Volume Density Of Peroxisomes Research Articles

Silencing of PPARαBb mRNA in brown trout primary hepatocytes: effects on molecular and morphological targets under the influence of an estrogen and a PPARα agonist.

The crosstalk between peroxisome proliferator-activated receptor α (PPARα) and estrogenic pathways are shared from fish to humans. Salmonid fish had an additional genome duplication, and two PPARα isoforms (PPARαBa and PPARαBb) were previously identified. Since a negative regulation between estrogen signaling and PPARα was described, a post-transcriptional gene silencing for PPARαBb was designed in primary brown trout hepatocytes. The aims of the study were to: (i) decipher the effects of PPARαBb knock-down on peroxisome morphology and on mRNA expression of potential target genes, and (ii) to assess the cross-interferences caused by an estrogenic compound (17α-ethinylestradiol - EE2) and a PPARα agonist (Wy-14,643 - Wy) using the established knock-down model. A knock-down efficiency of 70% was achieved for PPARαBb and its silencing significantly reduced the volume density of peroxisomes, but did not alter mRNA levels of the studied genes. Exposure to Wy did not change peroxisome morphology or mRNA expression, but under silencing conditions Wy rescued the volume density of peroxisomes to control levels, and increased acyl-coenzyme A oxidase 1-3l (Acox1-3l) mRNA. Exposure to EE2 caused a reduction of peroxisome volume density, but under silencing conditions this effect was abolished and ApoA1 mRNA level was diminished. The morphological alterations of peroxisomes by WY and EE2 demonstrated that obtained results are PPARαBb dependent, and suggest the regulation of unknown downstream targets of PPARαBb. In summary, PPARαBb is involved in the control of peroxisome size and/or number, which opens future opportunities to explore its regulation and molecular targets.

Sex-steroids and hypolipidemic chemicals impacts on brown trout lipid and peroxisome signaling — Molecular, biochemical and morphological insights

Lipid metabolism involves complex pathways, which are regulated in a similar way across vertebrates. Hormonal and hypolipidemic deregulations cause lipid imbalance from fish to humans, but the underlying mechanisms are far from understood. This study explores the potential of using juvenile brown trout to evaluate the in vivo interferences caused by estrogenic (17α-ethinylestradiol – EE2), androgenic (testosterone – T), and hypolipidemic (clofibrate – CLF) compounds in lipidic and/or peroxisomal pathways. Studied endpoints were from blood/plasma biochemistry, plasma fatty acid profile, ultrastructure of hepatocytes and abundance of their peroxisomes to mRNA expression in the liver. Both T and CLF caused minimal effects when compared to EE2. Estrogenized fish had significantly higher hepatosomatic indexes, increased triglycerides and very-low density lipoproteins (VLDL) in plasma, compared with solvent control. Morphologically, EE2 fish showed increased lipid droplets in hepatocytes, and EE2 and T reduced volume density of peroxisomes in relation to the hepatic parenchyma. Polyunsaturated fatty acids (PUFA) in plasma, namely n−3 PUFA, increased with EE2. EE2 animals had increased mRNA levels of vitellogenin A (VtgA), estrogen receptor alpha (ERα), peroxisome proliferator-activated receptor alpha (PPARα), PPARαBa and acyl-CoA long chain synthetase 1 (Acsl1), while ERβ-1, acyl-CoA oxidase 1–3I (Acox1–3I), Acox3, PPARγ, catalase (Cat), urate oxidase (Uox), fatty acid binding protein 1 (Fabp1) and apolipoprotein AI (ApoAI) were down-regulated. In summary, in vivo EE2 exposure altered lipid metabolism and peroxisome dynamics in brown trout, namely by changing the mRNA levels of several genes. Our model can be used to study possible organism-level impacts, viz. in gonadogenesis.

Peroxisomal alterations in Alzheimer’s disease

In Alzheimer’s disease (AD), lipid alterations are present early during disease progression. As some of these alterations point towards a peroxisomal dysfunction, we investigated peroxisomes in human postmortem brains obtained from the cohort-based, longitudinal Vienna-Transdanube Aging (VITA) study. Based on the neuropathological Braak staging for AD on one hemisphere, the patients were grouped into three cohorts of increasing severity (stages I–II, III–IV, and V–VI, respectively). Lipid analyses of cortical regions from the other hemisphere revealed accumulation of C22:0 and very long-chain fatty acids (VLCFA, C24:0 and C26:0), all substrates for peroxisomal β-oxidation, in cases with stages V–VI pathology compared with those modestly affected (stages I–II). Conversely, the level of plasmalogens, which need intact peroxisomes for their biosynthesis, was decreased in severely affected tissues, in agreement with a peroxisomal dysfunction. In addition, the peroxisomal volume density was increased in the soma of neurons in gyrus frontalis at advanced AD stages. Confocal laser microscopy demonstrated a loss of peroxisomes in neuronal processes with abnormally phosphorylated tau protein, implicating impaired trafficking as the cause of altered peroxisomal distribution. Besides the original Braak staging, the study design allowed a direct correlation between the biochemical findings and the amount of neurofibrillary tangles (NFT) and neuritic plaques, quantified in adjacent tissue sections. Interestingly, the decrease in plasmalogens and the increase in VLCFA and peroxisomal volume density in neuronal somata all showed a stronger association with NFT than with neuritic plaques. These results indicate substantial peroxisome-related alterations in AD, which may contribute to the progression of AD pathology.Electronic supplementary materialThe online version of this article (doi:10.1007/s00401-011-0836-9) contains supplementary material, which is available to authorized users.

Effects of exposure to Prestige-like heavy fuel oil and to perfluorooctane sulfonate on conventional biomarkers and target gene transcription in the thicklip grey mullet Chelon labrosus

Thicklip grey mullets Chelon labrosus inhabit coastal and estuarine areas where they can be chronically exposed to commonly released pollutants such as polycyclic aromatic hydrocarbons (PAHs) and perfluorinated compounds. These pollutants can also originate from accidental spills, such as the Prestige oil spill in 2002, which resulted in the release of a heavy fuel oil that affected coastal ecosystems in the Bay of Biscay. Peroxisome proliferation (PP), induced biotransformation metabolism, immunosuppression and endocrine disruption are some of the possible biological effects caused by such chemicals. With the aim of studying the effects of organic toxic chemicals on such biological processes at the transcriptional and at the cell/tissue level, juvenile mullets were exposed to the typical mammalian peroxisome proliferator perfluorooctane sulfonate (PFOS), and to fresh (F) and weathered (WF) Prestige-like heavy fuel oil for 2 and 16 days. First, fragments of genes relevant to biotransformation, immune/inflammatory and endocrine disruption processes were cloned using degenerate primers. Fuel oil elicited a significant PP response as proved by the transcriptional upregulation of palmitoyl-CoA oxidase (aox1), peroxisome proliferator activated receptor α (pparα) and retinoic X receptor, by the AOX1 activity induction and by the increased peroxisomal volume density. PFOS only elicited a significant induction of AOX1 activity at day 2 and of PPARα mRNA expression at day 16. All treatments significantly increased catalase mRNA expression at day 16 in liver and at day 2 in gill. Cyp1a transcription (liver and gill) and EROD activity were induced in fuel oil treated organisms. In the case of phase II metabolism only hepatic glutathione S-transferase mRNA was overexpressed in mullets exposed to WF for 16 days. Functionally, this response was reflected in a significant accumulation of bile PAH metabolites. WF treated fish accumulated mainly high molecular weight metabolites while F exposure resulted in accumulation of mainly low molecular ones. Fuel oil significantly regulated immune response related complement component C3 and hepcidin transcription followed by a significant regulation of inflammatory response related apolipoprotein-A1 and fatty acid binding protein mRNAs at day 16. These responses were accompanied by a significant hepatic inflammatory response with lymphocyte accumulations (IRLA) and accumulation of melanomacrophage centers (MMC). PFOS did not elicit any transcriptional response in the studied biotransformation and immune related genes, although histologically significant effects were recorded in IRLA and MMC. A significant reduction of lysosomal membrane stability was observed in all exposed animals. No endocrine disruption effects were observed in liver while brain aromatase mRNA was overexpressed after all treatments at day 2 and estrogen receptor α was downregulated under WF exposure at day 16. These results show new molecular and cellular biomarkers of exposure to organic chemicals and demonstrate that in mullets PP could be regulated through molecular mechanisms similar to those in rodents, although the typical mammalian peroxisome proliferator PFOS and heavy fuel oil follow divergent mechanisms of action.

Differential transcription of genes involved in peroxisome proliferation in thicklip grey mullets Chelon labrosus injected with benzo( a)pyrene

Benzo(a)pyrene (B( a)P) is a mutagenic polycyclic aromatic hydrocarbon (PAH) commonly released into the environment. B( a)P induces phase I biotransformation metabolism and peroxisome proliferation which is characterised in rodents by increased peroxisomal volume density, accompanied by the transcriptional induction of peroxisomal proteins. The aim of the present work was to study peroxisome proliferation at the transcriptional level, in comparison to the transcription of the well-characterised cytochrome P450 1A gene ( cyp1a) in the thicklip grey mullet Chelon labrosus. For this purpose, genes coding for the major peroxisomal membrane protein PMP70 and CYP1A were cloned using degenerate primers. Then juvenile mullets were single injected with B( a)P (5 mg/kg) and transcription of palmitoyl-CoA oxidase (aox1), multifunctional protein (mfp1), 3-ketoacyl-CoA thiolase (thio), Δ 2 ,Δ 4 dienoyl-CoA reductase 2, pmp70, catalase and cyp1a was semi-quantified in liver and gills 1 and 7 days after the injection. Transcription of aox1 and cyp1a was induced in gills 1 day after B( a)P injection. Cyp1a transcription was also induced in mullet liver one day after injection, indicating that B( a)P was available for the liver. This was further proved by the significant accumulation of B( a)P-like metabolites in bile 7 days after the injection. In liver, aox1, mfp1 and thio transcription was induced at day 1 followed by the induction of catalase transcription at day 7 that may reflect a response to an oxidative stress caused by B( a)P itself or by oxyradicals produced through the biotransformation metabolism and the peroxisomal β-oxidation. These hepatic responses were not reflected at AOX1 activity level. In conclusion, it has been shown for the first time that the three enzymes in the fish peroxisomal β-oxidation pathway are transcriptionally induced by B( a)P. It remains to be tested whether this enhanced transcription is reflected in an increase in the volume of peroxisomes.

Peroxisome proliferator-activated receptor α-independent peroxisome proliferation

Hepatic peroxisome proliferation, increases in the numerical and volume density of peroxisomes, is believed to be closely related to peroxisome proliferator-activated receptor α (PPARα) activation; however, it remains unknown whether peroxisome proliferation depends absolutely on this activation. To verify occurrence of PPARα-independent peroxisome proliferation, fenofibrate treatment was used, which was expected to significantly enhance PPARα dependence in the assay system. Surprisingly, a novel type of PPARα-independent peroxisome proliferation and enlargement was uncovered in PPARα-null mice. The increased expression of dynamin-like protein 1, but not peroxisome biogenesis factor 11α, might be associated with the PPARα-independent peroxisome proliferation at least in part.

Peroxisome proliferation and antioxidant enzymes in transplanted mussels of four basque estuaries with different levels of polycyclic aromatic hydrocarbon and polychlorinated biphenyl pollution

We aimed to determine the effects of changes in polycyclic aromatic hydrocarbon (PAH) and polychlorinated biphenyl (PCB) bioavailability on peroxisome proliferation and antioxidant enzymes to assess their potential use as pollution biomarkers. For this, mussels (Mytilus galloprovincialis) were sampled in Txatxarramendi and transplanted to Arriluze, Muskiz, and Plentzia (northern Spain), and vice versa. Arriluze was the most heavily polluted site, followed by Plentzia, Txatxarramendi, and Muskiz. Animals transplanted from a polluted station to a cleaner station lost contaminant load in three to six weeks, and when transplanted to a more polluted station, they accumulated PAHs and PCBs accordingly. Peroxisomal acyl-A oxidase (AOX) activity was the highest in animals from Arriluze, and animals transplanted to Arriluze showed increased AOX activity, reaching the levels of native mussels. Mussels from Txatxarramendi showed the lowest peroxisomal volume density (Vvp). Among mussels from Txatxarramendi, only those transplanted to Plentzia showed increased Vvp, whereas animals from Arriluze and Muskiz transplanted to Txatxarramendi after 2 d and six weeks, respectively, had decreased Vvp. Two days after transplant, superoxide dismutase and glutathione peroxidase activities were significantly lower in mussels from Arriluze and Muskiz, respectively, than in those from Txatxarramendi and than in animals transplanted to Txatxarramendi from these stations. In conclusion, transplant experiments with mussels are useful to assess the effects of pollution. Peroxisome proliferation, measured as induction of AOX or increased Vvp, shows great potential as a biomarker of pollution to be included in pollution monitoring programs. In the present work, we have demonstrated that peroxisome proliferation is a reversible phenomenon in mussels.

Biomarkers of Exposure and Reproduction-Related Effects in Mussels Exposed to Endocrine Disruptors

Biomarkers are useful tools to study the health of estuarine and marine ecosystems. Biomarkers can be measured in different organisms, but mussels have acquired a global importance as sentinels in marine pollution-monitoring programs. In the present work, we aimed to determine the effects of different endocrine disruptors in mussels by using peroxisome proliferation as a biomarker of exposure to organic pollutants and the levels of vitellogenin (Vtg)-like proteins as biomarker of endocrine disruption. In experiment 1, mussels Mytilus edulis were exposed for 3 weeks to North Sea crude oil (NSO 0.5 ppm) and a mixture of 0.5 ppm NSO, 0.1 ppm alkylphenol mix, and 0.1 ppm extra polycyclic aromatic hydrocarbons (PAHs) (MIX). In experiment 2, mussels were exposed for 3 weeks to diallylphthalate (DAP 50 ppb), bisphenol-A (BPA 50 ppb), and tetrabromodiphenylether (TBDE 5 ppb). Peroxisome proliferation was assessed by measuring acyl-CoA oxidase (AOX) activity and peroxisomal volume density (VVp) in digestive gland. Vtg-like protein levels were measured in gonads by the alkali-labile phosphate (ALP) method. Gonad was also analyzed histologically, and the gonad index (GI) calculated. Mussels exposed to NSO and MIX showed significantly increased AOX activities and VVP compared with control animals. Significantly higher VVP was also found in DAP- and TBDE-exposed mussels. Effects on ALP and GI depended significantly on sex and time of year. In female mussels, ALP levels and GI were lower in the NSO group. In male mussels, ALP levels were significantly increased in the MIX group. The volume density of athretic oocytes was higher in the NSO and MIX exposure groups than in controls, and gonad resorption was observed in the BPA exposure group. Our results confirm the usefulness of peroxisome proliferation as a biomarker of exposure to organic contaminants in mussels and indicate that changes in Vtg-like proteins could be used as potential indicator of pollutant effects on mussel reproduction.

Expression of peroxisome proliferator-activated receptors in zebrafish (Danio rerio) depending on gender and developmental stage

Peroxisome proliferator-activated receptors (PPARs) are members of the superfamily of nuclear hormone receptors involved in embryo development and differentiation of several tissues in mammals. The aim of the present study was to investigate the possible differential expression of the three PPAR subtypes (PPARalpha, PPARbeta, and PPARgamma) in relation to gender and developmental stage in zebrafish. For this purpose PPAR expression was assessed by immunohistochemistry in 7-day-old larvae, 1-month-old juveniles, and 1-year-old adults. Additionally, the activity of peroxisomal acyl-CoA oxidase (AOX), a gene regulated by PPARs, and the volume density of catalase-immunolabeled liver peroxisomes (V(VP)) was examined. No significant gender-related differences were detected in the tissue distribution of the three PPAR subtypes or in peroxisomal AOX activity and V(VP). The percentage of PPARbeta-positive hepatocytes was significantly higher in females than in males suggesting a specific regulatory role of this subtype in female zebrafish. The three PPAR subtypes were already expressed at the larval stage, with a similar tissue distribution pattern to that found in adults. For all stages, PPARalpha and PPARgamma were expressed at higher levels than PPARbeta, and PPARbeta immunolabeling was stronger in juveniles than in larval or adult stages. The percentages of hepatocyte nuclei immunolabeled for PPARs was higher in early developmental stages than in adults, similarly to AOX activity and V(VP). In conclusion, our results indicate that PPAR expression, the activity of its target gene AOX, and peroxisomal biogenesis are developmentally modulated in zebrafish.

Influence of amphotericin B deoxycholate or amphotericin B colloidal dispersion on renal tubule epithelium in rat.

Amphotericin B deoxycholate (AmB) or Amphotericin B colloidal dispersion (ABCD) are used in clinics for the treatment of systemic fungal infections. The goal of our study was to compare the nephrotoxicity of these drugs in rat kidney. The effects of AmB and ABCD on the ultrastructure of the epithelium of renal tubules were studied and evaluated using morphometric and statistical methods. Two groups of 3 animals were established: group 1 was treated with AmB desoxycholate and group 2, to which ABCD was applied. AmB caused more than ABCD ultrastructural changes in the cytoplasm of the epithelial cells: damage to mitochondria, vacuolation of cytoplasm, and increased values of volume density of peroxisomes. However, we failed to observe significant differences in morphology and density of the other cell organelles. The proximal tubules seemed to be more sensitive to the nephrotoxic influence of both formulas than the distal tubules of rat kidney. Although, AmB causes more severe damage than ABCD, both drugs cause damage to renal tubuli.

Biochemical and morphological effects of K-111, a peroxisome proliferator-activated receptor (PPAR)α activator, in non-human primates

K-111 has been characterized as a potent peroxisome proliferator-activated receptor (PPAR)α activator. Antidiabetic potency and amelioration of disturbed lipid metabolism were demonstrated in rodents, which were accompanied by elevations of peroxisomal enzymes and liver weight. To examine the possible therapeutic application of K-111 we have now assessed its efficacy in non-human primates with high transferability to humans. For this purpose obese, hypertriglyceridaemic, hyperinsulinaemic prediabetic rhesus monkeys were dosed sequentially with 0, 1, 3 and 10 mg/kg per day orally over a period of 4 weeks each. In addition, the effect of K-111 on the peroxisome compartment was analyzed in cynomolgus monkeys using liver samples obtained following a 13-week oral toxicity study. In prediabetic monkeys, the reduction of hyperinsulinaemia and improvement of insulin-stimulated glucose uptake rate indicated amelioration of insulin resistance. These effects were nearly maximal at a dose of 3 mg/kg per day, while triglycerides and body weight were lowered significantly in a dose-dependent manner. This reduction of body weight contrasts sharply with the adipogenic response observed with thiazolidinediones, another family of insulin-sensitizing agents. In young cynomolgus monkeys at a dosage of 5 mg/kg per day and more, K-111 induced an up to three-fold increase in lipid β-oxidation enzymes with an 1.5- to 2-fold increase in peroxisome volume density. This moderate increase in peroxisomal activity by K-111 in monkeys is consistent with its role as an PPARα activator and corresponds to the observations with fibrates in other low responder mammalian species. The increase in β-oxidation may explain, at least in part, the lipid modulating effect as well as the antidiabetic potency of K-111. This pharmacological profile makes K-111 a highly promising drug candidate for clinical applications in the treatment of type 2 diabetes, dyslipidaemia, obesity and the metabolic syndrome.

Biochemical and morphological effects of K-111, a peroxisome proliferator-activated receptor (PPAR)$alpha; activator, in non-human primates

K-111 has been characterized as a potent peroxisome proliferator-activated receptor (PPAR)α activator. Antidiabetic potency and amelioration of disturbed lipid metabolism were demonstrated in rodents, which were accompanied by elevations of peroxisomal enzymes and liver weight. To examine the possible therapeutic application of K-111 we have now assessed its efficacy in non-human primates with high transferability to humans. For this purpose obese, hypertriglyceridaemic, hyperinsulinaemic prediabetic rhesus monkeys were dosed sequentially with 0, 1, 3 and 10 mg/kg per day orally over a period of 4 weeks each. In addition, the effect of K-111 on the peroxisome compartment was analyzed in cynomolgus monkeys using liver samples obtained following a 13-week oral toxicity study. In prediabetic monkeys, the reduction of hyperinsulinaemia and improvement of insulin-stimulated glucose uptake rate indicated amelioration of insulin resistance. These effects were nearly maximal at a dose of 3 mg/kg per day, while triglycerides and body weight were lowered significantly in a dose-dependent manner. This reduction of body weight contrasts sharply with the adipogenic response observed with thiazolidinediones, another family of insulin-sensitizing agents. In young cynomolgus monkeys at a dosage of 5 mg/kg per day and more, K-111 induced an up to three-fold increase in lipid β-oxidation enzymes with an 1.5- to 2-fold increase in peroxisome volume density. This moderate increase in peroxisomal activity by K-111 in monkeys is consistent with its role as an PPARα activator and corresponds to the observations with fibrates in other low responder mammalian species. The increase in β-oxidation may explain, at least in part, the lipid modulating effect as well as the antidiabetic potency of K-111. This pharmacological profile makes K-111 a highly promising drug candidate for clinical applications in the treatment of type 2 diabetes, dyslipidaemia, obesity and the metabolic syndrome.

Peroxisome proliferation as a biomarker in environmental pollution assessment.

Peroxisome proliferators comprise a heterogeneous group of compounds known for their ability to cause massive proliferation of peroxisomes and liver carcinogenesis in rodents. In recent years it has become evident that other animals may be threatened by peroxisome proliferators, in particular aquatic organisms living in coastal and estuarine areas. These animals are exposed to a variety of pollutants of industrial, agricultural and urban origin which are potential peroxisome proliferators. Both laboratory and field studies have shown that phthalate ester plasticizers, PAHs and oil derivatives, PCBs, certain pesticides, bleached kraft pulp and paper mill effluents, alkylphenols and estrogens provoke peroxisome proliferation in different fish or bivalve mollusc species. The response appears to be mediated by peroxisome-proliferator activated receptors, members of the nuclear receptor family, recently cloned in fish. Based on these results it is proposed that peroxisome proliferation could be used as a biomarker of exposure to a variety of pollutants in environmental pollution assessment. This is illustrated by a case study in which mussels, used worldwide as sentinels of environmental pollution, were transplanted from reference to contaminated areas and vice versa. In mussels native to an area polluted with PAHs and PCBs, peroxisomal acyl-CoA oxidase (AOX) activity and peroxisomal volume density were 2-3 fold and 5-fold higher, respectively, compared to the reference site. When animals were transplanted to the polluted station, with increased concentration of organic xenobiotics, a concomitant significant increase of AOX was recorded. Conversely, in animals transplanted to the cleaner station, AOX activity and peroxisomal volume density decreased significantly. These results indicate that peroxisome proliferation is a rapid (i.e., two days) and reversible response to pollution in mussels. Before peroxisome proliferation can be implemented as a biomarker in biomonitoring programs, a well-defined protocol should be established and validated in intercalibration and quality assurance programmes. Furthermore, the influence of biotic and abiotic factors, some of which are known to affect peroxisome proliferation (season, tide level, interpopulation and interindividual variability), should be taken into consideration. The possible hepatocarcinogenic effects as well as the potential adverse effects on reproduction, development, and growth of peroxisome proliferators are unknown in aquatic organisms, thus providing a challenge for future investigations.

Expression of peroxisome proliferator-activated receptor α, and PPARα regulated genes in spontaneously developed hepatocellular carcinomas in fatty acyl-CoA oxidase null mice

Fatty acyl-CoA oxidase null mice (AOX-/-) develop hepatocellular carcinomas in 100% of animals between 10 and 15 months. We evaluated spontaneously developed HCC in AOX-/- mice for PPARalpha, PPARalpha regulated genes and peroxisome volume density and compared with adjacent non-neoplastic liver and liver in wild-type (AOX+/+) and heterozygous (AOX+/-) mice. The level of PPARalpha mRNA was 2.5-fold higher in HCC compared to the adjacent liver. mRNAs of PPARalpha regulated genes such as peroxisomal bifunctional enzyme, thiolase, cytochrome P450 CYP4A1 and CYP4A3 were similar in HCC and adjacent liver and increased by 7- to 22-fold compared with wild-type and heterozygous mice. Immunoblot analysis of HCC showed high amounts of PPARalpha, peroxisomal bifunctional enzyme and thiolase. Electron microscopic examination revealed 3.8 and 8.3-fold increase in the volume density of peroxisomes in HCC and adjacent liver, respectively, compared to the volume density in wild-type mice. These results demonstrate that spontaneously developed HCC in AOX-/- mice display a similar type of pleiotropic responses to high levels of PPARalpha ligands as the non-neoplastic liver. The changes observed in HCC and adjacent liver in AOX-/- mice were identical to those observed in rats and mice exposed to peroxisome proliferators.

Tumor Induction in Mouse Liver: Di-isononyl Phthalate Acts via Peroxisome Proliferation

Recently several chronic toxicity/carcinogenicity studies of di-isononyl phthalate (DINP) have been reported. These studies defined effect levels for liver tumors in male and female F344 rats at dietary levels exceeding 700 mg/kg/day; the no effect levels were 359 mg/kg/day in males and 442 mg/kg/day in females. Similar results were found in male B6C3F1 mice, but in female mice a significant increase in liver tumors was found at 336 mg/kg/day, making 112 mg/kg/day the NOAEL for liver tumors in that sex and species. DINP induces peroxisomal proliferation, and that, along with evidence that DINP is not mutagenic, is presumptive evidence for peroxisomal proliferation as the underlying mode of action for liver tumor development. To further explore the relationship between peroxisome proliferation and tumor induction in male and female mice, indicators of peroxisomal proliferation including liver weight, peroxisomal volume density, induction of peroxisomal enzyme activity, enhanced replicative DNA synthesis, and rates of apoptosis were measured at all of the dietary levels used in the chronic study in mice (500, 1500, 4000, and 8000 ppm, or approximately 100, 300, 800, and 1600 mg/kg/day). Liver weights, peroxisomal volume, and peroxisomal enzyme activity were significantly elevated in both male and female mice at the tumorigenic levels. Cell proliferation was also elevated in male and female mice, although the increases at levels below 4000 ppm in female mice were not significantly different from control values. Apoptosis was elevated at the 4000 and 8000 ppm levels, paralleling the increases in liver weight. These data along with previous results satisfy the criteria of the International Agency for Research on Cancer (IARC) and demonstrate that peroxisomal proliferation was indeed the mode of action for DINP-induced liver tumor induction in mice.

Peroxisomes of the nematode Caenorhabditis elegans: distribution and morphological characteristics.

We analyzed the distribution and morphological characteristics of peroxisomes in the nematode Caenorhabditis elegans by routine electron microscopy, immunoelectron microscopy, and morphometry. Peroxisomes were mainly contained in the epithelial cells of the digestive tract and pharyngeal gland, but some were observed in other cells. Their shape varied from round to twisted. The matrix of most peroxisomes was coarse and uneven, and contained electron-dense nucleoids and frequently tubular substructures. The diameter of peroxisomes in the gut (0.185 micro m) was smaller than that in pharyngeal gland (0.262 micro m). The volume density of peroxisomes per 100 micro m(2) of cytoplasm was 1.86 in the gut and 1.75 in the pharyngeal gland. After treatment with clofibrate, the diameter of peroxisomes increased approximately 1.11-fold in the gut and 1.2-fold in the pharyngeal gland. The volume density of peroxisomes also increased by 2.2-fold in the gut and 2.6-fold in the pharyngeal gland. The labeling density for catalase-2 was almost identical between gut and pharyngeal gland peroxisomes. The results show that in C. elegans peroxisomes mainly distribute in the epithelial cells of the gut and pharyngeal gland. Peroxisomes of the pharyngeal gland are larger than those of the gut, but peroxisomes of both tissues contain catalase-2 at similar concentrations.

Antioxidant enzymes and peroxisome proliferation in relation to contaminant body burdens of PAHs and PCBs in bivalve molluscs, crabs and fish from the Urdaibai and Plentzia estuaries (Bay of Biscay)

With the aim of studying levels of antioxidant and peroxisomal enzymes and the structure of peroxisomes in relation to body burdens of polycyclic aromatic hydrocarbons (PAHs) and polychlorinated biphenyls (PCBs), mussels Mytilus galloprovincialis, oysters Crassostrea sp., crabs Carcinus maenas and mullets Mugil cephalus were sampled in two Basque estuaries (Bay of Biscay): Urdaibai (Laida, Txatxarramendi, Arteaga, and downstream a sewage treatment plant—STP) and Plentzia. In general, animals showed higher concentrations of contaminants in winter than in summer and no relevant differences were detected among locations. Conversely, antioxidant enzyme activities were higher in summer. Enzyme expression was studied in mullets using immunochemical methods. By immunoblotting season-dependent differences were detected for Mn-superoxide dismutase (Mn-SOD). As for the immunohistochemical staining, mullets sampled in summer in Plentzia showed significantly higher optical densities for acyl-CoA oxidase and lower for both Cu,Zn-SOD and Mn-SOD than those collected downstream a STP as well as higher catalase immunostaining than those collected in winter. Peroxisomal volume density ( V vp) of mussels sampled in Laida and Txatxarramendi did not show seasonal variations, while for oysters collected in Laida and Arteaga V vp was higher in summer. Crab and mullet V vp were also higher in summer. In conclusion, the estuaries of Urdaibai and Plentzia can be considered as low to moderately polluted areas and levels of PAHs and PCBs do not show marked variations apart from seasonal variations. Animals can be adapted to low pollution conditions and, under these circumstances, seasonal factors might affect biomarker responses to a greater extent than pollution variations.

Interactive effects of benzo(a)pyrene and cadmium and effects of di(2-ethylhexyl) phthalate on antioxidant and peroxisomal enzymes and peroxisomal volume density in the digestive gland of mussel Mytilus galloprovincialis Lmk

Exposure of marine animals to certain organic and metal pollutants is thought to enhance reactive oxygen species (ROS) production with concomitant alterations of antioxidant defence mechanisms. Some of these organic pollutants cause peroxisome proliferation, a process resulting also in possible enhanced production of ROS. The aim of this study was to investigate the effects of two organic xenobiotics, benzo(a)pyrene (B(a)P) and di(2-ethylhexyl)phthalate (DEHP), as well as the effects of cadmium (Cd), on antioxidant and peroxisomal enzymes and on peroxisomal volume density in the digestive gland of mussel, Mytilus galloprovincialis Lmk., experimentally exposed for 21 days. Special attention was paid to the interactive effects of organic and metal compounds by exposing one group of mussels to a mixture of B(a)P and Cd. Exposure of mussels to Cd caused a decrease in superoxide dismutase (SOD) activity, in Mn-SOD protein levels and in volume density of peroxisomes. B(a)P exposure significantly increased catalase and glutathione peroxidase (GPX) and inhibited Mn-SOD after 21 days of exposure. B(a)P also caused a slight increase in acyl-CoA oxidase (AOX) activity and peroxisomal volume density after 21 days of exposure. Cd tended to inhibit changes provoked by B(a)P, indicating that responses to organic xenobiotics can be modulated by concomitant exposure to metal contaminants. Exposure to DEHP increased catalase and AOX and inhibited SOD activity and Mn-SOD protein levels. In conclusion, peroxisome proliferation, measured as an increase of the peroxisomal enzymes catalase and AOX (up to 1.53-fold for AOX), is a specific response to organic contaminants such as B(a)P and DEHP, whereas Cd does not cause peroxisome proliferation. Thus, peroxisome proliferation may be a specific biomarker of organic pollutants in mussels. Both organic and metal pollutants inhibited SOD activity and protein levels (up to 0.21-fold for Mn-SOD protein levels), the latter offering potential as general marker of pollution.

Ultrastructural, immunocytochemical and morphometric characterization of liver peroxisomes in gray mullet, Mugil cephalus.

Peroxisomes of the hepatocytes of gray mullets, Mugil cephalus, were characterized cytochemically and immunocytochemically using antibodies against the peroxisomal proteins catalase and palmitoyl-coenzyme A (CoA) oxidase. In addition, morphometric parameters of peroxisomes were investigated depending on the hepatic zonation, the age of the animals and the sampling season. Mullet liver peroxisomes were reactive for diaminobenzidine, but presented a marked heterogeneity in staining intensity. Most of the peroxisomes were spherical or oval in shape, although irregular forms were also observed. Their size was heterogeneous, with profile diameters ranging from 0.2 to 3 microm. Peroxisomes tended to occur in clusters, usually near the mitochondria and lipid droplets. They also showed a very close topographical relationship to the smooth endoplasmic reticulum. Mullet liver peroxisomes did not contain cores or nucleoids as rodent liver peroxisomes, but internal substructures were observed in the matrix, consisting of small tubules about 60 nm in diameter and larger semicircles 120 nm in diameter. The volume density of peroxisomes was higher in periportal hepatocytes of mullets sampled in summer than in pericentral hepatocytes, indicating that mullet peroxisomes vary depending on physiological and environmental conditions. By immunoblotting, the mammalian antibodies cross-react with the corresponding proteins in whole homogenates of mullet liver. Paraffin sections immunostained with the antibodies against catalase and palmitoyl-CoA oxidase showed a positive reaction corresponding to peroxisomes localized in the hepatocyte cytoplasm. In agreement, the ultrastructural study revealed that catalase and palmitoyl-CoA oxidase are exclusively localized in the peroxisomal matrix in fish hepatocytes, showing a dense gold labeling. The presence of the peroxisomal beta-oxidation enzyme palmitoyl-CoA oxidase in peroxisomes indicated that these organelles play a key role in the lipid metabolism of fish liver.

Seasonal variation of peroxisomal enzyme activities and peroxisomal structure in mussels Mytilus galloprovincialis and its relationship with the lipid content

Variations in structure and function of peroxisomes in digestive tissues of marine mussels have been proposed to be valid biomarkers of environmental contamination by organic xenobiotics. The aim of the present work was to study the seasonal variations in peroxisomal enzyme activities, catalase, palmitoyl-CoA oxidase (AOX) and d-amino acid oxidase (DAOX) and peroxisomal structure in mussels. Peroxisomal changes were related to the seasonal variation in the contents of neutral lipids in the digestive gland as the lipid metabolism in mussels is subjected to seasonal variations linked to the reproductive cycle and food intake. Significant higher catalase activities were recorded from April to June when compared to the rest of the year and AOX activity was also markedly induced during the late winter and spring (February to May) with maximal activities in April. DAOX activity did not vary seasonally, the highest activities being measured in November, February and May. Stereological studies of peroxisomes in digestive tubule cells revealed significantly higher volume, surface and numerical densities in animals collected in spring and summer. Changes in peroxisomal volume density were found to be significantly and positively correlated with changes in AOX and catalase activities. The peroxisomal structure and enzyme activities were negatively correlated with the lipid contents of digestive tubules. In April, the volume density occupied by neutral lipids was higher in duct epithelia while previously it was higher in digestive tubule epithelia. This trend was maintained during the period in which peroxisomes were more abundant until July. In the following September, digestive tubules recovered their lipid load. It is concluded that seasonal changes related to food intake and reproductive cycle induce changes in peroxisomal parameters that can be compared to typical peroxisome proliferation, with a 25-fold increase in AOX activity and an 8-fold increase in the peroxisomal numerical density in early spring.