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Cytogenetic studies in humans after short-term exposure to ethylene dibromide.

Ethylene dibromide (EDB) has been shown to increase sister chromatid exchange in animal cells in vitro, but its cytogenetic effects in humans have not been previously studied. A solution containing EDB is used in the summer months in Colorado to spray felled pine trees to kill pine beetles. We have assessed the frequencies of sister chromatid exchanges and chromosomal aberrations in the peripheral blood lymphocytes of 14 sprayers both before and after exposure. Six nonexposed individuals also were tested. Full-shift personal breathing-zone air samples indicated that the sprayers were exposed to an average of 60 ppb of EDB, as an eight-hour time weighted average. The range of exposure was from 5 to 281 ppb. Workers sprayed EDB for only five to 26 days during the summer, with an average of 14 days. After adjusting for smoking and the use of prescription medicine, there was no statistically significant difference between the frequencies of either sister chromatid exchange or chromosomal aberrations before and after spraying.

Adult↗

A cytogenetic study of papaya workers exposed to ethylene dibromide.

Ethylene dibromide (EDB) has been shown to be carcinogenic in animal studies and mutagenic in vitro. One cytogenetic study of workers exposed to low levels of EDB for short durations was negative. To test whether exposure to low levels of EDB over long periods caused cytogenetic changes, we have assessed the frequencies of sister-chromatid exchanges (SCE) and chromosomal aberrations (CA) in the peripheral blood lymphocytes of 60 men occupationally exposed to EDB. These men worked in papaya-packing plants where EDB was used to fumigate the fruit after harvest to kill fruit-fly larvae. 42 other men who worked at a nearby sugar mill served as controls. The average duration of exposure of the papaya workers was 5 years. 82 full shift personal breathing-zone air samples indicated that the papaya workers were exposed to a geometric mean of 88 ppb of EDB, as an 8-h time weighted average (TWA). Peaks up to 262 ppb were measured. The proposed OSHA 8-h TWA for EDB is 100 ppb, while NIOSH recommends 45 ppb. No differences in SCE levels were found between exposed and nonexposed workers. No differences were found in the total CA frequency between exposed and nonexposed workers. SCE levels were significantly increased in men who smoked cigarettes (p = 0.0001) and in men who smoked marijuana (p = 0.01). CA levels showed a significant increasing trend with age (p = 0.03).

Adult↗

Activation of alpha(1)-adrenergic receptors potentiates the nephrotoxicity of ethylene dibromide.

Ethylene dibromide (EDB) has been used as a model compound for eliciting hepato- and nephrotoxicity. Conjugation with glutathione (GSH) has been shown to play a role in the bioactivation of EDB. The aim of this study was to determine whether activation of alpha(1)-adrenergic receptors, which causes a decrease in cellular GSH levels, could modulate the nephrotoxicity of EDB. For this purpose, male ICR mice were treated with EDB and/or the alpha-adrenergic agonist, phenylephrine (Pe), or the alpha-adrenergic antagonist, phentolamine (Phe). Animals treated with EDB (40 mg/kg, i.p.) had a 9.3-fold increase in urinary gamma-glutamyltranspeptidase (GGTP: EC 2.3.2.2) activity and a 38% decrease in renal non-protein bound sulfhydryl (NPSH) levels; however, animals co-treated with EDB and Pe (50 mg/kg, i.p.) exhibited a 27.8-fold increase in urinary GGTP activity and a 60% decrease in NPSH levels. The enhanced presence of urinary GGTP and decrease in cellular levels of NPSH was nearly blocked by treating animals concomitantly with EDB and Phe (10 mg/kg, i.p.) or EDB, Pe, and Phe. Histopathological examination revealed the enhanced degree of tissue damage and necrosis following treatment with EDB and Pe, and the protective effect of Phe at ameliorating EDB toxicity. These results indicate that factors that can influence alpha-adrenergic receptors may be critical in assessing dose-response data used in the risk assessment process.

Adrenergic alpha-1 Receptor Agonists↗

The use of human in vitro metabolic parameters to explore the risk assessment of hazardous compounds: the case of ethylene dibromide.

Ethylene dibromide (1,2-dibromoethane, EDB) is metabolized by two routes: a conjugative route catalyzed by glutathione S-transferases (GST) and an oxidative route catalyzed by cytochrome P450 (P450). The GST route is associated with carcinogenicity. An approach is presented to use human purified GST and P450 enzymes to explore the importance of these metabolic pathways for man in vivo. This strategy basically consists of four steps: (i) identification of the most important isoenzymes in vitro, (ii) scaling to rate per milligram cytosolic and microsomal protein, (iii) scaling to rate per gram liver, and (iv) incorporation of data in a physiologically based pharmacokinetic (PBPK) model. In the first step, several GST isoenzymes were shown to be active toward EDB and displayed pseudo-first-order kinetics, while the EDB oxidation was catalyzed by CYP2E1, 2A6, and 2B6, which all displayed saturable kinetics. In the second step, the predictions were in agreement with the measured activity in a batch of 21 human liver samples. In the third step, rat liver P450 and GST metabolism of EDB was predicted to be in the same range as human metabolism (expressed per gram). Interindividual differences in GST activity were modeled to determine "extreme cases." For the most active person, an approximately 1.5-fold increase of the amount of conjugative metabolites was predicted. Lastly, it was shown that the GST route, even at low concentrations, will always contribute significantly to total metabolism. In the fourth step, a PBPK model describing liver metabolism after inhalatory exposure to EDB was used. The saturation of the P450 route was predicted to occur faster in the rat than in man. The rat was predicted to have a higher turnover of EDB from both routes. Nevertheless, when all data are combined, it is crucial to recognize that the GST remains significantly active even at low EDB concentrations. The limitations and advantages of the presented strategy are discussed.

Animals↗

Simultaneous analysis of grain and grain-based products for ethylene dibromide, carbon tetrachloride, and ethylene dichloride.

A method is described for the simultaneous measurement of parts per billion levels of the fumigants ethylene dibromide, carbon tetrachloride, and ethylene dichloride in grain and grain-based products. The fumigants are isolated by hexane co-distillation, separated by capillary gas chromatography, and detected with a mass spectrometer in the selected ion monitoring mode. Recoveries are greater than 90% and standard deviations are approximately 10% of the quantity measured. The method is free of interferences and its precision and accuracy are enhanced by the use of tetradeuterated ethylene dibromide and ethylene dichloride as internal standards.

Carbon Tetrachloride↗

Two cases of ethylene dibromide poisoning.

Ethylene dibromide (EDB) is commonly available as a liquid pesticide for use as fumigant and preservative for storage of cereals and grains in India. Accidental or suicidal ingestion is often associated with often fatal delayed sudden hepatic or renal failure. We report 2 cases of EDB poisoning in humans.

Accidents↗

Non-fatal ethylene dibromide ingestion.

Ethylene dibromide (1,2-dibromoethane) is widely used to fumigate grain and fruit in India. However, acute poisoning due to it has rarely been reported in the literature and most of these patients had an fatal outcome. We describe the suicide attempt of a young male who ingested an ampoule (3 ml) of it, developed acute hepatic and renal failure, metabolic acidosis and coagulopathy but survived following supportive measures.

Acute Kidney Injury↗

In vivo cytogenetic studies on mice exposed to ethylene dibromide.

The pesticide, ethylene dibromide (EDB), was evaluated with in vivo cytogenetic assays to determine its genotoxicity. CD1 male mice were exposed to EDB through intraperitoneal injections. Bone marrow cells isolated from femora were analyzed for sister-chromatid exchange (SCE), chromosome aberration and micronucleus formation. The results showed that only certain concentrations of EDB tested caused a slight but significant increase in SCEs and chromosome aberrations. However, these increases were not dose-related. No increase in the polychromatic erythrocytes with micronuclei was observed following EDB exposure. Also, EDB did not cause cell-cycle delay in comparison with controls. Thus, it appears that EDB is not an effective genotoxic agent in vivo in mice.

Animals↗

Inhibition of rat GSH S-transferases by ethylene dibromide.

Incubation of ethylene dibromide (EDB) (37 mM) with a mixture of rat hepatic cytosol GSH S-transferases at 25 degrees resulted in diminished activity towards 1-chloro-2,4-dinitrobenzene (CDNB) and 3,4-dichloronitrobenzene (DCNB). The loss of both activities followed pseudo first order kinetics with a rate constant of 0.13 +/- 0.03 min-1. The concentration of EDB required for half maximal loss of enzymic activity towards CDNB was 3.2 mM. Removal of EDB from the enzyme by lyophilization or gel filtration did not result in the return of activity towards CDNB. GSH partially prevented the loss of activity, but could not reverse the loss. EDB decreased the activity of forms A(YbYb) and C(YbYb) of rat liver GSH S-transferases but not of forms AA(YcYc), B(YaYc) or B(YaYa). It is concluded that EDB inhibits forms A and C of the GSH S-transferases via a mechanism not involving suicide inhibition.

Animals↗

How do cancer risks predicted from animal bioassays compare with the epidemiologic evidence? The case of ethylene dibromide.

Cancer risks for ethylene dibromide (EDB) were estimated by fitting several linear non-threshold additive models to data from a gavage bioassay. Risks predicted by these models were compared to the observed cancer mortality among a cohort of workers occupationally exposed to the same chemical. Models that accounted for the shortened latency period in the gavaged rats predicted upper bound risks that were within a factor of 3 of the observed cancer deaths. Data from an animal inhalation study of EDB also were compatible with the epidemiologic data. These findings contradict those of Ramsey et al. (1978), who reported that extrapolation from animal data produced highly exaggerated risk estimates for EDB-exposed workers. This paper explores the reasons for these discrepant findings.

Animals↗

Screening and characterization of variant Theta-class glutathione transferases catalyzing the activation of ethylene dibromide to a mutagen.

Ethylene dibromide (EDB) is a widespread environmental pollutant and mutagen/carcinogen. Certain Theta-class glutathione transferases (GSTs), enzymes that catalyze the reaction of reduced glutathione (GSH) with electrophiles, activate EDB to a mutagen. Previous studies have shown that human GST T1-1, but not rat GST T2-2, activates EDB. We have constructed an E. coli lacZ reversion mutagenicity assay system in which expression of recombinant GST supports activation of EDB to a mutagen. Hexa-histidine N-terminal tagging of GST T1-1 results in greatly enhanced expression of the recombinant enzyme and gives a lacZ strain that shows a mutagenic response to EDB at extremely low levels (approximately 1 ng EDB per plate). The hexa-histidine-tagged enzyme was purified in one step by Ni(2+)-affinity chromatography. We applied the lacZ mutagenicity assay to the rapid screening of a library of variant GST Theta enzymes. Sequence variants with altered catalytic activities were identified, purified, and characterized.

Animals↗

Ethylene dibromide as a mitogen for liver.

Intubation of ethylene dibromide (7.5 to 10 mg. per 100 gm. of body weight) into the stomach of nonfasted Wistar rats induces DNA synthesis and cell division in the liver. The peak of DNA synthesis, as measured by 3H-methyl thymidine incorporation, was attained at or shortly after 24 hours. The mitotic waves measured with the aid of colchicine occurred at 24 to 30 hours and 48 to 54 hours after ethylene dibromide treatment. Approximately 16 per cent of liver cells entered mitosis. The increase in DNA synthesis was confirmed by autoradiography. The stimulation of liver cell mitosis occurs in nonfasted animals without apparent cell necrosis. Thus, ethylene dibromide appears to be an effective mitogen for liver under some experimental conditions. The possible relationship between the mitogenic effect at a low dosage range and necrosis at a higher range is discussed.

Animals↗

Ethylene dibromide transformation under methanogenic conditions.

Ethylene dibromide present at a low concentration (less than 100 micrograms/liter) was transformed by reductive dehalogenation under methanogenic conditions in batch bacterial cultures and in a continuous-flow, methanogenic, fixed-film, laboratory-scale column.

Biotransformation↗

Transforming activity of ethylene dibromide in BALB/c 3T3 cells.

Ethylene dibromide was capable of inducing in vitro transformation of BALB/c 3T3 cells either in the presence or in the absence of exogenous metabolic activation (S9-mix). This transforming effect was evidenced by the induction of a higher number of transformed foci as compared to the controls performed with untreated cells or solvent vehicle-treated cells. In the absence of exogenous activation, all assayed doses (ranging from 23.4 micrograms/ml to 187.9 micrograms/ml) exerted transforming activity. Number of foci obtained in EDB-treated plates antransformation frequency of the target cells were higher than those detected in the transformation test performed in the presence of S9-mix.

3T3 Cells↗

Induction of delayed mutations by benzene and ethylene dibromide in Drosophila.

Two carcinogens, ethylene dibromide and benzene, were used to induce delayed (germinal mosaic) sex-linked recessive lethal mutations in spermatozoa and spermatids of adult Drosophila males. Significant numbers of delayed mutations (in F3) were scored in absence of conventional (in F2) mutations. A large proportion of nonlethal F2 cultures carried delayed mutations, so much so that, in some cultures, all F2 females were carriers of mutations. The mechanism through which single strand damage to treated X chromosomes can result in such delayed lethals is discussed. These observations indicate that the delayed mutation test should be used for testing the mutagenicity of environmental compounds, especially carcinogens, which tested negative in the conventional sex-linked recessive lethal mutation test. The data will support the relationship between mutagenesis and carcinogenesis and, also will further enhance the sensitivity of the Drosophila mutation assay.

Animals↗

Rat hepatic glutathione S-transferase-mediated embryotoxic bioactivation of ethylene dibromide.

The embryotoxic effects of ethylene dibromide (EDB) bioactivation, mediated by purified rat liver glutathione S-transferases (GST), were investigated using rat embryos in culture. Significant EDB metabolism was observed with rat liver GST purified by affinity chromatography (specific activity of 188 +/- 11.3 nmol/min/mg protein). The reaction was enzymatic in nature and the conjugation rate was proportional to the concentration of EDB (up to 0.75 mM) and the enzyme present in the reaction medium. EDB activation by 100 units (1 unit = 1 nmol of glutathione consumed per min) of purified rat liver GST caused a significant reduction in general development as measured by crown-rump length, yolk sac diameter, somite number, and the composite score for different morphological parameters (Brown and Fabro methodology). Structures most significantly affected were the central nervous and olfactory systems as well as the yolk sac circulation and allantois. The results of this study clearly indicate that under in vitro conditions, bioactivation of EDB by GST can lead to embryotoxicity.

Animals↗

Association of ethylene dibromide (EDB) with mature cranberry (Vaccinium macrocarpon) fruit.

Ethylene dibromide (EDB), a potential carcinogen, has been used in gasoline mixtures to avoid the accumulation of metallic lead in engines. Ethylene dibromide is present in the environment and in groundwater. Previous analysis has shown that EDB levels have reached up to 16 microg L-1 in the groundwater at two fuel spill plumes in the vicinity of the Massachusetts Military Reservation (MMR) Base and up to 1.69 microg L-1 in the Coonamessett and Quashnet Rivers in Cape Cod, MA (U.S. Air Force IRP, Fact Sheet #98-10, 1998). Groundwater and river water from this area are used to flood some local cranberry bogs for irrigation and harvesting of cranberry fruits. The potential sorption of EDB by cranberry fruits during harvest has caused concern but information regarding its occurrence is not available. In this study, low levels of EDB (0.04-0.15 microg kg-1) were found to be associated with cranberry fruits that were exposed to EDB at levels ranging from 3 to 12 microg L-1 at 10, 20, and 30 degrees C for up to 7 days. Rinsing EDB-exposed cranberry fruits twice with deionized water or once with 0.01 M NaCl solution reduced the amount of EDB associated with the cranberry fruits by 65-72% to a level of 0.02 microg kg-1. Therefore, the EDB most likely is associated with the water residue on the surface of the cranberry fruit rather than being absorbed into the flesh of the fruit during the EDB exposure.

Accidents, Occupational↗