Abstract
Emerging evidence supports a role for environmental chemical exposure in the pathology of non-alcoholic fatty liver disease (NAFLD), a disease process tightly linked to increased activity of the blood coagulation cascade. Exposure of C57BL/6 mice to the persistent environmental contaminant 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD) recapitulates features of the NAFLD spectrum, including steatosis, hepatic injury, inflammation, and fibrosis. We assessed coagulation cascade activation, and determined the role of the thrombin receptor protease activated receptor-1 (PAR-1) in experimental TCDD-elicited NAFLD. Chronic exposure to TCDD (30 µg/kg every 4 days for 28 days) was associated with intrahepatic coagulation, indicated by increased plasma thrombin-antithrombin levels and hepatic fibrin(ogen) deposition. PAR-1 deficiency diminished TCDD-elicited body weight loss and relative liver weight was reduced in TCDD-exposed PAR-1−/− mice compared with TCDD-exposed wild-type mice. PAR-1 deficiency did not affect TCDD-induced hepatic steatosis or hepatocellular injury, as indicated by serum alanine aminotransferase activity. Despite a lack of effect on these 2 features of NAFLD pathology, PAR-1 deficiency was associated with a reduction in hepatic inflammation evident in liver histopathology, and reflected by a reduction in serum levels of the proinflammatory cytokine interleukin-6. Moreover, TCDD-driven hepatic collagen deposition was markedly reduced in PAR-1-deficient mice. These results indicate that experimental TCDD-elicited steatohepatitis is associated with coagulation cascade activation and PAR-1-driven hepatic inflammation and fibrosis.
Keywords: TCDD, Coagulation, PAR-1, Fibrosis, NAFLD.
The worldwide incidence of non-alcoholic fatty liver disease (NAFLD) is continuously increasing, affecting over 35% of the US population alone (Ford et al., 2010; Vanni et al., 2010). Several factors, including genetics, diet, lifestyle, and age, have been implicated in the development of NAFLD and associated metabolic disorders including diabetes, dyslipidemia, and cardiovascular disease (Pitsavos et al., 2006; Unger and Scherer, 2010; Unger et al., 2010). Recent studies also suggest exposure to environmental contaminants including persistent organic pollutants and organochlorines contributes to metabolic disease development (Cave et al., 2010; Lee et al., 2006, 2007; Taylor et al., 2013). For example, 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD), the prototypical aryl hydrocarbon receptor (AhR) ligand, has been shown to contribute to the progression of NAFLD spectrum from simple, reversible steatosis, to steatohepatitis and early signs of fibrosis in mice (Kopec et al., 2013; Nault et al., 2015a; Pierre et al., 2014). Notably, all of these pathologies are elements of the NAFLD spectrum in humans. Activation of the AhR, a basic helix–loop–helix transcription factor, results in the dissociation of chaperone proteins, nuclear translocation, and dimerization with the AhR nuclear translocator (ARNT). The TCDD–AhR–ARNT complex then binds to dioxin response elements, and elicits changes in gene expression. Studies in AhR null mice strongly indicate that the impact of TCDD on NAFLD features, such as hepatic lipid accumulation, is driven by AhR activation (Fernandez-Salguero et al., 1996).
Development of liver diseases such as the NAFLD has been associated with tissue factor (TF)-dependent activation of the blood coagulation cascade (Kassel et al., 2011; Owens et al., 2012). Coagulation cascade activation results in generation of the serine protease thrombin, which cleaves soluble fibrinogen leading to deposition of insoluble fibrin polymers in the liver (Kassel et al., 2011). Thrombin also triggers intracellular signaling in numerous hepatic nonparenchymal cells (eg, macrophages, stellate cells) through activation of the protease activated receptor-1 (PAR-1; F2r). Thrombin activation of PAR-1 has been shown to drive multiple NAFLD-associated pathologies, including hepatic lipid accumulation, inflammation and hepatocellular injury, depending on the experimental setting (Kassel et al., 2011, 2012; Kopec et al., 2014; Luyendyk et al., 2010). Notably, PAR-1 activation promotes stellate cell activation in vitro (Fiorucci et al., 2004; Gaca et al., 2002), and hepatic fibrosis is reduced in PAR-1−/− mice challenged chronically with hepatocellular or biliary toxicants (Sullivan et al., 2010). Collectively, these studies indicate a central role for coagulation and thrombin signaling across the spectrum of NAFLD/NASH pathologies.
Repeated TCDD exposure in mice has been shown to promote the development of steatosis, steatohepatitis, and fibrosis (Fader et al., 2015; Nault et al., 2015a; Pierre et al., 2014). However, no studies have examined whether the progression of liver pathologies elicited by TCDD is coupled to coagulation cascade activation, and the role of PAR-1 in this experimental context is unknown. Consequently, we determined whether coagulation cascade activation accompanies TCDD-elicited hepatotoxicity and utilizing PAR-1−/− mice tested the hypothesis that progression of NAFLD-associated pathologies involves the thrombin receptor PAR-1.
MATERIALS AND METHODS
Animals
Age-matched male PAR-1−/− (Connolly et al., 1997) and PAR-1+/+ mice, both on an N8 C57BL/6J background, were obtained by homozygous breeding as previously described (Luyendyk et al., 2011). Mice used in the study were between 12 and 16 weeks of age and studies were performed in duplicate. All mice were housed in Innovive cages (Innovive Inc., San Diego, California) with alpha-dri bedding (Shepherd Specialty Papers, Milford, New Jersey) at 30-40% humidity and a 12 h light/dark cycle. Animals were fed ad libitum (Harlan Teklad 22/5 Rodent Diet 8940, Madison, Wisconsin) and had free access to Aquavive acidified water (Innovive Inc.). In both studies, mice were gavaged every 4 days (d) for 28 d (a total of 7 exposures) with sesame oil vehicle (Sigma-Aldrich, St. Louis, Missouri) or 30 µg/kg TCDD (AccuStandard, New Haven, Connecticut; 99.8% purity) in sesame oil with a volume of 100 µL. Doses were chosen based on previous studies suggesting that these potentially reflect the lifetime exposure to TCDD and related compounds in humans (Nault et al., 2016). 28 d following the initial dose, animals were anesthetized using isoflurane, plasma, and serum were collected from the caudal vena cava using a syringe with and without sodium citrate (0.38% final), respectively, and stored at –80 °C. Livers were collected, weighed, and frozen in liquid nitrogen and stored at –80 °C or fixed in 10% neutral buffered formalin (Sigma-Aldrich) for histological processing. All procedures were approved by the Michigan State University All-University Committee on Animal Use and Care.
Serum clinical chemistry
Serum alanine aminotransferase (ALT) activity was determined using a commercially available reagent (Infinity ALT/GPT; Thermo Fisher, Waltham, Massachusetts). Thrombin–antithrombin (TAT) levels in the plasma were determined using a commercial enzyme-linked immunosorbent assay kit (Enzygnost TAT micro; Siemens Healthcare Diagnostics, Deerfield, Illinois). Assays were performed using an infinite M200 plate reader (Tecan, Durham, North Carolina). Serum cytokine levels were determined using the Meso Scale V-PLEX Proinflammatory panel kit and Sector S 600 (Meso Scale Discovery, Rockville, Maryland).
Histopathology
All histological processing and staining were performed at the Michigan State University Investigative Histopathology Laboratory (https://humanpathology.natsci.msu.edu/; last accessed September 14, 2016) (Nault et al., 2015a). Briefly, frozen livers were sectioned at 6 µm and stained with an Oil Red O (ORO) solution and Gill 2 hematoxylin counterstain. Formalin-fixed paraffin-embedded sections were stained for collagen using PicroSirius Red (PSR), hematoxylin & eosin (H&E), and immunohistochemically for fibrin(ogen) as described previously (Joshi et al., 2016). In brief, fibrin(ogen) was stained using a polyclonal rabbit anti-human fibrin(ogen) antibody (Dako, Carpinteria, California) at a dilution of 1:200, and detected using biotinylated goat anti-rabbit IgG with Vectastain R.T.U. Elite ABC reagent and Vector Nova Red Peroxidase substrate (Vector Laboratories, Burlingame, California). Tissues were then counterstained with Gill 2 hematoxylin. Slides were digitized using an Olympus Virtual Slide System (VS110) at 20x magnification and images were sampled using the Visiomorph Microimager (Visiopharm, Denmark). Quantitation of histological features was performed using an in-house developed tool (Nault et al., 2015a). Semi-quantitative severity scoring of H&E-stained liver sections was performed by a board certified veterinary pathologist experienced in hepatic toxicologic pathology of laboratory rodents. The pathologist examined the slides without previous knowledge of the individual exposure history of the mice. Criteria used for scoring the severity of the individual microscopic lesions (ie, hepatocellular vacuolization, cellular inflammation, and bile duct hyperplasia) were (1) less than 10% of tissue affected (minimal), (2) 10–33% of tissue affected (mild), (3) 33–66% of tissue affected, and (4) greater than 66% of tissue affected (marked).
RNA extraction and gene expression analysis
Total RNA was extracted from 100 mg liver sections in 1.3 mL TRIzol (Life Technologies, Carlsbad, California), with an additional phenol:chloroform extraction, as previously described (Nault et al., 2015b). RNA was stored in RNA storage solution (Life Technologies) and assessed for purity by Nanodrop (A260/A280 ratio; Thermo Scientific). Synthesis of cDNA was performed using 1 µg of RNA, High Capacity cDNA Reverse Transcription kit (Applied Biosystems), and MyCycler thermal cycler (Bio-Rad). Quantitative real-time PCR (qPCR) was performed using SYBR Green master mix (Bio-Rad) and a CFX96 Real-Time PCR Detection System (Bio-Rad). The expression of each gene was normalized to the geometric mean of Actb, Gapdh, and Hprt and differential expression was calculated using the 2−ΔΔCT method. Primer sequences are provided in Supplementary Table S1.
Statistics
Statistical analyses were performed using R version 3.2.2 (R Foundation for Statistical Computing) and consisted of Student’s t-test for comparison of 2 groups. A 2-way ANOVA with treatment and genotype as factors was used for evaluation of genotype and treatment effects followed by Student–Newman–Keul’s post-hoc test. Differences were considered significant when P ≤ .05. Data from 2 independent studies were combined for body and liver weights, as well as ALT measurements. All other figures represent values for one independent study.
RESULTS
TCDD Exposure Activates the Coagulation Cascade
Activation of the coagulation cascade is coupled to the development and progression of NAFLD pathologies (Kassel et al., 2011; Owens et al., 2012). Notably, repeated exposure to TCDD in wild-type mice significantly increased plasma thrombin–antithrombin (TAT) levels, a stable biomarker of coagulation cascade activation (Fig. 1A). Consistent with increased thrombin proteolytic activity (Fig. 1B), TCDD-exposed mice had a significant increase in the amount of intrahepatic fibrin(ogen), largely located in the hepatic portal areas (Fig. 1C). These results indicate that repeated exposure to TCDD increases intrahepatic coagulation in mice.
PAR-1 Deficiency Does Not Reduce TCDD-Elicited Hepatotoxicity
Coagulation-driven steatohepatitis is mediated in part through activation of PAR-1 (Kassel et al., 2011; Owens et al., 2012). We have previously observed that PAR-1 expression is induced in livers of mice exposed repeatedly to TCDD (Nault et al., 2015b). To determine the role of PAR-1 in TCDD-elicited liver pathology, we utilized PAR-1−/− mice. Overall, unexpected mortalities were observed only in the wild-type TCDD treated animals (5/16), whereas no mortality occurred in PAR-1−/− mice. Noting protection from overt TCDD toxicity, TCDD-mediated weight loss was significantly reduced in PAR-1−/− mice compared with wild-type mice (Fig. 2A). The weight loss was observed beginning at ∼15 days (4 exposures) in 2 independent experiments (Supplementary Fig. S1). Concomitantly, an increase in relative liver weight (liver weight/body weight ratio) was observed in TCDD-treated animals although to a lesser extent in PAR-1−/− mice increasing 1.6- and 1.4-fold in PAR-1+/+ and PAR-1−/− mice, respectively (Fig. 2B). Absolute liver weights increased similarly (Supplementary Fig. S2). Induction of hepatic Cyp1a1 expression was similar in wild-type and PAR-1−/− mice suggesting equivalent AhR activation in both genotypes (Fig. 2C). Of importance, serum ALT activity, a marker of hepatocellular injury, increased in TCDD-exposed wild-type mice (Fig. 2D). This increase was similar in TCDD-exposed PAR-1−/− mice (Fig. 2D), indicating equivalent hepatotoxicity in both genotypes as a result of repeated TCDD exposure. Increases in ALT were observed in the absence of evidence of hepatocyte necrosis by histological evaluation.
Impact of PAR-1 Deficiency on the Development of NAFLD
Evaluation of hepatic lipid accumulation was performed by quantification of Oil Red O-stained liver sections (Fig. 3A), an approach shown previously to correlate with hepatic triglyceride levels (Levene et al., 2012). Wild-type and PAR-1−/− mice developed panacinar micro- and macrovesicular steatosis of similar severity (Fig. 3A and B). Examination of H&E-stained liver sections identified TCDD-induced periportal inflammation characterized by a mixed inflammatory cell response composed of neutrophilic granulocytes and mononuclear leukocytes (lymphocytes and monocytes) and occasional eosinophils in both wild-type and PAR-1−/− mice exposed to TCDD. Markedly less periportal inflammation and bile duct proliferation was observed in PAR-1−/− mice (Fig. 4 and Table 1). Interestingly, the increase in plasma TAT level was also attenuated in TCDD-exposed PAR-1−/− mice (3.4 ± 0.5 ng/ml [TCDD] vs 1.4 ± 0.3 ng/ml [vehicle]) compared with PAR-1+/+ mice (7.4 ± 2.1 ng/ml [TCDD] vs 1.6 ± 0.5 ng/ml [vehicle]), consistent with known crosstalk between coagulation and inflammation pathways (Esmon, 2005). Plasma levels of IFN-γ, IL-10, IL-6, and TNFα increased in both wild-type and PAR-1−/− mice exposed to TCDD (Fig. 5). Notably, IFN-γ and IL-6 in TCDD-treated PAR-1−/− mice were increased and reduced, respectively, compared with their wild-type counterparts (Fig. 5A and C). Specifically, IFN-γ increased to 1.75 ± 0.06 and 3.81 ± 0.40 pg/mL whereas IL-6 increased to 71.21 ± 11.30 and only 32.53 ± 5.01 pg/mL in wild-type and PAR-1−/− mice, respectively, revealing dichotomous effects on these cytokines.
TABLE 1.
TCDD (µg/kg) | Genotype | Vacuolizationa | Inflammationa | Bile Duct Proliferationa |
---|---|---|---|---|
0 | PAR-1+/+ | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 |
30 | 4.0 ± 0.0 | 3.6 ± 0.2 | 2.6 ± 0.6 | |
0 | PAR-1−/− | 0.0 ± 0.0 | 0.0 ± 0.0 | 0.0 ± 0.0 |
30 | 3.0 ± 0.3 | 2.2 ± 0.2 | 0.4 ± 0.4 |
H&E stained liver sections were semi-quantitatively scored from 0 to 4; 0—no findings, 1—minimal, 2—mild, 3—moderate, 4—marked. A total of 5 slides were evaluated for each group with the exception of vehicle PAR-1−/− mice in which 4 slides were evaluated. Scoring criteria are described in the materials and methods. Values represent mean +/− SEM.
Development of periportal fibrosis as indicated by excess collagen deposition was determined by qualitative and quantitative assessment of PSR-stained liver sections. In agreement with previous studies (Nault et al., 2015a; Pierre et al., 2014), TCDD treatment significantly increased collagen deposition in the liver (Fig. 6A and B). The TCDD-induced fibrosis in wild-type mice that was associated with the periportal inflammation and bile duct hyperplasia, often extended from the periportal regions to the liver capsule. Notably, collagen deposition was significantly reduced in PAR-1−/− mice, and was largely confined to portal regions (Fig. 6A and B). Concomitant with the reduction in collagen deposition there was a dramatic reduction in the TCDD-driven bile duct proliferation in PAR-1−/− mice (Table 1).
DISCUSSION
Activation of the coagulation cascade is tightly linked to the development of NAFLD-associated pathologies, particularly steatohepatitis and fibrosis (Kassel et al., 2011; Owens et al., 2012). Here, we found that subchronic TCDD exposure is also coupled to increased intrahepatic coagulation, marked by increased thrombin generation and hepatic fibrin(ogen) deposition. Notably, the pattern of fibrin(ogen) deposition in TCDD-exposed mice was distinct from that observed in other models of liver toxicity and disease, wherein the pattern of deposition is often coupled to the site of injury (Kopec and Luyendyk, 2016). A role for fibrin(ogen) deposits in TCDD-elicited pathology cannot be ruled out, as additional studies are required to define the role of fibrin(ogen) deposits in this experimental context. Our prior identification of increased PAR-1 mRNA expression in TCDD-exposed mice suggested a potential role for thrombin signaling in TCDD-elicited pathology. Indeed, here we report for the first time that PAR-1 activation plays a central role in hepatic fibrosis driven by chronic TCDD exposure.
TCDD is a well-known hepatotoxicant and chronic exposure has been reported to result in weight loss (wasting) and increased relative liver weight. Notably, both of these changes were diminished in TCDD-exposed PAR-1−/− mice, indicating that PAR-1 plays an important role in TCDD toxicity. To the best of our knowledge, this is the first report of thrombin signaling driving systemic toxicity of an environmentally relevant xenobiotic. PAR-1 is expressed by numerous cells in multiple tissues and the precise cellular source of PAR-1 in control of TCDD-mediated weight loss is a question for future study. Although PAR-1 plays a central role in the activation of human platelets, it is not expressed by mouse platelets (Kahn et al., 1999). Thus, whereas TCDD has been shown to impact platelet activation (Lindsey et al., 2014), our observations in PAR-1−/− mice cannot be ascribed to thrombin-mediated platelet activation. Notably, hepatic induction of classic AhR target genes (eg, Cyp1a1) in TCDD-exposed mice was not affected by PAR-1 deficiency, implying that protection from disease is not likely due to failed AhR activation.
Analogous to PAR-1−/− mice on a methionine-choline-deficient (MCD) diet-fed mice, PAR-1 deficiency had no effect on the development of hepatic steatosis in TCDD-exposed mice. Notably, this contrasts findings in models of NAFLD driven by diets high in fat, where PAR-1 deficiency largely prevents hepatic steatosis in the absence of effects on body weight (Kassel et al., 2011). Although the basis for this difference is not clear, it is possible that TCDD (and MCD challenge alike) alter normal metabolic function in liver leading to excess hepatic lipid accumulation irrespective of caloric intake. In contrast to MCD diet-challenged mice, PAR-1 deficiency had no effect on hepatocellular injury caused by TCDD as indicated by similarly increased serum ALT levels in TCDD-treated wild-type and PAR-1−/− mice. Thus, whereas PAR-1 driven hepatocellular injury is disconnected from hepatic steatosis in MCD diet-challenged mice, it appears that lipid accumulation and hepatocellular injury are PAR-1-independent in TCDD-exposed mice.
In agreement with the role of PAR-1 in promoting hepatic inflammation in experimental MCD diet-driven steatohepatitis, serum levels of the proinflammatory cytokine IL-6 were reduced in TCDD-exposed PAR-1−/− mice. Similarly, TCDD exposure increased serum TNFα levels in wild-type mice, but did not increase these levels in PAR-1−/− mice. This was coupled with a reduction in hepatic inflammation as assessed by histopathology. Interestingly, this is a potential mechanistic disconnect between hepatic injury and the inflammatory response in TCDD-exposed mice, as serum ALT levels were not reduced in PAR-1−/− mice. Characterization of the precise changes in hepatic cytokine expression and inflammatory cell accumulation driven by PAR-1 in TCDD-exposed, particularly in the context of cell-specific changes in oxidative stress, should form the next step of investigation in this experimental setting. However, it is intriguing to note that cytokine levels were not unilaterally reduced in PAR-1−/− mice. For example, serum IFN-γ expression increased in TCDD-exposed PAR-1−/− mice compared with wild-type mice. Although its role is certainly context-dependent, in some experimental settings IFN-γ is noted to have antifibrotic activity through induction of stellate cell quiescence and apoptosis (Weng et al., 2007). Additional studies are required to define the cellular source of IFN-γ and its role in the TCDD-induced steatohepatitis.
Interestingly, our studies show a robust increase in hepatic fibrosis in mice exposed chronically to TCDD, and identify PAR-1 signaling as an important contributor to hepatic fibrosis in this setting. Of importance, the reduction in hepatic fibrosis in PAR-1−/− mice could not be attributed to a reduction in hepatic steatosis or hepatocellular injury. This is analogous to fibrosis driven by chronic exposure to another hepatotoxic xenobiotic, carbon tetrachloride (CCl4). In that model, thrombin signaling does not impact CCl4 hepatotoxicity, but nevertheless contributes to the progression of fibrosis (Rullier et al., 2008). Cell culture studies indicate thrombin has direct profibrogenic effects on stellate cells in vitro, suggesting that local thrombin generation driven by TCDD hepatotoxicity could directly promote fibrogenesis by activation of PAR-1 on stellate cells. However, to date, there are no studies definitively identifying a profibrogenic role for PAR-1 expressed by stellate cells in vivo. Indeed, an equally intriguing possibility is that PAR-1 drives hepatic inflammation via macrophage activation, and that this indirectly promotes stellate cell activation. Indeed, bone-marrow transplant studies suggest a role for hematopoietic cell PAR-1 in CCl4-induced hepatic fibrosis (Kallis et al., 2014). Alternatively, the reduction in fibrosis may be coupled to the observed reduction in bile duct proliferation in PAR-1-deficient mice. TCDD exposure was previously reported to cause bile duct proliferation (Vos et al., 1974), although the mechanism remains elusive. Our results suggest that TCDD-mediated bile duct proliferation may be driven indirectly by thrombin activation of PAR-1. Indeed, previous studies demonstrated that PAR-1 signaling on bile duct epithelial cells contributes to experimental xenobiotic-induced bile duct fibrosis by enhancing αVβ6-mediated TGFβ activation (Sullivan et al., 2010, 2011).
In summary, we demonstrate that following chronic TCDD exposure, activation of the coagulation cascade drives hepatic inflammation and fibrosis, independent of hepatic lipid accumulation and injury, through a PAR-1-dependent mechanism. These studies are an important example of changes reactive to tissue injury, such as coagulation, driving penultimate pathologies associated with chronic chemical exposure. The observation that PAR-1 deficiency decreases inflammation and fibrosis without affecting steatosis is significant, insofar as it suggests a mechanism of disease progression apparently independent of underlying lipid metabolism. Comparison of these results to the role of PAR-1 in other experimental settings of NAFLD/NASH begins to reveal how exposure to TCDD and other AhR ligands may impact the mechanistic progression of NAFLD in humans.
SUPPLEMENTARY DATA
Supplementary data are available online at http://toxsci.oxfordjournals.org/.
ACKNOWLEDGMENTS
The authors would like to thank Holly Cline-Fedewa for her assistance in the management of the mouse colony.
FUNDING
National Institutes of Health (NIH R01 ES017537 to J.P.L.); National Institute of Environmental Health Sciences Superfund Research Program (NIEHS SRP P42ES04911) and AgBioResearch at MSU (to T.R.Z.); MSU Barnett Rosenberg Endowed Assistantship and Integrative Training in the Pharmacological Sciences grant (NIH 5T32GM092715 to R.N.). Canadian Institutes of Health Research (CIHR) Doctoral Foreign Study Award (DFS-140386 to K.A.F.).
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