The potential genotoxic effect resulting from occupational exposure of medical professionals to IR has raised significant concerns within the medical community (
13). Micronuclei are regarded as early biological indicators of genetic toxicity carcinogenesis (
11).
Our study demonstrated that exposure to low doses of IR significantly increased the noticeable level of MN in oral mucosal cells compared to non-exposed individuals. The use of oral mucosal cells to investigate occupational genetic damage from low doses of IR has been limited in two studies, showing that the frequency of MN was significantly higher in the exposed group than in the control group (
22,
23).
In this study, the highest level of MN was observed in the endoscopy group, while the lowest level was in the radiology group. Although this difference was not statistically significant, it raises questions, given that fluoroscopy-guided procedures, such as angiography, typically involve higher radiation exposure. However, several possible explanations exist. Endoscopy personnel, particularly those performing ERCP, often remain in close physical proximity to the patient and the fluoroscopy unit, which increases their exposure to scattered radiation (
7,
24,
25). Furthermore, multiple studies have shown that adherence to radiation safety protocols is often suboptimal among endoscopy staff (
26-
28). For instance, a recent study of 159 therapeutic endoscopists found that many lacked formal training in the use of fluoroscopy systems, and the consistent use of protective equipment, such as lead glasses and shielding curtains, was low. Over half of the participants did not routinely wear a dosimeter (
28). In contrast, radiology staff are generally more aware of radiation hazards and tend to operate imaging devices from shielded control rooms (
7). These differences in behavior, training, and protective practices may explain the relatively higher MN frequency observed in the endoscopy group despite the expected higher risk in angiography.
Aging leads to a decline in the efficiency of DNA repair processes and the accumulation of mutations, resulting in increased levels of DNA damage (
29). In our study, an increase in age did not lead to a rise in the MN levels in both exposed and non-exposed groups. The average age of both groups is approximately 38 years. Also, in the study by Aguiar Torres et al., the absence of a link between age and MN frequency may be due to the average age of participants in both groups (around 45 years). Given that participants in both groups are relatively young, they may not yet exhibit the increased levels of DNA damage typically associated with aging (
22).
In our study, no significant relationship was found between work experience and MN levels. While some studies have reported an increase in MN levels with an increase in work experience (
30-
32), some of these studies attributed this increase to aging (
31). Distinguishing whether the increase is due to aging or an increase in work experience requires further research and investigation (
32).
Smoking status is usually recognized as an important factor affecting MN frequency, but in this study, it was not significantly associated with the frequency of MN (
Table 3). Chemicals found in cigarette composition contain genotoxic substances (
18). Bonassi et al. (
33) showed that only heavy smokers (i.e., > 40 cigarettes/day) have a significant increase in MN frequency compared to nonsmokers. In our study, the tobacco consumption rates (cigarettes/day) were (3.2 ± 0.18).
In this study, two individuals from the exposed group mentioned alcohol consumption, and a significant relationship was observed between alcohol consumption and the frequency of MN (P > 0.05) (
Table 3). In a study by Singh et al. (
34), an increase in the frequency of MN in alcoholics and alcoholic smoker subjects as compared to healthy controls was found.
Micronuclei assays in buccal exfoliated cells have gained popularity as a minimally invasive biomarker for genomic damage in human populations. A comprehensive meta-analysis by Ceppi et al. (
18), which reviewed 63 studies, highlighted important methodological considerations, including controlling for confounding factors, adequate sample size, and appropriate statistical modeling. Their findings demonstrated a strong correlation between MN frequencies in buccal cells and PBL, supporting the use of buccal MN assays as reliable and sensitive indicators of genotoxic exposure. Additionally, the meta-analysis recommended scoring a minimum of 4,000 cells to reduce variability, which contrasts with the common practice of scoring 2,000 cells. Incorporating buccal MN evaluation in occupational health studies enables large-scale, noninvasive screening while maintaining robust predictive value for genomic damage.
One of the strengths of our study is that it is among the limited studies that utilized a simple and non-invasive method to assess genetic damage resulting from chronic occupational exposure to IR; however, other environmental factors may affect the result. In this study, the control group was selected from the same workplace, which was exposed similarly in terms of demographic factors and confounding factors, and various exposure departments were also investigated.
One of the limitations of this study is the absence of dosimetry data, as participants are not routinely monitored for radiation exposure, and no official dose records are available. This restricts our ability to conduct precise dose-response analyses between IR exposure and MN frequency. Future studies should incorporate real-time personal dosimetry monitoring to quantify individual radiation doses better and to strengthen the understanding of the dose-dependent genomic effects.
5.1. Conclusions
Our study demonstrated that evaluating MN in oral mucosal cells can serve as a simple, noninvasive screening method for the early detection of genomic damage in individuals exposed to IR. Based on our findings, we tentatively suggest a threshold of > 11 MN per 1,000 cells as a potential indicator for follow-up monitoring. This value, derived from the upper limit of the MN frequency distribution in the non-exposed population, may help guide future research and screening practices. It is recommended that this method be applied in larger populations and combined with dosimetry data to better assess dose-response relationships. Healthcare professionals routinely handling IR should adhere strictly to radioprotection protocols and radiation safety guidelines, utilizing all accessible protective equipment.