Endocrine disrupting chemicals: Friend or foe to brown and beige adipose tissue?

The effects of Endocrine Disrupting Chemicals (EDCs) on the current obesity epidemic is a growing field of interest. Numerous EDCs have shown the potential to alter energy metabolism, which may increase the risk of obesity, in part, through direct actions on adipose tissue. While white adipose tissue has historically been the primary focus of this work, evidence of the EDC-induced disruption of brown and beige adipose tissues continues to build. Both brown and beige fat are thermogenic adipose depots rich in mitochondria that dispense heat when activated. Due to these properties, brown and beige fat are implicated in metabolic diseases such as obesity, diabetes, and cachexia. This review delves into the current literature of different EDCs, including bisphenols, dioxins, air pollutants, phthalates, and phytochemicals. The possible implications that these EDCs have on thermogenic adipose tissues are covered. This review also introduces the possibility of using brown and beige fat as a therapeutic target organ by taking advantage of some of the properties of EDCs. Collectively, we provide a comprehensive discussion of the evidence of EDC disruption in white, brown, and beige fat and highlight gaps worthy of further exploration.

Propiconazole increases reactive oxygen species levels in mouse hepatic cells in culture and in mouse liver by a cytochrome P450 enzyme mediated process.

Propiconazole induces hepatocellular carcinomas and hepatocellular adenomas in mice and promotes liver tumors in rats. Transcriptional, proteomic, metabolomic and biochemical studies of hepatic tissues from mice treated with propiconazole under the conditions of the chronic bioassay indicated that propiconazole induced oxidative stress. Here we sought to identify the source of the reactive oxygen species (ROS) induced by propiconazole using both AML12 immortalized mouse hepatocytes in culture and liver tissues from mice. We also sought to further characterize the nature and effects of ROS formation induced by propiconazole treatment in mouse liver. ROS was induced in AML12 cells by propiconazole as measured by fluorescence detection and its formation was ameliorated by N-acetylcysteine. Propiconazole induced glutathione-S-transferase (GSTα) protein levels and increased the levels of thiobarbituric acid reactive substances (TBARS) in AML12 cells. The TBARS levels were decreased by diphenylene iodonium chloride (DPIC), a cytochrome P450 (CYP) reductase inhibitor revealing the role of CYPs in ROS generation. It has been previously reported that Cyp2b and Cyp3a proteins were induced in mouse liver by propiconazole and that Cyp2b and Cyp3a proteins undergo uncoupling of their CYP catalytic cycle releasing ROS. Therefore, salicylic acid hydroxylation was used as probe for ROS formation using microsomes from mice treated with propiconazole. These studies showed that levels of 2,3-dihydroxybenzoic acid (an ROS derived metabolite) were decreased by ketoconazole, melatonin and DPIC. In vivo, propiconazole increased hepatic malondialdehyde levels and GSTα protein levels and had no effect on hepatic catalase or superoxide dismutase activities. Based on these observations we conclude that propiconazole induces ROS in mouse liver by increasing CYP protein levels leading to increased ROS levels. Our data also suggest that propiconazole induces the hydroxyl radical as a major ROS form.

Chloral hydrate decreases gap junction communication in rat liver epithelial cells.

Gap junction communication (GJC) is involved in controlling cell proliferation and differentiation. Alterations in GJC are associated with carcinogenesis, but the mechanisms involved are unknown. Chloral hydrate (CH), a by-product of chlorine disinfection of water, is carcinogenic in mice, and we demonstrated that CH reduced GJC in a rat liver epithelial cell line (Clone 9). To examine the mechanism(s) by which CH inhibits GJC, Clone 9 cells treated with CH were examined using Western blot, real-time polymerase chain reaction, immunocytochemical, and dye-communication techniques. Treatment with CH (0.1­5 mM for 24 h) resulted in a dose-dependent inhibition of GJC as measured by Lucifer yellow dye transfer. Western blot analysis demonstrated expression of connexin (Cx) 43 and 26 in control cells and reduced expression of Cx 43 but not Cx 26 protein from 0.1 to 1 mM CH. CH treatment from 2.5 to 5 mM caused an apparent increase in expression of both connexins that was concomitant with a reduction in mRNA expression for both connexins. Similarly, with immunocytochemistry, a dose-dependent decrease in Cx 43 staining at sites of cell­cell contact was apparent in CH (0.5­5 mM)-treated cultures, whereas no Cx 26 staining was observed. Thus, Clone 9 cells contain two types of connexins but only one type of plasma membrane channel. Understanding of the regulation of connexin may shed light on mechanisms responsible for inhibition of GJC by chemical carcinogens.

Impact of life stage and duration of exposure on arsenic-induced proliferative lesions and neoplasia in C3H mice.

Epidemiological studies suggest that chronic exposure to inorganic arsenic is associated with cancer of the skin, urinary bladder and lung as well as the kidney and liver. Previous experimental studies have demonstrated increased incidence of liver, lung, ovary, and uterine tumors in mice exposed to 85 ppm (approximately 8 mg/kg) inorganic arsenic during gestation. To further characterize age susceptibility to arsenic carcinogenesis we administered 85 ppm inorganic arsenic in drinking water to C3H mice during gestation, prior to pubescence and post-pubescence to compare proliferative lesion and tumor outcomes over a one-year exposure period. Inorganic arsenic significantly increased the incidence of hyperplasia in urinary bladder (48%) and oviduct (36%) in female mice exposed prior to pubescence (beginning on postnatal day 21 and extending through one year) compared to control mice (19 and 5%, respectively). Arsenic also increased the incidence of hyperplasia in urinary bladder (28%) of female mice continuously exposed to arsenic (beginning on gestation day 8 and extending though one year) compared to gestation only exposed mice (0%). In contrast, inorganic arsenic significantly decreased the incidence of tumors in liver (0%) and adrenal glands (0%) of male mice continuously exposed from gestation through one year, as compared to levels in control (30 and 65%, respectively) and gestation only (33 and 55%, respectively) exposed mice. Together, these results suggest that continuous inorganic arsenic exposure at 85 ppm from gestation through one year increases the incidence and severity of urogenital proliferative lesions in female mice and decreases the incidence of liver and adrenal tumors in male mice. The paradoxical nature of these effects may be related to altered lipid metabolism, the effective dose in each target organ, and/or the shorter one-year observational period.

Genotoxicity and metabolism of the source-water contaminant 1,1-dichloropropene: activation by GSTT1-1 and structure-activity considerations.

1,1-Dichloropropene (1,1-DCPe) is a contaminant of some source waters used to make drinking water. Because of this and the fact that no toxicological data were available for this compound, which is structurally similar to the rodent carcinogen 1,3-dichloropropene (1,3-DCPe), 1,1-DCPe was placed on the Contaminant Candidate List of the US Environmental Protection Agency. Consequently, we have performed a hazard characterization of 1,1-DCPe by evaluating its mutagenicity in the Salmonella assay and its DNA damaging (comet assay) and apoptotic (caspase assay) activities in human lymphoblastoid cells. In Salmonella, 1,1-DCPe was not mutagenic in strains TA98, TA100, TA1535, or TA104 +/-S9 mix. However, it was clearly mutagenic in strain RSJ100, which expresses the rat GSTT1-1 gene. 1,1-DCPe did not induce DNA damage in GSTT1-1-deficient human lymphoblastoid cells, and it induced apoptosis in these cells only at 5 mM. Consistent with its mutagenesis in RSJ100, 1,1-DCPe reacted with glutathione (GSH) in vitro, suggesting an addition-elimination mechanism to account for the detected GSH conjugate. 1,1-DCPe was approximately 5000 times more mutagenic than its ethene congener 1,1-dichloroethylene (1,1-DCE or vinylidene chloride). Neither 1,1-DCE nor 1,3-DCPe showed enhanced mutagenicity in strain RSJ100, indicating a lack of activation of these congeners by GSTT1-1. Thus, 1,1-DCPe is a base-substitution mutagen requiring activation by GSTT1-1, possibly involving the production of a reactive episulfonium ion. This bioactivation mechanism of 1,1-DCPe is different from that of its congeners 1,1-DCE and 1,3-DCPe. The presence of 1,1-DCPe in source waters could pose an ecological or human health risk. Occurrence data for 1,1-DCPe in finished drinking water are needed to estimate human exposure to, and possible health risks from, this mutagenic compound.