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E J Søderlund

Publications and source records attributed to E J Søderlund.

At least 19 recordsLinked to original sources
PubMed1999

Situations with enhanced chemical risks due to toxicokinetic and toxicodynamic factors.

Recognizing toxicokinetic and toxicodynamic variability is important in risk assessment of chemicals and may help to explain interindividual differences in susceptibility in exposed populations. Both toxicokinetic and toxicodynamic factors may be influenced by age and disease processes and show genetic polymorphic variation. Decreased metabolic activity in the very young or very old may enhance chemical toxicity caused by the parent chemical. Similarly, disease processes affecting hepatic metabolism and renal excretion may delay inactivation of many xenobiotics. Genetic polymorphisms may enhance toxicity in rapid metabolizers when the toxicity is caused by a reactive intermediate and increase toxicity in slow metabolizers when the toxicity is caused by a parent chemical. Some cells of the developing conceptus are exquisitely sensitive to chemical exposure. Also, organs and tissues of newborns and elderly individuals may show increased responses toward xenobiotics. In addition, disease-induced altered receptor sensitivity and tissue repair may result in enhanced chemical toxicity. Further, tissue antioxidant defense against radical damage may be compromised under nutritional deficiencies and starvation. Hereditary peculiarities in individual responses to environmental chemicals may be due to polymorphic variation of receptor proteins and tissue repair enzymes, although the database for such variation is quite limited.

Aging↗
PubMed1998

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 micromol/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 micromol/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 micromol/L. Flow cytometric analysis showed that DBCP (1-10 micromol/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 micromol/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.

Animals↗
PubMed1996

Organ-specific and transplacental DNA damage and its repair in rats treated with 1,2-dibromo-3-chloropropane.

An in vivo genotoxicity assay system based on alkaline elution has been used to study the formation and removal of DNA damage induced by 1,2-dibromo-3-chloropropane (DBCP). Cells/nuclei from different tissues and organs of Wistar rats were prepared by a rapid mincing/homogenization technique. Thirty-six samples of which up to 11 were from different organs of the same animal, were then assayed in parallel for DNA damage (DNA single-strand breaks plus alkali-labile sites = SSBs) with a semi-automated alkaline elution system. A single i.p. injection of DBCP gave dose-(5 and 10 mg/kg) and time-(20 min-4 h) dependent SSBs in kidney and liver DNA from male rats. At 10 mg/kg DBCP, SSBs were formed in all organs examined except the bone marrow and colon; however, an increased dose of 40 mg/kg produced SSBs also in the latter two organs. The relative susceptibilities to DBCP-induced DNA damage were: kidney approximately duodenum > liver > lung approximately brain approximately urinary bladder approximately glandular stomach > spleen approximately testis > bone marrow approximately colon. These relative levels correlate with previous data on tissue distribution and organ necrosis in liver, kidney and testis of rats given a single i.p. dose of DBCP. When female rats were injected i.p. with 5, 10 or 20 mg/kg (nonhepatotoxic doses) at day 20 of pregnancy, similar levels of SSBs were detected in the livers of the dam and the fetuses. In adult male rats, time-dependent changes in SSBs were followed in the liver and kidney after DBCP exposure. In both organs SSBs peaked around 4 h post-exposure, 50% had been removed by 12-24 h, whereas at day 2-3 SSB frequencies had returned to control levels. Pretreatment of rats with phenobarbital prior to DBCP exposure reduced the maximum level of DNA damage as well as its persistence. In cultured primary hepatocytes from male rats exposed in vitro to DBCP (2-20 microM. 1 h), 50% of the initial DNA damage had been repaired within approximately 100 min. In conclusion, the experiments indicate that the distribution characteristics of DBCP are of major importance for DNA damage and its persistence in various organs of rats. The data are also in accordance with glutathione-S-transferase, rather than P450, being the most important pathway for metabolic activation of DBCP in rat extrahepatic tissues including the fetal liver. It appears that alkaline elution of cells/nuclei prepared from exposed animals constitutes a sensitive, rapid and versatile technique to study organ- and cell-specific genotoxicity in vivo.

Animals↗
PubMed1995

Metabolism of 1,2-dibromo-3-chloropropane by glutathione S-transferases.

The metabolism of 1,2-dibromo-3-chloropropane (DBCP), measured as the formation of water soluble metabolites and metabolites covalently bound to macromolecules, was studied in isolated rat liver, kidney, and testicular cells, in subcellular fractions, and with purified rat and human glutathione S-transferases (GSTs). The rate of formation of water soluble metabolites in the cells were in the order liver > kidney > testis. The rate of covalent macromolecular binding of reactive DBCP metabolites in the different cell types was of the same relative order. Pretreatment of the cells with the GSH depleting agent diethyl maleate (DEM) markedly decreased the rate of covalent binding in all cell types. Both the overall metabolism and the formation of DBCP metabolites that covalently bound to macromolecules, were substantially higher in rat testicular cells compared to hamster testicular cells. Rat liver cytosol and microsomes, and various purified rat and human GSTs extensively metabolized DBCP to water soluble metabolites in the presence of GSH. When compared to isolated cells, substantially lower rates of binding per mg protein could be observed in subcellular fractions. Binding of DBCP was detected in the microsomal and cytosolic fractions in the absence of NADPH, though in microsomes fortified with a NADPH-regenerating system, the generation of reactive DBCP metabolites was approximately doubled. Studies with purified rat GST isozymes showed that the relative overall GSH conjugation activity with DBCP was in the following order: GST form 3-3 > 2-2 approximately 12-12 > 1-1 > 4-4 approximately 8-8 approximately 7-7. Furthermore, human GST forms also readily metabolized DBCP with activities of GST A1-2 > A2-2 approximately A1-1 > M1a-1a > M3-3 approximately P1-1.

Animals↗
PubMed1995

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).

Animals↗
PubMed1994

Mutagenic activity of halogenated propanes and propenes: effect of bromine and chlorine positioning.

A series of halogenated propanes and propenes were studied for mutagenic effects in Salmonella typhimurium TA100 in the absence or presence of NADPH plus liver microsomes from phenobarbital-induced rats as an exogenous metabolism system. The cytotoxic and mutagenic effects of the halogenated propane 1,2-dibromo-3-chloropropane (DBCP) has previously been studied in our laboratories. These studies showed that metabolic activation of DBCP was required to exert its detrimental effects. All of the trihalogenated propane analogues were mutagenic when the microsomal activation system was included. The highest mutagenic activity was obtained with 1,2,3-tribromopropane, with approximately 50-fold higher activity than the least mutagenic trihalogenated propane, 1,2,3-trichloropropane. The order of mutagenicity was as follows: 1,2,3-tribromopropane > or = 1,2-dibromo- 3-chloropropane > 1,3-dibromo-2-chloropropane > or = 1,3-dichloro-2-bromopropane >> 1-bromo-2,3-dichloropropane > 1,2,3-trichloropropane. Compared to DBCP, the dihalogenated propanes were substantially less mutagenic. Only 1,2-dibromopropane was mutagenic and its mutagenic potential was approximately 1/30 of that of DBCP. In contrast to DBCP, 1,2-dibromopropane showed similar mutagenic activity with and without the addition of an activation system. The halogenated propenes 2,3-dibromopropene and 2-bromo-3-chloropropene were mutagenic to the bacteria both in the absence and presence of the activation system, whereas 2,3-dichloropropene did not show any mutagenic effect. The large differences in mutagenic potential between the various halogenated propanes and propenes are proposed to be due to the formation of different possible proximate and ultimate mutagenic metabolites resulting from the microsomal metabolism of the various halogenated propanes and propenes, and to differences in the rate of formation of the metabolites. Pathways are proposed for the formation of genotoxic metabolites of di- and trihalogenated propanes and dihalogenated propenes.

Alkenes↗
PubMed1994

Genotoxicity of paracetamol in mice and rats.

The genotoxicity of paracetamol, including covalent binding to DNA, induction of DNA single-strand breaks (SSBs), and inhibition of replicative and repair synthesis of DNA, has been investigated in rodents in vivo. In the covalent binding studies male ICR mice were fasted and pretreated with diethyl maleate to deplete hepatic glutathione (GSH) and 300 mg/kg of [G-3H]paracetamol was administered intraperitoneally (i.p.). Animals were killed at 2, 6, 24, 72 and 168 h after paracetamol and hepatic or renal DNA and protein were isolated and the extent of covalent binding determined. Maximal binding to liver DNA, 8.4 +/- 3.1 pmol/mg of DNA, was observed at 2 h and declined rapidly to 2.6 pmol/mg at 24 h. Measurable binding (1.4 pmol/mg of DNA) was detected at 7 days. Protein binding in the liver in these animals peaked between 2 and 6 h (887 pmol/mg of protein at 2 h) and declined monoexponentially to 52 pmol/mg at 7 days. Although based on a limited body of data, covalent binding was also detected in DNA isolated from the kidney. DNA damage measured as SSBs by alkaline elution was induced in nuclear DNA isolated from the liver but not from the kidney, 2 h after i.p. injection of paracetamol at 600 mg/kg in male B6 mice. Only marginal DNA damage was noted at 300 mg/kg. The alkaline elution profile from damaged liver nuclei was markedly biphasic, suggesting that breaks were induced in DNA from a subpopulation of liver cells. The non-hepatotoxic paracetamol regioisomer, acetyl-m-aminophenol (600 mg/kg), which binds covalently to proteins, did not cause DNA SSBs.(ABSTRACT TRUNCATED AT 250 WORDS)

4-Nitroquinoline-1-oxide↗
PubMed1993

Metabolic activation of tris(2,3-dibromopropyl)phosphate to reactive intermediates. I. Covalent binding and reactive metabolite formation in vitro.

Analogs of tris(2,3-dibromopropyl)phosphate (Tris-BP) either labeled at specific positions with carbon-14, phosphorus-32, or oxygen-18 or dual-labeled with both deuterium and tritium were used as metabolic probes to study the chemical and metabolic events in the bioactivation of Tris-BP to chemically reactive metabolites in liver microsomal preparations. Oxidation at the terminal (C-3) carbon atom of the propyl groups of Tris-BP yielded the direct-acting mutagen 2-bromoacrolein as the major metabolite that binds to DNA. Although this reactive metabolite also appears to bind to microsomal protein, the rate of binding of radiolabeled Tris-BP to protein is 15-20x greater than binding to DNA, and some metabolites that retain the phosphate group are bound. Studies with deuterated analogs of Tris-BP implicate oxidation at C-2 of the propyl group as a major pathway that leads to protein binding which is enhanced by phenobarbital pretreatment of rats. Moreover, investigations with 18O-Tris-BP and H2(18)O show that Bis-BP that is formed from oxidation of Tris-BP incorporates one atom of oxygen from water. Deuterium isotope studies suggest that most of the Bis-BP arises from initial oxidation at C-2. Taken together these studies indicate that P-450 oxidation of Tris-BP at C-2 of the propyl group yields a reactive alpha-bromoketone metabolite of Tris-BP that can either alkylate proteins directly or be hydrolyzed to Bis-BP and an alpha-bromo-alpha'-hydroxyketone that can alkylate microsomal proteins.

Acrolein↗
PubMed1993

Metabolic activation of tris(2,3-dibromopropyl)phosphate to reactive intermediates. II. Covalent binding, reactive metabolite formation, and differential metabolite-specific DNA damage in vivo.

Analogs of tris(2,3-dibromopropyl)phosphate (Tris-BP) either labeled at specific positions with carbon-14 and phosphorus-32 or dual-labeled with both deuterium and tritium were administered to male Wistar rats at a nephrotoxic dose of 360 mumol/kg. The covalent binding of Tris-BP metabolites to hepatic, renal, and testicular proteins was determined after 9 and 24 hr, and plasma concentrations of bis(2,3-dibromopropyl)-phosphate (Bis-BP) formed metabolically from Tris-BP were measured at intervals throughout the initial 9-hr postdosing period. The covalent binding of 14C-Tris-BP metabolites in the kidney (2495 +/- 404 pmol/mg protein) was greater than that in the liver (476 +/- 123 pmol/mg protein) or testes (94 +/- 11 pmol/mg protein); the extent of renal covalent protein binding of Tris-BP metabolites was decreased by 82 and 84% when deuterium was substituted at carbon-2 and carbon-3, respectively. Substitution of Tris-BP with deuterium at carbon-2 or carbon-3 also decreased the mean area under the curve for Bis-BP plasma concentration by 48 and 57%, respectively. The mechanism of Tris-BP-induced renal and hepatic DNA damage was evaluated in Wistar rats by an automated alkaline elution procedure after the administration of analogs of Tris-BP or Bis-BP labeled at specific positions with deuterium. Renal DNA damage was decreased when Tris-BP was substituted with deuterium at either carbon-2 or carbon-3; the magnitude of the change correlated with both a decrease in the area under the Bis-BP plasma curve and a decrease in renal covalent binding of Tris-BP metabolites for each of the deuterated analogs. In marked contrast, analogs of Bis-BP labeled with deuterium at carbon-2 or carbon-3 did not show a decrease in the severity of renal DNA damage compared to unlabeled Bis-BP. On the basis of these observations a metabolic scheme for hepatic P-450-mediated oxidation at either carbon-2 or carbon-3 of Tris-BP affording Bis-BP by two alternate pathways that are susceptible to primary deuterium kinetic isotope effects is proposed. The Tris-BP metabolite, Bis-BP, is subsequently metabolized to reactive intermediates that cause DNA damage and bind to kidney proteins in a mechanism independent of cytochrome P-450.

Animals↗
PubMed1993

Chemically induced DNA damage in isolated rabbit lung cells.

By use of an isolation procedure including centrifugal elutriation and density gradient centrifugation, relatively pure fractions of Clara cells and type II cells were obtained from rabbit lungs. These cells and alveolar macrophages isolated by lavage were exposed to methyl methanesulfonate (MMS), 1,2-dibromo-3-chloropropane (DBCP), 1-nitropyrene (1-NP), 2-nitrofluorene (2-NF), 4-(methylnitrosamino)-1-(3-pyridyl)-1-butanone (NNK), N'-nitrosonornicotine (NNN), N-nitrosoheptamethyleneimine (NHMI) or phorbol 12-myristate 13-acetate (TPA). DNA damage measured as alkali-labile sites and/or single-strand breaks was then determined in the different lung cells by an automated alkaline elution system. The direct-acting compound MMS showed similar DNA-damaging effect in Clara cells, type II cells and alveolar macrophages. The nematocide DBCP, activated by both P450- and glutathione S-transferase(s)-dependent pathways, caused considerably less DNA damage in macrophages than in Clara or type II cells. Similar differences between the lung cells in induction of DNA damage as observed with DBCP were demonstrated after exposure to the activation-dependent nitrosamines NNK and NHMI and the tumor promoter TPA. The other test substances (1-NP, 2-NF, NNN) did not cause any marked DNA damage measured by the alkaline elution technique. These findings are in agreement with the known metabolic capacity of these cell types, indicating that Clara and type II cells are possible primary targets for lung toxic/carcinogenic compounds.

Animals↗
PubMed1993

Genotoxic effects of cyclopenta-fused polycyclic aromatic hydrocarbons in isolated rat hepatocytes and rabbit lung cells.

Benz[j]aceanthrylene (B[j]A) and benz[l]aceanthrylene (B[l]A), two isomeric cyclopenta polycyclic aromatic hydrocarbons (CP-PAH) structurally related to 3-methylcholanthrene, were studied with respect to their genotoxic effects in isolated liver and lung cells. Both compounds were found to cause DNA adducts measured by the 32P-postlabelling technique. The level of DNA-adducts in rat hepatocytes exposed to 30 micrograms/ml B[l]A and B[j]A for 4 h were 46.5 +/- 22.0 and 8.3 +/- 5.1 fmol/micrograms DNA respectively. Using butanol extractions, the major and one of the minor B[j]A adducts co-chromatographed with B[j]A-1,2-oxide adducts of 2'-deoxyadenosine and 2'-deoxyguanosine. Thus, oxidation at the cyclopenta-ring of B[j]A appears to be an important activation pathway. In hepatocytes, 3-30 micrograms/ml of B[j]A and B[l]A induced DNA damage and repair measured both as increased alkaline elution of DNA and as increased incorporation of [3H]TdR in the DNA. B[l]A was somewhat more potent than B[j]A in inducing DNA repair. Reactive CP-PAH intermediates formed in the hepatocytes caused mutations in Salmonella typhimurium TA98 upon co-incubation. DNA adducts were also observed in isolated rabbit lung cells exposed to 30 micrograms/ml B[l]A or B[j]A for 2 h. A total of 14.5 +/- 6.9, 2.9 +/- 2.1 and 0.2 +/- 0.6 fmol B[l]A adducts/micrograms DNA were observed in Clara cells, type II pneumocytes and alveolar macrophages respectively. The main B[l]A adduct observed in the liver cells was not found in the lung cells. On the other hand, the levels of B[j]A adducts in the lung cells were in the range 4-14% of that found in liver cells, and no major differences between the various lung cells were observed. Neither B[l]A nor B[j]A induced DNA damage measured by alkaline elution in the lung cells, indicating that these adducts are not alkali labile.

Animals↗
PubMed1992

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↗
PubMed1991

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↗
PubMed1991

Genotoxic effects of 2-amino-3,4-dimethylimidazo(4,5-f)quinoline (MeIQ) in rats measured by alkaline elution.

The alkaline elution method was used to examine genotoxic effects of MeIQ in various organs of rats after in vivo exposure. No DNA damage could be observed in the stomach, small and large intestine, liver, kidney or testis of male Wistar rats 2 h after a single intraperitoneal dose of 80 mg/kg MeIQ. In rats that had been pretreated with Aroclor 1254 (PCB), MeIQ induced significant DNA damage in the liver after both oral and intraperitoneal injection. MeIQ induced DNA damage in the large intestine, liver and kidney of male F344 rats given a single intraperitoneal dose of 80 mg MeIQ/kg or fed 0.03% MeIQ for 13 days. The DNA damage did not seem to accumulate during the feeding period.

Animals↗
PubMed1991

Genotoxic effects of the drinking water mutagen 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]-furanone (MX) in mammalian cells in vitro and in rats in vivo.

The potent bacterial mutagen 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]- furanone) (MX), which is formed during chlorination of drinking water and accounts for about one third of the Ames mutagenicity of tap water, has been studied with respect to its genotoxicity in vitro and in vivo. Treatment with 30-300 microM MX (1 h) induced DNA damage in a concentration-dependent manner in suspensions of rat hepatocytes, as measured by an automated alkaline elution system. The effect was similar in hepatocytes from PCB-induced and uninduced rats. DNA damage was induced in V79 Chinese hamster cells and in isolated rat testicular cells, at the same concentration level as in hepatocytes. Pretreating testicular cells with diethylmaleate, which depletes 85% of cellular glutathione, had no significant effect on the DNA damage induced by MX. The treatment conditions used in the alkaline elution experiments were not cytotoxic to any of the cell types used, as determined by trypan blue exclusion. V79 cells exposed to 2-5 microM MX (2 h) showed an increased frequency of sister-chromatid exchanges (SCE) whereas no significant effect on HGPRT mutation induction was observed. Higher concentrations (greater than 10 microM, 2 h) apparently blocked cell division. The data indicate that MX can react directly with DNA or that MX is metabolized to an ultimate mutagen via some enzyme which is common in mammalian cells. The in vivo experiments showed no evidence of genotoxicity after intraperitoneal (18 mg/kg, 1 h) or oral (18, 63 or 125 mg/kg, 1 h) administration of MX, as measured by alkaline elution, in any of the following organs: the pyloric part of the stomach, the duodenum, colon ascendens, liver, kidney, lung, bone marrow, urinary bladder and the testes. In conclusion, MX is a direct-acting genotoxicant in vitro but no in vivo genotoxicity was detected.

4-Nitroquinoline-1-oxide↗
PubMed1991

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↗