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It has been recently proposed that exposure to polychlorinated biphenyls (PCBs) is a risk factor to type 2 diabetes mellitus (DM2). We investigated this hypothesis using long-term in vivo PCB126 exposure to rats addressing metabolic, cellular and proteomic parameters. Male Wistar rats were exposed to PCB126 (0.1, 1 or 10μg/kg of body weight/day; for 15 days) or vehicle by intranasal instillation. Systemic alterations were quantified by body weight, insulin and glucose tolerance, and blood biochemical profile. Pancreatic toxicity was measured by inflammatory parameters, cell viability and cycle, free radical generation, and proteomic profile on islets of Langerhans. In vivo PCB126 exposure enhanced the body weight gain, impaired insulin sensitivity, reduced adipose tissue deposit, and elevated serum triglycerides, cholesterol, and insulin levels. Inflammatory parameters in the pancreas and cell morphology, viability and cycle were not altered in islets of Langerhans. Nevertheless, in vivo PCB126 exposure increased free radical generation and modified the expression of proteins related to oxidative stress on islets of Langerhans, which are indicative of early β-cell failure. Data herein obtained show that long-term in vivo PCB126 exposure through intranasal route induced alterations on islets of Langerhans related to early end points of DM2.
Over the last three decades, incidence of type 2 diabetes mellitus (DM2) has reached epidemic proportions worldwide1. Although excessive caloric consumption and sedentary lifestyle are well recognized risk factors for DM2, recent evidence has suggested that exposures to persistent organic pollutants (POPs) may contribute to the rising risk of metabolic disorders2,3. POPs make up a broad class of chemical organic lipophilic compounds of natural or anthropogenic origins that are resistant to the environmental degradation, including aldrin, dieldrin, dioxins, furans, and polychlorinated biphenyls (PCBs)4.
PCBs cover a class of 209 congeners widely employed in industrial processes until the late 1980s, when their production was banned. By then, large quantities of PCBs had been released into the environment worldwide, and high concentrations of PCBs have been detected in the water, air, food, animals, and even human milk5,6. According to Toxic Equivalency Factor (TEF), the PCB126 (3,3′,4,4′,5-pentachlorobiphenyl) is considered the most toxic PCB congener, once its biological effects are comparable to those evoked by 2,3,7,8-tetrachlorodibenzo-p-dioxin (TCDD; TEF=0.1)7. In this regard, studies have clearly showed that chronic PCB126 exposure causes several toxic effects, including cancer development and impairment of liver, lung, and cardiovascular functions7. PCB126, a co-planar or dioxin-like PCB agent, activates genomic pathways by binding and activating the cytoplasmatic aryl hydrocarbon receptor (AhR). The consequent agonist-AhR complex translocates into the nucleus and heterodimers with the AhR nuclear translocator (ARNT). The complex AhR:ARNT activates the promoters of genes containing xenobiotic response elements (XRE) that induce the transcription and expression of AhR target genes8.
Although diet continues to be an important source of PCB intoxication, studies have shown that inhalation is a relevant route of PCB exposure. Because of their physical-chemical characteristics, PCBs are dispersed in the air and soil and are also sorbed to particulate matter9. Moreover, the use of building materials containing PCBs has contributed to high levels of indoor air contamination. Indeed, the positive correlation of longer time in contaminated indoor areas and endogenous accumulation of PCB has been shown10,11,12. Despite these data, the inhalation route remains a neglected pathway of exposure, and studies addressing the health outcomes of inhaled PCBs exposure must be considered in risk assessment11. Recently, our group demonstrated that long-term in vivo PCB126 exposure by intranasal instillation into Wistar rats induced the expression of AhR in in the liver, lungs, kidneys, and adipose tissue, and PCB126 levels were found in the lungs and liver. Moreover, intranasal PCB 126 exposure affected the G protein coupled receptor (GPCR) signaling in circulating leukocytes of rats and consequently impaired innate immunological functions related to the host’s defense to infections13.
The role of PCB126 on metabolic disease is not fully described, but it nevertheless has been shown that in vivo PCB126 exposure induces alterations in lipid14,15 and glucose metabolism16 and evokes chronic inflammation and atrophy of exocrine pancreas17. However, to our knowledge, the toxicity of the inhalatory pathway of PCB126 exposure on endocrine pancreas, a pivotal tissue to regulation of glucose and lipid homeostasis, have not been investigated. Therefore, we characterized the effects of long-term in vivo PCB126 exposure via intranasal instillation on metabolic and cellular parameters of rats and investigated the toxic mechanism on islets of Langerhans. Data obtained showed evident metabolic alterations caused by PCB126 exposure, and that oxidative stress and alteration on protein profile expression on islets of Langerhans are early end points of PCB126 intoxication.
Vehicle or PCB126 exposed rats gained body weight from the 1st until the 15thday of exposures (Fig. 1a); nevertheless, the body weight gain was significantly higher in rats exposed to PCB126 (10μg/kg) compared to rats exposed to vehicle or to lower doses of PCB126 (0.1 or 1μg/kg; Fig. 1a,b). The gain of weight in PCB126 exposed rats was not associated to alterations in food intake and water consumption, once these parameters were similar between all experimental groups (Fig. S1). It is important to mention that the gain of weight was not detected in rats exposed to PCB180, a non-dioxin PCB, following the same protocol of exposure to PCB126 (Fig. S2). The exacerbated gain of weight detected in PCB126 exposed rats was also not dependent on adipose tissue accumulation, because PCB126 exposure evoked a significant reduction in the mass of periepididymal and retroperitoneal adipose tissue (Fig. 1c). Moreover, PCB126 exposure did not cause inflammation in the retroperitoneal adipose tissue, as it had no effect in the amount of tumor necrosis factor-α (TNF-α; Fig. 1d), and reduced the levels of interleukin-6 (IL-6; Fig. 1e) and nitrite (Fig. 1f), the main metabolite of nitric oxide (NO). On the other hand, the expression of GLUT4, the insulin-regulated glucose transporter, was markedly enhanced in retroperitoneal adipose tissue from rats exposed to the higher dose of PCB126 (Fig. 1g). Leptin levels on adipose tissues were not altered (Fig. 1h).
Although it has been shown that PCB126 causes liver toxicity by enhancing cytochrome P450 and decreasing glutathione levels via AhR binding18,19, our data show for the first time that in vivo PCB126 inhalatory exposure elevated levels of serum creatinine and gamma-glutamyl transpeptidase (GGT), and total protein in urine (Table 1).
Nevertheless, levels of aspartate aminotransferase and alanine aminotransferase were not altered by PCB126 intoxication (Table 1). Therefore, we infer that the schedule of in vivo PCB126 exposure was not intense enough to cause liver damage and we foresee that longer exposure and/or higher dose of PCB126 must be employed to induce severe hepatic injuries. Moreover, in vivo PCB126 exposure also induced a significant elevation of serum levels of triglycerides, cholesterol, and very low density lipoprotein (VLDL) compared to animals exposed to vehicle (Table 1).
Fasting glycaemia in rats exposed to PCB126 was compared to that in vehicle exposure animals (Table 1). Furthermore, the AUC of glucose tolerance test (GTT) was similar between the experimental groups (Fig. 2b), although we observed higher glycemic peak in rats exposed to PCB126 compared to vehicle five minutes after IV administration of glucose (Fig. 2a). In addition, in vivo PCB126 exposure significantly reduced insulin sensibility (Fig. 2c,d) and increased serum levels of insulin (Fig. 2e) compared with rats exposed to vehicle. It is noteworthy to mention that levels of insulin in naïve rats is similar to those observed in vehicle treated rats (0.15–0.18ng/mL).
In vivo PCB126 exposure evoked significant increase in protein expression of AhR on islets of Langerhans (Fig. 3a), but had no effect on insulin secretion (Fig. S4A), islets morphology (Fig. S4B), viability (Fig. S4C), or cell cycle (Fig. S4D). Nevertheless, in vivo PCB126 exposure evoked a significant exacerbation of peroxynitrite generation on islets of Langerhans (Fig. 3b,c) while having no effect on superoxide anion production (Fig. 3d,e). Ex vivo incubation of islets of Langerhans with different concentrations of glucose showed that at physiological glucose levels (11.4mM), the NO production was similar in islets collected from vehicle or PCB126 exposed rats; nevertheless, significant increases in NO levels in islets from rats exposed to PCB126 were detected when islets were cultured in high glucose medium (16.7mM) (Fig. 3f).
Only elevated NO levels were observed in pancreatic homogenates of rats exposed to PCB126 (Fig. 4a). IL-6 levels (Fig. 4b) and numbers of rolling (Fig. 4c) or adherent leukocytes (Fig. 4d) on pancreatic microcirculation were not altered by PCB126 exposure. Moreover, PCB126 exposure did not alter plasma cytokines interleukin 1 β (IL-1β), IL-6, or tumor necrosis factor (TNF-α) (Fig. S3).
Fresh islets of Langerhans samples from experimental groups were submitted to 2D electrophoresis (Fig. 5a). We identified 105 and 201 spots in the vehicle and PCB126 exposed group, respectively. After a quantitative analysis, a 1.4-fold change in protein expression was adopted as a cut-off to consider changes between groups statistically significant. We found that 22 pairings satisfied this condition. Matched spots are represented in Table 2. Overall, it is interesting to note that in vivo PCB126 exposure up-regulated 8 and down-regulated 14 proteins. To better understand the way in which they are engaged against the influence of the PCB126, the biochemical pathways of these proteins were evaluated using the software suite for functional analysis MetaCore® (Fig. 5b). Altered proteins on islets from rats exposed to PCB126 possibly are related to oxidative stress and failure of β-cells, namely, Heat Shock protein 90kDa (HSP90), Electron transfer flavoprotein subunit alpha (Alpha-ETF), 78kDa glucose-regulated protein (GRP78), nucleoside diphosphate kinase A and B (NDKA/NDKB), and ribonuclease inhibitor (Table 2 and Fig. 5b).
Although the current literature has suggested that exposure to PCBs may contribute to the genesis of DM22,3,20, the mechanisms responsible for the toxic effect have not been fully understood. Therefore, by using an intranasal long-term PCB126 exposure into rats, we showed systemic toxicity, by altering lipid and glucose metabolisms and oxidative stress on islets of Langerhans, the endocrine portion of pancreas. Moreover, PCB126 exposure modified the expression of proteins on islets of Langerhans, leading to a profile of proteins closely correlated to failure of pancreatic β-cells.
Obesity is one factor responsible for the genesis of DM2, and a positive correlation of POP exposures and obesity has been fully described in the contemporary literature21,22. Indeed, we here confirmed that PCB126 exposure induces gain of weight, but it was not associated with the enhanced retroperitoneal or periepididymal fat depots or to enhanced food and water intake. Indeed, levels of leptin in adipose tissue were not altered. Conversely, similar exposure to non-co-plannar PCB 180 did not lead to weight gain, which would be expected considering that PCB180 exposure is associated with obesity in humans23. It is noteworthy that both PCBs 126 or 180 were well absorbed by animals in our studies, because higher levels of PCB126 or PCB180 were found in different tissues of exposed animals, and PCB126 exposure induced AhR expression in different tissues, as liver, adipose tissue, kidney, and lungs13.
The gain of weight after PCB126 exposure may be due to hydric retention, as creatinine levels in the plasma and total proteins in urine were elevated after the PCB126 exposure. The in vivo renal toxicity caused by PCB126 is shown here for the first time, as only in vitro studies had already demonstrated the ability of PCBs, especially non-coplannar congeners, to induce apoptosis in cell kidney cultures24.
The physiological role of AhR in regulating body weight and insulin sensitivity, and mediating environmental toxicant-induced obesity, insulin resistance, and development of diabetes has been fully shown25,26. Nevertheless, the molecular mechanisms underlying the AhR activation on metabolic diseases are very complex, and the outcomes vary during the development of diseases. In this context, we previously showed that in vivo inhalatory PCB126 exposure enhanced AhR expression in the adipose tissues13, and here we suppose that both reductions on periepididimal and retroperitoneal fat depots detected in PCB126 exposed rats may be due to direct activation of AhR in the adipocytes. This hypothesis is based on recent data showing that AhR null mice exhibited increased fat mass when fed a standard, low or high fat diet27; transgenic mice with constitutively activated AhR present decreased adipose tissue deposits associated with elevation of peripheral fat mobilization28; and in vitro ligand-activated AhR inhibits the lipid synthesis, adipocyte differentiation, and secretion of adypocyte proliferating mediators14,29,30,31. On the other hand, AhR activation induces inflammation in adipose tissue, contributing to obesity27,28,32,33,34. PCB126 exposure by intranasal route did not induce secretion of inflammatory cytokines in the adipose tissue and plasma, excluding an apparent inflammatory state as a hallmark of PCB126 intoxication by intranasal route. Together, our data suggest that weight gain is not due pro-adipogenic actions of PCB126 and may reflect hydric retention by kidney toxicity. We suppose that longer exposure, higher dose or different via of administration may be required to evoke the gain of adipose tissue after PCB126 exposure, as mentioned previously in literature17.
Meanwhile, biochemical analysis of serum clearly showed the effects of PCB126 exposure on lipid and glucose metabolism, reinforcing the interference of PCBs on both gluconeogenesis and fatty acid oxidation in the liver, which precedes PCBs hepatic toxicity14,15,35,36. In this context, it is important to mention that elevated levels of serum GGT, as here induced by PCB126 exposure, have been also considered an early biomarker for development of DM237,38,39. Furthermore, PCB126 exposure up-regulated the expression of GLUT-4 in the retroperitoneal adipose tissue, which was accompanied by marked reduction of insulin sensibility and elevated levels of serum insulin. Taken together, data obtained show that in vivo PCB126 exposure induces insulin resistance and pre-diabetic state, and we infer that GLUT-4 up-regulation may be a compensatory effect in response to insulin resistance.
The pathophysiological hallmarks of DM2 consist of insulin resistance and β-cell dysfunction40. At early stages, β-cells compensate for insulin resistance by up-regulating the secretion of the hormone to maintain physiologic glycemic levels41. The in vivo PCB126 exposure enhanced serum insulin levels, suggesting that normal glucose tolerance in our experimental model results from up-regulation of insulin secretion by β-cells. Moreover, in vivo PCB126 exposure up-regulated AhR expression on isolated islets of Langerhans, showing that endocrine pancreas is also a target of PCB126 intoxication. To our knowledge, the up-expression of AhR by POPs on islets of Langerhans is shown here for the first time. Long-term stimulation of islets of Langerhans can lead to β-cell failure, which may result from inadequate expansion of mass or failure of existing β-cells to respond to glucose41. Our data excluded the PCB126 actions on proliferation and viability of islets of Langerhans; nevertheless, PCB126 exposure enhanced peroxynitrite production by islets, an end-point of oxidative stress. Although both superoxide and NO levels were similar between the groups at basal conditions, in vivo PCB126 exposure exacerbated NO production in islets cultured in high glucose medium. Indeed, the NO levels were also elevated on pancreatic homogenates from rats exposed to PCB126. This may be an important mechanism of PCB126 actions, since NO inhibits insulin secretion induced by glucose42 and chronic exposure to high levels of NO promotes β-cell death43.
Increasing evidence has suggested that a subclinical inflammation is involved in impairment of β-cell function in the course of DM244,45. Indeed, it has previously been reported that in vivo PCB126 exposure induces chronic inflammation on exocrine pancreas17. Conversely, we did not find any signal of inflammation in the pancreas because the interaction of leukocytes into endothelial cells of pancreatic microcirculation and the production of cytokines were not modified by PCB126 exposure. It is noteworthy that leukocyte interaction into pancreas microcirculation is a hallmark to initial phases of pancreas inflammation. Intravital microscopy is a useful technique to identify the in vivo role of this phenomenon to evolution of the inflammatory response46,47.
Proteomic analysis has largely contributed to the knowledge of the phenotype of cells in different conditions48, and we here employed this experimental tool to better detect earlier end-point of in vivo PCB126 exposure. Data obtained highlighted 22 different proteins between the experimental groups, 8 of which were up-regulated and 14 of which were down-regulated by PCB126 exposure. Among the up-regulated proteins altered by PCB126 exposure, HSP90, Alpha-ETF, and GRP78 are related to oxidative stress. In this regard, a positive association was previously reported between DM2 and the up-regulation of HSP9049 on islets of Langerhans, since the overexpression of HSP90 on islets has been associated with elevation of β-cell ATP-sensitive potassium (KATP) channel expression50, enhanced insulin secretion, and promotion of glucokinase activation, the rate-limiting enzyme in glycolysis51. The up-regulation of Alpha-ETF also seems to be beneficial in response to PCB126 exposure, since it was previously reported that its down-regulation reduces respiratory chain in islets from an animal model of DM2, leading to mitochondrial dysfunction and oxidative stress52. On the other hand, the up-regulation of GRP78 probably represents a deleterious effect of PCB126 exposure. Previous studies have reported a positive association between up-regulation of GRP78 and reduction of insulin secretion, reticulum endoplasmic stress53, and development of DM254. In the same way, the down-regulation of both NDKA/B and ribonuclease inhibitor possibly represents an early sign of β-cell damage in response to PCB126 exposure. In this respect, previous studies reported the down-regulation of NDKA/B in islets of Langerhans from a rat model of DM255 and in insulin-secreting β-cells exposed to high glucose conditions56, suggesting that NDKA/B expression is reduced in islets submitted to glucolipotoxic conditions. Similarly, the down-regulation of ribonuclease inhibitor probably favors the exacerbation of free radical production on islets, since it has been demonstrated that this protein plays a key role as a defensive system against oxidative stress57. Taken together, the proteomic analysis suggests that up-regulation of HSP90 and Alpha-ETF possibly occurred to compensate for the insulin resistance induced by PCB126 exposure and played a protective role against oxidative stress. On the other hand, the up-regulation of GRP78 and the down-regulation of NDKA/B and ribonuclease inhibitor can represent early signs of β-cell failure induced by PCB126 exposure.
In conclusion, our study presents the first findings indicating that long-term in vivo PCB126 exposure through intranasal route induces toxic systemic effects associated with early end-points of DM2, including insulin resistance, hypertriglyceridemia, hyperinsulinemia, and oxidative stress on islets of Langerhans. A proteomic approach revealed that in vivo PCB126 exposure regulated the expression of some proteins (HSP90 and Alpha-ETF) to compensate for the insulin resistance and protect against oxidative stress, while others (GRP78, NDKA/B and ribonuclease inhibitor) may represent an early sign of β-cell failure. Taken together, our study highlights the influence of environmental pollutants on progression/development of DM2 and can help guide the adoption of new health public policies.
All reagents were purchased from Sigma-Aldrich (St. Louis, MO, USA) unless otherwise stated. PCB126 (purity 99%) was purchased from AccuStandard (New Haven, CT, USA) and antibodies from Abcam (Cambridge, MA, USA). Reagents for cell culture were obtained from Vitrocell (Campinas, SP, Brazil), and ketamine and xylazine were purchased from Vetbrands (Jacarei, SP, Brazil). Annexin-V FITC-conjugated antibody, IL-1β, IL-6, and TNF-α ELISA kits were purchased from BD Pharmingen (San Diego, CA, USA). Only ELISA insulin kit was purchased from Millipore (Billerica, MA, USA). Chemiluminescence detection solution was purchased from BioRad (CA, USA). BCA kit was obtained from Pierce® (Walthan, MA, USA).
Male Wistar rats (180-220g) were purchased from the animal facility of Chemistry Institute at the University of São Paulo. The animals were fed a standard pellet diet and water, ad libitum. All procedures were performed according to the Brazilian Society for the Science of Laboratory Animals (SBCAL) and approved by the Institutional Animal Care and Use Committee from Faculty of Pharmaceutical Sciences – University of Sao Paulo (Protocol number 315).
For 15 days, once a day, the animals were anaesthetized with ketamine/xylazine solution (80:8mg/kg respectively, intraperitoneally, i.p.) and exposed to PCB126 0.1; 1 or 10μg/kg of body weight by intranasal instillation, corresponding to 0.0001, 0.001, and 0.01ppm, respectively. Control animals received the equivalent volume of vehicle (saline solution containing 0.5% of dimethyl sulfoxide — DMSO). During exposure, the body weight, food intake, and water consumption were daily measured. Five hours after the last vehicle or PCB126 exposures, animals were anesthetized with pentobarbital sodium (40mg/kg; i.p.) instead ketamine/xylazine, since previous studies have shown that pentobarbital has less pronounced effects on basal glycaemia and other metabolic parameters58. Then, animals were euthanized and samples (blood, adipose tissue, pancreas, and liver) were collected.
Basal glycaemia in conscious animals was detected in a sample of blood collected from the tail vein using a glucometer (Accu-check Active®, Roche, Switzerland). Blood samples to determine other biochemical parameters were collected from abdominal aortae of anaesthetized animals (pentobarbital sodium, i.p.), and the serum was isolated by centrifugation (1500g, for 10min, at 4°C). Insulin was quantified by ELISA, while cholesterol, triglycerides, alanine aminotransferase (ALT), aspartate aminotransferase (AST), gamma-glutamyl transpeptidase (GGT), urea, and creatinine were quantified by enzymatic method in automated equipment (Labmax240®, Labtest, Brazil).
For both insulin tolerance test (ITT) and glucose tolerance test (GTT), glycaemia was measured with a blood sample obtained from the tail. For ITT, insulin (0.75U/kg) was intravenously (IV) administered and glycaemia was measured over time (0, 4, 8, 12, and 16min), as previously described59. The fall of glucose levels in the first 15minutes after i.v. insulin administration is a function of insulin-stimulated glucose uptake by tissues and its ability to suppress glucose output by the liver (shorter ITT measurement). For this reason, we carried out a shorter version of ITT, since the systemic counter-regulatory hormone response to hypoglycemia, which can interfere with insulin sensitivity, occurs only after 20minutes of the insulin injection (longer ITT measurement)60. The coefficient of glucose disappearance rate (KITT) was calculated as the slope of linear regression of glucose concentrations determined after insulin administration. GTT was administered as 375mg/mL of glucose (0.2mL/100g of body weight) through IV injection, and glycaemia was measured over time (0, 5, 10, 20, 30, and 60min). The index of glycaemia decay (mg/dL×min−1)×100 was calculated as the area under the curve (AUC).
After anesthesia (pentobarbital sodium; 40mg/kg; i.p.), blood was collected, followed by euthanasia (exsanguination). The common bile duct was cannulated, and the pancreas was inflated with digestion solution Hanks balanced salt solution (HBSS) containing 0.7mg/mL type V collagenase. Then, the pancreas was excised, picked, transferred to a Falcon® tube (50mL) containing 10mL of digestion solution, and incubated at 37°C for 25min. After incubation, samples were centrifuged (800rpm, 3min), followed by purification of islets with Histopaque®-1077 gradient. Subsequently, islets were examined using a dissecting microscope and were hand-picked.
Freshly isolated islets were incubated (30min at 37oC) with HBSS containing fluorescent probes to detect either peroxynitrite (2,7-dichlorodihydrofluorescein diacetate—DCFH-DA, 30μM) or superoxide anion (dihydroethidium—DHE, 10μM). After incubation, images of islets were obtained using a fluorescent microscope (Axiovert 100M, Carl Zeiss, Germany). Fluorescence intensity (optical density) was determined by using the software AxioVision Release 4.8 and expressed as arbitrary units (a.u.). For nitric oxide (NO) measurement, islets (40 islets/rat) were cultured (24hr at 37oC, 5% CO2) in RPMI medium containing 10% FBS and physiological (11.1mM) or high (16.5mM) levels of glucose. The NO2− levels were determined by performing the Griess reaction assay. The values of peroxynitrite, superoxide anion, and NO production by islets obtained from PCB126 exposed rats were expressed as percentage (%) in relationship to islets isolated from vehicle exposed rats (100%).
The western blot for detection of AhR and GLUT-4 on islets of Langerhans or adipose tissue, respectively, was carried out as previously reported13. Briefly, samples were suspended in RIPPA buffer containing inhibitor protease cocktail, sonicated, and centrifuged (12.000rpm at 4°C for 20min). Total protein content was determined by Bradford’s method, and samples were mixed to Laemmli’s sample buffer. Samples (50μg) were loaded in SDS-PAGE (10%), submitted to electrophoresis, and transferred to a nitrocellulose membrane in a transfer apparatus (Bio-Rad Laboratories, CA, USA). Membranes were incubated in blocking buffer (TBS-T — 20mM Tris; 137mM NaCl; 0.02% Tween 20 — containing 5% nonfat dry milk) followed by incubation (overnight at 4°C) with monoclonal antibodies anti-AhR (1:1000) or GLUT-4 (1:500). Sequentially, membranes were incubated with peroxidase-conjugated secondary antibody (1:10000). Membranes were incubated with chemiluminescence detection solution, and immunoreactive bands were detected by autoradiography exposition. Band intensities were determined by optical densitometry using the software Image J (NIH, USA). The expression of actin was used as loading control.
For determination of leukocyte-endothelium interaction on pancreatic microcirculation, animals were anesthetized with ketamine/xylazine solution (80:8mg/kg respectively, intramuscular injection - IM), and a portion of the pancreas was surgically exteriorized to allow observation of the microcirculation. Animals remained on a special board thermostatically controlled at 37°C, and the preparation was washed with Ringer-Locke solution (pH 7.4 at 37°C) containing 1% gelatin. Images of second-order venules (14–18μm of diameter) were obtained using an intravital microscopy system (Axioplan II, Carl-Zeiss, Germany) and captured with a video camera (AxioCam HRc, Carl-Zeiss). The number of adherent leukocytes (those that kept still for at least 30sec) per 100μm venule length and of the rolling leukocytes was monitored under basal conditions for 10min.
To determine inflammatory mediators, pancreas and retroperitoneal adipose tissue were homogenized and suspended in RIPPA buffer containing protease inhibitors. NO levels were determined by Griess reaction, while IL-6 and TNF-α levels were determined by ELISA commercial kit.
Isolated islets (2500, pool of 10 animals) were suspended in RIPPA buffer, homogenized, and centrifuged (16000g, 30min, 4°C). The supernatant was collected and concentrated in SpeedVac (Concentrator 5301, Eppendorf®, Hamburg, Germany), resuspended in PBS containing protease inhibitor cocktail. The protein determination was performed using the BCA kit.
Proteins (350μg) were precipitated with 1 volume of 20% (weight/volume - wt/vol) trichloroacetic acid, 0.07% (volume/volume - vol/vol) β-mercaptoethanol in acetone (−20°C, 60min), and washed 3 times with 0.07% (vol/vol) β-mercaptoethanol in acetone. Pellets were resuspended in rehydration buffer (2% Pharmalyte pH 3–10 in DeStreak Rehydration Solution, GE Healthcare).
Immobiline/IPG strips (pH 3–10, 7cm—GE Healthcare) were rehydrated overnight in rehydration buffer containing protein samples (250μg/strip). Strips were subjected to IEF on Ettan IPGphor 3 apparatus (GE Healthcare) under the following protocol: 300V/200Vh; 300–1000V/200 to 300Vh; 1000V to 5000V/300–4000 Vh e 5000V/1250Vh.
After IEF, strips were incubated in equilibration buffer Urea 6M, Tris-HCl pH 8.8 75mM, 30% (vol/vol) Glycerol, 2% (wt/vol) SDS containing 1.5% (wt/vol) DTT in the first step and 2.5% (wt/vol) iodoacetamide during the second step (15min per step). The SDS-PAGE was carried out using 12.5% polyacrylamide gels (10×8cm) on a SE 260 mini-vertical gel electrophoresis unit (Amersham Biosciences) under the following protocol: 80V/30min+200V/75min. Then, gels were fixed with 50% (vol/vol) methanol, 10% (vol/vol) acetic acid solution, and stained with Coomassie Blue R 350 (GE Healthcare). Stained gels were scanned using an ImageScanner III scanner and LabScan software (GE Healthcare).
Images were analyzed using Image Master Platinum software (v.7.0, GE Healthcare). Spots were detected automatically without filtering, and gel patterns were matched between groups. At least a 1.4-fold change in the relative abundance between matched spots was considered significant, and these protein spots were submitted to trypsin digestion and analysis by liquid chromatography tandem mass spectrometry (LC-MS/MS).
Protein spots were washed (water and 50% acetonitrile) and then reduced (50mM ammonium bicarbonate containing 10mM DTT) for 30min at 56°C and then alkylated (55mM iodoacetamide) for 30min. Excess iodoacetamide was neutralized using 5mM DTT. After washes with 50mM ammonium bicarbonate, proteins were digested overnight with sequencing grade modified trypsin (enzyme/protein ratio 1:50) at 37°C. The digest was evaporated to dryness in a SpeedVac and then kept at −80°C until analysis.
Each sample was suspended in 0.05% trifluoroacetic acid containing 5% acetonitrile and incubated for 10min at 37°C under stirring (1400rpm). The chromatographic analysis were performed by in a system composed by a nanoACQUITY UPLC (Waters) system coupled with a hybrid Quadrupole-Orbitrap mass spectrometer (Q-Exactive, Thermo Fisher Scientific) equipped with a nano-electrospray ionization source and operating at positive mode. Samples were loaded onto a PST C18 nanoACQUITY Trap column (180μm × 20mm) with flow rate set to 15μL/min of 0.1% (vol/vol) trifluoroacetic acid during 3minutes. Analytic separation of the peptides was performed using a nanoACQUITY UPLC HSS C18 Column (1.8μm, 75μm×150mm) and a two-step linear gradient was used starting from 2% (vol/vol) dimethyl sulfoxide (DMSO) and 0.1% (vol/vol) formic acid and increasing to 5% (vol/vol) DMSO, 25% (vol/vol) acetonitrile, and 0.1% (vol/vol) formic acid over 45minutes; followed by a 30-minute gradient of 5% (vol/vol) DMSO, 40% (vol/vol) acetonitrile, and 0.1% (vol/vol) formic acid. For each cycle, one full MS scan (m/z 390–1,650) was acquired in the Orbitrap at a resolution of 70,000 at m/z 200 with an automatic gain control target of 3e6. Each full scan was followed by the quadrupole selection and isolation of the 12 most intense ions at a window m/z 4, which were dissociated through higher-energy collisional dissociation, using normalized collision energy of 26 (MS/MS). The product ions were analyzed by the Orbitrap at a resolution of 17,500 at m/z 200 with an automatic gain control target of 1e5. Ions with an unassigned, 1, and >8 charges were rejected, and dynamic exclusion was set to 30sec. Data were analyzed by MaxQuant software (Max-Planck Institute of Biochemistry) and compared with a database Rattus norvegicus (rat)—UniProtKB— taxonomy 10116 (http://www.uniprot.org/taxonomy/10116). Proteins were considered identified when at least two peptides were identified, of which at least one was uniquely assigned to the respective sequence. The False Discovery Rate (FDR) was adjusted to 1%61. The Maximum Missed Cleavage (MMC) considered was 2, and the amino acid isoleucine was taken as leucine. Finally, among the list of generated proteins were classified those with lower Posterior Error Probability (PEP), highest sequencing coverage rates, and higher ion intensity. The identified proteins were analyzed using MetaCore™ software (Thomson Reuters) to assess the biochemical processes and metabolic pathways in which the most expressed proteins would be involved.
Results represent mean±SE (n=5–6 per group). Comparison between three or more groups were analyzed by one- or two-way ANOVA as appropriate, with post hoc comparisons using the Tukey or Bonferroni test, respectively. Comparisons between two groups were analyzed by student’s t-test. In all cases, P<0.05 was considered as statistically significant.
How to cite this article: Loiola, R. A. et al. Long-term in vivo polychlorinated biphenyl 126 exposure induces oxidative stress and alters proteomic profile on islets of Langerhans. Sci. Rep. 6, 27882; doi: 10.1038/srep27882 (2016).
The authors thank Fundação de Amparo a Pesquisa do Estado de São Paulo (FAPESP - grant #2012/02994-0) and Coordenação de Aperfeiçoamento de Pessoal de Nível Superior (CAPES) for financial support. R.A.L. and F.M.A. were post-doctoral fellow of CAPES (AUX-PE-PNPD: grant #2371/2009), A.L.B.S. was FAPESP PhD fellow (grant #2011/09677-8), S.H.P.F. and E.P. are fellow of the Conselho Nacional de Pesquisa e Tecnologia (CNPq).
Author Contributions R.A.L. and F.M.D.A. performed in vitro analysis of islets of Langerhans, and contributed to LC-MS/MS analysis and manuscript writing; A.L.B.S. exposed animals to PCB126 and performed in vivo experiments; C.C.D. and W.S.C. exposed animals to PCB180 and performed experiments; S.F.D.P.R. performed intravital microscopy experiments; K.H.M.C., V.M.C. and E.P. contributed to the LC-MS/MS analysis; and S.H.P.F. conceived the study and wrote the manuscript.