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AOP: 324

Title

A descriptive phrase which references both the Molecular Initiating Event and Adverse Outcome.It should take the form “MIE leading to AO”. For example, “Aromatase inhibition leading to reproductive dysfunction” where Aromatase inhibition is the MIE and reproductive dysfunction the AO. In cases where the MIE is unknown or undefined, the earliest known KE in the chain (i.e., furthest upstream) should be used in lieu of the MIE and it should be made clear that the stated event is a KE and not the MIE.  More help

Reactive oxygen species leading to growth inhibition via oxidative DNA damage and cell cycle disruption

Short name
A name that succinctly summarises the information from the title. This name should not exceed 90 characters. More help
ROS leading to growth inhibition via oxidative DNA damage and cell cycle disruption
The current version of the Developer's Handbook will be automatically populated into the Handbook Version field when a new AOP page is created.Authors have the option to switch to a newer (but not older) Handbook version any time thereafter. More help
Handbook Version v2.0

Graphical Representation

A graphical representation of the AOP.This graphic should list all KEs in sequence, including the MIE (if known) and AO, and the pair-wise relationships (links or KERs) between those KEs. More help
Click to download graphical representation template Explore AOP in a Third Party Tool

Authors

The names and affiliations of the individual(s)/organisation(s) that created/developed the AOP. More help

You Song, Li Xie, Knut Erik Tollefsen

Norwegian Institute for Water Research (NIVA), Sognsveien 72, 0855, Oslo, Norway

Point of Contact

The user responsible for managing the AOP entry in the AOP-KB and controlling write access to the page by defining the contributors as described in the next section.   More help

Contributors

Users with write access to the AOP page.  Entries in this field are controlled by the Point of Contact. More help
  • You Song

Coaches

This field is used to identify coaches who supported the development of the AOP.Each coach selected must be a registered author. More help
  • Shihori Tanabe

OECD Information Table

Provides users with information concerning how actively the AOP page is being developed and whether it is part of the OECD Workplan and has been reviewed and/or endorsed. OECD Project: Assigned upon acceptance onto OECD workplan. This project ID is managed and updated (if needed) by the OECD. OECD Status: For AOPs included on the OECD workplan, ‘OECD status’ tracks the level of review/endorsement of the AOP . This designation is managed and updated by the OECD. Journal-format Article: The OECD is developing co-operation with Scientific Journals for the review and publication of AOPs, via the signature of a Memorandum of Understanding. When the scientific review of an AOP is conducted by these Journals, the journal review panel will review the content of the Wiki. In addition, the Journal may ask the AOP authors to develop a separate manuscript (i.e. Journal Format Article) using a format determined by the Journal for Journal publication. In that case, the journal review panel will be required to review both the Wiki content and the Journal Format Article. The Journal will publish the AOP reviewed through the Journal Format Article. OECD iLibrary published version: OECD iLibrary is the online library of the OECD. The version of the AOP that is published there has been endorsed by the OECD. The purpose of publication on iLibrary is to provide a stable version over time, i.e. the version which has been reviewed and revised based on the outcome of the review. AOPs are viewed as living documents and may continue to evolve on the AOP-Wiki after their OECD endorsement and publication.   More help
OECD Project # OECD Status Reviewer's Reports Journal-format Article OECD iLibrary Published Version
This AOP was last modified on May 28, 2026 08:33

Revision dates for related pages

Page Revision Date/Time
Increase, Reactive oxygen species June 12, 2025 01:27
Increase, Oxidative Stress February 11, 2026 07:05
Increase, Oxidative DNA damage October 08, 2024 03:57
Inadequate DNA repair March 08, 2024 12:15
Increase, DNA strand breaks December 17, 2024 11:57
Increase, Cell cycle disruption May 19, 2026 02:04
Decrease, Cell proliferation December 07, 2020 06:55
Decrease, Growth July 06, 2022 07:36
Increase, ROS leads to Increase, Oxidative Stress August 02, 2024 15:40
Increase, Oxidative Stress leads to Increase, Oxidative DNA damage March 08, 2024 14:39
Increase, Oxidative DNA damage leads to Inadequate DNA repair March 08, 2024 14:48
Inadequate DNA repair leads to Increase, DNA strand breaks January 09, 2023 20:56
Increase, DNA strand breaks leads to Cell cycle disruption January 20, 2025 03:50
Cell cycle disruption leads to Decrease, Cell proliferation October 08, 2024 04:53
Decrease, Cell proliferation leads to Decrease, Growth July 06, 2022 07:43
Heavy metals (cadmium, lead, copper, iron, nickel) October 25, 2021 03:21

Abstract

A concise and informative summation of the AOP under development that can stand-alone from the AOP page. The aim is to capture the highlights of the AOP and its potential scientific and regulatory relevance. More help

This adverse outcome pathway (AOP 324) describes a linear genotoxic route by which increased reactive oxygen species (ROS) can lead to decreased organismal growth. In this AOP, increased ROS is treated operationally as the molecular initiating event because it represents the earliest common measurable redox perturbation shared by many stressors within the broader ROS-growth AOP network. Increased ROS leads to oxidative stress, which causes oxidative DNA damage. When oxidative DNA lesions exceed or impair repair capacity, inadequate DNA repair can occur, allowing DNA strand breaks to accumulate. Strand breaks activate cell cycle checkpoint responses and disrupt progression through the cell cycle. Sustained cell cycle disruption reduces cell proliferation, and reduced cell proliferation ultimately contributes to decreased growth. The AOP reuses and connects existing AOP-Wiki components, including key events (KEs) and key event relationships (KERs) from OECD/WPHA-WNT endorsed AOPs. In particular, the oxidative DNA damage module is derived from AOP 296, the oxidative stress and DNA damage context is supported by AOP 478, the cell-cycle disruption KE is shared with AOP 212, and the link from decreased cell proliferation to decreased growth is reused from AOP 263 (AOP-Wiki, 2026a, 2026b, 2026c, 2026d; OECD, 2022, 2023; Carrothers et al., 2025). The AOP is biologically plausible across aerobic eukaryotes because ROS metabolism, antioxidant defenses, DNA damage response pathways, DNA repair, cell cycle regulation, and growth processes are broadly conserved. Empirical support is derived from studies in algae, fish embryos and cell lines, mammalian cells, radiation models, and other systems exposed to oxidative or genotoxic stressors. The AOP is expected to be useful for mechanistic interpretation of oxidative stress-related toxicity, support of integrated approaches to testing and assessment (IATA), and prioritization of stressors that produce oxidative DNA damage and growth impairment.  

AOP Development Strategy

Context

Used to provide background information for AOP reviewers and users that is considered helpful in understanding the biology underlying the AOP and the motivation for its development.The background should NOT provide an overview of the AOP, its KEs or KERs, which are captured in more detail below. More help

ROS are continuously formed during aerobic metabolism and are also generated in response to environmental stressors. At controlled levels, ROS participate in redox signaling, while excessive ROS can disturb redox homeostasis and initiate oxidative damage to cellular macromolecules (Schieber and Chandel, 2014; Sies et al., 2017). DNA is a major target of oxidative attack. Oxidative DNA lesions such as 8-oxo-2'-deoxyguanosine and other oxidized bases can arise endogenously or following toxic insult, and these lesions may contribute to mutation, strand break formation, and activation of DNA damage responses if they are not repaired correctly or efficiently (Cooke et al., 2003; OECD, 2023). This AOP was developed to represent the DNA damage-driven linear route within the broader ROS-growth AOP network. The route was selected because oxidative DNA damage is a well-established consequence of oxidative stress and because downstream events such as inadequate DNA repair, strand breaks, cell cycle disruption, and reduced cell proliferation provide a mechanistically coherent bridge between molecular damage and decreased organismal growth (Cuddihy and O'Connell, 2003; Conlon and Raff, 1999; OECD, 2022; OECD, 2023). The AOP was therefore designed to provide a focused, reviewable linear representation of one major mechanistic branch by which excessive ROS can impair growth.  

Strategy

Provides a description of the approaches to the identification, screening and quality assessment of the data relevant to identification of the key events and key event relationships included in the AOP or AOP network.This information is important as a basis to support the objective/envisaged application of the AOP by the regulatory community and to facilitate the reuse of its components.  Suggested content includes a rationale for and description of the scope and focus of the data search and identification strategy/ies including the nature of preliminary scoping and/or expert input, the overall literature screening strategy and more focused literature surveys to identify additional information (including e.g., key search terms, databases and time period searched, any tools used). More help

AOP 324 was developed using the principles described in OECD AOP guidance, including modular description of KEs and KERs, reuse of existing AOP-Wiki content where appropriate, evidence evaluation using biological plausibility, empirical support, essentiality, and quantitative understanding, and clear description of the biological domain of applicability (OECD, 2018, 2021). The intent was not to create a fully de novo set of biological objects, but to assemble a linear AOP from established and reusable AOP-Wiki components wherever possible. This modular strategy is important because the AOP is part of a broader ROS-growth AOP network and because its individual KEs and KERs are expected to be reused in other oxidative stress, genotoxicity, and growth impairment AOPs. Existing AOP-Wiki content and OECD-endorsed AOPs were reviewed at an early stage to identify KEs and KERs that could be reused directly, adapted, or used as supporting context. AOP 296 was the primary source for the oxidative DNA damage module. It is an endorsed AOP describing oxidative DNA damage leading to chromosomal aberrations and mutations and includes KE 1634 (Increase, Oxidative DNA damage), KE 155 (Inadequate DNA repair), KE 1635 (Increase, DNA strand breaks), and relationships involving oxidative DNA damage, inadequate DNA repair, and strand break formation (AOP-Wiki, 2026b; OECD, 2023). AOP 478, an endorsed AOP on deposition of energy leading to cataracts, provided additional support for the upstream oxidative stress context, including KE 1392 (Oxidative stress), KE 1634, KE 155, KE 1635, and the relationship from oxidative stress to oxidative DNA damage in a radiation-relevant setting (AOP-Wiki, 2026a; Carrothers et al., 2025). AOP 212 was reviewed because it contains KE 1505 (Cell cycle, disrupted) and evidence that disruption of cell-cycle regulation can lead to downstream changes in cell fate (AOP-Wiki, 2026c). AOP 263 was reviewed because it is an endorsed AOP linking decreased cell proliferation to decreased growth, and AOP 324 reuses the downstream KE 1821 (Decrease, Cell proliferation), AO 1521 (Decrease, Growth), and KER 2205 (Decrease, Cell proliferation leads to Decrease, Growth) from that AOP (AOP-Wiki, 2026d; OECD, 2022; Song and Villeneuve, 2021). The resulting AOP 324 therefore represents an upstream extension and re-routing of established AOP-Wiki knowledge. Compared with AOP 296, AOP 324 extends upstream from oxidative DNA damage to increased ROS and oxidative stress and extends downstream from DNA damage response biology to decreased cell proliferation and growth. Compared with AOP 263, it reuses the final growth-relevant segment but provides a different upstream causal route, namely oxidative DNA damage and cell-cycle disruption rather than mitochondrial uncoupling and ATP depletion. Compared with AOP 478, it reuses the oxidative stress-DNA damage portion of the radiation AOP but directs that conserved genotoxic sequence toward growth inhibition rather than cataract formation. Compared with AOP 212, it reuses cell-cycle disruption as a modular KE but places it in the context of DNA strand break-mediated checkpoint activation rather than histone deacetylase inhibition. The literature review and evidence assembly process followed an AI-human hybrid workflow. The first phase consisted of AOP-helpFinder searching and preliminary analysis. Search terms were developed for each event in the pathway, including KE names, common synonyms, endpoint terms, assay terms, taxonomic descriptors, and relevant species names. These terms were used in AOP-helpFinder to search PubMed for co-occurrence patterns between key events and related mechanistic concepts, following published approaches for literature mining in support of AOP development (Carvaillo et al., 2019; Jornod et al., 2022). The exported results included PMIDs, titles, abstracts, and matched key-event terms. These outputs were subjected to overlap analysis to remove redundant records and to filter the initial literature pool, including elimination of clearly irrelevant records and separation of taxa-related evidence where needed. The second phase consisted of large-language-model (LLM)-assisted screening. Titles and abstracts from AOP-helpFinder, together with records identified from targeted manual searches, were pre-screened using an LLM as an auxiliary prioritization tool. The purpose of this step was not to replace expert judgment, but to increase efficiency and consistency during early evidence triage. The LLM was used to extract study metadata, including stressor, species, biological system, dose or concentration, and exposure duration; identify the evidence type represented in each study, such as biological plausibility, empirical support, or essentiality; and flag weight-of-evidence indicators including dose-response concordance, temporal concordance, incidence concordance, and intervention or rescue evidence. Studies were provisionally classified as high relevance, medium relevance, or low relevance. High-relevance studies were retrieved for full-text review, whereas medium-relevance studies were retained as potential supporting evidence. Low-relevance studies were documented as low priority and excluded from detailed curation. For studies moved forward to full-text review, a second LLM-assisted pass was used to organize relevant information from the full paper. All LLM-generated outputs were checked directly against the original article text by human reviewers. The LLM was therefore used only as a screening and structuring aid, not as an independent evaluator of the evidence. The final phase consisted of manual expert curation and weight-of-evidence evaluation. Domain experts verified the relevance and interpretation of the literature selected in the earlier stages, resolved ambiguous cases, and extracted information to populate KER evidence tables. These tables captured the biological system studied, stressor, method, endpoint, result, concordance pattern, weight-of-evidence category, and bibliographic source. Expert review was then used to evaluate the evidence for each KER in terms of biological plausibility, empirical support, essentiality, quantitative understanding, and evidence gaps. Targeted manual searches were also used to fill specific gaps for ROS biology, oxidative DNA damage, DNA repair, DNA strand breaks, DNA damage response, cell cycle disruption, cell proliferation, and growth inhibition. Studies were prioritized when they measured two or more KEs in the same biological system, reported exposure time and dose or concentration, or provided evidence relevant to dose-response, temporal, or incidence concordance. Mechanistic reviews and OECD reports were used primarily to support biological plausibility, whereas primary experimental studies were prioritized for empirical support wherever possible (Cooke et al., 2003; Cuddihy and O'Connell, 2003; Qian et al., 2009; Zachleder et al., 2011; Quevedo et al., 2021; OECD, 2023).

 

Summary of the AOP

This section is for information that describes the overall AOP.The information described in section 1 is entered on the upper portion of an AOP page within the AOP-Wiki. This is where some background information may be provided, the structure of the AOP is described, and the KEs and KERs are listed. More help

Events:

Molecular Initiating Events (MIE)
An MIE is a specialised KE that represents the beginning (point of interaction between a prototypical stressor and the biological system) of an AOP. More help
Key Events (KE)
A measurable event within a specific biological level of organisation. More help
Adverse Outcomes (AO)
An AO is a specialized KE that represents the end (an adverse outcome of regulatory significance) of an AOP. More help
Type Event ID Title Short name
MIE 1115 Increase, Reactive oxygen species Increase, ROS
KE 1392 Increase, Oxidative Stress Increase, Oxidative Stress
KE 1634 Increase, Oxidative DNA damage Increase, Oxidative DNA damage
KE 155 Inadequate DNA repair Inadequate DNA repair
KE 1635 Increase, DNA strand breaks Increase, DNA strand breaks
KE 1505 Increase, Cell cycle disruption Cell cycle disruption
KE 1821 Decrease, Cell proliferation Decrease, Cell proliferation
AO 1521 Decrease, Growth Decrease, Growth

Relationships Between Two Key Events (Including MIEs and AOs)

This table summarizes all of the KERs of the AOP and is populated in the AOP-Wiki as KERs are added to the AOP.Each table entry acts as a link to the individual KER description page. More help

Network View

This network graphic is automatically generated based on the information provided in the MIE(s), KEs, AO(s), KERs and Weight of Evidence (WoE) summary tables. The width of the edges representing the KERs is determined by its WoE confidence level, with thicker lines representing higher degrees of confidence. This network view also shows which KEs are shared with other AOPs. More help

Prototypical Stressors

A structured data field that can be used to identify one or more “prototypical” stressors that act through this AOP. Prototypical stressors are stressors for which responses at multiple key events have been well documented. More help

Life Stage Applicability

The life stage for which the AOP is known to be applicable. More help
Life stage Evidence
Not Otherwise Specified

Taxonomic Applicability

Latin or common names of a species or broader taxonomic grouping (e.g., class, order, family) can be selected.In many cases, individual species identified in these structured fields will be those for which the strongest evidence used in constructing the AOP was available. More help
Term Scientific Term Evidence Link
fish fish NCBI

Sex Applicability

The sex for which the AOP is known to be applicable. More help
Sex Evidence
Unspecific

Overall Assessment of the AOP

Addressess the relevant biological domain of applicability (i.e., in terms of taxa, sex, life stage, etc.) and Weight of Evidence (WoE) for the overall AOP as a basis to consider appropriate regulatory application (e.g., priority setting, testing strategies or risk assessment). More help

Domain of Applicability

Addressess the relevant biological domain(s) of applicability in terms of sex, life-stage, taxa, and other aspects of biological context. More help

The biological domain of applicability of AOP 324 is defined by the conservation of the KEs and KERs linking oxidative DNA damage to impaired proliferation and growth. The AOP is applicable to aerobic eukaryotic systems in which ROS can oxidize DNA, DNA repair and checkpoint responses regulate genomic integrity, cell cycle progression determines proliferation, and proliferation contributes to growth. The AOP is most relevant to developmental or actively growing systems, including algae, embryos, larvae, juveniles, and proliferative tissues. The stressor domain is broad but not unlimited. Stressors are relevant when they generate ROS, impair antioxidant defenses, induce oxidative DNA lesions, or produce DNA strand breaks through mechanisms that converge on oxidative damage and checkpoint activation. Examples include redox-cycling organic chemicals, peroxides, metals, nanoparticles, ionizing radiation, ultraviolet radiation, and other stressors capable of producing oxidative DNA damage. The AOP should not be used where decreased growth is driven primarily by mechanisms unrelated to oxidative DNA damage or cell-cycle disruption.  

Essentiality of the Key Events

The essentiality of KEs can only be assessed relative to the impact of manipulation of a given KE (e.g., experimentally blocking or exacerbating the event) on the downstream sequence of KEs defined for the AOP. Consequently, evidence supporting essentiality is assembled on the AOP page, rather than on the independent KE pages that are meant to stand-alone as modular units without reference to other KEs in the sequence. The nature of experimental evidence that is relevant to assessing essentiality relates to the impact on downstream KEs and the AO if upstream KEs are prevented or modified. This includes: Direct evidence: directly measured experimental support that blocking or preventing a KE prevents or impacts downstream KEs in the pathway in the expected fashion. Indirect evidence: evidence that modulation or attenuation in the magnitude of impact on a specific KE (increased effect or decreased effect) is associated with corresponding changes (increases or decreases) in the magnitude or frequency of one or more downstream KEs. More help

Essentiality was evaluated at the AOP level by considering whether modification of an upstream KE would be expected to prevent, attenuate, or alter downstream KEs and/or the AO. Because many KEs in this AOP represent conserved cellular stress-response processes, direct essentiality evidence is strongest for some biological modules and weaker for others. Evidence is summarized below.

Key event

Essentiality call

Rationale and supporting evidence with citations

Main uncertainties

Event 1115: Reactive oxygen species, increased

Moderate

ROS are causally linked to oxidative stress because oxidative stress occurs when oxidant formation exceeds antioxidant capacity. Antioxidant and radical-scavenging interventions can reduce oxidative stress and oxidative DNA damage in many systems, supporting the importance of ROS as an upstream driver (Schieber and Chandel, 2014; Sies et al., 2017; OECD, 2023).

ROS can also function in physiological signaling at low levels; oxidative stress can be sustained by altered antioxidant capacity even when a specific ROS source is removed.

Event 1392: Oxidative stress, increased

High

Oxidative stress provides the biochemical context for oxidative DNA damage. Excess ROS and redox imbalance can oxidize DNA bases and promote strand breaks; AOP 478 and AOP 296 both use oxidative stress/oxidative DNA damage relationships as central components of endorsed AOP logic (AOP-Wiki, 2026a, 2026b; Cooke et al., 2003; Carrothers et al., 2025; OECD, 2023).

Cellular antioxidant and DNA repair capacity can delay or prevent progression to downstream events.

Event 1634: Oxidative DNA damage, increased

Moderate to high

AOP 296 identifies oxidative DNA damage as a core initiating event for irreversible genomic damage and reports support from studies using ROS scavengers and DNA repair modulation (AOP-Wiki, 2026b; OECD, 2023). Oxidative lesions such as 8-oxo-dG are mechanistically linked to repair demand and strand break formation (Cooke et al., 2003).

Direct intervention studies that isolate oxidative DNA damage while keeping other ROS-mediated damage constant are limited.

Event 155: Inadequate DNA repair, increased

Moderate

DNA repair capacity determines whether oxidative lesions are correctly resolved or persist as repair intermediates and strand breaks. AOP 296 explicitly includes inadequate DNA repair as a key event connecting oxidative DNA damage to downstream genomic damage (AOP-Wiki, 2026b; OECD, 2023).

Repair systems differ by lesion type, cell-cycle phase, species, and tissue; direct essentiality evidence is context-specific.

Event 1635: DNA strand breaks, increased

Moderate

DNA strand breaks are strong activators of DNA damage checkpoint signaling and are central to the transition from molecular damage to cell-cycle disruption. AOP 296 and AOP 478 both include DNA strand breaks in genotoxic pathways downstream of oxidative stress or oxidative DNA damage (AOP-Wiki, 2026a, 2026b; Carrothers et al., 2025; OECD, 2023).

DNA strand breaks may arise from direct DNA attack, repair intermediates, or replication stress; separating these routes can be difficult.

Event 1505: Cell cycle disruption, increased

Moderate

Cell-cycle disruption is essential for translating DNA damage into reduced proliferation. AOP 212 reuses cell-cycle disruption as a key event in an endorsed pathway, and DNA damage checkpoint literature supports the causal role of checkpoint activation in delaying or arresting cell-cycle progression (AOP-Wiki, 2026c; Cuddihy and O'Connell, 2003).

Transient arrest may allow repair and recovery; sustained arrest is more clearly linked to decreased proliferation.

Event 1821: Cell proliferation, decreased

Moderate

Reduced proliferation is a direct determinant of tissue and organismal growth. AOP 263 reuses this KE and KER 2205 as the final step from decreased proliferation to decreased growth (AOP-Wiki, 2026d; OECD, 2022; Song and Villeneuve, 2021).

Growth is multifactorial and can also be influenced by energy allocation, nutrition, endocrine signaling, and cell death.

Evidence Assessment

Addressess the biological plausibility, empirical support, and quantitative understanding from each KER in an AOP. More help

The evidence assessment is organized by KER. Calls follow the OECD framework for biological plausibility, empirical support, and quantitative understanding (OECD, 2018, 2021).

Biological plausibility of KERs

KER

Biological plausibility call

Rationale with citations

Relationship 2009: ROS increase leads to oxidative stress increase

High

The relationship is mechanistic and widely accepted: oxidative stress reflects an imbalance between oxidants and antioxidant defenses, and ROS are the dominant oxidant species represented in this AOP. AOP 478 also describes deposition of energy leading to ROS production and oxidative stress (Schieber and Chandel, 2014; Sies et al., 2017; AOP-Wiki, 2026a; Carrothers et al., 2025).

Relationship 2810: oxidative stress increase leads to oxidative DNA damage increase

High

ROS generated under oxidative stress can oxidize DNA bases and damage the sugar-phosphate backbone. This KER is shared with endorsed AOP 478 and provides the upstream connection into the oxidative DNA damage module of AOP 296 (AOP-Wiki, 2026a, 2026b; Cooke et al., 2003; OECD, 2023).

Relationship 1909: oxidative DNA damage increase leads to inadequate DNA repair increase

High

Oxidative DNA lesions increase demand on base excision repair and related repair processes. When lesion burden or repair intermediates exceed repair capacity, repair becomes inadequate. This relationship is used in AOP 296 and AOP 478 (AOP-Wiki, 2026a, 2026b; OECD, 2023).

Relationship 1910: inadequate DNA repair increase leads to DNA strand breaks increase

Moderate to high

Inadequate or incomplete repair can generate or allow persistence of strand breaks, including repair intermediates and replication-associated breaks. AOP 296 includes this relationship as part of the oxidative DNA damage module (AOP-Wiki, 2026b; OECD, 2023).

Relationship 3480: DNA strand breaks increase leads to cell cycle disruption increase

High

DNA strand breaks activate DNA damage response pathways, including ATM/ATR and checkpoint signaling, that delay or arrest cell-cycle progression to allow repair or prevent propagation of damage (Cuddihy and O'Connell, 2003; OECD, 2023).

Relationship 3363: cell cycle disruption increase leads to cell proliferation decrease

High

Cell proliferation requires orderly progression through the cell cycle. Sustained checkpoint activation, G1/S arrest, G2/M arrest, or mitotic disruption reduces the rate of cell division. KE 1505 is shared with AOP 212, supporting its reuse as a modular checkpoint-related KE (AOP-Wiki, 2026c; Cuddihy and O'Connell, 2003).

Relationship 2205: cell proliferation decrease leads to growth decrease

High

Organismal and tissue growth depend on net accumulation of cell number, cell size, and extracellular components. This relationship is reused from endorsed AOP 263, where decreased cell proliferation is linked to decreased growth (AOP-Wiki, 2026d; Conlon and Raff, 1999; OECD, 2022; Song and Villeneuve, 2021).

Empirical support for KERs

KER

Empirical support call

Rationale and supporting evidence with citations

Inconsistencies or limitations

Relationship 2009: ROS increase leads to oxidative stress increase

High

Multiple experimental systems show concordance between ROS generation and oxidative stress biomarkers. For example, paraquat increased ROS and antioxidant enzyme responses in Chlorella vulgaris (Qian et al., 2009), and radiation-induced ROS/oxidative stress relationships are documented in AOP 478 (AOP-Wiki, 2026a; Carrothers et al., 2025).

Direct ROS measurements are technically challenging and probe-specific; some studies infer ROS from antioxidant responses or downstream damage.

Relationship 2810: oxidative stress increase leads to oxidative DNA damage increase

Moderate to high

Oxidative stress is widely associated with oxidative DNA lesions and DNA strand-break endpoints. AOP 478 includes oxidative stress leading to oxidative DNA damage and reports high biological plausibility, while AOP 296 provides a curated oxidative DNA damage module (AOP-Wiki, 2026a, 2026b; Cooke et al., 2003; OECD, 2023).

Some studies measure DNA strand breaks rather than lesion-specific oxidative DNA damage; stressor-specific pathways may include direct genotoxicity.

Relationship 1909: oxidative DNA damage increase leads to inadequate DNA repair increase

Moderate

AOP 296 identifies this relationship and supports it with evidence that excessive oxidative lesions can overwhelm or alter repair processes (AOP-Wiki, 2026b; OECD, 2023).

Direct co-measurement of oxidative lesions and inadequate repair in the same study is less common than measurement of damage endpoints alone.

Relationship 1910: inadequate DNA repair increase leads to DNA strand breaks increase

Moderate

AOP 296 includes inadequate repair leading to DNA strand breaks and broader genomic damage, supported by genotoxicity evidence and repair biology (AOP-Wiki, 2026b; OECD, 2023).

Directionality can be difficult because strand breaks can both result from repair intermediates and trigger repair responses.

Relationship 3480: DNA strand breaks increase leads to cell cycle disruption increase

Moderate

Green algal studies show DNA strand breaks and cell-cycle disruption or division impairment following genotoxic stressors such as N-OH-2-AAF and zeocin (Zachleder et al., 2011). Silver exposure in embryonic zebrafish cells produced DNA damage and cell-cycle arrest responses (Quevedo et al., 2021).

Evidence is taxonomically diverse but not always tied specifically to oxidative DNA damage as the upstream cause.

Relationship 3363: cell cycle disruption increase leads to cell proliferation decrease

Moderate

Cell-cycle disruption is empirically associated with reduced division and proliferation. AOP 212 provides support for cell-cycle disruption as a reusable KE in an endorsed AOP context, and algal and zebrafish cell studies show reduced division/proliferation following DNA damage-related cell-cycle effects (AOP-Wiki, 2026c; Zachleder et al., 2011; Quevedo et al., 2021).

Recovery can occur if damage is repaired; transient checkpoint activation does not necessarily lead to long-term proliferation decrease.

Relationship 2205: cell proliferation decrease leads to growth decrease

Moderate

AOP 263 reports this relationship as the final growth-relevant KER and assesses it in an endorsed AOP context. Growth effects in algae exposed to paraquat and other stressors provide additional organism-level consistency (AOP-Wiki, 2026d; Qian et al., 2009; Jamers and De Coen, 2010; OECD, 2022; Song and Villeneuve, 2021).

Growth is an apical endpoint influenced by many processes; direct co-measurement of cell proliferation and organismal growth is less common than measurement of growth alone.

Known Modulating Factors

Modulating factors (MFs) may alter the shape of the response-response function that describes the quantitative relationship between two KES, thus having an impact on the progression of the pathway or the severity of the AO.The evidence supporting the influence of various modulating factors is assembled within the individual KERs. More help

Modulating factors may alter the probability, magnitude, or timing of progression from one KE to the next. The factors below are expected to influence multiple KERs in AOP 324 and should be considered when interpreting experimental evidence.

Modulating factor

Influence or outcome

KER(s) involved

Supporting citations

Antioxidant capacity

Higher antioxidant capacity can buffer ROS and reduce oxidative stress and DNA damage; lower capacity can increase sensitivity.

2009, 2810

Sies et al. (2017); Schieber and Chandel (2014)

DNA repair capacity

Higher repair capacity can reduce persistence of oxidative DNA lesions and prevent strand breaks; impaired repair increases downstream risk.

1909, 1910

Cooke et al. (2003); OECD (2023)

Cell-cycle phase

DNA damage outcomes differ by cell-cycle phase because repair pathway choice and checkpoint sensitivity vary across G1, S, G2, and M phases.

1910, 3480, 3363

Cuddihy and O'Connell (2003); OECD (2023)

Life stage and growth rate

Rapidly growing or developing organisms may be more sensitive because decreased proliferation has a larger impact on growth.

3363, 2205

Conlon and Raff (1999); OECD (2022)

Stressor type and dose rate

Radiation, redox-cycling chemicals, metals, and nanoparticles can differ in ROS production dynamics and direct DNA-damaging potential.

2009, 2810, 3480

AOP-Wiki (2026a); Carrothers et al. (2025); Quevedo et al. (2021)

Quantitative Understanding

Optional field to provide quantitative weight of evidence descriptors.  More help

Quantitative understanding of AOP 324 is strongest for local relationships that have well-defined biological or assay endpoints, and weaker for full-pathway prediction from ROS increase to decreased growth. Direct quantitative prediction is limited by the short half-life and assay dependence of ROS measurements, variability in oxidative DNA damage endpoints, differences in repair capacity, and the multifactorial nature of growth.

KER

Quantitative understanding call

Rationale and supporting evidence with citations

Relationship 2009: ROS increase leads to oxidative stress increase

Low to moderate

ROS and oxidative stress biomarkers can be measured quantitatively, but direct ROS measurement is probe- and context-dependent. AOP 478 reports high quantitative understanding for deposition of energy leading to oxidative stress, but this does not translate directly into a generalized ROS-to-oxidative-stress response-response model for all stressors (AOP-Wiki, 2026a; Sies et al., 2017).

Relationship 2810: oxidative stress increase leads to oxidative DNA damage increase

Low to moderate

Oxidative DNA damage endpoints such as 8-oxo-dG and comet assay endpoints can be quantified, but quantitative prediction from oxidative stress biomarkers to DNA lesion burden remains limited and context-dependent (Cooke et al., 2003; OECD, 2023; AOP-Wiki, 2026a).

Relationship 1909: oxidative DNA damage increase leads to inadequate DNA repair increase

Low

Quantitative thresholds at which oxidative DNA damage overwhelms repair capacity are not well generalized across taxa, cell types, or lesion types (OECD, 2023).

Relationship 1910: inadequate DNA repair increase leads to DNA strand breaks increase

Low

Repair kinetics can be measured, but quantitative prediction of strand break accumulation from inadequate repair remains context-specific (OECD, 2023).

Relationship 3480: DNA strand breaks increase leads to cell cycle disruption increase

Moderate

DNA strand breaks and cell-cycle phase distribution can be quantified, and threshold-like checkpoint responses are biologically expected. However, quantitative relationships vary by cell type, repair capacity, and checkpoint status (Cuddihy and O'Connell, 2003; Zachleder et al., 2011; Quevedo et al., 2021).

Relationship 3363: cell cycle disruption increase leads to cell proliferation decrease

Moderate

Cell-cycle arrest and proliferation can both be quantified, but quantitative translation depends on arrest duration, reversibility, and cell population dynamics (Cuddihy and O'Connell, 2003).

Relationship 2205: cell proliferation decrease leads to growth decrease

Moderate

AOP 263 reports moderate quantitative understanding for this KER. Growth models and developmental biology support the relationship, but quantitative prediction across taxa and exposure contexts remains limited (AOP-Wiki, 2026d; Conlon and Raff, 1999; OECD, 2022; Song and Villeneuve, 2021).

Considerations for Potential Applications of the AOP (optional)

Addressess potential applications of an AOP to support regulatory decision-making.This may include, for example, possible utility for test guideline development or refinement, development of integrated testing and assessment approaches, development of (Q)SARs / or chemical profilers to facilitate the grouping of chemicals for subsequent read-across, screening level hazard assessments or even risk assessment. More help

AOP 324 can support mechanistic interpretation of toxicity data where ROS generation, oxidative stress, DNA damage, cell cycle disruption, or reduced proliferation are observed together with growth effects. The AOP may be useful for hazard identification, prioritization of stressors that generate oxidative DNA damage, and organization of evidence in IATA or defined approaches. It can also support chemical grouping or read-across where chemicals share evidence of ROS-mediated DNA damage and downstream checkpoint or proliferation effects. The AOP also highlights assay opportunities and gaps. Several KEs can be measured using established or standardized methods, including DNA strand breaks using OECD TG 489 and growth using OECD growth-related test guidelines such as TG 201 and TG 210 (OECD, 2011, 2013, 2014). Other KEs, such as ROS increase, oxidative DNA damage, inadequate DNA repair, and cell cycle disruption, are supported by mechanistic assays but may require careful interpretation of assay specificity and biological context. High-throughput or new approach methodology assays measuring oxidative stress responses, DNA damage signaling, cell cycle arrest, and proliferation may be mapped to the AOP to support screening and prioritization. For regulatory application, the AOP is currently most suitable for qualitative or semi-quantitative use, such as supporting biological plausibility, organizing mechanistic evidence, and identifying data gaps. More quantitative applications, such as prediction of decreased growth from upstream ROS or oxidative DNA damage measurements, will require further development of response-response relationships, better characterization of modulating factors, and additional studies measuring multiple KEs in the same biological system over time.  

References

List of the literature that was cited for this AOP. More help

Ankley, G. T., Bennett, R. S., Erickson, R. J., Hoff, D. J., Hornung, M. W., Johnson, R. D., Mount, D. R., Nichols, J. W., Russom, C. L., Schmieder, P. K., Serrano, J. A., Tietge, J. E., & Villeneuve, D. L. (2010). Adverse outcome pathways: A conceptual framework to support ecotoxicology research and risk assessment. Environmental Toxicology and Chemistry, 29(3), 730-741. https://doi.org/10.1002/etc.34 AOP-Wiki. (2026a). AOP 478: Deposition of energy leading to occurrence of cataracts. Collaborative Adverse Outcome Pathway Wiki. Accessed 14 May 2026. AOP-Wiki. (2026b). AOP 296: Oxidative DNA damage leading to chromosomal aberrations and mutations. Collaborative Adverse Outcome Pathway Wiki. Accessed 14 May 2026. AOP-Wiki. (2026c). AOP 212: Histone deacetylase inhibition leading to testicular atrophy. Collaborative Adverse Outcome Pathway Wiki. Accessed 14 May 2026. AOP-Wiki. (2026d). AOP 263: Uncoupling of oxidative phosphorylation leading to growth inhibition via decreased cell proliferation. Collaborative Adverse Outcome Pathway Wiki. Accessed 14 May 2026. Becker, R. A., Ankley, G. T., Edwards, S. W., Kennedy, S. W., Linkov, I., Meek, M. E., Sachana, M., Segner, H., Van der Burg, B., Villeneuve, D. L., Watanabe, H., & Barton-Maclaren, T. S. (2015). Increasing scientific confidence in adverse outcome pathways: Application of tailored Bradford-Hill considerations for evaluating weight of evidence. Regulatory Toxicology and Pharmacology, 72(3), 514-537. https://doi.org/10.1016/j.yrtph.2015.04.004 Carrothers, E., et al. (2025). Adverse Outcome Pathway on Deposition of Energy Leading to Cataracts. OECD Series on Adverse Outcome Pathways, No. 40. OECD Publishing, Paris. https://doi.org/10.1787/5ad6b263-en Carvaillo, J.-C., Barouki, R., Coumoul, X., & Audouze, K. (2019). Linking bisphenol S to adverse outcome pathways using a combined text mining and systems biology approach. Environmental Health Perspectives, 127(4), 047005. https://doi.org/10.1289/EHP4200 Conlon, I., & Raff, M. (1999). Size control in animal development. Cell, 96(2), 235-244. https://doi.org/10.1016/S0092-8674(00)80563-2 Cooke, M. S., Evans, M. D., Dizdaroglu, M., & Lunec, J. (2003). Oxidative DNA damage: Mechanisms, mutation, and disease. The FASEB Journal, 17(10), 1195-1214. https://doi.org/10.1096/fj.02-0752rev Cuddihy, A. R., & O'Connell, M. J. (2003). Cell-cycle responses to DNA damage in G2. International Review of Cytology, 222, 99-140. https://doi.org/10.1016/S0074-7696(02)22013-6 Fang, P., Li, X., Zhang, Y., & Wang, Z. (2024). Single and joint bioaccumulation and toxicity of isoproturon and cadmium in green algae (Chlamydomonas reinhardtii). Chemical and Biological Technologies in Agriculture, 11, 106. https://doi.org/10.1186/s40538-024-00617-6 Finkel, T., & Holbrook, N. J. (2000). Oxidants, oxidative stress and the biology of ageing. Nature, 408(6809), 239-247. https://doi.org/10.1038/35041687 Jamers, A., & De Coen, W. (2010). Effect assessment of the herbicide paraquat on a green alga using differential gene expression and biochemical biomarkers. Environmental Toxicology and Chemistry, 29(4), 893-901. https://doi.org/10.1002/etc.102 Jornod, F., Jaylet, T., Blaha, L., Sarigiannis, D., Tamisier, L., & Audouze, K. (2022). AOP-helpFinder webserver: A tool for comprehensive analysis of the literature to support adverse outcome pathways development. Bioinformatics, 38(4), 1173-1175. https://doi.org/10.1093/bioinformatics/btab750 Murphy, M. P. (2009). How mitochondria produce reactive oxygen species. Biochemical Journal, 417(1), 1-13. https://doi.org/10.1042/BJ20081386 OECD. (2011). Test No. 201: Freshwater alga and cyanobacteria, growth inhibition test. OECD Guidelines for the Testing of Chemicals, Section 2. OECD Publishing, Paris. https://doi.org/10.1787/9789264069923-en OECD. (2013). Test No. 210: Fish, early-life stage toxicity test. OECD Guidelines for the Testing of Chemicals, Section 2. OECD Publishing, Paris. https://doi.org/10.1787/9789264203785-en OECD. (2014). Test No. 489: In vivo mammalian alkaline comet assay. OECD Guidelines for the Testing of Chemicals, Section 4. OECD Publishing, Paris. https://doi.org/10.1787/9789264224179-en OECD. (2018). Users' Handbook Supplement to the Guidance Document for Developing and Assessing Adverse Outcome Pathways. OECD Series on Adverse Outcome Pathways, No. 1. OECD Publishing, Paris. https://doi.org/10.1787/5jlv1m9d1g32-en OECD. (2021). Guidance Document for the Scientific Review of Adverse Outcome Pathways. OECD Series on Testing and Assessment, No. 344. OECD Publishing, Paris. OECD. (2022). Uncoupling of oxidative phosphorylation leading to growth inhibition via decreased cell proliferation. OECD Series on Adverse Outcome Pathways, No. 28. OECD Publishing, Paris. https://doi.org/10.1787/f20867c1-en OECD. (2023). Oxidative DNA damage leading to chromosomal aberrations and mutations. OECD Series on Adverse Outcome Pathways, No. 29. OECD Publishing, Paris. https://doi.org/10.1787/399d2c34-en Qian, H., Chen, W., Sun, L., Jin, Y., Liu, W., & Fu, Z. (2009). Inhibitory effects of paraquat on photosynthesis and the response to oxidative stress in Chlorella vulgaris. Ecotoxicology, 18(5), 537-543. https://doi.org/10.1007/s10646-009-0311-8 Quevedo, A. C., Lynch, I., & Valsami-Jones, E. (2021). Cellular repair mechanisms triggered by exposure to silver nanoparticles and ionic silver in embryonic zebrafish cells. Environmental Science: Nano, 8(9), 2507-2522. https://doi.org/10.1039/D1EN00422K Schieber, M., & Chandel, N. S. (2014). ROS function in redox signaling and oxidative stress. Current Biology, 24(10), R453-R462. https://doi.org/10.1016/j.cub.2014.03.034 Sies, H., Berndt, C., & Jones, D. P. (2017). Oxidative stress. Annual Review of Biochemistry, 86, 715-748. https://doi.org/10.1146/annurev-biochem-061516-045037 Song, Y., & Villeneuve, D. L. (2021). AOP report: Uncoupling of oxidative phosphorylation leading to growth inhibition via decreased cell proliferation. Environmental Toxicology and Chemistry, 40(11), 2951-2963. https://doi.org/10.1002/etc.5197 Valko, M., Morris, H., & Cronin, M. T. D. (2005). Metals, toxicity and oxidative stress. Current Medicinal Chemistry, 12(10), 1161-1208. https://doi.org/10.2174/0929867053764635 Zachleder, V., Vítová, M., Šetlíková, E., & Bisová, K. (2011). DNA damage during G2 phase does not affect cell cycle progression of the green alga Scenedesmus quadricauda. PLoS ONE, 6(5), e19626. https://doi.org/10.1371/journal.pone.0019626