reported in this paper, fish were exposed to cobalt 60 gamma irradiation with or without copper or aluminum in the water. Doses of radiation ranged from 4 to 75 mGy delivered over 48 or 6 h. Copper doses ranged from 10 to 80 μg/L for the same time period. The aluminum dose was 250 μg/L. Gills and skin were removed from the fish after exposure and explanted in tissue culture flasks for investigation of bystander effects of the exposures using a stress signal reporter assay, which has been demonstrated to be a sensitive indicator of homeostatic perturbations in cells. The results show complex synergistic interactions of radiation and copper. Gills on the whole produce more toxic bystander signals than skin, but the additivity scores show highly variable results which depend on dose and time of exposure. The impacts of low doses of copper and low doses of radiation are greater than additive, medium levels of copper alone have a similar level of effect of bystander signal toxicity to the low dose. The addition of radiation stress, however, produces clear protective effects in the reporters treated with skin-derived medium. Gill-derived medium from the same fish did not show protective effects. Radiation exposure in the presence of 80 μg/L led to highly variable results, which due to animal variation were not significantly different from the effect of copper alone. The results are stressor type, stressor concentration and time dependent. Clearly co-exposure to radiation and heavy metals does not always lead to simple additive effects.     

Protective effects of <Emphasis Type="SmallCaps">l</Emphasis>-selenomethionine on space radiation induced changes in gene expression

Ionizing radiation can produce adverse biological effects in astronauts during space travel. Of particular concern are the types of radiation from highly energetic, heavy, charged particles known as HZE particles. The aims of our studies are to characterize HZE particle radiation induced biological effects and evaluate the effects of l-selenomethionine (SeM) on these adverse biological effects. In this study, microarray technology was used to measure HZE radiation induced changes in gene expression, as well as to evaluate modulation of these changes by SeM. Human thyroid epithelial cells (HTori-3) were irradiated (1 GeV/n iron ions) in the presence or in the absence of 5 μM SeM. At 6 h post-irradiation, all cells were harvested for RNA isolation. Gene Chip U133Av2 from Affymetrix was used for the analysis of gene expression, and ANOVA and EASE were used for a determination of the genes and biological processes whose differential expression is statistically significant. Results of this microarray study indicate that exposure to small doses of radiation from HZE particles, 10 and 20 cGy from iron ions, induces statistically significant differential expression of 196 and 610 genes, respectively. In the presence of SeM, differential expression of 77 out of 196 genes (exposure to 10 cGy) and 336 out of 610 genes (exposure to 20 cGy) is abolished. In the presence or in the absence of SeM, radiation from HZE particles induces differential expression of genes whose products have roles in the induction of G1/S arrest during the mitotic cell cycle, as well as heat shock proteins. Some of the genes, whose expressions were affected by radiation from HZE particles and were unchanged in irradiated cells treated with SeM, have been shown to have altered expression levels in cancer cells. The conclusions of this report are that radiation from HZE particles can induce differential expression of many genes, some of which are known to play roles in the same processes that have been shown to be activated in cells exposed to radiation from photons (like cell cycle arrest in G1/S), and that supplementation with SeM abolishes HZE particle-induced differential expression of many genes. Understanding the roles that these genes play in the radiation-induced transformation of cells may help to decipher the origins of radiation-induced cancer.     

Radiation effects on development

It has been widely reported that prenatal exposure to ionizing radiation can interfere with embryonic and fetal development, depending on dose and gestational age in which exposure occurs. According to several studies on animal models, different well-defined stages during prenatal life can be distinguished in relation to teratogenic effects. During the preimplantation stage, elevated doses of radiation can result in abortion, while lower doses may produce genomic damage that is usually repaired. On the other hand, during the organogenesis stage in mice (embryonic day 6.5 [E6.5] to E13.5), irradiation is associated with increased incidence of malformation and intrauterine growth restriction (IUGR). Later exposure is linked to brain damage. Doses used in animal studies are generally higher than those used for diagnostic procedures in humans. Usually, radiation exposure to diagnostic range (<0.05 Gy = 5 rads) is not associated with an increased risk of congenital anomalies. In human studies, elevated doses produce adverse outcomes, depending on stage of development, as in animal studies. Blastogenesis (up to two weeks) is associated with failure to implant or no significant health effects. An increased risk of malformation and growth retardation can be observed for two to seven weeks exposure (organogenesis stage), while exposure at later stages (fetogenesis) is mainly associated with brain damage. In this review we focus on the relevance of estimating the cumulative dose of radiation to the fetus and the gestational age in which exposure occurs, to provide appropriate counseling to pregnant women.     

The role of regulatory networks of the cell response to damages in radiation effects

In view of modern knowledge and concepts about components, function and mechanisms of response of cell molecular structures to damaging effects, response which is generating specialized modules of reactions, it is shown that main components of the mechanism of maintenance of genome constancy at ionizing radiation exposure are checkpoints of cell cycle, DNA repair and apoptosis. They operate under the control of a genetic system at participation of Tp53 gene, corresponding protein and of regulatory networks formed by cascades of mitogen-activated protein kinases (MAPK). At ionizing radiation exposure the MAPK special modules participate in formation of radiation effect: ERK 1/2 (extracellular signal-regulated kinase 1 and 2), JNK/SAPK (c-Jun N-terminal kinase/stress activated protein kinase) and p38 MAPK. Executing physiological functions of maintenance of normal life activity of cells, they do not lose this capacity after exposure to ionizing radiation, participating in formation of radiation effect in a wide range of doses, and are inactivated only by exposure to very high doses. It is concluded that in light of the modern data the main problem is not a problem of mechanisms of biological effect of ionizing radiation but a problem of biological mechanisms of radiation exposure.     

The effect of pesticides on the development in rats of osteosarcomas induced by 90Sr]

In experiments with rats the authors have assessed the development of remote effects of radiation (90Sr) combined with chronic exposure to chlorophos and lindane within a wide range of doses. It has been shown that chronically administered chlorophos and lindane have no carcinogenic and cocarcinogenic effects.     

Influence of prior exposure to low-dose adapting radiation on radiation-induced teratogenic effects in fetal mice with varying Trp53 function

Teratogenesis in tails and limb digits of fetal mice with varying Trp53 status was examined after exposure of pregnant females to 4 Gy gamma radiation with and without a prior 30-cGy exposure. Prior low-dose exposure modified the teratogenic effects of radiation in a manner dependent upon Trp53 status and gestation time. A 4-Gy exposure on gestation day 11 resulted in tail shortening and digit abnormalities. A 30-cGy exposure 24 h prior to a 4-Gy radiation exposure on day 11 reduced the extent of both digit abnormalities and the tail-shortening effects in Trp53(+/+) fetuses and also reduced tail shortening in Trp53(+/-) fetuses, but to a lesser extent. However, the pre-exposure enhanced the tail-shortening effects of 4 Gy in Trp53(-/-) fetuses. In contrast, a 30-cGy exposure given 24 h prior to a 4-Gy exposure on gestation day 12 had no effect on the reduced tail length resulting from the 4-Gy exposure of Trp53(+/+) or Trp53(+/-) fetuses, but it partly protected Trp53(-/-) fetuses against reduced tail length. A 4-Gy exposure alone on day 12 did not result in any increase in the frequency of digit abnormalities in Trp53(-/-) fetuses so any protective effect of the preirradiation could not be detected. However, the preirradiation did result in protection against in digit abnormalities in Trp53(+/-) fetuses. We conclude that radiation-induced teratogenesis reflects both Trp53-dependent and independent processes that lead to apoptosis, and these respond differently to prior adapting doses.     

An evaluation of several methods for assessing the effects of occupational exposure to radiation

Several methods for the analysis of occupational radiation exposure data, including procedures based on Cox's proportional hazards model, are presented and evaluated. Issues of interest include the contribution of an external control, the effective handling of highly skewed exposure data, and the potential for detecting effects in populations occupationally exposed to radiation. Expressions for evaluating the power of various procedures are derived and applied to data from the Hanford population in order to determine power curves for detecting leukemia effects, with both additive and multiplicative linear models being used. It is found that the introduction of an external control can increase power, although not when an overall adjustment factor must be estimated from the data or when death rates for the study population are substantially lower than those for the control population. It is also found that very little power is lost if exposures are grouped. Finally, the power calculations indicate, as expected, that in analyses of occupationally exposed populations, such as the Hanford workers, there is very little chance of detecting radiation effects at the levels of our current estimates. However, power is reasonably good for detecting effects that are 10 to 15 times larger.