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AOP: 646

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

Binding and activation of AhR/PPARγ lead to lipid metabolism disorders

Short name
A name that succinctly summarises the information from the title. This name should not exceed 90 characters. More help
Binding and activation of AhR/PPARγ lead to lipid metabolism disorders
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 v2.8

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

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Ruifang Fan、Shiheng Gui

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
Shiheng Gui   (email point of contact)

Contributors

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  • Shiheng Gui
  • Ruifang Fan

Coaches

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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 July 09, 2026 09:43

Revision dates for related pages

Page Revision Date/Time
Aryl hydrocarbon receptor(AhR)activation July 09, 2026 03:41
Activation of PPARγ March 18, 2018 09:40
Up Regulation, CYP1A1 September 16, 2017 10:15
Increase, Oxidative Stress February 11, 2026 07:05
Increase, Hepatic inflammation July 09, 2026 09:01
Increased , Fatty acid synthesis and transport July 09, 2026 09:03
Decrease, Fatty acid β-oxidation November 25, 2020 10:26
Increase, Abnormal lipid accumulation July 09, 2026 09:06
Increase, Hepatocyte injury July 09, 2026 09:08
Abnormal lipid metabolism April 07, 2022 09:21
AhR activation leads to Up Regulation, CYP1A1 July 09, 2026 09:10
Up Regulation, CYP1A1 leads to Increase, Oxidative Stress July 09, 2026 09:11
Increase, Oxidative Stress leads to Hepatic inflammation July 09, 2026 09:12
AhR activation leads to Activation of PPARγ July 09, 2026 09:14
Activation of PPARγ leads to Increased fatty acid synthesis and transport July 09, 2026 09:11
Activation of PPARγ leads to Decrease, FAO July 09, 2026 09:12
Increased fatty acid synthesis and transport leads to Abnormal lipid accumulation July 09, 2026 09:13
Decrease, FAO leads to Abnormal lipid accumulation July 09, 2026 09:26
Increase, Oxidative Stress leads to Hepatocyte injury July 09, 2026 09:27
Abnormal lipid accumulation leads to Hepatocyte injury July 09, 2026 09:28
Hepatocyte injury leads to Abnormal lipid metabolism July 09, 2026 09:29
Naphthalene July 03, 2026 11:28
Acenaphthylene July 09, 2026 06:14
Acenaphthene July 09, 2026 06:10
Fluorene July 09, 2026 06:14
Phenanthrene November 29, 2016 18:42
Anthracene July 03, 2026 11:29
Fluoranthene July 09, 2026 06:28
Pyrene July 03, 2026 11:30
Benz(a)anthracene July 03, 2026 11:31
Chrysene July 03, 2026 11:31
Benzo(b)fluoranthene July 03, 2026 11:22
Benzo(k)fluoranthene November 29, 2016 18:42
Benzo(a)pyrene March 20, 2020 20:17
Indeno(1,2,3-cd)pyrene July 09, 2026 07:32
Dibenz(a,h)anthracene July 09, 2026 07:32
Benzo(g,h,i)perylene July 09, 2026 07:33

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

Polycyclic aromatic hydrocarbons (PAHs) are a class of persistent organic pollutants derived from incomplete combustion processes, widely present in tobacco smoke, vehicle exhaust, industrial emissions, and high-temperature cooking fumes. Humans can be exposed through multiple routes including the respiratory tract, digestive tract, and skin, posing clear risks of teratogenicity, carcinogenicity, and mutagenicity. This Adverse Outcome Pathway (AOP) systematically describes how PAHs, upon exposure, bind to and activate the Aryl Hydrocarbon Receptor (AhR), inducing high mRNA expression of the phase I metabolic enzyme CYP1A1, while simultaneously triggering oxidative stress and elevated levels of pro-inflammatory factors. Through the interactive regulation between AhR and the Peroxisome Proliferator-Activated Receptor gamma (PPARγ) signaling pathways, this leads to an imbalance in the expression profile of lipid metabolism-related genes. Specifically, genes related to lipid synthesis and fatty acid transport (SREBP-1, DGAT1, FAS, CD36) are significantly upregulated, whereas genes related to fatty acid β-oxidation (PPARα, CPT1A) are significantly downregulated. The cascading effects of these molecular events ultimately drive abnormal elevations in hepatic triglyceride (TG) and total cholesterol (TC) levels, leading to lipid metabolism disorders. This AOP constructs a complete causal chain from the molecular initiating event to the adverse outcome, providing a mechanistic foundation and theoretical basis for the quantitative health risk assessment of PAHs and the targeted prevention and control of metabolic diseases.

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

Polycyclic aromatic hydrocarbons (PAHs) are a class of persistent organic compounds composed of two or more fused benzene rings, ubiquitous in the environment(Biache et al., 2014). They are primarily generated through incomplete combustion processes, such as vehicle exhaust, industrial emissions, tobacco smoke, and cooking fumes (Zhang and Tao, 2009), and are intrinsic to the optical properties and toxicity of combustion particles. Humans are mainly exposed to PAHs through inhalation, dietary intake, and dermal contact (Kim et al., 2013). The health effects of PAHs depend on both the exposure concentration, duration, and route, as well as the relative toxicity of individual PAHs (Mallah et al., 2022). The United States Environmental Protection Agency (USEPA) has listed 16 PAHs as priority control pollutants based on their environmental concentrations and biological toxicity (Mallah et al., 2022). Generally, PAHs are metabolized and detoxified by the liver; therefore, prolonged exposure to PAHs can exacerbate hepatic detoxification overload. As the core organ for lipid metabolism, the liver maintains lipid homeostasis through pathways including fatty acid uptake and export, de novo fatty acid synthesis, and fatty acid β-oxidation (Badmus et al., 2022). Imbalance in this regulatory network leads to intrahepatocellular lipid accumulation, accompanied by abnormal elevations in serum triglycerides (TG) and total cholesterol (TC), and may even induce cardiovascular diseases (Zhao et al., 2023). Therefore, it is necessary to assess the health risks of PAHs to the liver based on the Adverse Outcome Pathway (AOP) framework.

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

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 2430 Aryl hydrocarbon receptor(AhR)activation AhR activation
MIE 1507 Activation of PPARγ Activation of PPARγ
KE 80 Up Regulation, CYP1A1 Up Regulation, CYP1A1
KE 1392 Increase, Oxidative Stress Increase, Oxidative Stress
KE 2440 Increase, Hepatic inflammation Hepatic inflammation
KE 2441 Increased , Fatty acid synthesis and transport Increased fatty acid synthesis and transport
KE 1824 Decrease, Fatty acid β-oxidation Decrease, FAO
KE 2442 Increase, Abnormal lipid accumulation Abnormal lipid accumulation
KE 2443 Increase, Hepatocyte injury Hepatocyte injury
AO 1995 Abnormal lipid metabolism Abnormal lipid metabolism

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
During development and at adulthood 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
human Homo sapiens Low NCBI
rat Rattus norvegicus High NCBI

Sex Applicability

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

Since PAHs are volatile hydrocarbons produced by incomplete combustion of organic matter, previous research has focused on the damage caused by PAHs to the respiratory system, particularly the lungs. Epidemiological studies have also found that PAH exposure may increase the risk of fatty liver disease by affecting hepatic lipid metabolism (Zhou et al., 2024). Therefore, this Adverse Outcome Pathway (AOP) focuses on the association between PAH exposure and abnormal hepatic lipid metabolism. However, current in vivo and in vitro evidence exploring PAH exposure-induced abnormal hepatic lipid metabolism remains relatively scarce, and the specific mechanisms are still unclear. Moreover, existing studies have mostly focused on the exposure toxicity of individual PAH congeners, which cannot reflect real-world environmental PAH exposure scenarios. Therefore, this AOP uses the concentrations of 16 priority-controlled PAHs detected in the serum of the general population as a reference, setting three exposure concentration gradients to investigate the hepatotoxicity of PAH exposure and the molecular mechanisms by which it affects hepatic lipid metabolism.

This AOP takes AhR activation as the initiating event. PAHs can directly activate AhR, accompanied by enhanced systemic inflammation and oxidative stress, leading to significantly increased expression of PPARγ and genes related to lipid synthesis and fatty acid transport, significantly decreased expression of genes related to fatty acid β-oxidation, abnormal lipid accumulation, elevated hepatic TG and TC, and ultimately inducing abnormal lipid metabolism. Experimental results can be obtained from various models, including experimental animals and mice. Evidence from in vivo animal experiments, in vitro experiments, and computational simulations can confirm the associations between the Molecular Initiating Event (MIE) and Key Event Relationships (KERs).

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

In Hepa 1c1c7 cells, studies have found that benzo[a]pyrene exposure can cause AhR activation and lead to oxidative stress and lipid peroxidation (Elbekai et al., 2004). This indicates that AhR activation is the core initiating event for PAH-induced disruption of lipid metabolism. Similarly, in HepG2 cells, B[a]P exposure activates the Aryl Hydrocarbon Receptor (AHR), inducing cytochrome P450 enzyme expression, and further CYP1B1-induced mTOR activation and decreased lipophagy, ultimately leading to lipid accumulation (Bu et al., 2024).

Animal experiments demonstrate that AhR activation significantly promotes the development of abnormal lipid metabolism. In mouse models, low-dose B[a]P exposure can induce hepatic lipid deposition (Li et al., 2023) . Similarly, in mouse models, BbF exposure activates the AhR receptor, elevates CYP enzyme levels, upregulates SREBP-1c and SCD1, accompanied by inflammatory responses and hepatic oxidative stress, ultimately leading to lipid metabolism disorders (Liu et al., 2025) . Among CYP enzymes, CYP1A1 is a key enzyme in oxidative stress; its overexpression can trigger oxidative stress by affecting reactive oxygen species (ROS) and superoxide dismutase (SOD) levels. After African catfish were exposed to benzo[b]fluoranthene, hepatic antioxidant markers (glutathione-S-transferase, SOD, catalase) were significantly reduced, and oxidative stress was exacerbated (Obanya et al., 2019).

Meanwhile, epidemiological studies in human populations have found that PAH exposure is associated with disease risk. PAH exposure has significant effects on lipid metabolism, particularly on the development of dyslipidemia and fatty liver disease. One study found that elevated levels of urinary PAH metabolites were associated with increased concentrations of total cholesterol (TC) and LDL-C (Ma et al., 2019). Similarly, a study of 827 adolescents found that 22.13% of the adolescents had metabolic syndrome, and their urinary levels of PAH metabolites such as 2-hydroxynaphthalene (2-NAP) and 2-hydroxyfluorene (2-FLU) were significantly higher than those in the non-metabolic syndrome group (Wu et al., 2025). Occupational exposure is an important pathway for elevated internal PAH burdens in young and middle-aged populations (Jiang and Zhao, 2024). Typical high-risk occupations include coke oven workers and firefighters, whose work environments have significantly higher PAH concentrations than the general population (Pálešová et al., 2023). In addition, tobacco use rates are higher in this age group, and smoking behavior can further increase PAH exposure. Studies have shown that urinary PAH biomarker levels in smokers are significantly higher than in non-smokers (Wang et al., 2019).

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

MIE: AhR activation

After entering target cells as exogenous ligands, polycyclic aromatic hydrocarbons (PAHs) bind with high affinity to the Aryl Hydrocarbon Receptor (AhR), which is maintained in the cytoplasm by a chaperone complex including HSP90, XAP2, and p23. This binding induces conformational changes in AhR and releases the chaperones, exposing its nuclear localization signal. AhR then rapidly translocates to the nucleus, forms a heterodimer with the AhR Nuclear Translocator (ARNT), recognizes and binds to xenobiotic response elements (XREs) in the promoter regions of target genes, and initiates the transcription of phase I metabolic enzymes such as CYP1A1 and downstream inflammatory genes, thereby triggering the molecular initiating event of the entire toxicity cascade.

MIE: PPARγ activation

Under PAH exposure conditions, the Peroxisome Proliferator-Activated Receptor gamma (PPARγ), a core nuclear receptor regulating adipogenesis and lipid storage, undergoes abnormal changes in its activity state (activation or functional remodeling). It forms a heterodimer with the Retinoid X Receptor (RXR) and binds to PPRE response elements, directly regulating the transcription of downstream lipid metabolism target genes. This event, together with AhR activation, constitutes the MIE, laying the molecular foundation for subsequent lipid synthesis and oxidation imbalance through the interaction of two nuclear receptor signaling pathways.

KE1: Upregulated CYP1A1 mRNA leves

Driven by the binding of the AhR-ARNT dimer to XREs, the transcriptional level of the CYP1A1 gene is significantly upregulated, followed by increased protein expression and enzymatic activity. This accelerates the metabolic activation of PAHs, generating highly reactive electrophilic intermediate metabolites (such as benzo[a]pyrene-7,8-dihydrodiol-9,10-epoxide, BPDE), while simultaneously producing large amounts of reactive oxygen species (ROS).

KE2: Oxidative stress

CYP1A1-mediated metabolic activation of PAHs and mitochondrial electron transport chain dysfunction lead to excessive accumulation of ROS within hepatocytes, exceeding the scavenging capacity of endogenous antioxidant systems such as superoxide dismutase (SOD).

KE3: Hepatic inflammation

Under the dual activation of oxidative stress and AhR signaling, transcription factors such as Nuclear Factor-kappa B (NF-κB) are activated and translocate into the nucleus, driving the massive synthesis and secretion of pro-inflammatory cytokines and chemokines such as Tumor Necrosis Factor-alpha (TNF-α), Interleukin-6 (IL-6), and IL-1β. This forms a chronic low-grade inflammatory microenvironment, further disrupting lipid metabolic homeostasis.

KE4: Increased fatty acid synthesis and transport

Under the interactive regulation of inflammatory signals and dysregulated nuclear receptors (AhR/PPARγ), the expression of sterol regulatory element-binding protein-1 (SREBP-1), fatty acid synthase (FAS)a key enzyme for de novo fatty acid synthesis, diacylglycerol acyltransferase 1 (DGAT1)a key enzyme for triglyceride synthesis, and CD36a fatty acid uptake transporter, are significantly upregulated in the liver and adipose tissue. Together, these promote the uptake of exogenous fatty acids and the synthesis of endogenous lipids, leading to overactivation of the lipid input pathway.

KE5: Decreased fatty acid β-oxidation

Accompanying the activation of synthetic pathways, hepatic fatty acid β-oxidation capacity is significantly inhibited. The expression of key oxidative enzymes and transporters such as Peroxisome Proliferator-Activated Receptor alpha (PPARα) and Carnitine Palmitoyltransferase 1A (CPT1A) is markedly downregulated, forming a metabolic imbalance pattern characterized by "increased synthesis and decreased decomposition."

KE6: Abnormal lipid accumulation

Due to increased fatty acid synthesis and uptake coupled with decreased β-oxidation, triglycerides and cholesterol are massively deposited within hepatocytes and adipocytes, resulting in significantly elevated levels of triglycerides (TG) and total cholesterol (TC) in hepatic tissue, and forming lipid droplet accumulation.

KE7: Hepatocyte injury

Under normal conditions, aspartate aminotransferase (AST) and alanine aminotransferase (ALT) are primarily located within hepatocytes, with very low levels in serum. When hepatocyte membrane integrity is compromised or cells undergo necrosis, these enzymes are released into the bloodstream, leading to elevated serum levels.

Evidence Assessment

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

Essentiality of KE

Definitional Question

High (Strong)

Moderate

Low (Weak)

If the upstream KE is blocked, will the downstream KE and/or AO be prevented?

Direct evidence from specifically designed experimental studies indicating that at least one important KE is essential

Indirect evidence suggesting that sufficient modification of the expected modulating factor would weaken or enhance the KE

No or contradictory experimental evidence proving the essentiality of any KE

KE1: Upregulated CYP1A1 mRNA leves

High

Various PAHs such as BaP and TCDD can dose-dependently induce CYP1A1 mRNA and protein expression

KE2: Oxidative stress

High

CYP1A1 catalyzes the metabolic activation of PAHs to produce highly reactive epoxide and quinone intermediates, which can generate large amounts of ROS through redox cycling. Meanwhile, the catalytic cycle of CYP1A1 itself can also leak electrons to generate superoxide anions.

KE3: Hepatic inflammation

High

ROS can activate redox-sensitive signaling pathways such as NF-κB and release pro-inflammatory cytokines such as TNF-α, IL-1, and IL-6, leading to hepatocyte injury and inflammation.

KE4: Increased fatty acid synthesis and transport

High

Elevated PPARγ expression can upregulate lipogenic transcription factors such as SREBP-1c. Inflammatory factors (TNF-α, IL-1, and IL-6) can activate the SREBP-1c pathway, promoting fatty acid synthesis. Meanwhile, inflammation can induce the expression of uptake proteins such as CD36.

KE5: Decreased fatty acid β-oxidation

High

Elevated PPARγ expression may inhibit PPARα expression. Inflammatory factors can inhibit PPARα and reduce CPT1A expression. Meanwhile, inflammation may induce malonyl-CoA accumulation, inhibiting CPT1A activity.

KE6: Abnormal lipid accumulation

High

Increased fatty acid synthesis coupled with decreased oxidation creates a metabolic imbalance characterized by "more in, less out," leading to massive accumulation of fatty acids within hepatocytes and resulting in elevated TG and TC levels in hepatic tissue.

KE7: Hepatocyte injury

High

Excessive lipid accumulation in hepatic tissue may induce lipotoxicity, oxidative stress, and inflammatory responses, ultimately leading to hepatocyte apoptosis and necrosis, with elevated serum levels of AST and ALT.

AO: Abnormal hepatic lipid metabolism

High

Hepatocyte injury leads to impaired liver function, including dysfunction in lipid synthesis, oxidation, transport, and secretion, ultimately manifesting as comprehensive abnormal hepatic lipid metabolism.

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 (MF) Influence or Outcome KER(s) involved
     

Quantitative Understanding

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

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

References

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

References

[1]   Badmus, O.O., Hillhouse, S.A., Anderson, C.D., Hinds, T.D., Stec, D.E., 2022. Molecular mechanisms of metabolic associated fatty liver disease (MAFLD): functional analysis of lipid metabolism pathways. Clin Sci (Lond) 136, 1347-1366.10.1042/cs20220572

[2]   Biache, C., Mansuy-Huault, L., Faure, P., 2014. Impact of oxidation and biodegradation on the most commonly used polycyclic aromatic hydrocarbon (PAH) diagnostic ratios: Implications for the source identifications. Journal of Hazardous Materials 267, 31-39.https://doi.org/10.1016/j.jhazmat.2013.12.036

[3]   Bu, K.-B., Kim, M., Shin, M.K., Lee, S.-H., Sung, J.-S., 2024. Regulation of Benzo[a]pyrene-Induced Hepatic Lipid Accumulation through CYP1B1-Induced mTOR-Mediated Lipophagy. International Journal of Molecular Sciences 25, 1324https://www.mdpi.com/1422-0067/25/2/1324

[4]   Elbekai, R.H., Korashy, H.M., Wills, K., Gharavi, N., El-Kadi, A.O.S., 2004. Benzo[a]pyrene, 3-methylcholanthrene and beta-naphthoflavone induce oxidative stress in hepatoma hepa 1c1c7 Cells by an AHR-dependent pathway. Free radical research 38, 1191-1200.10.1080/10715760400017319

[5]   Jiang, M., Zhao, H., 2024. Joint association of heavy metals and polycyclic aromatic hydrocarbons exposure with depression in adults. Environmental Research 242, 117807.https://doi.org/10.1016/j.envres.2023.117807

[6]   Kim, K.-H., Jahan, S.A., Kabir, E., Brown, R.J.C., 2013. A review of airborne polycyclic aromatic hydrocarbons (PAHs) and their human health effects. Environment International 60, 71-80.https://doi.org/10.1016/j.envint.2013.07.019

[7]   Li, Y., Liang, N., Tang, T., Zheng, Z., Chen, M., Mo, J., Zhang, N., Liao, S., Lei, Y., Wu, Y., Lan, C., Ding, H., Du, B., Feng, M., Wang, X., Li, X., Huang, Y., Lu, C., Tang, S., Li, X., 2023. Low-dose benzo[a]pyrene exposure induces hepatic lipid deposition through LCMT1/PP2Ac-mediated autophagy inhibition. Food Chem Toxicol 179, 113986.10.1016/j.fct.2023.113986

[8]   Liu, X., Zhang, X., Zhu, J., Zou, W., Liang, L., Zhang, J., Wen, C., Li, Y., Liu, G., Xu, X., 2025. BbF-induced liver injury in Balb/c mice: AhR activation as the conductor of metabolism, oxidative stress, lipid metabolism disorder, and inflammatory response. Free Radical Biology and Medicine 241, 617-630.https://doi.org/10.1016/j.freeradbiomed.2025.10.008

[9]   Ma, J., Zhou, Y., Liu, Y., Xiao, L., Cen, X., Li, W., Guo, Y., Kim, M., Yuan, J., Chen, W., 2019. Association between urinary polycyclic aromatic hydrocarbon metabolites and dyslipidemias in the Chinese general population: A cross-sectional study. Environmental Pollution 245, 89-97.https://doi.org/10.1016/j.envpol.2018.10.134

[10] Mallah, M.A., Changxing, L., Mallah, M.A., Noreen, S., Liu, Y., Saeed, M., Xi, H., Ahmed, B., Feng, F., Mirjat, A.A., Wang, W., Jabar, A., Naveed, M., Li, J.-H., Zhang, Q., 2022. Polycyclic aromatic hydrocarbon and its effects on human health: An overeview. Chemosphere 296, 133948.https://doi.org/10.1016/j.chemosphere.2022.133948

[11] Obanya, H.E., Omoarukhe, A., Amaeze, N.H., Okoroafor, C.U., 2019. Polycyclic Aromatic Hydrocarbons in Ologe Lagoon and Effects of Benzo[b]fluoranthene in African Catfish. J Health Pollut 9, 190605.10.5696/2156-9614-9.22.190605

[12] Pálešová, N., Maitre, L., Stratakis, N., Řiháčková, K., Pindur, A., Kohoutek, J., Šenk, P., Bartošková Polcrová, A., Gregor, P., Vrijheid, M., Čupr, P., 2023. Firefighters and the liver: Exposure to PFAS and PAHs in relation to liver function and serum lipids (CELSPAC-FIREexpo study). International Journal of Hygiene and Environmental Health 252, 114215.https://doi.org/10.1016/j.ijheh.2023.114215

[13] Wang, Y., Wong, L.Y., Meng, L., Pittman, E.N., Trinidad, D.A., Hubbard, K.L., Etheredge, A., Del Valle-Pinero, A.Y., Zamoiski, R., van Bemmel, D.M., Borek, N., Patel, V., Kimmel, H.L., Conway, K.P., Lawrence, C., Edwards, K.C., Hyland, A., Goniewicz, M.L., Hatsukami, D., Hecht, S.S., Calafat, A.M., 2019. Urinary concentrations of monohydroxylated polycyclic aromatic hydrocarbons in adults from the U.S. Population Assessment of Tobacco and Health (PATH) Study Wave 1 (2013-2014). Environ Int 123, 201-208.10.1016/j.envint.2018.11.068

[14] Wu, J., Cui, S., Li, X., Zhang, X., Yang, S., Sun, J., Jiang, X., 2025. Association between polycyclic aromatic hydrocarbons exposure and metabolic dysfunction-associated steatotic liver disease in US adults. Frontiers in Public Health Volume 13 - 2025.10.3389/fpubh.2025.1540357

[15] Zhang, Y., Tao, S., 2009. Global atmospheric emission inventory of polycyclic aromatic hydrocarbons (PAHs) for 2004. Atmospheric Environment 43, 812-819.https://doi.org/10.1016/j.atmosenv.2008.10.050

[16] Zhao, T., Li, X., Qian, H., Miao, X., Zhu, Y., Wang, J., Hui, J., Zhou, L., Ye, L., 2023. PM2.5 induces the abnormal lipid metabolism and leads to atherosclerosis via Notch signaling pathway in rats. Toxicology 485, 153415.https://doi.org/10.1016/j.tox.2022.153415

[17] Zhou, S., Guo, C., Dai, Y., Pan, X., Luo, X., Qin, P., Tan, L., 2024. Association between polycyclic aromatic hydrocarbon exposure and liver function: The mediating roles of inflammation and oxidative stress. Environmental Pollution 342, 123068.https://doi.org/10.1016/j.envpol.2023.123068