The genetic toxicity of 1,2-dibromo-3-chloropropane, 1,2-dibromo-3- chloro-2-methylpropane,and 1,2,3-tribromo-2-methylpropane

1,2-Dibromo-3-chloro-2-methylpropane (DBCMP) and 1,2,3- tribromo-2-methylpropane (TBMP) are contaminants formed during the manufacture of bromobutyl rubber. These chemicals are structurally similar to 1,2-dibromo-3-chloropropane (DBCP), a known genotoxin and rodent carcinogen. The present study compared the genotoxic properties of DBCMP and TBMP to those of DBCP. In the Salmonella assay, DBCP was positive in strains TA98, TA-100 and TA-1535 in the presence of exogenous activation; DBCP was weakly active in TA-1535 in the absence of activation. Neither DBCMP nor TBMP produced reproducible evidence of mutagenic activity in the Salmonella assay despite the use of several different variations of this test. In the mouse lymphoma gene mutation assay DBCP and TBMP were positive in the presence and absence of activation, while DBCMP was positive only in the absence of activation. All three test compounds were active in the Syrian hamster embryo morphologic transformation assay. The results indicated that both DBCMP and TBMP exhibited some genotoxic activity as did DBCP. The presence of the methyl group on the 2-carbon position essentially eliminated the mutagenicity of DBCMP and TBMP in the Salmonella assay.abbreviations CHO Chinese hamster ovary cells - DBCMP 1,2-dibromo-3-chloro-2-methylpropane - DBCP 1,2-dibromo-3-chloropropane - DMEM Dulbecco's Eagle's minimal E medium - MNNG N-methyl-N'-nitro-N-nitrosoguanidine - S-9 microsomal fraction from rodent liver - TBMP 1,2,3-tribromo-2-methylpropane - TBP 1,2,3-tribromopropane - TFT trifluorothymidine     

Genetic toxicology of 1,2-dibromo-3-chloropropane (DBCP)

1,2-Dibromo-3-chloropropane (DBCP) is a nematocide, which has been used extensively as a soil fumigant in agriculture. Since sterility was found among male workers involved in the manufacture of DBCP, great concern has been focused on the genetic hazards of DBCP. DBCP gave positive results in many tests such as microbial, in vitro cytogenetics, and Drosophila studies. In mammalian test systems, DBCP caused chromosomal aberrations in the bone marrow cells and dominant-lethal mutations in germ cells in rats. In mice, there were no signs of DBCP-induced heritable mutation in germ cells, although point mutations were detected in somatic cells. The occurrence of Y-chromosomal non-disjunction was indicated in DBCP-exposed male workers by an increased number of sperm containing 2 Y-chromosomes.     

Genotoxicity and carcinogenicity testing of 1,2-dibromopropane and 1,1,3-tribromopropane in comparison to 1,2-dibromo-3-chloropropane

The activities of 1,2-dibromopropane (DBP) and 1,1,3-tribromopropane (TBP) were studied in seven genotoxicity assays, (i) SOS-induction inE. coli, (ii) DNA repair in primary rat hepatocyte culture, (iii) theSalmonella/microsome assay, (iv) a host-mediated assay usingSalmonella, (v) the somatic mutation and recombination assay inDrosophila melanogaster, (vi) HGPRT-mutagenesis assay in ARL 18 cells, and (vii) micronucleus formation assay in mouse polychromatophylic erythrocytes (PCE), forestomach (FS), glandular stomach (GS), duodenum (D), jejunum (J), cecum (C) and liver (L). The halopropanes were also tested for tumor formation in the fishDanio rerio. DBP was active in assays (ii), (v), (vii FS) and (vii L). TBP was positive in assays (ii) and (iii), strongly positive in (vii L) and borderline positive in (iv). However, neither DBP nor TBP induced tumors in fish, in contrast to the carcinogenic 1,2-dibromo-3-chloropropane. The genotoxicity and potential carcinogenicity of DBP and TBP in mammals is discussed.Abbreviations 2-AA 2-aminoanthracene - DBCP 1,2-dibromo-3-chloropropane - DBP 1,2-dibromopropane - HGPRT hypoxanthine-guanine phosphoribosyl transferase - i.p. intraperitoneal(ly) - NQO 4-nitro-quinoline-1-oxide - PCE polychromatic erythrocytes - TBP 1,1,3-tribromopropane - WME Williams' medium E     

Effects of 1,2-dibromo-3-chloropropane on male reproductive function in the rat

The pesticide 1,2-dibromo-3-chloropropane (DBCP) is a known male reproductive toxin. Previous studies employed production-grade DBCP containing allyl chloride and epichlorohydrin, both capable of producing effects similar to DBCP. The purpose of this study was to determine if purified DBCP caused the same effects as DBCP containing allyl chloride. Rats were injected for 6 mo with varying doses of pure or production-grade DBCP. Very few differences were observed in the parameters measured between pure and production-grade DBCP-treated animals at any one dose level. Treatment with 25 mg/kg DBCP, pure or production grade, reduced body weight as well as the weight of the testes, prostate glands and seminal vesicles, and elevated serum luteinizing hormone (LH) and follicle-stimulating hormone (FSH). This dose of pure DBCP reduced serum testosterone. Treatment with 5 mg/kg of either grade DBCP caused decreases only in body and testis weights. Animals treated with 1 mg/kg did not show any major differences from controls. These results indicate that DBCP, and probably not a contaminant, is responsible for the effects observed on male reproduction. Furthermore, DBCP appears to affect either androgen action or production since multiple androgenic indices are affected by DBCP administration.     

Effect of Temperature on the Dispersion of 1,2-dibromo-3-chloropropane in Soil

A study was conducted to evaluate the effect of temperature on the dispersion of 1,2-dibromo-3-chloropropane (DBCP) in soil. The facility of solution of DBCP in water was also investigated. Results of these studies show that the movement of DBCP from an injection site is temperature dependent. These data also indicate that DBCP dissolves readily in water and that dissolved chemical serves to limit the rate of outward dispersion once the liquid DBCP which was added has changed state. The mechanics of DBCP dispersion following soil injection are discussed.     

Biodehalogenation of bromotrichloromethane and 1,2-dibromo-3-chloropropane by Pseudomonas putida PpG-786

Biodehalogenation of 10(-5) M concentrations of bromotrichloromethane (BTM) and 1,2-dibromo-3-chloropropane (DBCP) was studied in static cultures of Pseudomonas putida PpG-786. The experimental cultures were prepared by growing P. putida on camphor, which is known to induce the synthesis of high concentrations of cytochrome P-450 in this bacterium. Measurements of bromide ion release were found to be approximately consistent with the amounts of halocarbon degraded. Gas chromatography/elctron capture detection (GC/ECD) measurements of hydrocarbon degradation products as a function of incubation time showed the transitory appearance of chloroform and bromodichloromethane from BTM and the transitory appearance of lower boiling but unidentified products from DBCP. The degradation of BTM to trihalomethanes and the halide ion is consistent with the enzymatic reductive dehalogenation by cytochrome P-450 reported by others. The dependence of initial conversion rates on halocarbon concentration (0.1-2 ppm) and cell mass concentration (1-28 g cell/L) was determined by measuring the decline of parent halocarbon in stirred batch cell suspensions. The rate of DBCP conversion was up to 10-fold higher than the rate of BTM conversion. When the intracellular, enzyme-catalyzed conversion BTM is analyzed by the effectiveness factor of heterogeneous catalysis, the initial conversion rates measured suggest that intrinsic enzyme kinetics, rather than halocarbon permeation of the cell membrane or other diffusive processes, is rate limiting.     

DNA damage and cell death induced by 1,2-dibromo-3-chloropropane (DBCP) and structural analogs in monolayer culture of rat hepatocytes: 3-aminobenzamide inhibits the toxicity of DBCP

1,2-Dibromo-3-chloropropane (DBCP) and a number of halogenated propane analogs induced DNA damage in rat hepatocytes in vitro measured by an automated alkaline elution method. Short-term (2 hrs) cytotoxic effects of DBCP were not observed until the DBCP concentration exceeded 1 mM. The short-term cytotoxicity of all the DBCP analogs occurred in the same concentration range. Significant membrane damage, measured as cell detachment, was observed after extended exposure to lower concentrations of DBCP (100 M) for 20 hrs. The relative, delayed cytotoxic effect of DBCP and analogs correlated with their ability to cause DNA damage. In general, the halogenated propanes with more bromines relative to chlorines were the more potent compounds. Propane analogs lacking the third halogen had little cytotoxic activity. The addition of the proposed specific poly(ADP-ribosyl)transferase inhibitor 3-aminobenzamide (3-ABA) protected against DBCP-induced cytotoxic effects and NAD⁺ depletion. However, 3-ABA also reduced DBCP-induced DNA damage, DBCP metabolic loss, and the formation of water soluble and covalently bound DBCP metabolites. Thus, 3-ABA may block DBCP-induced cell death by decreasing the formation of reactive DBCP-metabolites.Abbreviations 3-ABA 3-aminobenzamide - 3-AB acid 3-aminobenzoic acid - Asc ascorbate - BSA bovine serum albumin - DBCP, 1,2-diB-3-CP 1,2-dibromo-3-chloropropane - DMSO dimethylsulfoxide - DPPD N,N-diphenyl-p-phenylenediamine - GSH glutathione - Hoechst 33258 [2(2-(4-hydroxy-phenyl)-6-benzimidazole-6-(1-methyl-4-piperazyl)-benzimidazole trihydrochloride)] - 1,2,3-triBP 1,2,3-tribromopropane - 1,3-diB-2-CP 1,3-dibromo-2-chloropropane - 1,3-diC-2-BP 1,3-dichloro-2-bromopropane - 1,2,3-triCP 1,2,3-trichloropropane - 1,2-diBP 1,2-dibromopropane     

Mutagenicity of 1,2-dibromo-3-chloropropane (DBCP) in the mouse spot test

The spot test with 1,2-dibromo-3-chloropropane (DBCP) was carried out using male PW and female C57BL/6 mice. DBCP induced recessive colour spots in offspring with a significantly high frequency of 2.9%, showing that this chemical is mutagenic for somatic cells of mice in vivo.     

Micronucleus induction by azobenzene and 1,2-dibromo-3-chloropropane in the rat: evaluation of a triple-dose protocol

A triple-dose protocol was evaluated in the rat bone-marrow micronucleus test using azobenzene and 1,2-dibromo-3-chloropropane (DBCP) as test compounds. Dosing with 250 mg/kg azobenzene over 3 consecutive days led to an accumulation of micronucleated polychromatic erythrocytes. The magnitude of the effect was the same as that obtained after a single dose of 750 mg/kg in a previous study. In the single-dose study the effect was only detected at the 48 h sampling time. With the triple-dose protocol the effect was apparent 24 h after the last dose--thus eliminating the need for more than one sampling time. In the case of DBCP, the positive effect observed after a single dose diminished with increasing number of doses for the low dose but plateaued for the high dose, accompanied by a marked cytotoxic effect. It is therefore concluded, that for one of the compounds, azobenzene, the triple-dose protocol provided an advantage whereas for the other, DBCP, it failed to do so and led to results which are rather difficult to interpret. Furthermore, the number of animals necessary to select an appropriate dose level appears to be higher than in the single-dose protocol.     

Movement and Persistence of 1,2-dibromo-3-chloropropane in a Soil with a Plow-pan

Movement and persistence of 1,2-dibrotno-3-chloropropane (DBCP) in a Coastal Plain soil containing a sandy plow-pan were enhanced in each of 2 years by subsoiling, increased depth of application, and increased rate of application. DBCP was extracted from the soil with hexane and analyzed by gas chromatography. Subsoiling at a 35-cm depth gave the greatest increase in lateral movement and downward penetration of DBCP in 1975 (a wet year), but bad less effect in 1976 (a dry year). An increased application rate (10 kg/ha vs. 13.5) improved coverage moderately in 1975 by increasing lateral movement, but had little effect in 1976. Increased application depth (18 vs. 35 cm) improved coverage in both years though more in 1976. Deep placement extended DBCP retention time. Rainfall in 1975 probably decreased the number and size of air-filled pores, slowing loss of DBCP to the atmosphere. Because of reduced porosity, the plow-pan was impervious to the passage of DBCP unless disrupted by subsoiling.     

The effects of fetal exposure to 1,2-dibromo-3-chloropropane on adult male reproductive function

Several drugs have been shown to cross the placental barrier and affect the fetal testis causing a reduction in testosterone with a resultant impairment of sexual differentiation and an ultimate problem in adult sexual function. In this study, pregnant female rats were treated with 25 mg/kg of the pesticide 1,2-dibromo-3-chloropropane (DBCP). Treatment began on Days 14.5, 16.5, or 18.5 and continued through Day 19.5 of gestation. Some animals were killed on Day 20.5 of intrauterine life and fetal intratesticular testosterone was measured. All other animals were allowed to deliver, and the males were raised to adulthood. At adulthood, body, testis, prostate glands and seminal vesicle weights were recorded. Intratesticular testosterone and luteinizing hormone (LH) receptors were measured. Male and female sexual behavior was quantified and the volume of the sexually dimorphic nucleus of the preoptic area of the hypothalamus was calculated. The histological appearance of the testis was also examined. Treatment for 6 days during fetal life with DBCP decreased intratesticular testosterone by 50% compared to controls at 20.5 days of gestation. At adulthood, all male rats treated during fetal life had a reduced body weight that was correlated with the duration of exposure. Adult testis weight was reduced to 75% of controls as a result of 2 days of fetal exposure to DBCP, whereas 4 and 6 days of exposure during fetal life reduced testis weight by greater than 90%. LH receptors and intratesticular testosterone, in the adults treated during fetal life, were also dramatically reduced.(ABSTRACT TRUNCATED AT 250 WORDS)     

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)     

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).     

Tests for dominant-lethal effects of 1,2-dibromo-3-chloropropane (DBCP) in male and female mice

DBCP was studied for dominant-lethal effects in male and female mice and for total reproductive effects in females. In males it was administered either intraperitoneally or subcutaneously while in females it was given only by the former route. No DBCP-related response was observed in either males or females indicating its ineffectiveness in inducing chromosomal aberrations or cytotoxicity in mouse germ cells. These findings differ markedly from the observations made in rats by other investigators. Thus, the probable existence of a species difference in germ cell response to DBCP has been strengthened by the availability of the present results. It should be noted, however, that only two stocks of male mice have been studied so far for dominant-lethal and germ cell cytotoxicity effects.     

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). © 1995 Wiley-Liss, Inc.     

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 µmol/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 µmol/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 µmol/L. Flow cytometric analysis showed that DBCP (1–10 µmol/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 µmol/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.     

Infrared and raman spectra of specifically deuterated 1,2-dipalmitoyl-sn-glycero-3-phosphocholines

Deuterated methylene groups have been introduced synthetically in selected positions of the sn-2 palmitoyl chain of 1,2-dipalmitoyl-sn-glycero-3-phosphocholine (DPPC) and deuterated methyl groups in the sn-1 and sn-2 palmitoyl chains as well as in the sn-3 phosphocholine group.The vibrational spectra of seven such deuterium labelled derivatives of the title compound have been studied as the assignment of the C–D stretching vibrations is discussed.     

Simple preparation of 1,2-dipalmitoyl-sn-glycero-3-phosphoric acid and deuterated choline derivatives

Analytically pure 1,2-dipalmitoyl-sn-glycero-3-phosphoric acid was prepared in gram amounts, using a simplified version of a previous procedure. The main step, enzymatic cleavage of 1,2-dipalmitoyl-sn-glycero-3-phosphocholine with freshly extracted phospholipase D, was performed in the presence of chloroform and the crude phosphatidic acid was purified by silica gel column chromatography. The interest of the method was illustrated by the synthesis of two dipalmitoyl phosphatidylcholines selectively deuterated on the polar headgroup.     

The importance of 3,4-epoxy-1,2-butanediol and hydroxymethylvinyl ketone in 3-butene-1,2-diol associated mutagenicity

1,2:3,4-Diepoxybutane is hypothesized to be the main intermediate involved in mutagenicity following exposure to low levels of 1,3-butadiene (BD) in mice, while metabolites of 3-butene-1,2-diol (BD-diol) are thought to become involved in both rats and mice at higher exposures. BD-diol is biotransformed to hydroxymethylvinyl ketone (HMVK), a potentially mutagenic metabolite, and 3,4-epoxy-1,2-butanediol (EB-diol), a known mutagen. To determine the relative importance of HMVK and EB-diol in BD-diol associated mutagenesis, we have examined the dosimetry of a HMVK derived DNA adduct, as well as EB-diol derived DNA and hemoglobin adducts, in rodents exposed to BD-diol. We previously demonstrated similarities in the shapes of the dose-response curves for EB-diol derived DNA adducts, hemoglobin adducts, and Hprt mutant frequencies in BD-diol exposed rodents, indicating that EB-diol was involved in the mutagenic response associated with BD-diol exposure. To examine the role of HMVK in BD-diol mutagenicity, a method to quantify the alpha-regioisomer of HMVK derived 1,N(2)-propanodeoxyguanosine (alpha-HMVK-dGuo) was developed. The method involved enzymatic hydrolysis of DNA, HPLC purification, and adduct measurement by liquid chromatography - tandem mass spectrometry. Intra- and inter-experimental variabilities were determined to be 2.3-18.2 and 4.1%, respectively. The limit of detection was approximately 5 fmol of analyte standard injected onto the column or 5 fmol/200 microg DNA. The method was used to analyze liver DNA from control female F344 rats and female F344 rats exposed to 36 ppm BD-diol. In addition, liver samples from female Sprague-Dawley rats exposed to 1000 ppm BD were analyzed. alpha-HMVK-dGuo was not detected in any of the samples analyzed. Several possible explanations exist for the negative results including the possibility that alpha-HMVK-dGuo may be a minor adduct or may be efficiently repaired. Alternatively, HMVK itself may be readily detoxified by glutathione (GSH) conjugation. While experiments must be conducted to understand the exact mechanism(s), these results, in addition to published EB-diol derived adduct dosimetry and existing HMVK derived mercapturic acid data, suggest that EB-diol is primarily responsible for BD-diol induced mutagenicity in rodents.     

Use of Drosophila deoxynucleoside kinase to study mechanism of toxicity and mutagenicity of deoxycytidine analogs in Escherichia coli

Most bacteria, including Escherichia coli, lack an enzyme that can phosphorylate deoxycytidine and its analogs. Consequently, most studies of toxicity and mutagenicity of cytosine analogs use ribonucleosides such as 5-azacytidine (AzaC) and zebularine (Zeb) instead of their deoxynucleoside forms, 5-aza-2′-deoxycytidine (AzadC) and 2′-deoxy-zebularine (dZeb). The former analogs are incorporated into both RNA and DNA creating complex physiological responses in cells. To circumvent this problem, we introduced into E. coli the Drosophila deoxynucleoside kinase (Dm-dNK), which has a relaxed substrate specificity, and tested these cells for sensitivity to AzadC and dZeb. We find that Dm-dNK expression increases substantially sensitivity of cells to these analogs and dZeb is very mutagenic in cells expressing the kinase. Furthermore, toxicity of dZeb in these cells requires DNA mismatch correction system suggesting a mechanism for its toxicity and mutagenicity. The fluorescence properties of dZeb were used to quantify the amount of this analog incorporated into cellular DNA of mismatch repair-deficient cells expressing Dm-dNK and the results showed that in a mismatch correction-defective strain a high percentage of DNA bases may be replaced with the analog without long term toxic effects. This study demonstrates that the mechanism by which Zeb and dZeb cause cell death is fundamentally different than the mechanism of toxicity of AzaC and AzadC. It also opens up a new way to study the mechanism of action of deoxycytidine analogs that are used in anticancer chemotherapy.