Systemic Genotoxic Effects Research Articles

Acetaldehyde as a Food Flavoring Substance: Aspects of Risk Assessment.

The Senate Commission on Food Safety (SKLM) of the German Research Foundation (DFG) has reviewed the currently available data in order to assess the health risks associated with the use of acetaldehyde as a flavoring substance in foods. Acetaldehyde is genotoxic in vitro. Following oral intake of ethanol or inhalation exposure to acetaldehyde, systemic genotoxic effects of acetaldehyde in vivo cannot be ruled out (induction of DNA adducts and micronuclei). At present, the key question of whether acetaldehyde is genotoxic and mutagenic in vivo after oral exposure cannot be answered conclusively. There is also insufficient data on human exposure. Consequently, it is currently not possible to reliably assess the health risk associated with the use of acetaldehyde as a flavoring substance. However, considering the genotoxic potential of acetaldehyde as well as numerous data gaps that need to be filled to allow a comprehensive risk assessment, the SKLM considers that the use of acetaldehyde as a flavoring may pose a safety concern. For reasons of precautionary consumer protection, the SKLM recommends that the scientific base for approval of the intentional addition of acetaldehyde to foods as a flavoring substance should be reassessed.

Telomere length and genotoxicity in the lung of rats following intragastric exposure to food-grade titanium dioxide and vegetable carbon particles.

Vegetable carbon (E153) and titanium dioxide (E171) are widely used as black and white food colour additives. The aim of this study was to assess gastrointestinal tight junction and systemic genotoxic effects in rats following exposure to E153 and E171 for 10 weeks by oral gavage once a week. The expression of tight junction proteins was assessed in intestinal tissues. Levels of DNA strand breaks, oxidatively damaged DNA and telomere length were assessed in secondary organs. Hydrodynamic suspensions of E153 and E173 indicated mean particles sizes of 230 and 270 nm, respectively, and only E153 gave rise to intracellular production of reactive oxygen species in colon epithelial (Caco-2) cells. Rats exposed to E153 (6.4 mg/kg/week) or E171 (500 mg/kg/week) had decreased gene expression of the tight junction protein TJP1 (P < 0.05). E153 (6.4 mg/kg/week) also decreased OCLN (P < 0.05) in the colon and occludin protein expression in the small intestine (P < 0.05). Furthermore, E153 or E171 exposed rats had shorter telomeres in the lung (P < 0.05). Plasma from particle-exposed rats also produced telomere shortening in cultured lung epithelial cells. There were unaltered levels of oxidatively damaged DNA in the liver and lung and no changes in the DNA repair activity of oxidatively damaged DNA in the lung. Altogether, these results indicate that intragastric exposure to E153 and E171 is associated with reduced tight junction protein expression in the intestinal barrier and telomere length shortening in the lung in rats.

Absence of genotoxic impact assessed by micronucleus frequency in circulating lymphocytes of workers exposed to cadmium

PurposeCd is considered as a genotoxic carcinogen for which a threshold can be identified. This threshold has, however, not been established and the shape of the relationship between Cd exposure and genotoxic effects is unknown. The aim of the present study was to analyse the shape of the dose-response relationship for the genotoxic effects of Cd in occupational settings. MethodsThe study has a cross-sectional design and includes 60 healthy male and female workers with known Cd exposure selected from two plants manufacturing or recycling nickel-Cd batteries. The frequency of MN was measured in circulating lymphocytes, and related to internal Cd doses (Cd-B, Cd-U). Determinants of MN frequency were traced by multivariate regression analysis. ResultsCd exposure covered a wide range as measured by Cd-B (0.02–1.26 μg/dL), Cd-U (0.26–15.80 μg/g creat) and seniority in the plant (1–42 years). Gender was the only parameter significantly associated with MN frequency, women having on average 8.5 additional MN/1000 BN cells compared to men. Cd-B, Cd-U or Ni-U did not influence MN frequency when adjusted for gender and other potential confounders. ConclusionThis finding is consistent with the existing knowledge on the mechanisms governing the genotoxic activity of Cd, which are all non-stochastic and thresholded. The threshold for systemic genotoxic effects of Cd is thus beyond the range of internal exposure considered in the present investigation.

A Functional Immune System Is Required for the Systemic Genotoxic Effects of Localized Irradiation

Nontargeted effects of ionizing radiation, by which unirradiated cells and tissues are also damaged, are a relatively new paradigm in radiobiology. We recently reported radiation-induced abscopal effects (RIAEs) in normal tissues; namely, DNA damage, apoptosis, and activation of the local and systemic immune responses in C57BL6/J mice after irradiation of a small region of the body. High-dose-rate, synchrotron-generated broad beam or multiplanar x-ray microbeam radiation therapy was used with various field sizes and doses. This study explores components of the immune system involved in the generation of these abscopal effects. The following mice with various immune deficiencies were irradiated with the microbeam radiation therapy beam: (1) SCID/IL2γR-/- (NOD SCID gamma, NSG) mice, (2) wild-type C57BL6/J mice treated with an antibody-blocking macrophage colony-stimulating factor 1 receptor, which depletes and alters the function of macrophages, and (3) chemokine ligand 2/monocyte chemotactic protein 1 null mice. Complex DNA damage (ie, DNA double-strand breaks), oxidatively induced clustered DNA lesions, and apoptotic cells in tissues distant from the irradiation site were measured as RIAE endpoints and compared with those in wild-type C57BL6/J mice. Wild-type mice accumulated double-strand breaks, oxidatively induced clustered DNA lesions, and apoptosis, enforcing our RIAE model. However, these effects were completely or partially abrogated in mice with immune disruption, highlighting the pivotal role of the immune system in propagation of systemic genotoxic effects after localized irradiation. These results underline the importance of not only delineating the best strategies for tumor control but also mitigating systemic radiation toxicity.

Abstract 4573: Localized synchrotron radiation in mice induces persistent systemic genotoxic events mediated by the functional immune system

Abstract The discovery of the radiation-induced bystander effect has expanded knowledge of radiobiological mechanisms of ionizing radiation. A counterpart in vivo phenomenon is the radiation-induced abscopal effect (RIAE). It is not known how radiation settings affect non-targeted normal tissues and therefore the risk of adverse RIAE. At the Australian Synchrotron we examined systemic effects of microbeam radiotherapy (MRT) and broad beam (BB) configurations, in mice that were locally exposed to a very short pulse of a high dose-rate synchrotron beam (49 Gy/sec). We determined how radiation volume and dose impact the RIAE. C57BL/6 mice were irradiated with 10 or 40 Gy incident dose of MRT or BB in an 8x8, 8x1, or 2x2-mm area of the right hind leg. Blood samples, irradiated skin and a variety of normal unirradiated tissues were collected for DNA damage analysis of double-strand breaks (DSBs) quantified as gamma-H2AX foci and oxidatitive clustered DNA lesions (OCDL). OCDLs elevated in a wide variety of unirradiated normal tissues. In out-of-field duodenum, a trend for elevated apoptotic cells was observed, however DSBs elevated only after exposure to lower doses. These genotoxic events were accompanied by changes in concentrations of MDC, CCL2/MCP1, Eotaxin, IL-10, TIMP-1, VEGF, TGFβ-1 and TGFβ-2 plasma cytokines and by changes in frequencies of macrophages, neutrophils and T-lymphocytes in duodenum. Overall, systemic radiation responses were dose-independent (1). The MRT irradiations was repeated in immune-deficient mice: NSG, CCL2 knock-outs, and in C57BL/6 mice treated with anti-CSF1R antibody which effectively depletes macrophages. Strikingly, these effects and the abscopal innate and adaptive immune effector responses were completely or partially abrogated in the mice with various immune deficiencies, highlighting the role of the functional immune system in propagation of systemic genotoxic effects of radiation. These findings have implications for the planning of therapeutic and diagnostic radiation to reduce the risk of radiation-related adverse systemic effects. 1. Ventura et al, Cancer Research, e-pub (2017). Citation Format: Jessica Ventura, Pavel Lobachevsky, Jason Palazzolo, Helen Forrester, Nicole Haynes, Alesia Ivashkevich, Andrew Stevenson, Christopher Hall, Vassilis Gorgoulis, John Hamilton, Alexandros Georgakilas, Calr Sprung, Olga A. Martin. Localized synchrotron radiation in mice induces persistent systemic genotoxic events mediated by the functional immune system [abstract]. In: Proceedings of the American Association for Cancer Research Annual Meeting 2018; 2018 Apr 14-18; Chicago, IL. Philadelphia (PA): AACR; Cancer Res 2018;78(13 Suppl):Abstract nr 4573.

English

This study evaluated the anti-allergenic properties of the aqueous extract of the stem bark from Bowdichia virgilioides (AEBv). Oral administration of AEBv inhibited the plasma protein leakage at 30 min post allergenic challenge in Swiss mice actively sensitized with ovalbumin (OVA). AEBv inhibited OVA-induced histamine release in vitro in tissues obtained from sensitized mice. AEBv-treated mice exhibited a lower influx of neutrophils and eosinophils in allergen-induced pleurisy 24 h post OVA-challenge. This treatment also reduced tumor necrosis factor (TNF)-&alpha; content in the pleural effluent. Furthermore, AEBv treatment drastically inhibited the high levels of interleukin (IL)-5 and CC chemokine eotaxin (CCL11) mRNA expression in pleural leukocytes after OVA-challenge. Preliminary toxic effects were assessed, and a qualitative phytochemical profile was performed. The extract contained condensate tannins, flavonoids, saponins, and steroids but not triterpenes and alkaloids. Oral treatment with AEBv did not induce signs of systemic toxicity or genotoxic effects. These results demonstrated that AEBv is a potent inhibitor of contributors to the allergic inflammatory response, supporting its use in folk medicine to treat allergic conditions. Key words: Bowdichia virgilioides, allergy, inflammation, natural product.

In vitro and in vivo genotoxic effects of straight versus tangled multi-walled carbon nanotubes

Some multi-walled carbon nanotubes (MWCNTs) induce mesothelioma in rodents, straight MWCNTs showing a more pronounced effect than tangled MWCNTs. As primary and secondary genotoxicity may play a role in MWCNT carcinogenesis, we used a battery of assays for DNA damage and micronuclei to compare the genotoxicity of straight (MWCNT-S) and tangled MWCNTs (MWCNT-T) in vitro (primary genotoxicity) and in vivo (primary or secondary genotoxicity). C57Bl/6 mice showed a dose-dependent increase in DNA strand breaks, as measured by the comet assay, in lung cells 24 h after a single pharyngeal aspiration of MWCNT-S (1–200 μg/mouse). An increase was also observed for DNA strand breaks in lung and bronchoalveolar lavage (BAL) cells and for micronucleated alveolar type II cells in mice exposed to aerosolized MWCNT-S (8.2–10.8 mg/m3) for 4 d, 4 h/d. No systemic genotoxic effects, assessed by the γ-H2AX assay in blood mononuclear leukocytes or by micronucleated polychromatic erythrocytes (MNPCEs) in bone marrow or blood, were observed for MWCNT-S by either exposure technique. MWCNT-T showed a dose-related decrease in DNA damage in BAL and lung cells of mice after a single pharyngeal aspiration (1–200 μg/mouse) and in MNPCEs after inhalation exposure (17.5 mg/m3). In vitro in human bronchial epithelial BEAS-2B cells, MWCNT-S induced DNA strand breaks at low doses (5 and 10 μg/cm2), while MWCNT-T increased strand breakage only at 200 μg/cm2. Neither of the MWCNTs was able to induce micronuclei in vitro. Our findings suggest that both primary and secondary mechanisms may be involved in the genotoxicity of straight MWCNTs.

Genotoxicity of inhaled nanosized TiO2 in mice

In vitro studies have suggested that nanosized titanium dioxide (TiO2) is genotoxic. The significance of these findings with respect to in vivo effects is unclear, as few in vivo studies on TiO2 genotoxicity exist. Recently, nanosized TiO2 administered in drinking water was reported to increase, e.g., micronuclei (MN) in peripheral blood polychromatic erythrocytes (PCEs) and DNA damage in leukocytes. Induction of micronuclei in mouse PCEs was earlier also described for pigment-grade TiO2 administered intraperitoneally. The apparent systemic genotoxic effects have been suggested to reflect secondary genotoxicity of TiO2 due to inflammation. However, a recent study suggested that induction of DNA damage in mouse bronchoalveolar lavage (BAL) cells after intratracheal instillation of nanosized or fine TiO2 is independent of inflammation. We examined here, if inhalation of freshly generated nanosized TiO2 (74% anatase, 26% brookite; 5 days, 4h/day) at 0.8, 7.2, and (the highest concentration allowing stable aerosol production) 28.5mg/m3 could induce genotoxic effects in C57BL/6J mice locally in the lungs or systematically in peripheral PCEs. DNA damage was assessed by the comet assay in lung epithelial alveolar type II and Clara cells sampled immediately following the exposure. MN were analyzed by acridine orange staining in blood PCEs collected 48h after the last exposure. A dose-dependent deposition of Ti in lung tissue was seen. Although the highest exposure level produced a clear increase in neutrophils in BAL fluid, indicating an inflammatory effect, no significant effect on the level of DNA damage in lung epithelial cells or micronuclei in PCEs was observed, suggesting no genotoxic effects by the 5-day inhalation exposure to nanosized TiO2 anatase. Our inhalation exposure resulted in much lower systemic TiO2 doses than the previous oral and intraperitoneal treatments, and lung epithelial cells probably received considerably less TiO2 than BAL cells in the earlier intratracheal study.

Micronucleus assays in rodent tissues other than bone marrow

This report updates previous reviews that were conducted as part of the third and fourth International Workshops on Genetic Toxicology Testing of micronucleus (MN) assays in rodent tissues other than bone marrow. Tissues discussed here are liver, lung, skin, colon, spleen, testes and foetal/neonatal tissues with transplacental exposure. Previous reviews have been updated to include literature published after 2000. In addition to the previously described tissues, MN assays in bladder, buccal mucosal cells, stomach and vagina are also included. MN assays using tissues other than bone marrow are critical for risk assessments, for in situ evaluation and for studies of systemic genotoxic effects and modes of action. Protocols for the majority of assays in tissues other than bone marrow have not yet been well standardised and validated for regulatory application, and further development is needed to support regulatory studies.

Inhalation of formaldehyde does not induce genotoxic effects in broncho-alveolar lavage (BAL) cells of rats

Male Fischer-344 rats were exposed to formaldehyde (FA) by inhalation for 4 weeks (6h/day, 5 days/week). Groups of six rats each were exposed to the target concentrations of 0, 0.5, 1, 2, 6, 10 and 15ppm. Potential genotoxic effects in the lung were investigated as part of a comprehensive study on local and systemic toxic and genotoxic effects. Broncho-alveolar lavage (BAL) cells were obtained by lung lavage with physiological saline and counted. From one half of the cells, slides for the micronucleus test (MNT) were prepared by cytocentrifugation; with the other half, the comet assay was performed. DNA migration in the comet assay was measured both directly and after irradiation of the cells with 2Gy gamma-radiation. The latter modification of the comet assay was included to increase its sensitivity for the detection of DNA-protein cross-links (DPX). For the comet assay, four slides were analysed from each cell sample, two without and two with irradiation. From each slide, 50 randomly selected cells were measured by image analysis and tail intensity (% tail DNA) and tail moment were evaluated. The frequency of micronucleated BAL cells was determined in acridine orange-stained slides by analysing 2000 cells per animal. FA did not induce any significant effect in any of the genotoxicity tests performed. It can be concluded that inhalation of FA in a 28 days study with FA concentrations up to 15ppm does not lead to genotoxic effects in BAL cells of rats. Because detection of DPX by the comet assay is a very sensitive biomarker of FA exposure of cells, our results suggest that there is no genetically relevant exposure of the lung after FA inhalation. The results of our inhalation study, which was performed under GLP conditions, call into question the biological significance of previously reported genotoxic effects in the lung of rats after FA inhalation.

Inhalation of formaldehyde does not induce systemic genotoxic effects in rats

Male Fischer-344 rats were exposed to formaldehyde (FA) by inhalation for 4 weeks (6 h/day, 5 days/week). Groups of six rats each were exposed to the target concentrations of 0, 0.5, 1, 2, 6, 10 and 15 ppm. Potential systemic genotoxic effects were investigated as part of a comprehensive study on local and systemic toxic and genotoxic effects. For this purpose, peripheral blood samples were obtained by puncturing the retro-orbital venous plexus at the end of the exposure period. Blood sampling was carried out in a randomized sequence and samples were coded by sequence number to ensure blind evaluation. Blood samples were used for the comet assay, the sister chromatid exchange test (SCE test) and the micronucleus test (MNT). DNA migration in the comet assay was measured both directly and after irradiation of the blood samples with 2 Gy gamma-radiation. The latter modification of the comet assay was included to increase its sensitivity for the detection of DNA–protein cross-links (DPX). The following positive control groups were included: one group (six animals) was treated with 50 mg/kg methyl methanesulfonate (MMS) once by gavage 4 h before blood sampling. Another group (six animals) was treated twice orally with 10 mg/kg cyclophosphamide (CP) with an interval of 24 h. The last application of CP was 24 h before blood sampling. For the comet assay, four slides were analysed from each blood sample, two without and two with irradiation. From each slide, 50 randomly selected cells were measured by image analysis, and tail intensity (% tail DNA) and tail moment were evaluated. For the SCE test, blood was cultured for 56 h in the presence of BrdU (10 μg/ml for the last 35 h) and SCE were counted in 30 second-division metaphases per sample. The MNT with peripheral blood was performed according to the instructions for the micronucleus analysis kit MICROFLOW (Litron Laboratories). Approximately 20,000 cells per sample were analysed by flow cytometry and the percentage of reticulocytes with micronuclei (MN) was determined. The positive control substances induced a significant effect in the genotoxicity tests and thus demonstrated the sensitivity of the test systems. FA did not induce any significant effect in any of the genotoxicity tests performed. It can be concluded that inhalation of FA in a 28-day study with FA concentrations up to 15 ppm does not lead to systemic genotoxic effects in the blood of rats.

Evaluation of Toxicological Monitoring Markers Using Proteomic Analysis

In our study, we chose three different concentrations of FA (0, 5, and 10 ppm), and cytotoxic (lipid peroxidation and protein oxidation) and genotoxic assays (DNA damage) were carried out on plasma, blood, and liver cells of rats subjected to FA-inhalation treatment. The profiles of plasma protein changes determined using 2-DE analysis were also evaluated to identify potential toxicological monitoring markers in FA-exposed rats. Concern was raised that our genotoxic analyses did not follow previously published research data and that the results of our rat plasma proteomic studies were difficult to interpret because we did not directly determine the plasma concentration of FA. However, we had already determined the concentration of FA using HPLC in an exposure chamber to monitor FA inhalation concentrations. We suggest that our experimental design was suitable to determine the FA effects on rat using an inhalation chamber system. For the similarity of genotoxic effects in lymphocytes and liver cells, we chose to present our data on the general cytological toxic effects on lipid peroxidation and protein oxidation which revealed a similarity between plasma and liver cells of FA-exposed rats. We have shown strong correlations between genotoxicity and lipid peroxidation, and lipid peroxidation is known to mediate DNA damage in many in vitro, and in vivo studies. We are well aware of the 'implausibility' of leukemia induction by FA, but for precisely this reason, we feel the need for further study to prove the systemic genotoxic effects of FA.

The Implausibility of Systemic Genotoxic Effects Measured by the Comet Assay in Rats Exposed to Formaldehyde

A recent publication reported genotoxic effects in the alkaline comet assay in lymphocytes and liver cells of rats exposed to formaldehyde (FA) by inhalation (Im,H.; et al. J. Proteome Res. 2006, 5, 1354-1366). Rats were exposed to 5 and 10 ppm FA for 2 weeks in inhalation chambers. A similar dose-related increase in DNA migration was measured in both cell types. These results are inconsistent with published data concerning FA toxicity: (i) Systemic genotoxic effects are reported, whereas previous animal experiments indicated only local effects. (ii) Similar effects were observed in liver cells and lymphocytes despite administration by inhalation. (iii) Increased DNA migration was measured, whereas FA-induced DNA-protein cross-links (DPX) should reduce DNA migration. These three aspects are critically discussed, and the plausibility of the results published by Im and colleagues is questioned.

Systemic genotoxic effects produced by light, and synergism with cigarette smoke in the respiratory tract of hairless mice.

No information is available on the interaction between cigarette smoke, the most important man-made carcinogen, and light, the most widespread natural carcinogen. In order to clarify this issue, SKH-1 hairless mice were exposed to environmental smoke and/or to the light emitted by sunlight-simulating halogen quartz bulbs. After 28 days, intermediate biomarkers were evaluated in skin, respiratory tract, bone marrow and peripheral blood. The results showed that, individually, the light produced extensive alterations not only in the skin but even at a systemic level, as shown by formation of bulky DNA adducts in both lung and bone marrow and induction of cytogenetic damage in bone marrow and peripheral blood erythrocytes. Smoke damaged the respiratory tract and produced significant alterations in the skin as well as an evident cytogenetic damage in both bone marrow and peripheral blood. Interestingly, as compared with exposure to smoke only, alternate daily cycles of exposure to both light and smoke significantly increased malondialdehyde concentrations and DNA adduct levels in lung and the frequency of micronuclei in pulmonary alveolar macrophages. The oral administration of sulindac, a non-steroidal anti-inflammatory drug, attenuated several biomarker alterations due to the combined exposure of mice to light and smoke. In conclusion, the light induces a systemic genotoxic damage, which is presumably due to the UV-mediated formation in the skin of long-lived derivatives, such as aldehydes. This damage may mechanistically be involved in light-related hematopoietic malignancies. In addition, the light displayed an insofar unsuspected synergism with smoke in the induction of DNA damage in the respiratory tract.