Author(s):
Mevissen M*, Ducray A, Ward JM, Kopp-Schneider A, McNamee JP, Wood AW, Rivero TM, Straif K.
* Veterinary Pharmacology & Toxicology, Department of Clinical Research and Veterinary Public Health (DCR-VPH), Vetsuisse Faculty, University of Bern, Bern.
International
Published in:
Environ Int 2025; 199: 109482
Published: 25.04.2025
on EMF:data since 23.08.2025
Further publications: Study funded by:

This review was partly funded by the World Health Organization (WHO).

Keywords for this study:
Effects on animals  |  Cancer diseases (unspecified)
Reviews
Go to EMF:data assessment

Effects of radiofrequency electromagnetic field exposure on cancer in laboratory animal studies, a systematic review.

Original Abstract

Background: More than ten years ago, the World Health Organization's (WHO) International Agency for Research on Cancer (IARC) published a monograph concluding there was limited evidence in experimental animals for carcinogenicity of Radio Frequency Electromagnetic Field (RF EMF).

Objective: The objective of this review was to systematically evaluate the effects of RF EMF exposure on cancer in experimental animals.

Methods: Eligibility criteria: Based on pre-established Populations, Exposures, Comparators, Outcomes, and Study Type (PECOS) criteria, studies in experimental animals of the following study types were included: chronic cancer bioassays, initiation-(co-)promotion studies, and studies with tumor-prone animals.

Information sources: MEDLINE (PubMed), Science Citation Index Expanded and Emerging Sources Citation Index (Web of Science), and the EMF Portal. Data abstraction and synthesis: Data are publicly available online as interactive visuals with downloadable metadata. We adapted the risk-of-bias (RoB) tool developed by Office of Health Assessment and Translation (OHAT) to include considerations pertinent to the evaluation of RF EMF exposure and cancer bioassays. Study sensitivity was assessed with a tool adopted from the Report on Carcinogens (RoC). We synthesized studies using a narrative approach. Effect size was calculated as the 1% Bayesian Average benchmark dose (BMD) of a respective study when dose-response or a trend was identified (see BMDAnalysisSupplementaryMaterial) (Supplement 1). Evidence Assessment: Certainty of the evidence (CoE) was assessed using the Grading of Recommendations, Assessment, Developing and Evaluations (GRADE) approach, as refined by OHAT. Evidence from chronic cancer bioassays was considered the most directly applicable to evaluation of carcinogenicity.

Results: We included 52 studies with 20 chronic bioassays No studies were excluded based on risk of bias concerns. Studies were not considered suitable for meta-analysis due to heterogeneity in study design, species, strain, sex, exposure characteristics, and cancer outcome. No or minimal evidence of RF EMF exposure-related cancer outcomes was found in most systems or organs in any study (these included gastrointestinal/digestive, kidney, mammary gland, urinary, endocrine, musculoskeletal, reproductive, and auditory). For lymphoma (18 studies), with 6 chronic bioassays (1,120 mice, 1,780 rats) inconsistency between two chronic bioassays was not plausibly explainable, and the CoE for lymphoma was rated 'moderate'. For brain tumors (20 studies), including 5 chronic bioassays (1,902 mice, 6,011 rats), an increase in glial cell-derived neoplasms was reported in two chronic bioassays in male rats. The CoE for an increased risk in glioma was judged as high. The BMD analysis was statistically significant for only one study and the BMD was 4.25 (95% CI 2.70, 10.24). For neoplasms of the heart (4 chronic bioassays with 6 experiments), 3 studies were performed in rats (∼2,165 animals), and 1 in mice (∼720 animals). Based on 2 bioassays, statistically significant increases in malignant schwannomas was judged as high CoE for an increase in heart schwannomas in male rats. The BMDs from the two positive studies were 1.92 (95 %CI 0.71, 4.15) and 0.177 (95 %CI 0.125, 0.241), respectively. Twelve studies reported neoplasms in the adrenal gland (5 chronic bioassays). The CoE for an increased risk in pheochromocytoma was judged as moderate. None of these findings were dose-dependent when compared to the sham controls. Sixteen studies investigated tumors of the liver with 5 of these being chronic bioassays. The CoE was evaluated as moderate for hepatoblastomas. For neoplasms of the lung (3 chronic bioassays), 8 studies were conducted in rats (∼1,296 animals) and 23 studies in mice (∼2,800 animals). In one chronic bioassay, a statistically significant positive trend was reported for bronchoalveolar adenoma or carcinoma (combined), which was rated as moderate CoE for an increase in lung neoplasms with some evidence from 2 initiation-(co-)promotion studies.

Discussion: Meta-analysis was considered inappropriate due to the heterogeneity in study methods. The GRADE/OHAT CoE framework has not been frequently applied to animal studies and experience to date suggests refinements are needed. We referred to standard methods in environmental health where CoE is framed in the context of strength of the evidence providing positive support for carcinogenicity. High CoE can be interpreted as the true effect is highly likely to be reflected in the apparent relationship. Moderate CoE indicates the true effect may be reflected in the apparent relationship. Cancer bioassays conducted in experimental animals are commonly used to identify potential human carcinogens. We note that the two tumor types with high CoE in animals in this systematic review are the same as those identified with limited evidence in humans by the IARC Working Group. However, even in cases where the animal evidence demonstrates high CoE, the extrapolation of risk from cancer bioassays to humans is particularly complex for RF EMF. Without a better understanding of the mechanism of the carcinogenicity of RF-EMF, the choice of exposure metric for risk extrapolation (whole body versus localized), intensity or cumulative exposure, whether or not a monotonic dose-response holds for carcinogenic effects, and whether SAR is the appropriate dose metric for adverse effects induced by RF-EMF, may be critical.

Other: This review was partially funded by the WHO radioprotection programme. The protocol for this review was registered in Prospero reg. no. CRD42021265563 and published in Environment International 2022 (Mevissen et al. 2022).

Keywords

Animal studies | Bioassay | Carcinogenesis, toxicity | Carcinogenicity | Radiofrequency electromagnetic fields | Radiofrequency exposure | Systematic review.

Copyright © 2025 The Author(s). Published by Elsevier Ltd.. All rights reserved.

Exposure:

RF/microwaves (1 - 300 GHz)
2450 MHz

EMF:data assessment

Summary

As exposure to mobile phones, Wi-Fi, and other wireless communication applications increases, the question of whether radiofrequency (RF) fields are carcinogenic to humans becomes highly relevant. The International Agency for Research on Cancer (IARC) currently classifies radiofrequency electromagnetic fields as “possibly carcinogenic” (2011) based on limited evidence from human and animal studies. For this review, the animal data are particularly pertinent. The IARC rationale is summarized in its preamble as follows: “The data indicate a carcinogenic effect, but are insufficient for a definitive evaluation because, for example, (b) unresolved questions remain concerning the adequacy of the design, conduct or analyses of the studies.” Since the IARC evaluation, many studies have been published, necessitating an updated assessment. This WHO-co-funded review aims to systematically assess the quality of experimental animal studies that address increased cancer incidence and rate the evidence using GRADE/OHAT.

Source: ElektrosmogReport | Issue 3/2025

Study design and methods

The authors conducted a comprehensive literature review up to July 2023 using MEDLINE, Web of Science, and the EMF Portal. They included chronic carcinogenicity bioassays (standardized long-term rodent studies, n = 10), initiation/promotion models (additional administration of a tumor initiator or promoter, n = 24), and experiments with tumor-prone strains (n = 18), provided that exposure was quantified by SAR values or field strengths. Selection followed pre-published PECOS criteria, and data extraction was performed in HAWC.  The OHAT RoB tool was used for risk of bias analysis, and GRADE was used to evaluate the quality of the evidence. Due to their high evidentiary value, chronic carcinogenicity bioassays were given special weight. Only endpoints (tumor types) confirmed in carcinogenicity bioassays could achieve a “high” evidence rating. A total of 52 primary studies published between 1978 and 2020 were included in this review.

Results

Compared with their respective controls, no indications of an increased cancer risk associated with mobile phone RF exposure were observed for most organ systems. Organ systems in which at least one study reported exposure-related effects were analyzed in detail. These included the lymphatic system, brain, heart, adrenal glands, liver, and lungs. A statistically and methodologically robust increase in tumor incidence attributable to RF exposure was found with high confidence in the heart (malignant schwannomas) and brain (malignant gliomas). The analysis also identified an increased tumor incidence with moderate confidence in the lymphatic system (malignant lymphomas), liver (hepatoblastomas), lungs (bronchioalveolar neoplasms), and adrenal glands (pheochromocytomas). However, a quantitative meta-analysis could not be performed due to the insufficient number of studies with sufficiently similar experimental designs.

Conclusions

In general, robust evidence of carcinogenic potential in animal models is relevant for identifying carcinogenic hazards to humans. Although extrapolating cancer bioassays to humans in the context of mobile phone exposure is complex, bioassays remain the best available tool for identifying hazards. This is partly because solid tumors in humans have such long latencies that epidemiological studies only become informative after technologies have been in widespread use for 10, 20, or more years.

Editor's note:

The review's data clearly indicate a carcinogenic effect of radiofrequency (RF) exposure from mobile phones in animal models. As noted above, these models are the best available means of assessing cancer risk in humans. In this context, the authors call for adapting the GRADE/OHAT criteria for animal studies. For instance, they argue that blinding prior to study initiation is irrelevant and that greater heterogeneity among animal models (e.g. inbred strains, outbred strains, and genetically heterogeneous models) is to be expected. This would explain many apparent irregularities, rendering it unnecessary to downgrade the quality of the evidence for multiple studies. The two studies chiefly supporting the high-confidence evidence of an increased cancer risk were published in 2018 (Falcioni et al., 2018; National Toxicology Program, 2018) and discussed in the ElektrosmogReport (June 2019), among others. In the Falcioni study, whole-body exposure was applied with SAR values between 0.001 and 0.1 W/kg, similar to human exposure levels. Despite having access to these data for about seven years, regulatory decision-makers have not taken any consequential action to date. Given the global implications for human health, the authors consider this omission negligent. (RH)

Falcioni L, Bua L, Tibaldi E, Lauriola M (2018). Report of Final Results Regarding Brain and Heart Tumours in Sprague-Dawley Rats Exposed from Prenatal Life until Natural Death to Mobile Phone Radiofrequency Field Representative of a 1.8 GHz GSM Base Station Environmental Emission. Environmental Research, 165, 496–503. https://doi.org/10.1016/j.envres.2018.01.037

National Toxicology Program (2018). Toxicology and carcinogenesis studies in Sprague Dawley (Hsd:Sprague Dawley SD) rats exposed to whole-body radio frequency radiation at a frequency (900 MHz) and modulations (GSM and CDMA) used by cell phones. National Toxicology Program Technical Report Series, 595. https://doi.org/10.22427/NTP-TR-595