Effect of internal contamination with tritiated water on the neoplastic colonies in the lungs, innate anti-tumour reactions, cytokine profile, and haematopoietic system in radioresistant and radiosensitive mice.

Tritium is a potentially significant source of internal radiation exposure which, at high levels, can be carcinogenic. We evaluated whether single intraperitoneal injection of BALB/c and C57BL/6 mice with tritiated water (HTO) leading to exposure to low (0.01 or 0.1 Gy) and intermediate (1.0 Gy) cumulative whole-body doses of ß radiation is immunosuppressive, as judged by enhancement of artificial tumour metastases, functioning of NK lymphocytes and macrophages, circulating cytokine's levels, and numbers of bone marrow, spleen, and peripheral blood cells. We demonstrate that internal contamination of radiosensitive BALB/c and radioresistant C57BL/6 mice with HTO at all the absorbed doses tested did not affect the development of neoplastic colonies in the lungs caused by intravenous injection of syngeneic cancer cells. However, internal exposure of BALB/c and C57BL/6 mice to 0.1 and 0.01 Gy of ß radiation, respectively, up-regulated cytotoxic activity of and IFN-γ synthesis in NK lymphocytes and boosted macrophage secretion of nitric oxide. Internal contamination with HTO did not affect the serum levels of pro- (IL-1ß, IL-2, IL-6, TNF-α,) and anti-inflammatory (IL-1Ra, IL-4, IL-10) cytokines. In addition, exposure of mice of both strains to low and intermediate doses from the tritium-emitted ß-particles did not result in any significant changes in the numbers of bone marrow, spleen, and peripheral blood cells. Overall, our data indicate that internal tritium contamination of both radiosensitive and radioresistant mice leading to low and intermediate absorbed ß-radiation doses is not immunosuppressive but may enhance some but not all components of anticancer immunity.

A Revised System of Radiological Protection Is Needed.

ABSTRACT: The system of radiological protection has been based on linear no-threshold theory and related dose-response models for health detriment (in part related to cancer induction) by ionizing radiation exposure for almost 70 y. The indicated system unintentionally promotes radiation phobia, which has harmed many in relationship to the Fukushima nuclear accident evacuations and led to some abortions following the Chernobyl nuclear accident. Linear no-threshold model users (mainly epidemiologists) imply that they can reliably assess the cancer excess relative risk (likely none) associated with tens or hundreds of nanogray (nGy) radiation doses to an organ (e.g., bone marrow); for 1,000 nGy, the excess relative risk is 1,000 times larger than that for 1 nGy. They are currently permitted this unscientific view (ignoring evolution-related natural defenses) because of the misinforming procedures used in data analyses of which many radiation experts are not aware. One such procedure is the intentional and unscientific vanishing of the excess relative risk uncertainty as radiation dose decreases toward assigned dose zero (for natural background radiation exposure). The main focus of this forum article is on correcting the serious error of discarding risk uncertainty and the impact of the correction. The result is that the last defense of the current system of radiological protection relying on linear no-threshold theory (i.e., epidemiologic studies implied findings of harm from very low doses) goes away. A revised system is therefore needed.

Low-dose gamma-irradiation inhibits IL-6 secretion from human lung fibroblasts that promotes bronchial epithelial cell transformation by cigarette-smoke carcinogen.

Despite decades of research in defining the health effects of low-dose (<100 mGy) ionizing photon radiation (LDR), the relationship between LDR and human cancer risk remains elusive. Because chemical carcinogens modify the tumor microenvironment, which is critical for cancer development, we investigated the role and mechanism of LDR in modulating the response of stromal cells to chemical carcinogen-induced lung cancer development. Secretion of proinflammatory cytokines such as interleukin-6 (IL-6), CXCL1 and CXCL5 from human lung fibroblasts was induced by cigarette-smoke carcinogen benzo[a]pyrene diol epoxide (BPDE), which was inhibited by a single dose of LDR. The activation of NF-κB, which is important for BPDE-induced IL-6 secretion, was also effectively suppressed by LDR. In addition, conditioned media from BPDE-treated fibroblasts activated STAT3 in the immortalized normal human bronchial epithelial cell line Beas-2B, which was blocked with an IL-6 neutralizing antibody. Conditioned medium from LDR-primed and BPDE-treated fibroblast showed diminished capacity in activating STAT3. Furthermore, IL-6 enhanced BPDE-induced Beas-2B cell transformation in vitro. These results suggest that LDR inhibits cigarette smoke-induced lung carcinogenesis by suppressing secretion of cytokines such as IL-6 from fibroblasts in lung tumor-prone microenvironment.

Modeling Cell Survival Fraction and Other Dose-Response Relationships for Immunodeficient C.B-17 SCID Mice Exposed to 320-kV X Rays.

US homeland security concerns related to potential misuse of γ-ray-emitting radiation sources employed in radiobiological research (eg, shielded cesium-137 irradiators) led to recommendations by the National Research Council to conduct studies into possibly replacing γ-ray irradiators used in research involving small rodent and other models with X-ray instruments. A limiting factor is suitability of the X-ray photon energy spectra. The objective of our research was to demonstrate the suitability of the radiation energy spectrum of 320-kV X rays after filtration (HVL = 4 mm Cu) for in-vivo cytotoxicity studies in immunodeficient C.B-17 SCID mice. By using a previously-published Hazard Function (HF) model to characterize dose-response relationships for in vivo bone marrow and spleen cell survival fractions and also to characterize the acute lethality risk (hematopoietic syndrome mode) we demonstrate that the filtered 320-kV X-ray beam appears suitable for such studies. A key finding for C.B-17 SCID mice when compared to results previously obtained for immunocompetent C.B-17 mice is that the immunodeficient mice appear to be more radioresistant, implicating a possible role of the immune system capacity in radiosensitivity of mammals.

A Comparison of Cs-137 γ Rays and 320-kV X-Rays in a Mouse Bone Marrow Transplantation Model.

US homeland security concerns regarding the potential misuse of some radiation sources used in radiobiological research, for example, cesium-137 (137Cs), have resulted in recommendations by the National Research Council to conduct studies into replacing these sources with suitable X-ray instruments. The objective of this research is to compare the effectiveness of an X-RAD 320 irradiator (PXINC 2010) with a 137Cs irradiator (Gammacell-1000 Unit) using an established bone marrow chimeric model. Using measured radiation doses for each instrument, we characterized the dose-response relationships for bone marrow and splenocyte ablation, using a cytotoxicity-hazard model. Our results show that the X-RAD 320 photon energy spectrum was suitable for ablating bone marrow at the 3 exposure levels used, similar to that of 137Cs photons. However, the 320-kV X-rays were not as effective as the much higher energy γ rays at depleting mouse splenocytes. Furthermore, the 3 X-ray levels used were less effective than the higher energy γ rays in allowing the successful engraftment of donor bone marrow, potentially as a result of the incomplete depletion of the spleen cells. More defined studies are warranted for determining whether bone marrow transplantation in mice can be successfully achieved using 320-kV X-rays. A higher X-ray dose then used is likely needed for transplantation success.

Genotoxicity of 1,3-butadiene and its epoxy intermediates.

Current risk assessments of 1,3-butadiene (BD*) are complicated by limited evidence of its carcinogenicity in humans. Hence, there is a critical need to identify early events and factors that account for the heightened sensitivity of mice to BD-induced carcinogenesis and to deter-mine which animal model, mouse or rat, is the more useful surrogate of potency for predicting health effects in BD-exposed humans. HEI sponsored an earlier investigation of mutagenic responses in mice and rats exposed to BD, or to the racemic mixture of 1,2-epoxy-3-butene (BDO) or of 1,2,3,4-diepoxybutane (BDO2; Walker and Meng 2000). In that study, our research team demonstrated (1) that the frequency of mutations in the hypoxanthine-guanine phosphoribosyl transferase (Hprt) gene of splenic T cells from BD-exposed mice and rats could be correlated with the species-related differences in cancer susceptibility; (2) that mutagenic-potency and mutagenic-specificity data from mice and rats exposed to BD or its individual epoxy intermediates could provide useful information about the BD metabolites responsible for mutations in each species; and (3) that our novel approach to measuring the mutagenic potency of a given chemical exposure as the change in Hprt mutant frequencies (Mfs) over time was valuable for estimating species-specific differences in mutagenic responses to BD exposure and for predicting the effect of BD metabolites in each species. To gain additional mode-of-action information that can be used to inform studies of human responses to BD exposure, experiments in the current investigation tested a new set of five hypotheses about species-specific patterns in the mutagenic effects in rodents of exposure to BD and BD metabolites: 1. Repeated BD exposures at low levels that approach the occupational exposure limit for BD workers (set by the U.S. Occupational Safety and Health Administration) are mutagenic in female mice. 2. The differences in mutagenic responses of the Hprt gene to BD in similarly exposed rodents of a given species (reported in various earlier studies) are primarily associated with age-related thymus activity and trafficking of T cells and with sex-related differences in BD metabolism. 3. The mutagenic potency of the stereochemical forms of BD's epoxy intermediates plays a significant role in the species-related mutagenicity of BD. 4. The hydrolysis-detoxification pathway of BD through 1,2-dihydroxy-3-butene (BD-diol) is a major contributor to mutagenicity at high-level BD exposures in mice and rats. 5. Significant and informative species-specific differences in mutation spectra can be identified by examining both large- and small-scale genetic alterations in the Hprt gene of BD-exposed mice and rats. The first four hypotheses were tested by exposing mice and rats to BD, meso-BDO2, or BD-diol and measuring Hprt Mfs as the primary biomarker. For this, we used the T-cell-cloning assay of lymphocytes isolated from the spleens of exposed and control (sham-exposed) mice and rats. The first hypothesis was tested by exposing female B6C3F1 mice (4 to 5 weeks of age) by inhalation for 2 weeks (6 hours/day, 5 days/week) to 0 or 3 ppm BD. Hprt Mfs were measured at the time of peak mutagenic response after exposure for this age of mice. We then compared the resulting data to those from mutagenicity studies with mice of the same age that had been exposed in a similar protocol to higher levels of BD (Walker and Meng 2000). In mice exposed to 3 ppm BD (n = 27), there was a significant 1.6-fold increase over the mean background Hprt Mf in control animals (n = 24, P = 0.004). Calculating the efficiency of Hprt mutant induction, by dividing induced Hprt Mfs by the respective BD exposure levels, demonstrated that the mutagenic potency of 3 ppm BD was twice that of 20 ppm BD and almost 20 times that of 625 or 1250 ppm BD in exposed female mice. Sample-size calculations based on the Hprt Mf data from this experiment demonstrated the feasibility of conducting a future experiment to find out whether induced Mfs at even lower exposure levels (between 0.1 and 1.0 ppm BD) fit the supralinear exposure-response curve found with exposures between 3.0 and 62.5 ppm BD, or whether they deviate from the curve as Mf values approach the background levels found in control animals. The second hypothesis was tested by estimating mutagenic potency for female mice exposed by inhalation for 2 weeks to 0 or 1250 ppm BD at 8 weeks of age and comparing this estimate to that reported for female mice exposed to BD in a similar protocol at 4 to 5 weeks of age (Walker and Meng 2000). For these two age groups, the shapes of the mutant splenic T-cell manifestation curves were different, but the mutagenic burden was statistically the same. These results support our contention that the disparity in responses reported in earlier Hprt-mutation studies of BD-exposed rodents is related more to age-related T-cell kinetics than to age-specific differences in the metabolism of BD. The third hypothesis was tested by estimating mutagenic potency for female mice and rats (4 to 5 weeks of age) exposed by inhalation to 2 or 4 ppm meso-BDO2 and comparing these estimates to those previously obtained for female mice and rats of the same age and exposed in a similar protocol to (+/-)-BDO2 (Meng et al. 1999b; Walker and Meng 2000). These exposures to stereospecific forms of BDO2 caused equivalent mutagenic effects in each species. This suggests that the small differences in the mutagenic potency of the individual stereoisomers of BDO2 appear to be of less consequence in characterizing the sources of BD-induced mutagenicity than the much larger differences between the mutagenic potencies of BDO2 and the other two BD epoxides (BDO and 1,2-dihydroxy-3,4-epoxybutane [BDO-diol]). The fourth hypothesis was tested in several experiments. First, female and male mice and rats (4 to 5 weeks of age) were exposed by nose only for 6 hours to 0, 62.5, 200, 625, or 1250 ppm BD or to 0, 6, 18, 24, or 36 ppm BD-diol primarily to establish BD and BD-diol exposure levels that would yield similar plasma concentrations of BD-diol. Second, animals were exposed in inhalation chambers for 4 weeks to 0, 6, 18, or 36 ppm BD-diol to determine the mutagenic potency estimates for these exposure levels and to compare these estimates with those reported for BD-exposed female mice and rats (Walker and Meng 2000) in which similar blood levels of BD-diol had been achieved. Measurements of plasma concentrations of BD-diol (via a gas chromatography and mass spectrometry [GC/MS] method developed for this purpose) showed these results: First, BD-diol accumulated in a sublinear manner during a single 6-hour exposure to more than 200 ppm BD. Second, BD-diol accumulated in a linear manner during single (6-hour) or repeated (4-week) exposure to 6 or 18 ppm BD and in a sublinear manner with increasing levels of BD-diol exposure. Third, exposure of female mice and rats to 18 ppm BD-diol produced plasma concentrations equivalent to those produced by exposure to 200 ppm BD (exposure to 36 ppm BD-diol produced plasma concentrations of about 25% of those produced by exposure to 625 ppm BD). In general, 4-week exposure to 18 or 36 ppm BD-diol was significantly mutagenic in female and male mice and rats. The differences in mutagenic responses between the species and sexes were not remarkable, except that the mutagenic effects were greatest in female mice. The substantial differences in the exposure-related accumulation of BD-diol in plasma after rodents were exposed to more than 200 ppm BD compared with the relatively small differences in the mutagenic responses to direct exposures to 6, 18, or 36 ppm BD-diol in female mice provided evidence that the contribution of BD-diol-derived metabolites to the overall mutagenicity of BD has a narrow range of effect that is confined to relatively high-level BD exposures in mice and rats. This conclusion was supported by the results of parallel analyses of adducts in mice and rats concurrently exposed to BD-diol (Powley et al. 2005b), which showed that the exposure-response curves for the formation of N-(2,3,4-trihydroxybutyl)valine (THB-Val) in hemoglobin, formation of N7-(2,3,4-trihydroxybutyl)guanine (THB-Gua) in DNA, and induction of Hprt mutations in exposed rodents were remarkably similar in shape (i.e., supralinear). Combined, these data suggest that trihydroxybutyl (THB) adducts are good quantitative indicators of BD-induced mutagenicity and that BD-diol-derived BDO-diol (the major source of the adducts) might be largely responsible for mutagenicity in rodents exposed to BD-diol or to hight levels of BD. The mutagenic-potency studies of meso-BDO2 and BD-diol reported here, combined with our earlier studies of BD, (+/-) BDO, and(+/-)-BDO2 (Walker and Meng 2000), revealed important trends in species-specific mutagenic responses that distinguish the relative degree to which the epoxy intermediates contribute to mutation induction in rodents at selected levels of BD exposures. These data as a whole suggest that , in mice, BDO2 largely causes mutations at exposures less than 62.5 ppm BD and that BD-diol-derived metabolites add to these mutagenic effects at higher BD exposures. In rats, it appears that the BD-diol pathway might account for nearly all the mutagenicity at the hight-level BD exposures where significant increases in Hprt Mfs are found and cancers are induced. Additional exposure-response studies of hemoglobin and DNA adducts specifics to BDO2, BDO-diol, and other reactive intermediates are needed to determine more definitively the relative contribution of each metabolite to the DNA alkylation and mutation patterns induced by BD exposure in mice and rats. For the fifth hypothesis, a multiplex polymerase chain reaction (PCR) procedure for the analysis of genomic DNA mutations in the Hprt gene of mice was developed. (ABSTRACT TRUNCATED)

Epidemiologic Studies Cannot Reveal the True Shape of the Dose-Response Relationship for Radon-Induced Lung Cancer.

A long-standing controversy is the correct shape of the dose-response relationship for lung cancer induction by inhaled radon (eg, residential radon) at low levels. A probabilistic approach is used in this commentary to show that cohort and case-control epidemiologic studies cannot reveal the true shape of the dose-response relationship for radon-induced lung cancer. Using the indicated approach, it is found that while the dose response for radon-induced lung cancer is expected to be threshold-increasing, the dose-response curve for the cancer incidence when cancers caused by smoking and other carcinogens are included is expected to be threshold-decreasing (ie, threshold-hormetic), as low-level radon can protect from cancer induction by other carcinogens via stimulating the body's natural defenses against cancer. These defenses include DNA damage repair, removal of aberrant cells via apoptosis, suppression of cancer promoting inflammation, and anticancer immunity.

The LNT model for cancer induction is not supported by radiobiological data.

The hallmarks of cancer have been the focus of much research and have influenced the development of risk models for radiation-induced cancer. However, natural defenses against cancer, which constitute the hallmarks of cancer prevention, have largely been neglected in developing cancer risk models. These natural defenses are enhanced by low doses and dose rates of ionizing radiation, which has aided in the continuation of human life over many generations. Our natural defenses operate at the molecular, cellular, tissue, and whole-body levels and include epigenetically regulated (epiregulated) DNA damage repair and antioxidant production, selective p53-independent apoptosis of aberrant cells (e.g. neoplastically transformed and tumor cells), suppression of cancer-promoting inflammation, and anticancer immunity (both innate and adaptive components). This publication reviews the scientific bases for the indicated cancer-preventing natural defenses and evaluates their implication for assessing cancer risk after exposure to low radiation doses and dose rates. Based on the extensive radiobiological evidence reviewed, it is concluded that the linear-no-threshold (LNT) model (which ignores natural defenses against cancer), as it relates to cancer risk from ionizing radiation, is highly implausible. Plausible models include dose-threshold and hormetic models. More research is needed to establish when a given model (threshold, hormetic, or other) applies to a given low-dose-radiation exposure scenario.

Low-dose radiation risk extrapolation fallacy associated with the linear-no-threshold model.

Managing radiation risks typically involves establishing regulations that limit radiation exposure. The linear-no-threshold (LNT) dose-response model has been the traditional regulatory default assumption. According to the LNT model, for low a linear-energy-transfer (LET) radiation-induced stochastic effects (e.g., neoplastic transformation and cancer), the risk increases linearly without a threshold. Any radiation exposure is predicted to increase the number of cancer cases among a large population of people. Cancer risk extrapolation from high to low doses based on this model is widespread. Here, indirect evidence is provided that the excess cancer risk calculated at very low doses of low-LET radiation (e.g., around 1 mGy), based on extrapolating from high dose data for an irradiated human population using the LNT model, is likely a phantom excess risk. Indirect evidence is provided, suggesting that for brief exposures to low-LET radiation doses on the order of 1 mGy, that a decrease below the spontaneous level is many orders of magnitude more probable than for any increase in risk as would be predicted by extrapolating from high to low doses using the LNT model. Such a decrease is, however, not expected after exposure to high-LET alpha radiation. The risk reduction has been largely attributed to the induction of a protective apoptosis-mediated (PAM) process that selectively eliminates cells that contain genomic instability (e.g., mutant and neoplastically transformed cells). The PAM process appears to require a dose-rate-dependent stochastic threshold for activation whose minimum is estimated to possibly be as low as 0.01 mGy for X-rays and gamma rays. However, if the dose is too high (e.g., above 250 mGy for brief exposure at a high rate to X-rays or gamma rays), the PAM process is not expected to be activated. For protracted exposure to X-rays or gamma rays, doses as high as 400 mGy (and possibly higher) may activate the PAM process.

A Critique of Recent Epidemiologic Studies of Cancer Mortality Among Nuclear Workers.

Current justification by linear no-threshold (LNT) cancer risk model advocates for its use in low-dose radiation risk assessment is now mainly based on results from flawed and unreliable epidemiologic studies that manufacture small risk increases (ie, phantom risks). Four such studies of nuclear workers, essentially carried out by the same group of epidemiologists, are critiqued in this article. Three of the studies that forcibly applied the LNT model (inappropriate null hypothesis) to cancer mortality data and implicated increased mortality risk from any radiation exposure, no matter how small the dose, are demonstrated to manufacture risk increases for doses up to 100 mSv (or 100 mGy). In a study where risk reduction (hormetic effect/adaptive response) was implicated for nuclear workers, it was assumed by the researchers to relate to a "strong healthy worker effect" with no consideration of the possibility that low radiation doses may help prevent cancer mortality (which is consistent with findings from basic radiobiological research). It was found with basic research that while large radiation doses suppress our multiple natural defenses (barriers) against cancer, these barriers are enhanced by low radiation doses, thereby decreasing cancer risk, essentially rendering the LNT model to be inconsistent with the data.

Adaptive response for chromosomal inversions in pKZ1 mouse prostate induced by low doses of X radiation delivered after a high dose.

Adaptive responses are induced by stress such as X radiation and result in a lower than expected biological response. Two-dose adaptive response experiments typically involve a low priming dose followed by a subsequent high radiation dose. Here, we used a sensitive in vivo chromosomal inversion assay to demonstrate for the first time an adaptive response when a low dose (0.01-1 mGy) was given several hours after a high 1000-mGy radiation dose. The adaptive responses in this study were of similar magnitude to the two-dose adaptive responses previously observed in this test system when the low dose was given first. A chromosomal inversion adaptive response was also induced by two 1000-mGy doses and when a 1-mGy dose was preceded or followed by a dose of 0.01 mGy, but not by two 4000-mGy doses. This is also the first example of an adaptive response when both doses are low. Our data agree with previous reports of an on-off mechanism of adaptive response. The induction of an adaptive response by a low dose after a high damaging dose provides evidence that the mechanisms underlying radiation adaptive responses are not due to prevention of damage induced by the high dose but to modulation of the cellular response to this damage.

Extremely low priming doses of X radiation induce an adaptive response for chromosomal inversions in pKZ1 mouse prostate.

An adaptive response is a response to a stress such as radiation exposure that results in a lower than expected biological response. We describe an adaptive response to X radiation in mouse prostate using the pKZ1 chromosomal inversion assay. pKZ1 mice were treated with a priming dose of 0.001, 0.01, 1 or 10 mGy followed 4 h later by a 1000-mGy challenge dose. All priming doses caused a similar reduction in inversions compared to the 1000-mGy group, supporting the hypothesis that the adaptive response is the result of an on/off mechanism. The adaptive response was induced by a priming dose of 0.001 mGy, which is three orders of magnitude lower than has been reported previously. The adaptive responses completely protected against the inversions that would have been induced by a single 1000-mGy dose as well as against a proportion of spontaneous background inversions. The distribution of inversions across prostate gland cross sections after priming plus challenge irradiation suggested that adaptive responses were predominantly due to reduced low-dose radiation-induced inversions rather than to reduced high-dose radiation-induced inversions. This study used radiation doses relevant to human exposure.