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NTP Toxicology and Carcinogenesis Studies of Telone II(R) (Technical-Grade 1,3-Dichloropropene [CAS No. 542-75-6] Containing 1.0% Epichlorohydrin as a Stabilizer) in F344/N Rats and B6C3F1 Mice (Gavage Studies).

Toxicology and carcinogenesis studies of Telone II(R) (a soil fumigant containing approximately 89% cis- and trans-1,3-dichloropropene, 2.5% 1,2-dichloropropane, 1.5% of a trichloropropene isomer, and 1.0% epichlorohydrin) were conducted by administering the commercial-grade formulation in corn oil by gavage to groups of 52 male and 52 female F344/N rats at doses of 0, 25, or 50 mg/kg and to groups of 50 male and 50 female B6C3F1 mice at doses of 0, 50, or 100 mg/kg. Doses were administered three times per week for 104 weeks. Ancillary studies were conducted in which dose groups containing five male and five female rats were killed after receiving Telone II(R) for 9, 16, 21, 24, or 27 months. Mean body weights of high dose male rats were about 5% lower than those for the vehicle control and low dose male rats; no differences in body weights were observed among groups of female rats. Survival was comparable for the different groups of male and female rats. For male and female mice, the dosed groups initially weighed 6%-22% less than did the vehicle controls; the weight differential decreased to 5%-9% by the end of the studies. Twenty-five vehicle control male mice died during weeks 48-51 from suppurative inflammation of the heart (myocarditis). At the end of the studies, the survival of male mice was as follows: vehicle control, 8/50; low dose, 28/50; high dose 31/50. Survival of female mice was lower (P<0.05) in the high dose group than in the vehicle controls (46/50; 45/50; 36/50). The primary organs affected were the forestomach (rats and mice), urinary bladder (mice), lung (mice), and liver (rats). Compound-related nonneoplastic lesions included basal cell or epithelial hyperplasia of the forestomach (rats and mice), epithelial hyperplasia of the urinary bladder (mice), and kidney hydronephrosis (mice). Neoplastic lesions associated with administration of Telone II(R) included squamous cell papillomas of the forestomach (male rats: 1/52; 1/52; 9/52; female rats: 0/52; 2/52; 3/52; female mice: 0/50; 1/50; 2/50), squamous cell carcinomas of the forestomach (male rats: 0/52; 0/52; 4/52; female mice: 0/50; 0/50; 2/50), transitional cell carcinomas of the urinary bladder (female mice: 0/50; 8/50; 21/48), alveolar/bronchiolar adenomas (female mice: 0/50; 3/50; 8/50), and neoplastic nodules of the liver (male rats: 1/52; 6/52; 7/52). Although the study in male mice was considered inadequate due to the deaths at weeks 48-51 of 25/50 vehicle control animals, 2/50 of the high dose males had transitional cell carcinomas of the urinary bladder. Furthermore, increases were seen in the incidences of alveolar/bronchiolar neoplasms of the lung (1/50; 13/50; 12/50) and of squamous cell papillomas of the forestomach (0/50; 2/50; 3/50). These findings plus the finding of nonneoplastic lesions in two of these organs (basal cell or epithelial hyperplasia of the forestomach: 0/50; 0/50; 4/50; epithelial hyperplasia of the urinary bladder: 0/50; 9/50; 18/50) suggest that Telone II(R) may have been responsible for the development of these lesions in male mice. Development of lesions of the forestomach (basal cell hyperplasia and squamous cell papilloma) was observed to be time dependent. The results of the scheduled kills supported the findings of the carcinogenesis studies. When the results from the scheduled kills at all time points were pooled with those of the 24-month carcinogenesis studies, the incidences were as follows: basal cell or epithelial hyperplasia of the forestomach-- male rats: 3/77; 13/77; 31/77; female rats: 1/75; 5/77; 35/77; squamous cell papilloma of the forestomach-- male rats: 1/77; 1/77; 13/77; female rats: 0/75; 2/77; 8/77; neoplastic nodules of the liver--male rats: 1/77; 6/76; 8/77; female rats: 6/75; 8/77; 12/77. cis- and trans-1,3- Dichloropropane are the principle components (89%) in Telone II(R), but the 1.0% epichlorohydrin, a direct-acting mutagen and carcinogen added as a stabilizer, may have influenced the development of the forestomach lesions. 1,3-Dichloropropene was mutagenic in Salmonella typhimuriumnt of the forestomach lesions. 1,3-Dichloropropene was mutagenic in Salmonella typhimurium strains TA98, TA100, and TA1535 without metabolic activation and in TA100 and TA1535 with metabolic activation by Aroclor-induced male Sprague-Dawley rat and Syrian hamster liver S9. No mutagenic response was seen in TA1537. Sex-linked recessive lethal mutations were observed in Drosophila melanogaster, and 1,3-dichloropropene did not induce reciprocal translocations in D. melanogaster. A data audit was conducted on the Telone II&reg; 2-year carcinogenesis studies in rats and mice and the ancillary studies in rats. Except for the already known problem of survival of male vehicle control mice, no other discrepancies or problems that would compromise the validity of the findings or alter the interpretations of these studies were found. Under the conditions of these gavage studies, there was clear evidence of carcinogenicity for male F344/N rats, as indicated by Telone II&reg;-related increased incidences of squamous cell papillomas and carcinomas of the forestomach, as well as an increased incidence of neoplastic nodules of the liver. In female F344/N rats, there was some evidence of carcinogenicity because Telone II&reg; caused an increased incidence of squamous cell papillomas of the forestomach. The experiment in male B6C3F1 mice was considered to be an inadequate study of carcinogenicity because of reduced survival in the vehicle control group. However, there was some indication in the male mice of Telone II&reg;-related increases of transitional cell carcinomas of the urinary bladder, squamous cell papillomas of the forestomach, and alveolar/bronchiolar adenomas and carcinomas of the lung. There was clear evidence of carcinogenicity for female B6C3F1 mice, since Telone II&reg; caused increased incidences of transitional cell carcinomas of the urinary bladder; Telone II&reg; also increased the incidences of alveolar/bronchiolar adenomas of the lung and of squamous cell papillomas or carcinomas of the forestomach in the female mice. Telone II&reg;-related nonneoplastic lesions included basal cell or epithelial cell hyperplasia in the forestomach of male and female rats and male and female mice and epithelial hyperplasia of the urinary bladder in male and female mice. Synonyms: cis,trans-1,3-dichloropropene, D-D&reg; Soil Fumigant; Telone&reg; Soil Fumigants; Vorlex&reg; Soil Fumigants

Journal Article↗

Propylene oxide and epichlorohydrin induce DNA strand breaks in human diploid fibroblasts.

The induction of DNA strand breaks in human diploid fibroblasts (VH-10) was demonstrated after in vitro exposure with two carcinogenic epoxides, propylene oxide (PO) and epichlorohydrin (ECH). Alkaline DNA unwinding (ADU), pulsed field gel electropharosis (PFGE), and the comet assay were used to measure DNA single. (SSBs) and double-strand breaks (DSBs). A dose-dependent increase of DNA strand breaks, measured by ADU, was observed in the dose range 2.5-20 mMh of PO and 0.25-2 mMh of ECH. The dose-response of ECH was about five times higher compared with that of PO (211 vs. 41 SSBs. 100 Mbp-1.mMh-1). The induction rates of DSBs, measured by PFGE, were found to be 18 times higher for ECH compared to PO (4.8 and 0.27 DSBs.100 Mbp-1.mMh-1 for ECH and PO, respectively). Using these two methods, the SSBs/ DSBs ratio was estimated to be 148 for PO and 44 for ECH. The data obtained by the comet assay also demonstrated a dose-dependent ability of PO and ECH to induce DNA damage. It was found that ECH was about six times more effective as an inducer of DNA strand breaks compared to PO (200 and 32x100 Mbp-1.mMh-1 for ECH and PO, respectively). The SSBs/DSBs ratios calculated using comet assay and PFGE data were 125 for ECH and 41 for PO. In addition, ECH is about 10 times more toxic than PO with respect to survival. These properties of ECH can at least in part be explained by its higher chemical reactivity connected with a higher rate of DNA alkylation.

Carcinogens↗

Poly(styrene)-supported co-salen complexes as efficient recyclable catalysts for the hydrolytic kinetic resolution of epichlorohydrin.

Here we describe an unprecedented synthetic approach to poly(styrene)-supported chiral salen ligands by the free radical polymerization of an unsymmetrical styryl-substituted salen monomer (H2salen = bis(salicylidene)ethylenediamine). The new method allows for the attachment of salen moieties to the polymer main chain in a flexible, pendant fashion, avoiding grafting reactions that often introduce ill-defined species on the polymers. Moreover, the loading of the salen is controlled by the copolymerization of the styryl-substituted salen monomer with styrene in different ratios. The polymeric salen ligands are metallated with cobalt(II) acetate to afford the corresponding supported Co-salen complexes, which are used in the hydrolytic kinetic resolution of racemic epichlorohydrin, exhibiting high reactivity and enantioselectivity. Remarkably, the copolymer-supported Co-salen complexes showed a better catalytic performance (>99 % ee, 54 % conversion, one hour) in comparison to the homopolymeric analogues and the small molecule Co-salen complex. The soluble poly(styrene)-supported catalysts were recovered by precipitation after the catalytic reactions and were recycled three times to afford almost identical enantiomeric excesses as the first run, with slightly reduced reaction rates.

Acetates↗

Ion trap mass spectrometry in the structural analysis of haemoglobin peptides modified by epichlorohydrin and diepoxybutane.

Ion trap mass spectrometry has been shown to be particularly suitable for the structural analysis of high molecular weight peptides directly fragmented in the mass analyser without needing further sub-digestion reactions. Here we report the advantages of using multi-stage ion trap mass spectrometry in the structural characterisation of haemoglobin alkylated with epichlorohydrin and diepoxybutane. Alkylated globins were digested with trypsin and the peptide mixtures were analysed by MS(3). This technique allows the sequential fragmentation of peptides under analysis, giving rise to MS(3) product ion spectra with additional information with respect to MS(2) mass spectra. The results obtained complete the previously reported structural characterisation of alkylated haemoglobin, demonstrating the potential of ion trap mass spectrometry.

Epichlorohydrin↗

Biomonitoring of epichlorohydrin by hemoglobin adducts.

A gas chromatographic mass spectrometric method for monitoring exposure to epichlorohydrin (ECH) by means of quantitative analysis of N-(2,3-dihydroxypropyl)valine in hemoglobin has been developed. The analysis is based on the modified Edman method for measurement of adducts to the N-terminal valine, one of the reactive sites of the globin chains. The presence of two hydroxyl groups in the adduct to be analyzed required special precautions to be introduced into the method, such as acetylation of the Edman derivative. An in vitro treated globin with [2H5]N-2,3-dihydroxypropyl adducts was used as internal standard. The limit of detection achieved is 4 fmol in analysis by tandem mass spectrometry. Adduct levels found in smokers (15 to 20 cigarettes per day) were between 6.5 and 11.2 pmol/g globin and for nonsmokers the adduct levels were close to the detection limit (about 2 pmol/g globin). In two rats, treated ip with 40 mg ECH/kg body wt and sacrificed after 30 days, the average adduct level was 44 pmol/g globin and that for two nonexposed rats was close to the detection level. The method will be useful for monitoring of exposure and for cancer risk estimation of ECH.

Animals↗

Mortality in an european cohort occupationally exposed to epichlorohydrin (ECH).

A study was undertaken on the mortality of workers exposed to ECH at four European sites with plants producing epichlorohydrin (ECH), epoxy resins, glycerin, and other specialty chemicals derived from ECH. The vital status of 606 individuals with at least one year of exposure to ECH, starting at least 10 years before the final date of the study on 31 December, 1978, were collected. Mortality was analysed for a subgroup with 10 or fewer years of exposure, and another subgroup with more than 10 years of exposure. Four deaths from different cancers were observed against five expected. No excess mortality from cancer was observed in either subgroup or the complete cohort, which could be related to ECH exposure. The small size of the cohort and the limited number of deaths due to low average age (42 years), as well as the short duration of the observation period, do not allow a firm conclusion to be reached regarding the potential carcinogenicity of ECH in man. Current exposure levels are low, but exposure in the early days of production occasionally reached levels high enough to be irritating. We recommend updating the study 5 years from the final date of the present study, i.e. on 31 December, 1983. Within their limitations this and other epidemiological studies so far provide no evidence for an association between occupational exposure to ECH and the occurrence of malignant neoplasms in man.

Chlorohydrins↗

Exposure to epichlorohydrin and dimethylformamide, glutathione S-transferases and sister chromatid exchange frequencies in peripheral lymphocytes.

Workers in epoxy resin, synthetic leather, and printed circuit board manufacturing plants are exposed to epichlorohydrin (ECH), or dimethylformamide (DMF), or both. ECH, an alkylating agent, has been shown to cause malignancy in animals, but its genotoxicity in humans is unclear. DMF is a well-known hepatotoxic chemical, although evidence of its genotoxicity in humans is also limited. In this study, we examined the effects of exposure to ECH and DMF on sister chromatid exchange (SCE) in plant workers, in order to examine the genotoxicity of these two agents. Because the genotoxicity of certain agents can be modulated by metabolic traits, we also investigated influence of the glutathione S-transferase (GST) micro (GST M1) and GST theta (GST T1) genes on the genotoxicity of ECH and DMF. A total of 85 male plant workers were included in this study. The subjects were divided into five exposure groups, based on their job titles and the airborne ECH and DMF concentrations in their areas of work. A questionnaire was administered to obtain detailed occupational, smoking, alcohol consumption, and medication histories. Standardized cytogenetic methods were used to determine the frequency of sister chromatid exchange (SCE) in peripheral blood lymphocytes. GST M and GST T1 genotypes were identified using polymerase chain reaction (PCR). In analysis, smoking was significantly associated with increased SCE frequency (P<0.01). Workers with high ECH exposure also had significantly higher SCE frequencies than those with low or no ECH exposure (P<0.05). However, DMF exposure was not associated with SCE frequency. The GST M1 null genotype was also found to be associated with an increased SCE frequency (P = 0.06). We conclude that ECH exposure may be associated with genetic toxicity and that DMF does not appear to be genotoxic.

Adult↗

The reaction between epichlorohydrin and polysaccharides: Part 2, Synthesis of some model substances, with cyclic substituents.

Eight derivatives of methyl alpha-D-glucopyranoside, in which the substituents are part of cyclic structures, have been prepared as model substances for possible structural elements formed on reaction of polysaccharides with epichlorohydrin. The substances were converted into the permethylated alditol-1-d acetates and characterised by CIMS and EIMS.

Epichlorohydrin↗

The reaction between epichlorohydrin and polysaccharides: Part 1. Syntheses of some model substances with non-cyclic substituents.

Five derivatives of methyl alpha-D-glucopyranoside, in which the substituents form noncyclic structures, have been prepared as model substances for possible structural elements formed on reaction of polysaccharides with epichlorohydrin. The substances were converted into the permethylated alditol-1-d derivatives and characterised by CIMS and EIMS.

Carbohydrate Sequence↗

Reaction of epichlorohydrin with 2'-deoxynucleosides: characterization of adducts.

Epichlorohydrin (ECH) is a simple 3-carbon epoxide of industrial importance and thus has the potential for human exposure in the workplace. It has been shown to be genotoxic in several systems and is a compound capable of reacting with biological nucleophiles. This study details the products formed from the reaction of ECH with 2'-deoxynucleosides at pH 7 and 37 degrees C for 6 h. Reaction with 2'-deoxyguanosine yielded 7-(3-chloro-2-hydroxypropyl) guanine (7-CHP-Gua) resulting from alkylation at N-7 of 2'-deoxyguanosine followed by depurination. Two unusual adducts were also partially characterized which resulted from further reaction of 7-CHP-Gua with another molecule of ECH to yield 1,7-bis(3-chloro-2-hydroxypropyl)guanine (1,7-bis-CHP-Gua) which could then cyclize with the exocyclic amino group to yield 1,N2-(2-hydroxypropano)-7-(3-chloro-2-hydroxypropyl) guanine (1,N2-HP-7-CHP-Gua). Reaction with 2'-deoxyadenosine gave only one product, namely 1,N6-(2-hydroxypropano)-2'-deoxyadenosine (1,N6-HP-dAdo). The reaction of 2'-deoxythymidine with ECH also yielded one product which was identified as 3-(3-chloro-2-hydroxypropyl)-2'-deoxythymidine (3-CHP-dThd). A 3-(3-chloro-2-hydroxypropyl)-2'-deoxyuridine (3-CHP-dUrd) product was isolated from the reaction of ECH with 2'-deoxycytidine. This product most likely resulted from the deamination of an initially formed 3-(3-chloro-2-hydroxypropyl) -2'-deoxycytidine (3-CHP-dCyd), a phenomenon which we have previously reported to occur during the reaction of 2'-deoxycytidine with other aliphatic epoxides. Evidence is also presented that 3-CHP-dUrd is converted to 3-(2,3-dihydroxypropyl)-2'deoxyuridine (3-DHP-dUrd) under physiological conditions, with a half-life of 213 h. Reaction of ECH with calf thymus DNA (pH 7.0, 37 degrees C, 3 h) resulted in the formation of 7-CHP-Gua (200 nmol/mg DNA.

Chromatography, High Pressure Liquid↗

Mutagenic effect of epichlorohydrin. I. Testing on human lymphocytes in vitro in comparison with TEPA.

The mutagenic effect of the monofunctional alkylating agent epichlorohydrin was tested on human lymphocytes in vitro and compared with the mutagenic effect of the polyfunctional alkylating agent TEPA. The same descending concentrations were used for both mutagens: 10(-4), 10(-5), 10(-6), 10(-7), 10(-8), 10(-9), 10(-10) and 10(-11) M. Similar types of chromosomal aberration were found, but the effect of ECHH was 4-5 times lower than that of TEPA. ECHH was found to be a mild mutagen. Different timing of mutagen application was used in the course of 56 h of cultivation of lymphocytes: 1 h before cultivation, one hour between the 24th and 25th h of cultivation and 24 h before the end of cultivation. From the results presented we conclude that the application of the chemical for the last 24 h of human lymphocyte cultivation should be recommended for routine mutagenicity testing.

Azirines↗

Banding technique used for the detection of chromosomal aberrations induced by radiation and alkylating agents TEPA and epichlorohydrin.

Blood samples from two healthy donors were exposed, (1) to 200 R of X-rays in G0 and G1S phases of the cell cycle, and (2) to epichlorohydrin 10(-6) M and TEPA 10(-4) M in G0 and/or in G1S and G2 phases. Part of the cells was processed for chromosome studies conventionally and the other part by the trypsinization banding technique. Detailed chromosomal analysis showed that, after irradiation, 38.2% of aberrations in G0 and 18.7% in G1S phases escaped cytogenetic detection when the conventional technique was used. After exposures to TEPA and ECHH, 10.9% of aberrations were undectable in G0 and 3.3% in G1S and G2 phases. The distribution of chromosome breaks was non-random both after irradiation and after exposure to alkylating agents. However, it differed according to the mutagen used. Some chromosomal segments were broken significantly more frequently than the others (e.g. 9q12), some were resistant to breakage (e.g. the whole Y chromsome). The segments represented by G-negative bands were more fragile than the G-positive and G-variable segments.

Chromosome Aberrations↗

Cytogenetic analysis of peripheral lymphocytes in workers occupationally exposed to epichlorohydrin.

Peripheral lymphocytes of 3 groups of adult subject (28 workers occupationally exposed for 4 years to epichlorohydrin [ECHH], 34 matching controls and 21 subjects of the general population (control group) were cytogenetically analysed. In total, 11 806 metaphases were scored. The following frequencies of aberrant cells (bearing mostly chromatid and chromosome breaks) were detected in individual groups: ECHH-exposed group 3.12%; matching controls 2.06%; general population control group 1.33%. The results seem to indicate that even the concentration of 1 mg ECHH/m3 was capable of increasing the frequency of aberrant cells in the occupationally exposed group of workers.

Adult↗

Mutagenic relevance of rat hepatocyte nuclei in the activation and inactivation of xenobiotica. Cyclophosphamide and epichlorohydrin activity on the yeasts S. pombe and S. cerevisiae.

The influence on the mutagenicity of cyclophosphamide (Cy) and epichlorohydrin (ECH), of liver nuclei and hepatic post-mitochondrial (S9) preparations from phenobarbital-treated rats, was examined. The study was conducted in vitro, with 2 yeasts, Schizosaccharomyces pombe (P1 strain) which allows the detection of forward mutations, and Saccharomyces cerevisiae (D5 strain), in which the induction of different genetic effects, such as mitotic recombination, can be evaluated. The results indicated that the nuclear fraction has a qualitative capacity for biotransformation of compounds, overlapping that of S9. From a quantitative point of view, the Cy-activating capacity of the nuclear fraction was twice as high as that of S9 whereas the two fractions showed a similar ECH-inactivating ability. The present study strengthens the hypothesis of the relevance of nuclei as a site of metabolic activation and inactivation of exogenous compounds.

Animals↗

Evaluation of epichlorohydrin (ECH) genotoxicity. Microsomal epoxide hydrolase-dependent deactivation of ECH mutagenicity in Schizosaccharomyces pombe in vitro.

The mutagenic effect of epichlorohydrin (ECH) on the yeast Schizosaccharomyces pombe was studied in vitro in the presence of mouse-liver S9 mix and microsomal and cytosolic fractions. The incubations were always performed in the absence of NADPH-generating systems. S9 mix and microsomes from phenobarbital-pretreated mice significantly reduced ECH mutagenicity, whereas the cytosol did not result in any deactivating effect. The various protein contents of the subcellular fractions were not involved in any scavenger effect as regards ECH mutagenic activity. Moreover, the addition of reduced glutathione to the incubation mixtures indicated that it did not play an important role, either per se or through the enzyme(s) glutathione-S-epoxide transferase(s), in preventing ECH genotoxicity. Our results suggest that microsomal epoxide hydrolase(s) represents the major step in the detoxifying pathway of ECH. These observations were supported by measurements of the specific epoxide hydrolase activity in the various fractions on the same substrate.

Ascomycota↗

The comparative effects of 1,2-dibromo-3-chloropropane (DBCP) and its metabolites, 3-chloro-1,2-propaneoxide (epichlorohydrin), 3-chloro-1,2-propanediol (alphachlorohydrin), and oxalic acid, on the urogenital system of male rats.

Reported similarities in the acute toxic effects of 1,2-dibromo-3-chloropropane (DBCP), 3-chloro-1,2-propaneoxide (epichlorohydrin, ECH), 3-chloro-1,2-propanediol (alphachlorohydrin, ACH), and oxalic acid (OA) have been suggested as presumptive evidence that the metabolism of DBCP to OA, via ECH and ACH, is the cause of the resulting injuries to the kidney and, perhaps, to the epididymis and testis. To test this hypothesis, the comparative toxicities of these four chemicals were studied in male rats after single subcutaneous (sc) injections of maximally tolerated (nonlethal) doses. Kidney, testicular, and liver functions were monitored, and the occurrences of morphological changes in these and several other organs were evaluated 24 hr, 3, 8, 25, and 75 days post-treatment. DBCP caused renal dysfunction (alterations in urine composition and reduced glomerular filtration rate) and marked necrosis of the proximal tubular epithelium in the outer medulla of the kidney. ACH and OA also elicited renal dysfunction, but ACH produced only a mild swelling of the proximal tubular epithelium in the renal cortex and OA produced a focal necrosis anatomically associated with crystal deposition. ECH caused a swelling of the proximal tubular epithelium in the renal cortex, but not frank kidney dysfunction. DBCP also caused a reversible vacuolization of the tubular epithelium in the caput epididymis, progressive testicular atrophy, and a reduction of cauda epididymal sperm concentration. ACH and ECH produced similar effects, as well as epididymal sperm granulomas, spermatocoeles, and an increase in the number of morphologically abnormal spermatozoa. OA failed to produce discernible epididymal or testicular lesions at any time during the study. The development of similar lesions in the epididymis and testis following DBCP, ECH, or ACH treatments is consistent with the theory of metabolism of these chemicals to a common causative gonadotoxic agent. Oxalic acid (OA), however, would not appear to be the common gonadal toxicant. Differences in the effects, both morphological and functional, of DBCP, ECH, ACH, and OA on the kidney, moreover, indicate that DBCP nephropathy is not mediated through metabolism to OA and suggest, as well, that it differs causally from that induced by ECH or ACH. Therefore, the metabolism of DBCP to ECH or ACH, and of ECH or ACH to OA, is insufficient to explain totally the toxic effects of these agents on the urogenital system in male rats.

Animals↗

Cytogenetic investigation of occupational exposure to epichlorohydrin.

Cytogenetic evaluation of peripheral lymphocytes from 93 workers currently exposed to epichlorohydrin has revealed an increase in aberration rates as compared to that of a 75-person group seen for preemployment examination. Statistically significant differences were found in the distribution of individuals with chromatid breaks, chromosome breaks, severely damaged cells, and total abnormal cells. These results confirm the observations of Kucerova et al. in a similar occupational group.

Adult↗

In vitro induction of SCE in human lymphocytes by epichlorohydrin with and without metabolic activation.

Human lymphocytes cultured for 73 h in the presence of BrdU were exposed to epichlorohydrin (ECH) with and without metabolic activation. Cells exposed for the entire culture time without activation showed a significant dose related increase in SCE yield. Exposure for the final 25 h only showed a similar response but with increased tolerance. The presence of S9 mix significantly reduced the effect of ECH compared with a similar exposure without activation. Without activation 4 X 10(-4) M ECH produced a 3-fold increase in the incidence of SCE over the control level. However, with S9 mix a concentration of 10(-3) M ECH was required to produce such an increase indicating that S9 mix may have a detoxifying effect.

Animals↗