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 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.     

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.     

Postplant Fumigation with DBCP for Citrus Nematode Control in Florida

Eleven citrus groves of diverse varieties and ages infected with Tylenchulus semipenetrans growing in differing soils in Florida were treated with three rates of 1,2-dibromo-3-chloropropane (DBCP) applied by various means. Yield, fruit size, and T. semipenetrans populations in the roots were compared between DBCP-treated and untreated trees over a period of I-3 yr. Maximum fruit size and yield were obtained by applying DBCP at 38-58 kg/hectare (ha) (34-52 lb/acre); whereas best nematode control was with a rate of 77 kg/ha (69 lb/acre). Application of chemical emulsion with a special, drilled, low-profile sprinkler irrigation ground pipe was the most suitable method. Effect of DBCP treatment generally lasted for 3 yr. A mean annual I. 1% increase in fruit diameter, 15.2% increase in fruit yield and a 55.7% decrease incitrus nematode populations was found for D BC P-treated trees in contrast to untreated trees.     

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.     

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.     

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.     

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)     

Penetration of 1,2-Dibromo-3-Chloropropane in a Florida Soil

Gas-liquid chromatography was used to detect movement of the nematicide, 1,2-dibromo-3-chloropropane (DBCP), in soil columns containing top- and subsoil of Astatula fine sand. Topsoil contained 1.4-1.6% organic matter and subsoil 0.20-0.25%. DBCP was applied at various rates as aqueous drenches. Depth of penetration was controlled by organic matter in topsoil and varied with the amount of water applied. Maximum DBCP penetration after 14 days was 28 cm; maximum water infiltration, 115 cm. Maximum depth of penetration was obtained with a water emulsion of 30 μg/ml of DBCP applied in 15 cm of water. DBCP applied in 5 cm of water to soils containing 2.0% and 0.125% organic matter penetrated 6 cm and 60 cm, respectively.     

Effect of Planting Site Preparation, Hydrated Lime,and DBCP (1, 2-dibromo-3-chloropropane) on Populations of Macroposthonia xenoplax and Peach Tree Short Life in Georgia

Annual postplanting applications of 40.7 kg/ha DBCP (1,2-dibromo-3-chloropropane) controlled Macroposthonia xenoplax (Raski, 1952) deGrisse and Loof, 1965 in peach tree short life sites, reduced bacterial canker incidence from 74% to 6%, and inreased the average life of the trees from 3.9 to 6.8 yr for a 7-yr test period. Hydrated lime at 5.5 kg per planting site reduced bacterial canker incidence from 81% 57 % and increased the tree longevity from 2.6 to 6.0 yr. Populations M. xenoplax were inversely correlated with tree longevity.     

Control of Tylenchulus semipenetrans on Citrus With Aldicarb,Oxamyl, and DBCP

Soil application of DBCP (l,2-dibromo-3-chloropropane) and foliar applications of oxamyl (methyl N'',N''-dimethyl-N-[(methylcarbamoyl)oxy]-l-thiooxamimidate) were compared for control of Tylenchulus semipenetrans in a grapefruit (Citrus paradisi) orchard, DBCP reduced nematode populations and increased fruit growth rate, fruit size at harvest, and yield compared to the untreated controls in the 2 years following treatments. Foliar applications of oxamyl reduced nematode populations and increased fruit growth rate slightly the first year, but not in the second. Foliar applications of oxamyl did not improve control attained by DBCP alone. Soil application of aldicarb [2-methyl-2-(methylthio)propionaldehyde-O-(methylcarbamoyl)oxime] or DBCP to an orange (C. sinensis) orchard reduced T. semipenetrans populations in the 3 years tested and increased yield in 1 of 3 years. Aldicarb treatment reduced fruit damage caused by the citrus rust mite, Phyllocoptruta oleivora. Aldicarb, applied at 5.7 or 11.4 kg/ha, by disk incorporation or chisel injection, was equally effective in controlling nematodes, improving yields, fruit size, and external quality. In a grapefruit orchard, chisel-applied aldicarb reduced nematode populations and rust mite damage and increased yields in both years and increased fruit size in one year. The 11.4-kg/ha rate was slightly more effective than the 5.7-kg/ha rate. Aldicarb appears to be an adequate substitute for DBCP for nematode control in Texas citrus orchards and well-suited to an overall pest management system for Texas citrus.     

Some Factors Causing Variability in 1,2-Dibromo-3-Chloropropane Concentrations in Soil

Relative to nematicides with greater fuming capabilities, 1,2-dibromo-3-chloropropane (DBCP) moved nonuniformly through soil. DBCP concentrations in soil were reduced by low soil temperature and the presence of lime or roots within the soil profile, Applications by either water or chisel injection provided DBCP movement to 120 cm and below. Concentrations were least persistent in the upper 15 cm of the field surface and in one situation where application was not followed by irrigation. Values for Henry''s Constant are reported for DBCP at a range of solution temperatures. Certain advantages and disadvantages of soil atmosphere sampling of DBCP are discussed.     

Mouse specific-locus test for the induction of heritable gene mutations by dibromochloropropane (DBCP)

The nematocide DBCP (1,2-dibromo-3-chloropropane) produced negative results in a specific-locus test for gene-mutation induction in the germline of male (101 X C3H)F1 mice, most of which were treated with 5 daily intraperitoneal injections of 80 mg/kg (total exposure, 400 mg/kg); a few received lower exposures. For treated spermatogonial stem cells, the finding of 2 mutations among 39519 offspring--a rate almost identical to the control rate--rules out (at the 5% significance level) an induced mutation frequency greater than 2.0 times the historical control rate. From treated poststem-cell stages, no mutants were found among 6240 offspring, ruling out (at the 5% significance level) a multiple of 8.0 times the control for these cell types. A multiple rearrangement (7 chromosomes involved in 3 translocations) found in one of the mutants probably arose as a postmeiotic event not associated with the DBCP treatment. The fertility of DBCP-treated males was not disturbed, in keeping with the absence of germ-cell toxicity and dominant lethals found by other investigators in these mice, and in contrast to results in certain other species. While the treated (101 X C3H)F1 mice are Ah-responsive, other findings make it questionable whether biotransformation of DBCP to reactive intermediates is accomplished via the Ah-receptor system.     

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     

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).     

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.     

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.     

Efficacy of 1,2-Dibromo-3-chloropropane for Control of Meloidogyne javanica as Influenced by Concentration,Exposure Time and Rate of Degradation

Laboratory experiments were conducted by applying 1,2-dibromo-3-chloropropane (DBCP) to sealed vials of soil infested with Meloidogyne javanica. A minimum initial concentration of 0.25 μg of DBCP/g of oven-dry soil killed all nematodes within 35 days. A concentration of 1.0 μg/g killed all nematodes within 28 days. The rate of degradation of this chemical was determined by treatment of steamed and nonsteamed dry soil in open and sealed vials. Extraction of tile chemical, followed by quantification by gas chromatography, showed approximately 100% of the amount applied recovered after 14 days in sealed vials without soil. With soil present, approximately 10% of the amount of chemical applied was recovered.     

Conversion of chlorinated propanes by Methylosinus trichosporium OB3b expressing soluble methane monooxygenase

Chlorinated propanes are important pollutants that may show persistent behaviour in the environment. The biotransformation of 1-chloropropane, 1,2-dichloropropane, 1,3-dichloropropane and 1,2,3-trichloropropane was studied using resting cell suspensions of Methylosinus trichosporium OB3b expressing soluble methane monooxygenase. The transformation followed first-order kinetics. The rate constants were in the order 1-chloropropane > 1,3-dichloropropane > 1,2-dichloropropane > 1,2,3-trichloropropane, and varied from 0.07 to 1.03 ml min⁻¹ mg of cells⁻¹ for 1,2,3-trichloropropane and 1-chloropropane respectively. Turnover-dependent inactivation occurred for all of the chloropropanes tested. The inactivation constants were lower for 1-chloropropane and 1,2-dichloropropane than for 1,2,3-trichloropropane and 1,3-dichloropropane. Not all the chloride was released during cometabolic transformation of the chlorinated propanes and production of monochlorinated- and dichlorinated propanols was found by gas chromatography. The reaction pathway of 1,2,3-trichloropropane conversion was studied by mass spectrometric analysis of products formed in ²H₂O, which indicated that 1,2,3-trichloropropane was initially oxidized to 2,3-dichloropropionaldehyde and 1,3-dichloroacetone, depending on whether oxygen insertion occurred on the C-3 or C-2 carbon of 1,2,3,-trichloropropane, followed by reduction to the corresponding propanols. The results show that chloropropanes are susceptible to cometabolic oxidation by methanotrophs, but that the transformation kinetics is worse than with cometabolic conversion of trichloroethylene. Received: 27 November 1997 / Received revision: 27 February 1998 / Accepted: 27 February 1998