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Relationship: 3799
Title
Bulky DNA adducts, increase leads to Increase, Chromosomal aberrations
Upstream event
Downstream event
Key Event Relationship Overview
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding | Point of Contact | Author Status | OECD Status |
|---|---|---|---|---|---|---|
| Bulky DNA adducts leading to chromosomal aberrations and mutations | non-adjacent | Beckner Andersano (send email) | Under development: Not open for comment. Do not cite |
Taxonomic Applicability
| Term | Scientific Term | Evidence | Link |
|---|---|---|---|
| all species | all species | High | NCBI |
Sex Applicability
| Sex | Evidence |
|---|---|
| Unspecific | High |
Life Stage Applicability
| Term | Evidence |
|---|---|
| All life stages | High |
Key Event Relationship Description
This KER describes the relationship between increased Bulky DNA adduct formation (upstream KD/MIE) and increased chromosomal aberrations (downstream KE/AO2). The likelihood of chromosomal aberrations (downstream KE/AO2) increases with the accumulation and persistence of DNA adducts, particularly bulky adducts that substantially distort DNA structure and interfere with normal DNA replication and repair. Under these conditions, DNA damage is more likely to be converted into structural chromosomal alterations, resulting in an increased frequency of chromosomal aberrations.
Evidence Collection Strategy
Evidence was collected for this KER in two methods. The initial method being through expert knowledge from Dr. Carole Yauk, Emmanuelle Demuynck, and the research team at PARC. The second strategy followed that described in Huliganga (2025).
The initial articles collected were from expert knowledge through presentation as well as previous searches conducted by the PARC team with Emmanuelle as a lead. Notably, the paper provided by Dr. Yauk was used to look for direct connections in connectedpapers.com. Any paper with direct connections, that being a forward or backward citation, were collected. The papers provided by Emmanuelle and the PARC team were already sorted in an Excel spreadsheet. These were then sorted for which were labeled as having “relevance” to the overall AOP and collected. The final two collections were conducted on 6/26/2026 & 7/15/2026, using OMNI (provided by the University of Ottawa). The searches consisted of Boolean strings using either “any field contains” or “any phrase contains exact phrase” requirements with the titles of the KEs as the terms (e.g. “any field contains Bulky adducts & chromosomal aberrations”). A full list of terms used has been included below.
All articles from expert sources were added to covidence.com for tracking systematic review of the articles. For the searches using OMNI, only the top 50 results were downloaded to RIS file and submitted to covidence.com for review. During this time, covidence was able to remove duplicates as well as help organize inclusion criteria following a modified PECO like that in Huliganga (2025). The inclusion criteria, for this specific KER, included: Bulky DNA adducts, Chromosomal aberrations (or any combination of these two), All species, all life stages. During review of the titles and abstracts it was noted on each paper the reason for inclusion to the next step or the reason for exclusion from the review. Once they reached full text review, the paper was reviewed for relevant data, graphs, methods, as well as background of the KER. Once all papers were reviewed, the data was extracted and placed into the corresponding KER. The final search day, on the 15th of July, was not included in Covidence.com, as there were only 24 articles and it was found easier to read through each paper separately and determine inclusion at the point of reading using the same inclusion criteria.
Evidence Supporting this KER
The scientific evidence supporting this KER is generally strong particularly with respect to dose-response and incidence concordance. Multiple studies have demonstrated consistent increases in upstream and downstream events across a range of exposure levels and biological tissues, while epidemiological observations show an association between adduct formation and chromosomal aberrations in exposed populations with polymorphisms. Temporal concordance remains less well established, as relatively few studies have directly measured both key events within the same experimental design. This limitation introduces some uncertainty regarding the precise progression of events. Nevertheless, the mechanistic relationship is supported by substantial biological plausibility and convergent empirical evidence from both experimental and observational studies. Overall, despite gaps in temporal evidence and direct event-to-event measurements, the weight of evidence supports a high level of confidence in this KER.
Biological Plausibility
Bulky DNA adducts distort DNA structure and impede DNA replication and nucleotide excision repair. Persistent adducts can stall replication forks and generate replication stress, leading to fork collapse and formation of DNA double-strand breaks. Double-strand breaks are particularly important precursors of chromosomal aberrations because inaccurate repair through pathways such as non-homologous end joining can result in chromosome deletions, translocations, inversions, and other structural alterations. Consistent with this mechanism, exposure to benzo[a]pyrene and its reactive metabolite BPDE induces bulky DNA adduct formation, increases markers of DNA double-strand breaks, and is associated with elevated frequencies of chromosomal damage including micronuclei and chromosomal translocations (Kaufmann, 1989; Georgiadis et al., 2004; Long et al., 2018; Rossner et al., 2015). Thus, the relationship between bulky DNA adduct formation and chromosomal aberrations is biologically plausible and supported by established understanding of replication stress, DNA repair failure, and double-strand break generation.
Empirical Evidence
| Species, Life Stage, Sex Tested | Stressor(s) | Upstream effect (Y/N) | Downstream effect (Y/N) | Effect on Upstream event (descriptive) | Effect on downstream event (descriptive) | Citation |
|---|---|---|---|---|---|---|
|
- Homo Sapiens - mean age 21.4 (+- 1.5 yrs) |
PAHs (Environmental Tobacco Smoke (ETS) & B[a]P) | Y | Y | Higher ETS and PAH exposure, particularly in individuals with susceptible CYP1A1 genotypes, was associated with increased bulky DNA adduct levels | Increased frequencies of aberrant cells (chromosomal aberrations) were observed under the same exposure and genotype conditions that produced elevated bulky DNA adduct levels. Changes in chromosomal aberrations paralleled changes in DNA adduct levels | Georgiadis et al., 2004 |
|
- Homo Sapiens - 18-25 yrs - 58 males - 136 females |
B[a]P | Y | Y | Increase bulky DNA adducts in lymphocytes | Increased amount of aberrant chromosomes | Georgiadis et al., 2005 |
|
- MutaMouse - male - 12-13 weeks old |
B[a]P | Y | Y | Increasing oral doses of B[a]P resulted in increasing levels of Adducts | Increased doses of BaP also yielded increased rates of micronuclei | Long et al., 2018 |
|
- V79 chinese hamster cells (metabolically deficient) - V79 derived cells exposing human CP450 1A2 and human sulfotransferase 1A1, - Human colorectal cancer cells (HCT116, Caco-2) - Non-transformed human colonic epithelial cells (HCEC) |
PhIP & metabolite N-OH-PhIP | Y | Y | Increase in adducts over time as well as concentration | Increased chromosomal aberrations in human colonic epithelial cells after N-OH-PhIP-induced adduct formation (C8-PhIP-dG adducts) | Mimmler et al., 2016 |
|
- HCT116 human colon carcinoma cell line - human glioma cell lines M059K - human lymphoblast GM00536B & GM01526E - ~28 hrs old |
Hedamycin, Adozelesin, Camptotehcin, aphidicolin, caffeine, colcemid, Hoechst 33258, ethidium bromide | N | Y | UV and camtothecin are both known to induce bulky DNA adducts | Increased doses of camptothecin induces a larger number of chromosomal aberrations | Tu et al., 2005 |
Uncertainties and Inconsistencies
The empirical evidence supporting this KER primarily addresses dose concordance and incidence concordance with limited information regarding temporal concordance. An additional source of uncertainty is that one study conducted by Tu et al. did not directly measure bulky DNA adduct levels. It instead relied on exposure to a known DNA-adduct-forming chemical and subsequent measurement of downstream genetic aberrations. Consequently, the study assumes adduct formation rather than confirming the magnitude or incidence of the upstream KE. This limitation reduces confidence in the quantitative characterization of the relationship. Additionally, without direct adduct measurement, it is difficult to determine downstream sensitivity or other experimental or biological factors. Overall, these limitations introduce uncertainty into the overall weight of evidence supporting the KER.
Known modulating factors
| Modulating Factor (MF) | MF Specification | Effect(s) on the KER | Reference(s) |
|---|---|---|---|
| Genetic Polymorphism | - CYP1A1*2A (T3801C): MspI resticion site in 3’ non-coding region of gene | CYP1A12A carriers have ~2 to 2.5 fold increase in DNA adduct levels (KE upstream) and similar trend in aberrant chromosomes (KE downstream) relative to CYP1A11 homozygotes (when exposure exceeded 0.8 h/day) These findings suggest that CYP1A1*2A polymorphism increases susceptibility and may enhance sensitivity of downstream KE to changes in upstream KE. | Georgiadis et al. 2004 |
|
Genetic Polymorphism |
- CYP1A1*2A (T3801C): MspI resticion site in 3’ non-coding region of gene - EPHX Arg139Arg polymorphism |
Carriers of CYP1A12A allele (both heterozygous and homozygous) exhibited approximately two-fold higher levels of bulky DNA adducts compared with wild-type, particurlarly under higher environmental tobacco smoke (ETS). Although not statistically significant, there was an increase in aberrant chromosome levels. This indicates that CYP1A12A polymorphism increases susceptibility to DNA adduct formation and may enhance likelihood of downstream chromosomal damage at a given level of exposure. As well, the Arg139Arg polymorphism found in EPHX gene had lower levels of adduct levels in all season, indicating that this polymorphism has a possible protection against adduct levels. |
Georgiadis et al. 2005 |
| Diet | - Exposure level of dietary carcinogens | Elevated PhIP exposure increases the magnitude and persistence of DNA adducts (upstream KE) and is associated with increased chromosomal aberrations (downstream KE). | Mimmler et al., 2016 |
Quantitative Understanding of the Linkage
Available evidence suggests that a substantial increase in DNA adduct formation is required before detection of chromosomal aberrations. In the study conducted by Long et al., increases in DNA adducts were observed at doses as low as 0.20 mg/kg bw/day. While statistically significant increases in micronucleated reticulocytes and normochromatic erythrocytes were not observed until 3.13 mg/kg bw/day. Micronucleus frequencies increased approximately 4.5-fold and 3.7-fold above control levels at this dose, indicating that substantial accumulation of DNA adducts is required before measurable chromosomal damage is induced. This threshold-like relationship is further supported by benchmark dose modelling, where the BMD100 for DNA adduct formation (0.0286 mg/kg bw/day), demonstrating that DNA adduct formation is a considerably more sensitive endpoint.
Evidence for the temporal relationship between these key events is more limited. Mimmler et al., demonstrated that DNA adducts were detectable within 2-8 hours of exposure and remained elevated for up to 48 hours depending on the compound and concentration used. In contrast, chromosomal aberrations were only evaluated after approximately 38 hours (24-hours exposure plus 14-hour mitotic arrest), at which point significant increases were observed. These findings indicate that DNA adduct formation precedes chromosomal aberration induction. However, the minimum duration or magnitude of adduct accumulation required to trigger chromosomal damage cannot be quantitatively defined because both key events were not assessed concurrently across multiple time points. Consequently, while there is strong evidence that DNA adduct formation occurs earlier and at lower doses than chromosomal aberrations, the precise temporal and quantitative relationship between the two key events remains uncertain.
Response-response Relationship
Long et al. measured a dose-dependent increase in DNA adduct formation across multiple tissues following exposure to B[a]P. The lowest observed genotoxic effect level (LOGEL) was found to differ in measured tissues starting in the spleen at 0.20 mg/kg BW/day and largest at 1.56 mg/kg BW/day in the glandular stomach tissue. These findings suggest tissue specific responses to adduct formation from B[a]P exposure. At the highest level of exposure tested (50 mg/kg BW/day), there was a substantial increase in DNA adduct levels in each tissue with approximately 506-fold in spleen, 433-fold in lung, 219-fold in liver, 187-fold in kidney, 139-fold in bladder, 46.3-fold in Glandular stomach, 27.4-fold in small intestine, and 19.6-fold in small intestine.
In the same study, a statistically significant increase in micronucleated cells was observed in both reticulocytes (RETs) and normochromatic erythrocytes (NCEs) at 3.13 mg/kg bw/day. This correlates to ~4.5-fold and 3.7-fold increases over control levels, respectively. These findings suggest that substantial accumulation of DNA adducts precedes detectable chromosomal damage as measured by micronucleus formation. The data shows a threshold-like relationship between adduct formation and micronucleus formation. This indicates that a greater magnitude of upstream DNA damage is required before a measurable increase in micronuclei is observed.
This study demonstrates a clear dose-response relationship for both key events. The authors also detailed specific BMD100 , BMDL, and BMDU for DNA adducts and micronuclei in Bone marrow and normochromatic erythrocytes, respectively. More specifically, the BMD100 , BMDL, and BMDU for DNA adducts are 0.0286, 0.0196, and 0.06613 respectively. While the BMD100 , BMDL, and BMDU for DNA adducts for micronuclei are 10.2, 8.348, and 12.24 respectively. This shows that DNA adduct formation is a more sensitive endpoint and requires approximately 4- to 16- fold lower dose than those required to induce significant micronucleus formation.
Another study completed by Tu et al., measured chromosomal aberrations in cels 24 hours after 4-hour exposure to hedamycin. They treated four different concentrations, 0.25, 1, and 2.5 nmol/L with increases of damaged chromosomes of 4%, 21%, and 63% relative to control, respectively. Hedamycin is a known genotoxic agent that produces bulky adducts in the DNA. This study demonstrates a dose-response relationship between hedamycin and chromosomal aberrations. A limitation of this study is a lack of directly measuring DNA adduct levels. Due to this limitation, correlation of the two key events cannot be directly associated but can be inferred.
Time-scale
Mimmler et al. investigated the temporal relationship between DNA adduct formation (upstream KE) and chromosomal aberrations (downstream KE) following exposure to PhIP and its reactive metabolite N-OH-PhIP. DNA adducts were detected as early as 2 hours after exposure to 50 uM PhIP and continued to increase through 48 hours. Following exposure to 1 uM N-OH-PhIP, adduct levels were detectable at 8 hours but declined by 24 hours. Whereas exposure to 10 uM N-OH-PhIP produced significantly elevated adduct levels at both time points. In contrast, chromosomal aberrations were assessed only after a 24-hour exposure to 2.5 uM N-OH-PhIP followed by 14-hour mitotic arrest period, at which time aberration frequencies were significantly increased. These observations indicate that DNA adduct formation precedes chromosomal aberration induction. However, because DNA adducts and chromosomal aberrations were not measured concurrently across multiple time points, the precise temporal relationship between the events cannot be determined.
Known Feedforward/Feedback loops influencing this KER
No positive or negative feedback mechanisms related to this KER were identified in the literature reviewed. Consequently, there is currently no evidence to indicate whether feedback/feedforward loops influence this relationship, nor is there information available on their time-course, persistence, or homeostatic limits. It should be noted that this conclusion is based on the studies identified in the present literature search. Relevant publications may exist but were not captured due to limitations in search terminology, database coverage, or the number of papers assessed.
Domain of Applicability
Due to the conserved structure of DNA across cellular organisms, the potential for bulky adduct formation exists across taxa, sexes, and life stages. Bulky DNA adducts can form in a wide range of cell types following exposure to endogenous and exogenous genotoxic agents (Long et al., 2018). The cellular processes involved in DNA damage recognition and repair are also broadly conserved across species. While quantitative differences in adduct formation and repair may occur among taxa, sexes, and developmental stages, elevated levels of persistent DNA adduct increase the likelihood of chromosomal aberrations in dividing cells. Therefore, this KER is considered broadly applicable across taxa, sexes, and life stages.
References
Bi, Xiaohui, et al. “DNA Polymerase κ Is Specifically Required for Recovery from the Benzo[a]Pyrene-Dihydrodiol Epoxide (BPDE)-Induced S-Phase Checkpoint.” The Journal of Biological Chemistry [United States], vol. 280, no. 23, June 2005, pp. 22343–55, https://doi.org/10.1074/jbc.M501562200.
Georgiadis, P., et al. “Impact of Phase I or Phase II Enzyme Polymorphisms on Lymphocyte DNA Adducts in Subjects Exposed to Urban Air Pollution and Environmental Tobacco Smoke.” Toxicology Letters [Shannon], vol. 149, no. 1, April 2004, pp. 269–80, https://doi.org/10.1016/j.toxlet.2003.12.038.
Georgiadis, Panagiotis, et al. “Interactions between CYP1A1 Polymorphisms and Exposure to Environmental Tobacco Smoke in the Modulation of Lymphocyte Bulky DNA Adducts and Chromosomal Aberrations.” Carcinogenesis (New York) [Oxford], vol. 26, no. 1, January 2005, pp. 93–101, https://doi.org/10.1093/carcin/bgh294.
Long, Alexandra S., et al. “Benchmark Dose Analyses of Multiple Genetic Toxicity Endpoints Permit Robust, Cross-Tissue Comparisons of MutaMouse Responses to Orally Delivered Benzo[a]Pyrene.” Archives of Toxicology [Berlin/Heidelberg], vol. 92, no. 2, February 2018, pp. 967–82, https://doi.org/10.1007/s00204-017-2099-2.
Mimmler, Maximilian, et al. “DNA Damage Response Curtails Detrimental Replication Stress and Chromosomal Instability Induced by the Dietary Carcinogen PhIP.” Nucleic Acids Research [England], vol. 44, no. 21, December 2016, pp. 10259–76, https://doi.org/10.1093/nar/gkw791.
Nikolova, Teodora, et al. “The γH2AX Assay for Genotoxic and Nongenotoxic Agents: Comparison of H2AX Phosphorylation with Cell Death Response.” Toxicological Sciences [United States], vol. 140, no. 1, July 2014, pp. 103–17, https://doi.org/10.1093/toxsci/kfu066.
Pavel Rossner, et al. “Genetic Toxicology and Carcinogenesis.” Toxicology for the Health and Pharmaceutical Sciences, edited by Antonio Peña-Fernández et al., 1st ed., CRC Press, 2022, pp. 81–97, https://doi.org/10.1201/9780203730584-5.
Rossner, Pavel, et al. “Molecular Epidemiology Focused on Airborne Carcinogens.” Air Pollution and Health Effects, edited by Srikanth S. Nadadur and John W. Hollingsworth, Springer London, Limited, 2015, pp. 185–212, https://doi.org/10.1007/978-1-4471-6669-6_7.
Tu, Lan Chun, et al. “Hedamycin, a DNA Alkylator, Induces γH2AX and Chromosome Aberrations: Involvement of Phosphatidylinositol 3-Kinase–Related Kinases and DNA Replication Fork Movement.” Molecular Cancer Therapeutics, vol. 4, no. 8, August 2005, pp. 1175–85, https://doi.org/10.1158/1535-7163.MCT-05-0054.