AOP ID and Title:
Graphical Representation
Status
| Author status | OECD status | OECD project | SAAOP status |
|---|---|---|---|
| Under development: Not open for comment. Do not cite |
Abstract
Liver fibrosis, characterized by excessive accumulation of extracellular matrix proteins, represents a significant health burden worldwide. The Ah receptor (AhR), a ligand-activated transcription factor primarily known for its involvement in xenobiotic metabolism, has emerged as a key player in various physiological processes, including liver homeostasis and inflammation. Recent studies have implicated the AhR signaling pathway in the development and progression of liver fibrosis. This AOP provides a comprehensive overview of the molecular mechanisms underlying the association between AhR activation and liver fibrogenesis. AhR activation by endogenous ligands, such as tryptophan metabolites and environmental toxins, triggers a cascade of events leading to hepatic stellate cell activation, inflammation, and fibrogenesis. Understanding the intricate interplay between AhR and liver fibrosis offers novel insights into the pathogenesis of chronic liver diseases and highlights AhR as a potential therapeutic target for the management of liver fibrosis.
Background
Understanding the biological link between Ah receptor (AhR) activation and liver fibrosis holds significant relevance due to its implications in the pathogenesis of various liver diseases. Liver fibrosis represents a common pathological process underlying the progression of chronic liver disorders, including hepatitis, alcoholic liver disease, and non-alcoholic fatty liver disease (NAFLD). Notably, NAFLD, characterized by hepatic steatosis, inflammation, and fibrosis, has become a global health concern, closely associated with obesity, metabolic syndrome, and insulin resistance. Given that AhR activation has been implicated in the regulation of lipid metabolism and inflammation, elucidating its role in liver fibrosis provides valuable insights into the molecular mechanisms driving NAFLD progression. Moreover, the interconnected nature of liver diseases underscores the importance of investigating AhR-mediated pathways as potential therapeutic targets for the management of liver fibrosis and its comorbidities, including hepatic steatosis. Therefore, establishing a biological link between AhR activation and liver fibrosis not only enhances our understanding of disease pathogenesis but also offers promising avenues for the development of targeted therapies for liver-related disorders.
Summary of the AOP
Events
Molecular Initiating Events (MIE), Key Events (KE), Adverse Outcomes (AO)
| Sequence | Type | Event ID | Title | Short name |
|---|---|---|---|---|
| MIE | 18 | Activation, AhR | Activation, AhR | |
| KE | 80 | Up Regulation, CYP1A1 | Up Regulation, CYP1A1 | |
| KE | 1364 | Increase, Reactive oxygen species | Increase, ROS | |
| KE | 55 | Increase, Cell injury/death | Cell injury/death | |
| KE | 459 | Increased, Liver Steatosis | Increased, Liver Steatosis | |
| KE | 265 | Activation, Stellate cells | Activation, Stellate cells | |
| KE | 1494 | Leukocyte recruitment/activation | Leukocyte recruitment/activation | |
| KE | 1501 | Increased, extracellular matrix deposition | Increased extracellular matrix deposition | |
| AO | 344 | N/A, Liver fibrosis | N/A, Liver fibrosis |
Key Event Relationships
| Upstream Event | Relationship Type | Downstream Event | Evidence | Quantitative Understanding |
|---|---|---|---|---|
| Activation, AhR | adjacent | Up Regulation, CYP1A1 | High | High |
| Up Regulation, CYP1A1 | adjacent | Increase, Reactive oxygen species | High | High |
| Activation, AhR | adjacent | Increased, Liver Steatosis | High | Moderate |
| Increased, Liver Steatosis | adjacent | Increase, Cell injury/death | Moderate | Moderate |
| Increase, Cell injury/death | adjacent | Activation, Stellate cells | Moderate | Moderate |
| Increase, Cell injury/death | adjacent | Leukocyte recruitment/activation | Moderate | Moderate |
| Leukocyte recruitment/activation | adjacent | Increased, extracellular matrix deposition | Moderate | Moderate |
| Activation, Stellate cells | adjacent | Increased, extracellular matrix deposition | High | High |
| Increased, extracellular matrix deposition | adjacent | N/A, Liver fibrosis | High | High |
Stressors
| Name | Evidence |
|---|---|
| 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) |
Overall Assessment of the AOP
The biological plausibility of KERs is defined by the OECD as the « understanding of the fundamental biological processes involved and whether they are consistent with the causal relationship being proposed in the AOP ». The biological plausibility is strong due to the presence of overwhelming evidence present in different studies. A minor setback would be the difficulty to dismiss alternative mechanisms caused by the ligands used for AhR activation.
The essentiality of KEs refers to « experimental data for whether or not downstream KEs or the AO are prevented or modified if an upstream event is blocked ». The essentiality of KEs is strong: most works converge to imply the AhR in fibrotic processes. One setback would be that AhR knockout mice also develop a specific liver fibrosis. We propose that exogenous ligands alter the activity of endogenous ligands and therefore contribute just like the knockout to the occurence of liver fibrosis. The AhR activation needs to be considered then as the binding of exogenous ligands (xenobiotics) counteracting on the physiological processes which regulate the physiological functions.
Finally, the empirical support of KERs, is often « based on toxicological data derived by one or more reference chemicals where dose–response and temporal concordance for the KE pair can be assessed ». The overall assessment of the empirical support of our KERs is also strong. There is evidence in human cell lines and mice showing a dose–response and temporal concordance for severity of our KEs and the adverse outcomes (for example, a dose-dependant effect of TCDD on the development of liver fibrosis in mice).
Domain of Applicability
Life Stage Applicability| Life Stage | Evidence |
|---|---|
| Adults | Moderate |
| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| Homo sapiens | Homo sapiens | Moderate | NCBI |
| Mus musculus | Mus musculus | High | NCBI |
| Sex | Evidence |
|---|---|
| Mixed | Moderate |
References
Appendix 1
List of MIEs in this AOP
Event: 18: Activation, AhR
Short Name: Activation, AhR
Key Event Component
| Process | Object | Action |
|---|---|---|
| aryl hydrocarbon receptor activity | aryl hydrocarbon receptor | increased |
AOPs Including This Key Event
Stressors
| Name |
|---|
| Benzidine |
| Dibenzo-p-dioxin |
| Polychlorinated biphenyl |
| Polychlorinated dibenzofurans |
| Hexachlorobenzene |
| Polycyclic aromatic hydrocarbons (PAHs) |
Biological Context
| Level of Biological Organization |
|---|
| Molecular |
Domain of Applicability
Taxonomic Applicability| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| zebra danio | Danio rerio | High | NCBI |
| Gallus gallus | Gallus gallus | High | NCBI |
| Pagrus major | Pagrus major | High | NCBI |
| Acipenser transmontanus | Acipenser transmontanus | High | NCBI |
| Acipenser fulvescens | Acipenser fulvescens | High | NCBI |
| rainbow trout | Oncorhynchus mykiss | High | NCBI |
| Salmo salar | Salmo salar | High | NCBI |
| Xenopus laevis | Xenopus laevis | High | NCBI |
| Ambystoma mexicanum | Ambystoma mexicanum | High | NCBI |
| Phasianus colchicus | Phasianus colchicus | High | NCBI |
| Coturnix japonica | Coturnix japonica | High | NCBI |
| mouse | Mus musculus | High | NCBI |
| rat | Rattus norvegicus | High | NCBI |
| human | Homo sapiens | High | NCBI |
| Microgadus tomcod | Microgadus tomcod | High | NCBI |
| Homo sapiens | Homo sapiens | NCBI |
| Life Stage | Evidence |
|---|---|
| Embryo | High |
| Development | High |
| All life stages | High |
| Sex | Evidence |
|---|---|
| Unspecific | High |
The AHR structure has been shown to contribute to differences in species sensitivity to DLCs in several animal models. In 1976, a 10-fold difference was reported between two strains of mice (non-responsive DBA/2 mouse, and responsive C57BL/6 14 mouse) in CYP1A induction, lethality and teratogenicity following TCDD exposure[3]. This difference in dioxin sensitivity was later attributed to a single nucleotide polymorphism at position 375 (the equivalent position of amino acid residue 380 in chicken) in the AHR LBD[30][19][31]. Several other studies reported the importance of this amino acid in birds and mammals[32][30][22][33][34][35][31][36]. It has also been shown that the amino acid at position 319 (equivalent to 324 in chicken) plays an important role in ligand-binding affinity to the AHR and transactivation ability of the AHR, due to its involvement in LBD cavity volume and its steric effect[35]. Mutation at position 319 in the mouse eliminated AHR DNA binding[35].
The first study that attempted to elucidate the role of avian AHR1 domains and key amino acids within avian AHR1 in avian differential sensitivity was performed by Karchner et al.[22]. Using chimeric AHR1 constructs combining three AHR1 domains (DBD, LBD and TAD) from the chicken (highly sensitive to DLC toxicity) and common tern (resistant to DLC toxicity), Karchner and colleagues[22], showed that amino acid differences within the LBD were responsible for differences in TCDD sensitivity between the chicken and common tern. More specifically, the amino acid residues found at positions 324 and 380 in the AHR1 LBD were associated with differences in TCDD binding affinity and transactivation between the chicken (Ile324_Ser380) and common tern (Val324_Ala380) receptors[22]. Since the Karchner et al. (2006) study was conducted, the predicted AHR1 LBD amino acid sequences were been obtained for over 85 species of birds and 6 amino acid residues differed among species[14][37] . However, only the amino acids at positions 324 and 380 in the AHR1 LBD were associated with differences in DLC toxicity in ovo and AHR1-mediated gene expression in vitro[14][37][16]. These results indicate that avian species can be divided into one of three AHR1 types based on the amino acids found at positions 324 and 380 of the AHR1 LBD: type 1 (Ile324_Ser380), type 2 (Ile324_Ala380) and type 3 (Val324_Ala380)[14][37][16].
- Little is known about differences in binding affinity of AhRs and how this relates to sensitivity in non-avian taxa.
- Low binding affinity for DLCs of AhR1s of African clawed frog (Xenopus laevis) and axolotl (Ambystoma mexicanum) has been suggested as a mechanism for tolerance of these amphibians to DLCs (Lavine et al 2005; Shoots et al 2015).
- Among reptiles, only AhRs of American alligator (Alligator mississippiensis) have been investigated and little is known about the sensitivity of American alligator or other reptiles to DLCs (Oka et al 2016).
- Among fishes, great differences in sensitivity to DLCs are known both for AhRs and for embryos among species that have been tested (Doering et al 2013; 2014).
- Differences in binding affinity of the AhR2 have been demonstrated to explain differences in sensitivity to DLCs between sensitive and tolerant populations of Atlantic Tomcod (Microgadus tomcod) (Wirgin et al 2011).
- This was attributed to the rapid evolution of populations in highly contaminated areas of the Hudson River, resulting in a 6-base pair deletion in the AHR sequence (outside the LBD) and reduced ligand binding affinity, due to reduces AHR protein stability.
- Information is not yet available regarding whether differences in binding affinity of AhRs of fishes are predictive of differences in sensitivity of embryos, juveniles, or adults (Doering et al 2013).
The AhR is a very conserved and ancient protein (95) and the AhR is present in human and mice (96–98). The AhR is present in human physiology and pathology. The AhR is highly expressed at several important physiological barriers such as the placenta, lung, gastrointestinal system, and liver in human (Wakx, Marinelli, Watanabe). In these tissues, the AhR is involved in both detoxication processes involving xenobiotic metabolizing enzymes such as cytochromes P450, and in immune functions translating chemical signals into immune defence pathways (Marinelli, Stobbe). Moreover, it has a regulatory role in human dendritic cells and myelination (Kado, Shackleford). The lung constitutes another barrier exposed to components of air pollution such as particles and hydrocarbons (air pollution, cigarette smoke). The AhR detects such hydrocarbons and protects the pulmonary cells from their deleterious effects through metabolization. The regulatory effect on blood cells of the AhR, balancing different related cell types, can be extended to the megakaryocytes and their precursors; indeed, StemRegenin 1 (SR1), an antagonist of the AhR increases the human population of CD34+CD41low cells, a fraction of very efficient precursors of proplatelets (Bock). The occurrence of a nystagmus has been subsequently diagnosed in humans bearing a AhR mutation (Borovok).
In human cancer, the AhR has either a pro or con tumor effect depending on the tissue, the ligand, and the duration of the activation (Zudaire, Chang, Litzenburg, Gramatzki, Lin, Wang). In human breast cancer, the AhR is thoughts to be responsible of its progression (Goode, Kanno, Optiz, Novikov, Hall, Subramaniam, Barhoover). In human mammary benign cells, Brooks et al. noted that a high level of AhR was associated with a modified cell cycle (with a 50% increase in population doubling time in cells expressing the AhR by more than 3-fold) and EMT including increased cell migration. Narasimnhan et al. found that suppression of the AhR pathway had a pro-tumorigenic effect in vitro (EMT, tumor migration) in triple negative breast cancer.
Many endogenous and exogenous ligands are present for the AhR in human (Optiz, Adachi, Schroeder, Rothhammer). Indoles, such as indole-3-carbinol or one of its secondary metabolites, 3-3'- Diindolylmethane, are degradation products found in cruciferous vegetables and characterized as AhR ligands (Ema, Kall, Miller) they are also inducers of the human and rat CYP1A1 (Optiz). FICZ is the most potent AhR ligand known to date: it has a stronger affinity than TCDD for the human AhR (TCDD Kd=0.48 nM/FICZ Kd=0.07 nM) (Coumoul).
Key Event Description
The AHR Receptor
The aryl hydrocarbon receptor (AHR) is a ligand-activated transcription factor that belongs to the basic helix-loop-helix Per-ARNT-Sim (bHLH-PAS) superfamily and consists of three domains: the DNA-binding domain (DBD), ligand binding domain (LBD) and transactivation domain (TAD)[1]. Other members of this superfamily include the AHR nuclear translocator (ARNT), which acts as a dimerization partner of the AHR [2][3]; Per, a circadian transcription factor; and Sim, the “single-minded” protein involved in neuronal development [4][5]. This group of proteins shares a highly conserved PAS domain and is involved in the detection of and adaptation to environmental change[4].
Investigations of invertebrates possessing early homologs of the AhR suggest that the AhR evolutionarily functioned in regulation of the cell cycle, cellular proliferation and differentiation, and cell-to-cell communications (Hahn et al 2002). However, critical functions in angiogenesis, regulation of the immune system, neuronal processes, metabolism, development of the heart and other organ systems, and detoxification have emerged sometime in early vertebrate evolution (Duncan et al., 1998; Emmons et al., 1999; Lahvis and Bradfield, 1998).
The molecular Initiating Event
The molecular mechanism for AHR-mediated activation of gene expression is presented in Figure 1. In its unliganded form, the AHR is part of a cytosolic complex containing heat shock protein 90 (HSP90), the HSP90 co-chaperone p23 and AHR-interacting protein (AIP)[6]. Upon ligand binding, the AHR migrates to the nucleus where it dissociates from the cytosolic complex and forms a heterodimer with ARNT[7]. The AHR-ARNT complex then binds to a xenobiotic response element (XRE) found in the promoter of an AHR-regulated gene and recruits co-regulators such as CREB binding protein/p300, steroid receptor co-activator (SRC) 1, SRC-2, SRC-3 and nuclear receptor interacting protein 1, leading to induction or repression of gene expression[6]. Expression levels of several genes, including phase I (e.g. cytochrome P450 (CYP) 1A, CYP1B, CYP2A) and phase II enzymes (e.g. uridine diphosphate glucuronosyl transferase (UDP-GT), glutathione S-transferases (GSTs)), as well as genes involved in cell proliferation (transforming growth factor-beta, interleukin-1 beta), cell cycle regulation (p27, jun-B) and apoptosis (Bax), are regulated through this mechanism [6][8][7][9].
AHR Isoforms
- Over time the AhR has undergone gene duplication and diversification in vertebrates, which has resulted in multiple clades of AhR, namely AhR1, AhR2, and AhR3 (Hahn 2002).
- Fishes and birds express AhR1s and AhR2s, while mammals express a single AhR that is homologous to the AhR1 (Hahn 2002; Hahn et al 2006).
- The AhR3 is poorly understood and known only from some cartilaginous fishes (Hahn 2002).
- Little is known about diversity of AhRs in reptiles and amphibians (Hahn et al 2002).
- In some taxa, subsequent genome duplication events have further led to multiple isoforms of AhRs in some species, with up to four isoforms of the AhR (α, β, δ, γ) having been identified in Atlantic salmon (Salmo salar) (Hansson et al 2004).
- Although homologs of the AhR have been identified in some invertebrates, compared to vertebrates these AhRs have differences in binding of ligands in the species investigated to date (Hahn 2002; Hahn et al 1994).
Roles of isoforms in birds:
Two AHR isoforms (AHR1 and AHR2) have been identified in the black-footed albatross (Phoebastria nigripes), great cormorant (Phalacrocorax carbo) and domestic chicken (Gallus gallus domesticus)[10]. AHR1 mRNA levels were similar in the kidney, heart, lung, spleen, brain, gonad and intestine from the great cormorant but were lower in muscle and pancreas. AHR2 expression was mainly observed in the liver, but was also detected in gonad, brain and intestine. AHR1 levels represented a greater proportion (80%) of total AHR levels than AHR2 in the cormorant liver[10], and while both AHR isoforms bound to TCDD, AHR2 was less effective at inducing TCDD-dependent transactivation compared to AHR1 in black-footed albatross, great cormorant and domestic chicken[11][10].
- AhR1 and AhR2 both bind and are activated by TCDD in vitro (Yasui et al 2007).
- AhR1 has greater binding affinity and sensitivity to activation by TCDD relative to AhR2 (Yasui et al 2007).
- AhR1 is believed to mediate toxicities of DLCs, while AhR2 has no known role in toxicities (Farmahin et al 2012; Farmahin et al 2013; Manning et al 2012).
Roles of isoforms in fishes:
- AhR1 and AhR2 both bind and are activated by TCDD in vitro (Bak et al 2013; Doering et al 2014; 2015; Karchner et al 1999; 2005).
- AhR1 has greater sensitivity to activation by TCDD than AhR2 in red seabream (Pagrus major), white sturgeon (Acipenser transmontanus), and lake sturgeon (Acipenser fulvescens) (Bak et al 2013; Doering et al 2014; 2015)
- AhR2 has greater binding affinity or activation by TCDD than AhR1 in zebrafish (Danio rerio) and mummichog (Fundulus heteroclitus) (Karchner et al 1999; 2005).
- AhR2 is believed to mediate toxicities in fishes, while AhR1 has no known role in toxicities. Specifically, knockdown of AhR2 protects against toxicities of dioxin-like compounds (DLCs) and polycyclic aromatic hydrocarbons (PAHs) in zebrafish (Danio rerio) and mummichog (Fundulus heteroclitus), while knockdown of AhR1 offers no protection (Clark et al 2010; Prasch et al 2003; Van Tiem & Di Giulio 2011).
Roles of isoforms in amphibians and reptiles:
- Less is known about AhRs of amphibians or reptiles.
- AhR1 is believed to mediate toxicities in amphibians (Hahn 2002; Lavine et al 2005; Oka et al 2016; Shoots et al 2015). However, all AhRs of amphibians that have been investigated have very low affinity for TCDD (Hahn 2002; Lavine et al 2005; Oka et al 2016; Shoots et al 2015).
- Both AhR1s and AhR2 of American alligator (Alligator mississippiensis) are activated by agonists with comparable sensitivities (Oka et al 2016). AhRs of no other reptiles have been investigated.
How it is Measured or Detected
Methods that have been previously reviewed and approved by a recognized authority should be included in the Overview section above. All other methods, including those well established in the published literature, should be described here. Consider the following criteria when describing each method: 1. Is the assay fit for purpose? 2. Is the assay directly or indirectly (i.e. a surrogate) related to a key event relevant to the final adverse effect in question? 3. Is the assay repeatable? 4. Is the assay reproducible?
Transactivation Reporter Gene Assays (recommended approach)
Transient transfection transactivation
Transient transfection transactivation is the most common method for evaluating nuclear receptor activation[12]. Full-length AHR cDNAs are cloned into an expression vector along with a reporter gene construct (chimeric luciferase, P-lactamase or CAT reporter vectors containing the appropriate response elements for the gene of interest). There are a number of commercially available cell lines that can serve as recipients for these vectors (CV-1, HuH7, FLC-7, LS174T, LS180 MCF-7, HEC1, LLC-PK1, HEK293, HepG2, and Caco-2 cells)[12]. The greatest advantage of using transfected cells, rather than primary cell cultures, is the assurance that the nuclear receptor of interest is responsible for the observed induction. This would not be possible in a primary cell culture due to the co-regulation of different receptors for the same target genes. This model makes it easy to compare the responsiveness of the AHR across multiple species under the same conditions simply by switching out the AHR clone. One disadvantage to the transient transfection assay is the inherent variability associated with transfection efficiency, leading to a movement towards the use of stable cell lines containing the nuclear receptor and reporter gene linked to the appropriate response elements[12].
Luciferase reporter gene (LRG) assay
The described luciferase reporter gene (LRG) assays have been used to investigate activation of AhRs of:
- Humans (Homo sapiens) (Abnet et al 1999)
- Species of birds, namely chicken (Gallus gallus), ring-necked pheasant (Phasianus colchicus), Japanese quail (Coturnix japonica), and common tern (Sterna hirundo) (Farmahin et al 2012; Manning et al 2013), Mutant AhR1s with ligand binding domains resembling those of at least 86 avian species have also been investigated (Farmahin et al 2013). AhR2s of birds have only been investigated in black-footed albatross (Phoebastria nigripes) and common cormorant (Phalacrocorax carbo) (Yasio et al 2007).
- American alligator (Alligator mississippiensis) is the only reptile for which AhR activation has been investigated (Oka et al 2016), AhR1A, AhR1B, and AhR2 of American alligator were assayed (Oka et al 2016).
- AhR1 of two amphibians have been investigated, namely African clawed frog (Xenopus laevis) and salamander (Ambystoma mexicanum) (Lavine et al 2005; Shoots et al 2015; Ohi et al 2003),
- AhR1s and AhR2s of several species of fish have been investigated, namely Atlantic salmon (Salmo salar), Atlantic tomcod (Microgadus tomcod), white sturgeon (Acipenser transmontanus), rainbow trout (Onchorhynchys mykiss), red seabream (Pagrus major), lake sturgeon (Acipenser fulvescens), and zebrafish (Danio rerio) (Andreasen et al 2002; Abnet et al 1999; Bak et al 2013; Doering et al 2014; 2015; Evans et al 2005; Hansson & Hahn 2008; Karchner et al 1999; Tanguay et al 1999; Wirgin et al 2011).
For demonstrative purposes, a luciferase reporter gene assay used to measure AHR1-mediated transactivation for avian species is described here. However, comparable assays are utilized for investigating AHR1s and AHR2s of all taxa. A monkey kidney cell line (Cos-7) that has low endogenous AHR1 expression was transfected with the appropriate avian AHR1 clone, cormorant ARNT1, a CYP1A5 firefly luciferase reporter construct and a Renilla luciferase vector to control for transfection efficiency. After seeding, the cells were exposed to DLC and luciferase activity was measured using a luminometer. Luminescence, which is proportional to the extent of AHR activation, is expressed as the ratio of firefly luciferase units to Renilla luciferase units [13]. This particular assay was modified from its original version to increase throughput efficiency; (a) cells were seeded in 96-well plates rather than Petri dishes or 48- well plates, (b) DLCs were added directly to the wells without changing the cell culture medium, and (c) the same 96-well plates were used to measure luminescence without lysing the cells and transferring to another plate. Similar reporter gene assays have been used to measure AHR1 activation in domestic and wild species of birds, including the chicken, ring-necked pheasant (Phasianus colchicus), Japanese quail (Coturnix japonica), great cormorant, black-footed albatross and peregrine falcon (Falco peregrinus).[14][13][15][11][16][17]
Transactivation in stable cell lines
Stable cell lines have been developed and purified to the extent that each cell contains both the nuclear receptor and appropriate reporter vector, eliminating the variability associated with transfection [12]. A stable human cell line containing a luciferase reporter driven by multiple dioxin response elements has been developed that is useful in identifying AhR agonists and antagonists[18]. An added benefit of this model is the potential to multiplex 3 assays in a single well: receptor activation, cell viability and enzyme activity[12]. Such assays are used extensively in drug discovery due to their high throughput efficiency, and may serve just as useful for risk assessment purposes.
Ligand-Binding Assays
Ligand binding assays measure the ability of a test compound to compete with a labeled, high-affinity reference ligand for the LBD of a nuclear receptor. It is important to note that ligand binding does not necessitate receptor activation and therefore cannot distinguish between agonists and antagonists; however, binding affinities of AHR ligands are highly correlated with chemical potencies[19] and can explain differences in species sensitivities to DLCs[20][21][22]; they are therefore worth mentioning. Binding affinity and efficacy have been used to develop structure-activity relationships for AHR disruption[20][23] that are potentially useful in risk-assessment. There has been tremendous progress in the development of ligand-binding assays for nuclear receptors that use homogenous assay formats (no wash steps) allowing for the detection of low-affinity ligands, many of which do not require a radiolabel and are amenable to high throughput screening[24][12]. This author however was unable to find specific examples of such assays in the context of AHR binding and therefore some classic radioligand assays are described instead.
Hydroxyapatite (HAP) binding assay
The HAP binding assay makes use of an in vitro transcription/translation method to synthesize the AHR protein, which is then incubated with radiolabeled TDCPP and a HAP pellet. The occupied protein adsorbs to the HAP and the radioactivity is measured to determine saturation binding. An additional ligand can also be included in the mixture in order to determine its binding affinity relative to TCDD (competitive binding)[25][22]. This assay is simple, repeatable and reproducible; however, it is insensitive to weak ligand-receptor interactions[22][21][26].
Whole cell filtration binding assay
Dold and Greenlee[27] developed a method to detect specific binding of TCDD to whole mammalian cells in culture and was later modified by Farmahin et al.[21] for avian species. The cultured cells are incubated with radiolabeled TCDD with or without the presence of a competing ligand and filtered. The occupied protein adsorbs onto the filter and the radioactivity is measured to determine saturation binging and/or competitive binding. This assay is able to detect weak ligand-receptor interactions that are below the detection limit of the HAP assay[21].
Protein-DNA Interaction Assays
The active AHR complexed with ARNT can be measured using protein-DNA interaction assays. Two methods are described in detail by Perez-Romero and Imperiale[28]. Chromatin immunoprecipitation measures the interaction of proteins with specific genomic regions in vivo. It involves the treatment of cells with formaldehyde to crosslink neighboring protein-protein and protein-DNA molecules. Nuclear fractions are isolated, the genomic DNA is sheared, and nuclear lysates are used in immunoprecipitations with an antibody against the protein of interest. After reversal of the crosslinking, the associated DNA fragments are sequenced. Enrichment of specific DNA sequences represents regions on the genome that the protein of interest is associated with in vivo. Electrophoretic mobility shift assay (EMSA) provides a rapid method to study DNA-binding protein interactions in vitro. This relies on the fact that complexes of protein and DNA migrate through a nondenaturing polyacrylamide gel more slowly than free DNA fragments. The protein-DNA complex components are then identified with appropriate antibodies. The EMSA assay was found to be consistent with the LRG assay in chicken hepatoma cells dosed with dioxin-like compounds[29].
In silico Approaches
In silico homology modeling of the ligand binding domain of the AHR in combination with molecular docking simulations can provide valuable insight into the transactivation-potential of a diverse array of AHR ligands. Such models have been developed for multiple AHR isoforms and ligands (high/low affinity, endogenous and synthetic, agonists and antagonists), and can accurately predict ligand potency based on their structure and physicochemical properties (Bonati et al 2017; Hirano et al 2015; Sovadinova et al 2006).
References
- ↑ 1.0 1.1 Okey, A. B. (2007). An aryl hydrocarbon receptor odyssey to the shores of toxicology: the Deichmann Lecture, International Congress of Toxicology-XI. Toxicol.Sci. 98, 5-38.
- ↑ Hoffman, E. C., Reyes, H., Chu, F. F., Sander, F., Conley, L. H., Brooks, B. A., and Hankinson, O. (1991). Cloning of a factor required for activity of the Ah (dioxin) receptor. Science 252, 954-958.
- ↑ 3.0 3.1 Poland, A., Glover, E., and Kende, A. S. (1976). Stereospecific, high affinity binding of 2,3,7,8-tetrachlorodibenzo-p-dioxin by hepatic cytosol. Evidence that the binding species is receptor for induction of aryl hydrocarbon hydroxylase. J.Biol.Chem. 251, 4936-4946.
- ↑ 4.0 4.1 Gu, Y. Z., Hogenesch, J. B., and Bradfield, C. A. (2000). The PAS superfamily: sensors of environmental and developmental signals. Annu.Rev.Pharmacol.Toxicol. 40, 519-561.
- ↑ Kewley, R. J., Whitelaw, M. L., and Chapman-Smith, A. (2004). The mammalian basic helix-loop-helix/PAS family of transcriptional regulators. Int.J.Biochem.Cell Biol. 36, 189-204.
- ↑ 6.0 6.1 6.2 6.3 Fujii-Kuriyama, Y., and Kawajiri, K. (2010). Molecular mechanisms of the physiological functions of the aryl hydrocarbon (dioxin) receptor, a multifunctional regulator that senses and responds to environmental stimuli. Proc.Jpn.Acad.Ser.B Phys.Biol.Sci. 86, 40-53.
- ↑ 7.0 7.1 Mimura, J., and Fujii-Kuriyama, Y. (2003). Functional role of AhR in the expression of toxic effects by TCDD. Biochimica et Biophysica Acta - General Subjects 1619, 263-268.
- ↑ Giesy, J. P., Kannan, K., Blankenship, A. L., Jones, P. D., and Newsted, J. L. (2006). Toxicology of PCBs and related compounds. In Endocrine Disruption Biological Bases for Health Effects in Wildlife and Humans (D. O. Norris, and J. A. Carr, Eds.), pp. 245-331. Oxford University Press, New York.
- ↑ 9.0 9.1 9.2 Safe, S. (1994). Polychlorinated biphenyls (PCBs): Environmental impact, biochemical and toxic responses, and implications for risk assessment. Critical Reviews in Toxicology 24, 87-149.
- ↑ 10.0 10.1 10.2 Yasui, T., Kim, E. Y., Iwata, H., Franks, D. G., Karchner, S. I., Hahn, M. E., and Tanabe, S. (2007). Functional characterization and evolutionary history of two aryl hydrocarbon receptor isoforms (AhR1 and AhR2) from avian species. Toxicol.Sci. 99, 101-117.
- ↑ 11.0 11.1 Lee, J. S., Kim, E. Y., and Iwata, H. (2009). Dioxin activation of CYP1A5 promoter/enhancer regions from two avian species, common cormorant (Phalacrocorax carbo) and chicken (Gallus gallus): association with aryl hydrocarbon receptor 1 and 2 isoforms. Toxicol.Appl.Pharmacol. 234, 1-13.
- ↑ 12.0 12.1 12.2 12.3 12.4 12.5 Raucy, J. L., and Lasker, J. M. (2010). Current in vitro high throughput screening approaches to assess nuclear receptor activation. Curr. Drug Metab 11 (9), 806-814.
- ↑ 13.0 13.1 13.2 Farmahin, R., Wu, D., Crump, D., Hervé, J. C., Jones, S. P., Hahn, M. E., Karchner, S. I., Giesy, J. P., Bursian, S. J., Zwiernik, M. J., and Kennedy, S. W. (2012). Sequence and in vitro function of chicken, ring-necked pheasant, and Japanese quail AHR1 predict in vivo sensitivity to dioxins. Environ.Sci.Technol. 46, 2967-2975.
- ↑ 14.0 14.1 14.2 14.3 Farmahin, R., Manning, G. E., Crump, D., Wu, D., Mundy, L. J., Jones, S. P., Hahn, M. E., Karchner, S. I., Giesy, J. P., Bursian, S. J., Zwiernik, M. J., Fredricks, T. B., and Kennedy, S. W. (2013b). Amino acid sequence of the ligand binding domain of the aryl hydrocarbon receptor 1 (AHR1) predicts sensitivity of wild birds to effects of dioxin-like compounds. Toxicol.Sci. 131, 139-152.
- ↑ Fujisawa, N., Ikenaka, Y., Kim, E. Y., Lee, J. S., Iwata, H., and Ishizuka, M. (2012). Molecular evidence predicts aryl hydrocarbon receptor ligand insensitivity in the peregrine falcon (Falco peregrines). European Journal of Wildlife Research 58, 167-175.
- ↑ 16.0 16.1 16.2 Manning, G. E., Farmahin, R., Crump, D., Jones, S. P., Klein, J., Konstantinov, A., Potter, D., and Kennedy, S. W. (2012). A luciferase reporter gene assay and aryl hydrocarbon receptor 1 genotype predict the embryolethality of polychlorinated biphenyls in avian species. Toxicol.Appl.Pharmacol. 263, 390-399.
- ↑ Mol, T. L., Kim, E. Y., Ishibashi, H., and Iwata, H. (2012). In vitro transactivation potencies of black-footed albatross (Phoebastria nigripes) AHR1 and AHR2 by dioxins to predict CYP1A expression in the wild population. Environ.Sci.Technol. 46, 525-533.
- ↑ Yueh, M. F., Kawahara, M., and Raucy, J. (2005). Cell-based high-throughput bioassays to assess induction and inhibition of CYP1A enzymes. Toxicol. In Vitro 19 (2), 275-287.
- ↑ 19.0 19.1 Poland, A., and Knutson, J. C. (1982). 2,3,7,8-tetrachlorodibenzo-p-dioxin and related halogenated aromatic hydrocarbons: examination of the mechanism of toxicity. Annu. Rev. Pharmacol. Toxicol. 22, 517-554.
- ↑ 20.0 20.1 Hestermann, E. V., Stegeman, J. J., and Hahn, M. E. (2000). Relative contributions of affinity and intrinsic efficacy to aryl hydrocarbon receptor ligand potency. Toxicol. Appl. Pharmacol 168 (2), 160-172.
- ↑ 21.0 21.1 21.2 21.3 21.4 Farmahin, R., Jones, S. P., Crump, D., Hahn, M. E., Giesy, J. P., Zwiernik, M. J., Bursian, S. J., and Kennedy, S. W. (2014). Species-specific relative AHR1 binding affinities of 2,3,4,7,8-pentachlorodibenzofuran explain avian species differences in its relative potency. Comp Biochem. Physiol C. Toxicol. Pharmacol. 161C, 21-25.
- ↑ 22.0 22.1 22.2 22.3 22.4 22.5 22.6 Karchner, S. I., Franks, D. G., Kennedy, S. W., and Hahn, M. E. (2006). The molecular basis for differential dioxin sensitivity in birds: Role of the aryl hydrocarbon receptor. Proc. Natl. Acad. Sci. U. S. A 103 (16), 6252-6257.
- ↑ Lee, S., Shin, W. H., Hong, S., Kang, H., Jung, D., Yim, U. H., Shim, W. J., Khim, J. S., Seok, C., Giesy, J. P., and Choi, K. (2015). Measured and predicted affinities of binding and relative potencies to activate the AhR of PAHs and their alkylated analogues. Chemosphere 139, 23-29.
- ↑ Jones, S. A., Parks, D. J., and Kliewer, S. A. (2003). Cell-free ligand binding assays for nuclear receptors. Methods Enzymol. 364, 53-71.
- ↑ Gasiewicz, T. A., and Neal, R. A. (1982). The examination and quantitation of tissue cytosolic receptors for 2,3,7,8-tetrachlorodibenzo-p-dioxin using hydroxylapatite. Anal. Biochem. 124 (1), 1-11.
- ↑ Nakai, J. S., and Bunce, N. J. (1995). Characterization of the Ah receptor from human placental tissue. J Biochem. Toxicol. 10 (3), 151-159.
- ↑ Dold, K. M., and Greenlee, W. F. (1990). Filtration assay for quantitation of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) specific binding to whole cells in culture. Anal. Biochem. 184 (1), 67-73.
- ↑ Perez-Romero, P., and Imperiale, M. J. (2007). Assaying protein-DNA interactions in vivo and in vitro using chromatin immunoprecipitation and electrophoretic mobility shift assays. Methods Mol. Med. 131, 123-139.
- ↑ Heid, S. E., Walker, M. K., and Swanson, H. I. (2001). Correlation of cardiotoxicity mediated by halogenated aromatic hydrocarbons to aryl hydrocarbon receptor activation. Toxicol. Sci 61 (1), 187-196.
- ↑ 30.0 30.1 Ema, M., Ohe, N., Suzuki, M., Mimura, J., Sogawa, K., Ikawa, S., and Fujii-Kuriyama, Y. (1994). Dioxin binding activities of polymorphic forms of mouse and human arylhydrocarbon receptors. J.Biol.Chem. 269, 27337-27343.
- ↑ 31.0 31.1 Poland, A., Palen, D., and Glover, E. (1994). Analysis of the four alleles of the murine aryl hydrocarbon receptor. Mol.Pharmacol. 46, 915-921.
- ↑ Backlund, M., and Ingelman-Sundberg, M. (2004). Different structural requirements of the ligand binding domain of the aryl hydrocarbon receptor for high- and low-affinity ligand binding and receptor activation. Mol.Pharmacol. 65, 416-425.
- ↑ Murray, I. A., Reen, R. K., Leathery, N., Ramadoss, P., Bonati, L., Gonzalez, F. J., Peters, J. M., and Perdew, G. H. (2005). Evidence that ligand binding is a key determinant of Ah receptor-mediated transcriptional activity. Arch.Biochem.Biophys. 442, 59-71.
- ↑ Pandini, A., Denison, M. S., Song, Y., Soshilov, A. A., and Bonati, L. (2007). Structural and functional characterization of the aryl hydrocarbon receptor ligand binding domain by homology modeling and mutational analysis. Biochemistry 46, 696-708.
- ↑ 35.0 35.1 35.2 Pandini, A., Soshilov, A. A., Song, Y., Zhao, J., Bonati, L., and Denison, M. S. (2009). Detection of the TCDD binding-fingerprint within the Ah receptor ligand binding domain by structurally driven mutagenesis and functional analysis. Biochemistry 48, 5972-5983.
- ↑ Ramadoss, P., and Perdew, G. H. (2004). Use of 2-azido-3-[125I]iodo-7,8-dibromodibenzo-p-dioxin as a probe to determine the relative ligand affinity of human versus mouse aryl hydrocarbon receptor in cultured cells. Mol.Pharmacol. 66, 129-136.
- ↑ 37.0 37.1 37.2 Head, J. A., Hahn, M. E., and Kennedy, S. W. (2008). Key amino acids in the aryl hydrocarbon receptor predict dioxin sensitivity in avian species. Environ.Sci.Technol. 42, 7535-7541.
- ↑ 38.0 38.1 Denison, M. S., Soshilov, A. A., He, G., DeGroot, D. E., and Zhao, B. (2011). Exactly the same but different: promiscuity and diversity in the molecular mechanisms of action of the aryl hydrocarbon (dioxin) receptor. Toxicol.Sci. 124, 1-22.
- ↑ van den Berg, M., Birnbaum, L. S., Bosveld, A. T., Brunström, B., Cook, P., Feeley, M., Giesy, J. P., Hanberg, A., Hasegawa, R., Kennedy, S. W., Kubiak, T. J., Larsen, J. C., Van Leeuwen, F. X. R., Liem, A. K. D., Nolt, C., Peterson, R. E., Poellinger, L., Safe, S., Schrenk, D., Tillitt, D. E., Tysklind, M., Younes, M., Wærn, F., and Zacharewski, T. R. (1998). Toxic equivalency factors (TEFs) for PCBs, PCDDs, PCDFs for humans and wildlife. Environ.Health Perspect. 106, 775-792.
- ↑ Cohen-Barnhouse, A. M., Zwiernik, M. J., Link, J. E., Fitzgerald, S. D., Kennedy, S. W., Hervé, J. C., Giesy, J. P., Wiseman, S. B., Yang, Y., Jones, P. D., Wan, Y., Collins, B., Newsted, J. L., Kay, D. P., and Bursian, S. J. (2011b). Sensitivity of Japanese quail (Coturnix japonica), Common pheasant (Phasianus colchicus), and White Leghorn chicken (Gallus gallus domesticus) embryos to in ovo exposure to TCDD, PeCDF, and TCDF. Toxicol.Sci. 119, 93-103.
- ↑ Farmahin, R., Crump, D., Jones, S. P., Mundy, L. J., and Kennedy, S. W. (2013a). Cytochrome P4501A induction in primary cultures of embryonic European starling hepatocytes exposed to TCDD, PeCDF and TCDF. Ecotoxicology 22(4), 731-739.
- ↑ Hervé, J. C., Crump, D., Jones, S. P., Mundy, L. J., Giesy, J. P., Zwiernik, M. J., Bursian, S. J., Jones, P. D., Wiseman, S. B., Wan, Y., and Kennedy, S. W. (2010a). Cytochrome P4501A induction by 2,3,7,8-tetrachlorodibenzo-p-dioxin and two chlorinated dibenzofurans in primary hepatocyte cultures of three avian species. Toxicol. Sci. 113(2), 380-391.
- ↑ Hervé, J. C., Crump, D. L., McLaren, K. K., Giesy, J. P., Zwiernik, M. J., Bursian, S. J., and Kennedy, S. W. (2010b). 2,3,4,7,8-pentachlorodibenzofuran is a more potent cytochrome P4501A inducer than 2,3,7,8-tetrachlorodibenzo-p-dioxin in herring gull hepatocyte cultures. Environ. Toxicol. Chem. 29(9), 2088-2095.
- ↑ Poland, A., and Glover, E. (1973). Studies on the mechanism of toxicity of the chlorinated dibenzo-p-dioxins. Environ.Health Perspect. 5, 245-251.
- ↑ 45.0 45.1 McFarland, V. A., and Clarke, J. U. (1989). Environmental occurrence, abundance, and potential toxicity of polychlorinated biphenyl congeners: Considerations for a congener-specific analysis. Environ.Health Perspect. 81, 225-239.
- ↑ 46.0 46.1 Omiecinski, C. J., Vanden Heuvel, J. P., Perdew, G. H., and Peters, J. M. (2011). Xenobiotic metabolism, disposition, and regulation by receptors: from biochemical phenomenon to predictors of major toxicities. Toxicol.Sci. 120 Suppl 1, S49-S75.
- ↑ Swedenborg, E., and Pongratz, I. (2010). AhR and ARNT modulate ER signaling. Toxicology 268, 132-138.
- ↑ Diani-Moore, S., Ma, Y., Labitzke, E., Tao, H., David, W. J., Anderson, J., Chen, Q., Gross, S. S., and Rifkind, A. B. (2011). Discovery and biological characterization of 1-(1H-indol-3-yl)-9H-pyrido[3,4-b]indole as an aryl hydrocarbon receptor activator generated by photoactivation of tryptophan by sunlight. Chem. Biol. Interact. 193(2), 119-128.
- ↑ Wincent, E., Bengtsson, J., Mohammadi, B. A., Alsberg, T., Luecke, S., Rannug, U., and Rannug, A. (2012). Inhibition of cytochrome P4501-dependent clearance of the endogenous agonist FICZ as a mechanism for activation of the aryl hydrocarbon receptor. Proc. Natl. Acad. Sci. U. S. A 109(12), 4479-4484.
- ↑ Baba, T., Mimura, J., Nakamura, N., Harada, N., Yamamoto, M., Morohashi, K., and Fujii-Kuriyama, Y. (2005). Intrinsic function of the aryl hydrocarbon (dioxin) receptor as a key factor in female reproduction. Mol.Cell Biol. 25, 10040-10051.
- ↑ Fernandez-Salguero, P. M., Pineau, T., Hilbert, D. M., McPhail, T., Lee, S. S., Kimura, S., Nebert, D. W., Rudikoff, S., Ward, J. M., and Gonzalez, F. J. (1995). Immune system impairment and hepatic fibrosis in mice lacking the dioxin-binding Ah receptor. Science 268, 722-726.
- ↑ Ichihara, S., Yamada, Y., Ichihara, G., Nakajima, T., Li, P., Kondo, T., Gonzalez, F. J., and Murohara, T. (2007). A role for the aryl hydrocarbon receptor in regulation of ischemia-induced angiogenesis. Arterioscler.Thromb.Vasc.Biol. 27, 1297-1304.
- ↑ Lahvis, G. P., Lindell, S. L., Thomas, R. S., McCuskey, R. S., Murphy, C., Glover, E., Bentz, M., Southard, J., and Bradfield, C. A. (2000). Portosystemic shunting and persistent fetal vascular structures in aryl hydrocarbon receptor-deficient mice. Proc.Natl.Acad.Sci U.S.A 97, 10442-10447.
- ↑ Mimura, J., Yamashita, K., Nakamura, K., Morita, M., Takagi, T. N., Nakao, K., Ema, M., Sogawa, K., Yasuda, M., Katsuki, M., and Fujii-Kuriyama, Y. (1997). Loss of teratogenic response to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in mice lacking the Ah (dioxin) receptor. Genes Cells 2, 645-654.
- ↑ Schmidt, J. V., Su, G. H., Reddy, J. K., Simon, M. C., and Bradfield, C. A. (1996). Characterization of a murine Ahr null allele: involvement of the Ah receptor in hepatic growth and development. Proc.Natl.Acad.Sci U.S.A 93, 6731-6736.
- ↑ Thackaberry, E. A., Gabaldon, D. M., Walker, M. K., and Smith, S. M. (2002). Aryl hydrocarbon receptor null mice develop cardiac hypertrophy and increased hypoxia-inducible factor-1alpha in the absence of cardiac hypoxia. Cardiovasc.Toxicol. 2, 263-274.
- ↑ Zhang, N., Agbor, L. N., Scott, J. A., Zalobowski, T., Elased, K. M., Trujillo, A., Duke, M. S., Wolf, V., Walsh, M. T., Born, J. L., Felton, L. A., Wang, J., Wang, W., Kanagy, N. L., and Walker, M. K. (2010). An activated renin-angiotensin system maintains normal blood pressure in aryl hydrocarbon receptor heterozygous mice but not in null mice. Biochem.Pharmacol. 80, 197-2040.
Abnet, C.C.; Tanguay, R.L.; Heideman, W.; Peterson, R.E. 1999. Transactivation activity of human, zebrafish, and rainbow trout aryl hydrocarbon receptors expressed in COS-7 cells: Greater insight into species differences in toxic potency of polychlorinated dibenzo-p-dioxin, dibenzofuran, and biphenyl congeners. Toxicol. Appl. Pharmacol. 159, 41-51.
Andreasen, E.A.; Tanguay, R.L.; Peterson, R.E.; Heideman, W. 2002. Identification of a critical amino acid in the aryl hydrocarbon receptor. J. Biol. Chem. 277 (15), 13210-13218.
Bak, S.M.; Lida, M.; Hirano, M.; Iwata, H.; Kim, E.Y. 2013. Potencies of red seabream AHR1- and AHR2-mediated transactivation by dioxins: implications of both AHRs in dioxin toxicity. Environ. Sci. Technol. 47 (6), 2877-2885.
Clark, B.W.; Matson, C.W.; Jung, D.; Di Giulio, R.T. 2010. AHR2 mediates cardiac teratogenesis of polycyclic aromatic hydrocarbons and PCB-126 in Atlantic killifish (Fundulus heteroclitus). Aquat. Toxicol. 99, 232-240.
Doering, J.A.; Farmahin, R.; Wiseman, S.; Beitel, S.C.; Kennedy, S.W.; Giesy, J.P.; Hecker, M. 2015. Differences in activation of aryl hydrocarbon receptors of white sturgeon relative to lake sturgeon are predicted by identities of key amino acids in the ligand binding domain. Enviro. Sci. Technol. 49, 4681-4689.
Doering, J.A.; Farmahin, R.; Wiseman, S.; Kennedy, S.; Giesy J.P.; Hecker, M. 2014. Functionality of aryl hydrocarbon receptors (AhR1 and AhR2) of white sturgeon (Acipenser transmontanus) and implications for the risk assessment of dioxin-like compounds. Enviro. Sci. Technol. 48, 8219-8226.
Doering, J.A.; Giesy, J.P.; Wiseman, S.; Hecker, M. Predicting the sensitivity of fishes to dioxin-like compounds: possible role of the aryl hydrocarbon receptor (AhR) ligand binding domain. Environ. Sci. Pollut. Res. Int. 2013, 20(3), 1219-1224.
Doering, J.A.; Wiseman, S; Beitel, S.C.; Giesy, J.P.; Hecker, M. 2014. Identification and expression of aryl hydrocarbon receptors (AhR1 and AhR2) provide insight in an evolutionary context regarding sensitivity of white sturgeon (Acipenser transmontanus) to dioxin-like compounds. Aquat. Toxicol. 150, 27-35.
Duncan, D.M.; Burgess, E.A.; Duncan, I. 1998. Control of distal antennal identity and tarsal development in Drosophila by spineless-aristapedia, a homolog of the mammalian dioxin receptor. Genes Dev. 12, 1290-1303.
Eisner, B.K.; Doering, J.A.; Beitel, S.C.; Wiseman, S.; Raine, J.C.; Hecker, M. 2016. Cross-species comparison of relative potencies and relative sensitivities of fishes to dibenzo-p-dioxins, dibenzofurans, and polychlorinated biphenyls in vitro. Enviro. Toxicol. Chem. 35 (1), 173-181.
Emmons, R.B.; Duncan, D.; Estes, P.A.; Kiefel, P.; Mosher, J.T.; Sonnenfeld, M.; Ward, M.P.; Duncan, I.; Crews, S.T. 1999. The spineless-aristapedia and tango bHLH-PAS proteins interact to control antennal and tarsal development in Drosophila. Development. 126, 3937-3945.
Evans, B.R.; Karchner, S.I.; Franks, D.G.; Hahn, M.E. 2005. Duplicate aryl hydrocarbon receptor repressor genes (ahrr1 and ahrr2) in the zebrafish Danio rerio: structure, function, evolution, and AHR-dependent regulation in vivo. Arch. Biochem. Biophys. 441, 151-167.
Hahn, M.E. 2002. Aryl hydrocarbon receptors: diversity and evolution. Chemico-Biol. Interact. 141, 131-160.
Hahn, M.E.; Karchner, S.I.; Evans, B.R.; Franks, D.G.; Merson, R.R.; Lapseritis, J.M. 2006. Unexpected diversity of aryl hydrocarbon receptors in non-mammalian vertebrates: Insights from comparative genomics. J. Exp. Zool. A. Comp. Exp. Biol. 305, 693-706.
Hahn, M.E.; Poland, A.; Glover, E.; Stegeman, J.J. 1994. Photoaffinity labeling of the Ah receptor: phylogenetic survey of diverse vertebrate and invertebrate species. Arch. Biochem. Biophys. 310, 218-228.
Hansson, M.C.; Hahn, M.E. 2008. Functional properties of the four Atlantic salmon (Salmo salar) aryl hydrocarbon receptor type 2 (AHR2) isoforms. Aquat. Toxicol. 86, 121-130.
Hansson, M.C.; Wittzell, H.; Persson, K.; von Schantz, T. 2004. Unprecedented genomic diversity of AhR1 and AhR2 genes in Atlantic salmon (Salmo salar L.). Aquat. Toxicol. 68 (3), 219-232.
Karchner, S.I.; Franks, D.G.; Hahn, M.E. (2005). AHR1B, a new functional aryl hydrocarbon receptor in zebrafish: tandem arrangement of ahr1b and ahr2 genes. Biochem. J. 392 (1), 153-161.
Karchner, S.I.; Powell, W.H.; Hahn, M.E. 1999. Identification and functional characterization of two highly divergent aryl hydrocarbon receptors (AHR1 and AHR2) in the Teleost Fundulus heteroclitus. Evidence for a novel subfamily of ligand-binding basic helix loop helix-Per-ARNT-Sim (bHLH-PAS) factors. J. Biol. Chem. 274, 33814-33824.
Lahvis, G.P.; Bradfield, C.A. 1998. Ahr null alleles: distinctive or different? Biochem. Pharmacol. 56, 781-787.
Lavine, J.A.; Rowatt, A.J.; Klimova, T.; Whitington, A.J.; Dengler, E.; Beck, C.; Powell, W.H. 2005. Aryl hydrocarbon receptors in the frog Xenopus laevis: two AhR1 paralogs exhibit low affinity for 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD). Toxicol. Sci. 88 (1), 60-72.
Oka, K.; Kohno, S.; Ohta, Y.; Guillette, L.J.; Iguchi, T.; Katsu, Y. (2016). Molecular cloning and characterization of the aryl hydrocarbon receptors and aryl hydrocarbon receptor nuclear translocators in the American alligator. Gen. Comp. Endo. 238, 13-22.
Pongratz, I.; Mason, G.G.; Poellinger, L. Dual roles of the 90-kDa heat shock protein hsp90 in modulating functional activities of the dioxin receptor. Evidence that the dioxin receptor functionally belongs to a subclass of nuclear receptors which require hsp90 both for ligand binding activity and repression of intrinsic DNA binding activity. J. Biol. Chem. 1992, 267 (19), 13728-13734
Prasch, A.L.; Teraoka, H.; Carney, S.A.; Dong, W.; Hiraga, T.; Stegeman, J.J.; Heideman, W.; Peterson, R.E. 2003. Toxicol. Sci. Aryl hydrocarbon receptor 2 mediated 2,3,7,8-tetrachlorodibenzo-p-dioxin developmental toxicity in zebrafish. 76 (1), 138-150.
Shoots, J.; Fraccalvieri, D.; Franks, D.G.; Denison, M.S.; Hahn, M.E.; Bonati, L.; Powell, W.H. 2015. An aryl hydrocarbon receptor from the salamander Ambystoma mexicanum exhibits low sensitivity to 2,3,7,8-tetrachlorodibenzo-p-dioxin. Enviro. Sci. Technol. 49, 6993-7001.
Tanguay, R.L.; Abnet, C.C.; Heideman, W. Peterson, R.E. (1999). Cloning and characterization of the zebrafish (Danio rerio) aryl hydrocarbon receptor1. Biochimica et Biophysica Act 1444, 35-48.
Van den Berg, M.; Birnbaum, L.; Bosveld, A.T.C.; Brunstrom, B.; Cook, P.; Feeley, M.; Giesy, J.P.; Hanberg, A.; Hasegawa, R.; Kennedy, S.W.; Kubiak, T.; Larsen, J.C.; van Leeuwen, R.X.R.; Liem, A.K.D.; Nolt, C.; Peterson, R.E.; Poellinger, L.; Safe, S.; Schrenk, D.; Tillitt, D.; Tysklind, M.; Younes, M.; Waern, F.; Zacharewski, T. Toxic equivalency factors (TEFs) for PCBs, PCDDs, PECDFs for human and wildlife. Enviro. Hlth. Persp. 1998, 106, 775-792.
Van Tiem, L.A.; Di Giulio, R.T. 2011. AHR2 knockdown prevents PAH-mediated cardiac toxicity and XRE- and ARE-associated gene induction in zebrafish (Danio rerio). Toxicol. Appl. Pharmacol. 254 (3), 280-287.
Whitlock, J.P.; Okino, S.T.; Dong, L.Q.; Ko, H.S.P.; Clarke Katzenberg, R.; Qiang, M.; Li, W. 1996. Induction of cytochrome P4501A1: a model for analyzing mammalian gene transcription. Faseb. J. 10, 809-818.
Wirgin, I.; Roy, N.K.; Loftus, M.; Chambers, R.C.; Franks, D.G.; Hahn, M.E. 2011. Mechanistic basis of resistance to PCBs in Atlantic tomcod from the Hudson River. Science. 331, 1322-1324.
Yamauchi, M.; Kim, E.Y.; Iwata, H.; Shima, Y.; Tanabe, S. Toxic effects of 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in developing red seabream (Pagrus major) embryos: an association of morphological deformities with AHR1, AHR2 and CYP1A expressions. Aquat. Toxicol. 2006, 16, 166-179.
Yasui, T.; Kim, E.Y.; Iawata, H.; Franks, D.G.; Karchner, S.I.; Hahn, M.E.; Tanabe, S. 2007. Functional characterization and evolutionary history of two aryl hydrocarbon receptor isoforms (AhR1 and AhR2) from avian species. Toxicol. Sci. 99 (1), 101-117.
Bonati, L.; Corrada, D.; Tagliabue, S.G.; Motta, S. (2017) Molecular modeling of the AhR structure and interactions can shed light on ligand-dependent activation and transformation mechanisms. Current Opinion in Toxicology 2: 42-49. https://doi.org/10.1016/j.cotox.2017.01.011.
Sovadinová, I. , Bláha, L. , Janošek, J. , Hilscherová, K. , Giesy, J. P., Jones, P. D. and Holoubek, I. (2006), Cytotoxicity and aryl hydrocarbon receptor‐mediated activity of N‐heterocyclic polycyclic aromatic hydrocarbons: Structure‐activity relationships. Environmental Toxicology and Chemistry, 25: 1291-1297. doi:10.1897/05-388R.1
Wakx A, Nedder M, Tomkiewicz-Raulet C, Dalmasso J, Chissey A, et al. 2018. Expression,
Localization, and Activity of the Aryl Hydrocarbon Receptor in the Human Placenta. Int J Mol Sci. 19(12)
Ema M, Ohe N, Suzuki M, Mimura J, Sogawa K, et al. 1994. Dioxin binding activities of polymorphic forms of mouse and human arylhydrocarbon receptors.
Kall MA, Vang O, Clausen J. 1996. Effects of dietary broccoli on human in vivo drug metabolizing enzymes:
evaluation of caffeine, oestrone and chlorzoxazone metabolism. Carcinogenesis. 17(4):793–99
Miller CA. 1997. Expression of the human aryl hydrocarbon receptor complex in yeast. Activation of transcription by indole compounds. J. Biol. Chem. 272(52):32824–29
Opitz CA, Litzenburger UM, Sahm F, Ott M, Tritschler I, et al. 2011. An endogenous tumour promoting ligand of the human aryl hydrocarbon receptor. Nature. 478(7368):197–203
Adachi J, Mori Y, Matsui S, Takigami H, Fujino J, et al. 2001. Indirubin and indigo are potent aryl hydrocarbon receptor ligands present in human urine. J. Biol. Chem. 276(34):31475–78
Marinelli L, Martin-Gallausiaux C, Bourhis J-M, B.guet-Crespel F, Blotti.re HM, Lapaque N. 2019. Identification of the novel role of butyrate as AhR ligand in human intestinal epithelial cells. Sci
Rep. 9(1):643
Stobbe-Maicherski N, Wolff S, Wolff C, Abel J, Sydlik U, et al. 2013. The interleukin-6-type cytokine oncostatin M induces aryl hydrocarbon receptor expression in a STAT3-dependent manner in human HepG2 hepatoma cells. FEBS J. 280(24):6681–90
Kado S, Chang WLW, Chi AN, Wolny M, Shepherd DM, Vogel CFA. 2017. Aryl hydrocarbon receptor signaling modifies Toll-like receptor-regulated responses in human dendritic cells. Arch Toxicol. 91(5):2209–21
Bock KW. 2019. Human AHR functions in vascular tissue: Pro- and anti-inflammatory responses of AHR agonists in atherosclerosis. Biochem Pharmacol. 159:116–20
Schroeder JC, Dinatale BC, Murray IA, Flaveny CA, Liu Q, et al. 2010. The uremic toxin 3- indoxyl sulfate is a potent endogenous agonist for the human aryl hydrocarbon receptor. Biochemistry. 49(2):393–400
Watanabe I, Tatebe J, Namba S, Koizumi M, Yamazaki J, Morita T. 2013. Activation of aryl hydrocarbon receptor mediates indoxyl sulfate-induced monocyte chemoattractant protein-1 expression in human umbilical vein endothelial cells. Circ J. 77(1):224–30
Shackleford G, Sampathkumar NK, Hichor M, Weill L, Meffre D, et al. 2018. Involvement of Aryl hydrocarbon receptor in myelination and in human nerve sheath tumorigenesis. Proc Natl Acad Sci U S 115(6):E1319–28
Zudaire E, Cuesta N, Murty V, Woodson K, Adams L, et al. 2008. The aryl hydrocarbon receptor repressor is a putative tumor suppressor gene in multiple human cancers. J Clin Invest. 118(2):640–50
Goode GD, Ballard BR, Manning HC, Freeman ML, Kang Y, Eltom SE. 2013. Knockdown of aberrantly upregulated aryl hydrocarbon receptor reduces tumor growth and metastasis of MDA-MB- 231 human breast cancer cell line. Int J Cancer. 133(12):2769–80
Chang JT, Chang H, Chen P-H, Lin S-L, Lin P. 2007. Requirement of aryl hydrocarbon receptor overexpression for CYP1B1 up-regulation and cell growth in human lung adenocarcinomas. Clin Cancer
Res. 13(1):38–45
Kanno Y, Takane Y, Izawa T, Nakahama T, Inouye Y. 2006. The inhibitory effect of aryl hydrocarbon receptor repressor (AhRR) on the growth of human breast cancer MCF-7 cells. Biol Pharm Bull. 29(6):1254–57
Goode G, Pratap S, Eltom SE. 2014. Depletion of the aryl hydrocarbon receptor in MDA-MB- 231 human breast cancer cells altered the expression of genes in key regulatory pathways of cancer. PLoS One. 9(6):e100103
Opitz CA, Litzenburger UM, Sahm F, Ott M, Tritschler I, et al. 2011. An endogenous tumour promoting ligand of the human aryl hydrocarbon receptor. Nature. 478(7368):197–203
Novikov O, Wang Z, Stanford EA, Parks AJ, Ramirez-Cardenas A, et al. 2016. An Aryl Hydrocarbon Receptor-Mediated Amplification Loop That Enforces Cell Migration in ER-/PR-/Her2- Human Breast Cancer Cells. Mol Pharmacol. 90(5):674–88
Litzenburger UM, Opitz CA, Sahm F, Rauschenbach KJ, Trump S, et al. 2014. Constitutive IDO expression in human cancer is sustained by an autocrine signaling loop involving IL-6, STAT3 and the AHR. Oncotarget. 5(4):1038–51
Hall JM, Barhoover MA, Kazmin D, McDonnell DP, Greenlee WF, Thomas RS. 2010. Activation of the aryl-hydrocarbon receptor inhibits invasive and metastatic features of human breast cancer cells and promotes breast cancer cell differentiation. Mol Endocrinol. 24(2):359–69
Gramatzki D, Pantazis G, Schittenhelm J, Tabatabai G, K.hle C, et al. 2009. Aryl hydrocarbon receptor inhibition downregulates the TGF-beta/Smad pathway in human glioblastoma cells. Oncogene. 28(28):2593–2605
Subramaniam V, Ace O, Prud’homme GJ, Jothy S. 2011. Tranilast treatment decreases cell growth, migration and inhibits colony formation of human breast cancer cells. Exp Mol Pathol. 90(1):116–22
Rothhammer V, Borucki DM, Kenison JE, Hewson P, Wang Z, et al. 2018. Detection of aryl hydrocarbon receptor agonists in human samples. Sci Rep. 8(1):4970
Lin P, Chang H, Tsai W-T, Wu M-H, Liao Y-S, et al. 2003. Overexpression of aryl hydrocarbon receptor in human lung carcinomas. Toxicol Pathol. 31(1):22–30
Barhoover MA, Hall JM, Greenlee WF, Thomas RS. 2010. Aryl hydrocarbon receptor regulates cell cycle progression in human breast cancer cells via a functional interaction with cyclin-dependent kinase 4. Mol Pharmacol. 77(2):195–201
Wang K, Li Y, Jiang Y-Z, Dai C-F, Patankar MS, et al. 2013. An endogenous aryl hydrocarbon receptor ligand inhibits proliferation and migration of human ovarian cancer cells. Cancer Lett. 340(1):63–71
Borovok N, Weiss C, Sharkia R, Reichenstein M, Wissinger B, et al. 2020. Gene and Protein Expression in Subjects With a Nystagmus-Associated AHR Mutation. Front Genet. 11:582796
List of Key Events in the AOP
Event: 80: Up Regulation, CYP1A1
Short Name: Up Regulation, CYP1A1
Key Event Component
| Process | Object | Action |
|---|---|---|
| gene expression | cytochrome P450 1A1 | increased |
AOPs Including This Key Event
| AOP ID and Name | Event Type |
|---|---|
| Aop:57 - AhR activation leading to hepatic steatosis | KeyEvent |
| Aop:494 - AhR activation leading to liver fibrosis | KeyEvent |
Biological Context
| Level of Biological Organization |
|---|
| Molecular |
Cell term
| Cell term |
|---|
| hepatocyte |
Domain of Applicability
Taxonomic Applicability| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| Acipenser transmontanus | Acipenser transmontanus | High | NCBI |
| Oncorhynchus mykiss | Oncorhynchus mykiss | High | NCBI |
Event: 1364: Increase, Reactive oxygen species
Short Name: Increase, ROS
AOPs Including This Key Event
| AOP ID and Name | Event Type |
|---|---|
| Aop:325 - Thermal stress leading to population decline (2) | KeyEvent |
| Aop:396 - Deposition of ionizing energy leads to population decline via impaired meiosis | KeyEvent |
| Aop:481 - AOPs of amorphous silica nanoparticles: ROS-mediated oxidative stress increased respiratory dysfunction and diseases. | MolecularInitiatingEvent |
| Aop:494 - AhR activation leading to liver fibrosis | KeyEvent |
Biological Context
| Level of Biological Organization |
|---|
| Molecular |
Event: 55: Increase, Cell injury/death
Short Name: Cell injury/death
Key Event Component
| Process | Object | Action |
|---|---|---|
| cell death | increased |
AOPs Including This Key Event
Biological Context
| Level of Biological Organization |
|---|
| Cellular |
Cell term
| Cell term |
|---|
| eukaryotic cell |
Domain of Applicability
Taxonomic Applicability| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| human | Homo sapiens | High | NCBI |
| human and other cells in culture | human and other cells in culture | High | NCBI |
| Rattus norvegicus | Rattus norvegicus | High | NCBI |
| mouse | Mus musculus | High | NCBI |
| Life Stage | Evidence |
|---|---|
| All life stages |
| Sex | Evidence |
|---|---|
| Unspecific |
Cell death is an universal event occurring in cells of any species (Fink and Cookson,2005).
Key Event Description
Two types of cell death can be distinguished by morphological features, although it is likely that these are two ends of a spectrum with possible intermediate forms. Apoptosis involves shrinkage, nuclear disassembly, and fragmentation of the cell into discrete bodies with intact plasma membranes. These are rapidly phagocytosed by neighbouring cells. An important feature of apoptosis is the requirement for adenosine triphosphate (ATP) to initiate the execution phase. In contrast, necrotic cell death is characterized by cell swelling and lysis. This is usually a consequence of profound loss of mitochondrial function and resultant ATP depletion, leading to loss of ion homeostasis, including volume regulation, and increased intracellular Ca2+. The latter activates a number of nonspecific hydrolases (i.e., proteases, nucleases, and phospholipases) as well as calcium dependent kinases. Activation of calpain I, the Ca2+-dependent cysteine protease cleaves the death-promoting Bcl-2 family members Bid and Bax which translocate to mitochondrial membranes, resulting in release of truncated apoptosis-inducing factor (tAIF), cytochrome c and endonuclease in the case of Bid and cytocrome c in the case of Bax. tAIF translocates to cell nuclei, and together with cyclophilin A and phosphorylated histone H2AX (γH2AX) is responsible for DNA cleavage, a feature of programmed necrosis. Activated calpain I has also been shown to cleave the plasma membrane Na+–Ca2+ exchanger, which leads to build-up of intracellular Ca2+, which is the source of additional increased intracellular Ca2+. Cytochrome c in cellular apoptosis is a component of the apoptosome.
DNA damage activates nuclear poly(ADP-ribose) polymerase-1(PARP-1), a DNA repair enzyme. PARP-1 forms poly(ADP-ribose) polymers, to repair DNA, but when DNA damage is extensive, PAR accumulates, exits cell nuclei and travels to mitochondrial membranes, where it, like calpain I, is involved in AIF release from mitochondria. A fundamental distinction between necrosis and apoptosis is the loss of plasma membrane integrity; this is integral to the former but not the latter. As a consequence, lytic release of cellular constituents promotes a local inflammatory reaction, whereas the rapid removal of apoptotic bodies minimizes such a reaction. The distinction between the two modes of death is easily accomplished in vitro but not in vivo. Thus, although claims that certain drugs induce apoptosis have been made, these are relatively unconvincing. DNA fragmentation can occur in necrosis, leading to positive TUNEL staining (see explanation below). Conversely, when apoptosis is massive, it can exceed the capacity for rapid phagocytosis, resulting in the eventual appearance of secondary necrosis.
Two alternative pathways - either extrinsic (receptor-mediated) or intrinsic (mitochondria-mediated) - lead to apoptotic cell death. The initiation of cell death begins either at the plasma membrane with the binding of TNF or FasL to their cognate receptors or within the cell. The latter is due to the occurrence of intracellular stress in the form of biochemical events such as oxidative stress, redox changes, covalent binding, lipid peroxidation, and consequent functional effects on mitochondria, endoplasmic reticulum, microtubules, cytoskeleton, or DNA. The intrinsic mitochondrial pathway involves the initiator, caspase-9, which, when activated, forms an “apoptosome” in the cytosol, together with cytochrome c, which translocates from mitochondria, Apaf-1 and dATP. The apoptosome activates caspase-3, the central effector caspase, which in turn activates downstream factors that are responsible for the apoptotic death of a cell (Fujikawa, 2015). Intracellular stress either directly affects mitochondria or can lead to effects on other organelles, which then send signals to the mitochondria to recruit participation in the death process (Fujikawa, 2015; Malhi et al., 2010). Constitutively expressed nitric oxide synthase (nNOS) is a Ca2+-dependent cytosolic enzyme that forms nitric oxide (NO) from L-arginine, and NO reacts with the free radical such as superoxide (O2−) to form the very toxic free radical peroxynitrite (ONOO−). Free radicals such as ONOO−, O2 − and hydroxyl radical (OH−) damage cellular membranes and intracellular proteins, enzymes and DNA (Fujikawa, 2015; Malhi et al., 2010; Kaplowitz, 2002; Kroemer et al., 2009).
How it is Measured or Detected
Necrosis:
Lactate dehydrogenase (LDH) is a soluble cytoplasmic enzyme that is present in almost all cells and is released into extracellular space when the plasma membrane is damaged. To detect the leakage of LDH into cell culture medium, a tetrazolium salt is used in this assay. In the first step, LDH produces reduced nicotinamide adenine dinucleotide (NADH) when it catalyzes the oxidation of lactate to pyruvate. In the second step, a tetrazolium salt is converted to a colored formazan product using newly synthesized NADH in the presence of an electron acceptor. The amount of formazan product can be colorimetrically quantified by standard spectroscopy. Because of the linearity of the assay, it can be used to enumerate the percentage of necrotic cells in a sample (Chan et al., 2013).
The MTT assay is a colorimetric assay for assessing cell viability. NAD(P)H-dependent cellular oxidoreductase enzymes may reflect the number of viable cells present. These enzymes are capable of reducing the tetrazolium dye MTT 3-(4,5-dimethylthiazol-2-yl)-2,5-diphenyltetrazolium bromide to its insoluble formazan, which has a purple color. Other closely related tetrazolium dyes include XTT, MTS and the WSTs. Tetrazolium dye assays can also be used to measure cytotoxicity (loss of viable cells) or cytostatic activity (shift from proliferation to quiescence) of potential medicinal agents and toxic materials. MTT assays are usually done in the dark since the MTT reagent is sensitive to light (Berridgeet al.,2005).
Propidium iodide (PI) is an intercalating agent and a fluorescent molecule used to stain necrotic cells. It is cell membrane impermeant so it stains only those cells where the cell membrane is destroyed. When PI is bound to nucleic acids, the fluorescence excitation maximum is 535 nm and the emission maximum is 617 nm (Moore et al.,1998)
Alamar Blue (resazurin) is a fluorescent dye. The oxidized blue non fluorescent Alamar blue is reduced to a pink fluorescent dye in the medium by cell activity (O'Brien et al., 2000) (12).
Neutral red uptake, which is based on the ability of viable cells to incorporate and bind the supravital dye neutral red in lysosomes (Repetto et al., 2008)(13). Moreover, quantification of ATP, signaling the presence of metabolically active cells, can be performed (CellTiter-Glo; Promega).
ATP assay: Quantification of ATP, signaling the presence of metabolically active cells (CellTiter-Glo; Promega).
Apoptosis:
TUNEL is a common method for detecting DNA fragmentation that results from apoptotic signalling cascades. The assay relies on the presence of nicks in the DNA which can be identified by terminal deoxynucleotidyl transferase or TdT, an enzyme that will catalyze the addition of dUTPs that are secondarily labeled with a marker. It may also label cells that have suffered severe DNA damage.
Caspase activity assays measured by fluorescence. During apoptosis, mainly caspase-3 and -7 cleave PARP to yield an 85 kDa and a 25 kDa fragment. PARP cleavage is considered to be one of the classical characteristics of apoptosis. Antibodies to the 85 kDa fragment of cleaved PARP or to caspase-3 both serve as markers for apoptotic cells that can be monitored using immunofluorescence (Li, Peng et al., 2004).
Hoechst 33342 staining: Hoechst dyes are cell-permeable and bind to DNA in live or fixed cells. Therefore, these stains are often called supravital, which means that cells survive a treatment with these compounds. The stained, condensed or fragmented DNA is a marker of apoptosis (Loo, 2002; Kubbies and Rabinovitch, 1983).
Acridine Orange/Ethidium Bromide staining is used to visualize nuclear changes and apoptotic body formation that are characteristic of apoptosis. Cells are viewed under a fluorescence microscope and counted to quantify apoptosis.
References
- Fujikawa, D.G. (2015), The role of excitotoxic programmed necrosis in acute brain injury, Comput Struct Biotechnol J, vol. 13, pp. 212-221.
- Malhi, H. et al. (2010), Hepatocyte death: a clear and present danger, Physiol Rev, vol. 90, no. 3, pp. 1165-1194.
- Kaplowitz, N. (2002), Biochemical and Cellular Mechanisms of Toxic Liver Injury, Semin Liver Dis, vol. 22, no. 2, http://www.medscape.com/viewarticle/433631 (accessed on 20 January 2016).
- Kroemer, G. et al., (2009), Classification of cell death: recommendations of the Nomenclature Committee on Cell Death, Cell Death Differ, vol. 16, no. 1, pp. 3-11.
- Chan, F.K., K. Moriwaki and M.J. De Rosa (2013), Detection of necrosis by release of lactate dehydrogenase (LDH) activity, Methods Mol Biol, vol. 979, pp. 65–70.
- Berridge, M.V., P.M. Herst and A.S. Tan (2005), Tetrazolium dyes as tools in cell biology: new insights into their cellular reduction. Biotechnology Annual Review, vol. 11, pp 127-152.
- Moore, A, et al.(1998), Simultaneous measurement of cell cycle and apoptotic cell death,Methods Cell Biol, vol. 57, pp. 265–278.
- Li, Peng et al. (2004), Mitochondrial activation of apoptosis, Cell, vol. 116, no. 2 Suppl,pp. S57-59, 2 p following S59.
- Loo, D.T. (2002), TUNEL Assay an overview of techniques, Methods in Molecular Biology, vol. 203: In Situ Detection of DNA Damage, chapter 2, Didenko VV (ed.), Humana Press Inc.
- Kubbies, M. and P.S. Rabinovitch (1983), Flow cytometric analysis of factors which influence the BrdUrd-Hoechst quenching effect in cultivated human fibroblasts and lymphocytes, Cytometry, vol. 3, no. 4, pp. 276–281.
- Fink, S.L. and B.T. Cookson (2005), Apoptosis, pyroptosis, and necrosis: mechanistic description of dead and dying eukaryotic cells, Infect Immun, vol. 73, no. 4, pp.1907-1916.
- O'Brien J, Wilson I, Orton T, Pognan F. 2000. Investigation of the Alamar Blue (resazurin) fluorescent dye for the assessment of mammalian cell cytotoxicity. European journal of biochemistry / FEBS 267(17): 5421-5426.
- Repetto G, del Peso A, Zurita JL. 2008. Neutral red uptake assay for the estimation of cell viability/cytotoxicity. Nature protocols 3(7): 1125-1131.
Event: 459: Increased, Liver Steatosis
Short Name: Increased, Liver Steatosis
Key Event Component
| Process | Object | Action |
|---|---|---|
| Hepatic steatosis | increased |
AOPs Including This Key Event
Biological Context
| Level of Biological Organization |
|---|
| Organ |
Organ term
| Organ term |
|---|
| liver |
Domain of Applicability
Taxonomic Applicability| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| Vertebrates | Vertebrates | High | NCBI |
| Life Stage | Evidence |
|---|---|
| All life stages | High |
| Sex | Evidence |
|---|---|
| Unspecific | High |
Steatosis is the result of perturbations in well-known metabolic pathways that are well-studied and well-known in many taxa.
Life Stage: The life stage applicable to this key event is all life stages with a liver. Older individuals are more likely to manifest this adverse outcome pathway (adults > juveniles) due to accumulation of triglycerides.
Sex: This key event applies to both males and females.
Taxonomic: This key event appears to be present broadly in vertebrates, with most representative studies in mammals (humans, lab mice, lab rats).
Key Event Description
Biological state: liver steatosis is the inappropriate storage of fat in hepatocytes. Four major pathways for triglyceride accumulation are: 1. Increased fatty acid uptake; 2. Increased De Novo FA and Lipid Synthesis; 3. Decreased FA Oxidation; 4. Decreased Lipid Efflux (Angrish et al. 2016). Chemical stressors can increase gene expression of key genes involving these pathways, leading to increased accumulation of triglycerides (Aguayo-Orozco et al. 2018). In addition, excessive dietary compounds of fatty compounds can also increase likelihood of accumulation of triglycerides (Nguyen et al. 2008).
Biological compartment: steatosis is generally an organ-level diagnosis; however, the pathology occurs within the hepatocytes.
Role in biology: steatosis is an adverse endpoint.
Description from EU-ToxRisk:
Activation of stellate cells results in collagen accumulation and change in extracellular matrix composition in the liver causing fibrosis. (Landesmann, 2016; Koo et al 2016)
How it is Measured or Detected
Steatosis is measured by lipidomics approaches (e.g. Yang and Han 2016) that measure lipid levels, or by histology. Concentrations of triglycerides, cholesterols, fatty acids, and related compounds are measured biochemically include high throughput enzymatic analyses, analytical ultracentrifuging, gradient gel electrophoresis, Nuclear Magnetic Resonance, and other direct assessment techniques (Schaefer et al. 2016).
Regulatory Significance of the AO
Steatosis is a regulatory endpoint and has been used as an endpoint in many US EPA assessments, including IRIS assessments.
References
Aguayo-Orozco, A.A., Bois, F.Y., Brunak, S., and Taboureau, O. 2018. Analysis of Time-Series Gene Expression Data to Explore Mechanisms of Chemical-Induced Hepatic Steatosis Toxicity. Frontiers in Genetics 9(Article 396): 1-15.
Angrish, M.M., Kaiser, J.P., McQueen, C.A., and Chorley, B.N. 2016. Tipping the Balance: Hepatotoxicity and the 4 Apical Key Events of Hepatic Steatosis. Toxicological Sciences 150(2): 261–268.
Landesmann, B. (2016). Adverse Outcome Pathway on Protein Alkylation Leading to Liver Fibrosis, (2).
https://doi.org/10.1016/j.molcel.2005.08.010
Koo, J. H., Lee, H. J., Kim, W., & Kim, S. G. (2016). Endoplasmic Reticulum Stress in Hepatic Stellate Cells Promotes Liver Fibrosis via PERK-Mediated Degradation of HNRNPA1 and Up-regulation of SMAD2. Gastroenterology, 150(1), 181–193.e8. https://doi.org/10.1053/j.gastro.2015.09.039
Nguyen, P., Leray, V., Diez, M., Serisier, S., Le Bloc’h, J., Siliart, B., and Dumon, H. 2008. Liver lipid metabolism. Journal of Animal Physiology and Animal Nutrition 92: 272–283.
Schaefer EJ, Tsunoda F, Diffenderfer M, Polisecki, E., Thai, N., and Astalos, B. The Measurement of Lipids, Lipoproteins, Apolipoproteins, Fatty Acids, and Sterols, and Next Generation Sequencing for the Diagnosis and Treatment of Lipid Disorders. [Updated 2016 Mar 29]. In: Feingold KR, Anawalt B, Blackman MR, et al., editors. Endotext [Internet]. South Dartmouth (MA): MDText.com, Inc.; 2000-. Available from: https://www.ncbi.nlm.nih.gov/books/NBK355892/
Yang, K. and Han, X. 2016. Lipidomics: Techniques, applications, and outcomes related to biomedical sciences. Trends in Biochemical Sciences 2016 November ; 41(11): 954–969.
NOTE: Italics symbolize edits from John Frisch
Event: 265: Activation, Stellate cells
Short Name: Activation, Stellate cells
Key Event Component
| Process | Object | Action |
|---|---|---|
| hepatic stellate cell activation | hepatic stellate cell | increased |
AOPs Including This Key Event
| AOP ID and Name | Event Type |
|---|---|
| Aop:38 - Protein Alkylation leading to Liver Fibrosis | KeyEvent |
| Aop:144 - Endocytic lysosomal uptake leading to liver fibrosis | KeyEvent |
| Aop:494 - AhR activation leading to liver fibrosis | KeyEvent |
Biological Context
| Level of Biological Organization |
|---|
| Cellular |
Cell term
| Cell term |
|---|
| hepatic stellate cell |
Domain of Applicability
Taxonomic Applicability| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| human | Homo sapiens | High | NCBI |
| human and other cells in culture | human and other cells in culture | High | NCBI |
| Rattus norvegicus | Rattus norvegicus | High | NCBI |
| mouse | Mus musculus | High | NCBI |
| pigs | Sus scrofa | High | NCBI |
| Life Stage | Evidence |
|---|---|
| All life stages |
| Sex | Evidence |
|---|---|
| Unspecific |
Human: Friedman, 2008
Rat: George et al.,1999
Mouse: Chang et al., 2014
Pig: Costa et al., 2001
Key Event Description
Stellate cell activation means a transdifferentiation from a quiescent vitamin A–storing cell to a proliferative and contractile myofibroblast. Multiple cells and cytokines play a part in the regulation of hepatic stellate cell (HSC) activation that consists of discrete phenotype responses, mainly proliferation, contractility, fibrogenesis, matrix degradation, chemotaxis, and retinoid loss.
HSCs undergo activation through a two-phase process. The first step, the initiation phase, is triggered by injured hepatocytes, reactive oxygen speecies (ROS) and paracrine stimulation from neighbouring cell types (Kupffer cells (KCs), Liver sinusoidal endothelial cells (LSECs), and platelets) and make HSCs sensitized to activation by up-regulating various receptors. The perpetuation phase refers to the maintenance of HSC activation, which is a dynamic process including the secretion of autocrine and paracrine growth factors (such as TGF-β1), chemokines, and the up-regulation of collagen synthesis (mainly type I collagen). In response to growth factors (including Platelet-derived Growth Factor (PDGF) and Vascular Endothelial Growth Factor (VEGF)) HSCs proliferate. Increased contractility (Endothelin-1 and NO are the key opposing counter-regulators that control HSC contractility, in addition to angiotensinogen II, and others) leads to increased portal resistance. Driven by chemoattractants their accumulation in areas of injury is enhanced. TGF-β1 synthesis promotes activation of neighbouring quiescent hepatic stellate cells, whereas the release of HGF (hepatocyte growth factor) stimulates regeneration of adjacent hepatocytes. The release of chemoattractants (monocyte chemoattractant protein-1(MCP-1) and colony-stimulating factors (CSFs)) amplifies inflammation (Lee and Friedman; 2011; Friedman, 2010; 2008; 2000; Bataller and Brenner, 2005; ↑ Lotersztain et al., 2005; Poli, 2000). Activated HSCs (myofibroblasts) are the primary collagen producing cell, the key cellular mediators of fibrosis and a nexus for converging inflammatory pathways leading to fibrosis. Experimental inhibition of stellate cell activation prevents fibrosis (Li, Jing-Ting et al.,2008; George et al. (1999).
How it is Measured or Detected
Alpha-smooth muscle actin (α-SMA) is a well-known marker of hepatic stellate cells activation. Anti-alpha smooth muscle Actin [1A4] monoclonal antibody reacts with the alpha smooth muscle isoform of actin.
Gene expression profiling confirmed early changes for known genes related to HSC activation such as alpha smooth muscle actin (Acta2), lysyl oxidase (Lox) and collagen, type I, alpha 1 (Col1a1). Insulin-like growth factor binding protein 3 (Igfbp3) was identified as a gene strongly affected and as marker for culture-activated HSCs and plays a role in HSC migration (Morini et al., 2005; Mannaerts et al., 2013).
References
- Lee, U.E. and S.L. Friedman (2011), Mechanisms of Hepatic Fibrogenesis, Best Pract Res Clin Gastroenterol, vol. 25, no. 2, pp. 195-206.
- Friedman, S.L (2010), Evolving challenges in hepatic fibrosis, Nat. Rev. Gastroenterol. Hepatol, vol. 7, no. 8, pp. 425–436.
- Friedman, S.L. (2008), Mechanisms of Hepatic Fibrogenesis, Gastroenterology, vol. 134, no. 6, pp. 1655–1669.
- Friedman, S.L (2000), Molecular regulation of hepatic fibrosis, an integrated cellular response to tissue injury, J. Biol. Chem, vol. 275, no. 4, pp. 2247-2250.
- Bataller, R. and D.A. Brenner (2005), Liver Fibrosis, J.Clin. Invest, vol. 115, no. 2, pp. 209-218.
- Lotersztain, S. et al. (2005), Hepatic fibrosis: molecular mechanisms and drug targets, Annu. Rev. Pharmacol. Toxicol, vol. 45, pp. 605–628.
- Poli, G. (2000), Pathogenesis of liver fibrosis: role of oxidative stress, Mol Aspects Med, vol. 21, no. 3, pp. 49 – 98.
- Li, Jing-Ting et al. (2008), Molecular mechanism of hepatic stellate cell activation and antifibrotic therapeutic strategies, J Gastroenterol, vol. 43, no. 6, pp. 419–428.
- George, J. et al. (1999), In vivo inhibition of rat stellate cell activation by soluble transforming growth factor beta type II receptor: a potential new therapy for hepatic fibrosis. Proc Natl Acad Sci, vol. 96, no. 22, pp. 12719-12724.
- Morini, S. et al. (2005), GFAP expression in the liver as an early marker of stellate cells activation, Ital J Anat Embryol, vol. 110, no. 4, pp. 193-207.
- Mannaerts, I. et al. (2013), Gene expression profiling of early hepatic stellate cell activation reveals a role for Igfbp3 in cell migration, PLoS One, vol. 8, no.12, e84071.
- Chang et al., 2014, Isolation and culture of hepatic stellate cells from mouse liver. Acta Biochim Biophys Sin (Shanghai).;46(4):291-8.
- Costa et al., 2001, Early activation of hepatic stellate cells and perisinusoidal extracellular matrix changes during ex vivo pig liver perfusion. J Submicrosc Cytol Pathol.;33(3):231-40.
Event: 1494: Leukocyte recruitment/activation
Short Name: Leukocyte recruitment/activation
Key Event Component
| Process | Object | Action |
|---|---|---|
| cell activation involved in immune response | leukocyte | increased |
AOPs Including This Key Event
Biological Context
| Level of Biological Organization |
|---|
| Cellular |
Domain of Applicability
Taxonomic Applicability Life Stage Applicability| Life Stage | Evidence |
|---|---|
| All life stages |
| Sex | Evidence |
|---|---|
| Unspecific |
Key Event Description
The inflammatory response is the cornerstone of the body’s defense mechanism against bacterial and viral pathogens, as well as physical-, chemical- and environmental-mediated tissue and organ damage. Leucocyte recruitment at the site of pathogen evasion or sterile tissue injury is a critical adaptation for the preservation of tissue integrity. Neutrophils are the cell population that acutely responds to the alterations of inflammatory micro-environment. Neutrophil infiltration takes place within 6-8 hours from the initiation of the inflammatory process and is followed by the recruitment of other cell populations, like monocytes, lymphocytes, and eosinophils, which either promote or drive the resolution of inflammation. Leukocyte infiltration into sites of infection or sterile inflammation is a tightly regulated process that follows a sequence of adhesive events, termed as leukocyte adhesion cascade. One can broadly generalize that most leukocytes follow a similar multi-step cascade in the peripheral (non-lymphoid) vasculature with some exceptions. Accordingly, an updated adhesion cascade in postcapillary venules involves free-flowing leukocytes initial attachment or tethering and slow velocity rolling (step 1),stable adhesion (arrest) on endothelial cells (step 2), leukocyte flattening (step 3), and subsequent crawling on the vascular endothelium, transendothelial cell migration (TEM) between (paracellular route) or through (transcellular) the vascular endothelium (step 4), and uropod elongation to complete transmigration of postcapillary venules (step 5). The initial attachment and rolling steps are initiated by interactions of endothelial E- and P-selectins and their counterreceptors on leukocytes L-selectin (Leick et al., 2014).
Each of these steps is necessary for effective leukocyte recruitment; these steps are not phases of inflammation, but represent the sequence of events from the perspective of each leukocyte. At any given moment they all happen in parallel, involving different leukocytes in the same microvessels.
From the initial selectin-dependent leukocyte tethering to endothelial cells to the final migration of leukocytes into the sub-endothelium, this process depends on the interplay between leukocyte receptors and endothelial cell counter-receptors, as well as on the presence of endogenous inhibitors of leukocyte adhesion enabling the targeted recruitment of leukocytes to inflamed tissues.
To enable the infiltration of leukocytes at the site of inflammation, a series of alterations in endothelial cells and leukocytes takes place:
- regulation of the expression of adhesion molecules in leukocytes
- increased secretion of chemokines by endothelial cells
- increased expression of adhesion molecules in the luminal surface of endothelial cells
(Kourtzelis and Mitroulis, 2015) (Robbins and Cotran: Pathologic Basis of Disease 2010).
After recruitment, activation includes phenotype modification with morphologic alterations, changes in marker proteins (MHC, adhesion molecules, co-stimulatory signal), expression of mediators, enzymes, and pro-inflammatory proteins/lipids. Recruited monocytes recruited mature into macrophages with phagocytic activity and elaboration of a myriad of mediators of inflammation. The macrophage can replicate within tissues or die, including by apoptosis.
How it is Measured or Detected
in vivo imaging:
- Flow cytometry (FC/FACS),
- immunhistochemistry
- two photon-intravital microscopy (TP-IVM) (van Grinsven et al., 2017)
- Spinning Disk Confocal Microscopy-IVM (Jenne et al., 2011)
- Histology, increased cell numbers and altered composition
In vitro
- transwell Migration Assay (Justus et al., 2014)
- T-Lymphocyte & Innate Immune Cell Activation Assays
- Leukocyte Surface Markers (Monoclonal Antibodies to Leukocyte Surface Markers)
- Markers of leukocyte activation – protease release, ROS/RNS, NADPH oxidase (NOX), defense response - expression of anti-oxidants.
- organs-on-a-chip (Bnam et al., 2016; Ribas et al., 2017; Wufuer et al. 2016)
REFERENCES:
Benam KH, Villenave R, Lucchesi C, Varone 1, Hubeau C, Lee HH, Alves SE, Salmon M, Ferrante TC, Weaver JC, Bahinski A, Hamilton GA, Ingber DE., Small airway-on-a-chip enables analysis of human lung inflammation and drug responses in vitro, Nat Methods. 2016 Feb;13(2):151-7.
Ribas, J., Zhang, Y. S., Pitrez, P. R., Leijten, J., Miscuglio, M., Rouwkema, J., Dokmeci, M. R., Nissan, X., Ferreira, L. and Khademhosseini, A. (2017), Organ-On-A-Chip: Biomechanical Strain Exacerbates Inflammation on a Progeria-on-a-Chip Model doi:10.1002/smll.201770087
Wufuer M, Lee G, Hur W, Jeon B, Kim BJ, Choi TH, Lee SH, Skin-on-a-chip model simulating inflammation, edema and drug-based treatment, Nature Scientific Reports 6, Article number: 37471 (2016) doi:10.1038/srep37471
References
Kourtzelis I and Mitroulis I, Encyclopedia of Inflammatory Diseases, Leukocyte Recruitment, pp 1-9, Compendium of Inflammatory Diseases, Editors: Michael J. Parnham , Springer Basel, 2015, DOI 10.1007/978-3-0348-0620-6_177-1
Kumar, V.; Abbas, AK.; Fausto, N.; Aster, J. Robbins and Cotran: Pathologic Basis of Disease. 8. Elsevier; Philadelphia: 2010.
Leick M, Azcutia V, Newton G, Luscinskas FW., Leukocyte recruitment in inflammation: basic concepts and new mechanistic insights based on new models and microscopic imaging technologies, Cell Tissue Res. 2014 Mar;355(3):647-56
Nourshargh S, Alon R., Leukocyte migration into inflamed tissues., Immunity. 2014 Nov 20;41(5):694-707
Event: 1501: Increased, extracellular matrix deposition
Short Name: Increased extracellular matrix deposition
AOPs Including This Key Event
Biological Context
| Level of Biological Organization |
|---|
| Tissue |
Key Event Description
ECM is a macromolecular structure that provides physical support to tissues and is essential for organ function. The composition of ECM is tissue specific and consists mainly of fibrous proteins, glycoproteins, and proteoglycans. The ECM in lung is compartmentalised to basement membrane and the interstitial space. Fibroblasts found in the interstitial space are the main sources of ECM in lung (White, 2015). Altered composition of ECM is observed in several lung diseases of inflammatory origin in humans including chronic obstructive pulmonary disease, asthma and idiopathic lung fibrosis. The composition and architecture of the ECM determines 1) the open sites of attachment that are available to cells, 2) the mechanical properties of the ECM and 3) the mechanical loading (breathing) experienced by the cells. Thus, changes in the ECM composition during the exaggerated wound healing process determines if an organism commits to fibrotic process or completes the wound healing (Blaauboer et al., 2014).
Evidence for its perturbation in the context of pulmonary fibrosis:
In lung fibrosis, an exaggerated amount of ECM is distributed in the alveolar parenchyma in a non-heterogenous manner, leading to lower spirometry readings implying occlusion of alveolar regions and reduced gas exchange. Collagen 1 and Collagen III are suggested to be the main components of the ECM in the thickened alveolar septa in fibrosis with other constituents such as fibronectin, elastin and tenacin C (Zhang et al., 1994; Hinz, 2006; Kuhn & McDonald, 1991; Crabb et al., 2006; Bensadoun et al., 1996; Klingberg et al., 2012; McKleroy et al., 2013). It is suggested that ECM composition dramatically changes during the fibrotic process. The early fibrotic process is characterised by collagen III deposition and collagen 1 predominates the later stages of the fibrosis. Excessive collagen production by myofibroblasts is necessary for the development of fibrosis (scarred tissue), with established areas of scar formation containing almost exclusively Type I collagen (Bateman et al., 1981; McKleroy et al., 2013; Zhang et al., 1994). Studies have demonstrated that while total collagen increases in IPF, there is also a shift toward the less elastic type I collagen, which contributes to the stiffness of the scar tissue within the lung (Nimni, 1983; Rozin et al., 2005; McKleroy et al., 2013).
The fibrotic ECM contains characteristic accumulation of fibroblasts and myofibroblasts, which are the major contributors of ECM synthesised. The proliferation of fibroblasts and their differentiation into myofibroblasts is, in turn, guided by the composition and structure of the ECM. For example, studies have demonstrated that cytokines secreted in response to inflammation are capable of activating fibroblasts, and that these changes could cause alterations in the fibroblasts that lead to excessive proliferation and ECM deposition (Sivakumar et al., 2012; Wynn, 2011).
How it is Measured or Detected
qRT-PCR, Immunosorbant assays, and immunohistochemistry:
The qRT-PCR, ELISA, and immunohistochemistry are routinely used to assess the levels of protein and mRNA levels. The various genes and proteins that are assessed include, collagen I, collagen III, elastin and tenacin C. Histological staining with stains such as Masson Trichrome, Picro-sirius red are used to identify the tissue/cellular distribution of collagen, which can be quantified using morphometric analysis both in vivo and in vitro. The assays are routinely used and are quantitative.
Sircol Collagen Assay for collagen quantification:
The Serius dye has been used for many decades to detect collagen in histology samples. The Serius Red F3BA selectively binds to collagen and the signal can be read at 540 nm (Chen & Raghunath, 2009; Nikota et al., 2017).
Hydroxyproline assay:
Hydroxyproline is a non-proteinogenic amino acid formed by the prolyl-4-hydroxylase. Hydroxyproline is only found in collagen and thus, it serves as a direct measure of the amount of collagen present in cells or tissues. Colorimetric methods are readily available and have been extensively used to quantify collagen using this assay (Chen & Raghunath, 2009; Nikota et al., 2017).
Ex vivo and in vitro models of ECM deposition:
No models currently exist which allow for in vitro assessment of ECM deposition. Using single, or co-cultures containing fibroblasts, the production of soluble ECM components can be assessed after exposure to a stressor of interest using either ELISA or qRT-PCR experiments as a proxy.
References
1. Bateman, E., Turner-Warwick, M. and Adelmann-Grill, B. (1981). Immunohistochemical study of collagen types in human foetal lung and fibrotic lung disease. Thorax, 36(9), pp.645-653.
2. Bensadoun, E., Burke, A., Hogg, J. and Roberts, C. (1996). Proteoglycan deposition in pulmonary fibrosis. American Journal of Respiratory and Critical Care Medicine, 154(6), pp.1819-1828.
3. Blaauboer M et al. Extracellular matrix proteins: A positive feedback loop in lung fibrosis. Matrix Biology, 2014, 34, 170-178
4. Chen, C. and Raghunath, M. (2009). Focus on collagen: in vitro systems to study fibrogenesis and antifibrosis _ state of the art. Fibrogenesis & Tissue Repair, 2(1).
5. Crabb, R., Chau, E., Decoteau, D. and Hubel, A. (2006). Microstructural Characteristics of Extracellular Matrix Produced by Stromal Fibroblasts. Annals of Biomedical Engineering, 34(10), pp.1615-1627.
6. HINZ, B. (2006). Masters and servants of the force: The role of matrix adhesions in myofibroblast force perception and transmission. European Journal of Cell Biology, 85(3-4), pp.175-181.
7. Kuhn C, McDonald JA. The roles of the myofibroblast in idiopathic pulmonary fibrosis. Ultrastructural and immunohistochemical features of sites of active extracellular matrix synthesis. Am J Pathol. 1991;138(5):1257–1265.
8. Klingberg, F., Hinz, B. and White, E. (2012). The myofibroblast matrix: implications for tissue repair and fibrosis. The Journal of Pathology, 229(2), pp.298-309.
9. McKleroy, W., Lee, T. and Atabai, K. (2013). Always cleave up your mess: targeting collagen degradation to treat tissue fibrosis. American Journal of Physiology-Lung Cellular and Molecular Physiology, 304(11), pp.L709-L721.
10. Nikota, J., Banville, A., Goodwin, L., Wu, D., Williams, A., Yauk, C., Wallin, H., Vogel, U. and Halappanavar, S. (2017). Stat-6 signaling pathway and not Interleukin-1 mediates multi-walled carbon nanotube-induced lung fibrosis in mice: insights from an adverse outcome pathway framework. Particle and Fibre Toxicology, 14(1).
11. Nimni, M. (1983). Collagen: Structure, function, and metabolism in normal and fibrotic tissues. Seminars in Arthritis and Rheumatism, 13(1), pp.1-86.
12. Rozin, G., Gomes, M., Parra, E., Kairalla, R., de Carvalho, C. and Capelozzi, V. (2005). Collagen and elastic system in the remodelling process of major types of idiopathic interstitial pneumonias (IIP). Histopathology, 46(4), pp.413-421.
13. Sivakumar, P., Ntolios, P., Jenkins, G. and Laurent, G. (2012). Into the matrix. Current Opinion in Pulmonary Medicine, 18(5), pp.462-469.
14. White, E. (2015). Lung Extracellular Matrix and Fibroblast Function. Annals of the American Thoracic Society, 12(Supplement 1), pp.S30- S33.
15. Wynn, T. (2011). Integrating mechanisms of pulmonary fibrosis. The Journal of Experimental Medicine, 208(7), pp.1339-1350.
16. Zhang K, Rekhter MD, Gordon D, Phan SH. Myofibroblasts and their role in lung collagen gene expression during pulmonary fibrosis. A combined immunohistochemical and in situ hybridization study. Am J Pathol. 1994;145(1):114–125
List of Adverse Outcomes in this AOP
Event: 344: N/A, Liver fibrosis
Short Name: N/A, Liver fibrosis
Key Event Component
| Process | Object | Action |
|---|---|---|
| liver fibrosis | liver | occurrence |
AOPs Including This Key Event
| AOP ID and Name | Event Type |
|---|---|
| Aop:38 - Protein Alkylation leading to Liver Fibrosis | AdverseOutcome |
| Aop:144 - Endocytic lysosomal uptake leading to liver fibrosis | AdverseOutcome |
| Aop:383 - Inhibition of Angiotensin-converting enzyme 2 leading to liver fibrosis | AdverseOutcome |
| Aop:494 - AhR activation leading to liver fibrosis | AdverseOutcome |
Biological Context
| Level of Biological Organization |
|---|
| Organ |
Organ term
| Organ term |
|---|
| liver |
Domain of Applicability
Taxonomic Applicability| Term | Scientific Term | Evidence | Links |
|---|---|---|---|
| human | Homo sapiens | High | NCBI |
| Rattus norvegicus | Rattus norvegicus | High | NCBI |
| mouse | Mus musculus | High | NCBI |
| Life Stage | Evidence |
|---|---|
| All life stages |
| Sex | Evidence |
|---|---|
| Unspecific |
Human: Bataller and Brenner, 2005;Merck Manual, 2015; Blachier et al., 2013.
Rat, mouse: Liedtke et al., 2013
Key Event Description
Liver fibrosis results from perpetuation of the normal wound healing response, as a result of repeated cycles of hepatocyte injury and repair and is a dynamic process, characterised by an excessive deposition of ECM (extracellular matrix) proteins including glycoproteins, collagens, and proteoglycans. It is usually secondary to hepatic injury and inflammation, and progresses at different rates depending on the aetiology of liver disease and is also influenced by environmental and genetic factors. If fibrosis continues, it disrupts the normal architecture of the liver, altering the normal function of the organ and ultimately leading to liver damage. Cirrhosis represents the final stage of fibrosis. It is characterised by fibrous septa which divide the parenchyma into regenerative nodules which leads to vascular modifications and portal hypertension with its complications of variceal bleeding, hepatic encephalopathy, ascites, and hepatorenal syndrome. In addition, this condition is largely associated with hepatocellular carcinoma with a further increase in the relative mortality rate (Bataller and Brenner, 2005; Merck Manual,2015)
Liver fibrosis is an important health issue with clear regulatory relevance. The burden of disease attributable to liver fibrosis is quite high; progressive hepatic fibrosis, ultimately leading to cirrhosis, is a significant contributor to global health burden (Lim and Kim, 2008). In the European Union, 0.1 % of the population is affected by cirrhosis, the most advanced stage of liver fibrosis with full architectural disturbances (Blachier et al., 2013). Besides the epidemiological relevance, liver fibrosis also imposes a considerable economic burden on society. Indeed, the only curative therapy for chronic liver failure is liver transplantation. More than 5.500 orthotopic liver transplantations are currently performed in Europe on a yearly basis, costing up to €100.000 the first year and €10.000 yearly thereafter (Van Agthoven et al., 2001).
How it is Measured or Detected
Liver biopsy is an important part of the evaluation of patients with a variety of liver diseases. Besides establishing the diagnosis, the biopsy is often used to assess the severity of the disease. Until recently it has been assumed that fibrosis is an irreversible process, so most grading and staging systems have relatively few stages and are not very sensitive for describing changes in fibrosis. In all systems, the stages are determined by both the quantity and location of the fibrosis, with the formation of septa and nodules as major factors in the transition from one stage to the next. The absolute amount of fibrous tissue is variable within each stage, and there is considerable overlap between stages. Commonly used systems are the Knodell score with 4 stages - no fibrosis (score 0) to fibrous portal expansion (score 2) to bridging fibrosis (score 3) and Cirrhosis (score 4) – and the more sensitive Ishak fibrosis score with six stages - from no fibrosis (stage 0) over increasing fibrous expansion on portal areas (stages 1-2), bridging fibrosis (stages 3-4), and nodules (stage 5) to cirrhosis (stage 6) (Goodman, 2007). Liver biopsy is an invasive test with many possible complications and the potential for sampling error. Noninvasive tests become increasingly precise in identifying the amount of liver fibrosis through computer-assisted image analysis. Standard liver tests are of limited value in assessing the degree of fibrosis. Direct serologic markers of fibrosis include those associated with matrix deposition — e.g.procollagen type III amino-terminal peptide (P3NP), type I and IV collagens, laminin, hyaluronic acid, and chondrex. P3NP is the most widely studied marker of hepatic fibrosis. Other direct markers of fibrosis are those associated with matrix degradation, ie, matrix metalloproteinases 2 and 3 (MMP-2, MMP- 3) and tissue inhibitors of metalloproteinases 1 and 2 (TIMP-1, TIMP-2).These tests are not commercially available, and the components are not readily available in most clinical laboratories. Some indirect markers that combine several parameters are available but not very reliable. Conventional imaging studies (ultrasonography and computed tomography) are not sensitive for fibrosis. Hepatic elastography, a method for estimating liver stiffness, is a recent development in the noninvasive measurement of hepatic fibrosis. Currently, elastography can be accomplished by ultrasound or magnetic resonance. Liver biopsy is still needed if laboratory testing and imaging studies are inconclusive (Carey, 2010; Germani et al., 2011) .
Regulatory Significance of the AO
From the OECD - GUIDANCE DOCUMENT ON DEVELOPING AND ASSESSING ADVERSE OUTCOME PATHWAYS - Series on Testing and Assessment 18: "...an adverse effect that is of regulatory interest (e.g. repeated dose liver fibrosis)"
References
- Bataller, R. and D.A. Brenner (2005), Liver Fibrosis, J.Clin. Invest, vol. 115, no. 2, pp. 209-218.
- Merck Manual available at: http://www.merckmanuals.com/professional/hepatic_and_biliary_disorders/fibrosis_and_cirrhosis/hepatic_fibrosis.html,(accessed 10 February 2015).
- Lim, Y. and W. Kim (2008), The global impact of hepatic fibrosis and end-stage liver disease, Clin Liver Dis, vol. 12, no. 4, pp. 733-746.
- Blachier, M. et al. (2013), The burden of liver disease in Europe: a review of available epidemiological data, J Hepatol, vol. 58, no. 3, pp. 593-608.
- Van Agthoven, M. et al. (2001), A comparison of the costs and effects of liver transplantation for acute and for chronic liver failure. Transpl Int, vol. 14, no. 2, pp. 87-94.
- Goodman, Z.D. (2007), Grading and staging systems for inflammation and fibrosis in chronic liver diseases, Journal of Hepatology, vol. 47, no. 4, pp. 598-607.
- Carey, E. (2010), Noninvasive tests for liver disease, fibrosis, and cirrhosis: Is liver biopsy obsolete? Cleveland Clinic Journal of Medicine, vol. 77, no. 8, pp. 519-527.
- Germani, G. et al. (2011), Assessment of Fibrosis and Cirrhosis in Liver Biopsies, Semin Liver Dis, vol. 31, no. 1, pp. 82-90. available at http://www.medscape.com/viewarticle/743946_2,(accessed 10 February 2015).
- Liedtke, C. et al. (2013), Experimental liver fibrosis research: update on animal models, legal issues and translational aspects, Fibrogenesis Tissue Repair, vol. 6, no. 1, p. 19.
Appendix 2
List of Key Event Relationships in the AOP
List of Adjacent Key Event Relationships
Relationship: 19: Activation, AhR leads to Up Regulation, CYP1A1
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding |
|---|---|---|---|
| AhR activation leading to hepatic steatosis | adjacent | High | |
| AhR activation leading to liver fibrosis | adjacent | High | High |
Relationship: 2887: Up Regulation, CYP1A1 leads to Increase, ROS
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding |
|---|---|---|---|
| AhR activation leading to liver fibrosis | adjacent | High | High |
Relationship: 3219: Activation, AhR leads to Increased, Liver Steatosis
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding |
|---|---|---|---|
| AhR activation leading to liver fibrosis | adjacent | High | Moderate |
Relationship: 3218: Increased, Liver Steatosis leads to Cell injury/death
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding |
|---|---|---|---|
| AhR activation leading to liver fibrosis | adjacent | Moderate | Moderate |
Relationship: 68: Cell injury/death leads to Activation, Stellate cells
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding |
|---|---|---|---|
| Protein Alkylation leading to Liver Fibrosis | non-adjacent | High | |
| AhR activation leading to liver fibrosis | adjacent | Moderate | Moderate |
Evidence Supporting Applicability of this Relationship
Human: [7][18] Rat: [12] Mouse: [4]
Key Event Relationship Description
Damaged hepatocytes can lead to activation of hepatic stellate cells (HSCs) through the release of ROS, cytokines and chemokines. Engulfment of apoptotic bodies from hepatocytes results in HSC activation and induces NOX (NADPH oxidases) expression in HSCs. DNA from apoptotic hepatocytes induces toll-like receptor 9 (TLR9)-dependent changes of HSCs that are consistent with late stages of HSC differentiation (activation), with up-regulation of collagen production and inhibition of platelet derived growth factor (PDGF)-mediated chemotaxis to retain HSCs at sites of cellular apoptosis. The release of latent TGF-beta complex into the micro-environment by damaged hepatocytes is likely to be one of the first signals for adjacent HSCs leading to their activation.
[1] [2] [3] [4] [5] [6] [7] [8] [9] [10]
Damaged hepatocytes also influence liver sinusoidal endothelial cell (LSECs), which make an integral part of the hepatic reticulo-endothelial system and have a role in HSC activation. LSECs are morphologically identified by their fenestrations, which are transcytoplasmic canals arranged in sieve plates. In healthy liver, hepatocytes and HSCs maintain this phenotype of LSECs through release of vascular endothelial growth factor (VEGF). Differentiated (i.e. fenestrated) LSECs prevent HSC activation and promote reversal of activated HSC to quiescence, but LSEC lose this effect when they are de-differentiated due to liver injury. Preclinical studies have demonstrated that LSECs undergo defenestration as an early event that not only precedes liver fibrosis, but may also be permissive for it. Changes in LSEC differentiation might be an integral part of the development of fibrosis. Furthermore, in fibrosis LSECs become highly pro-inflammatory and secrete an array of cytokines and chemokines [11] [12] [13] [14] [15]
This relationship is classified as indirect as HSCs activation is partly mediated by TGF-β1 and LSECs.
Evidence Supporting this KER
Biological PlausibilityThere is a functional relationship between KE 1 and KE 4 consistent with established biological knowledge. [1] [2] [3] [4] [5] [6] [7] [8] [9] [10]
Empirical Evidence
There is temporal concordance as HSC activation follows hepatic injury and there is experimental evidence for this KER. Canbay et al. could show that Fas-mediated hepatocyte injury is mechanistically linked to liver fibrogenesis. Markers of HSC activation were significantly reduced when apoptosis was prevented in Fas-deficient bile duct ligated mice. These findings (reduction of inflammation, markers of HSC activation, and collagen I expression) could be repeated by pharmacological inhibition of liver cell apoptosis using a pan-caspase inhibitor. Coulouarn et al found in a co-culture model that hepatocyte - HSC crosstalk engenders a permissive inflammatory microenvironment. [16] [17] [18]
Uncertainties and InconsistenciesThere are no inconsistencies
References
- ↑ 1.0 1.1 Roth, S., K. Michel and A.M. Gressner (1998), (Latent) transforming growth factor beta in liver parenchymal cells, its injury-dependent release, and paracrine effects on rat HSCs, Hepatology, vol. 27, no. 4, pp. 1003-1012.
- ↑ 2.0 2.1 Gressner , A.M. et al. (2002), Roles of TGF-β in hepatic fibrosis. Front Biosci, vol. 7, pp. 793-807.
- ↑ 3.0 3.1 Malhi, H. et al. (2010), Hepatocyte death: a clear and present danger, Physiol Rev, vol. 90, no. 3, pp. 1165-1194.
- ↑ 4.0 4.1 4.2 Canbay, A., S.L. Friedman and G.J. Gores (2004), Apoptosis: the nexus of liver injury and fibrosis, Hepatology, vol. 39, no. 2, pp. 273-278.
- ↑ 5.0 5.1 Orrenius, S., P. Nicotera and B. Zhivotovsky (2011), Cell death mechanisms and their implications in toxicology, Toxicol. Sci, vol. 119, no. 1, pp. 3-19.
- ↑ 6.0 6.1 Kolios, G., V. Valatas and E. Kouroumalis (2006), Role of Kupffer cells in the pathogenesis of liver disease, World J.Gastroenterol, vol. 12, no. 46, pp. 7413-7420.
- ↑ 7.0 7.1 7.2 Kisseleva T and Brenner DA, (2008), Mechanisms of Fibrogenesis, Exp Biol Med, vol. 233, no. 2, pp. 109-122.
- ↑ 8.0 8.1 Li, Jing-Ting et al. (2008), Molecular mechanism of hepatic stellate cell activation and antifibrotic therapeutic strategies, J Gastroenterol, vol. 43, no. 6, pp. 419–428.
- ↑ 9.0 9.1 Friedman, S.L. (2008), Mechanisms of Hepatic Fibrogenesis, Gastroenterology, vol. 134, no. 6, pp. 1655–1669.
- ↑ 10.0 10.1 Lee, U.E. and S.L. Friedman (2011), Mechanisms of Hepatic Fibrogenesis, Best Pract Res Clin Gastroenterol, vol. 25, no. 2, pp. 195-206.
- ↑ DeLeve, L.D. (2013), Liver sinusoidal endothelial cells and liver regeneration, J Clin Invest, vol. 123, no. 5, pp. 1861–1866.
- ↑ 12.0 12.1 Xie, G. et al. (2012), Role of differentiation of liver sinusoidal endothelial cells in progression and regression of hepatic fibrosis in rats, Gastroenterology, vol. 142, no. 4, pp. 918–927.
- ↑ Xie, G. et al. (2013), Hedgehog signalling regulates liver sinusoidal endothelial cell capillarisation, Gut, vol. 62, no. 2, pp. 299–309.
- ↑ Ding, B.S. et al. (2014), Divergent angiocrine signals from vascular niche balance liver regeneration and fibrosis, Nature, vol. 505, no. 7481, pp. 97–102.
- ↑ Connolly, M.K. et al. (2010), In hepatic fibrosis, liver sinusoidal endothelial cells acquire enhanced immunogenicity, J Immunol, vol. 185, no. 4, pp. 2200-2208.
- ↑ Canbay, A. et al. (2002), Fas enhances fibrogenesis in the bile duct ligated mouse: a link between apoptosis and fibrosis, Gastroenterology, vol. 123, no. 4, pp. 1323-1330.
- ↑ Canbay, A. et al. (2004), The caspase inhibitor IDN-6556 attenuates hepatic injury and fibrosis in the bile duct ligated mouse, J Pharmacol Exp Ther, vol. 308, no. 3, pp. 1191-1196.
- ↑ 18.0 18.1 Coulouarn, C. et al. (2012), Hepatocyte-stellate cell cross-talk in the liver engenders a permissive inflammatory micro-environment that drives progression in hepatocellular carcinoma, Cancer Res, vol. 72, no. 10, pp. 2533–2542.
Relationship: 2890: Cell injury/death leads to Leukocyte recruitment/activation
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding |
|---|---|---|---|
| AhR activation leading to liver fibrosis | adjacent | Moderate | Moderate |
Relationship: 2891: Leukocyte recruitment/activation leads to Increased extracellular matrix deposition
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding |
|---|---|---|---|
| AhR activation leading to liver fibrosis | adjacent | Moderate | Moderate |
Relationship: 2892: Activation, Stellate cells leads to Increased extracellular matrix deposition
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding |
|---|---|---|---|
| AhR activation leading to liver fibrosis | adjacent | High | High |
Relationship: 2325: Increased extracellular matrix deposition leads to N/A, Liver fibrosis
AOPs Referencing Relationship
| AOP Name | Adjacency | Weight of Evidence | Quantitative Understanding |
|---|---|---|---|
| Inhibition of Angiotensin-converting enzyme 2 leading to liver fibrosis | adjacent | Moderate | Not Specified |
| AhR activation leading to liver fibrosis | adjacent | High | High |