Single-strand breaks, cell cycle arrest and apoptosis in HL-60 and LLCPK1 cells exposed to 1,2-dibromo-3-chloropropane.

We investigated 1,2-dibromo-3-chloropropane (DBCP)-induced DNA damage, cell cycle alterations and cell death in two cell lines, the human leukemia HL-60 and the pig kidney LLCPK1, both of which are derived from potential target sites for DBCP-induced toxicity. DBCP (30-300 micromol/L) caused a concentration-dependent increase in the levels of DNA single-strand breaks in both cell lines as well as in cultured human renal proximal tubular cells. After extended DBCP exposure in LLCPK1 cells (100 micromol/L, 30 h), the level of DNA breaks returned almost to control values. Incubation for 48 h showed a clear reduction of growth with DBCP concentrations as low as 10 micromol/L. Flow cytometric analysis showed that DBCP (1-10 micromol/L) exposure for 24 h caused an accumulation of LLCPK1 cells in the G2/M-phase. In HL-60 cells the accumulation in G2/M-phase was less marked, and at higher concentrations the cells accumulated in S-phase. Flow cytometric studies of HL-60 and LLCPK1 cells exposed to 100-500 micromol/L DBCP showed increased number of apoptotic cells/bodies with a lower DNA content than that of the G1 cells. Microscopic studies revealed that there were increased numbers of cells with nuclear condensation and fragmentation, indicating that apoptosis was the dominant mode of death in these cell lines, following exposure to DBCP. The characteristic ladder pattern of apoptotic cells was observed when DNA from DBCP-treated HL-60 cells and LLCPK1 cells was electrophoresed in agarose. The finding that DBCP can cause an accumulation of cells in G2/M-phase and induce apoptosis in vitro may be of importance for the development of DBCP-induced toxicity in vivo.

DNA strand breaks in testicular cells from humans and rats following in vitro exposure to 1,2-dibromo-3-chloropropane (DBCP).

Preparations of testicular cells from human organ transplant donors and from Wistar rats were compared with respect to their composition of the different testicular cell types, their ability to metabolize 1,2-dibromo-3-chloropropane (DBCP), and their relative sensitivity to induction of DNA single strand breaks and alkali labile sites (ssDNA breaks) after treatment with DBCP, 4-nitroquinoline N-oxide (4-NQO), and X rays. Flow cytometric and microscopic analysis demonstrated that the interindividual variation in the composition of testicular cell types was considerably greater in the human tissue than in that from rats. The in vitro metabolic activation of DBCP (50 to 250 microM), measured as radiolabel covalently bound to macromolecules, was three-fold faster in rat testicular cells compared to human testicular cells. X rays (1 to 10 Gy) and 4-NQO (0.5 to 2.5 microM) induced ssDNA breaks to a similar extent in both human and rat testicular cells as measured by single cell get electrophoresis (SCGE) and alkaline filter elution. In contrast, 1,2-dibromo-3-chloropropane (DBCP) (3 to 300 microM) caused no significant DNA damage in human testicular cells, whereas in rats there was a clear concentration-dependent increase in ssDNA breaks. The data show that, compared to rats, testicular cells from humans are less efficient in activating DBCP to metabolites binding covalently to macromolecules. However, from the rate of covalent binding observed one would expect a significant degree of DBCP-induced ssDNA breaks in the human testicular cells. The low level of DBCP-induced ssDNA breaks in human testicular cells could indicate that different reactive DBCP metabolites are involved in binding to cellular macromolecules compared to DNA damage, or that different rates of DNA repair exist in human and rat testicular cells.

Metabolism of 1,2-dibromo-3-chloropropane by glutathione S-transferases.

The metabolism of 1,2-dibromo-3-chloropropane (DBCP), measured as the formation of water soluble metabolites and metabolites covalently bound to macromolecules, was studied in isolated rat liver, kidney, and testicular cells, in subcellular fractions, and with purified rat and human glutathione S-transferases (GSTs). The rate of formation of water soluble metabolites in the cells were in the order liver > kidney > testis. The rate of covalent macromolecular binding of reactive DBCP metabolites in the different cell types was of the same relative order. Pretreatment of the cells with the GSH depleting agent diethyl maleate (DEM) markedly decreased the rate of covalent binding in all cell types. Both the overall metabolism and the formation of DBCP metabolites that covalently bound to macromolecules, were substantially higher in rat testicular cells compared to hamster testicular cells. Rat liver cytosol and microsomes, and various purified rat and human GSTs extensively metabolized DBCP to water soluble metabolites in the presence of GSH. When compared to isolated cells, substantially lower rates of binding per mg protein could be observed in subcellular fractions. Binding of DBCP was detected in the microsomal and cytosolic fractions in the absence of NADPH, though in microsomes fortified with a NADPH-regenerating system, the generation of reactive DBCP metabolites was approximately doubled. Studies with purified rat GST isozymes showed that the relative overall GSH conjugation activity with DBCP was in the following order: GST form 3-3 > 2-2 approximately 12-12 > 1-1 > 4-4 approximately 8-8 approximately 7-7. Furthermore, human GST forms also readily metabolized DBCP with activities of GST A1-2 > A2-2 approximately A1-1 > M1a-1a > M3-3 approximately P1-1.

Comparative toxicity of (+)-(R)- and (-)-(S)-1,2-dibromo-3-chloropropane.

The haloalkane 1,2-dibromo-3-chloropropane (DBCP), an environmental pollutant that was widely used as a soil fumigant, is a carcinogen and a mutagen and displays target-organ toxicity to the testes and the kidneys. Because little is known about effects of stereochemistry on the metabolism and toxicity of halogenated alkyl compounds and because DBCP, which has a chiral center at C-2, may show enantioselectivity in its metabolism and/or toxicities, the optically pure enantiomers of DBCP were tested in vivo in rats for organ toxicity as well as for bacterial mutagenicity. Organ toxicity studies showed that (S)-DBCP was slightly more renal toxic than (R)-DBCP but was not significantly more toxic than the racemate, and that no significant differences were observed in the extents of testicular necrosis and atrophy caused by either enantiomer or the racemate. In contrast, (R)-DBCP was more mutagenic than either (S)-DBCP or the racemate to Salmonella typhimurium (S. typhimurium) strains TA 100 and TA104. However, there was little or no enantioselectivity in glutathione S-transferase (GST)-catalyzed conjugation reactions of glutathione with DBCP based on the lack of selectivity in the rates of disappearance of the enantiomers of DBCP in the presence of glutathione (GSH) and GSTs as monitored by chiral gas chromatography (GC).

Increased mutagenicity of 1,2-dibromo-3-chloropropane and tris(2,3-dibromopropyl)phosphate in Salmonella TA100 expressing human glutathione S-transferases.

We have expressed human glutathione S-transferases GSTA1-1 and GSTP1-1 in Salmonella typhimurium TA100 in order to assess the ability of these enzymes to modulate the mutagenicity of 1,2-dibromo-3-chloropropane (DBCP) and tris(2,3-dibromopropyl)phosphate (Tris-BP). Both compounds were mutagenic when activated by Aroclor-induced rat liver microsomes. However, when Aroclor-induced rat liver microsomes were used together with the GST-expressing strains the mutagenicity of both DBCP and Tris-BP was markedly potentiated. Neither of the GST-expressing strains potentiated the mutagenicity in the absence of microsomes, indicating that cytochrome P450-mediated metabolism was a prerequisite for GST-mediated potentiation. With DBCP both isozymes had comparable effects on mutagenic frequency, although the highest dose of DBCP was toxic in strains expressing GSTP1-1. In the case of Tris-BP, GSTP1-1 was much more active in potentiating the mutagenicity. These results indicate that human GSTs can play an important role in the activation of compounds such as DBCP and Tris-BP to mutagenic metabolites.

Genotoxic effects of cyclopenta-fused polycyclic aromatic hydrocarbons in isolated rat hepatocytes and rabbit lung cells.

Benz[j]aceanthrylene (B[j]A) and benz[l]aceanthrylene (B[l]A), two isomeric cyclopenta polycyclic aromatic hydrocarbons (CP-PAH) structurally related to 3-methylcholanthrene, were studied with respect to their genotoxic effects in isolated liver and lung cells. Both compounds were found to cause DNA adducts measured by the 32P-postlabelling technique. The level of DNA-adducts in rat hepatocytes exposed to 30 micrograms/ml B[l]A and B[j]A for 4 h were 46.5 +/- 22.0 and 8.3 +/- 5.1 fmol/micrograms DNA respectively. Using butanol extractions, the major and one of the minor B[j]A adducts co-chromatographed with B[j]A-1,2-oxide adducts of 2'-deoxyadenosine and 2'-deoxyguanosine. Thus, oxidation at the cyclopenta-ring of B[j]A appears to be an important activation pathway. In hepatocytes, 3-30 micrograms/ml of B[j]A and B[l]A induced DNA damage and repair measured both as increased alkaline elution of DNA and as increased incorporation of [3H]TdR in the DNA. B[l]A was somewhat more potent than B[j]A in inducing DNA repair. Reactive CP-PAH intermediates formed in the hepatocytes caused mutations in Salmonella typhimurium TA98 upon co-incubation. DNA adducts were also observed in isolated rabbit lung cells exposed to 30 micrograms/ml B[l]A or B[j]A for 2 h. A total of 14.5 +/- 6.9, 2.9 +/- 2.1 and 0.2 +/- 0.6 fmol B[l]A adducts/micrograms DNA were observed in Clara cells, type II pneumocytes and alveolar macrophages respectively. The main B[l]A adduct observed in the liver cells was not found in the lung cells. On the other hand, the levels of B[j]A adducts in the lung cells were in the range 4-14% of that found in liver cells, and no major differences between the various lung cells were observed. Neither B[l]A nor B[j]A induced DNA damage measured by alkaline elution in the lung cells, indicating that these adducts are not alkali labile.

Chemically induced DNA damage in isolated rabbit lung cells.

By use of an isolation procedure including centrifugal elutriation and density gradient centrifugation, relatively pure fractions of Clara cells and type II cells were obtained from rabbit lungs. These cells and alveolar macrophages isolated by lavage were exposed to methyl methanesulfonate (MMS), 1,2-dibromo-3-chloropropane (DBCP), 1-nitropyrene (1-NP), 2-nitrofluorene (2-NF), 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK), N'-nitrosonornicotine (NNN), N-nitrosoheptamethyleneimine (NHMI) or phorbol 12-myristate 13-acetate (TPA). DNA damage measured as alkali-labile sites and/or single-strand breaks was then determined in the different lung cells by an automated alkaline elution system. The direct-acting compound MMS showed similar DNA-damaging effect in Clara cells, type II cells and alveolar macrophages. The nematocide DBCP, activated by both P450- and glutathione S-transferase(s)-dependent pathways, caused considerably less DNA damage in macrophages than in Clara or type II cells. Similar differences between the lung cells in induction of DNA damage as observed with DBCP were demonstrated after exposure to the activation-dependent nitrosamines NNK and NHMI and the tumor promoter TPA. The other test substances (1-NP, 2-NF, NNN) did not cause any marked DNA damage measured by the alkaline elution technique. These findings are in agreement with the known metabolic capacity of these cell types, indicating that Clara and type II cells are possible primary targets for lung toxic/carcinogenic compounds.

The non-genotoxicity to rodents of the potent rodent bladder carcinogens o-anisidine and p-cresidine.

The two potent rodent bladder carcinogens o-anisidine and p-cresidine, and the structurally related non-carcinogen 2,4-dimethoxyaniline, have been extensively evaluated for genotoxicity to rodents and found to be inactive. Most data were generated on o-anisidine, an agent that is also only marginally genotoxic in vitro. The two carcinogens induced methaemoglobinaemia in rodents indicating that the chemicals are absorbed and metabolically oxidized. Despite their total lack of genotoxicity in vivo, the two carcinogens have the hall-marks of being genotoxic carcinogens given that most test animals of both sexes of B6C3F1 mice and F344 rats are reported to have succumbed rapidly to malignant bladder cancer. No reasons for this dramatic conflict of test data are so far apparent. The experiments described involve, in one or other combination, 2 strains of mice (including B6C3F1) and 4 strains of rat (including F344), the use of oral and i.p. routes of exposure and observations made after 1, 3 or 6 doses of test chemical. 6 tissues (including the rat bladder) were assayed using 3 genetic endpoints (unscheduled DNA synthesis, DNA single-strand breaks and micronuclei induction). Aroclor-induced rats were employed in one set of experiments with o-anisidine. In the case of one set of mouse bone-marrow micronucleus experiments the same batch of the 3 chemicals as used in the cancer bioassays, and the same strain of mouse, were used. Possible further experiments and the implications of these findings are discussed.

Genotoxic effects of the drinking water mutagen 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]-furanone (MX) in mammalian cells in vitro and in rats in vivo.

The potent bacterial mutagen 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]- furanone) (MX), which is formed during chlorination of drinking water and accounts for about one third of the Ames mutagenicity of tap water, has been studied with respect to its genotoxicity in vitro and in vivo. Treatment with 30-300 microM MX (1 h) induced DNA damage in a concentration-dependent manner in suspensions of rat hepatocytes, as measured by an automated alkaline elution system. The effect was similar in hepatocytes from PCB-induced and uninduced rats. DNA damage was induced in V79 Chinese hamster cells and in isolated rat testicular cells, at the same concentration level as in hepatocytes. Pretreating testicular cells with diethylmaleate, which depletes 85% of cellular glutathione, had no significant effect on the DNA damage induced by MX. The treatment conditions used in the alkaline elution experiments were not cytotoxic to any of the cell types used, as determined by trypan blue exclusion. V79 cells exposed to 2-5 microM MX (2 h) showed an increased frequency of sister-chromatid exchanges (SCE) whereas no significant effect on HGPRT mutation induction was observed. Higher concentrations (greater than 10 microM, 2 h) apparently blocked cell division. The data indicate that MX can react directly with DNA or that MX is metabolized to an ultimate mutagen via some enzyme which is common in mammalian cells. The in vivo experiments showed no evidence of genotoxicity after intraperitoneal (18 mg/kg, 1 h) or oral (18, 63 or 125 mg/kg, 1 h) administration of MX, as measured by alkaline elution, in any of the following organs: the pyloric part of the stomach, the duodenum, colon ascendens, liver, kidney, lung, bone marrow, urinary bladder and the testes. In conclusion, MX is a direct-acting genotoxicant in vitro but no in vivo genotoxicity was detected.

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)

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)

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.

Genotoxicity of the food mutagen 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine (PhIP): formation of 2-hydroxamino-PhIP, a directly acting genotoxic metabolite.

Hepatocytes isolated from Aroclor 1254 (PCB) pretreated rats metabolized 2-amino-1-methyl-6-phenylimidazo[4,5-b]pyridine (PhIP) to a reactive metabolite that induced DNA damage measured by alkaline elution or as increased unscheduled DNA synthesis. PhIP induced mutations in Salmonella typhimurium TA98 and DNA strand breaks and sister chromatid exchange(s) in Chinese hamster V79 cells co-incubated with PCB-hepatocytes. No, or only minor genotoxic, effects were observed when hepatocytes from non-induced rats were used. The bacterial mutagenicity could be inhibited by alpha-naphthoflavone, indicating a role of P-450 in the activation of PhIP. At least eight different metabolites could be separated on HPLC after PhIP had been incubated with PCB-hepatocytes. All of the directly acting mutagenicity towards S.typhimurium TA98 co-eluted with one of the metabolites. The identity of this metabolite was concluded to be 2-hydroxamino-PhIP based on the following evidence: (i) it reduced ferric ion to ferrous ion as hydroxylamines do, (ii) it had an identical UV spectrum and chromatographic properties as a species formed upon reduction of 2-nitro-PhIP by NADPH P-450 reductase. This product displayed a major peak at m/z 241 during thermospray mass spectrometry in the positive-ion mode as would be expected from 2-hydroxamino-PhIP. 2-Hydroxamino-PhIP was directly genotoxic both to TA98 and V79 cells. The genotoxic activity of the medium after removing the hepatocytes remained stable for several hours. Compared to 2-amino-3,4-dimethylimidazo[4,5-f]quinolone (MeIQ), PhIP caused a much larger increase in DNA damage in V79 cells (with hepatocyte activation), whereas MeIQ was more potent with respect to DNA damage induced in hepatocytes and bacteria.

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.

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.

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.

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.

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.

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

Selectively deuterated and methylated analogs of the nematocide 1,2-dibromo-3-chloropropane (DBCP) were compared to DBCP in causing acute renal damage in rats. All of the six deuterated analogs tested at 340 mumol/kg, including the perdeutero compound, failed to significantly alter the kidney necrosis observed at 48 hr compared to DBCP. Furthermore, when the perdeutero analog was administered at several doses (42.5, 85, 170, and 340 mumol/kg), it caused kidney damage that was not significantly different than that caused by an equivalent molar dose of nondeuterated DBCP. Of the five methylated analogs tested at 170 and 340 mumol/kg, only C3-methyl-DBCP and 1,2-dibromo-4-chlorobutane caused nephrotoxicity. The C2-methyl-, C1-dimethyl-, and C2-methyl-DBCP analogs failed to cause renal necrosis determined 48 hr after dosing. In distribution studies DBCP, perdeutero-DBCP, and all the methylated analogs were found to concentrate in the kidney approximately 25 times relative to plasma 1 hr after administration. DBCP at doses of 4.3 mumol/kg and higher caused DNA damage in the kidney as early as 10 min after administration, as measured by alkaline elution of DNA from isolated kidney nuclear preparations. Perdeuteration did not decrease the DNA damaging effect of DBCP. The ability of the methylated DBCP analogs to induce renal DNA damage correlated with their necrogenic potential. Experiments using pretreatments that are known to decrease the nephrotoxicity caused by glutathione and cysteine conjugates of several halogenated alkenes were conducted to examine the effect of these pretreatments on DBCP-induced nephrotoxicity. Probenecid, L-(alpha S,5S)-alpha-amino-3-chloro-4,5-dihydro-5-isoxazoleacetic acid (AT-125) and aminooxyacetic acid did not significantly alter renal necrosis or DNA damage induced by DBCP. Based on the absence of any significant isotope effects with the predeutero-DBCP analog, it appears that breaking of a carbon-hydrogen bond is not the rate-limiting step in DBCP-induced nephrotoxicity. Studies with the methylated DBCP analogs indicate that a vicinal dibromo ethyl group must minimally be present for nephrotoxic potential. Furthermore, it seems unlikely that metabolism by renal cysteine conjugate beta-lyase is rate-limiting for DBCP nephrotoxicity.