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AOP: 646
Title
Binding and activation of AhR/PPARγ lead to lipid metabolism disorders
Short name
Graphical Representation
Point of Contact
Contributors
- Shiheng Gui
- Ruifang Fan
Coaches
OECD Information Table
| 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
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
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
Summary of the AOP
Events:
Molecular Initiating Events (MIE)
Key Events (KE)
Adverse Outcomes (AO)
| 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)
| Title | Adjacency | Evidence | Quantitative Understanding |
|---|
| AhR activation leads to Up Regulation, CYP1A1 | adjacent | High | High |
| Up Regulation, CYP1A1 leads to Increase, Oxidative Stress | adjacent | High | High |
| Increase, Oxidative Stress leads to Hepatic inflammation | adjacent | High | High |
| AhR activation leads to Activation of PPARγ | adjacent | High | High |
| Activation of PPARγ leads to Increased fatty acid synthesis and transport | adjacent | High | High |
| Activation of PPARγ leads to Decrease, FAO | adjacent | High | High |
| Increased fatty acid synthesis and transport leads to Abnormal lipid accumulation | adjacent | High | High |
| Decrease, FAO leads to Abnormal lipid accumulation | adjacent | High | High |
| Increase, Oxidative Stress leads to Hepatocyte injury | adjacent | Moderate | Moderate |
| Abnormal lipid accumulation leads to Hepatocyte injury | adjacent | Moderate | Moderate |
| Hepatocyte injury leads to Abnormal lipid metabolism | adjacent | High | High |
Network View
Prototypical Stressors
Life Stage Applicability
| Life stage | Evidence |
|---|---|
| During development and at adulthood | High |
Taxonomic Applicability
Sex Applicability
| Sex | Evidence |
|---|---|
| Male | High |
Overall Assessment of the AOP
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
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
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 CD36—a 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
|
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 Factor (MF) | Influence or Outcome | KER(s) involved |
|---|---|---|
Quantitative Understanding
Considerations for Potential Applications of the AOP (optional)
References
References
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