Carcinogenesis vol.19 no.9 pp.1603–1607, 1998 Synthesis and excretion profile of 1,4-[14C]phenylenebis(methylene)selenocyanate in the rat Karam El-Bayoumy1, Pramod Upadhyaya, Ock-Soon Sohn, José G.Rosa and Emerich S.Fiala American Health Foundation, 1 Dana Road, Valhalla, NY 10595, USA 1To whom correspondence should be addressed 1,4-Phenylenebis(methylene)selenocyanate (p-XSC) inhibits chemically induced tumors in several laboratory animal models. To understand its mode of action, we synthesized p-[14C]XSC, examined its excretion pattern in female CD rats and also the nature of its metabolites. p-[14C]XSC was synthesized from α,α-dibromo-p-[ring-14C]xylene in 80% yield. The excretion profile of p-[14C]XSC (15.8 mg/kg body wt, 200 µCi/rat, oral administration, in 1 ml corn oil) in vivo was monitored by measuring radioactivity and selenium content. On the basis of radioactivity, ~20% of the dose was excreted in the urine and 68% in the feces over 3 days. The cumulative percentages of the dose excreted over 7 days were 24% in urine and 75% in feces, similar to excretion rates of selenium. According to selenium measurement, <1% of the dose was detected in exhaled air; radioactivity was not detected. Only 15% of the dose was extractable from the feces with EtOAc and was identified as tetraselenocyclophane (TSC). Most of the radioactivity remained tightly bound to the feces. Approximately 10% of this bound material converted to TSC on reduction with NaBH4. Organic soluble metabolites in urine did not exceed 2% of the dose; sulfate (9% of urinary metabolites) and glucuronic acid (19.5% of urinary metabolites) conjugates were observed but their structural identification is still underway. Co-chromatography with a synthetic standard led to the detection of terephthalic acid (1,4-benzenedicarboxylic acid) as a minor metabolite. The major urinary conjugates contained selenium. Despite the low levels of selenium in the exhaled air, the reductive metabolism of p-XSC to H2Se cannot be ruled out. Identification of TSC in vivo indicates that a selenol may be a key intermediate responsible for the chemopreventive action of p-XSC. Introduction Chemoprevention refers to the administration of either synthetic or naturally occurring chemical agents that minimize or prevent tumor initiation (mutational) and/or tumor promoting events during the process of carcinogenesis (1). The list of agents with chemopreventive activity is growing rapidly (2). One important class of chemopreventive agents is that of organic and inorganic forms of selenium (3). Studies in our laboratory have focused on the design of synthetic organoselenium compounds with improved chemopreventive efficacy and lower toxicity than inorganic selenium compounds, and Abbreviations: AAS, atomic absorption spectrometry; BSC, benzyl selenocyanate; HPLC, high performance liquid chromatography; NMR, nuclear magnetic resonance; p-XSC, 1,4-phenylenebis(methylene)selenocyanate; THF, tetrahydrofuran; TMSe, trimethylselenonium; TSC, 1,4-tetraselenocyclophane. © Oxford University Press the naturally occurring selenoamino acids (e.g. selenomethionine) (3). Ideally, such agents would be used as dietary supplements to inhibit tumor development caused in different organs by various classes of chemical carcinogens. We have demonstrated repeatedly that one of the most effective of these organoselenium compounds, 1,4-phenylenebis (methylene)selenocyanate (p-XSC), inhibits tumors in the mammary glands, colon, lung and tongue of laboratory animals (4,5). Our results combined with other observations described in the literature make it clear that the chemopreventive efficacy of selenium as an anticarcinogen depends on the chemical form in which it is administered, suggesting that metabolism is a prerequisite for the cancer preventive potential of selenium compounds (6). Understanding the metabolism of organoselenium compounds is essential to determine whether the parent compound or any of its metabolites are responsible for the chemoprevention of tumorigenesis. To this end, and as an initial investigation, the synthesis of p-[14C]XSC, the most potent chemopreventive organoselenium agent, was performed, its excretion profile in female CD rats was studied and some of its metabolites were identified. We anticipate that more detailed knowledge of p-XSC metabolism will provide important leads to the development of even more effective chemopreventive organoselenium compounds. Materials and methods Apparatus Chromatographic analyses were done with a Waters Associates Model ALC/ GPC 204 high-performance, high-speed liquid chromatograph equipped with a Model 510 solvent delivery system, a Model U6K septumless injector, a Model 440 UV/visible detector and a Model 680 automatic gradient controller. Mass spectra were obtained on a Hewlett-Packard Model HP5988A mass spectrometer. 1H NMR studies were performed on a Bruker AM 360-MHz spectrophotometer, in DMSO-d6 and DMSO-d6/D2O. A Beckman Model LS9800 scintillation counter was employed for measuring radioactivity in a scintillation cocktail and radiochromatography was done with a radioactivity flow detector (Radiomatic Instruments and Chemical Co. Inc., Tampa, FL). Atomic absorption spectrometry (AAS) was employed for selenium determination, i.e. an AAS, Varian AA-1475 series (Varian Tectron, Springvale, Australia) was used. This instrument was equipped with a deuterium arc background correction and a Model GTA-95 graphite tube atomizer with sample dispenser. With argon (99.996%) as the sheath and purge gas, the parameters described by Voth-Beach and Shrader (7) were utilized for operating the furnace. A hollow cathode lamp was used with background correction in the ‘on’ position, lamp current, 10 or 12 mA; wavelength, 196 nm; slit, 1 nm. In most cases, samples were dissolved or diluted in 14% HNO3, and for each injection 40 µl of sample was introduced into the pyrolytically-coated graphite tube along with 10 µl of reduced Pd matrix modifier (3.33 g of PdCl2/l, 2% hydroxylamine hydrochloride and 2% HCl) by the sample dispenser (8). The peak height of absorbance was recorded, and the analyses were based on the mean of duplicate injections. Ganther et al. (9) have described the difficulties encountered in the analysis of trimethylselenonium ion (TMSe) in the urine by AAS. In order to address this problem, the iodine salt of TMSe was obtained commercially (Organometallics Inc., East Hampstead, NH) and dissolved in H2O. Indeed, we found that TMSe was underestimated by our method upon using a final concentration of 0.35% of HNO3. However, with HNO3 concentration of 7% or even higher (14%), which is used in the current study, we achieved 100% recovery. In the case of rat urine spiked with TMSe, the recovery was ~80% at 7% HNO3. The reason for this difference is not 1603 K.El-Bayoumy et al. Fig. 1. Electron impact mass spectrum of 1,4-tetraselenocyclophane. yet clear. However, when urine samples that had been spiked with TMSe were digested using the microwave digestion system as described previously (8), full recovery was achieved. This experimental approach was used for the analysis of urine samples from rats treated with p-XSC. Chemicals p-XSC was obtained as described previously (10). α,α-Dibromo-p-[ring14C]xylene was obtained commercially (Chemsyn Science Laboratories, Lenexa, KS; 100 mCi/mmol, radiochemical purity .95%). Briefly, the synthesis of p-[14C]XSC was as follows. As for the synthesis of [14C]benzyl selenocyanate (BSC) (11,12), and for the unlabeled p-XSC (10), the bromo compound was added dropwise to a solution of KSeCN in acetone at room temperature and was stirred for 12 h. The reaction mixture was diluted with CH2Cl2 and washed with H2O. The organic layer was dried over MgSO4 and concentrated under reduced pressure. The pure p-[14C]XSC was purified by HPLC; Rt 5 22–23 min, with an elution gradient of 20% CH3OH–H2O to 100% CH3OH in 60 min at a flow rate of 3 ml/min, using a semi-preparative Vydac-C18-10 µ reverse phase column (1.3325 cm, Separations Group, Hesperia, CA). The yield was 80% and the purity of the compound was .96% as ascertained by HPLC and radioflow monitored radioactivity. Synthesis of 1,4-tetraselenocyclophane (TSC) To a solution of p-XSC (0.314 g, 1 mmol) in dry THF (34 ml), a solution of KOH (0.06 g, 1 mmol) in CH3OH (34 ml) was added over a period of 4 h at room temperature under N2. During this time, the solution turned cloudy and then yellowish. The reaction mixture was stirred overnight at which point TLC (100% CH2Cl2) showed the complete disappearance of p-XSC (Rf 0.58). The polymer by-product was collected by filtration as a yellow powder (0.2162 g). The filtrate was concentrated in vacuo to yield the crude TSC. Purification by column chromatography on silica (initially eluted with hexane, and gradually increasing CH2Cl2 until final elution with 40% CH2Cl2 in hexane) yielded a pure product (0.017 g, 3%), Rf 0.85 (CH2Cl2). The mass spectrum (Figure 1) showed the following fragmentation (m/z, relative intensity) 528 (M1, 4%), 448 (M1-Se, 88%), 368 (M1-2Se, 12%), 288 (M13Se, 65%), 208 (M1-4Se, 30%); 1H NMR (CDCl3) δ 7.16 (s, 8H, ArH), 3.75 (s, 8H, -CH2); HPLC (254 nm) Rt was 65 min with an elution gradient of 20% CH3OH–H2O to 100% CH3OH over 60 min at a flow rate of 3 ml/min, using a semipreparative Vydac-C18-10 µ reverse phase column. The polymer by-product (0.05 g) was suspended in 2 ml of 4:1 THF:0.5 N NaOH and 1 ml of CH3OH and then subjected to NaBH4 reduction in a N2 atmosphere. The reaction mixture was stirred for 10 min at 0°C and allowed to warm up to room temperature over a period of 60 min under N2. The flow of N2 was terminated and the reaction mixture continuously stirred overnight at room temperature. At this time, CH2Cl2 (5 ml) was added and the reaction mixture filtered. The filtrate was washed with H2O (4310 ml), and the organic layer dried and evaporated under reduced pressure to give a slightly yellow solid in 20% yield. This solid had HPLC characteristics identical to those of the synthetic standard, TSC. Enzymes and reagents Arylsulfatase (from limpets, type V) and β-glucuronidase (from Escherichia coli, type IX) were purchased from Sigma (St Louis, MO). Monofluor was acquired from National Diagnostics (Somerville, NJ). In vivo metabolism of p-[14C]XSC in the rat Female CD rats, ~200 g, body wt each, obtained from Charles River Breeding Laboratories (Wilmington, MA), were acclimated for 2 weeks prior to metabolism studies. Four rats (one rat/chamber) were housed in Delmar– Roth-type glass metabolism chambers (Bioserv Inc., Frenchtown, NJ) designed for urine and feces collection, and for trapping volatile metabolites in the exhaled air over three sequential traps with 8 N HNO3 (13). Rats were fed a 1604 modified AIN-76A semipurified high-fat diet (10) 1 week before and then throughout the experiment; diet and water were given ad libitum. The metabolism room was controlled at 22 6 1°C and 50% humidity, 12 h light/ dark cycle. p-[14C]XSC was administered by intragastric gavage in 1 ml corn oil at a dose of 15.8 mg/kg body wt, 200 µCi/rat. Urine and feces were collected every 24 h for 7 days and stored below 0°C until analysis. The contents of the gas wash bottles were checked for [14C] radioactivity and selenium content daily for 1 week following p-XSC administration. Analysis of urinary and fecal metabolites of p-[14C]XSC Rat urine was extracted with ethyl acetate or benzene. The extract was dried (MgSO4) and concentrated to dryness, and the residue dissolved in THF and analysed by HPLC using a linear gradient from 2% CH3COOH in H2O to 100% CH3OH in 60 min at a flow rate of 3 ml/min using a Vydac-C18-10 µ reverse phase column (1.3325 cm). Fractions were collected and analysed for selenium content using AAS. For the isolation of water-soluble metabolites, urine was adjusted to pH 5.5 with citrate buffer and the mixture incubated with β-glucuronidase or arylsulfatase for 4 h at 37°C. In a typical experiment, 10 000 U (3 mg) of β-glucuronidase, or 63 U (5 mg) of arylsulfatase, and 20 mg of saccharic acid 1,4-lactone were used for each 10 ml of pH-adjusted urine sample. Control experiments were performed as described above but in the absence of enzymes. Feces were suspended in 50% ethyl acetate–ethanol and vortexed at 37°C for 30 min. The residue was filtered and the filtrate was dried (MgSO4), concentrated and analysed by HPLC. The percentage of recovery of radioactivity eluted from the HPLC column was determined to be 96.7 6 5.2%. AAS was used for selenium determination in urine and exhaled air (8,14). Urine samples were diluted with 14% HNO3 prior to analysis by AAS. Results The time courses of excretion of radioactivity in urine and feces after oral administration of p-[14C]XSC to female CD rats are depicted in Figure 2. Approximately 20% of the dose was excreted in urine and 68% was excreted in the feces over the course of 3 days. The cumulative percentages of the dose excreted over 7 days were 24% in urine and 75% in feces; consistent with a previous report, the analysis of selenium content by AAS yielded comparable results (14). Less than 1% of the dose, based on selenium measurement, was detected in the exhaled air; the latter was free of radioactivity. Only 15% of the dose was extractable from the feces with EtOAc. HPLC analysis of the EtOAc extract showed a major and a minor peak (Figure 3A); the major peak was identified as TSC based on comparison of its chromatographic characteristics with those of the synthetic standard. Although the synthesis and characterization of other selenocyclophanes have been described (15,16), this is the first report on the synthesis of TSC. To determine the nature of the unextractable radioactivity, the remaining dried pellets were suspended in 4:1 THF:0.5 N NaOH and reduced with NaBH4 in CH3OH. The outcome of this experiment indicates the formation of TSC in ~10% yield (Figure 3B). Approximately 1.8% of the dose was extractable with Synthesis and excretion profile of p-XSC Fig. 2. Excretion of radioactivity following administration of p-[14C]XSC to female CD rats by gavage. For urine analysis, each time point represents the average of four individual rats. For fecal analysis, each time point represents one animal, since feces from three rats were pooled to obtain ample materials for spectral analysis. Fig. 4. Radiochromatogram obtained upon reverse phase HPLC analysis of whole urine. On the basis of enzyme hydrolysis, peaks 1 and 4 were identified as glucuronic acid and sulfate conjugate, respectively. Peak 3 was identified as terephthalic acid (1,4-benzenedicarboxylic acid) based on co-chromatography with the standard. Peaks 2, 5 and 6 remain to be identified. 3) all other peaks contain selenium. On the basis of cochromatography, peak 3 was assigned as terephthalic acid; as expected, it did not contain any measurable selenium. Enzymatic hydrolysis of water-soluble metabolites indicated the presence of sulfate (9% of urinary metabolites) and glucuronide conjugates (19.5% of urinary metabolites). The radioactivity eluting between 29–31 min (peak 4) decreased drastically following sulfatase hydrolysis. Radioactivity eluting between 10–12 min (peak 1) almost disappeared upon β-glucuronidase hydrolysis. These results indicate that peaks 1 and 4 are glucuronic acid and sulfate conjugates, respectively. Structural determination of these two major urinary conjugates requires further investigation. Discussion Fig. 3. Radiochromatogram obtained upon reverse phase HPLC analysis of EtOAc extractable metabolite from feces (A); NaBH4 reduction of the unextractable material in the feces (B). EtOAc, but ,0.05% of the dose was extractable with benzene from the urine. Figure 4 shows a typical radiochromatogram obtained upon HPLC analysis of 24 h urine sample after p-XSC administration. Qualitatively similar radiochromatograms were obtained following HPLC analysis of urine voids collected after 48, 72 and 168 h. Analysis of urine fractions collected, clearly showed that (with the exception of peak The purpose of this study was to examine the excretion profile and to provide some structural information of in vivo metabolites of p-XSC in an animal model (female CD rats) that is currently being used in efficacy studies for the evaluation of organoselenium compounds as chemopreventive agents against mammary cancer. Such knowledge is essential to understand the mode of action of p-XSC and provide insights as to those forms of selenium that are responsible for its chemopreventive effects (4,17). The dose of p-XSC was selected based on our previous study (14) in which two doses (15.8 and 1.58 mg/kg body wt) were employed. The results of the excretion kinetics were highly comparable at the two dose levels (14). Therefore, for comparative purposes, we used 15.8 mg/kg body wt in the present investigation. In chemoprevention protocols a range of doses (5, 10, 15 and 40 p.p.m. as selenium in the diet) was used (10,17). Accordingly, one can estimate the daily dietary intake of selenium. For example, at 15 p.p.m. selenium in the diet, the daily consumption would amount to 300 µg selenium per 200 g rat consuming 20 g diet/day; this is comparable with a single oral administration of 1.58 mg/kg body wt which was used in our previous study (14). The results indicate that fecal elimination is the major route of excretion; TSC was identified as a minor fecal metabolite. However, detectable amounts of the parent compound, pXSC, were not observed. Although the major portion of the 1605 K.El-Bayoumy et al. radioactivity excreted in the feces remained unknown, it appeared that a high molecular weight metabolite(s) containing an Se–S bond may be present. This notion is based on the fact that this material was not extractable in organic solvents, but yielded TSC upon NaBH4 treatment. Collectively, these results indicate that the facile reaction of p-XSC with proteins and amino acids containing a thiol (-SH) functionality can yield intermediates with an Se–S bond. This type of reaction has been demonstrated with organoselenium compounds (12,18– 20). Moreover, compounds containing functional groups other than selenocyanate (e.g. ebselen) were postulated to react with proteins containing SH groups to form Se–S-containing intermediates (21). Reductive cleavage of the Se–S bond of such intermediates will lead to the formation of selenols that will be highly susceptible to oxidation to form diselenide containing the Se–Se functionality. In the present study, the reductive metabolism of such an intermediate metabolite(s) derived from p-XSC, led to the formation of selenols and, finally, to TSC. The formation of selenols is of particular significance since it is now well established that the anti-tumor properties of selenium compounds are strongly influenced by their metabolism and, furthermore, selenols appear to be important intermediates in cancer prevention by selenium compounds (6,12,22–24). We have demonstrated previously the formation of benzyl selenol, benzyl seleninic acid and dibenzyl diselenide as metabolites of BSC (12). We hypothesize that selenols derived from aryl selenocyanate may be acting as chemopreventive intermediates in a similar fashion as methyl selenol derived from sodium selenite (6,20,21). Therefore, the role of TSC and possibly that of selenols derived from p-XSC in efficacy studies will be evaluated shortly in our laboratories. The anti-tumor properties of selenite are strongly influenced by its metabolism. After absorption, selenite is reduced by glutathione via selenodiglutathione to the highly toxic H2Se (6,25). The latter can be incorporated as selenocysteine into selenoproteins, such as glutathione peroxidases (26–29), type I iodothyronine deiodinase (30,31), or the 57 kDa plasma selenoprotein and selenoprotein P (32). H2Se is methylated to mono-, di- and tri-methylated derivatives before excretion. Several experiments with compounds that are directly converted into methyl selenol indicate that the latter mediates the anticarcinogenic effect of selenite (6,23,24). In the case of p-XSC metabolism, ,1% of the selenium dose was detected in the exhaled air. Despite the low levels of selenium in the exhaled air, the reductive metabolism of p-XSC to H2Se cannot be ruled out. In fact, Ip et al. (17) have shown that p-XSC restores glutathione peroxidase activity in selenium-deficient rats which supports the formation, although minor, of inorganic selenium. Our results indicate that urine is a minor route of excretion; water-soluble metabolites constitute most of the radioactivity excreted in urine after oral administration of p-[14C]XSC. We did not detect TMSe as a urinary metabolite. Moreover, unmetabolized p-XSC was not detected in the organic-extractable metabolites of urine that accounted for ,2% of the dose. The lack of selenium in peak 3 and its chromatographic characteristics support the identity of this metabolite as terephthalic acid. Cleavage of selenium from p-XSC leading to the formation of terephthalic acid in the urine is a minor pathway; an observation which is in line with the low levels of selenium found in the exhaled air as described above. Although this constitutes only a minor urinary metabolite, its formation is 1606 expected since, in our previous investigation, we were able to identify benzoic acid as a metabolite from the monofunctional selenocyanate compound BSC (12). Selenols are highly nucleophilic in nature and their biotransformation to glucuronic acid conjugates has been suggested with other organoselenium compounds (21). On the basis of enzyme hydrolysis, we demonstrated that peak 1 is a glucuronic acid conjugate; the same approach was also used to assign peak 4 as a sulfate conjugate. Unequivocal structural identification of these conjugates requires further investigation. In the present investigation, we did not measure levels of selenium in various organs since we have already reported (14) that ,5% of selenium was distributed among all major organs of the rat following the oral administration of p-XSC at a dose equal to that used here. However, in a separate study (unpublished data) and under chemoprevention protocols (15 p.p.m. as selenium in the diet), we found that the liver had the highest selenium content, followed by the kidney and the target organ (mammary) had the lowest selenium content. The method employed for selenium analysis in these organs cannot provide structural information on the form of selenium (14). Collectively, on the basis of the present investigation and results described in the literature, we believe that the major focus in cancer prevention by organoselenium compounds may be directed toward the design of agents that lead to the facile formation of selenols in vivo. Currently, our efforts focus on testing this hypothesis. Acknowledgements We thank Mrs Patricia Sellazzo for preparing, and Mrs Ilse Hoffmann for editing, this manuscript. This work was supported by grant CA 46589 from the National Cancer Institute. This is paper no. 24 in the series ‘Selenium in the Chemoprevention of Carcinogenesis’. References 1. Wattenberg,L.W. (1985) Chemoprevention of cancer. Cancer Res., 45, 1–8. 2. Boone,C.W., Kelloff,G.J. and Malone,W.E. (1990) Identification of candidate cancer chemopreventive agents and their evaluation in animal models and human clinical trials: a review. Cancer Res., 50, 2–9. 3. El-Bayoumy,K. (1991) The role of selenium in cancer prevention. In DeVita,V.T. Jr, Hellman,S. and Rosenberg,S.A. (eds) Cancer Prevention. J. B. Lippincott Company, Philadelphia, pp. 1–15. 4. El-Bayoumy,K., Upadhyaya,P., Chae,Y.-H., Sohn,O.-S., Rao,C.V., Fiala,E. and Reddy,B.S. (1995) Chemoprevention of cancer by organoselenium compounds. J. Cell. Biochem., 22 (Suppl.), 92–100. 5. Tanaka,T., Makita,H., Kawabata,K., Mori,H. and El-Bayoumy,K. (1997) 1,4-Phenylenebis(methylene)selenocyanate exerts exceptional chemopreventive activity in rat tongue carcinogenesis. Cancer Res., 57, 3644–3648. 6. Ganther,H.E. and Lawrence, J.R. (1997) Chemical transformations of selenium in living organisms. Improved forms of selenium for cancer prevention. Tetrahedron, 53, 12299–12310. 7. Voth-Beach,L.M. and Shrader,D.E. (1986) Graphite furnace atomic absorption spectroscopy: new approaches to matrix modification. Spectroscopy, 1, 49–59. 8. Sohn,O.-S., Blackwell,L., Mathis,J., Asaad,W.W., Reddy,B.S. and ElBayoumy,K. (1991) Excretion and tissue distribution of selenium following treatment of male F344 rats with benzylselenocyanate or sodium selenite. Drug Metab. Dispos., 19, 865–870. 9. Ganther,H.E., Kraus,R.J. and Foster,S.J. (1986) Trimethylselenonium ion. Method. Enzymol., 143, 195–201. 10. El-Bayoumy,K., Chae,Y.-H., Upadhyaya,P., Meschter,C., Cohen,L.A. and Reddy,B.S. (1992) Inhibition of 7,12-dimethylbenz(a)anthracene-induced tumors and DNA adduct formation in the mammary glands of female Sprague–Dawley rats by the synthetic organoselenium compound 1,4phenylenebis(methylene)selenocyanate. Cancer Res., 52, 2402–2407. 11. El-Bayoumy,K. (1985) Effects of organoselenium compounds on induction of mouse forestomach tumors by benzo(a)pyrene. Cancer Res., 45, 3631–3635. Synthesis and excretion profile of p-XSC 12. El-Bayoumy,K., Upadhyaya,P., Date,V., Sohn,O.-S., Fiala,E.S. and Reddy,B. (1991) Metabolism of [14C]benzyl selenocyanate in the F344 rat. Chem. Res. Toxicol., 4, 560–565. 13. Vadhanavikit,S., Ip,C. and Ganther,H.E. (1993) Metabolites of sodium selenite and methylated selenium compounds administered at cancer chemoprevention levels in the rat. Xenobiotica, 23, 731–745. 14. Sohn,O.-S., Li,H., Surace,A., El-Bayoumy,K., Upadhyaya,P. and Fiala,E.S. (1995) Contrasting patterns of selenium excretion by female CD rats treated with chemically related chemopreventive organic selenocyanate componds. Anticancer Res., 15, 1849–1856. 15. Mitchell,R.H. (1976) 2,3,12,13-Tetraselena[4,4]metacyclophane. A disparity with the literature. Can. J. Chem., 54, 238–241. 16. Hojjatie,M., Muralidharan,S. and Freiser,H. (1989) Synthesis and multinuclear NMR characterization of some [3.3]diselena- and [4.4]tetraselenacyclophanes. Tetrahedron, 45, 1611–1622. 17. Ip,C., El-Bayoumy,K., Upadhyaya,P., Ganther,H., Vadhanavikit,S. and Thompson,H. (1994) Comparative effect of inorganic and organic selenocyanate derivatives in mammary cancer chemoprevention. Carcinogenesis, 15, 187–192. 18. Hasegawa,T., Mihara,M., Okuno,T., Nakamuro,K. and Sayato,Y. (1995) Chemical form of selenium-containing metabolite in small intestine and liver of mice following orally administered selenocystine. Arch. Toxicol., 69, 312–317. 19. Hasegawa,T., Okuno,T., Nakamuro,K. and Sayato,Y. (1996) Identification and metabolism of selenocystein-glutathione selenenyl sulfide (CySeSG) in small intestine of mice orally exposed to selenocystine. Arch. Toxicol., 71, 39–44. 20. Clark,E.R. and Al-Turaihi,M.A.S. (1977) The reaction of o-nitro and p-nitrophenyl selenocyanates with arylthiols. J. Organomet. Chem., 134, 181–187. 21. Fischer,H., Terlinden,R., Lohr,J.P. and Römer,A. (1988) A novel biologically active seleno-organic compound. VIII. Biotransformation of ebselen. Xenobiotica, 18, 1347–1359. 22. Ip,C. and Ganther,H. (1988) Efficacy of trimethylselenonium versus selenite in cancer chemoprevention and its modulation by arsenite. Carcinogenesis, 9, 1481–1484. 23. Ip,C., Hayes,C., Budnick,R.M. and Ganther,H.E. (1991) Chemical form of selenium, critical metabolites and cancer prevention. Cancer Res., 51, 595–600. 24. Ip,C. and Ganther,H.E. (1990) Activity of methylated forms of selenium in cancer prevention. Cancer Res., 50, 1206–1211. 25. Ganther,H. (1984) Selenium metabolism and function in man and animals. In Brutter,P and Schramel,P. (eds) Trace Element—Analytical Chemistry in Medicine and Biology, Vol. 3. Walter de Gruyter, Germany, pp. 3–24. 26. Chambers,I., Frampton,J., Goldfarb,P., Affara,N., McBain,W. and Harrison,P.R. (1986) The structure of the mouse glutathione peroxidase gene: the selenocysteine in the active site is encoded by the ‘termination’ codon, TGA. EMBO J., 5, 1221–1227. 27. Takahashi,K., Akasaka,M., Yamamoto,Y., Kobayashi,C., Mizoguchi,J. and Koyama,J. (1990) Primary structure of human plasma glutathione peroxidase deduced from cDNA sequences. J. Biochem., 108, 145–148. 28. Yoshimura,S., Watanabe,K., Suemizu,H., Onozawa,T., Mizoguchi,J., Tsuda,K., Hatta,H. and Moriuchi,T. (1991) Tissue specific expression of the plasma glutathione-peroxidase gene in rat kidney. J. Biochem., 109, 918–923. 29. Schuckelt,R., Brigelius-Flohe,R., Maiorino,M., Roveri,A., Reumkens,J., Strassburger,W., Usani,F., Wolf,B. and Flohe,L. (1992) Phospholipidhydroperoxide glutathione peroxidase is a selenoenzyme distinct from the classical glutathione peroxidase as evident from cDNA and amino acid sequencing. Free Rad. Res. Commun., 14, 343–361. 30. Berry,M.J., Banu,L. and Larsen,P.R. (1991) Type I iodothyronine deiodinase is a selenocysteine containing enzyme. Nature, 349, 438–440. 31. Arthur,J.R., Nicol,F., Grant,E. and Beckett,G.H. (1991) The effects of selenium deficiency on hepatic type-I iodothyronine deiodinase and protein disulphide isomerase assessed by activity measurements and affinity labelling. Biochem. J., 274, 297–300. 32. Hill,K.E., Lloyd,R.S., Yang,J.-G., Read,R. and Burk,R.F. (1991) The cDNA for rat selenoprotein P contains 10 TGA codons in the open reading frame. J. Biol. Chem., 266, 10050–10053. Received on March 9, 1998; revised on May 22, 1998; accepted on May 29, 1998 1607
© Copyright 2026 Paperzz