Abstract
2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD), a persistent environmental contaminant, induces steatosis by increasing hepatic uptake of dietary and mobilized peripheral fats, inhibiting lipoprotein export, and repressing β-oxidation. In this study, the mechanism of β-oxidation inhibition was investigated by testing the hypothesis that TCDD dose-dependently repressed straight-chain fatty acid oxidation gene expression in mice following oral gavage every 4 days for 28 days. Untargeted metabolomic analysis revealed a dose-dependent decrease in hepatic acyl-CoA levels, while octenoyl-CoA and dicarboxylic acid levels increased. TCDD also dose-dependently repressed the hepatic gene expression associated with triacylglycerol and cholesterol ester hydrolysis, fatty acid binding proteins, fatty acid activation, and 3-ketoacyl-CoA thiolysis while inducing acyl-CoA hydrolysis. Moreover, octenoyl-CoA blocked the hydration of crotonyl-CoA suggesting short chain enoyl-CoA hydratase (ECHS1) activity was inhibited. Collectively, the integration of metabolomics and RNA-seq data suggested TCDD induced a futile cycle of fatty acid activation and acyl-CoA hydrolysis resulting in incomplete β-oxidation, and the accumulation octenoyl-CoA levels that inhibited the activity of short chain enoyl-CoA hydratase (ECHS1).
Subject terms: RNA sequencing, Lipids, Transcriptomics
Introduction
Although the liver is the largest internal organ, it is second to adipose tissue in regard to lipid storage capacity. Approximately 15–25% (fasted vs fed state, respectively) are derived from chylomicron remnants, 5–30% (fasted vs fed state, respectively) from de novo lipogenesis, and 5–30% from visceral fat tissues1. Under normal circumstances, lipid accumulation is coordinated by regulating uptake, utilization, and export (via very low-density lipoproteins [VLDL]) to ensure triacylglycerol (TAG) and cholesterol ester (CE) levels remain low. Excess fatty acids (FAs) are packaged into TAGs and CEs, not only for storage, but to reduce their potential lipotoxicity2,3. Chronic simple, reversible, fat accumulation, or steatosis, may progress to steatohepatitis with fibrosis, as in the case of non-alcoholic fatty liver disease (NAFLD). NAFLD impairs liver function and increases the risk for more complex metabolic diseases such as: metabolic syndrome (MetS), diabetes, cardiovascular disease and hepatocellular carcinoma (HCC). NAFLD alone is estimated to affect ≥ 35% of the U.S. population and has become the second leading reason for requiring a liver transplant4.
NAFLD development is described by a ‘multi-hit hypothesis’ in which consecutive insults collectively promote the progression of liver pathologies such as steatosis, inflammation and fibrosis5. Diverse pharmaceuticals and xenobiotics induce hepatic fat accumulation. For example, pesticides and solvents are the most frequently identified chemicals to induce hepatic steatosis while 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) and related compounds exhibit the greatest potency6,7. Previous studies have shown that male mice exhibit greater sensitivity to TCDD-elicited reductions in body weight gain compared to females, despite no change in daily food intake8–10. Hepatic micro- and macro-steatosis, immune cell infiltration, fibrosis, and bile duct proliferation (males only) were dose-dependently induced following oral gavage with TCDD every 4 days for 28 days11,12. Lipidomic analysis of hepatic steatosis induced by TCDD and related compounds reported marked increases in FAs, TAGs, phospholipids, and CEs13–15. Fat accumulation has been attributed to increased hepatic uptake of dietary and mobilized peripheral fats, inhibition of VLDL export, and repression of FA oxidation8,13,16,17. In humans, TCDD and related compounds are associated with altered lipid homeostasis, including steatosis with fibrosis and inflammation6,18–20. Epidemiological studies also report elevated serum TAG and cholesterol levels in exposed workers21,22. More recently, a study of second generation Seveso accident victims (age 2–39 years) suggested in utero TCDD exposure increased MetS risk in males23. These data suggest that environmental contaminants may play an underappreciated role in the development of NAFLD and its associated metabolic diseases24.
Most, if not all, of the effects of TCDD and related compounds are mediated by the aryl hydrocarbon receptor (AHR), a ligand-activated basic-helix-loop-helix Per-Arnt-Sim transcription factor. Mouse models deficient in AHR report no adverse effects following treatment with TCDD compared to wild-type animals25–27. Although numerous endogenous metabolites, drugs, xenobiotics, and natural products bind to the AHR, its endogenous ligand(s) and role(s) remain elusive28. Ligand binding to the cytosolic AHR causes dissociation of chaperone proteins, followed by translocation to the nucleus and heterodimerization with the aryl hydrocarbon receptor nuclear translocator (ARNT). In the canonical pathway, the AHR-ARNT complex interacts with dioxin response elements (DREs) within the promoter region of target genes, leading to recruitment of transcriptional co-regulators and differential gene expression29. Studies also report binding to non-consensus DREs and DRE-independent mechanisms of differential gene expression28,30. The dose-dependent species-, sex-, age-, tissue-, and cell-specific biochemical and toxicological responses are believed to be the result of aberrant differential gene expression mediated by the AHR28,31. Despite our detailed understanding of AHR-mediated gene regulation, links between TCDD-elicited differential expression and adverse biological effects have not been fully elucidated.
Though FAs can undergo α- and ω-oxidation, β-oxidation is the primary pathway for FA oxidation to produce ATP, as well as intermediates for macromolecular and ketone biosynthesis. Binding proteins, such as diazepam binding inhibitor (DBI; aka acyl-CoA binding protein), fatty acid binding proteins (FABPs), and sterol carrier protein 2 (SCP2), not only shunt FAs to acyl-CoA synthetases for activation, but also protect acyl-CoAs from hydrolysis, channel acyl-CoAs to specific pathways, and protect against free FA and acyl-CoA toxicity32–35. In β-oxidation, activated FAs are subjected to oxidation, hydration, a second oxidation, and finally coenzyme A (CoASH)-dependent thiolytic cleavage to complete the cycle, producing an acetyl-CoA and acyl-CoA that is two carbons shorter36. Peroxisomal and mitochondrial β-oxidation employ similar strategies but exhibit different substrate preferences and use different enzymes encoded by distinct genes. Mitochondrial β-oxidation prefers long, medium, and short chain FAs (LCFAs, MCFAs and SCFAs, respectively), while peroxisomes metabolize very long chain FAs (VLCFAs), LCFAs, bile acid precursor side chains, and dicarboxylic acids (DCAs) produced via ω-oxidation, as well as branched chain FAs following α-oxidation37. Under conditions of acyl-CoA accumulation that limits CoASH availability due to sequestration, cytosolic, peroxisomal, and mitochondrial thioesterases exert control by hydrolyzing β-oxidation substrates and end products, but not intermediates. This releases CoASH in order to support CoASH-dependent reactions in other pathways38.
Despite studies reporting β-oxidation inhibition by TCDD and related compounds in rodents, the mechanism remains uncertain. In this study, we examined straight chain FA oxidation to test the hypothesis that TCDD dose-dependently represses gene expression at key steps in β-oxidation. Notably, TCDD decreased hepatic acyl-CoA levels except for the marked dose-dependent increase in octenoyl-CoA and non-monotonic increases in DCAs, consistent with the inhibition of β-oxidation. TCDD repressed genes associated with lipid hydrolysis, FA binding proteins, FA activation, and thiolytic cleavage while inducing thioesterases. These results suggest TCDD induced a futile cycle of FA activation by acyl-CoA synthetases followed by thioesterase-mediated acyl-CoA hydrolysis resulting in incomplete β-oxidation and the accumulation of octenoyl-CoA.
Results
MS analysis of acyl-CoA species
Untargeted metabolomics identified dose-dependent decreases in hepatic acyl-CoAs following oral gavage every 4 days for 28 days (Table 1). Octanoyl-, hexanoyl-, butyryl- and acetyl-CoA were annotated based on parent ion mass, isotope similarity, and theoretical fragmentation. Scores > 40 had features matching parent ion mass and isotope distribution and MSE fragmentation data matching in silico mass fragmentation, while most metabolite scores averaged ~ 35 based on parent ion mass and isotope distribution metrics. The presence of 426.1 m/z and 408.0 m/z coenzyme A fragment ions observed in the MSE fragmentation mass spectra further confirmed the acyl-CoA identifications for octanoyl-, hexanoyl-, butyrl-, and acetyl-CoA39. Hepatic levels of hexanoyl-, butyryl-, and acetyl-CoA were repressed 34.9-, 11.8-, and 6.3-fold at 30 μg/kg TCDD, respectively. Other β-oxidation metabolites also exhibited dose-dependent decreases including butenoyl-CoA, 3-hydroxyhexanoyl-CoA and 3-hydroxybutanoyl-CoA, while octenoyl-CoA was dose-dependently induced 138.9-fold (Table 1, Supplementary Table 1). These dose-dependent decreases in FA oxidation intermediates are consistent with β-oxidation inhibition13,17.
Table 1.
Compound ID | Description | Cn | Score | Fold-Change (TCDD vs. Veh.) | ||||
---|---|---|---|---|---|---|---|---|
0.3 µg/kg | 1 µg/kg | 3 µg/kg | 10 µg/kg | 30 µg/kg | ||||
HMDB01070 | Octanoyl-CoA | 8 | 36.8 | 1.77 ± 0.63 | 0.04 ± 0.01 | 0.28 ± 0.04 | 0.06 ± 0.03 | 0.01 ± 0.01 |
HMDB02845 | Hexanoyl-CoA | 6 | 37.2 | 1.43 ± 0.47 | 0.08 ± 0.02* | 0.36 ± 0.05 | 0.08 ± 0.02 | 0.03 ± 0.02* |
HMDB01088 | Butyryl-CoA | 4 | 44.3 | 1.24 ± 0.33 | 0.17 ± 0.05* | 0.57 ± 0.10 | 0.09 ± 0.01* | 0.08 ± 0.04* |
HMDB01206 | Acetyl-CoA | 2 | 52.1 | 0.95 ± 0.12 | 0.30 ± 0.05* | 0.53 ± 0.07* | 0.04 ± 0.01* | 0.16 ± 0.06* |
HMDB03949 | Octenoyl-CoA | 8 | 34 | 1.66 ± 0.19 | 1.14 ± 0.23 | 26.16 ± 25.31 | 114.31 ± 4.89* | 139.82 ± 6.88* |
Acyl-CoA levels were assessed using untargeted liquid chromatography tandem mass spectrometry. Mice (n = 4–5) were orally gavaged every 4 days for 28 days with sesame oil vehicle or TCDD. Fold-changes were calculated for each treatment group relative to the vehicle control group. Bold font and asterisks (*) denote statistical significance (p ≤ 0.05) determined using a one-way ANOVA with a Dunnett’s post-hoc analysis. Scores were determined by Progenesis with 60 being the maximum value and 0 being the minimum value. Scores ranging from 30 to 40 are based on mass error and isotope distribution similarity, while score > 40 are based on mass error, isotope distribution and fragmentation score. All annotated compounds have a score distribution averaging ~ 35.
TAG and CE hydrolysis
Figure 1 summarizes the dose-dependent effects of TCDD on lipases, carboxylesterases, and a deacylase associated with TAG and CE hydrolysis. Note that because gene expression can vary significantly throughout the day due to circadian regulation, all fold-changes discussed in the text were derived from the circadian gene expression dataset to highlight the TCDD effects when controlled for diurnal rhythm (unless otherwise indicated). Despite similar trends, there may be fold-change discrepancies between the dose response and diurnal rhythmicity studies since the former study was not controlled for sample time collection.
Although TCDD induced gene expression of adipose triglyceride lipase (ATGL, Pnpla2) 4.3-fold, its paralog, Pnpla3, was repressed 37.7-fold. The requisite ATGL co-activator, CGI-58 (Abhydrolase Domain Containing 5, Abhd5) was also repressed 2.0-fold, as was G0s2 (10.9-fold), a potent ATGL inhibitor40. In addition, other ATGL regulators including Faf2 (-1.6-fold), Cidec (8.7-fold), Plin2 (2.6-fold) and Plin5 (-3.1-fold) exhibited differential expression41. Lysosomal lipase A (Lipa, 2.3-fold), which deacylates endocytosed low-density lipoprotein TAGs and CEs, was dose-dependently repressed. Similarly, hormone sensitive lipase (Lipe, 3.3-fold), and hepatic lipase C (Lipc, 12.0-fold), which deacylate extracellular low-density lipoprotein TAGs and CEs, were also dose-dependently repressed. Highly expressed carboxylesterases, which serve important roles in lipid metabolism and VLDL assembly42, exhibited dose-dependent repression with the exception of Ces1b. Specifically, highly expressed Ces2a, Ces2e, Ces3a, and Ces3b were repressed 56.3-, 4.0-, 1,923-, and 1,333-fold, respectively. Ces mRNA, protein and/or enzymatic activity repression by TCDD and related compounds in mice and rats has been previously reported43–45. Arylamide deacetylase (Aadac), another highly expressed gene associated with hepatic TAG metabolism40 was dose-dependently repressed 28.6-fold. Both CESs and AADAC are localized to the extracellular region or endoplasmic reticulum. Interestingly, ATGL and monoglyceride lipase (Mgll, 2.7-fold), which are primarily located in the nucleus, cytosol, and plasma membranes, were both induced. In addition to substrate preferences based on fatty acid composition and cellular location, hydrolyases channel released FAs to specific fates such as β-oxidation, membrane formation, VLDL assembly or PPAR activation40,42. Some lipases and carboxylesterases also exhibit cholesterol and retinyl ester hydrolysis activity.
The differential expression of genes associated with lipid hydrolysis was more pronounced at 28 days in mice treated with 30 μg/kg TCDD. Differential expression did not occur exclusively with genes exhibiting AHR enrichment. Although TCDD disrupted the diurnal rhythmicity of most lipid hydrolysis genes, this was not the case for highly expressed carboxylesterases which did not exhibit diurnal regulation. Ces genes are localized to a tandem cluster on chromosome 8 which may explain their collective repression by TCDD except for Ces1b42. Ces repression may also be due to the induction of proinflammatory cytokine signaling43. Overall, the effect of TCDD on gene expression suggests lipid hydrolysis was repressed. However, cellular lipase mRNA levels do not always correlate with enzyme activity due to extensive post-translational regulation46. Accordingly, hepatic levels of TAG, CEs, and bile acids were higher, as were free FAs suggesting esterification may be saturated13,15.
FA and acyl-CoA binding proteins
We next examined the effect of TCDD on binding proteins that are important for lipid uptake, intra-/extra-cellular trafficking, and cytoprotection (Fig. 2)34,35. In addition to channeling lipids to specific metabolic pathways, fatty acid binding proteins (FABPs), acyl-CoA binding protein (ACBP; aka diazepam binding inhibitor [DBI]), and sterol carrier protein 2 (SCP2) mitigate the toxicity, hydrolysis, and signaling potential of free acyl-CoAs. FABPs, DBI, and SCP2 also bind acyl-CoAs as well as other hydrophobic ligands including peroxisome proliferators, prostaglandins, bile acids, bilirubin, heme, fatty acid, and lipid metabolites. Highly expressed Fabp1, Dbi, and Scp2 encode for the majority of acyl-CoA buffering capacity and were repressed 5.9-, 7.1-, and 3.5-fold, respectively. Repression of the highly expressed DBI was consistent with gene expression patterns (Fig. 2E). Only Dbi exhibited an oscillating expression pattern that was abolished by TCDD (Fig. 2F). Despite AHR enrichment at 2 h in the presence of a putative DRE (pDRE), Fabp1, Dbi, and Scp2 exhibited minimal repression within 168 h of a single bolus gavage of 30 µg/kg TCDD. At 28 days, dose-dependent repression of Fabp1, Dbi, and Scp2 was observed with 10 and 30 µg/kg TCDD. Fabp2 and 5 were also repressed 4.5- and 1.9-fold, respectively. Despite the 6.6-, 14.0-, and 120.1-fold induction of Fabp4, 7, and 12, respectively, their induction would likely be insufficient to compensate for the loss of buffering capacity provided by FABP1, which showed expression levels ~ 125-fold higher than the other FABPs. FABP1, unlike other FABPs that only bind one FA, binds two FAs and accounts for 7–11% of the cytosolic protein in normal human liver34. Fabp1, 5, and 12 all had multiple AHR enrichment sites but only Fabp2 and 12 exhibited differential expression at 168 h. Acyl-CoA binding domain containing proteins 4 and 5 (Acbd4 and 5), which facilitate acyl-CoA transfer to peroxisomes, were also repressed 2.7- and 3.1-fold, respectively. Consequently, decreased binding protein levels may impair FA and acyl-CoA channeling to specific pathways while increasing the potential for toxicity, signaling, and membrane disruption, as well as acyl-CoA susceptibility to hydrolysis.
FA activation
Twenty-five mouse acyl-CoA synthetases (ACSs) catalyze the irreversible activation of FAs for β-oxidation or lipid biosynthesis. Each exhibits different tissue expression, subcellular locations, and substrate preferences while also channeling substrates to different pathways47. Twenty-two ACS genes were detected in the mouse liver including short- (Acss1-2; carbons length (C) 2–4), medium- (Acsm1-5; C6-10), long- (Acsl1, 3–6; C12-18), and very long- (Slc27a1-6; C12-30) members. Of the 17 abundantly expressed ACS genes, 15 were repressed including highly expressed (> 10,000 counts) Acsm1 (-12.5-fold), Acsl1 (-9.1-fold), Acsl5 (-5.6-fold), Slc27a2 (-5.9-fold), and Slc27a5 (-16.9-fold) following TCDD treatment (Fig. 3). In general, repression was dose-dependently observed within 168 h of a single bolus gavage of 30 µg/kg TCDD. Most ACS loci exhibited AHR enrichment in the presence of a pDRE at 2 h and exhibited disrupted diurnal expression. Although ACS mRNA levels poorly correlate with protein and enzyme activity48, TCDD-elicited gene repression was consistent with decreases in ACSM3 and ACSL1 protein levels (Fig. 3F,H). Collectively, these data point to ACS repression by TCDD being a direct target of AHR activation.
Mitochondrial and peroxisomal transport
While SCFAs and MCFAs passively enter mitochondria, LCFAs and VLCFAS must be transported into the mitochondria49. At the outer mitochondrial membrane, carnitine palmitoyltransferase I (Cpt1a; -2.7-fold) replaces CoASH in the activated FA with carnitine for transport of the acyl-carnitine (Fig. 4). Carnitine/acylcarnitine translocase (Slc25a20 aka CACT; -1.6-fold), transports acyl-carnitine species across the inner mitochondrial membrane into the matrix where carnitine palmitoyltransferase 2 (Cpt2; no change in gene expression) reactivates the acyl-carnitine into acyl-CoA in preparation for β-oxidation. Cpt1a and Slc25a20, which both possess pDREs, were also repressed within 168 h with evidence of AHR enrichment at 2 h.
ATP binding cassette subfamily member D (ABCD) 1 and 2, and to a lesser extent ABCD3, transport long- and very long-chain acyl-CoAs into peroxisomes50. ABCD1 (Abcd1), which prefers saturated and unsaturated 18-22C acyl-CoA substrates, and ABCD3 (Abcd3), with a preference for bile acid conjugated FAs51, were both repressed 2.2-fold (Fig. 4). Abcd1 and 3 exhibited negligible differential expression in the time course study despite AHR enrichment with pDREs. In contrast, Abcd2 showed disrupted oscillating expression in the time course and dose response studies. Although Abcd2 prefers C22:6- and C24:6-CoAs51, the level of very long unsaturated FAs in TAGs and CEs was increased by TCDD13.
Dehydrogenation of activated acyl-CoA species
Despite the repression of lipid hydrolases and decreased acyl-CoA binding capacity, Table 1 indicates ongoing β-oxidation in the presence of TCDD as evidenced by the presence of short- and medium-chain acyl-CoAs. The first step involves acyl-CoA dehydrogenation between C2 and C3 to produce trans-2-enoyl-CoA. In the mitochondria, this oxidation is catalyzed by acyl-CoA dehydrogenases (ACAD) which exhibit different tissue expression, subcellular locations, and substrate preferences. Highly expressed Acad11, which preferentially oxidizes saturated C22-CoA52, was repressed in the time course and dose response (3.8-fold at 30 µg/kg TCDD) studies with AHR enrichment at 2 h in the presence of a pDRE (Fig. 5). However, highly expressed Acadvl (induced 1.6-fold), which has overlapping substrate preferences, likely offsets the decreased expression of Acad11 while the effects on Acadm, which preferentially oxidizes medium-chain acyl-CoAs, were negligible. Overall, the effects of TCDD on mitochondrial acyl-CoA dehydrogenase gene expression were modest. In contrast, highly expressed acyl-CoA oxidase 1 (ACOX1), the rate-limiting step in peroxisomal β-oxidation, was repressed in the time course, dose response and circadian (3.9-fold at 30 µg/kg TCDD) studies in the presence of AHR enrichment at 2 h and pDREs (Fig. 5). Accordingly, ACOX1 protein levels were also repressed (Fig. 5F). The results suggests peroxisomal β-oxidation is impeded by TCDD, consistent with the accumulation of free and esterified very long- and long-chain FAs within TAGs, CEs, and phospholipids13,15.
Hydration of trans-2-enoyl-CoA
The hydration of trans-2-enoyl-CoA to 3-hydroxyacyl-CoA is catalyzed by enoyl-CoA hydratases depending on the number of carbons in the substrate (Fig. 5). In the mitochondria, long chain enoyl-CoAs are hydrated by the HADHA subunit of the mitochondrial trifunctional protein (MTP). HADHA exhibits the highest activity for C12-16 enoyl-CoAs with virtually no activity towards C4 enoyl-CoAs53. The expression of Hadha was not affected by TCDD. In contrast, ECHS1, the short chain enoyl-CoA hydratase, prefers C4 enoyl-CoAs with diminishing activity towards C10 enoyl-CoAs54. Although Echs1 transcript levels was repressed 2.0-fold in the presence of AHR enrichment and pDREs, protein levels were induced (Fig. 5H). Furthermore, Fig. 5I shows that octenoyl-CoA inhibited the hydration of crotonyl-CoA, the preferred C4-enoyl substrate of ECHS1. A tenfold higher concentration of octenoyl-CoA inhibited the hydration of crotonyl-CoA > 90% providing compelling evidence that octenoyl-CoA can inhibit ECHS1 activity. TCDD does not directly inhibit ECHS1 enzymatic activity at concentrations previously reported to repress HepG2 cell proliferation and colony formation (Supplementary Fig. S2)55.
In peroxisomes, Ehhadh, which encodes for the enoyl-CoA hydratase subunit of the liver bifunctional enzyme (L-BPE), was induced 7.7-fold in the absence of AHR enrichment and pDREs. After several cycles, the resulting peroxisomal medium-chain acyl-CoAs are transported to the mitochondria for further β-oxidation. Despite the expression of multiple acyl-CoA dehydrogenases that produce medium-chain enoyl-CoAs, there is only one enoyl-CoA hydratase, ECHS1, with a preference for medium and short-chain acyl-CoAs. Consequently, Echs1 repression may contribute to the dose-dependent accumulation of octenoyl-CoA (Table 1, Fig. 5).
Eci1 and 2, and Decr1 and 2 isomerize mono- and poly-unsaturated acyl-CoA cis double bonds to the 2-trans configuration, and the reduction of 2,4-dienoyl-CoAs to trans-3-enoyl CoA, respectively (Supplementary Fig. 1). Eci1, Eci2 and peroxisomal Decr2 were repressed by TCDD (2.1-, 2.2-, and 2.9-fold, respectfully) while highly expressed mitochondrial Decr1 was unaffected by TCDD. All four genes exhibited AHR enrichment in the presence of a pDRE. Without appropriate standards, it was not possible to determine the presence of cis- versus trans-enoyl-CoA or 2- versus 3-enoyl-CoA or the existence of polyunsaturated enoyl-CoA species. Collectively, the data suggests Δ2,3-octenoyl-CoA is present although other octenoyl-CoA species may also exist.
Dehydrogenation of 3-hydroxyacyl-CoA
The oxidation of 3-hydroxyacyl-CoA to 3-ketoacyl-CoA is catalyzed by 3-hydroxyacyl-CoA dehydrogenase (Fig. 5). In the mitochondria, long-chain 3-hydroxyacyl-CoAs are oxidized by the highly expressed alpha subunit (Hadha) of MTP which was not affected by TCDD. In peroxisomes, the highly expressed Ehhadh subunit, which was induced 7.7-fold, preferentially oxidizes very long- and long-chain 3-hydroxyacyl-CoAs. Medium- and short-chain 3-hydroxyacyl-CoAs are then oxidized by Hadh and Hsd17b4 which were repressed 1.5- and 1.8-fold, respectively. Hadh and Hsd17b4 both exhibited AHR enrichment in the presence of a pDRE while Ehhadh induction occurred in the absence of AHR enrichment or pDREs.
Thiolysis of 3-ketoacyl-CoA
Thiolytic cleavage of 3-ketoacyl-CoA requires an additional CoASH to generate acetyl-CoA and an acyl-CoA that is two carbons shorter (Fig. 5). In the mitochondria, the MTP beta subunit (Hadhb), which exhibited no change, catalyzes the cleavage of long-chain 3-ketoacyl-CoAs. In peroxisomes, ACAA1A (Acaa1a), ACAA1B (Acaa1b) and SCP2 (Scp2), which preferentially catalyze very long 3-ketoacyl-CoA thiolysis, were repressed 1.8-, 3.9- and 3.5-fold, respectively. Long-, medium- and short-chain 3-ketoacyl-CoAs undergo thiolytic cleavage catalyzed by ACAA2 (Acaa2) and ACAT1 (Acat1) which were repressed 4.2- and 3.0-fold. All six genes with thiolytic cleavage activity exhibited AHR enrichment in the presence of a pDRE. Collectively, 5 of 6 genes associated with thiolase activity were repressed by TCDD.
Acyl-CoA deactivation
Excess FAs can overload β-oxidation causing mitochondrial stress that reduces flux and depletes free CoASH needed for other metabolic pathways including the TCA cycle and FA metabolism. In response, acyl-CoA thioesterases (ACOTs) hydrolyze acyl-CoAs releasing the CoASH from activated FAs (Fig. 6)56. Therefore, we examined the effect of TCDD on cytosolic and mitochondrial thioesterase expression. Acot1 and Acot2, which exhibit a preference for long-chain acyl-CoAs, were induced 8.9- and 21.2-fold, respectively. ACOT2 is the primary mitochondrial thioesterase with little activity for < 10C acyl-CoAs. In contrast, Acot7 and Acot13, are enzymatically inhibited by CoASH, and were repressed 2.4- and 2.8-fold, respectively. Peroxisomal thioesterase Acot4, which prefers very long- and long-chain acyl-CoAs was induced 3.7-fold, while CoASH sensitive Acot8 that exhibits broad substrate preferences (C2-20 acyl-CoAs), was repressed 1.5-fold. Unlike the mitochondria, which catalyzes complete FA oxidation, peroxisomes only complete 2–5 β-oxidative cycles producing medium-chain acyl-CoAs that are hydrolyzed by ACOT3 (Acot3; induced 12.5-fold) and readily taken up by the mitochondria. Alternatively, they are transported to the mitochondria following conversion to medium-chain acylcarnitine by carnitine O-octanoyltransferase (Crot) (Fig. 7). Mitochondrial Acot9, which preferentially hydrolyzes medium- and short-chain acyl-CoAs, and is inhibited by CoASH, was also induced 6.0-fold (Fig. 6). Accumulating mitochondrial CoASH could then either be used to reactivate free FAs in the matrix or be exported to the cytosol via PMP34 (Slc25a17, no expression change) initiating a futile cycle (Fig. 7)56. Nudt7 which preferentially cleaves medium-chain acyl-CoAs to acyl-phosphopantetheines and 3',5'-ADP, was repressed 8.0-fold57. This futile cycle may be exacerbated by the 23.3-fold induction of Ucp2 which would not only facilitate the mitochondrial export of liberated FAs and FA peroxides, but dissipate the proton gradient and uncouple oxidative phosphorylation58,59. In summary, TCDD-elicited differential gene expression of thioesterases favors the hydrolysis of very long- and long-chain acyl-CoAs freeing CoASH required for other reactions while leaving medium-chain acyl-CoAs intact for peroxisomal and mitochondrial β-oxidation.
Omega(ω)-oxidation of fatty acids
FAs can also undergo ω-hydroxylation with subsequent metabolism by alcohol and aldehyde dehydrogenases to produce dicarboxylic acids (DCAs) when β-oxidation is impeded. Consequently, we examined our metabolomics data for the presence of DCAs. Dose-dependent changes in short-, medium- and long-chain DCAs were identified (Table 2). MCFAs (C10:0 and C12:0) are reported to have the greatest affinity for ω-oxidation60. Sebacic (C10:0) and dodecanedioic (C12:0) acids were induced 20.4- and 1.5-fold. Both can undergo further peroxisomal β-oxidation to produce shorter DCAs. Suberic (C8:0), azelaic (C9:0) and undecanedioic (C11:0) acids were induced 2.8-, 2.7-, and 8.9-fold, respectively, between 1 and 10 µg/kg TCDD with decreasing levels at higher doses. The detection of azelaic acid has been previously reported in TCDD treated mice43.
Table 2.
Compound ID | Description | Cn | Score | Fold-Change (TCDD vs. Veh.) | ||||
---|---|---|---|---|---|---|---|---|
0.3 µg/kg | 1 µg/kg | 3 µg/kg | 10 µg/kg | 30 µg/kg | ||||
HMDB00672 | Hexadecanedioic acid | 16 | 46.1 | 1.00 ± 0.03 | 0.93 ± 0.04 | 1.10 ± 0.14 | 1.33 ± 0.17 | 1.90 ± 0.41* |
HMDB00872 | Tetradecanedioic acid | 14 | 43.5 | 0.99 ± 0.02 | 1.10 ± 0.07 | 0.91 ± 0.11 | 0.38 ± 0.04* | 0.57 ± 0.10* |
HMDB00623 | Dodecanedioic acid | 12 | 37.9 | 0.95 ± 0.01 | 1.13 ± 0.05 | 1.12 ± 0.05 | 1.18 ± 0.07 | 1.53 ± 0.11* |
HMDB00888 | Undecanedioic acid | 11 | 42.7 | 0.36 ± 0.02 | 2.05 ± 0.21 | 3.01 ± 1.38 | 8.79 ± 0.67* | 5.40 ± 1.96* |
HMDB00792 | Sebacic acid | 10 | 36.5 | 0.44 ± 0.06 | 3.67 ± 0.53 | 6.54 ± 3.33 | 20.39 ± 3.53* | 12.79 ± 5.62* |
HMDB00784 | Azelaic acid | 9 | 45.9 | 0.90 ± 0.09 | 2.73 ± 0.26* | 2.32 ± 0.57* | 1.66 ± 0.12 | 2.22 ± 0.20* |
HMDB00893 | Suberic acid | 8 | 37.9 | 0.83 ± 0.02 | 1.54 ± 0.13 | 1.50 ± 0.32 | 2.82 ± 0.38* | 2.06 ± 0.31* |
Dicarboxylic acid levels were assessed in mice using untargeted liquid chromatography tandem mass spectrometry. Mice (n = 4–5) were orally gavaged every 4 days for 28 days with sesame oil vehicle or TCDD. Fold-changes were calculated for each treatment group relative to the vehicle control group. Bold font and asterisks (*) denote statistical significance (p ≤ 0.05) determined using a one-way ANOVA with Dunnett’s post-hoc analysis. Scores were determined by Progenesis with 60 being the maximum value and 0 being the minimum value. Scores ranging from 30—40 are based on mass error and isotope distribution similarity, while score > 40 are based on mass error, isotope distribution and fragmentation score. All annotated compounds have a score distribution averaging ~ 35.
In ω-oxidation, SCFAs, MCFAs, LCFAs and VLCFAs are first ω-hydroxylated by the CYP4Bs, CYP4As, CYP4Fs or CYP4Us. However, most cytochrome P450, ADH, and ALDH genes associated with ω-oxidation were repressed (Fig. 8). Specifically, Cyp4a12a, Cyp4a12b and Cyp4a32 which preferentially ω-hydroxylate MCFAs were repressed 150.9-, 23.6 and 1.9-fold, respectively. Similarly, Cyp4f13 (-3.2-fold), Cyp4f14 (-387.6-fold), Cyp4f15 (-12.2-fold), Cyp4f17 (-3.1-fold) and Cyp4v3 (-4.5-fold) that preferentially ω-hydroxylate LCFAs were all repressed. Cyp2u1 which mediates the ω-hydroxylation of LCFAs was also repressed 10.2-fold. However, the principal genes that mediate FA ω-hydroxylation, Cyp4a10 and Cyp4a14, were induced 4.2-, and 6.7-fold, respectively. Cyp4a10 and Cyp4a14 induction is primarily mediated by PPARA (Ppara), which was repressed 8.7-fold, with AHR enrichment in the presence of a pDRE. Cyp4a31 and Cyp4f16 were also induced 25.9- and 4.1-fold. Of these induced genes, only Cyp4a31 exhibited AHR enrichment with a pDRE by TCDD at 2 h. Poorly defined alcohol and aldehyde dehydrogenases are responsible for the oxidation of ω-hydroxylated FAs. Adh4 and Adh5 expression was repressed 14.8- and 2.2-fold, respectively, consistent with other reports61,62. TCDD did not affect Adh7 which is reported to oxidize long ω-hydroxylated FAs63. Highly expressed Aldh1a1 was repressed 1.9-fold, while Aldh3a2 showed negligible changes. However, Aldh3b1 and Aldh18a1 were induced 41.1- and 19.0-fold, respectively. Despite most genes being repressed, key ω-oxidation genes were induced by TCDD consistent with increased DCA levels.
Discussion
In this study, TCDD is used as a prototypical AHR ligand and represents the cumulative burden of all AHR agonists. The dose range and regimen approached steady state levels while inducing full dose response curves for many genes in the absence of (i) necrosis or apoptosis, (ii) significant serum ALT increases, (iii) changes in food consumption and (iv) body weight loss > 15%8,9. To provide perspective, 30 µg/kg TCDD resulted in mouse hepatic tissue levels comparable to serum levels reported in Viktor Yushchenko following intentional poisoning, while 0.03–0.1 μg/kg resulted in serum levels comparable to the Seveso cohort of women following the 1976 chemical release accident. At 0.01 µg/kg, hepatic levels were comparable to control hepatic levels, and to dioxin-like compound levels in US, German, Spanish and British serum samples8,64,65. Consequently, the dose range and regimen are relevant to human exposures, and the elicited effects cannot be attributed to overt toxicity. Conservation of the AHR, and similarities in AHR-mediated dyslipidemia and metabolic disease between rodents and humans, suggest a common mechanism that may identify novel therapeutic interventions for NAFLD which currently has limited treatment options66.
TCDD dose-dependently induced steatosis in mice with marked increases in TAGs, CEs, phospholipids, and free FAs in the absence of acute toxicity13,15. This steatosis is attributed, in part, to the accumulation of dietary lipids and the inhibition of VLDL export13,67. Previous metabolomic analysis suggested TCDD disruptedd β-oxidation based increased palmitoylcarnitine15, with more targeted functional assays demonstrating repression of hepatic β-oxidation13,17, which was confirmed by dose-dependent decreases in shorter chain acyl-CoAs. This is consistent with reported decreases of acyl-CoAs by 2,3,7,8-tetrachlorodibenzo-p-furan (TCDF) in mice and in human liver Huh-7 cells following TCDD treatment68,69. We further investigated this inhibition by integrating metabolomics, ChIP-seq, and RNA-seq datasets to determine the effects of TCDD on FA oxidation, focusing on differential gene expression associated with lipid hydrolysis, FA activation, binding proteins, β-oxidation, and acyl-CoA hydrolysis.
RNA-seq analysis identified seven of nine lipid hydrolases repressed by TCDD with only Pnpla2 and Lpl showing induction. Yet, TCDD increased hepatic free FA levels which could serve as substrate for β-oxidation. The increase in FA levels is attributed not only to increased hepatic uptake of dietary FAs and mobilized peripheral lipids following CD36 induction, but also reduced ACS levels13,15,17. ACSs catalyze a two-step, ATP-dependent, reaction producing activated FAs required for β-oxidation to proceed. In addition, genes encoding the predominant FA binding proteins FABP1, DBI, and SCP2, which also bind acyl-CoAs, heme, bile acids, retinoids, and other hydrophobic ligands, were repressed by TCDD, therefore reducing cytosolic, peroxisomal, and mitochondrial acyl-CoA binding capacity and trafficking. Furthermore, FABPs, DBI, and SCP2 buffer the toxicity, block the signaling potential of free ligands, and protect acyl-CoAs from hydrolysis34,70. For example, long-chain acyl-CoAs are powerful disruptors of membrane bilayers, inhibit diverse enzyme activities, and alter ion channel function71. Consequently, decreases in ACS and binding proteins would impede FA metabolism by reducing activated FA levels, and increasing acyl-CoA susceptibility to hydrolysis.
CoASH is an obligate cofactor for > 100 different metabolic reactions. It does not passively diffuse across membranes, and therefore distinct cytosolic, peroxisomal, and mitochondrial CoASH and acyl-CoA pools exist. Hereditary or acquired conditions involving CoA ester accumulation, often referred to as CoASH sequestration, toxicity, or redistribution (CASTOR) disease, lead to the accumulation of one or more acyl-CoA species that reduce free CoASH levels causing adverse effects72. Deficiencies in short-, medium-, long-, and very long-chain acyl-CoA dehydrogenase, trifunctional protein, and carnitine shuttle activities are associated with CASTOR disease72. This phenomena is also associated with the toxicity of valproic, salicylic, pivalic, phenylbutyric, and benzoic acids and does not solely arise from free CoASH depletion72,73.
In response to CoASH sequestration, thioesterases prevent acyl-CoA levels from reaching toxic levels38. TCDD dose-dependently induced cytosolic, peroxisomal, and mitochondrial thioesterases including Acot9 which prefers medium-chain acyl-CoAs, but is strongly inhibited by CoASH favoring octanoyl-CoA accumulation. Furthermore, Nudt7 which hydrolyzes free CoASH and acyl-CoAs to (acyl)phosphopantetheines and 3’,5’-ADP, was repressed57. Nudt7 repression and thioesterase induction would increase free CoASH levels and de-activate FAs in an ATP-consuming futile cycle that inhibits β-oxidation. Collectively, (i) ACS repression and thioesterase induction would reduce activated FA levels required for β-oxidation, while (ii) decreased FABPs, DBI, and SCP2 binding capacity would increase acyl-CoA susceptibility to hydrolysis and compromise trafficking substrates to metabolic pathways. Moreover, Ucp2 induction would export liberated FAs from the matrix, uncoupling oxidative phosphorylation and further compromise energy production. The accumulation of TAGs and CEs containing long-chain FAs13, the dose-dependent decrease in acyl-CoA levels (Table 1), and the detection of palmitoylcarnitine in serum, all suggest TCDD impaired FA oxidation15. Increased palmitoyl (C16)-, tetradecanoyl (C14)-, and decanoyl (C10)-carnitine levels are also reported in factory workers with 29.49–765.35 pg TEQs/g lipid levels74. Elevated serum acylcarnitine levels are associated with NAFLD75, suggesting the effects of TCDD in mice may have relevance in humans.
An unexpected result was the dose-dependent increase in octenoyl-CoA. In the mitochondria, long-chain acyl-CoAs are oxidized by multiple dehydrogenases that were minimally affected by TCDD. The trifunctional protein (MTP), encoded by Hadha and Hadhb, carries out the enoyl-CoA hydratase, hydroxyacyl-CoA dehydrogenase, and 3-ketothiolase activities. Hadha expression was not affected by TCDD, Hadhb was modestly induced, and thiolases (Acaa1b, Acaa2) were repressed. Enoyl-, 3-hydroxy- and 3-keto-acyl-CoA intermediates are not substrates for thioesterases. Very long- and long-chain acyl-CoAs that escape thioesterase hydrolysis and complete several β-oxidation spirals would result in the production of medium-chain acyl-CoAs. TCDD induced thioesterases with a preference for very long- and long-chain acyl-CoAs. Acot9 which prefers medium-chain acyl-CoAs was also induced but is strongly inhibited by CoASH38. Peroxisomal MCFAs produced by peroxisomal β-oxidation would be ferried into the mitochondrial matrix via carnitine O-octanoyltransferase (Crot) which prefers medium-chain acyl-CoAs36,57, MCFA trafficking is not dependent on binding proteins and tend to be metabolized by hepatic mitochondrial β–oxidation following activation as opposed to being incorporated into TAGs, CEs or phospholipids49. We posit that accumulating peroxisomal and mitochondrial octanoyl-CoAs are oxidized to octenoyl-CoA by ACADM which was largely unaffected by TCDD. Accumulating octenoyl-CoA levels represent a metabolic conundrum since the HADHA enoyl-CoA hydratase subunit prefers substrate chain lengths of C12-16 with virtually no activity53. ECHS1, the short chain enoyl-CoA hydratase, prefers C4 enoyl-CoAs with diminishing activity towards C10 enoyl-CoAs, although ECHS1 has been reported hydrate enoyl-CoA species up to C1054,76. This is somewhat analogous to ACADM deficient mice where octanoyl-CoA oxidation is not compensated by other acyl-CoA dehydrogenases77. Moreover, in addition to being a poor substrate for hydration, we showed octenoyl-CoA inhibited the hydration of crotonyl-CoA, the preferred substrate of ECHS1.
When β-oxidation is hindered, FAs can undergo ω-hydroxylation, primarily by CYP4A10 and CYP4A14, with subsequent oxidation by poorly defined cytosolic alcohol and aldehyde dehydrogenases to produce DCAs78. In humans, ω-oxidation is a secondary pathway responsible for 5–10% of FA metabolism under normal conditions. During fasting, starvation, or when β-oxidation is impeded due to an inborn error of metabolism, ω-oxidation is considered a rescue pathway producing DCAs that undergo peroxisomal β-oxidation to produce TCA cycle and gluconeogenesis intermediates79. Conversely, DCAs are also associated with oxidative stress, lipotoxicity and PPAR activation that induces β-oxidation80. However, TCDD repressed Ppara expression and inhibits PPARα-mediated gene expression81, thus compromising β-oxidation induction by DCAs.
Long-chain DCAs can be reactivated to the corresponding CoA ester and undergo chain shortening by peroxisomal β-oxidation to produce DCAs of varying length following hydrolysis by thioesterases82. For example, dodecanedioic acid (12C) can be oxidized to sebacic (C10) and suberic acids (C8) while undecanedioic acid (11C) is rarely detected since it is partially oxidized in peroxisomes before further mitochondrial metabolism. Interestingly, TCDD decreased serum azelaic (C9) acid levels due to the repression of CES3 that hydrolyzes monoesters to release azelaic acid43. By extrapolation, we surmise that decreasing DCA levels (Table 2) at higher TCDD doses is inversely correlated with the repression of Ces genes that exhibit different DCA monoester preferences as reported for other carboxylesterase substrates43,83.
In summary (Fig. 9), we propose that β-oxidation inhibition by TCDD is due to the differential expression of genes peripheral to the spiral itself. More specifically, TCDD represses lipid hydrolysis, FA activation, and binding protein expression, while inducing thioesterases. However, most of the effects reported here are limited to gene expression and selected proteins, and do not consider post-translational modifications that can also regulate enzyme activity. Nevertheless, the data suggest TCDD induces a futile cycle of FA activation by ACSs and de-activation by thioesterases that inhibits complete oxidation of FAs, uncouples oxidative phosphorylation, and depletes ATP levels. Consequently, FAs underwent ω-oxidation producing PPAR ligands in an attempt to induce β-oxidation. However, Ppara and Fabp1, the encoded proteins, of which, deliver ligands to PPARα, were repressed thwarting efforts to induce β-oxidation. This would not only further deplete energy levels but also increase free FA and DCA levels that likely exacerbate TCDD toxicity. The inhibition of ECHS1 activity and accumulation of mitochondrial octenoyl-CoA may also contribute to toxicity by precipitating metabolic decompensation due to the exhaustion of free CoASH required by enzymes in other pathways. Moreover, octenoyl-CoA may itself be toxic by inappropriately inducing signaling, and/or possess lytic (detergent-like) properties that disrupt membranes. Although many of these effects are consistent with the development and progression of NAFLD, as well as AHR-mediated hepatotoxicity following activation by TCDD and related compounds, their relevance in human models warrants further investigation. This should include complementary metabolomic analyses of other fractions and compartments such as serum and urine for metabolites associated with impaired β-oxidation and NAFLD.
Methods
Animal treatment
Postnatal day 25 (PND25) male C57BL/6 mice weighing within 10% of each other were obtained from Charles River Laboratories (Kingston, NY). Mice were housed in Innovive Innocages (San Diego, CA) containing ALPHA-dri bedding (Shepherd Specialty Papers, Chicago, IL) in a 23 °C environment with 30–40% humidity and a 12 h/12 h light/dark cycle. Aquavive water (Innovive) and Harlan Teklad 22/5 Rodent Diet 8940 (Madison, WI) was provided ad libitum. TCDD (AccuStandard, New Haven, CT) was dissolved in acetone and diluted in sesame oil to a working stock. The acetone from the working stock was then evaporated off using nitrogen gas. On PND28, mice were orally gavaged at the start of the light cycle (zeitgeber [ZT] 0) with 0.1 ml sesame oil vehicle (Sigma-Aldrich, St. Louis, MO) or 0.01, 0.03, 0.1, 0.3, 1, 3, 10, and 30 μg/kg body weight TCDD every 4 days for 28 days for a total of 7 treatments. The first gavage was administered on day 0, while the final gavage was on day 24 of the 28-day study. This dosing regimen was selected to approach steady state levels given the 8–12 day half-life of TCDD in mice84. Comparable treatment has been used in previous studies8,9,13,16,17,43. Mice were fasted six hours prior to the end of the study. On day 28, vehicle- and TCDD-treated mice were weighed and euthanized. Liver samples were immediately flash frozen in liquid nitrogen and stored at − 80 °C until analysis. This study was conducted in accordance with relevant guidelines and regulations. All animal procedures were approved by the Michigan State University (MSU) Institutional Animal Care and Use Committee (IACUC; PROTO201800043) and meet the ARRIVE guidelines.
Liquid chromatography tandem mass spectrometry
Samples were extracted using methanol:water:chloroform as previously described with slight modifications9. Briefly, untargeted extractions were reconstituted with 400 µl tributylamine with no dilutions for analysis. Analysis was performed using a Xevo G2-XS QTOF attached to a Waters UPLC (Waters, Milford, MA) with negative-mode electrospray ionization run in MSE continuum mode. LC phases, gradient rates, and columns were used as previously published9. For untargeted acyl-CoA analysis, MSE continuum data was processed with Progenesis QI (Waters) to align features, peaks, deconvolute, and annotate metabolite peaks. Metabolite annotations were scored based on a mass error < 12 ppm to Human metabolome Database entries85, isotopic distribution similarity, and theoretical fragmentation comparisons to MSE high-energy mass spectra using the MetFrag option with each metric contributing a max of 20 points towards a max score of 60. Raw signals for each compound abundances were normalized to a correction factor calculated using a median and mean absolute deviation approach by Progenesis QI. Significance was determined by a one-way ANOVA adjusted for multiple comparisons with a Dunnett’s post-hoc test.
Protein quantification and capillary electrophoresis protein analysis
Frozen samples (~ 50 mg) were homogenized in RIPA buffer with protease inhibitor (Sigma-Aldrich) using a Polytron PT2100 homogenizer (Kinematica, Lucerne, Switzerland) and sonicated on ice. Samples were centrifuged and protein concentration measured using a bovine serum albumin standard curve and a bicinchoninic acid (BCA) assay (Sigma-Aldrich). The WES capillary electrophoresis system (ProteinSimple, San Jose, CA) was used following standard manufacturer protocols with the following antibodies and dilutions from Proteintech (Rosemont, IL): ACOX1 (1:50; 10,957–1-AP), ACSM3 (1:50; 10,168–2-AP), ACSL1 (1:50; 13,989–1-AP), DBI (1:50; 14,490–1-AP). Primary antibodies were detected using an anti-rabbit detection module (ProteinSimple). Chemiluminescence signal intensity was analyzed with Compass Software v4.0.0 (ProteinSimple). Representative spectra for each protein in each treatment group can be found in Figure S3. GraphPad Prism v8.4.3 (La Jolla, CA, USA) was used to conduct a one-way ANOVA followed by a Dunnett’s post-hoc analysis to determine statistical significance (p ≤ 0.05).
ECHS1 enzymatic activity assay
Enoyl-CoA hydratase, short chain 1 (ECHS1) activity was measured spectrophotometrically as previously described86,87. Hepatic extracts were prepared from control mice treated with sesame oil vehicle every 4 days for 28 days using crotonyl-CoA (Sigma-Aldrich) and trans-2,3-octenoyl-CoA (Toronto Research Chemicals, Toronto, Canada) as substrates. Total protein lysates were isolated from frozen samples with NP-40 cell lysis buffer (Thermo Fisher Scientific, Waltham, MA) with protease inhibitor using a Polytron PT2100 homogenizer (Kinematica). Incubations were performed in 100 mM Tris buffer (pH 8.0) supplemented with 0.1 mg/ml bovine serum albumin at 37 °C for 5 min. Reactions were started with 0.02 mg/ml total protein lysate and one of the following substrate ratios: 0.025 mM crotonyl-CoA (1:0 ratio), 0.025 mM crotonyl-CoA:0.025 mM octenoyl-CoA (1:1 ratio), or 0.025 mM crotonyl-CoA:0.25 mM octenoyl-CoA (1:10 ratio). ECHS1 activity was measured by following the decrease in absorbance over time at 263 nm using a SpectraMax ABS Plus (Molecular Devices, San Jose, CA). Enzymatic activity was calculated using 6700 cm−1 M−1 as the extinction coefficient.
Protein location data
COMPARTMENTS (accessed September 30, 2020) was used for cytosol (C), endoplasmic reticulum (ER), extracellular space (ES), Golgi apparatus (GA), lipid droplet (LD), lysosome (L), mitochondrion (M), mitochondrial outer membrane (OMM), mitochondrial inner membrane (IMM), nucleus (N), peroxisome (P), and plasma membrane (PM) mouse protein localizations88. COMPARTMENTS is a database that integrates evidence on protein subcellular localization from multiple sources including curated literature, high-throughput screens, automatic text mining, and sequence-based prediction methods.
Supplementary Information
Acknowledgements
This project was supported by the National Institute of Environmental Health Sciences (NIEHS) Superfund Research Program [NIEHS SRP P42ES004911] and the NIEHS Research Project Grant Program [NIEHS R01ES029541] to TRZ. TRZ was partially supported by AgBioResearch at Michigan State University. GNC and RRF were supported by NIEHS Multidisciplinary Training in Environmental Toxicology [T32ES007255]. KAF was supported by the Canadian Institutes of Health Research Doctoral Foreign Study Award [DFS-140386].
Author contributions
G.N.C., R.R.F. and T.R.Z. designed the project. R.R.F., K.A.F., N.A.Z. and R.N. performed the animal work. G.N.C., R.R.F., N.A.Z., and K.A.F. performed the experiments. R.R.F. developed the LC–MS workflow for untargeted metabolomics. G.N.C., R.R.F. and N.A.Z. compiled all the data and produced the figures and tables. G.N.C., R.R.F. and T.R.Z. wrote the manuscript. All authors reviewed the manuscript.
Data availability
Hepatic RNA-seq data sets were previously published9,10,89. Differentially expressed genes (|fold-change|≥ 1.5 and posterior probability (P1(t)) ≥ 0.8) were determined by empirical Bayes analysis90. Time course (GSE109863), dose response (GSE87519), and diurnal rhythmicity (GSE119780) sequencing data are available at the Gene Expression Omnibus. Diurnal rhythmicity was determined using JTK_CYCLE as previously described9. AHR ChIP-seq (GSE97634) and computationally identified putative dioxin response elements (pDREs, https://doi.org/10.7910/DVN/JASCVZ) data were previously published10. ChIP-seq analysis used a false discovery rate (FDR) ≤ 0.05. pDREs were considered functional with a matrix similarity score (MSS) ≥ 0.856 and associated with genes when located 10 kb upstream of the transcription start site (TSS) to the transcription end site (TES). Raw metabolomic data is deposited in the NIH Metabolomics Workbench (ST001379).
Competing interests
The authors declare no competing interests.
Footnotes
Publisher's note
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Supplementary Information
The online version contains supplementary material available at 10.1038/s41598-021-95214-0.
References
- 1.Mashek DG. Hepatic Fatty Acid Trafficking: Multiple Forks in the Road. Adv. Nutr. 2013;4:697–710. doi: 10.3945/an.113.004648. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 2.Neuschwander-Tetri BA. Hepatic lipotoxicity and the pathogenesis of nonalcoholic steatohepatitis: The central role of nontriglyceride fatty acid metabolites. Hepatology. 2010;52:774–788. doi: 10.1002/hep.23719. [DOI] [PubMed] [Google Scholar]
- 3.Marra F, Svegliati-Baroni G. Lipotoxicity and the gut-liver axis in NASH pathogenesis. J. Hepatol. 2018;68:280–295. doi: 10.1016/j.jhep.2017.11.014. [DOI] [PubMed] [Google Scholar]
- 4.Wong RJ, et al. Nonalcoholic steatohepatitis is the second leading etiology of liver disease among adults awaiting liver transplantation in the United States. Gastroenterology. 2015;148:547–555. doi: 10.1053/j.gastro.2014.11.039. [DOI] [PubMed] [Google Scholar]
- 5.Buzzetti E, Pinzani M, Tsochatzis EA. The multiple-hit pathogenesis of non-alcoholic fatty liver disease (NAFLD) Metabolism. 2016;65:1038–1048. doi: 10.1016/j.metabol.2015.12.012. [DOI] [PubMed] [Google Scholar]
- 6.Wahlang B, et al. Toxicant-associated steatohepatitis. Toxicol. Pathol. 2013;41:343–360. doi: 10.1177/0192623312468517. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7.Al-Eryani L, et al. Identification of environmental chemicals associated with the development of toxicant-associated fatty liver disease in rodents. Toxicol. Pathol. 2015;43:482–497. doi: 10.1177/0192623314549960. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 8.Nault R, et al. Dose-dependent metabolic reprogramming and differential gene expression in TCDD-elicited hepatic fibrosis. Toxicol. Sci. 2016;154:253–266. doi: 10.1093/toxsci/kfw163. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 9.Fader KA, Nault R, Doskey CM, Fling RR, Zacharewski TR. 2,3,7,8-Tetrachlorodibenzo-p-dioxin abolishes circadian regulation of hepatic metabolic activity in mice. Sci. Rep. 2019;9:1–18. doi: 10.1038/s41598-019-42760-3. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10.Fader KA, et al. Convergence of hepcidin deficiency, systemic iron overloading, heme accumulation, and REV-ERBα/β activation in aryl hydrocarbon receptor-elicited hepatotoxicity. Toxicol. Appl. Pharmacol. 2017;321:1–17. doi: 10.1016/j.taap.2017.02.006. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11.Fader KA, et al. 2,3,7,8-Tetrachlorodibenzo-p-dioxin (TCDD)-elicited effects on bile acid homeostasis: Alterations in biosynthesis, enterohepatic circulation, and microbial metabolism. Sci. Rep. 2017;7:5921. doi: 10.1038/s41598-017-05656-8. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 12.Nault R, Colbry D, Brandenberger C, Harkema JR, Zacharewski TR. Development of a computational high-throughput tool for the quantitative examination of dose-dependent histological features. Toxicol. Pathol. 2015;43:366–375. doi: 10.1177/0192623314544379. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 13.Nault R, Fader KA, Lydic TA, Zacharewski TR. Lipidomic evaluation of aryl hydrocarbon receptor-mediated hepatic steatosis in male and female mice elicited by 2,3,7,8-tetrachlorodibenzo-p-dioxin. Chem. Res. Toxicol. 2017;30:1060–1075. doi: 10.1021/acs.chemrestox.6b00430. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 14.Kania-Korwel I, Wu X, Wang K, Lehmler HJ. Identification of lipidomic markers of chronic 3,3′,4,4′,5-pentachlorobiphenyl (PCB 126) exposure in the male rat liver. Toxicology. 2017;390:124–134. doi: 10.1016/j.tox.2017.09.005. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 15.Lin S, Yang Z, Liu H, Cai Z. Metabolomic analysis of liver and skeletal muscle tissues in C57BL/6J and DBA/2J mice exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin. Mol. Biosyst. 2011;7:1956–1965. doi: 10.1039/c1mb05057e. [DOI] [PubMed] [Google Scholar]
- 16.Angrish MM, Dominici CY, Zacharewski TR. TCDD-Elicited effects on liver, serum, and adipose lipid composition in C57BL/6 mice. Toxicol. Sci. 2013;131:108–115. doi: 10.1093/toxsci/kfs277. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 17.Lee JH, et al. A novel role for the dioxin receptor in fatty acid metabolism and hepatic steatosis. Gastroenterology. 2010;139:653–663. doi: 10.1053/j.gastro.2010.03.033. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Lee CC, Yao YJ, Chen HL, Guo YL, Su HJ. Fatty liver and hepatic function for residents with markedly high serum PCDD/Fs levels in Taiwan. J. Toxicol. Environ. Health Part A. 2006;69:367–380. doi: 10.1080/15287390500244972. [DOI] [PubMed] [Google Scholar]
- 19.Warner M, et al. Diabetes, metabolic syndrome, and obesity in relation to serum dioxin concentrations: The Seveso Women’s Health Study. Environ. Health Perspect. 2013;121:906–911. doi: 10.1289/ehp.1206113. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 20.Pelclová D, et al. Adverse health effects in humans exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) Rev. Environ. Health. 2006;21:119–138. doi: 10.1515/REVEH.2006.21.2.119. [DOI] [PubMed] [Google Scholar]
- 21.Martin JV. Lipid abnormalities in workers exposed to dioxin. Br. J. Ind. Med. 1984;41:254–256. doi: 10.1136/oem.41.2.254. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 22.Sweeney MH, et al. Review and update of the results of the NIOSH medical study of workers exposed to chemicals contaminated with 2,3,7,8-tetrachlorodibenzodioxin. Teratog. Carcinog. Mutagen. 1997;17:241–247. doi: 10.1002/(SICI)1520-6866(1997)17:4/5<241::AID-TCM6>3.0.CO;2-I. [DOI] [PubMed] [Google Scholar]
- 23.Warner M, et al. In utero dioxin exposure and cardiometabolic risk in the Seveso Second Generation Study. Int. J. Obes. 2019;43:2233–2243. doi: 10.1038/s41366-018-0306-8. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 24.Wahlang B, et al. Mechanisms of environmental contributions to fatty liver disease. Curr. Environ. Heal. Reports. 2019;6:80–94. doi: 10.1007/s40572-019-00232-w. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 25.Mimura J, et al. Loss of teratogenic response to 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) in mice lacking the Ah (dioxin) receptor. Genes Cells. 1997;2:645–654. doi: 10.1046/j.1365-2443.1997.1490345.x. [DOI] [PubMed] [Google Scholar]
- 26.Fernandez-Salguero PM, Hilbert DM, Rudikoff S, Ward JM, Gonzalez FJ. Aryl-hydrocarbon receptor-deficient mice are resistant to 2,3,7,8-tetrachlorodibenzo-p-dioxin-induced toxicity. Toxicol. Appl. Pharmacol. 1996;140:173–179. doi: 10.1006/taap.1996.0210. [DOI] [PubMed] [Google Scholar]
- 27.Schmidt JV, Su GHT, Reddy JK, Simon MC, Bradfield CA. Characterization of a murine Ahr null allele: Involvement of the Ah receptor in hepatic growth and development. Proc. Natl. Acad. Sci. U. S. A. 1996;93:6731–6736. doi: 10.1073/pnas.93.13.6731. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 28.Denison MS, Soshilov AA, He G, Degroot DE, Zhao B. Exactly the same but different: Promiscuity and diversity in the molecular mechanisms of action of the aryl hydrocarbon (dioxin) receptor. Toxicol. Sci. 2011;124:1–22. doi: 10.1093/toxsci/kfr218. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 29.Hankinson O. The aryl hydrocarbon receptor complex. Annu. Rev. Pharmacol. Toxicol. 1995;35:307–340. doi: 10.1146/annurev.pa.35.040195.001515. [DOI] [PubMed] [Google Scholar]
- 30.Dere E, Lo R, Celius T, Matthews J, Zacharewski TR. Integration of genome-wide computation DRE Search, AhR ChIP-chip and gene expression analyses of TCDD-elicited responses in the mouse liver. BMC Genomics. 2011;12:365. doi: 10.1186/1471-2164-12-365. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 31.Safe S. Polychlorinated biphenyls (PCBs), dibenzo-p-dioxins (PCDDs), dibenzofurans (PCDFs), and related compounds: Environmental and mechanistic considerations which support the development of toxic equivalency factors (TEFs) Crit. Rev. Toxicol. 1990;21:51–88. doi: 10.3109/10408449009089873. [DOI] [PubMed] [Google Scholar]
- 32.Knudsen, J., Mandrup, S. & Rasmussen, J. T. The function of acyl-CoA-binding protein (ACBP)/Diazepam binding inhibitor (DBI) Jens. Mol. Cell. Biochem.123, 129–138 (1993). [DOI] [PubMed]
- 33.Frolov A, Cho TH, Billheimer JT, Schroeder F. Sterol carrier protein-2, a new fatty acyl coenzyme A-binding protein. J. Biol. Chem. 1996;271:31878–31884. doi: 10.1074/jbc.271.50.31878. [DOI] [PubMed] [Google Scholar]
- 34.Wang GQ, Bonkovsky HL, De Lemos A, Burczynski FJ. Recent insights into the biological functions of liver fatty acid binding protein 1. J. Lipid Res. 2015;56:2238–2247. doi: 10.1194/jlr.R056705. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 35.Amiri M, et al. Diverse roles of fatty acid binding proteins (FABPs) in development and pathogenesis of cancers. Gene. 2018;676:171–183. doi: 10.1016/j.gene.2018.07.035. [DOI] [PubMed] [Google Scholar]
- 36.Houten SM, Wanders RJA. A general introduction to the biochemistry of mitochondrial fatty acid β-oxidation. J. Inherit. Metab. Dis. 2010;33:469–477. doi: 10.1007/s10545-010-9061-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 37.Wanders RJA, Ferdinandusse S, Brites P, Kemp S. Peroxisomes, lipid metabolism and lipotoxicity. Biochim. Biophys. Acta. Mol. Cell Biol. Lipids. 2010;1801:272–280. doi: 10.1016/j.bbalip.2010.01.001. [DOI] [PubMed] [Google Scholar]
- 38.Tillander V, Alexson SEH, Cohen DE. Deactivating fatty acids: Acyl-CoA thioesterase-mediated control of lipid metabolism. Trends Endocrinol. Metab. 2017;28:473–484. doi: 10.1016/j.tem.2017.03.001. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 39.Haynes CA, et al. Quantitation of fatty acyl-coenzyme As in mammalian cells by liquid chromatography-electrospray ionization tandem mass spectrometry. J. Lipid Res. 2008;49:1113–1125. doi: 10.1194/jlr.D800001-JLR200. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 40.Quiroga AD, Lehner R. Liver triacylglycerol lipases. Biochim. Biophys. Acta. 2012;1821:762–769. doi: 10.1016/j.bbalip.2011.09.007. [DOI] [PubMed] [Google Scholar]
- 41.Mashek DG, Khan SA, Sathyanarayan A, Ploeger JM, Franklin MP. Hepatic lipid droplet biology: Getting to the root of fatty liver. Hepatology. 2015;62:964–967. doi: 10.1002/hep.27839. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 42.Lian J, Nelson R, Lehner R. Carboxylesterases in lipid metabolism: from mouse to human. Protein Cell. 2018;9:178–195. doi: 10.1007/s13238-017-0437-z. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 43.Matsubara T, et al. Metabolomics identifies an inflammatory cascade involved in dioxin- and diet-induced steatohepatitis. Cell Metab. 2012;16:634–644. doi: 10.1016/j.cmet.2012.10.006. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 44.Ovando BJ, Ellison CA, Vezina CM, Olson JR. Toxicogenomic analysis of exposure to TCDD, PCB126 and PCB153: Identification of genomic biomarkers of exposure to AhR ligands. BMC Genomics. 2010;11:583. doi: 10.1186/1471-2164-11-583. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 45.Vezina CM, Walker NJ, Olson JR. Subchronic exposure to TCDD, PeCDF, PCB126, and PCB153: Effect on hepatic gene expression. Environ. Health Perspect. 2004;112:1636–1644. doi: 10.1289/txg.7253. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 46.Zechner R, et al. FAT SIGNALS—Lipases and lipolysis in lipid metabolism and signaling. Cell Metab. 2012;15:279–291. doi: 10.1016/j.cmet.2011.12.018. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 47.Watkins PA, Maiguel D, Jia Z, Pevsner J. Evidence for 26 distinct acyl-coenzyme A synthetase genes in the human genome. J. Lipid Res. 2007;48:2736–2750. doi: 10.1194/jlr.M700378-JLR200. [DOI] [PubMed] [Google Scholar]
- 48.Mashek DG, Li LO, Coleman RA. Rat long-chain acyl-CoA synthetase mRNA, protein, and activity vary in tissue distribution and in response to diet. J. Lipid Res. 2006;47:2004–2010. doi: 10.1194/jlr.M600150-JLR200. [DOI] [PubMed] [Google Scholar]
- 49.Schönfeld P, Wojtczak L. Short- and medium-chain fatty acids in energy metabolism: The cellular perspective. J. Lipid Res. 2016;57:943–954. doi: 10.1194/jlr.R067629. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 50.Hlaváč V, Souček P. Role of family D ATP-binding cassette transporters (ABCD) in cancer. Biochem. Soc. Trans. 2015;43:937–942. doi: 10.1042/BST20150114. [DOI] [PubMed] [Google Scholar]
- 51.Morita M, Imanaka T. Peroxisomal ABC transporters: Structure, function and role in disease. Biochim. Biophys. Acta Mol. Basis Dis. 2012;1822:1387–1396. doi: 10.1016/j.bbadis.2012.02.009. [DOI] [PubMed] [Google Scholar]
- 52.He M, et al. Identification and characterization of new long chain Acyl-CoA dehydrogenases. Mol. Genet. Metab. 2011;102:418–429. doi: 10.1016/j.ymgme.2010.12.005. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 53.Eaton S, et al. The mitochondrial trifunctional protein: Centre of a β-oxidation metabolon? Biochem. Soc. Trans. 2000;28:177–182. doi: 10.1042/bst0280177. [DOI] [PubMed] [Google Scholar]
- 54.Burgin HJ, McKenzie M. Understanding the role of OXPHOS dysfunction in the pathogenesis of ECHS1 deficiency. FEBS Lett. 2020;594:590–610. doi: 10.1002/1873-3468.13735. [DOI] [PubMed] [Google Scholar]
- 55.Yamaguchi M, Hankinson O. 2,3,7,8-Tetrachlorodibenzo-p-dioxin suppresses the growth of human liver cancer HepG2 cells in vitro: Involvement of cell signaling factors. Int. J. Oncol. 2018;53:1657–1666. doi: 10.3892/ijo.2018.4507. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 56.Ellis, J. M., Bowman, C. E. & Wolfgang, M. J. Metabolic and tissue-specific regulation of acyl-CoA metabolism. PLoS One10, e0116587 (2015). [DOI] [PMC free article] [PubMed]
- 57.Hunt MC, Tillander V, Alexson SEH. Regulation of peroxisomal lipid metabolism: The role of acyl-CoA and coenzyme A metabolizing enzymes. Biochimie. 2014;98:45–55. doi: 10.1016/j.biochi.2013.12.018. [DOI] [PubMed] [Google Scholar]
- 58.Brand MD, Esteves TC. Physiological functions of the mitochondrial uncoupling proteins UCP2 and UCP3. Cell Metab. 2005;2:85–93. doi: 10.1016/j.cmet.2005.06.002. [DOI] [PubMed] [Google Scholar]
- 59.Ježek P, Holendová B, Garlid KD, Jabůrek M. Mitochondrial uncoupling proteins: Subtle regulators of cellular redox signaling. Antioxidants Redox Signal. 2018;29:667–714. doi: 10.1089/ars.2017.7225. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 60.Christensen E, Grønn M, Hagve TA, Christophersen BO. Omega-oxidation of fatty acids studied in isolated liver cells. Biochim. Biophys. Acta. 1991;1081:167–173. doi: 10.1016/0005-2760(91)90022-A. [DOI] [PubMed] [Google Scholar]
- 61.Attignon EA, et al. Novel roles for AhR and ARNT in the regulation of alcohol dehydrogenases in human hepatic cells. Arch. Toxicol. 2017;91:313–324. doi: 10.1007/s00204-016-1700-4. [DOI] [PubMed] [Google Scholar]
- 62.Forgacs AL, Dere E, Angrish MM, Zacharewski TR. Comparative analysis of temporal and dose-dependent TCDD-elicited gene expression in human, mouse, and rat primary hepatocytes. Toxicol. Sci. 2013;133:54–66. doi: 10.1093/toxsci/kft028. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 63.Allali-Hassani A, Peralba JM, Martras S, Farrés J, Parés X. Retinoids, ω-hydroxyfatty acids and cytotoxic aldehydes as physiological substrates, and H2-receptor antagonists as pharmacological inhibitors, of human class IV alcohol dehydrogenase. FEBS Lett. 1998;426:362–366. doi: 10.1016/S0014-5793(98)00374-3. [DOI] [PubMed] [Google Scholar]
- 64.Alcock RE, Behnisch PA, Jones KC, Hagenmaier H. Dioxin-Like PCBs in the environment—Human exposure and the significance of sources. Chemosphere. 1998;37:1457–1472. doi: 10.1016/S0045-6535(98)00136-2. [DOI] [PubMed] [Google Scholar]
- 65.Päpke O. PCDD/PCDF: human background data for Germany, a 10-year experience. Environ. Health Perspect. 1998;106(Suppl):723–731. doi: 10.1289/ehp.106-1533397. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 66.Polyzos SA, Mantzoros CS. Making progress in nonalcoholic fatty liver disease (NAFLD) as we are transitioning from the era of NAFLD to dys-metabolism associated fatty liver disease (DAFLD) Metabolism. 2020;111S:154318. doi: 10.1016/j.metabol.2020.154318. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 67.Angrish MM, Mets BD, Jones AD, Zacharewski TR. Dietary fat is a lipid source in 2,3,7,8-Tetrachlorodibenzo-ρ-Dioxin (TCDD)-elicited hepatic steatosis in C57BL/6 mice. Toxicol. Sci. 2012;128:377–386. doi: 10.1093/toxsci/kfs155. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 68.Liu, Q. et al. A Quantitative HILIC-MS/MS assay of the metabolic response of Huh-7 cells exposed to 2,3,7,8-tetrachlorodibenzo-p-dioxin. Metabolites9, 118 (2019). [DOI] [PMC free article] [PubMed]
- 69.Zhang L, et al. Metabolomics reveals that aryl hydrocarbon receptor activation by environmental chemicals induces systemic metabolic dysfunction in mice. Environ. Sci. Technol. 2015;49:8067–8077. doi: 10.1021/acs.est.5b01389. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 70.Hotamisligil GS, Bernlohr DA. Metabolic functions of FABPs—Mechanisms and therapeutic implications. Nat. Rev. Endocrinol. 2015;11:592–605. doi: 10.1038/nrendo.2015.122. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 71.Neess D, Bek S, Engelsby H, Gallego SF, Færgeman NJ. Long-chain acyl-CoA esters in metabolism and signaling: Role of acyl-CoA binding proteins. Prog. Lipid Res. 2015;59:1–25. doi: 10.1016/j.plipres.2015.04.001. [DOI] [PubMed] [Google Scholar]
- 72.Mitchell GA, et al. Hereditary and acquired diseases of acyl-coenzyme A metabolism. Mol. Genet. Metab. 2008;94:4–15. doi: 10.1016/j.ymgme.2007.12.005. [DOI] [PubMed] [Google Scholar]
- 73.Knights KM. Role of hepatic fatty acid:coenzyme a ligases in the metabolism of xenobiotic carboxylic acids. Clin. Exp. Pharmacol. Physiol. 1998;25:776–782. doi: 10.1111/j.1440-1681.1998.tb02152.x. [DOI] [PubMed] [Google Scholar]
- 74.Liang Y, et al. Serum metabolic changes associated with dioxin exposure in a Chinese male cohort. Environ. Int. 2020;143:105984. doi: 10.1016/j.envint.2020.105984. [DOI] [PubMed] [Google Scholar]
- 75.Enooku K, et al. Altered serum acylcarnitine profile is associated with the status of nonalcoholic fatty liver disease (NAFLD) and NAFLD-related hepatocellular carcinoma. Sci. Rep. 2019;9:1–9. doi: 10.1038/s41598-019-47216-2. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 76.Binstock JF, Schulz H. Fatty Acid Oxidation Complex from Escherichia coli. Methods Enzymol. 1981;71:403–411. doi: 10.1016/0076-6879(81)71051-6. [DOI] [PubMed] [Google Scholar]
- 77.Martines ACMF, et al. Transcriptome analysis suggests a compensatory role of the cofactors coenzyme A and NAD+ in medium-chain acyl-CoA dehydrogenase knockout mice. Sci. Rep. 2019;9:1–11. doi: 10.1038/s41598-019-50758-0. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 78.Hardwick JP. Cytochrome P450 omega hydroxylase (CYP4) function in fatty acid metabolism and metabolic diseases. Biochem. Pharmacol. 2008;75:2263–2275. doi: 10.1016/j.bcp.2008.03.004. [DOI] [PubMed] [Google Scholar]
- 79.Wanders RJA, Komen J, Kemp S. Fatty acid omega-oxidation as a rescue pathway for fatty acid oxidation disorders in humans. FEBS J. 2011;278:182–194. doi: 10.1111/j.1742-4658.2010.07947.x. [DOI] [PubMed] [Google Scholar]
- 80.Reddy JK, Hashimoto T. Peroxisomal beta-oxidation and peroxisome proliferator-activated receptor alpha: An adaptive metabolic system. Annu. Rev. Nutr. 2001;21:193–230. doi: 10.1146/annurev.nutr.21.1.193. [DOI] [PubMed] [Google Scholar]
- 81.Shaban Z, et al. Down regulation of hepatic PPARα function by AhR ligand. J. Vet. Med. Sci. 2004;66:1377–1386. doi: 10.1292/jvms.66.1377. [DOI] [PubMed] [Google Scholar]
- 82.Westin MAK, Hunt MC, Alexson SEH. The identification of a succinyl-CoA thioesterase suggests a novel pathway for succinate production in peroxisomes. J. Biol. Chem. 2005;280:38125–38132. doi: 10.1074/jbc.M508479200. [DOI] [PubMed] [Google Scholar]
- 83.Wang D, et al. Human carboxylesterases: A comprehensive review. Acta Pharm. Sin. B. 2018;8:699–712. doi: 10.1016/j.apsb.2018.05.005. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 84.Birnbaum LS. Distribution and excretion of 2,3,7,8-tetrachlorodibenzo-p-dioxin in congenic strains of mice which differ at the Ah locus. Drug Metab. Dispos. 1986;14:34–40. [PubMed] [Google Scholar]
- 85.Wishart DS, et al. HMDB 40: The human metabolome database for 2018. Nucleic Acids Res. 2018;46:D608–D617. doi: 10.1093/nar/gkx1089. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 86.Haack TB, et al. Deficiency of ECHS1 causes mitochondrial encephalopathy with cardiac involvement. Ann. Clin. Transl. Neurol. 2015 doi: 10.1002/acn3.189. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 87.Fong JC, Schulz H. Purification and properties of pig heart crotonase and the presence of short chain and long chain enoyl coenzyme A hydratases in pig and guinea pig tissues. J. Biol. Chem. 1977;252:542–547. doi: 10.1016/S0021-9258(17)32751-5. [DOI] [PubMed] [Google Scholar]
- 88.Binder JX, et al. COMPARTMENTS: Unification and visualization of protein subcellular localization evidence. Database. 2014;2014:1–9. doi: 10.1093/database/bau012. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 89.Nault R, Doskey CM, Fader KA, Rockwell CE, Zacharewski T. Comparison of hepatic NRF2 and aryl hydrocarbon receptor binding in 2,3,7,8-tetrachlorodibenzo-p-dioxin–treated mice demonstrates NRF2-independent PKM2 induction. Mol. Pharmacol. 2018;94:876–884. doi: 10.1124/mol.118.112144. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 90.Eckel JE, Gennings C, Chinchilli VM, Burgoon LD, Zacharewski TR. Empirical bayes gene screening tool for time-course or dose-response microarray data. J. Biopharm. Stat. 2004;14:647–670. doi: 10.1081/BIP-200025656. [DOI] [PubMed] [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Data Availability Statement
Hepatic RNA-seq data sets were previously published9,10,89. Differentially expressed genes (|fold-change|≥ 1.5 and posterior probability (P1(t)) ≥ 0.8) were determined by empirical Bayes analysis90. Time course (GSE109863), dose response (GSE87519), and diurnal rhythmicity (GSE119780) sequencing data are available at the Gene Expression Omnibus. Diurnal rhythmicity was determined using JTK_CYCLE as previously described9. AHR ChIP-seq (GSE97634) and computationally identified putative dioxin response elements (pDREs, https://doi.org/10.7910/DVN/JASCVZ) data were previously published10. ChIP-seq analysis used a false discovery rate (FDR) ≤ 0.05. pDREs were considered functional with a matrix similarity score (MSS) ≥ 0.856 and associated with genes when located 10 kb upstream of the transcription start site (TSS) to the transcription end site (TES). Raw metabolomic data is deposited in the NIH Metabolomics Workbench (ST001379).