Toshinari Suzuki

Metabolism of 2-hydroxy-4-methoxybenzophenone in isolated rat hepatocytes and xenoestrogenic effects of its metabolites on MCF-7 human breast cancer cells

The metabolism and cytotoxicity of 2-hydroxy-4-methoxybenzophenone (HMB) in isolated rat hepatocytes and the xenoestrogenic activity of HMB and its metabolites in MCF-7 human breast cancer cells and an estrogen receptor competitive binding assay have been studied, respectively. The incubation of hepatocytes with HMB caused a concentration- and time-dependent decrease in cell viability, accompanied by loss of intracellular ATP and adenine nucleotide pools. HMB at a low-toxic level (0.25 mM) in the hepatocyte suspensions was converted enzymatically to 2,4-dihydroxybenzophenone (DHB) and a hydroxylated intermediate, which was tentatively identified as an isomer of 2,2prime prime or minute-dihydroxy-4-methoxybenzophenone (DHMB) as determined by mass spectroscopy coupled with HPLC. Furthermore, the parent compound and both intermediates were rapidly conjugated to glucuronides, whereas free unconjugated DHMB and 2,3,4-trihydroxybenzophenone (THB) were identified as trace intermediates. In another experiment, DHB and THB displaced competitively 17beta-estradiol bound to the recombinant human estrogen receptor alpha in a concentration-dependent manner: IC(50) of diethylstilbestrol and bisphenol A, which are known xenoestorogenic compounds, and DHB and THB was approximately 1 x 10(-8), 1 x 10(-5), 5 x 10(-5) and 5 x 10(-4) M, respectively. Further, DHB at concentrations from 10(-8) to 10(-6) M caused a concentration-dependent proliferation of MCF-7 cells. DHMB and THB at 10(-7) and 10(-6) M also elicited a slight increase in cell numbers, whereas HMB at concentrations from 10(-9) to 10(-4) M did not affect the cell proliferation. Based on the relative IC50 for the competitive binding and the proliferative effect on MCF-7 cells, it follows that in estrogenic potency, DHB>THB>DHMB. These results indicate that some hydroxylated intermediates such as DHB rather than the parent compound act as a xenoestrogen via biotransformation.

Metabolism and toxicity of benzophenone in isolated rat hepatocytes and estrogenic activity of its metabolites in MCF-7 cells

The metabolism and cytotoxicity of benzophenone and estrogenic activity of its metabolites have been studied in freshly isolated rat hepatocytes and cultured MCF-7 human breast cancer cells, respectively. The incubation of hepatocytes with benzophenone (0.25-1.0 mM) elicited a concentration- and time-dependent cell death, accompanied by loss of intracellular ATP and depletion of adenine nucleotide pools. Benzophenone at a low-toxic level (0.25 mM) in the hepatocyte suspensions was converted to benzhydrol, p-hydroxybenzophenone and its sulfate conjugate, without marked loss of cell viability. The amounts of benzhydrol and sulfate conjugate increased with time. In contrast, addition of 2,6-dichloro-4-nitrophenol (an inhibitor of sulfotransferase; 0.1 mM), nontoxic to hepatocytes during the incubation period, enhanced benzophenone-induced cytotoxicity, and this effect was accompanied by a decrease in the formation of sulfate conjugate and increase in the amount of free p-hydroxybenzophenone. In another experiment, MCF-7 cells, estrogen-responsible breast cancer cells were cultured in estradiol free medium and then exposed to 10 nM-500 microM benzophenone or its metabolites for 6 days. Although at higher concentrations all the compounds were toxic, except for benzophenone and benzhydrol, 10-100 microM p-hydroxybenzophenone significantly increased cell proliferation. These results indicate that benzophenone is enzymaticaly converted to benzhydrol, p-hydroxybenzophenone and its sulphate conjugate in rat hepatocytes. Even if there is less free p-hydroxybenzophenone than benzhydrol and sulfate conjugate in hepatocyte suspensions, p-hydroxybenzophenone itself acts as a weak xeno-estrogen on MCF-7 cells.

Spatially detailed survey on pollution by multiple perfluorinated compounds in the Tokyo Bay basin of Japan.

Pollution from 35 perfluorinated compounds (PFCs) in the water of the Tokyo Bay basin was examined. The water in the basin contained relatively high levels of perfluorononanoate (PFNA), perfluorooctanoate (PFOA), and perfluorooctane sulfonate (PFOS) compared to the other PFCs, which were present at concentrations of 20.1 ng/L, 6.7 ng/L, and 5.8 ng/L, respectively. In contrast, the concentrations of their precursors and degradation products were an order of magnitude lower. Sewage treatment plant (STP) effluent in the area also contained high levels of PFNA compared with the river water samples (Mann-Whitney U-test, p<0.0002). From a spatial aspect, increases in PFC pollution levels correlated with increased urbanization in the study area suggested that there are nonpoint source contributors to the PFC pollution in this area. Branched isomers of the PFCs were also quantified. Samples that contained high concentrations of perfluoroalkyl carboxylates (PFCA) showed lower proportions of its branched isomer. This indicates that the branched isomers are more prominent in the area with lower PFC pollution. This analysis was beneficial for estimating the individual contributions of different PFCA production processes. This survey provided new information on the sources, spatial distribution, and behavioral characteristics of PFC pollutants in this area.

Existence of acetyl-CoA-dependent chain elongation system in hepatic peroxisomes of rat: Effects of clofibrate and di-(2-ethylhexyl)phthalate on the activity☆

The acetyl-CoA-dependent elongation of medium-chain acyl-CoA in the presence of pyridine nucleotide was studied in rat liver. The activity was increased by the administration of peroxisome proliferators, clofibrate and di-(2-ethylhexyl)phthalate, and the change was more remarkable in peroxisomes than in mitochondria. Addition of 0.01% Triton X-100 to the incubation mixture caused an increase in the mitochondrial activity, whereas the peroxisomal activity did not increase significantly. The pH optimum for the peroxisomal activity was in the range of pH 6.5-7.0 and that for the mitochondrial activity was pH 7.5-8.0. The specificities of primer chain length in both organelles were almost the same, and octanoyl-CoA was the preferred substrate. Peroxisomal activity was completely inhibited by the addition of 1 mM N-ethylmaleimide or 1 mM p-hydroxymercuribenzoic acid, while the activity did not change on the addition of 1 mM KCN or an antibody to acyl-CoA oxidase, the first enzyme of the peroxisomal beta-oxidation system. The activity of enoyl-CoA reductase, which catalyzes the last step of the elongation system, was also detected in peroxisomes, although the main activity was localized in microsomes. When the liver peroxisomal fraction of clofibrate-treated rats was incubated with a mixture of octanoyl-CoA, acetyl-CoA, NADH, NADPH, and Triton X-100 in a buffer system, dodecanoyl-CoA was detected as the main product by radio-gas chromatography. On the other hand, the elongation activity was decreased greatly by the addition of NAD+ into the mixture. These results indicate that (i) peroxisomes have activity to elongate medium chain acyl-CoA; (ii) the peroxisomal elongation system may consist of the reverse reaction of the beta-oxidation system except for the last step, which is catalyzed by enoyl-CoA reductase; and (iii) the peroxisomal elongation system is less active than the beta-oxidation system under physiological conditions.

Chronic toxicity of an environmentally relevant mixture of pharmaceuticals to three aquatic organisms (alga, daphnid, and fish)

Principles of concentration addition and independent action have been used as effective tools to predict mixture toxicity based on individual component toxicity. The authors investigated the toxicity of a pharmaceutical mixture composed of the top 10 detected active pharmaceutical ingredients (APIs) in the Tama River (Tokyo, Japan) in a relevant concentration ratio. Both individual and mixture toxicities of the 10 APIs were evaluated by 3 short-term chronic toxicity tests using the alga Pseudokirchneriella subcapitata, the daphnid Ceriodaphnia dubia, and the zebrafish Danio rerio. With the exception of clarithromycin toxicity to alga, the no-observed-effect concentration of individual APIs for each test species was dramatically higher than the highest concentration of APIs found in the environment. The mixture of 10 APIs resulted in toxicity to alga, daphnid, and fish at 6.25 times, 100 times, and 15,000 times higher concentrations, respectively, than the environmental concentrations of individual APIs. Predictions by concentration addition and independent action were nearly identical for alga, as clarithromycin was the predominant toxicant in the mixture. Both predictions described the observed mixture toxicity to alga fairly well, whereas they slightly underestimated the observed mixture toxicity in the daphnid test. In the fish embryo test, the observed toxicity fell between the predicted toxicity by concentration addition and independent action. These results suggested that the toxicity of environmentally relevant pharmaceutical mixtures could be predicted by individual toxicity using either concentration addition or independent action.

Determination of pesticides in water by capillary gas chromatography with splitless injection of large sample volumes

Abstract A large-volume injection for a capillary gas chromatograph equipped with an electron-capture, nitrogen—phosphorus-selective (NPD) or flame photometric detector is proposed for the determination of pesticides. The cold-trap column, a deactivated fused-silica column (3 m × 0.53 mm I.D.), was attached to the analytical column (30 m) and the regulation column (3 cm), DB-5, both of 0.25 mm I.D. with film thickness 0.25 μm, with a dual-outlet splitter. The regulation column was connected with the solvent-diversion column, a deactivated fused-silica column (2 m × 0.53 mm I.D.), which was led out of the column oven and attached to an electromagnetic valve. By opening the valve in the splitless mode, the pesticides slowly injected in n-hexane in a volume from 25 to 150, μl were trapped in the cold-trap column, and a large volume of n-hexane was almost all diverted from the gas chromatograph through the diversion column. The trapped pesticides were introduced to the analytical column by closing the valve. Twenty-five pesticides, scattered on a golf course in Japan, were determined at concentrations from 1 to 100 ng/ml in n-hexane. The reproducibility of separation of the pesticides by the proposed method was similar to that of normal splitiess (1-μl) injection. The proposed method was applied to the screening of the pesticides in groundwater after liquid—liquid extraction with dichloromethane; the pesticides could be determined at levels lower than 1 μg/l in a 20-ml water sample.

Spatial distribution and loading amounts of particle sorbed and dissolved perfluorinated compounds in the basin of Tokyo Bay.

In this study, we analyzed over 30 types of PFCs, including precursors in both the dissolved phase and particle solid phase, in 50 samples of river water collected from throughout the Tokyo Bay basin. PFCs were detected in suspended solids (SSs) at levels ranging from <0.003-4.4 ng L(-1) (0.11-2470 ng g(-1) dry weight). The concentrations of PFCs in the SS were one to two order(s) of magnitude lower than those of PFCs in the dissolved phase. Relatively high levels of PFCs (total of 35 PFCs) in SS were observed in urbanized areas. The concentration of PFCAs, including PFOA and PFNA, were significantly correlated with the geographic index as artificial area (R(2) of the linear regression curve in a double logarithmic plot: 0.09-0.55). Conversely, PFOS and FOSA were significantly correlated with the arterial traffic area (R(2) in a double logarithmic plot: 0.29-0.55). Those spatial trends were similar to the trends in dissolved PFCs. We estimated the loading amount of PFCs into Tokyo Bay from six main rivers and found that more than 90% of the total PFCs reached Tokyo Bay in the dissolved phase. However, 40.0-83.5% of the long chain PFCAs (C12-C15), were transported as particle sorbed PFCs. Rain runoff events might increase the loading amount of PFCs in SS. Overall, the results presented herein indicate that greater attention should be given to PFCs, especially for longer chain PFCs in SS in addition to dissolved PFCs.

Mitochondrial dysfunction and biotransformation of β-carboline alkaloids, harmine and harmaline, on isolated rat hepatocytes.

The cytotoxic effects and biotransformation of harmine and harmaline, which are known β-carboline alkaloids and potent hallucinogens, were studied in freshly isolated rat hepatocytes. The exposure of hepatocytes to harmine caused not only concentration (0-0.50mM)- and time (0-3h)-dependent cell death accompanied by the formation of cell blebs and the loss of cellular ATP, reduced glutathione, and protein thiols but also the accumulation of glutathione disulfide. Of the other analogues examined, the cytotoxic effects of harmaline and harmol (a metabolite of harmine) at a concentration of 0.5mM were less than those of harmine. The loss of mitochondrial membrane potential and generation of oxygen radical species in hepatocytes treated with harmine were greater than those with harmaline and harmol. In the oxygen consumption of mitochondria isolated from rat liver, the ratios of state-3/state-4 respiration of these β-carbolines were decreased in a concentration-dependent manner. In addition, harmine resulted in the induction of the mitochondrial permeability transition (MPT), and the effects of harmol and harmaline were less than those of harmine. At a weakly toxic level of harmine (0.25mM), it was metabolized to harmol and its monoglucuronide and monosulfate conjugates, and the amounts of sulfate rather than glucuronide predominantly increased with time. In the presence of 2,5-dichloro-4-nitrophenol (50μM; an inhibitor of sulfotransferase), harmine-induced cytotoxicity was enhanced, accompanied by decrease in the amount of harmol-sulfate conjugate, due to an increase in the amount of unconjugated harmol and the inhibition of harmine loss. Taken collectively, these results indicate that (a) mitochondria are target organelles for harmine, which elicits cytotoxicity through mitochondrial failure related to the induction of the MPT, mitochondrial depolarization, and inhibition of ATP synthesis; and (b) the toxic effects of harmine are greater than those of either its metabolite harmol or its analogue harmaline, suggesting that the onset of harmine-induced cytotoxicity may depend on the initial and/or residual concentrations of harmine rather than on those of its metabolites.

Occurrence and behavior of the chiral anti-inflammatory drug naproxen in an aquatic environment

The present study reports on the occurrence and chiral behavior of the anti-inflammatory drug (S)-naproxen (NAP)-(S)-2-(6-methoxynaphthalen-2-yl)propionic acid-in an aquatic environment under both field and laboratory conditions. In influents and effluents of sewage treatment plants (STPs) in the Tama River basin (Tokyo), (S)-NAP was detected at concentrations of 0.03 µg L(-1) to 0.43 µg L(-1) and 0.01 µg L(-1) to 0.11 µg L(-1), respectively. The concentrations of a major metabolite, 6-O-desmethyl NAP (DM-NAP) were up to 0.47 µg L(-1) and 0.56 µg L(-1) in influents and effluents, respectively. (R)-naproxen was not detected in STP influents, although it was present in effluents, and the enantiomeric faction (= S/[S + R]) of NAP ranged from 0.88 to 0.91. Under laboratory conditions with activated sludge from STPs, rapid degradation of (S)-NAP to DM-NAP and chiral inversion of (S)-NAP to (R)-NAP were observed. During river die-away experiments, degradation and chiral inversion of NAP were extremely slow. In addition, chiral inversion of (S)-NAP to (R)-NAP was not observed during photodegradation experiments. In the river receiving STP discharge, NAP and DM-NAP concentrations reached 0.08 µg L(-1) and 0.16 µg L(-1) , respectively. The enantiomeric faction of NAP in the river ranged from 0.84 to 0.98 and remained almost unchanged with the increasing contribution of rainfall to the river water. These results suggest that the absence and decrease of (R)-NAP in river waters could indicate the inflow of untreated sewage. E

Cytotoxic effects of 2,6-di-tert-butyl-4-methylphenyl N-methylcarbamate (terbutol) herbicide on hepatocytes and mitochondria isolated from male rats

The cytotoxic effects of 2,6-di-tert-butyl-4-methylphenyl N-methylcarbamate (terbutol) and its major metabolites were investigated in freshly isolated rat hepatocytes. Terbutol and its metabolite, especially 2,6-di-tert-butyl-4-methylphenyl carbamate (N-demethylterbutol), at a concentration of 1.0 mM resulted in a time dependent cell killing accompanied by losses of intracellular ATP, protein thiols, and glutathione (GSH) and the accumulation of oxidized GSH. Supplementation of the hepatocyte suspension with 5 mM N-acetylcysteine, a precursor of intracellular GSH, inhibited the cytotoxicity of N-demethylterbutol. In mitochondria isolated from rat liver, terbutol and its metabolites impaired respiration related to oxidative phosphorylation and the potency of their toxicity is associated with impairment of mitochondrial respiration. These results indicate that N-demethylterbutol is the most cytotoxic followed by terbutol and other metabolites, and that both the mitochondrial respiratory system and protein thiols are important targets for these compounds.