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AOP: 326

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 lipid peroxidation and decreased cell proliferation

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 LPO and decreased cell proliferation
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 June 19, 2026 14:32

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, Lipid peroxidation June 20, 2026 06:09
Decrease, Coupling of oxidative phosphorylation November 07, 2025 05:15
Decrease, Adenosine triphosphate pool June 14, 2021 13:40
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, LPO April 11, 2024 16:21
Increase, LPO leads to Decrease, Coupling of OXPHOS June 29, 2017 08:10
Decrease, Coupling of OXPHOS leads to Decrease, ATP pool July 06, 2022 07:39
Decrease, ATP pool leads to Decrease, Cell proliferation December 07, 2020 07:43
Decrease, Cell proliferation leads to Decrease, Growth July 06, 2022 07:43
Heavy metals (cadmium, lead, copper, iron, nickel) October 25, 2021 03:21
Hydrogen peroxide May 19, 2019 17:21
Paraquat November 29, 2016 18:42
tert-Butyl hydroperoxide May 19, 2019 17:24
Rotenone November 29, 2016 18:42
Ionizing Radiation May 07, 2019 12:12
Ultraviolet B radiation April 15, 2017 16:04

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 326) describes a linear route by which increased reactive oxygen species (ROS) can lead to decreased organismal growth through lipid peroxidation-mediated impairment of mitochondrial bioenergetics. 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 chemical and non-chemical stressors within the broader ROS-growth AOP network. Increased ROS leads to oxidative stress, which promotes lipid peroxidation. Oxidative damage to membrane lipids, particularly polyunsaturated fatty acids in cellular and mitochondrial membranes, can alter membrane integrity, proton conductance, mitochondrial membrane potential, and respiratory efficiency. These effects reduce coupling of oxidative phosphorylation (OXPHOS), decrease the cellular ATP pool, impair energy-dependent cellular proliferation, and ultimately reduce organismal growth.

    AOP 326 reuses and connects established AOP-Wiki components from two important AOP contexts. The upstream oxidative stress component is associated with AOP 478, in which deposition of energy leads to oxidative stress through increased free radical generation, with subsequent oxidative molecular damage (AOP-Wiki, 2026a). This provides a curated AOP-Wiki context for the use of oxidative stress as a conserved hub KE downstream of free radical or ROS-producing stressors. The downstream bioenergetic and growth segment is directly associated with AOP 263, which causally links decreased coupling of OXPHOS to growth inhibition through ATP depletion and decreased cell proliferation and has been published in the OECD Series on Adverse Outcome Pathways (AOP-Wiki, 2026b; OECD, 2022; Song and Villeneuve, 2021). Thus, AOP 326 links an oxidative-stress/lipid-damage module to an OECD-endorsed bioenergetics-to-growth module. The AOP is relevant to environmental and human health contexts because ROS production, lipid peroxidation, mitochondrial ATP generation, cell proliferation, and organismal growth are broadly conserved in aerobic eukaryotes.    Empirical support is derived from studies in algae, daphnids, mollusks, fish, mammalian systems, and human cells exposed to redox-active chemicals, metals, pesticides, hypoxia-reoxygenation, radiation, and endogenous oxidative stressors. This AOP can support mechanistic interpretation of oxidative stress-mediated growth impairment, assay selection, chemical prioritization, integrated approaches to testing and assessment (IATA), and development of quantitative AOP approaches for mitochondrial and oxidative stress-related toxicity.

Acknowledgement

This project was funded by the Research Council of Norway (RCN), grant no. RCN-315929 “EXPECT: In silico and experimental screening platform for characterizing environmental impact of industry development in the Arctic” (https://www.niva.no/en/projects/expect), the European Partnership for the Assessment of Risks from Chemicals (PARC) through European Union’s Horizon Europe research and innovation programme (Grant Agreement No 101057014, and supported by the NIVA Computational Toxicology Program, NCTP (https://www.niva.no/en/featured-pages/nctp, grant. No. RCN-342628).

AI disclosure

Artificial intelligence (AI) tools were used to support literature prioritization, review and AOP-Wiki page preparation in this work. AOP-helpFinder was used for automated literature mining, and ChatGPT (OpenAI) was used as an auxiliary tool for title and abstract screening, extraction of study metadata, and identification of potential weight-of-evidence indicators. AI-assisted outputs were used only to organize and prioritize information and were verified against the original sources by the authors before inclusion. Additional AI assistance was used for formatting, copy-editing, citation cross-checking, and harmonization of the AOP-Wiki pages. All scientific interpretations, weight-of-evidence judgments, final wording, and conclusions were determined and approved by the authors, who take full responsibility for the content and integrity of the work.

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 can also be generated in response to environmental stressors. At controlled levels, ROS participate in redox signaling, whereas excessive ROS can disturb redox homeostasis and initiate oxidative stress (Schieber and Chandel, 2014; Sies et al., 2017). Lipids are important targets of oxidative attack because membrane phospholipids, especially those containing polyunsaturated fatty acyl chains, can undergo radical-driven peroxidation. Lipid peroxidation generates lipid hydroperoxides and secondary reactive products, including malondialdehyde and 4-hydroxy-2-nonenal, which can alter membrane structure, propagate oxidative damage, and affect protein and organelle function (Ayala et al., 2014).

    AOP 326 was developed to represent the lipid peroxidation-driven linear route within the broader ROS-growth AOP network. This route was selected because lipid peroxidation is a well-established consequence of oxidative stress and because mitochondrial membranes are central determinants of OXPHOS coupling. Peroxidative modification of mitochondrial membrane lipids can alter membrane fluidity, proton leak, respiratory control, and mitochondrial membrane potential, providing a mechanistically coherent bridge from oxidative stress to impaired ATP production (Murphy, 2009; Nicholls and Ferguson, 2013; Ouillon et al., 2021). The downstream sequence from decreased coupling of OXPHOS to decreased ATP pool, decreased cell proliferation, and decreased growth is already represented in AOP 263 and provides the growth-relevant terminal module for AOP 326 (AOP-Wiki, 2026b; OECD, 2022; Song and Villeneuve, 2021).

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 326 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 purpose was to assemble a focused linear pathway from reusable AOP-Wiki elements rather than to create an isolated de novo pathway. This is particularly important because AOP 326 is one branch of the broader ROS-growth AOP network and because its KEs and KERs overlap with oxidative stress, mitochondrial dysfunction, energy metabolism, cell proliferation, and growth-related AOPs.

    Reuse of existing AOP-Wiki content was considered at the beginning of development. AOP 478 was reviewed because it provides an AOP-Wiki precedent for oxidative stress as a central KE downstream of free radical generation, and because it describes oxidative stress as a pathway by which energy deposition can damage biological molecules (AOP-Wiki, 2026a). Although AOP 478 is not a lipid peroxidation-to-growth AOP, its use of KE 1392 (Increase, Oxidative stress) and its oxidative damage context support the upstream portion of AOP 326. AOP 263 was reviewed because it provides the directly relevant downstream module consisting of KE 1446 (Decrease, Coupling of OXPHOS), KE 1771 (Decrease, ATP pool), KE 1821 (Decrease, Cell proliferation), and AO 1521 (Decrease, Growth), together with KERs 2203, 2204, and 2205 (AOP-Wiki, 2026b; OECD, 2022; Song and Villeneuve, 2021). In AOP 326, the novel linking logic is therefore the connection of ROS-driven oxidative stress and lipid peroxidation to the existing OXPHOS-ATP-cell proliferation-growth module.

    The evidence base was assembled through a structured AI-human hybrid workflow. Search terms were first developed for the events in the pathway, including KE names, synonyms, endpoint names, assay terms, taxa, and species. AOP-helpFinder was then used to search PubMed for co-occurrence of KE-related terms, following approaches previously described for literature mining in support of AOP development (Carvaillo et al., 2019; Jornod et al., 2022). The exported AOP-helpFinder results included PMIDs, titles, abstracts, and matched KE terms. Overlap analysis was applied to remove redundant hits and filter literature that was unrelated to the taxa or biological systems considered relevant to this AOP.

    A large language model (LLM) was then used as an auxiliary screening and structuring tool. During abstract pre-screening, the LLM was used to extract study metadata such as stressor, species, biological system, dose or concentration, and exposure time; to identify whether a study provided evidence for biological plausibility, empirical support, essentiality, or quantitative understanding; and to flag indicators of dose-response, temporal, or incidence concordance. Studies were provisionally classified as high, medium, or low priority. High-priority studies were retrieved for full-text review, medium-priority studies were reserved for supporting evidence, and low-priority studies were documented as low relevance. For studies passing the abstract screen, the LLM was used to assist full-text review by organizing information relevant to the KER evidence table. All LLM outputs were checked manually against the full text by expert reviewers before any evidence was accepted.

    The final phase consisted of manual expert curation. Experts verified the LLM-assisted extractions, populated KER evidence tables with methods, endpoints, results, weight-of-evidence categories, and references, and made final calls for biological plausibility, empirical support, essentiality, and evidence gaps. Targeted manual searches were also used to fill gaps identified during evidence curation, especially for the lipid peroxidation to OXPHOS coupling relationship and the downstream AOP 263 KERs. Searches focused on combinations of terms such as reactive oxygen species, oxidative stress, lipid peroxidation, malondialdehyde, 4-hydroxynonenal, mitochondrial membrane potential, proton leak, oxidative phosphorylation, ATP depletion, cell proliferation, growth inhibition, paraquat, copper, cadmium, hypoxia-reoxygenation, Daphnia, algae, bivalves, fish, and AOP. Studies were prioritized when they measured two or more KEs in the same biological system, reported exposure dose or concentration and time, or provided evidence relevant to dose-response, temporal, or incidence concordance.

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 1445 Increase, Lipid peroxidation Increase, LPO
KE 1446 Decrease, Coupling of oxidative phosphorylation Decrease, Coupling of OXPHOS
KE 1771 Decrease, Adenosine triphosphate pool Decrease, ATP pool
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
All life stages High

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 High NCBI
mammals mammals High NCBI
crustaceans Daphnia magna Moderate NCBI
green algae Ulva compressa High NCBI

Sex Applicability

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

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

The overall weight of evidence supporting AOP 326 is considered moderate to high. Biological plausibility is high for all six KERs in the pathway, reflecting well-established mechanistic connections between ROS, oxidative stress, lipid peroxidation, mitochondrial membrane integrity, OXPHOS coupling, ATP production, cell proliferation, and growth. The downstream bioenergetic module from decreased coupling of OXPHOS through decreased ATP pool and decreased cell proliferation to decreased growth (KERs 2203, 2204, 2205) is directly reused from OECD-endorsed AOP 263, which was published in the OECD Series on Adverse Outcome Pathways and has independently established high to moderate WoE for these relationships (OECD, 2022; Song and Villeneuve, 2021). The upstream oxidative stress-lipid peroxidation module is supported by high empirical concordance across algae, crustaceans, bivalves, fish, and mammalian systems. The novel linking relationship from lipid peroxidation to decreased OXPHOS coupling (KER 1599) is rated moderate in empirical support, as studies measuring both endpoints concurrently in the same experimental system are less common, although mechanistic evidence for cardiolipin oxidation and inner mitochondrial membrane integrity is strong. Essentiality is rated moderate to high, with the strongest support for the OXPHOS-to-ATP segment shared with AOP 263. Quantitative understanding is highest for the AOP 263-derived downstream module and low to moderate for the upstream lipid peroxidation-to-OXPHOS segment. The main uncertainties are the directionality and quantitative strength of the lipid peroxidation-to-OXPHOS relationship, given that mitochondrial dysfunction can also promote lipid peroxidation, and the potential for compensatory glycolytic ATP production to buffer depletion. AOP 326 is suitable for mechanistic interpretation, IATA development, and chemical prioritisation for oxidative stress-mediated growth impairment affecting mitochondrial energy metabolism (OECD, 2018; OECD, 2022; Becker et al., 2015).

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 domain of applicability for AOP 326 is broad across aerobic eukaryotic organisms in which ROS generation, oxidative stress responses, lipid peroxidation, mitochondrial oxidative phosphorylation, ATP-dependent cell proliferation, and growth are biologically relevant. The AOP is most applicable to taxa and life stages in which growth depends substantially on cell proliferation and energy supply, including algae, developing aquatic organisms, juvenile fish, and proliferating mammalian or human cells. It is also relevant to adult organisms when growth, regeneration, tissue condition, or organismal size is influenced by mitochondrial energy metabolism.

The stressor domain is also broad and includes direct ROS generators, redox-cycling chemicals, metals, pesticides, mitochondrial toxicants, hypoxia-reoxygenation, and radiation. Because the MIE is defined operationally as increased ROS rather than as a chemical-specific interaction, AOP 326 should be applied to stressors that can be shown to increase ROS or oxidative stress and to produce evidence consistent with lipid peroxidation and mitochondrial bioenergetic impairment. Environmental factors such as temperature, oxygen availability, diet, lipid composition, nutrient status, and antioxidant capacity may modulate the pathway by altering ROS production, lipid susceptibility to peroxidation, mitochondrial coupling, or growth rate.

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 is evaluated for the overall AOP based on whether preventing or modifying upstream KEs changes downstream KEs or the AO. Direct essentiality evidence is strongest for the AOP 263 downstream module, where removal of mitochondrial uncouplers or restoration of coupling can restore mitochondrial membrane potential and ATP production. Essentiality for lipid peroxidation is biologically plausible and supported by intervention and association studies, but direct experiments showing that blocking lipid peroxidation prevents all downstream events are less common.

Key event

Essentiality

Rationale

Experimental manipulation evidence (KE knock-out / inhibition / rescue)

Uncertainties

Event 1115: Reactive oxygen species, increased

Moderate

ROS scavenging or antioxidant interventions frequently attenuate oxidative stress and downstream lipid peroxidation in oxidative stress models. ROS is also used as a common early perturbation in the broader ROS-growth AOP network (Schieber and Chandel, 2014; Sies et al., 2017).

Indirect (stop/attenuation): antioxidant and ROS-scavenger pre-treatment reduces oxidative stress and downstream damage across oxidative-stress models (Schieber and Chandel, 2014; Sies et al., 2017). No selective single-source ROS knock-out is available.

ROS also participate in normal signaling; increased ROS does not always progress to adversity if antioxidant and repair systems compensate.

Event 1392: Oxidative stress, increased

Moderate to high

Oxidative stress is required for lipid peroxidation when ROS production exceeds antioxidant buffering. AOP 478 supports oxidative stress as a central KE downstream of free radical generation (AOP-Wiki, 2026a).

Indirect: modulation of antioxidant capacity alters progression to oxidative macromolecular damage; oxidative stress is the curated hub KE in endorsed AOP 478 (AOP-Wiki, 2026a; Carrothers et al., 2025).

Oxidative stress can be measured using multiple indirect biomarkers; equivalence across methods is not always clear.

Event 1445: Lipid peroxidation, increased

Moderate

Lipid peroxidation can alter membrane properties and generate reactive aldehydes that affect mitochondrial function (Ayala et al., 2014). Dietary PUFA studies in Daphnia show higher lipid peroxidation with lower mitochondrial membrane potential (Moore et al., 2023), supporting a causal role in mitochondrial impairment.

Indirect: antioxidant intervention attenuates lipid peroxidation in oxidative-stress models; direct block-and-rescue isolating LPO from other oxidative damage is uncommon (Murphy, 2009; Ouillon et al., 2021).

Direct blocking experiments are limited; lipid peroxidation may be both a cause and consequence of mitochondrial dysfunction.

Event 1446: Coupling of OXPHOS, decreased

High

This KE is reused from AOP 263. Evidence from AOP 263 supports essentiality because removal of uncouplers or restoration of coupling can recover mitochondrial membrane potential and ATP levels, reducing downstream impairment (AOP-Wiki, 2026b; OECD, 2022; Song and Villeneuve, 2021).

Direct (rescue): removal of uncouplers or restoration of coupling recovers mitochondrial membrane potential and ATP in the endorsed AOP 263 module (AOP-Wiki, 2026b; OECD, 2022; Song and Villeneuve, 2021).

Mild uncoupling can sometimes reduce ROS generation and may be adaptive; severity and duration determine progression.

Event 1771: ATP pool, decreased

Moderate

ATP depletion is a direct consequence of impaired OXPHOS coupling and is associated with reduced cell proliferation and cytotoxicity in multiple systems. AOP 263 identifies ATP depletion as an intermediate KE linking OXPHOS uncoupling to reduced proliferation (AOP-Wiki, 2026b; OECD, 2022).

Indirect: ATP-restoration experiments reduce downstream injury/proliferation deficits; central KE in endorsed AOP 263 (Leist et al., 1997; Nicotera et al., 1998; OECD, 2022).

Cells may compensate through glycolysis or other energy pathways; total ATP may recover transiently depending on exposure scenario.

Event 1821: Cell proliferation, decreased

Moderate

Growth depends on accumulation of cell number and biomass. AOP 263 provides evidence that decreased cell proliferation links ATP depletion to decreased growth (AOP-Wiki, 2026b; OECD, 2022; Song and Villeneuve, 2021).

Indirect: proliferation deficit links bioenergetic/genotoxic upstream to growth; reused from endorsed AOP 263 with KER 2205 (AOP-Wiki, 2026d; Conlon and Raff, 1999; OECD, 2022; Song and Villeneuve, 2021).

Growth can be influenced by cell size, metabolism, development, nutrient status, and cell death, not proliferation alone.

Event 1521: Growth, decreased (AO)

Not applicable (AO)

Growth is the adverse outcome and is regulatory relevant across algae, aquatic invertebrate, fish, amphibian, and plant test systems. AOP 263 provides precedent for using decreased growth as the AO in a mitochondrial bioenergetics AOP (OECD, 2022; Song and Villeneuve, 2021).

As the adverse outcome, essentiality is assessed for upstream KEs; AOP 263 provides precedent for decreased growth as an AO downstream of these modules (OECD, 2022; Song and Villeneuve, 2021).

Growth is an integrative endpoint and can arise through multiple independent or interacting mechanisms.

Evidence Assessment

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

Evidence assessment is organized by KER. Calls follow OECD weight-of-evidence considerations for biological plausibility, empirical support, and quantitative understanding (OECD, 2018, 2021).

Biological plausibility of KERs

KER

Biological plausibility call

Rationale

Relationship 2009: ROS increase leads to oxidative stress increase

High

The relationship is mechanistically established because oxidative stress reflects an imbalance between oxidant production and antioxidant capacity, and ROS are primary oxidant species in cellular redox biology (Schieber and Chandel, 2014; Sies et al., 2017). AOP 478 provides a curated AOP-Wiki context for oxidative stress downstream of free radical generation (AOP-Wiki, 2026a).

Relationship 3116: oxidative stress increase leads to lipid peroxidation increase

High

Free radicals and other ROS can initiate peroxidation of polyunsaturated fatty acids in membranes, generating lipid hydroperoxides and reactive aldehydes such as MDA and 4-HNE (Ayala et al., 2014; Sies et al., 2017).

Relationship 1599: lipid peroxidation increase leads to decreased coupling of OXPHOS

High

Mitochondrial coupling depends on the integrity and composition of the inner mitochondrial membrane. Lipid peroxidation can disrupt membrane properties, promote proton leak, alter membrane potential, and impair respiratory control (Murphy, 2009; Nicholls and Ferguson, 2013; Ouillon et al., 2021).

Relationship 2203: decreased coupling of OXPHOS leads to decreased ATP pool

High

This relationship is directly reused from AOP 263. OXPHOS coupling is a major determinant of ATP production in aerobic eukaryotic cells; reduced coupling lowers ATP synthesis efficiency (AOP-Wiki, 2026b; OECD, 2022; Song and Villeneuve, 2021).

Relationship 2204: decreased ATP pool leads to decreased cell proliferation

High

This relationship is reused from AOP 263. Cell proliferation requires ATP for DNA replication, mitosis, biosynthesis, and maintenance of cellular processes; ATP depletion therefore plausibly reduces proliferation (AOP-Wiki, 2026b; OECD, 2022; Bonora et al., 2012; Song and Villeneuve, 2021).

Relationship 2205: decreased cell proliferation leads to decreased growth

High

This relationship is reused from AOP 263. Organismal, tissue, and population growth require accumulation of cells and biomass; sustained reduction in proliferation is therefore expected to reduce growth (AOP-Wiki, 2026b; Conlon and Raff, 1999; OECD, 2022).

Empirical support for KERs

KER

Empirical support call

Rationale

Inconsistencies or evidence gaps

Relationship 2009: ROS increase leads to oxidative stress increase

High

Multiple studies demonstrate concordance between ROS or ROS-producing stressors and oxidative stress markers. Paraquat increased ROS and antioxidant enzyme responses in Chlorella vulgaris (Qian et al., 2009). Paraquat also induced oxidative stress responses and lipid peroxidation in Daphnia magna (Barata et al., 2005).

ROS is often measured indirectly and may be transient; oxidative stress biomarkers vary by assay and tissue.

Relationship 3116: oxidative stress increase leads to lipid peroxidation increase

High

Oxidative stress and lipid peroxidation are often observed together. Copper increased antioxidant enzyme activity and MDA/TBARS in freshwater green microalgae (Knauert and Knauer, 2008). Paraquat and other redox-cycling stressors induced lipid peroxidation in algae and Daphnia (Barata et al., 2005; Esperanza et al., 2015; Qian et al., 2009). In the aquatic macrophyte Lemna minor, gamma radiation and the respiratory uncoupler 3,5-dichlorophenol induced a concordant oxidative stress to lipid peroxidation sequence preceding growth inhibition (Xie et al., 2018; Xie et al., 2019; Xie et al., 2022).

Lipid peroxidation can occur at different times than enzyme responses, and MDA/TBARS assays have specificity limitations.

Relationship 1599: lipid peroxidation increase leads to decreased coupling of OXPHOS

Moderate

Dietary PUFA manipulation in Daphnia showed higher lipid peroxidation associated with lower mitochondrial membrane potential (Moore et al., 2023). Cyclic hypoxia in Mya arenaria increased proton leak and reduced OXPHOS coupling efficiency, consistent with oxidative lipid and membrane damage effects on mitochondrial coupling (Ouillon et al., 2021). In Lemna minor, gamma radiation and 3,5-dichlorophenol reduced mitochondrial membrane potential downstream of lipid peroxidation, providing primary-producer support for the lipid-peroxidation to OXPHOS-coupling link (Xie et al., 2018; Xie et al., 2019).

Direct studies measuring lipid peroxidation and OXPHOS coupling in the same exposure series are limited; mitochondrial dysfunction can also promote lipid peroxidation, complicating directionality.

Relationship 2203: decreased coupling of OXPHOS leads to decreased ATP pool

High

AOP 263 reports strong evidence for this KER. Experimental studies with mitochondrial toxicants and uncouplers show concordance between impaired mitochondrial function and reduced ATP production across cell types and taxa (AOP-Wiki, 2026b; OECD, 2022; Song and Villeneuve, 2021). Cadmium exposure in oysters reduced state 3 respiration and affected mitochondrial bioenergetics (Sokolova et al., 2005).

Compensatory glycolysis or altered metabolic demand can obscure total ATP changes.

Relationship 2204: decreased ATP pool leads to decreased cell proliferation

Moderate to high

AOP 263 provides curated evidence that ATP depletion is associated with reduced cell proliferation, with dose and incidence concordance in several systems (AOP-Wiki, 2026b; OECD, 2022; Song and Villeneuve, 2021). In Chlamydomonas reinhardtii, paraquat caused ATP depletion and cell injury/death or growth-related effects in multiple-endpoint assays (Nestler et al., 2012; Jamers and De Coen, 2010).

Total ATP assays may partly reflect cell number or viability; separating ATP depletion from cytotoxicity requires careful study design.

Relationship 2205: decreased cell proliferation leads to decreased growth

Moderate

AOP 263 supports this KER using evidence that reduced proliferation contributes to growth inhibition across taxa (AOP-Wiki, 2026b; OECD, 2022; Song and Villeneuve, 2021). Algal cell density and growth rate endpoints are directly linked to cell proliferation; reduced proliferation also supports developmental growth impairment in animals.

Growth is influenced by both cell number and cell size, as well as energy allocation, development, and environmental conditions.

Inconsistencies and uncertainties

The main uncertainty for AOP 326 is the directionality and quantitative strength of the lipid peroxidation to OXPHOS coupling relationship. Lipid peroxidation can impair mitochondrial membranes, but mitochondrial dysfunction can also enhance ROS generation and thereby increase lipid peroxidation. The linear AOP represents one biologically plausible and empirically supported direction within a broader feedback-prone network. A second uncertainty is that mild mitochondrial uncoupling may reduce ROS production and serve as an adaptive response, whereas severe or sustained uncoupling reduces ATP synthesis and supports adverse outcomes. Finally, growth is a multifactorial endpoint; reduced cell proliferation is an important contributor, but organismal growth may also be influenced by nutrient status, development, endocrine regulation, cell death, and environmental factors.

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 factor

Influence or outcome

KER(s) involved

Antioxidant capacity and redox buffering

Higher antioxidant capacity reduces oxidative stress and lipid peroxidation; depletion or inhibition of antioxidant systems increases progression probability (Sies et al., 2017).

2009, 3116

Membrane lipid composition and PUFA content

High PUFA content increases susceptibility to lipid peroxidation and may increase effects on membrane potential and mitochondrial coupling (Ayala et al., 2014; Moore et al., 2023).

3116, 1599

Mitochondrial density and metabolic demand

Cells or taxa with high mitochondrial demand may be more susceptible to OXPHOS impairment and ATP depletion (Murphy, 2009; Nicholls and Ferguson, 2013).

1599, 2203

Oxygen availability and hypoxia-reoxygenation

Fluctuating oxygen can increase ROS production, proton leak, and mitochondrial bioenergetic disruption (Ouillon et al., 2021).

2009, 3116, 1599

Temperature

Temperature modifies membrane properties, oxygen demand, ROS production, and growth rate, potentially altering all downstream relationships.

Multiple

Compensatory energy metabolism

Glycolysis and other ATP-generating pathways can buffer ATP depletion after OXPHOS impairment.

2203, 2204

Life stage and growth rate

Rapidly growing or developing systems may be more sensitive to ATP depletion and reduced proliferation.

2204, 2205

Quantitative Understanding

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

Quantitative understanding varies across the AOP. The downstream AOP 263 module has the strongest quantitative foundation, whereas upstream oxidative stress and lipid peroxidation relationships are more often described qualitatively or semi-quantitatively.

KER

Quantitative understanding call

Rationale

2009: ROS increase to oxidative stress increase

Low to moderate

ROS measurements are reactive, transient, and assay-dependent. Quantitative relationships can be developed within a defined assay system, but generalizable prediction across taxa and stressors remains limited (Sies et al., 2017).

3116: oxidative stress increase to lipid peroxidation increase

Low to moderate

Dose-response relationships are reported for oxidative stress markers and lipid peroxidation in several systems, but assay differences and lipid composition strongly affect response magnitude (Ayala et al., 2014; Knauert and Knauer, 2008).

1599: lipid peroxidation increase to decreased OXPHOS coupling

Low to moderate

Some quantitative associations exist between lipid peroxidation and mitochondrial membrane potential or coupling efficiency, but models generalizable across taxa and membrane types are not yet established (Moore et al., 2023; Ouillon et al., 2021).

2203: decreased OXPHOS coupling to decreased ATP pool

High

AOP 263 reports strong quantitative understanding, supported by bioenergetic theory and models linking mitochondrial coupling and ATP production (AOP-Wiki, 2026b; OECD, 2022; Song and Villeneuve, 2021).

2204: decreased ATP pool to decreased cell proliferation

Moderate

Quantitative relationships are available in defined cell systems, but thresholds depend on cell type, metabolic state, and viability effects (AOP-Wiki, 2026b; OECD, 2022).

2205: decreased cell proliferation to decreased growth

Moderate

Growth models provide quantitative relationships between proliferation and tissue or organismal growth, but extrapolation across species and exposure contexts remains uncertain (Conlon and Raff, 1999; OECD, 2022).

 

BMD/POD-anchored concordance

The following benchmark-dose/point-of-departure (BMD/POD) concordance table anchors AOP 326 to quantitative cross-KE ordering, in line with Handbook section 4C. The multiomics point-of-departure (moPOD) dataset for gamma-irradiated Daphnia magna (Song et al., 2023) provides POD magnitudes for increased ROS, decreased ATP, decreased OXPHOS coupling, and cell death, demonstrating the expected upstream-to-downstream POD ordering (more sensitive PODs upstream). The moPOD is presented as POD magnitude evidence, not as a causal re-ordering of KEs. The Lemna minor EDR50 range provides a whole-pathway apical anchor in an aquatic primary producer.

Key event (functional category)

POD metric

POD value (mGy/h)

POD ordering

Source

KE 1115: ROS, increased (mROS)

moPOD (multiomics POD)

0.4

1 (most sensitive)

Song et al., 2023

KE 1771: ATP pool, decreased

moPOD

2.5

2

Song et al., 2023

KE 1446: OXPHOS coupling, decreased (UPS/OXPHOS module)

moPOD

42.3

3

Song et al., 2023

KE 55: Cell injury/death (apoptosis)

moPOD

42.3

3 (least sensitive)

Song et al., 2023

Upstream KE chain → growth (Lemna minor, gamma)

EDR50 (growth)

31.5–54.8 (mGy/h)

whole-pathway apical

Xie et al., 2018, 2019, 2022

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 326 can support mechanistic interpretation of growth impairment caused by oxidative stressors that induce lipid peroxidation and mitochondrial bioenergetic dysfunction. The AOP is particularly relevant for hazard identification and chemical prioritization when evidence indicates increased ROS or oxidative stress together with lipid peroxidation, mitochondrial membrane potential changes, OXPHOS impairment, ATP depletion, reduced proliferation, or growth inhibition. The AOP may also support IATA development by linking upstream NAM endpoints, such as ROS assays, lipid peroxidation markers, mitochondrial membrane potential, oxygen consumption rate, ATP content, and proliferation assays, to an apical growth endpoint.

AOP 326 can also support chemical grouping and read-across for stressors that share evidence of oxidative lipid damage and mitochondrial bioenergetic impairment. Because oxidative stress and lipid peroxidation are not chemical-specific, this AOP should not be used as a stand-alone basis for regulatory decisions. Instead, it should be used as part of a weight-of-evidence framework that considers stressor mode of action, exposure context, taxonomic relevance, assay specificity, and concordance across multiple KEs. The AOP also highlights important method-development needs, particularly standardized assays for lipid peroxidation, mitochondrial coupling, and ATP depletion that can be applied across taxa and integrated into quantitative AOP approaches.

References

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

AOP-Wiki. 2026a. AOP 478: Deposition of energy leading to occurrence of cataracts. Collaborative Adverse Outcome Pathway Wiki. Available from: https://aopwiki.org/aops/478.

AOP-Wiki. 2026b. AOP 263: Uncoupling of oxidative phosphorylation leading to growth inhibition via decreased cell proliferation. Collaborative Adverse Outcome Pathway Wiki. Available from: https://aopwiki.org/aops/263.

Ayala A, Munoz MF, Arguelles S. 2014. Lipid peroxidation: production, metabolism, and signaling mechanisms of malondialdehyde and 4-hydroxy-2-nonenal. Oxidative Medicine and Cellular Longevity 2014:360438.

Barata C, Varo I, Navarro JC, Arun S, Porte C. 2005. Antioxidant enzyme activities and lipid peroxidation in the freshwater cladoceran Daphnia magna exposed to redox cycling compounds. Comparative Biochemistry and Physiology Part C: Toxicology & Pharmacology 140:175-186.

Bonora M, Patergnani S, Rimessi A, De Marchi E, Suski JM, Bononi A, Giorgi C, Marchi S, Missiroli S, Poletti F, Wieckowski MR, Pinton P. 2012. ATP synthesis and storage. Purinergic Signaling 8:343-357.

Carvaillo JC, 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 127:047005.

Cherkasov AS, Biswas PK, Ridings DM, Ringwood AH, Sokolova IM. 2006. Effects of acclimation temperature and cadmium exposure on cellular energy budgets in the marine mollusk Crassostrea virginica: linking cellular and mitochondrial responses. Journal of Experimental Biology 209:1274-1284.

Conlon I, Raff M. 1999. Size control in animal development. Cell 96:235-244.

Esperanza M, Cid A, Herrero C, Rioboo C. 2015. Acute effects of a prooxidant herbicide on the microalga Chlamydomonas reinhardtii: screening cytotoxicity and genotoxicity endpoints. Aquatic Toxicology 165:210-221.

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 29:893-901.

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 38:1173-1175.

Knauert S, Knauer K. 2008. The role of reactive oxygen species in copper toxicity to two freshwater green microalgae. Journal of Phycology 44:311-321.

Moore TD, Martin-Creuzburg D, Yampolsky LY. 2023. Diet effects on longevity, heat tolerance, lipid peroxidation and mitochondrial membrane potential in Daphnia. Oecologia 202:151-163.

Murphy MP. 2009. How mitochondria produce reactive oxygen species. Biochemical Journal 417:1-13.

Nestler H, Groh KJ, Schonenberger R, Eggen RIL, Suter MJF. 2012. Multiple-endpoint assay provides a detailed mechanistic view of responses to herbicide exposure in Chlamydomonas reinhardtii. Aquatic Toxicology 110-111:214-224.

Nicholls DG, Ferguson SJ. 2013. Bioenergetics 4. London: Academic Press.

Nicotera P, Leist M, Ferrando-May E. 1998. Intracellular ATP, a switch in the decision between apoptosis and necrosis. Toxicology Letters 102-103:139-142. https://doi.org/10.1016/S0378-4274(98)00298-7

OECD. 2018. Users' handbook supplement to the guidance document for developing and assessing adverse outcome pathways. OECD Series on Adverse Outcome Pathways No. 1. Paris: OECD Publishing.

OECD. 2021. Guidance document for the scientific review of adverse outcome pathways. OECD Series on Testing and Assessment No. 344. Paris: OECD Publishing.

OECD. 2022. Uncoupling of oxidative phosphorylation leading to growth inhibition via decreased cell proliferation. OECD Series on Adverse Outcome Pathways No. 28. Paris: OECD Publishing.

Ouillon N, Sokolov EP, Otto S, Rehder G, Sokolova IM. 2021. Effects of variable oxygen regimes on mitochondrial bioenergetics and reactive oxygen species production in a marine bivalve, Mya arenaria. Journal of Experimental Biology 224:jeb237156.

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 18:537-543.

Schieber M, Chandel NS. 2014. ROS function in redox signaling and oxidative stress. Current Biology 24:R453-R462.

Sies H, Berndt C, Jones DP. 2017. Oxidative stress. Annual Review of Biochemistry 86:715-748.

Sokolova IM, Sokolov EP, Ponnappa KM. 2005. Cadmium exposure affects mitochondrial bioenergetics and gene expression of key mitochondrial proteins in the eastern oyster Crassostrea virginica Gmelin (Bivalvia: Ostreidae). Aquatic Toxicology 73:242-255.

Song Y, Villeneuve DL. 2021. Uncoupling of oxidative phosphorylation leading to growth inhibition via decreased cell proliferation. Environmental Toxicology and Chemistry 40:2951-2963.

Xie L, Gomes T, Solhaug KA, Song Y, Tollefsen KE. 2018. Linking mode of action of the model respiratory and photosynthesis uncoupler 3,5-dichlorophenol to adverse outcomes in Lemna minor. Aquatic Toxicology 197:98-108. https://doi.org/10.1016/j.aquatox.2018.02.005

Xie L, Solhaug KA, Song Y, Brede DA, Lind OC, Salbu B, Tollefsen KE. 2019. Modes of action and adverse effects of gamma radiation in an aquatic macrophyte Lemna minor. Science of the Total Environment 680:23-34. https://doi.org/10.1016/j.scitotenv.2019.05.016

Xie L, Song Y, Petersen K, Solhaug KA, Lind OC, Brede DA, Salbu B, Tollefsen KE. 2022. Ultraviolet B modulates gamma radiation-induced stress responses in Lemna minor at multiple levels of biological organisation. Science of the Total Environment 846:157457. https://doi.org/10.1016/j.scitotenv.2022.157457