In vitro evaluation of baseline and induced DNA damage in human sperm exposed to benzo[a]pyrene or its metabolite benzo[a]pyrene-7,8-diol-9,10-epoxide, using the comet assay.

Exposure to genotoxins may compromise DNA integrity in male reproductive cells, putting future progeny at risk for developmental defects and diseases. To study the usefulness of sperm DNA damage as a biomarker for genotoxic exposure, we have investigated cellular and molecular changes induced by benzo[a]pyrene (B[a]P) in human sperm in vitro, and results have been compared for smokers and non-smokers. Sperm DNA obtained from five smokers was indeed more fragmented than sperm of six non-smokers (mean % Tail DNA 26.5 and 48.8, respectively), as assessed by the alkaline comet assay (P < 0.05). B[a]P-related DNA adducts were detected at increased levels in smokers as determined by immunostaining. Direct exposure of mature sperm cells to B[a]P (10 or 25 microM) caused moderate increases in DNA fragmentation which was independent of addition of human liver S9 mix for enzymatic activation of B[a]P, suggesting some unknown metabolism of B[a]P in ejaculates. In vitro exposure of samples to various doses of B[a]P (with or without S9) did not reveal any significant differences in sensitivity to DNA fragmentation between smokers and non-smokers. Incubations with the proximate metabolite benzo[a]pyrene-r-7,t-8-dihydrodiol-t9,10-epoxide (BPDE) produced DNA fragmentation in a dose-dependent manner (20 or 50 microM), but only when formamidopyrimidine DNA glycosylase treatment was included in the comet assay. These levels of DNA fragmentation were, however, low in relation to very high amounts of BPDE-DNA adducts as measured with (32)P postlabelling. We conclude that sperm DNA damage may be useful as a biomarker of direct exposure of sperm using the comet assay adapted to sperm, and as such the method may be applicable to cohort studies. Although the sensitivity is relatively low, DNA damage induced in earlier stages of spermatogenesis may be detected with higher efficiencies.

Genomic damage in children accidentally exposed to ionizing radiation: a review of the literature.

During the last decade, our knowledge of the mechanisms by which children respond to exposures to physical and chemical agents present in the environment, has significantly increased. Results of recent projects and programmes focused on children's health underline a specific vulnerability of children to environmental genotoxicants. Environmental research on children predominantly investigates the health effects of air pollution while effects from radiation exposure deserve more attention. The main sources of knowledge on genome damage of children exposed to radiation are studies performed after the Chernobyl nuclear plant accident in 1986. The present review presents and discusses data collected from papers analyzing genome damage in children environmentally exposed to ionizing radiation. Overall, the evidence from the studies conducted following the Chernobyl accident, nuclear tests, environmental radiation pollution and indoor accidental contamination reveals consistently increased chromosome aberration and micronuclei frequency in exposed than in referent children. Future research in this area should be focused on studies providing information on: (a) effects on children caused by low doses of radiation; (b) effects on children from combined exposure to low doses of radiation and chemical agents from food, water and air; and (c) specific effects from exposure during early childhood (radioisotopes from water, radon in homes). Special consideration should also be given to a possible impact of a radiochemical environment to the development of an adaptive response for genomic damage. Interactive databases should be developed to provide integration of cytogenetic data, childhood cancer registry data and information on environmental contamination. The overall aim is to introduce timely and efficient preventive measures, by means of a better knowledge of the early and delayed health effects in children resulting from radiation exposure.

Highly efficient base excision repair (BER) in human and rat male germ cells.

The quality of germ cell DNA is critical for the fate of the offspring, yet there is limited knowledge of the DNA repair capabilities of such cells. One of the main DNA repair pathways is base excision repair (BER) which is initiated by DNA glycosylases that excise damaged bases, followed by incision of the generated abasic (AP) sites. We have studied human and rat methylpurine-DNA glycosylase (MPG), uracil-DNA glycosylase (UNG), and the major AP endonuclease (HAP1/APEX) in male germ cells. Enzymatic activities and western analyses indicate that these enzymes are present in human and rat male germ cells in amounts that are at least as high as in somatic cells. Minor differences were observed between different cellular stages of rat spermatogenesis and spermiogenesis. Repair of methylated DNA was also studied at the cellular level using the Comet assay. The repair was highly efficient in both human and rat male germ cells, in primary spermatocytes as well as round spermatids, compared to rat mononuclear blood cells or hepatocytes. This efficient BER removes frequently occurring DNA lesions that arise spontaneously or via environmental agents, thereby minimising the number of potential mutations transferred to the next generation.

Nucleotide excision repair in rat male germ cells: low level of repair in intact cells contrasts with high dual incision activity in vitro.

The acquisition of genotoxin-induced mutations in the mammalian germline is detrimental to the stable transfer of genomic information. In somatic cells, nucleotide excision repair (NER) is a major pathway to counteract the mutagenic effects of DNA damage. Two NER subpathways have been identified, global genome repair (GGR) and transcription-coupled repair (TCR). In contrast to somatic cells, little is known regarding the expression of these pathways in germ cells. To address this basic question, we have studied NER in rat spermatogenic cells in crude cell suspension, in enriched cell stages and within seminiferous tubules after exposure to UV or N-acetoxy-2-acetylaminofluorene. Surprisingly, repair in spermatogenic cells was inefficient in the genome overall and in transcriptionally active genes indicating non-functional GGR and TCR. In contrast, extracts from early/mid pachytene cells displayed dual incision activity in vitro as high as extracts from somatic cells, demonstrating that the proteins involved in incision are present and functional in premeiotic cells. However, incision activities of extracts from diplotene cells and round spermatids were low, indicating a stage-dependent expression of incision activity. We hypothesize that sequestering of NER proteins by mispaired regions in DNA involved in synapsis and recombination may underlie the lack of NER activity in premeiotic cells.

Enhanced susceptibility of obese mice to glycidamide-induced sperm chromatin damage without increased oxidative stress.

Diet-induced obesity is known to impair male reproduction and may aggravate the male reproductive toxicity of the food contaminant acrylamide. Exposure of male mice to acrylamide induces paternally mediated pre- and post-implantation losses because of spermatozoal toxicity and these effects are potentiated in mice fed a high-fat diet. Glycidamide - an acrylamide metabolite - is the primary mediator of reproductive effects in males. The mechanisms causing the interaction between diet and acrylamide are not clear. However, diet-induced obesity is associated with oxidative stress in male reproductive tissues which might contribute to increased germ cell susceptibility. In this study, we investigated whether a moderate diet-induced obesity regimen could interfere with glycidamide-induced spermatozoal toxicity and increase oxidative stress. For this purpose, sperm chromatin integrity, oxidised DNA and protein levels, transcript levels of oxidative stress responsive genes and glycidamide-induced DNA and haemoglobin adducts were analysed in samples from male mice exposed to a high-fat diet for 6 weeks in combination with a single glycidamide exposure 7 days prior to sacrifice. We found that glycidamide-induced sperm DNA fragmentation was markedly higher in obese than in lean mice. However, the levels of oxidised DNA and/or protein in blood, liver and testicular tissue was lower in obese than in lean mice. Accompanying the reduced level of oxidised macromolecules, the transcript levels of several oxidative stress-related genes were altered in the liver and testis from obese mice suggesting induction of an antioxidant response in these animals. The haemoglobin-glycidamide adduct levels were higher in obese than in lean animals, whereas obesity did not seem to increase the level of glycidamide-induced DNA adducts. These findings show that a moderate diet-induced obesity regimen may potentiate glycidamide-induced sperm cells toxicity and suggest that the increase in glycidamide-induced sperm toxicity observed in obese mice does not depend on overt oxidative stress.

Photoprotection by furocoumarin-induced melanogenesis against DNA photodamage in mouse epidermis in vivo.

The photoprotective properties of furocoumarin plus UVA-induced epidermal melanogenesis were assessed in hairless mice. The ear and dorsal surfaces were topically treated with 6,4,4'-trimethylangelicin (TMA), 5-methoxypsoralen (5-MOP), 8-methoxypsoralen (8-MOP) or psoralen and exposed to UVA for 12 consecutive week-days. The TMA treatment induced intense tanning whereas modest tanning was seen with the other compounds. Seven days after the last treatment, the mice were challenged with a DNA damaging dose of UV radiation. Single strand breaks (SSB) in epidermal DNA were assessed by alkaline elution. Photoprotection was assessed by comparing SSB in furocoumarin-treated mice with control mice (vehicle plus UVA and also no treatment). No photoprotection was seen, with any compound, in dorsal epidermis despite intense pigmentation induced by TMA. Modest photoprotection with all compounds was seen in ear epidermis that was independent of the level of pigmentation. These data show that induced melanogenesis is not always associated, with photoprotection.

Detection of UVR-induced DNA damage in mouse epidermis in vivo using alkaline elution.

Alkaline elution has been used to detect ultraviolet radiation (UVR)-induced DNA damage in the epidermis of C3H/Tif hr/hr mice. This technique detects DNA damage in the form of single-strand breaks and alkali-labile sites (SSB) formed directly by UVA (320-400 nm) or indirectly by UVB (280-320 nm). The latter induces DNA damage such as cyclobutane pyrimidine dimers and pyrimidine-pyrimidone (6-4)-photoproducts, which are then converted into transient SSB by cellular endonucleases, during nucleotide excision repair (NER). The irradiation system used had a spectral output similar in effect to solar UVR, with the UVB component inducing 94% of the edema response observed in mice. Consequently, the majority of SSB detected were those formed via NER of UVB-induced photoadducts. The number of SSB detected immediately after 8 kJ/m2 (2.7 minimum erythema doses determined at 48 h post-UVR [MED]) was low, indicating the formation of only small numbers of transient SSB. When DNA repair inhibitors hydroxyurea and 1-beta-D-arabinofuranosylcytosine were administered (intraperitoneally) to mice 30 min before UVR, they prevented sealing of the DNA SSB formed during NER. A four-fold increase in the number of SSB detected resulted, which was found to be linearly related to the UVR dose. The SSB induced by 2 kJ/m2 (less than an MED) were readily detected, with the ear showing lower numbers of SSB than the dorsum. When repair inhibitors were added post-UVR, the rate of formation of SSB declined rapidly with time of administration, reflecting repair of DNA lesions. After a UVR dose of 6 kJ/m2 (2 MED), 50% of the initial repair-dependent SSB had been removed after approximately 2 h in the ear and 4 h in the dorsum; no more SSB appeared to be incised by 24 h post-UVR. The technique described is an efficient and highly sensitive one for the quantification of SSB induced in UV-irradiated skin samples in vivo.

Interferon-alpha-2b alone and combined with octreotide in primary carcinoid cell-cultures.

Interferon and octreotide are two main therapeutic options in metastatic carcinoid disease. In primary cell cultures prepared from 26 previously untreated carcinoid patients interferon-alpha 2b (alpha-INF), alone and combined with octreotide, significantly reduced medium serotonin (5-HT). The amines were measured with reversed phase HPLC and electrochemical detection, total DNA with a photometric method. Interferon lowered the medium concentration of serotonin to 53% (range 42-79%), octreotide alone to 44% (range 23-48%). Neither interferon, octreotide nor the combined treatment decreased DNA content. Octreotide had no effect on intracellular 5-HT. Both interferon alone and combined with octreotide lowered intracellular 5-HT concentrations significantly. This may represent a direct biochemical effect of interferon on tryptophan metabolism.

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.

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.

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.

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.

Apoptosis in HL-60 cells induced by 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]-furanone (MX).

The potent bacterial mutagen 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]-furanone (MX), which is formed during chlorination of drinking water, has been studied with respect to induction of cell death in promyelocytic leukemic HL-60 cells. Cells exposed to MX for 1 h and further incubated for 3 h, revealed no significant increase in the proportion of cells with compromised plasma membrane damage as judged by trypan blue or propidium iodide exclusion. However, flow cytometric studies and microscopic analysis of HL-60 cells after staining with Giemsa or Hoechst 33342, revealed that more than 30% of the cells exposed to 30-100 microM of MX, showed the characteristic morphology and biochemical markers of apoptosis. On the other hand, in cultures exposed to 300 microM MX, less than 5% of the cells appeared to be apoptotic (< G1 DNA) 3 h after treatment, which is similar to control values. Microscopic analysis of Hoechst 33342-stained cells revealed that they were 'arrested' in the early stages of chromatin condensation, but these cells eventually became necrotic. Some decrease in the percentage of cells in S-phase was observed 3 h after exposure to MX (10, 30 and 100 microM), but the induced cell death was not markedly cell stage specific. The characteristic ladder pattern of apoptotic cells was observed when DNA isolated from MX-exposed HL-60 cells was electrophoresed in agarose. The apoptotic process could also be detected by analysis with alkaline filter elution (AE), as a decrease in the total DNA recovered; and by single cell gel electrophoresis, as a decrease in the average number of cells/comets observable on each slide. With the protocols used no apparent increase in values in the normalized area above the curve (NAAC) (alkaline elution) or tail moments (single cell gel electrophoresis (SCGE)) were detected, indicating that apoptotic cells are not necessarily a confounding factor when assaying for genotoxicity with these techniques.

Metabolism and activation of cyclopenta polycyclic aromatic hydrocarbons in isolated human lymphocytes, HL-60 cells and exposed rats.

The metabolism of radiolabelled benz(j)aceanthrylene (B(j)A) was studied in suspensions of isolated human peripheral mononuclear blood cells (lymphocytes), using high performance liquid chromatography (HPLC). The only known metabolite found after 24 h exposure to 30 microg/ml (120 microM) B(j)A, was B(j)A-1,2-dihydrodiol, representing approximately 35% of the total metabolites formed. B(j)A, benz(l)aceanthrylene (B(l)A) and benzo(a)pyrene (B(a)P) all caused DNA adducts in human lymphocytes, as well as in the human promyelocytic cell line HL-60 cells, as measured by the 32P-postlabelling technique (30 microg/ml, 24 h). The total DNA adduct levels in human lymphocytes exposed to B(j)A, B(l)A or B(a)P were 0.13 +/- 0.03, 1.10 +/- 0.62 and 0.37 +/- 0.10 fmol/microg DNA, respectively, and similar levels were obtained in HL-60 cells (0.18 +/- 0.14, 0.97 +/- 0.35 and 0.29 +/- 0.17 fmol/microg DNA, respectively). For each compound, the human lymphocytes and HL-60 cells in addition showed similar DNA adduct patterns. Cells exposed to B(j)A revealed only one DNA adduct, which, judged by its TLC properties, resulted from B(j)A-1,2-epoxide. As measured by the alkaline filter elution technique, only low levels of single strand DNA breaks (SSB) were observed in both human lymphocytes and HL-60 cells after exposure to B(j)A, B(l)A or B(a)P (24 h, 30 microg/ml). By adding cytosine-1-beta-D-arabinofuranoside (Are C) and hydroxyurea (HU) 1 h prior to analysis to prevent strand break rejoining, some increase in SSB (2-3 times) was observed in the lymphocytes. Co-incubation of human lymphocytes with liver microsomes from PCB-treated rats for 1 h and exposure to B(j)A or B(l)A, increased the DNA adduct levels in the lymphocytes to 12.3 and 37.8 fmol/microg DNA, respectively. A large increase in SSB was also observed, whereas no such increase was observed after co-incubation with human liver microsomes. In vivo exposure of rats to 30 mg/kg B(j)A (i.p.) for 24 h revealed one major DNA adduct in lymphocytes and lung tissue (only one of three rats showed an adduct in liver tissue), apparently resulting from B(j)A-1,2-epoxide. The total DNA adduct level in the lymphocytes was 0.09 fmol/microg DNA, and in lung tissue between 0.10 and 0.62 fmol/microg DNA. Overall, the present data suggests that oxidation at the cyclopenta-ring is an important activation pathway for B(j)A in rats as well as in humans.

DNA strand breaks in testicular cells from humans and rats following in vitro exposure to 1,2-dibromo-3-chloropropane (DBCP).

Preparations of testicular cells from human organ transplant donors and from Wistar rats were compared with respect to their composition of the different testicular cell types, their ability to metabolize 1,2-dibromo-3-chloropropane (DBCP), and their relative sensitivity to induction of DNA single strand breaks and alkali labile sites (ssDNA breaks) after treatment with DBCP, 4-nitroquinoline N-oxide (4-NQO), and X rays. Flow cytometric and microscopic analysis demonstrated that the interindividual variation in the composition of testicular cell types was considerably greater in the human tissue than in that from rats. The in vitro metabolic activation of DBCP (50 to 250 microM), measured as radiolabel covalently bound to macromolecules, was three-fold faster in rat testicular cells compared to human testicular cells. X rays (1 to 10 Gy) and 4-NQO (0.5 to 2.5 microM) induced ssDNA breaks to a similar extent in both human and rat testicular cells as measured by single cell get electrophoresis (SCGE) and alkaline filter elution. In contrast, 1,2-dibromo-3-chloropropane (DBCP) (3 to 300 microM) caused no significant DNA damage in human testicular cells, whereas in rats there was a clear concentration-dependent increase in ssDNA breaks. The data show that, compared to rats, testicular cells from humans are less efficient in activating DBCP to metabolites binding covalently to macromolecules. However, from the rate of covalent binding observed one would expect a significant degree of DBCP-induced ssDNA breaks in the human testicular cells. The low level of DBCP-induced ssDNA breaks in human testicular cells could indicate that different reactive DBCP metabolites are involved in binding to cellular macromolecules compared to DNA damage, or that different rates of DNA repair exist in human and rat testicular cells.

In vitro toxicity of 1,2-dibromo-3-chloropropane (DBCP) in different testicular cell types from rats.

1,2-Dibromo-3-chloropropane (DBCP)-induced toxicity was studied in rat germ cells from different stages of spermatogenesis, separated by centrifugal elutriation, and in Sertoli cells prepared from sexually mature and immature animals. The in vitro metabolic activation of 50 to 250 microM DBCP, measured as covalent binding of 14C-DBCP to macromolecules, was highest in round spermatids, lowest in Sertoli cells and elongating/elongated spermatids, and intermediate in spermatocytes. High concentrations of DBCP (> or = 250 microM) caused a decrease in oxygen consumption and mitochondrial rhodamine 123 uptake, indicating an effect on mitochondrial function. Altered Sertoli cell function, measured as detachment of germ cells in Sertoli-germ cell cocultures, was evident at DBCP concentrations > or = 300 microM. DBCP-induced DNA damage occurred at much lower concentrations (10 to 30 microM) when compared to effects on mitochondrial function and Sertoli cell function. The extent of single strand DNA breaks and alkali-labile sites (ssDNA breaks) measured by the alkaline filter elution technique and the single cell gel electrophoresis assay, were greatest in the round spermatids > spermatocytes = Sertoli cells > elongating/elongated spermatids. The study demonstrates that various testicular cell types show differences in their rates of activation of DBCP to metabolites that bind to macromolecules. DNA is a more sensitive intracellular target in DBCP-induced testicular toxicity than mitochondria. Round spermatids appear to be more susceptible to DBCP-induced ssDNA breaks than spermatocytes, elongating/elongated spermatids, or Sertoli cells.

A comparative study of chemically induced DNA damage in isolated human and rat testicular cells.

Testicular cells prepared from human organ transplant donors or from Wistar rats were used to compare 15 known reproductive toxicants with respect to their ability to induce DNA damage, measured as single-strand DNA breaks and alkali labile sites (ssDNA breaks) with alkaline filter elution. The compounds tested included various categories of chemicals (i.e., pesticides, industrial chemicals, cytostatics, and mycotoxins) most of which are directly acting genotoxicants (i.e., reacting with DNA either spontaneously or via metabolic activation). In addition, a few indirect genotoxic and nongenotoxic reproductive toxicants were included. Six of the chemicals induced no significant levels of ssDNA breaks in human and rat testicular cells; methoxychlor (10 to 100 microM, human and rat), benomyl (10 to 100 microM, human and rat), thiotepa (10 to 1000 microM, human and rat), cisplatin (30 to 1000 microM, human; 100 to 1000 microM, rat), Cd2+ (30 to 1000 microM, human; 100 to 1000 microM, rat), and acrylonitrile (30 to 1000 microM, human; 30 to 300 microM, rat). Four chemicals induced significant levels of ssDNA breaks in testicular cells from both species: styrene oxide (> or = 100 microM, rat and human), 1,2-dibromoethane (EDB) (> or = 100 microM, rat; 1000 microM human), thiram (> or = 30 microM, rat; > or = 100 microM, human), and chlordecone (300 microM, rat; > or = 300 microM, human). Finally, five chemicals induced ssDNA breaks in one of the two species. Four chemicals induced significant ssDNA breaks in rat testicular cells only: 1,2-dibromo-3-chloropropane (DBCP) (> or = 10 microM), 1,3-dinitrobenzene (1,3-DNB) (> or = 300 microM), Cr6+ (1000 microM), and aflatoxin B1 (> or = 100 microM), the last two of these produced only a minor positive response. One chemical, acrylamide, induced a marginal increase in ssDNA breaks in human at 1000 microM, but not in rat testicular cells. Although based on a limited number of donors, the data indicate a close correlation between the induction of DNA damage in human and rat testicular cells in vitro. For some chemicals, however, there appears to be differences in the susceptibility to chemically induced ssDNA breaks of isolated testicular cells from the two species. The data indicate that the parallel use of human and rat testicular cells provides a valuable tool in the assessment of human testicular toxicity.

Inhibitory effects of paracetamol on DNA repair in mammalian cells.

Paracetamol blocks DNA replication by inhibiting deoxyribonucleotide (dNTP) synthesis and may therefore also interfere with DNA repair. In the present work various mammalian cell types were treated with genotoxic agents and allowed to repair in the presence or absence of paracetamol. Alkaline elution was used to assay DNA single-strand breaks plus alkali-labile sites (= SSBs). Resting human mononuclear blood cells (MNC) exposed to 4-nitroquinoline N-oxide (NQO, 3 microM) plus 0.3 mM paracetamol contained twice as many DNA SSBs compared to MNC exposed to NQO alone, and the level of SSBs decreased more slowly during repair in the presence of paracetamol. Deoxyribonucleosides reversed the effects of paracetamol. SSBs induced by MMS or X-rays (2.6 Gy) were not increased by paracetamol. Resting and growth-stimulated MNC, HL-60 cells, rat hepatocytes and human fibroblasts exposed to UV-C (3-12 J/m2) showed varying levels of transient SSBs formed during repair but these were consistently higher in the presence of paracetamol (0.3-1 mM). In rat testicular cells SSBs were induced by NQO and the levels were further increased in the presence of paracetamol, whereas after UV almost no SSBs were detected during repair. The cell-type specific levels of transient SSBs after UV did not correlate with the rate of incision of DNA lesions, measured as the rate of SSB accumulation in the presence of repair inhibitors Ara C plus hydroxyurea. Transient SSBs were present in resting MNC for at least 24 h after UV and paracetamol increased these breaks 4-fold however the overall rate of removal of excisable photodamage during repair did not appear to be reduced by the presence of paracetamol. The present data indicate that paracetamol interferes with nucleotide excision repair in several mammalian cell types. This constitutes a mechanism by which paracetamol may contribute to genotoxicity in humans.

Modulation of the mutagenic effects of 2-amino-3-methylimidazo[4,5-f]quinoline (IQ) and 2-amino-3,4-dimethylimidazo[4,5-f]quinoline (MeIQ) in bacteria with rat-liver 9000 x g supernatant or monolayers of rat hepatocytes as an activation system.

An in vitro protocol was designed to separate the process of metabolic activation from the mutational events. Cultured rat hepatocytes were first incubated with the food mutagens 2-amino-3-methylimidazo[4,5-f]quinoline (IQ) or 2-amino-3,4-dimethylimidazo[4,5-f]quinoline (MeIQ). After the incubation period the medium was removed and further incubated with Salmonella typhimurium TA98. A high direct mutagenic activity of the culture medium was then measured. The half-lives of the mutagenic metabolites formed from IQ and MeIQ were in the order of 45 min. The presence of the cytochrome P450 inhibitors alpha-naphthoflavone and metyrapone during the pre-incubation period reduced the accumulation of mutagenic metabolites. No effects of ascorbate on the mutagenic effects of IQ and MeIQ were seen. (+)-Catechin, another antioxidant and free-radical scavenger, markedly enhanced the number of IQ/MeIQ-induced revertants when added to the hepatocytes. In contrast, (+)-catechin clearly decreased the number of revertants when 9000 X g supernatant from rat liver (S9) was used as an activation system. No marked effect of pentachlorophenol, an inhibitor of hepatocyte sulfation and bacterial O-acetylation, was seen using hepatocytes as an activation system, while the mutagenic activity of both IQ and MeIQ was reduced by 90% in the S9/Salmonella system. The addition of an inhibitor of glucuronidation, galactosamine, or the nucleophile glutathione caused no or only minor decreases in the genotoxic effects of the IQ compounds. With both S9 and hepatocytes as activation systems the relative mutagenic effects observed in the S. typhimurium strains TA98 and TA98 NR were in the same order of magnitude, while a large decrease was seen with TA98/1,8-DNP6. The results show that this in vitro test protocol may be useful as a tool to study mechanisms involved in the formation of mutagenic metabolites.

DNA damage induced by the drinking water mutagen 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]-furanone (MX) in mammalian cells in vitro and in mice.

3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]-furanone (MX) formed during chlorination of water containing natural organic substances, is a very potent bacterial mutagen. Recently, tumours at multiple sites were reported in rats given MX-containing drinking water. We have investigated the genotoxicity of MX in mammalian cells exposed in vitro and in vivo using alkaline filter elution to detect DNA single-strand breaks and/or alkali-labile sites (SSBs). Concentrations as high as 100 and 300 microM MX were required to induce detectable levels of SSBs in the HL-60 cells. If MX treatment was carried out in the presence of DNA repair inhibitors (AraC plus hydroxyurea), the sensitivity of the assay to detect MX-induced SSBs was increased by a factor of 100. The presence of serum proteins during exposure resulted in a minor reduction of the MX-induced DNA damage in HL-60 cells at the lowest MX concentrations. In primary cultures of testicular cells as well as in resting human peripheral blood mononuclear cells (PBMC), a slightly increased level of SSBs was observed at MX-concentrations above 30 microM, this effect was not further increased by repair inhibitors. In LLC-PK1 renal proximal tubular epithelial cells and in growth stimulated human peripheral PBMC, increased SSBs were detected at MX concentrations as low as low as 3-10 microM and higher using repair inhibitors, and at 10 times higher concentrations without repair inhibitors. No dose dependent DNA damage was detected in the liver, kidney, spleen and colon of male B6C3F1 mice administrated high doses of MX (40 and 80 mg kg-1). Moderately increased and dose dependent SSBs were detected in the liver and kidney in the presence of DNA repair inhibitors during MX treatment, but no such increase was observed in the spleen and colon.