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E Dybing

Publications and source records attributed to E Dybing.

At least 73 records · Page 4Linked to original sources
PubMed1991

Co-culture systems for assessing the stability and genotoxicity of reactive 1,2-dibromo-3-chloropropane (DBCP) metabolites.

1,2-Dibromo-3-chloropropane (DBCP) induced DNA damage, measured by alkaline elution, at low concentrations (5-10 microM) in suspensions of hepatocytes and testicular cells isolated from rats. At higher concentrations (greater than or equal to 100 microM) DBCP caused DNA damage and increased the frequency of sister chromatid exchanges in Chinese hamster V79 cells. When DBCP (2.5-10 microM) was tested for its ability to cause unscheduled DNA synthesis (UDS) in monolayers of liver cells isolated from untreated rats, a clear positive response was obtained. No increase in UDS was detectable when liver cells isolated from PCB-pretreated rats were used. In contrast, DBCP (greater than or equal to 50 microM) was metabolized in hepatocytes from PCB-pretreated rats to products mutagenic to Salmonella typhimurium TA100 in co-culture with the hepatocytes, whereas control hepatocytes were substantially (40-fold) less active. No bacterial mutagenicity could be detected when the TA100 strain was co-incubated with isolated rat testicular cells and DBCP. In co-cultures of hepatocytes and V79 cells DBCP-induced DNA damage in V79 cells occurred at low concentrations (10 microM DBCP) compared to the concentration (100 microM) needed to induce DNA damage in the V79 cells incubated without hepatocytes. Testicular cells were not able to enhance DBCP-induced DNA damage in the V79 cells. The data indicate that the putative reactive DBCP episulphonium ion metabolite formed in the testicular cells presumably responsible for testicular cell DNA damage, is not capable of escaping the cell where it is formed. Other reactive DBCP metabolites generated in the liver cells seem to be able to interact with the DNA of neighbouring cells.

Animals↗
PubMed1990

Metabolic activation of 1,2-dibromo-3-chloropropane: evidence for the formation of reactive episulfonium ion intermediates.

The nematocide and soil fumigant 1,2-dibromo-3-chloropropane (DBCP) is a carcinogen and a mutagen and displays target-organ toxicity to the testes and the kidney. It has been proposed that both cytochrome P-450 mediated activation and glutathione (GSH) conjugation pathways are operative in DNA damage and organotropy induced by DBCP. To determine the chemical mechanisms involved in the bioactivation of DBCP and to assess a role for an episulfonium ion intermediate, the mechanism of formation of GSH conjugate metabolites of DBCP was investigated. Five biliary GSH conjugates of DBCP were isolated from rats and identified by fast atom bombardment tandem mass spectrometry: S-(2,3-dihydroxy-propyl)glutathione (I), S-(2-hydroxypropyl)glutathione (IIA), S-(3-chloro-2-hydroxypropyl)glutathione (III), 1,3-di(S-glutathionyl)propan-2-ol (IV), and 1-(glycyl-S-cysteinyl)-3- (S-glutathionyl)propan-2-ol (V). The mechanisms of conjugate formation were addressed by assessing deuterium retention in conjugates derived from [1,1,2,3,3-2H5] DBCP (D5-DBCP). GSH conjugates I, III, IV, and V displayed quantitative retention of deuterium, an observation consistent with the formation of an episulfonium ion intermediate. GSH conjugate IIA, however, retained three atoms of deuterium, thus invoking a P-450 mechanism in its genesis. The involvement of glutathione transferase (GST) and sequential episulfonium ion intermediates in the formation of metabolites I, III, and IV was demonstrated in vitro. Upon incubation of DBCP with GST, metabolites I, III, and IV were identified by tandem mass spectrometry and were found to arise with quantitative retention of deuterium when D5-DBCP was employed as a substrate. An additional GSH conjugate, 1,2,3-tri(S-glutathionyl)propane (VI), was observed as the major metabolite in incubations of GST with DBCP. When the incubations of DBCP with GST were performed in H2(18)O, metabolite I incorporated two atoms of 18O, and metabolites III and IV incorporated one atom of 18O. The ability of GST to catalyze the formation of the four GSH conjugates observed in vivo, with quantitative retention of deuterium and incorporation of 18O from H2(18)O, may be rationalized by a mechanism invoking the initial formation of S-(2-bromo-3-chloropropyl)glutathione. Rearrangement of this unstable conjugate via several reactive episulfonium ions, with either hydrolysis by water or alkylation of GSH at various stages, would account for the pattern of metabolites and their status of isotopic enrichment observed under various incubation conditions.(ABSTRACT TRUNCATED AT 400 WORDS)

Animals↗
PubMed1990

Formation of genotoxic products from N-nitrosoheptamethyleneimine (NHMI), 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK) and N'-nitrosonornicotine (NNN) by isolated rabbit lung cells.

The genotoxic potentials of N-nitrosoheptamethyleneimine (NHMI), 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK) and N'-nitrosonornicotine (NNN) were studied in fresh preparations of Clara cells and type II cells isolated by centrifugal elutriation and density gradient centrifugation, and macrophages from rabbit lung. The activation of the compounds to bacterial mutagens was assayed in the Salmonella mutagenicity test using strains of TA 100 and TA 1530 preincubated with test chemicals and cells placed in chambers with nucleopore membranes to separate cells and bacteria. Unscheduled DNA synthesis was measured by incorporation of [3H]-thymidine in the cells after exposure to the compounds. NHMI, NNK and NNN were not activated to bacterial mutagens by Clara cells, type II cells or macrophages, presumably because the reactive metabolites generated were not released into the incubation medium. However, NHMI and NNK increased unscheduled DNA synthesis in Clara cells, and the highest repair activity was found after incubation with NNK. The effect of NNN was only marginal. This indicates that NHMI and NNK are genotoxic in the rabbit lung and that the Clara cells are involved in the metabolic activation of these compounds.

Animals↗
PubMed1990

Species differences in short term toxicity from inhalation exposure to bromobenzene.

Lung, liver and kidney injury were studied in mice, rats and rabbits 48 h after termination of a 4 h inhalation exposure to bromobenzene vapour (250-3400 ppm). Light and electron microscopy of lung tissue revealed injury to Clara cells and adjacent epithelium in mouse bronchioli (bromobenzene concentration 250 ppm and 1000 ppm) and to Clara cells of rat bronchi and bronchioli (1000 ppm bromobenzene) and of rabbit bronchi (2500 ppm and 3400 ppm). Histological and clinicochemical indices of liver damage were found in the same animals, whereas kidney toxicity was observed in mice (two out of ten showed tubular necrosis and elevated concentration of plasma urea) and rats (all had elevated plasma concentrations of creatinine) exposed to 1000 ppm bromobenzene. Inhalation exposure thus produced less kidney injury than expected from previous studies with equimolar doses given intraperitoneally. The mouse was the most severely affected species, followed by the rat, and lastly the rabbit. The animal susceptibility could not be ranked according to the rate of 14C-bromobenzene covalent binding in lung or liver, but it was inversely related to the rate of N-demethylation of benzphetamine (indicative of P450IIB activity) in both lung and liver microsomal preparations. Differences in a P450 mediated detoxification could therefore be of importance in species variability to bromobenzene injury.

Administration, Inhalation↗
PubMed1990

Species differences in kidney necrosis and DNA damage, distribution and glutathione-dependent metabolism of 1,2-dibromo-3-chloropropane (DBCP).

Species differences and mechanisms of 1,2-dibromo-3-chloropropane (DBCP) nephrotoxicity were investigated by studying DBCP renal necrosis and DNA damage, distribution and glutathione-dependent metabolism in rats, mice, hamsters and guinea pigs. Extensive renal tubular necrosis was observed in rats 48 hr after a single intraperitoneal administration (21-170 mumol/kg) of DBCP. Significantly less necrosis was found in mice and guinea pigs, whereas no renal damage was evident (less than 680 mumol/kg) in hamsters. The activation of DBCP to DNA damaging intermediates in vivo, as measured by alkaline elution of DNA isolated from kidney nuclei 60 min. after intraperitoneal injection of DBCP, was compared in all four species. Distinct DNA damage was detected in rats, mice and hamsters as early as 10 min. after administration of DBCP and within 30 min. in guinea pigs. Rats and guinea pigs showed similar sensitivity towards DBCP-induced DNA damage (extensive DNA damage greater than 21 mumol/kg DBCP), whereas in mice and hamsters a 10-50 times higher DBCP dose was needed to cause a similar degree of DNA damage. Renal DBCP concentrations at various time-points (20 min., 1, 3 and 8 hr) after intraperitoneal administration (85 mumol/kg) revealed that the initial (20 min.) DBCP concentration was substantially higher in rats and guinea pigs compared to the other two species. Furthermore, kidney elimination of DBCP occurred at a significantly lower rate in rats than in mice, hamsters and guinea pigs.(ABSTRACT TRUNCATED AT 250 WORDS)

Acute Kidney Injury↗
PubMed1990

Short term inhalation of bromobenzene: methodology and absorption characteristics in mouse, rat and rabbit.

In a dynamic inhalation system, mice, rats and rabbits were exposed to bromobenzene vapour (250-3400 p.p.m.) for 4 hr. Blood concentrations of bromobenzene were determined by head-space gas chromatography. After inhalation of 1000 p.p.m. for 4 hr, concentrations of 153, 102 and 47 micrograms bromobenzene/ml blood were found in mice, rats and rabbits, respectively. In vitro experiments showed a blood/air partition coefficient at 37 degrees of approximately 200, which was reflected by a linear uptake of bromobenzene up to an air concentration of 2500 p.p.m. Compared with results obtained previously by intraperitoneal bromobenzene administration inhalation resulted in higher blood concentrations.

Absorption↗
PubMed1989

Species differences in testicular necrosis and DNA damage, distribution and metabolism of 1,2-dibromo-3-chloropropane (DBCP).

The human testicular toxicant 1,2-dibromo-3-chloropropane (DBCP) was studied for the same end-point in 4 different species of laboratory animals. Marked necrosis and atrophy of the seminiferous epithelium were observed in rats and guinea pigs 10 days after a single i.p. administration of DBCP (170-340 mumol/kg), whereas significantly less damage was observed in hamsters and mice. The testicular concentrations of DBCP measured at various time-points after the i.p. injection of DBCP indicated that factors in addition to tissue concentration were of importance for the observed species differences in sensitivity towards DBCP-induced testicular damage. Also, there did not seem to be any direct correlation between DBCP-induced in vivo testicular toxicity and in vitro GSH-dependent dehalogenation, inasmuch as the rate of bromide release from DBCP with hamster testicular cytosol was as fast as that with rat cytosol. Testicular DNA damage, as determined by alkaline elution 60 min after in vivo administration of 170 mumol/kg DBCP, was observed only in rats and guinea pigs. Thus, induction of DNA damage correlates with the relative susceptibilities of the species towards DBCP-induced testicular necrosis. To further study species differences in testicular activation of DBCP to DNA-damaging intermediate(s), cells isolated from the testes of the 4 species were incubated with DBCP. Testicular cells from rats and guinea pigs were the only preparations developing substantial DNA damage after 60 min incubation with low concentrations of DBCP (5-50 microM). The findings indicate that rats are sensitive towards DBCP-induced testicular necrosis because rat testicular cells easily activate DBCP to a DNA-damaging intermediate(s). The relative high testicular DBCP concentration as well as the ability to activate DBCP may explain the sensitivity of guinea pigs towards DBCP-induced testicular toxicity.

Animals↗
PubMed1989

Role of P-450 activity and glutathione levels in 1,2-dibromo-3-chloropropane tissue distribution, renal necrosis and in vivo DNA damage.

Treatments known to alter P-450 activity and glutathione levels were used to elucidate the involvement of P-450 and glutathione S-transferase metabolism in 1,2-dibromo-3-chloropropane (DBCP) organ toxicity in the rat. Phenobarbital pretreatment abolished DBCP-induced renal necrosis, whereas it had only a small effect on initial renal DNA damage. The DBCP levels in plasma and tissues were markedly reduced by phenobarbital pretreatment. Perdeuterated DBCP had much higher plasma and tissue levels than protio-DBCP in phenobarbital-pretreated animals, but perdeuteration was without effect in uninduced animals. This indicates that P-450 metabolism of DBCP is of major importance only in phenobarbital-pretreated animals. In order to study the effects of decreased glutathione levels on renal distribution and toxicity, rats were pretreated with either diethyl maleate or buthionine sulfoximine. The DBCP levels in plasma and tissues showed transitory elevations after diethyl maleate and buthionine sulfoximine pretreatment compared to the control situation. Despite the fact that diethyl maleate and buthionine sulfoximine pretreatments are known to block DBCP-induced DNA damage in vitro, these pretreatments did not significantly alter DBCP-induced renal necrosis nor DNA damage. Thus, a role for glutathione conjugation in DBCP-induced in vivo renal toxicity could not be established in the present study.

Animals↗
PubMed1989

Metabolism of selectively methylated and deuterated analogs of 1,2-dibromo-3-chloropropane: role in organ toxicity and mutagenicity.

In vitro bromide release and in vivo glutathione (GSH) depletion in rat liver, kidney and testis by 1,2-dibromo-3-chloropropane (DBCP) and selectively methylated and deuterated DBCP analogs were studied. With liver microsomes from phenobarbital-pretreated rats the bromide release from the C1-C3-D4- and the perdeuterated DBCP analogs were 54% and 26% of that of DBCP, respectively. Inhibitors of P-450 reduced the bromide release to 10-20% of that without additions. This correlated with the effects of deuterium substitution and additions of P-450 inhibitors on DBCP-induced bacterial mutagenicity as reported elsewhere by this laboratory. To study the importance of GSH-dependent metabolism in DBCP toxicity, bromide release was assayed in cytosolic preparations using methylated analogs of DBCP. With the C1-methyl-derivative, bromide release was markedly reduced compared to that with DBCP in cytosols from liver, kidney and testis. A similar reduction in in vivo nephrotoxicity and testicular damage has recently been reported. The obtained correlation between in vitro GSH-dependent metabolism of methylated DBCP analogs and their in vivo organ damaging potential, points to an involvement of GSH-dependent metabolism in DBCP-induced in vivo toxicity. Both DBCP and the methylated analogs (360 mumol/kg i.p.) depleted the GSH levels in liver after 1 and 3 h and in kidney after 1 h, whereas in the testis no significant depletion of GSH was obtained. As kidney and testis are reported to be the primary target organs for DBCP, there was an apparent lack of correlation between tissue depletion of GSH and organ toxicity.

Animals↗
PubMed1989

Different mechanisms are involved in DNA damage, bacterial mutagenicity and cytotoxicity induced by 1,2-dibromo-3-chloropropane in suspensions of rat liver cells.

1,2-Dibromo-3-chloropropane (DBCP) induced DNA damage, measured by an automated alkaline elution method, in suspensions of rat liver parenchymal cells at low concentrations (1-10 microM). At much higher concentrations (0.5-2.5 mM), DBCP was metabolized to products that were mutagenic to Salmonella typhimurium TA100 co-incubated with the liver cells. At these higher concentrations a marked depletion of cellular glutathione was seen and at 2.5 mM DBCP was cytotoxic. Perdeuterated DBCP (D5-DBCP) caused less DNA damage in the liver cells than DBCP, most likely because of decrease in cytochrome P-450 dependent metabolism. A more pronounced decrease in mutagenicity occurred with D5-DBCP compared to DBCP, whereas the two compounds were equally cytotoxic. Preincubation of the liver cells with diethylmaleate or buthionine sulfoximine, to lower cellular levels of glutathione, decreased DBCP induced DNA damage. The decrease in DNA damage was proportional to the decrease in cellular glutathione levels. In contrast, diethylmaleate enhanced DBCP-induced bacterial mutagenicity and cellular cytotoxicity. The cytotoxic effect could be partly blocked by addition of ascorbate. From the data presented we suggest that: (i) cytochrome P-450 dependent oxidation as well as glutathione conjugation are involved in DBCP induced DNA damage, (ii) cytochrome P-450 dependent oxidation leads to formation of products mutagenic to bacteria and (iii) the cytotoxicity induced by DBCP in the liver cells in vitro is caused by oxidative damage following glutathione depletion and/or direct membrane damage.

Animals↗
PubMed1988

An automated alkaline elution system: DNA damage induced by 1,2-dibromo-3-chloropropane in vivo and in vitro.

An automated alkaline elution system for the detection of DNA damage has been developed. After manual application of samples, which is completed within 5 min, the subsequent supply of liquids, changes in flow rates, and temperature are controlled automatically. The system operates 16 filters and may easily be expanded. The sensitivity of the fluorometric DNA determinations with the Hoechst 33258 dye is increased by using an elution buffer (20 mM Na2EDTA, pH 12.50) with low background fluorescence. DNA is determined using an automated setup similar to the one recently presented by Sterzel et al. (1985, Anal. Biochem. 147, 462-467). The most significant modification is the use of a neutralization buffer which allows variations in the pH of eluted fractions. This change increases the sensitivity of the DNA measurements. The automated alkaline elution system was evaluated using the nematocide 1,2-dibromo-3-chloropropane (DBCP) in a study of its genotoxic effects in the testes and the kidneys. Significant DNA damage was induced in testicular cells by 2.5 microM DBCP (1 h) in vitro and 85 mumol/kg DBCP ip (3 h) in vivo. The damage appeared after short treatment times (10 min in vivo). Variations in the observed DBCP response in vivo were largely due to interanimal variations. The automated alkaline elution system proved to be a sensitive assay also for the detection of DNA damage in kidney nuclei prepared from rats exposed to DBCP. Provided that kidney nuclei from untreated rats, mice, or hamster were kept ice-cold until lysing, 85-100% of their DNA was retained after 16 h of elution, indicating highly intact DNA. Under the same conditions, guinea pig DNA was rapidly degraded unless the nuclei were prepared in a buffer with a higher concentration of Na2EDTA (20 mM).

Alkalies↗
PubMed1988

Testicular necrosis and DNA damage caused by deuterated and methylated analogs of 1,2-dibromo-3-chloropropane in the rat.

To study the role of metabolism in 1,2-dibromo-3-chloropropane (DBCP)-induced testicular damage in rats, selectively deuterated and methylated analogs of DBCP were given as a single ip dose of 340 mumol/kg and testicular toxicity was determined 10 days after treatment. None of the four deuterated analogs C1-D2-, C2-D1-, C3-D2-, or C1-C2-C3-D5-DBCP reduced the degree of testicular damage compared to DBCP, indicating that metabolic cleavage of a C-H bond was not rate-limiting in DBCP-induced testicular toxicity. Of the five methylated analogs, C1-methyl-, C1-dimethyl-, C2-methyl-, and C3-methyl-DBCP and 1,2-dibromo-4-chlorobutane, only C3-methyl-DBCP caused testicular toxicity. DBCP treatment resulted in increased testicular DNA damage at doses of 85-170 mumol/kg as measured by alkaline elution of DNA from testicular cells isolated 3 hr after in vivo treatment. The perdeutero-DBCP analog induced testicular DNA damage that was at least as extensive as that induced by DBCP. Of the methylated analogs tested, only C3-methyl-DBCP gave a marked dose-dependent increase in testicular DNA damage between 170 and 540 mumol/kg. There were no significant differences in the testicular tissue distribution between DBCP, perdeutero-DBCP, and the methylated DBCP analogs. Furthermore, in distribution studies with DBCP, C1-methyl- and C3-methyl-DBCP, and 1,2-dibromo-4-chlorobutane, the highest tissue concentrations were found in the kidneys, followed by the liver and then the testes. The fact that testicular DNA damage of DBCP and its deuterated and methylated analogs paralleled their ability to cause testicular necrosis and atrophy makes measurement of DNA damage a very useful correlate in mechanistic studies of DBCP-induced testicular cell death.

Animals↗
PubMed1988

Detection and mechanism of formation of the potent direct-acting mutagen 2-bromoacrolein from 1,2-dibromo-3-chloropropane.

The nematocide 1,2-dibromo-3-chloropropane (DBCP) was converted to products which are mutagenic for Salmonella typhimurium TA 100 in the presence of rat liver microsomes, NADPH, and oxygen. Typical in vivo and in vitro inhibitors of cytochrome P-450 decreased DBCP mutagenicity in the presence of microsomes. Addition of glutathione to cytosolic preparations failed to bioactivate DBCP to mutagenic metabolites. Mutagenicity studies with selectively deuterated analogs showed that substitution of deuterium for hydrogen at C-1 or C-3 of DBCP modestly decreased mutagenicity, but that deuteration at both C-1 and C-3 markedly decreased mutagenicity. The formation rates of the potent direct-acting mutagen, 2-bromoacrolein (2-BA), in incubations of DBCP and its deuterated analogs with rat liver microsomes, correlated with the isotope effects on mutagenicity. Characterization of 2-BA was accomplished by gas chromatography-mass spectrometry using positive-ion chemical ionization. Mass spectral analysis of 2-BA formed from specifically deuterated analogs of DBCP indicated that initial oxidative dehalogenation at C-1 followed by a spontaneous beta-elimination reaction was the preferred pathway in the formation of 2-BA from DBCP. These results demonstrate that mutagenic metabolites of DBCP are formed by cytochrome P-450-mediated oxidative metabolism, and that 2-BA is a major mutagen formed.

Animals↗
PubMed1988

Nephrotoxicity of selectively deuterated and methylated analogues of Tris-BP and Bis-BP in the rat.

Selectively deuterated and methylated analogues of the flame retardant tris(2,3-dibromopropyl)phosphate (Tris-BP) and its nephrotoxic metabolite bis(2,3-dibromopropyl)phosphate (Bis-BP) were compared to Tris-BP and Bis-BP in inducing acute renal damage in rats. None of the deuterated Tris-BP or Bis-BP analogues significantly altered morphological evidence of nephrotoxicity compared to the protio compounds. On the other hand, some of the selectively methylated analogues were much less nephrotoxic. Although the C1-methyl analogues of both Tris-BP and Bis-BP were as potent nephrotoxicants as Tris-BP and Bis-BP, respectively, neither the C2-methyl nor the C3-methyl analogues were significantly nephrotoxic. Interestingly, whereas the 3,4-dibromobutyl homologue of Tris-BP was not nephrotoxic, the corresponding 3,4-dibromobutyl-Bis homologue was as nephrotoxic as Bis-BP. Additional investigations with treatments that are known to decrease nephrotoxicity caused by several halogenated alkenes, showed that L-(alpha S,5S)-alpha-amino-3-chloro-4,5-dihydro-5-isoxazoleacetic acid (AT-125) and aminooxyacetic acid were without effects on Tris-BP induced renal damage. Probenecid pretreatment led to a reduction in Tris-BP and Bis-BP tubular necrosis, these effects may be related to inhibition of Bis-BP uptake in the kidney. It appears that the cysteine conjugate beta-lyase pathway is not involved in the generation of nephrotoxic metabolites of Tris-BP.

Animals↗
PubMed1988

The role of oxidative and conjugative pathways in the activation of 1,2-dibromo-3-chloropropane to DNA-damaging products in rat testicular cells.

The ability of 1,2-dibromo-3-chloropropane (DBCP), several methylated analogs of DBCP and perdeuterated DBCP (DBCP-D5) to cause DNA damage in isolated testicular cells from rats was measured by the alkaline elution technique. Of the methylated analogs studied, only the C3-methyl analog was capable of causing significant DNA damage at concentrations of 0-50 microM. In both time- (0-60 min) and concentration- (0-10 microM) dependent experiments, the testicular cell DNA damage caused by the perdeuterated analog of DBCP closely mimicked the damage resulting from DBCP itself. The lack of an isotope effect between DBCP-D5 and DBCP strongly suggests that metabolism via a cytochrome P-450-dependent pathway is not involved in the DNA-damaging effects of DBCP in rat testicular cells. In contrast, preincubation for 1 hr with diethylmaleate (DEM) inhibited DBCP-induced (10 microM) DNA damage in a concentration-dependent manner (0-500 microM DEM). The decrease in testicular DNA damage was proportional to the decrease in cellular nonprotein sulfhydryl levels. Similarly, it was shown that 1,2-dibromoethane (EDB), a structurally related halogenated alkane, produced DNA damage in isolated testicular cells in both a time- (0-60 min) and concentration- (0-600 microM) dependent fashion. The DNA damage produced by EDB (600 microM) was also inhibited by pretreatment of testicular cells with DEM (1 mM). The testicular genotoxicity induced by EDB is thought to involve its initial conjugation to glutathione and the subsequent formation of a reactive episulfonium ion. The data presented indicate that similar events may be occurring in DBCP-induced DNA damage in rat testicular cells.

Animals↗
PubMed1987

Mutagenic activation of 2-amino-3-methylimidazo[4,5-f]-quinoline (IQ) and 2-amino-3,4-dimethylimidazo[4,5-f]-quinoline (MeIQ) by subcellular fractions and cells isolated from small intestine, kidney and liver of the rat.

The mutagenic activity of the pyrolysis products 2-amino-3-methyl-imidazo[4,5-f]-quinoline 2-amino-3,4-dimethylimidazo[4,5-f]-quinoline in Salmonella typhimurium TA98 using rat intestinal and renal subcellular fractions as activation systems was approximately 1 and 5 revertants per nmol, respectively. This was 1,000 times less than the activity with a subcellular fraction from rat liver. The mutagenic activity of both compounds was considerably increased using intestinal, renal and hepatic preparations isolated from PCB (Aroclor 1254)-pretreated rats, compared to preparations from control animals. In addition, both compounds displayed a moderate direct-acting mutagenic activity at concentrations above 10(-5) M. Isolated cells from small intestine, kidney and liver incubated in nucleopore chambers were able to convert both compounds into products which mutated bacteria outside the chambers. The concentrations of chemicals required to yield responses of a similar magnitude were approximately 3 orders of magnitude higher in the intestinal and renal systems compared to the hepatic system. The formation of metabolites mutagenic for Salmonella typhimurium by hepatic subcellular and cellular systems was shown to be superior to the respective intestinal and renal systems.

Animals↗