Clinical and reproductive effects of Clophen A50 (PCB) administered during gestation on pregnant guinea pigs and their offspring

Female and male guinea pigs exposed to polychlorinated biphenyls (PCBs) in utero and via mother's milk showed growth retardation and signs of delayed onset of sexual maturation. In female young exposed to PCBs first vaginal opening occurred at a significantly older age and was of shorter duration compared with control females. The age at the first ovulation did not differ significantly between PCB-exposed females and control females. Male young exposed to PCBs had significantly lower absolute and relative testis weights at 3 months of age compared with control males. No differences in plasma testosterone concentrations were observed.     

Reduced levels of 1,25-dihydroxyvitamin D(3) in rat dams and offspring after exposure to a reconstituted PCB mixture.

Previous studies revealed effects of polychlorinated biphenyls (PCBs) and other polyhalogenated hydrocarbons on steroid hormone levels and hormone-dependent functions including behavior. In the present study serum concentrations of the vitamin D(3) metabolites 25-hydroxycholecalciferol (25-D) and 1,25-dihydroxycholecalciferol (1,25-D) were determined in rat dams and offspring after exposure to a PCB mixture that was reconstituted according to the congener pattern found in human breast milk. Unmated females were exposed to diets adulterated with 0; 5; 20; or 40 mg PCBs/kg diet. Exposure started 50 days prior to mating and was terminated at birth. Gestational exposure reduced serum concentrations of 1,25-D in dams in a dose-dependent manner. Concentration of 25-D was also decreased at the time of delivery, but not at weaning. Determination of 1,25-D in offspring at weaning revealed reductions in both high-exposure groups. Levels of 25-D were diminished only at the highest exposure level. Internal PCB concentrations in adipose tissue and brains exhibited a linear relation to dosages in diet. Concentrations of PCBs in brains were similar in dams and offspring at birth, but decreased at the end of lactation in dams. In offspring, values increased during this period because of continued exposure via the milk. In the adipose tissue, PCB levels were much lower in offspring than in dams. To our knowledge, this is the first report of PCB-induced effects on vitamin D(3) metabolites. In dams, reductions were seen even at the lowest exposure level used. Further studies are needed to evaluate the biological significance of these reductions in pregnant dams and possible consequences for the developing offspring.     

Short term effects of Clophen A 50 and of dichlorobiphenyl in rats.

In short term experiments, rats were treated with single oral doses of the polychlorinated biphenyls (PCB's), Clophen A 50 (high chlorinated compound) and dichlorobiphenyl (low chlorinated compound). Clophen A 50 treatment resulted in a marked increase in liver weight and in the activities of GPT, GOT and G1DH in rat serum at 1000 mg/kg similar effects were observed, but to a lesser degree. The levels of the serum lipids, cholesterol and triglycerides were significantly elevated at both dose levels and they remained elevated up to seven days. In contrast, one single oral dose of 1000 mg of dichlorobiphenyl per kg did not cause significant changes in the above mentioned parameters. Histological examination of the liver showed irregularly disseminated droplets of fat in both experiments. These results indicate that Clophen A 50 causes liver damage and alters the lipid metabolism of rats, whereas the low chlorinated dichlorobiphenyl does not exert such effects.     

Embryonic co-exposure to methoxychlor and Clophen A50 alters sexual behavior in adult male quail

Embryonic exposure to estrogens and estrogenic pollutants is known to demasculinize sexual behavior in adult male Japanese quail. In the present study, we administered the insecticide methoxychlor to quail eggs at a dose of 150 µg/g egg and then studied sexual behavior and other reproductive variables in adult males. In a second experiment we administered the same dose of methoxychlor together with 10 µg/g egg of the commercial polychlorinated biphenyl (PCB) mixture Clophen A50 (CA50) and also CA50 alone. Neither methoxychlor nor CA50 had any significant effects by themselves, but when they were administered together a significant reduction in male sexual behavior was observed. It seems likely that induction of biotransformation enzymes in the embryos by CA50 resulted in increased conversion of methoxychlor to the more estrogenic metabolite 2,2-bis(p-hydroxyphenyl)-1,1,1-trichloroethane (HPTE).     

Lipidomic changes in rat liver after long-term exposure to ethanol

Alcoholic liver disease (ALD) is a serious health problem with significant morbidity and mortality. In this study we examined the progression of ALD along with lipidomic changes in rats fed ethanol for 2 and 3 months to understand the mechanism, and identify possible biomarkers. Male Fischer 344 rats were fed 5% ethanol or caloric equivalent of maltose-dextrin in a Lieber-DeCarli diet. Animals were killed at the end of 2 and 3 months and plasma and livers were collected. Portions of the liver were fixed for histological and immunohistological studies. Plasma and the liver lipids were extracted and analyzed by nuclear magnetic resonance (NMR) spectroscopy. A time dependent fatty infiltration was observed in the livers of ethanol-fed rats. Mild inflammation and oxidative stress were observed in some ethanol-fed rats at 3 months. The multivariate and principal component analysis of proton and phosphorus NMR spectroscopy data of extracted lipids from the plasma and livers showed segregation of ethanol-fed groups from the pair-fed controls. Significant hepatic lipids that were increased by ethanol exposure included fatty acids and triglycerides, whereas phosphatidylcholine (PC) decreased. However, both free fatty acids and PC decreased in the plasma. In liver lipids unsaturation of fatty acyl chains increased, contrary to plasma, where it decreased. Our studies confirm that over-accumulation of lipids in ethanol-induced liver steatosis accompanied by mild inflammation on long duration of ethanol exposure. Identified metabolic profile using NMR lipidomics could be further explored to establish biomarker signatures representing the etiopathogenesis, progression and/or severity of ALD.     

Modes of cell death in rat liver after monocrotaline exposure.

Monocrotaline (MCT) is a pyrrolizidine alkaloid (PA) plant toxin that produces sinusoidal endothelial cell (SEC) injury, hemorrhage, fibrin deposition, and coagulative hepatic parenchymal cell (HPC) oncosis in centrilobular regions of rat livers. Cells with apoptotic morphology have been observed in the livers of animals exposed to other PAs. Whether apoptosis occurs in the livers of MCT-treated animals and whether it is required for full manifestation of pathological changes is not known. To determine this, rats were treated with 300 mg MCT/kg, and apoptosis was detected by transmission electron microscopy and the TUNEL (TdT-mediated dUTP nick end labeling) assay. MCT produced significant apoptosis in the liver by 4 h after treatment. To determine if MCT kills cultured HPCs by apoptosis, HPCs were isolated from the livers of rats and exposed to MCT. MCT caused a concentration-dependent release of alanine aminotransferase (ALT), a marker of HPC injury. Furthermore, caspase 3 was activated and TUNEL staining increased in MCT-treated HPCs. MCT-induced TUNEL staining and release of ALT into the medium were completely prevented by the pancaspase inhibitors z-VAD.fmk and IDN-7314, suggesting that MCT kills cultured HPCs by apoptosis. To determine if caspase inhibition prevents MCT-induced apoptosis in the liver, rats were cotreated with MCT and IDN-7314. IDN-7314 reduced MCT-induced TUNEL staining in the liver and release of ALT into the plasma. Morphometric analysis confirmed that IDN-7314 reduced HPC oncosis in the liver by approximately 50%. Inasmuch as HPC hypoxia occurred in the livers of MCT-treated animals, upregulation of the hypoxia-regulated cell-death factor, BNIP3 (Bcl2/adenovirus EIB 19kD-interacting protein 3), was examined. BNIP3 was increased in the livers of mice treated 24 h earlier with MCT. Results from these studies show that MCT kills cultured HPCs by apoptosis but causes both oncosis and apoptosis in the liver in vivo. Furthermore, caspase inhibition reduces both apoptosis and HPC oncosis in the liver after MCT exposure.     

Polychlorinated biphenyl (PCB) exposure in mothers and time to pregnancy in daughters

Developmental exposure to polychlorinated biphenyls (PCBs) disrupts reproduction in animals. Human data are lacking. We measured PCBs in preserved mothers' serum samples collected during 1960-1963, 1-3 days after their daughters' birth. We recorded time to pregnancy (TTP) in 289 daughters 28-31 years later. PCB congeners 187, 156, and 99 in mother's serum were associated with longer TTP in their daughters while PCB congeners 105, 138 and 183 were associated shorter TTP. Probability of pregnancy fell by 38% (95% CI 17-53%) and infertility was higher (30% not pregnant after 13 cycles versus 11% not pregnant after 13 cycles) among women whose mothers had a higher proportion of PCB congeners associated with longer TTP (75th percentile versus 25th percentile). This study demonstrates, for the first time, that developmental exposure to PCBs may disrupt pregnancy in humans.     

Endothelial cell injury and fibrin deposition in rat liver after monocrotaline exposure.

Monocrotaline (MCT) is a pyrrolizidine alkaloid (PA) plant toxin that produces hepatotoxicity in people and animals. Human exposure to PAs occurs through consumption of contaminated grains and herbal remedies. Injection (ip) of MCT in rats produced dose-dependent hepatic parenchymal cell injury that was significant at 200 mg/kg. Injection of 300 mg/kg MCT produced time-dependent hepatotoxicity with significant injury beginning by 12 h after treatment. Histopathologic examination of liver sections revealed coagulative hepatocellular necrosis, widening of sinusoids and hemorrhage in centrilobular regions. MCT-induced damage to central venular endothelial cells (CVECs) and sinusoidal endothelial cells (SECs) in the liver was quantified using immunohistochemical staining and by increased plasma hyaluronic acid concentration. MCT damaged CVECs and SECs in the liver by 8 h after treatment. Extensive endothelial cell injury was restricted to centrilobular regions. To determine if damage to endothelial cells in the liver stimulated activation of the coagulation system, fibrin deposition was quantified using immunohistochemistry. Extensive fibrin deposition occurred in the liver after MCT treatment and was restricted to centrilobular regions. Interestingly, both endothelial cell damage and fibrin deposition preceded the onset of hepatic parenchymal cell injury. These results suggest that endothelial cell damage and fibrin deposition in centrilobular regions of the liver are prominent features of MCT-induced liver injury.     

Rat liver changes after subchronic exposition to polychlorinated biphenyls (PCB)of low chlorine content

Liver changes were studied after subchronic feeding a diet containing 2000 ppm PCB [chlorine content 42% corresponding to trichlorobiphenyls (triCB)]. The products differed in their content of highly chlorinated biphenyls (Cl₅-biphenyl; 5%=triCB-5, 2%=triCB-2 and 0.4%=triCB-0.4). The most striking difference was observed in respect to their porphyrinogenic actions. TriCB-0.4 and triCB-2 caused an increase of porphyrins about 10-fold, whereas the liver porphyrin content of triCB-5 treated rats was 175-fold higher than normal. In all cases of porphyria the porphyrins consisted mainly of uro- and heptacarboxyporphyrin. In contrast to their different porphyrinogenic effects all triCB products caused an equal induction of -aminolaevulinate synthetase, but no increase of -aminolaevulinate dehydratase activity.TriCB-5 was also a stronger inducer than triCB-0.4 and triCB-2 regarding microsomal monoxygenases and UDP-glucuronyltransferase. The quantitative differences of the effect can be correlated to PCB residues in the liver. In triCB-5 fed rats a much higher accumulation of highly chlorinated components could be determined.The histological examination by light and electron microscopy showed no significant differences in the effects caused by all three triCB products. In livers of all rats cell hypertrophy could be observed due to a considerable hyperproliferation of tubular and vesicular SER. SER membranes were tightly packed and sometimes disrupted. Membrane arrays of various size were found in most hepatocytes. The mitochondria were dislocated by these formations and were sometimes swollen. There was neither centrilobular or periportal necrosis nor fibrosis nor fatty degeneration.It may be concluded that PCB of low chlorine content (42%) are much less toxic than highly chlorinated PCB. However, the small amount of highly chlorinated components, present as contaminants in commercial products containing 42% chlorine, may accumulate and exert toxic effects.

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Zusammenfassung Es wird über Leberveränderungen an Ratten nach subchronischer Fütterung mit 2000 ppm PCB berichtet. Dabei wurden drei Chargen eines technischen Trichlorbiphenyls eingesetzt, die einen unterschiedlichen Gehalt (%) an hochchlorierten Komponenten (d. h.5 Cl) hatten, und zwar: 5% =triCB-5; 2% = triCB-2 und 0,4% = triCB-04. Der auffälligste Wirkungsunterschied der Präparate bestand in den porphyrinogenen Eigenschaften. Während triCB-0,4 und triCB-2 einen Anstieg des Porphyringehaltes der Leber um den Faktor 17 bzw. 7 verursachten, stieg der Gehalt nach triCB-5 175fach höher als normal an. Die Porphyrine bestanden hauptsächlich aus Uroporphyrin und Heptacarboxyporphyrin. Im Gegensatz zu den unterschiedlichen porphyrinogenen Wirkungen bewirkten alle drei triCB-Präparate eine gleich hohe Induktion der -Aminolaevulinatsynthetase. Die -Aminolaevulinatdehydratase erfuhr keine Veränderung ihrer Aktivität.Die mikrosomalen Monoxygenasen und die UDP-Glucuronyltransferase wurden durch alle drei triCB induziert. Die höchsten Werte wurden wieder durch triCB-5 erzielt. Sie korrelieren damit zu den PCB-Rückständen in der Leber, denn nach Fütterung mit triCB-5 kam es zu einer wesentlich höheren Akkumulation der hochchlorierten Komponenten.Bei licht- und elektronenmikroskopischer Untersuchung konnten keine signifikant unterschiedlichen Wirkungen der triCB-Präparate festgestellt werden. Die Lebern aller Tiere zeigten eine erhebliche Zellhypertrophie, die durch die Hyperproliferation des tubulären und vesikulären glatten endoplasmatischen Retikulums hervorgerufen wurde. Die Membranen des Retikulums waren dicht gepackt und manchmal zerrissen. In den meisten Zellen konnten außerdem unterschiedlich große membrane arrays gesehen werden, die zu einer Verdrängung von Mitochondrien führte. Einige Mitochondrien waren geschwollen. Zentrolobuläre oder periportale Nekrosen, Fibrosen oder fettige Degenerationen konnten nicht beobachtet werden.Aus den Untersuchungen kann gefolgert werden, daß PCB-Produkte mit niedrigem Chlorgehalt (42%) wesentlich weniger toxisch sind als solche mit hohem Gehalt. Toxische Effekte können aber dadurch auftreten, daß die in den Handelspräparaten als Verunreinigung enthaltenen hochchlorierten Komponenten akkumulieren.

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Abbreviations ALA-D -aminolaevulinate dehydratase - ALA-S -aminolaevulinate synthetase - BSP sulfobromophthalein - cyt. cytochrome - diCB commercial PCB mixture (Aroclor^® 1232, Monsanto) of preferably dichlorobiphenyls - hexaCB commercial PCB mixture (Aroclor^® 1260) of preferably hexachlorobiphenyls - tetraCB commercial PCB mixture (Aroclor^® 1248) of preferably tetrachlorobiphenyls - triCB-5, triCB-2, triCB-0.4 PCB mixtures of preferably trichlorobiphenyls containing 5% (2%, 0.4%) highly chlorinated biphenyls ( pentachlorobiphenyls) Some of these results have been reported at the Spring Meeting of the Deutsche Pharmakologische Gesellschaft, Mainz, 1975 (Grote et al., 1975c)This work was carried out within the coordinated research program Polychlorinated Biphenyls in the Environment which was supported by a grant of the German Federal Ministry for Research and Technology     

Microarray analysis in the zebrafish (Danio rerio) liver and telencephalon after exposure to low concentration of 17alpha-ethinylestradiol

17alpha-ethinylestradiol (EE2) is detected in sewage effluent at concentrations that can disrupt normal reproductive function in fish. The objectives of this study were to identify novel genomic responses to EE2 exposure using microarray and real-time RT-PCR analysis in the liver and telencephalon of male zebrafish. Zebrafish were exposed to an environmentally relevant nominal concentration of 10ng/L EE2 for a 21-day period. In the liver, common biomarkers for estrogenic exposure such as vitellogenin 1 and 3 (vtg1; vtg3), estrogen receptor alpha (esr1), and apolipoprotein A1 (apoA1) mRNA were identified by microarray analysis as being differentially regulated. Real-time RT-PCR confirmed that vtg1 was induced approximately 700-fold, vtg3 was induced approximately 100-fold and esr1 was induced approximately 20-fold. As determined by microarray analysis, ATPase Na+/K+ alpha 1a.4 (atp1a1a.4) and ATPase Na+/K+ beta 1a (atp1b1a) mRNA were down-regulated in the liver. Gene ontology (GO) analysis revealed that there were common biological processes and molecular functions regulated by EE2 in both tissues (e.g. electron transport and cell communication) but there were tissue specific changes in gene categories. For example, genes involved in protein metabolism, carbohydrate metabolism were down-regulated in the liver but were induced in the telencephalon. This study demonstrates that (1) tissues exhibit different gene responses to low EE2 exposure; (2) there are pronounced genomic effects in the liver and (3) multi-tissue gene profiling is needed to improve understanding of the effects of human pharmaceuticals on aquatic organisms.     

Gene expression and estrogen sensitivity in rat uterus after developmental exposure to the polybrominated diphenylether PBDE 99 and PCB

Considering the presence of polybrominated diphenylethers (PBDEs) in human milk and cord blood, and the estrogenic activity of some congeners, it is conceivable that PBDEs may interact with developing neuroendocrine systems. We investigated effects of 2,2′,4,4′,5-pentabromo-DE (PBDE 99), a major congener in human milk, on development of brain and reproductive organs, with focus on estrogen target gene expression. Time-pregnant Long Evans rats were subcutaneously injected with PBDE 99 (1 or 10 mg/kg/day), the PCB mixture Aroclor 1254 (10 mg/kg/day), known to interfere with sexual development, or vehicle, from gestational day (GD) 10 to GD 18. In female offspring, anogenital distance was unaffected by PBDE 99 but increased by Aroclor; puberty (vaginal opening) was not significantly changed. Adult PBDE 99-exposed offspring exhibited unchanged uterine weight but increased ovarian weight. Uterine mRNA levels of estrogen target genes were determined by real-time PCR. Progesterone receptor (PR) mRNA was down-regulated at both PBDE 99 doses, estrogen receptor alpha (ER alpha), ER beta and insulin-like growth factor-I (IGF-I) were up-regulated at the lower dose. Aroclor induced different effect patterns. In order to investigate possible changes in sensitivity of target genes to estrogen, some offspring were ovariectomized at 10 weeks of age, s.c. injected with estradiol-17β (E2, 10 μg/kg) or vehicle at 12 weeks, and sacrificed 6 h later. PBDE 99 dose-dependently reduced the magnitude of IGF-I mRNA induction by E2, and increased the magnitude of ER beta repression. PBDE 99 also influenced baseline levels of PR, IGF-I and ER beta mRNAs in ovariectomized, vehicle-injected controls. These data indicate that developmental exposure to PBDE 99 at doses devoid of general toxicity, affects the regulation of estrogen target genes in uterus. Since PBDE 99 was detected in blood and adipose tissue of adult offspring, these effects may result from interactions with developmental processes, adult functions, or a combination of both.     

Intracellular distribution of inorganic and organic mercury in rat liver after exposure to methylmercury salts

The intracellular distribution of inorganic and organic mercury in rat liver after exposure to methylmercury salts has been reported. The results have been discussed comparing intracellular distribution of mercury after exposure to various mercury compounds. After exposure to methylmercury salts the lysosomes/peroxisomes contain the highest concentration of mercury followed by microsomes and mitochondria. Differences in distribution between various mercury compounds seem to be related to the stability of the carbon-mercury bond, lysosomes accumulating inorganic mercury by preference either injected as such, or released in vivo from the intact organomercurial. Toxicological and pharmacokinetic implications of these conclusions have been discussed.     

Altered gene profiles in fetal rat testes after in utero exposure to di(n-butyl) phthalate.

Di(n-butyl) phthalate (DBP) has antiandrogenic-like effects on the developing reproductive tract in the male rat and produces regions of interstitial cell hyperplasia and gonocyte degeneration in the developing fetal testes at maternal doses of 100-500 mg/kg/day. Neither DBP nor its primary metabolites interact with the androgen receptor in vitro. The present study was performed to examine gene expression in the fetal rat testes following in utero DBP exposure. Pregnant Sprague-Dawley rats received corn oil, DBP (500 mg/kg/day), or flutamide (reference antiandrogen, 50 mg/kg/day) by gavage daily from gestation day (GD) 12 to 21. Dose levels were selected to maximize fetal response with minimal maternal toxicity. Testes were isolated on GD 16, 19, and 21. Global changes in gene expression were determined by microarray analysis. Selected genes were further examined by quantitative RT-PCR. DBP, but not flutamide, reduced expression of the steroidogenic enzymes cytochrome P450 side chain cleavage, cytochrome P450c17, and steroidogenic acute regulatory protein. Testicular testosterone and androstenedione were decreased on GD 19 and 21, while progesterone was increased on GD 19 in DBP-exposed testes. Testosterone-repressed prostate message-2 (TRPM-2) was upregulated, while c-kit (stem cell factor receptor) mRNA was downregulated following DBP exposure. TRPM-2 and bcl-2 protein staining was elevated in GD 21 DBP-exposed Leydig and Sertoli cells. Results of this study have led to the identification of several possible mechanisms by which DBP can induce its antiandrogenic effects on the developing male reproductive tract without direct interaction with the androgen receptor. Our results suggest that the antiandrogenic effects of DBP are due to decreased testosterone synthesis. In addition, enhanced expression of cell survival proteins such as TRPM-2 and bcl-2 may be involved in DBP-induced Leydig cell hyperplasia, whereas, downregulation of c-kit may play a role in gonocyte degeneration. Future studies will explore the link between these identified gene expression alterations and ultimate adverse responses.     

Experimental exposure of rat skin to methyl bromide: a toxicokinetic and histopathological study

Methyl bromide was experimentally exposed to a 12 cm² area of the back skin of Wistar rats for 30 s, and for 1, 3, and 5 min, and time courses of both changes in plasma bromide concentration and of histopathological changes were examined. To measure bromide ion, a head space gas chromatography was used. The concentration of plasma bromide ion showed a sharp increase immediately after the exposure in all exposed groups, reaching a peak level after 1 h, then decreased rapidly. The ion level gradually decreased after 72 h to 1 week, and returned to a normal level after 4 to 8 weeks. Calculating from a regressive curve, the biological half lives of plasma bromide ion were 5.0 days to 6.5 days. Histopathologically, the impairments to the epidermal cells, fibroblasts and blood vessels were observed in the early phase. These cellular changes could be due to the direct cytotoxicity of the compound. In the next phase, newly infiltrating cells showed degeneration and necrosis. Subsequently, an impairment of the collagen bundles was observed. Our experiments suggested an immediate permeation and rapid metabolization of methyl bromide in the skin and a multistep formation of the skin damage induced by the compound. These processes of methyl bromide-induced skin damage are quite different from chemical skin injuries caused by the representative causative agents such as alkaline and acid. Received: 26 April 1999 / Accepted: 2 November 1999     

Excretion of 3-hydroxy-benzo(a)pyrene and mutagenicity in rat urine after exposure to benzo(a)pyrene

3-hydroxy-benzo(a)pyrene (3-OH-B(a)P) and mutagenic activity in rat urine were determined after the oral administration of benzo(a)pyrene given in three repeated doses of 10, 20 and 50 mumol kg-1. The procedure for the determination of 3-OH-B(a)P consisted of enzymic hydrolysis, separation and HPLC-analysis. The mutagenic activity of concentrated urine samples was assayed with the Salmonella typhimurium strain TA98 in the presence of S9 mix and beta-glucuronidase. The urinary excretion of 3-OH-B(a)P and mutagens showed a correlation and both increased dose-dependently during the sampling period of 6 days. Data indicated that 3-OH-B(a)P can be regarded as a reliable representative of all urinary (pre)-mutagens derived from benzo(a)pyrene and exposure of rats to benzo(a)pyrene could be detected with greater sensitivity by the HPLC assay of 3-OH-B(a)P than with the non-specific mutagenicity assay.     

Gene expression profiles in zebrafish (Danio rerio) liver after acute exposure to okadaic acid

Okadaic acid (OA), a main component of diarrheic shellfish poisoning (DSP) toxins, is a strong and specific inhibitor of the serine/threonine protein phosphatases PP1 and PP2A. However, not all of the OA-induced effects can be explained by this phosphatase inhibition, and controversial results on OA are increasing. To provide clues on potential mechanisms of OA other than phosphatase inhibition, here, acute toxicity of OA was evaluated in zebrafish, and changes in gene expression in zebrafish liver tissues upon exposure to OA were observed by microarray. The i.p. ED₅₀ (6 h) of OA on zebrafish was 1.54 μg OA/g body weight (bw). Among the genes analyzed on the zebrafish array, 55 genes were significantly up-regulated and 36 down-regulated in the fish liver tissue upon exposure to 0.176 μg OA/g bw (low-dose group, LD) compared with the low ethanol control (LE). However, there were no obvious functional clusters for them. On the contrary, fish exposure to 1.760 μg OA/g bw (high-dose group, HD) yielded a great number of differential expressed genes (700 up and 285 down) compared with high ethanol control (HE), which clustered in several functional terms such as p53 signaling pathway, Wnt signaling pathway, glutathione metabolism and protein processing in endoplasmic reticulum, etc. These genes were involved in protein phosphatase activity, translation factor activity, heat shock protein binding, as well as transmembrane transporter activity. Our findings may give some useful information on the pathways of OA-induced injury in fish.     

Induction of glutathione-S-transferase and heat-shock proteins in rat liver after ethylene oxide exposure

Defense mechanisms in rat liver against depletion of glutathione (GSH) and cellular injuries induced by ethylene oxide (EO) were studied. Rats were exposed to EO under either high dose (1300 ppm for 4 hr, once) or low dose (500 ppm for 6 hr, three times a week for 6 weeks) conditions. The hepatic content of GSH decreased dramatically after EO treatment, probably due to detoxication of EO. After the high dose treatment the hepatic GSH content fell by 90% of the control values but recovered within 10 to 15 hr. EO reacts directly with a variety of cellular macromolecules but all rats survived the exposure. Since the metabolites of EO are ethylene glycol and GSH-conjugates, the enzymatic activities of epoxide hydrolase and glutathione-S-transferase (GST) were determined. Only GST activity was found to occur after low dose chronic exposure. The defense mechanism at mRNA level was investigated using probes for GST and several heat-shock proteins (hsps). Enhanced accumulation of GST mRNA was detectable during the recovery period of rats after both high and low dose exposure to EO. Interestingly, both hsp32 (less than 40-fold) and hsp90 (less than 3-fold) mRNA increased after high dose exposure but the mRNA level of one of the major heat-shock proteins, hsp70, did not change under these conditions. Diethylmaleate, which is known to be a GSH depleter in liver, induced hsp32 mRNA only in rat liver, while hsp70 and hsp90 mRNA levels did not change when GSH was depleted. These results suggest that individual heat-shock proteins are induced in different ways under unphysiological conditions such as EO exposure.