Butylated hydroxyanisole isomers induce distinct adipogenesis in 3T3-L1 cells

https://doi.org/10.1016/j.jhazmat.2019.120794Get rights and content

Highlights

  • 3-BHA promoted adipogenic differentiation in 3T3-L1 cells, while 2-BHA had no effect.

  • 3-BHA increased lipid deposition in the differentiated adipocytes together with the upregulation of phenotypic biomarkers.

  • 3-BHA interfered the early molecular events in 3T3-L1 during the first four differentiation days.

  • 3-BHA enhanced adipogenic effect was independent of its direct binding to PPARγ.

  • Foodborne BHA exposure could potentially be involved in the increasing incidence of obesity.

Abstract

Butylated hydroxyanisole (BHA) isomers, as the widely used anthropogenic antioxidants in food, have been revealed to induce endocrine disrupting effects, while the mechanism how BHA isomers regulate the lipogenic differentiation remains to be elucidated. Using 3T3-L1 differentiation model, the effects of BHA isomers, including 2-tert-butyl-4-hydroxyanisole (2-BHA), 3-tert-butyl-4-hydroxyanisole (3-BHA) and their mixture (BHA), on adipogenesis were tested. The results showed that 3-BHA and BHA promoted adipocyte differentiation and enhanced the cellular lipid accumulation through the regulation of the transcriptional and protein levels of the adipogenetic biomarkers, while 2-BHA had no effect. The effective window for 3-BHA induced lipogenesis was the first four days during 3T3-L1 differentiation. BHA isomers showed no binding affinities for peroxisome proliferator activated receptor γ (PPARγ). Instead, the upstream of PPARγ signaling pathway, i.e. the phosphorylation of cAMP-response element binding protein (CREB), upregulation of CAAT/enhancer-binding proteins β (C/EBPβ) and elevated cell proliferation during postconfluent mitosis stage were induced by 3-BHA exposure. Altogether, this study revealed the adipogenic effect of 3-BHA through interference with the upstream events of the PPARγ signaling pathway. The authorized usage of BHA as food additives and its occurrence in human sera can potentially contribute to the incidence of obesity, which is of high concern.

Introduction

Butylated hydroxyanisole (BHA), a synthetic monophenolic antioxidant, has two isomers, 2-tert-butyl-4-hydroxyanisole (2-BHA) and 3-tert-butyl-4-hydroxyanisole (3-BHA), according to the site of tert-butyl group on the benzene ring (Figure S1). The commercial product is a mixture, typically consisting of 10% 2-BHA and 90% 3-BHA. Considering its superior properties in preventing lipid oxidation, BHA has been authorized for its usage in food industry since late 1950s to delay deterioration, rancidity and discoloration of oils, fats and lipid-containing foods during processing, packing and storage, thus extending their shelf-lives [1,2]. The wide usage of BHA potentially results in substantial releases into the environment. Subsequently, BHA was detected in various environmental media, like municipal sewage sludge, surface water and commercially farmed fish [[3], [4], [5], [6], [7], [8]]. Due to all sorts of unintended exposures like other reported synthetic phenolic antioxidants (SPAs), BHA contributed to prevalent human burden in population at large [9]. The extensive environmental occurrence of BHA and the potential human exposure suggested the high importance of its biosafety evaluation.

The accumulating data has been gathered for the biological effects of BHA from diverse aspects in recent years. Some studies revealed that BHA exerted beneficial effects, regarding its anti-tumor effects [[10], [11], [12], [13]], potentially being a promise in clinic therapy. Nevertheless, the toxicological studies revealed that BHA was genotoxic [14,15], and could cause adverse effects towards developmental and reproductive systems [[16], [17], [18]]. The studies on the endocrine disrupting effects showed that BHA could exert estrogenic or anti-estrogenic activities [19,20]. Steroidogenesis assay indicated that BHA significantly induced estrogen secretion, thus perturbing the steroid hormone hemostasis in vivo [21]. Considering the fact that endocrine disrupting chemicals (EDCs) can contribute to the etiology of obesity and high fat diet is commonly involved in this pathology [22], whether BHA, a potential endocrine disruptor abundant in lipid-containing foods, might perturb adipogenesis and induce obesity development was worthy of being studied. What’s more, previous studies mainly reported the toxicological effects of BHA mixture, further exploration on the specific differences in two BHA isomer-induced effects was thus needed.

Adipose tissue, a dynamic organ primarily composed of adipocytes, plays a crucial role in lipid metabolism, whole-body insulin sensitivity and systemic energy homeostasis. Its dysfunction can cause health risks, including obesity and the associated metabolic abnormalities, such as, insulin resistance, type 2 diabetes, cardiovascular disease or hypertension [23,24]. A growing body of epidemic evidence has revealed the steadily increasing incidence of obesity or overweight around the world over the last several decades, especially for children [25]. The roles of EDCs have now been recognized in the mediation of adipose physiology and energy metabolism [26,27], besides lifestyle changes. A cluster of EDCs, such as tributyltin (TBT), bisphenol A (BPA) and flame retardants, have been shown to alter adipogenesis and predispose individuals to gain weight, thus being considered as environmental obesogens [[28], [29], [30]]. The adipose tissue is likely a critical target for obesogens [31], and 3T3-L1 cell differentiation model has been well established for the screening of environmental obesogens [32,33]. The enhanced lipid accumulation observed in BHA exposed Crypthecodinium cohnii [34] and its affinity for fatty tissues [35] suggested the possibility of this compound as an obesogen. Due to the lack of evidences showing that BHA isomers might perturb adipogenesis in mamals, testing their effects on 3T3-L1 cell differentiation would be helpful to reveal their potential risks in inducing human obesity from the prevalent food additive uasge.

The present study firstly evaluated the effects of BHA isomers on adipogenesis using 3T3-L1 confluent cell differentiation. The findings on BHA-induced perturbation in adipogenesis would be helpful for guiding the sound control of this chemical’s usage in food industries.

Section snippets

Chemicals

The chemicals, including 2-BHA (> 98.0%), commercial BHA (≥ 98.5%, consisting of 9% 2-BHA and 90% 3-BHA), and rosiglitazone (Rosi, ≥ 98.0%), were purchased from Sigma (St. Louis, MO, USA). 3-BHA (> 98.0%) was bought from Tokyo Chemical Industry (TCI, Tokyo, Japan). The stock solutions of 50 mM 2-BHA, 3-BHA, BHA and 20 mM Rosi were prepared in dimethyl sulfoxide (DMSO, Sigma), and stored in darkness at 4 °C.

Adipogenic differentiation of 3T3-L1

The culture of 3T3-L1 preadipocytes (passage 4, the Cell Resource Center, Peking Union

The effects of BHA isomers on the adipogenesis of 3T3-L1

To test whether BHA isomers influenced adipogenesis, the lipid accumulation was evaluated using Oil red O staining in 3T3-L1 cells with chemical treatments during their adipogenesis. The results in Fig. 1A revealed that a few adipocytes were positively stained by Oil red O in MDI group, showing limited amounts of adipocytes naturally formed upon the induction of MDI [40]. In contrast, 2 μM Rosi, a PPARγ agonist, strongly induced the adipogenesis of 3T3-L1, as evidenced by the substantial

Discussion

Obesity, a well-recognized public health issue, is growing around the world and presents a societal burden for governments and individuals [44]. The sustained increases in the average midlife weights over the past several decades suggested that animals possibly face a similar problem [45]. Apart from excess caloric food intake and insufficient physical activities, the environmental obesogens are considered to be the potential primary culprit, perturbing the lipid homeostasis and causing

Acknowledgements

This work was financially supported by Major International (Regional) Joint Project (21461142001), National Natural Science Foundation of China (21876195, 21621064), Chinese Academy of Sciences (14040302, QYZDJ-SSW-DQC017), and Sanming Project of Medicine in Shenzhen (SZSM201811070).

References (66)

  • M. de Cock et al.

    Obesogenic effects of endocrine disruptors, what do we know from animal and human studies?

    Environ. Int.

    (2014)
  • S.M. Regnier et al.

    Adipocytes under assault: environmental disruption of adipose physiology

    Biochim. Biophys. Acta Mol. Basis Dis.

    (2014)
  • K. Zebisch et al.

    Protocol for effective differentiation of 3T3-L1 cells to adipocytes

    Anal. Biochem.

    (2012)
  • K.J. Livak et al.

    Analysis of relative gene expression data using real-time quantitative PCR and the 2−ΔΔCT method

    Methods

    (2001)
  • F. Wilfling et al.

    Lipid droplet biogenesis

    Curr. Opin. Cell Biol.

    (2014)
  • M. Bouaboula et al.

    Anandamide induced PPARgamma transcriptional activation and 3T3-L1 preadipocyte differentiation

    Eur. J. Pharmacol.

    (2005)
  • R. Siersbaek et al.

    Transcriptional networks and chromatin remodeling controlling adipogenesis

    Trends Endocrinol. Metab.

    (2012)
  • J.M. Ntambi et al.

    Adipocyte differentiation and gene expression

    J. Nutr.

    (2000)
  • J. Zhai et al.

    Different mechanisms of cis-9,trans-11- and trans-10,cis-12-conjugated linoleic acid affecting lipid metabolism in 3T3-L1 cells

    J. Nutr. Biochem.

    (2010)
  • C. Taxvig et al.

    Differential effects of environmental chemicals and food contaminants on adipogenesis, biomarker release and PPARγ activation

    Mol. Cell. Endocrinol.

    (2012)
  • B. Saad et al.

    Determination of synthetic phenolic antioxidants in food items using reversed-phase HPLC

    Food Chem.

    (2007)
  • C. Li et al.

    Synthetic phenolic antioxidants and their major metabolites in human fingernail

    Environ. Res.

    (2019)
  • W. Wang et al.

    Quantitative identification of and exposure to synthetic phenolic antioxidants, including butylated hydroxytoluene, in urine

    Environ. Int.

    (2019)
  • M.A. Soliman et al.

    Human pharmaceuticals, antioxidants, and plasticizers in wastewater treatment plant and water reclamation plant effluents

    Water Environ. Res.

    (2007)
  • R. Liu et al.

    Occurrence of synthetic phenolic antioxidants and major metabolites in municipal sewage sludge in China

    Environ. Sci. Technol.

    (2015)
  • W. Wang et al.

    Synthetic phenolic antioxidants and their metabolites in indoor dust from homes and microenvironments

    Environ. Sci. Technol.

    (2016)
  • A.K. Lundebye et al.

    Levels of synthetic antioxidants (ethoxyquin, butylated hydroxytoluene and butylated hydroxyanisole) in fish feed and commercially farmed fish

    Food Addit. Contam. Part A Chem.

    (2010)
  • R. Liu et al.

    Synthetic phenolic antioxidants and transformation products in human sera from United States donors

    Environ. Sci. Technol. Lett.

    (2018)
  • S. Ansar et al.

    Antioxidant and nephroprotective potential of butylated hydroxyanisole against ferric nitrilotriacetate-induced oxidative stress and early tumor events

    Hum. Exp. Toxicol.

    (2016)
  • B. Singh et al.

    Antioxidant butylated hydroxyanisole inhibits estrogen-induced breast carcinogenesis in female ACI rats

    J. Biochem. Mol. Toxicol.

    (2009)
  • Y. Zhang et al.

    Butylated hydroxyanisole blocks the occurrence of tumor associated macrophages in tobacco smoke carcinogen-induced lung tumorigenesis

    Cancers

    (2013)
  • X. Liang et al.

    Adverse effect of sub-choronic exposure to benzo(a)pyrene and protective effect of butylated hydroxyanisole on learing and memory ability in male Sprague-Dawley rat

    J. Toxicol. Sci.

    (2014)
  • S. Kashanian et al.

    In vitro study of calf thymus DNA interaction with butylated hydroxyanisole

    DNA Cell Biol.

    (2009)
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