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Biomedical subjects

E Dybing

Publications and source records attributed to E Dybing.

At least 19 recordsLinked to original sources

Organ-specific DNA damage of tris(2,3-dibromopropyl)-phosphate and its diester metabolite in the rat.

The organ specificity of tris(2,3-dibromopropyl)phosphate(Tris-BP)-induced DNA damage was investigated in the rat 2 h after a single i.p. injection of 350 mumol/kg. Extensive DNA damage, measured with the alkaline elution method, was found in the kidney, liver and small intestine. Less, but significant DNA damage was detected in the brain, lung, spleen, large intestine and testis. The role of different pathways in the activation of Tris-BP to DNA damaging products was studied in isolated liver and testicular cells. Concentrations as low as 2.5-5 microM Tris-BP caused DNA damage in the hepatocytes, whereas an approximately 10-fold higher concentration was needed in testicular cells to produce a similar amount of DNA damage. Depletion of GSH by diethyl maleate (DEM) did not affect the extent of DNA damage caused by Tris-BP in the liver cells, but blocked the genotoxic effect in testicular cells. Two specifically deuterated Tris-BP analogs, C3D2-Tris-BP and C2D1-Tris-BP, were significantly less potent in causing DNA damage than the protio compound in isolated liver cells and were somewhat less potent in testicular cells. The major urinary metabolite of Tris-BP, bis(2,3-dibromopropyl)phosphate (Bis-BP), was less potent than Tris-BP in causing kidney DNA damage after in vivo exposure. Furthermore, Bis-BP induced substantially less DNA damage in isolated liver and testicular cells. Similar to the effect of DEM on the DNA damage caused by Tris-BP, the DNA damage caused by Bis-BP could be decreased by DEM-pretreatment in testicular cells but not in liver cells. The present study shows that Tris-BP is a potent multiorgan genotoxic agent in vivo. The in vitro data indicate that P-450 mediated metabolism of Tris-BP is more important than activation by glutathione S-transferases of Tris-BP in liver cells, whereas the latter activation pathway seems to be most important in testicular cells.

Animals

Species differences in carcinogen metabolism and interspecies extrapolation.

Many carcinogens demonstrate both qualitative and quantitative species differences in activity. Since many carcinogens must be metabolized to reactive electrophiles to elicit their tumorigenic effects, the observed species differences may have a metabolic basis. A number of examples exist that support the concept that metabolic differences are the underlying cause of species variation in carcinogenicity. Such differences are most often of a quantitative nature, but qualitative differences in carcinogenicity may also be due to differences in rates and/or pathways between species. There are also many instances in which there is no clear evidence that metabolism explains species differences in carcinogenicity. Carcinogenicity studies are often performed at much higher doses than those encountered by humans. Since metabolic processes may become saturated at high tissue concentrations, the rates and pathways of metabolic activation and detoxication may be different at high doses from those at lower doses. Such metabolic variation can lead to differences in target tissue doses, resulting in altered tissue responses at high doses in relation to lower doses. In situations in which no saturation of the metabolic pathways occurs, tissue concentrations are proportional to the administered dose. Scaling of doses from those used in experimental animals to those experienced by humans has often involved simple conversion factors, such as body weight or surface area. Since the reactions involved in carcinogen metabolism may differ both for high and low doses and for various species, much more realistic extrapolations from animal to human can be obtained using physiologically based kinetic modelling. The metabolism of carcinogens in humans shows large interindividual variation, which in turn may be reflected in differences in individual risks. The occurrence of genetic polymorphisms in carcinogen metabolizing enzymes indicates that subgroups of the population may experience carcinogenic risks distinctly different from those of the rest of the population.

Animals

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 microM) 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.

Animals

Prevention of 1,2-dibromo-3-chloropropane (DBCP)-induced kidney necrosis and testicular atrophy by 3-aminobenzamide.

The poly(ADP-ribosyl)transferase inhibitor, 3-aminobenzamide (3-ABA), reduced morphological evidence of 1,2-dibromo-3-chloropropane (DBCP)-induced DNA damage determined by alkaline elution. The DBCP plasma, kidney, and testis tissue doses determined between 1 and 8 hr after a single intraperitoneal injection were somewhat higher with than without 3-ABA pretreatment. Furthermore, the amount of DBCP metabolites covalently bound to macromolecules was reduced to about 20-30 percent of control, indicating that 3-ABA may have an effect on the formation/detoxication of reactive DBCP metabolites. Inhibitors of replicative DNA synthesis such as hydroxyurea or stimulation of DNA replication by nephrectomy did not affect the cytotoxicity, neither did inhibitors of DNA repair such as beta-cytosine arabinoside and beta-lapachone.

Animals

Co-culture systems for assessing the stability and genotoxicity of reactive 1,2-dibromo-3-chloropropane (DBCP) metabolites.

1,2-Dibromo-3-chloropropane (DBCP) induced DNA damage, measured by alkaline elution, at low concentrations (5-10 microM) in suspensions of hepatocytes and testicular cells isolated from rats. At higher concentrations (greater than or equal to 100 microM) DBCP caused DNA damage and increased the frequency of sister chromatid exchanges in Chinese hamster V79 cells. When DBCP (2.5-10 microM) was tested for its ability to cause unscheduled DNA synthesis (UDS) in monolayers of liver cells isolated from untreated rats, a clear positive response was obtained. No increase in UDS was detectable when liver cells isolated from PCB-pretreated rats were used. In contrast, DBCP (greater than or equal to 50 microM) was metabolized in hepatocytes from PCB-pretreated rats to products mutagenic to Salmonella typhimurium TA100 in co-culture with the hepatocytes, whereas control hepatocytes were substantially (40-fold) less active. No bacterial mutagenicity could be detected when the TA100 strain was co-incubated with isolated rat testicular cells and DBCP. In co-cultures of hepatocytes and V79 cells DBCP-induced DNA damage in V79 cells occurred at low concentrations (10 microM DBCP) compared to the concentration (100 microM) needed to induce DNA damage in the V79 cells incubated without hepatocytes. Testicular cells were not able to enhance DBCP-induced DNA damage in the V79 cells. The data indicate that the putative reactive DBCP episulphonium ion metabolite formed in the testicular cells presumably responsible for testicular cell DNA damage, is not capable of escaping the cell where it is formed. Other reactive DBCP metabolites generated in the liver cells seem to be able to interact with the DNA of neighbouring cells.

Animals

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)

Animals

Formation of genotoxic products from N-nitrosoheptamethyleneimine (NHMI), 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK) and N'-nitrosonornicotine (NNN) by isolated rabbit lung cells.

The genotoxic potentials of N-nitrosoheptamethyleneimine (NHMI), 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK) and N'-nitrosonornicotine (NNN) were studied in fresh preparations of Clara cells and type II cells isolated by centrifugal elutriation and density gradient centrifugation, and macrophages from rabbit lung. The activation of the compounds to bacterial mutagens was assayed in the Salmonella mutagenicity test using strains of TA 100 and TA 1530 preincubated with test chemicals and cells placed in chambers with nucleopore membranes to separate cells and bacteria. Unscheduled DNA synthesis was measured by incorporation of [3H]-thymidine in the cells after exposure to the compounds. NHMI, NNK and NNN were not activated to bacterial mutagens by Clara cells, type II cells or macrophages, presumably because the reactive metabolites generated were not released into the incubation medium. However, NHMI and NNK increased unscheduled DNA synthesis in Clara cells, and the highest repair activity was found after incubation with NNK. The effect of NNN was only marginal. This indicates that NHMI and NNK are genotoxic in the rabbit lung and that the Clara cells are involved in the metabolic activation of these compounds.

Animals

Species differences in short term toxicity from inhalation exposure to bromobenzene.

Lung, liver and kidney injury were studied in mice, rats and rabbits 48 h after termination of a 4 h inhalation exposure to bromobenzene vapour (250-3400 ppm). Light and electron microscopy of lung tissue revealed injury to Clara cells and adjacent epithelium in mouse bronchioli (bromobenzene concentration 250 ppm and 1000 ppm) and to Clara cells of rat bronchi and bronchioli (1000 ppm bromobenzene) and of rabbit bronchi (2500 ppm and 3400 ppm). Histological and clinicochemical indices of liver damage were found in the same animals, whereas kidney toxicity was observed in mice (two out of ten showed tubular necrosis and elevated concentration of plasma urea) and rats (all had elevated plasma concentrations of creatinine) exposed to 1000 ppm bromobenzene. Inhalation exposure thus produced less kidney injury than expected from previous studies with equimolar doses given intraperitoneally. The mouse was the most severely affected species, followed by the rat, and lastly the rabbit. The animal susceptibility could not be ranked according to the rate of 14C-bromobenzene covalent binding in lung or liver, but it was inversely related to the rate of N-demethylation of benzphetamine (indicative of P450IIB activity) in both lung and liver microsomal preparations. Differences in a P450 mediated detoxification could therefore be of importance in species variability to bromobenzene injury.

Administration, Inhalation

Species differences in kidney necrosis and DNA damage, distribution and glutathione-dependent metabolism of 1,2-dibromo-3-chloropropane (DBCP).

Species differences and mechanisms of 1,2-dibromo-3-chloropropane (DBCP) nephrotoxicity were investigated by studying DBCP renal necrosis and DNA damage, distribution and glutathione-dependent metabolism in rats, mice, hamsters and guinea pigs. Extensive renal tubular necrosis was observed in rats 48 hr after a single intraperitoneal administration (21-170 mumol/kg) of DBCP. Significantly less necrosis was found in mice and guinea pigs, whereas no renal damage was evident (less than 680 mumol/kg) in hamsters. The activation of DBCP to DNA damaging intermediates in vivo, as measured by alkaline elution of DNA isolated from kidney nuclei 60 min. after intraperitoneal injection of DBCP, was compared in all four species. Distinct DNA damage was detected in rats, mice and hamsters as early as 10 min. after administration of DBCP and within 30 min. in guinea pigs. Rats and guinea pigs showed similar sensitivity towards DBCP-induced DNA damage (extensive DNA damage greater than 21 mumol/kg DBCP), whereas in mice and hamsters a 10-50 times higher DBCP dose was needed to cause a similar degree of DNA damage. Renal DBCP concentrations at various time-points (20 min., 1, 3 and 8 hr) after intraperitoneal administration (85 mumol/kg) revealed that the initial (20 min.) DBCP concentration was substantially higher in rats and guinea pigs compared to the other two species. Furthermore, kidney elimination of DBCP occurred at a significantly lower rate in rats than in mice, hamsters and guinea pigs.(ABSTRACT TRUNCATED AT 250 WORDS)

Acute Kidney Injury

Short term inhalation of bromobenzene: methodology and absorption characteristics in mouse, rat and rabbit.

In a dynamic inhalation system, mice, rats and rabbits were exposed to bromobenzene vapour (250-3400 p.p.m.) for 4 hr. Blood concentrations of bromobenzene were determined by head-space gas chromatography. After inhalation of 1000 p.p.m. for 4 hr, concentrations of 153, 102 and 47 micrograms bromobenzene/ml blood were found in mice, rats and rabbits, respectively. In vitro experiments showed a blood/air partition coefficient at 37 degrees of approximately 200, which was reflected by a linear uptake of bromobenzene up to an air concentration of 2500 p.p.m. Compared with results obtained previously by intraperitoneal bromobenzene administration inhalation resulted in higher blood concentrations.

Absorption

Species differences in testicular necrosis and DNA damage, distribution and metabolism of 1,2-dibromo-3-chloropropane (DBCP).

The human testicular toxicant 1,2-dibromo-3-chloropropane (DBCP) was studied for the same end-point in 4 different species of laboratory animals. Marked necrosis and atrophy of the seminiferous epithelium were observed in rats and guinea pigs 10 days after a single i.p. administration of DBCP (170-340 mumol/kg), whereas significantly less damage was observed in hamsters and mice. The testicular concentrations of DBCP measured at various time-points after the i.p. injection of DBCP indicated that factors in addition to tissue concentration were of importance for the observed species differences in sensitivity towards DBCP-induced testicular damage. Also, there did not seem to be any direct correlation between DBCP-induced in vivo testicular toxicity and in vitro GSH-dependent dehalogenation, inasmuch as the rate of bromide release from DBCP with hamster testicular cytosol was as fast as that with rat cytosol. Testicular DNA damage, as determined by alkaline elution 60 min after in vivo administration of 170 mumol/kg DBCP, was observed only in rats and guinea pigs. Thus, induction of DNA damage correlates with the relative susceptibilities of the species towards DBCP-induced testicular necrosis. To further study species differences in testicular activation of DBCP to DNA-damaging intermediate(s), cells isolated from the testes of the 4 species were incubated with DBCP. Testicular cells from rats and guinea pigs were the only preparations developing substantial DNA damage after 60 min incubation with low concentrations of DBCP (5-50 microM). The findings indicate that rats are sensitive towards DBCP-induced testicular necrosis because rat testicular cells easily activate DBCP to a DNA-damaging intermediate(s). The relative high testicular DBCP concentration as well as the ability to activate DBCP may explain the sensitivity of guinea pigs towards DBCP-induced testicular toxicity.

Animals

Role of P-450 activity and glutathione levels in 1,2-dibromo-3-chloropropane tissue distribution, renal necrosis and in vivo DNA damage.

Treatments known to alter P-450 activity and glutathione levels were used to elucidate the involvement of P-450 and glutathione S-transferase metabolism in 1,2-dibromo-3-chloropropane (DBCP) organ toxicity in the rat. Phenobarbital pretreatment abolished DBCP-induced renal necrosis, whereas it had only a small effect on initial renal DNA damage. The DBCP levels in plasma and tissues were markedly reduced by phenobarbital pretreatment. Perdeuterated DBCP had much higher plasma and tissue levels than protio-DBCP in phenobarbital-pretreated animals, but perdeuteration was without effect in uninduced animals. This indicates that P-450 metabolism of DBCP is of major importance only in phenobarbital-pretreated animals. In order to study the effects of decreased glutathione levels on renal distribution and toxicity, rats were pretreated with either diethyl maleate or buthionine sulfoximine. The DBCP levels in plasma and tissues showed transitory elevations after diethyl maleate and buthionine sulfoximine pretreatment compared to the control situation. Despite the fact that diethyl maleate and buthionine sulfoximine pretreatments are known to block DBCP-induced DNA damage in vitro, these pretreatments did not significantly alter DBCP-induced renal necrosis nor DNA damage. Thus, a role for glutathione conjugation in DBCP-induced in vivo renal toxicity could not be established in the present study.

Animals