Comparative toxicity of chloro- and bromo-nitromethanes in mice based on a metabolomic method

Halonitromethanes (HNMs) as one typical class of nitrogenous disinfection byproducts have been widely found in drinking water. In vitro test found HNMs could induce higher cytotoxicity and genotoxicity than trihalomethanes and haloacetic acids. However, data on toxic effect from in vivo experiment is limited. In this study, bromonitromethane (BNM), bromochloronitromethane (BCNM) and trichloronitromethane (TCNM) were chosen as target HNMs, and exposed to mice for 30 d. Hepatic toxicity and serum metabolic profiles were determined to reveal toxic effects and mechanisms of the three HNMs. Results showed the three HNMs significantly decreased relative liver weight, indicating liver is one of the target organs. Further, the three HNMs exposure damaged hepatic antioxidant defense system, and increased oxidative DNA damage. Nuclear magnetic resonance based metabolomics analysis found amino acid metabolism and carbohydrate metabolism were disturbed by HNMs exposure. Some metabolites in these metabolisms are related to oxidative stress and damage. Combined with above results, BNM had the highest toxicity, followed by BCNM and TCNM, indicating bromo-HNMs had higher toxicity than chloro-HNMs. Induction of oxidative stress is one of the toxicity mechanisms of HNMs. This study firstly provides the insight into in vivo toxicity of HNMs and their underlying mechanisms based on metabolomics methods, which is very useful for their health risk assessment in drinking water.

Oxidative stress alters base excision repair pathway and increases apoptotic response in apurinic/apyrimidinic endonuclease 1/redox factor-1 haploinsufficient mice

Apurinic/apyrimidinic endonuclease 1/redox factor-1 (APE1/Ref-1) is the redox regulator of multiple stress-inducible transcription factors, such as NF-kappaB, and the major 5'-endonuclease in base excision repair (BER). We utilized mice containing a heterozygous gene-targeted deletion of APE1/Ref-1 (Apex(+/-)) to determine the impact of APE1/Ref-1 haploinsufficiency on the processing of oxidative DNA damage induced by 2-nitropropane (2-NP) in the liver tissue of mice. APE1/Ref-1 haploinsufficiency results in a significant decline in NF-kappaB DNA-binding activity in response to oxidative stress in liver. In addition, loss of APE1/Ref-1 increases the apoptotic response to oxidative stress, in which significant increases in GADD45g expression, p53 protein stability, and caspase activity are observed. Oxidative stress displays a differential impact on monofunctional (UNG) and bifunctional (OGG1) DNA glycosylase-initiated BER in the liver of Apex(+/-) mice. APE1/Ref-1 haploinsufficiency results in a significant decline in the repair of oxidized bases (e.g., 8-OHdG), whereas removal of uracil is increased in liver nuclear extracts of mice using an in vitro BER assay. Apex(+/-) mice exposed to 2-NP displayed a significant decline in 3'-OH-containing single-strand breaks and an increase in aldehydic lesions in their liver DNA, suggesting an accumulation of repair intermediates of failed bifunctional DNA glycosylase-initiated BER.

Mutagenicity of N-nitrosodiethanolamine in a V79-derived cell line expressing two human biotransformation enzymes

N-nitrosodiethanolamine (NDELA) has demonstrated carcinogenic activity in various rodent models. However, it is negative or only weakly active in standard in vitro genotoxicity assays. This poor response might be due to the requirement of specific enzymes for its activation. Previous work indicated that cytochrome P450 (CYP) 2E1, alcohol dehydrogenases and sulphotransferases (SULTs) can convert NDELA into reactive metabolites. We report here that NDELA induces concentration-dependent gene mutations (at the hprt locus) in V79-hCYP2E1-hSULT1A1 cells, engineered for expression of human CYP2E1 and human SULT1A1, but is inactive in parental V79 cells. Mutagenicity of NDELA in V79-hCYP2E1-hSULT1A1 cells was abolished by the CYP2E1 inhibitor 1-aminobenzotriazole, but unaffected by the SULT1A1 inhibitor pentachlorophenol. The efficiency and specificity of these inhibitors was demonstrated in gene mutation assays using SULT- and CYP2E1-dependent reference mutagens, 2-nitropropane and N-nitrosodimethylamine, respectively. In this study, it is documented for the first time that NDELA can induce gene mutations in mammalian cells. Whereas human CYP2E1 was required for its activation, human SULT1A1 was not involved either in its activation or its inactivation in our cell model.

Method for quantifying nitromethane in blood as a potential biomarker of halonitromethane exposure

The cytotoxicity and genotoxicity of nitromethane and its halogenated analogues in mammals raise concerns about potential toxicity to humans. This study shows that halonitromethanes are not stable in human blood and undergo dehalogenation to form nitromethane. We quantified nitromethane in human blood using solid-phase microextraction (SPME) headspace sampling coupled with gas chromatography (GC) and high resolution mass spectrometry (HRMS). The limit of detection was 0.01 microg/L with a linear calibration curve spanning 3 orders of magnitude. This method employs isotope dilution to precisely quantify trace amounts of nitromethane (coefficient of variation <6%). At three spiked concentrations of nitromethane, method accuracy ranged from 88 to 99%. We applied this method to blood samples collected from 632 people with no known occupational exposure to nitromethane or halonitromethanes. Nitromethane was detected in all blood samples tested (range: 0.28-3.79 microg/L, median: 0.66 microg/L). Time-course experiments with trichloronitromethane- and tribromonitromethane-spiked blood showed that nitromethane was the major product formed (1 nmole tribromonitromethane formed 0.59 nmole of nitromethane, whereas 1 nmole trichloronitromethane formed 0.77 nmole nitromethane). Nitromethane may form endogenously from peroxynitrite: nitromethane concentrations increased proportionately in blood samples spiked with peroxynitrite. Blood nitromethane can be a biomarker of exposure to both nitromethane and halonitromethanes. This sensitive, accurate, and precise analytical method can be used to determine baseline blood nitromethane level in the general population. It can also be used to study the health impact from exposure to nitromethane and halonitromethanes in occupational environments and to assess trichloronitromethane (chloropicrin) exposure in chemical terrorism investigations.

Acute liver damage induced by 2-nitropropane in rats: Effect of diphenyl diselenide on antioxidant defenses

The effect of post-treatment with diphenyl diselenide on liver damage induced by 2-nitropropane (2-NP) was examined in male rats. Rats were pre-treated with a single dose of 2-NP (100 mg/kg body weight dissolved in canola oil). Afterward, the animals were post-treated with a dose of diphenyl diselenide (10, 50 or 100 micromol/kg). The parameters that indicate tissue damage such as liver histopathology, plasma aspartate aminotransferase (AST), alanine aminotransferase (ALT), gamma-glutamyl transferase (GGT), urea and creatinine were determined. Since the liver damage induced by 2-NP is related to oxidative damage, lipid peroxidation, superoxide dismutase (SOD), catalase (CAT) and ascorbic acid level were also evaluated. Diphenyl diselenide (50 and 100 micromol/kg) effectively restored the increase of ALT and AST activities and urea level when compared to the 2-NP group. At the higher dose, diphenyl diselenide decreased GGT activity. Treatment with diphenyl diselenide, at all doses, effectively ameliorated the increase of hepatic and renal lipid peroxidation when compared to 2-NP group. 2-NP reduced CAT activity and neither alter SOD activity nor ascorbic acid level. This study points out the involvement of CAT activity in 2-NP-induced acute liver damage and suggests that the post-treatment with diphenyl diselenide was effective in restoring the hepatic damage induced by 2-NP.

NTP carcinogenesis studies of 2,2-bis(bromomethyl)-1,3-propanediol, nitromethane, and 1,2,3-trichloropropane (cas nos. 3296-90-0, 75-52-5, and 96-18-4) in guppies (Poecilia reticulata) and medaka (Oryzias latipes) (Waterborne Studies)

The NTP chose to initiate studies in fish as an exploration of alternate or additional models for examining chemical toxicity and carcinogenicity. The use of small fish species in carcinogenicity testing offered potential advantages as a bioassay test system, including significant savings in cost and time over rodent studies. Large numbers of small fish could be easily maintained in a limited area. The two species chosen for study were guppy (Poecilia reticulata) and medaka (Oryzias latipes), both of which are hardy, easily maintained, and have a low occurrence of background lesions. The three chemicals chosen for study in fish had already been studied by the NTP in rodents, permitting a comparison of results between the two models. Two of the chemicals used (2,2-bis(bromomethyl)-1,3-propanediol and 1,2,3-trichloropropane) were mutagenic and multisite carcinogens in rats and mice. The third chemical, nitromethane, was nonmutagenic with a more modest carcinogenic response in rodents. Male and female guppies and medaka were exposed to 2,2-bis(bromomethyl)- 1,3-propanediol (greater than 99% pure), nitromethane, (greater than 99% pure), or 1,2,3-trichloropropane (99% pure) in aquaria water for up to 16 months. OVERALL STUDY DESIGN: Groups of approximately 220 guppies (two replicates of 110) were maintained in aquaria water containing nominal concentrations of 0, 24, 60, or 150 mg/L 2,2-bis(bromomethyl)-1,3-propanediol; 0, 10, 30, or 70 mg/L nitromethane; or 0, 4.5, 9.0, or 18.0 mg/L 1,2,3-trichloropropane. Groups of approximately 340 medaka (two replicates of 170) were maintained in aquaria water containing 0, 24, 60, or 150 mg/L 2,2-bis(bromomethyl)-1,3-propanediol; 0, 10, 20, or 40 mg/L nitromethane; or 0, 4.5, 9.0, or 18.0 mg/L 1,2,3-trichloropropane. The overall study durations were 16 months for all guppy studies, 14 months for 2,2-bis(bromomethyl)-1,3-propanediol-exposed medaka, and 13 months for nitromethane- and 1,2,3-trichloropropane-exposed medaka. Ten guppies and 10 medaka from each group replicate were sacrificed at 9 months for histopathologic analysis. Approximately one third of the remaining fish from each group were placed in chemical-free water at 9 months and constituted a stop-exposure study component. The remainder of the fish were exposed for the duration of the study and constituted the core study component. A stop-exposure component was added to determine if stopping the exposure at 9 months and transferring to chemical-free aquaria might allow for better survival and tumor development. The sex of guppies and medaka was determined at histopathologic analysis. 2,2-BIS(BROMOMETHYL)-1,3-PROPANEDIOL - 16-MONTH STUDY IN GUPPIES: 2,2-Bis(bromomethyl)-1,3-propanediol was chronically toxic to guppies in the 60 and 150 mg/L core and stop-exposure groups. Due to mortality, exposure of core study animals in the 150 mg/L group was terminated on day 443, after approximately 64 weeks on study, and fish were maintained in 2,2-bis(bromomethyl)- 1,3-propanediol-free water in the exposure system until the end of the study at 69 weeks. Nominal exposure concentrations of 24, 60, and 150 mg/L provided actual aquaria water exposure concentrations of 20.0, 53.5, and 139.0 mg/L 2,2-bis(bromomethyl)- 1,3-propanediol, respectively. There were no treatment-related differences between the control and exposed groups in body weights or lengths. At 9 months, hepatocellular adenomas occurred in one 24 mg/L male and in one 150 mg/L male. In the core study, the incidence of hepatocellular adenoma or carcinoma (combined) in 150 mg/L males was greater than that in the controls; multiple adenomas occurred in two 150 mg/L males and in one 150 mg/L female. Cholangioma occurred in a small number of exposed males and females. In the stop-exposure study, incidences of hepatocellular adenoma (including multiple) and of hepatocellular carcinoma were greater in 150 mg/L males than in controls. One cholangioma and one cholangiocarcinoma occurred in the 150 mg/L female group. 14-MONTH STUDY IN MEDAKA: Exposure to 2,2-bis(bromomethyl)-1,3-propanediol did not result in any significant reduction in survival, although the mortality of fish was somewhat greater in the 60 and 150 mg/L core study groups than in the control and 24 mg/L groups. After reallocation, mortality of medaka in the 60 and 150 mg/L core groups was slightly increased over the corresponding stop-exposure groups. Nominal exposure concentrations of 24, 60, and 150 mg/L provided actual exposure concentrations of 19.4, 56.9, and 137.8 mg/L 2,2-bis(bromomethyl)- 1,3-propanediol, respectively. Core study animals in the 60 and 150 mg/L groups were significantly larger, in both body length and weight, than control group fish. In the core study, the incidence of hepatocellular adenoma or carcinoma (combined) was increased in 150 mg/L males. Cholangiocarcinomas occurred in a few exposed males and females, with all but one occurring in 150 mg/L fish. One cholangioma occurred in a 150 mg/L female, and one occurred in a control female. In the stop-exposure study, incidences of hepatocellular adenoma or carcinoma (combined) were marginally increased in the 150 mg/L group of males and in the 60 and 150 mg/L groups of females as compared with controls. Cholangiocarcinoma occurred in one male and one female in the 150 mg/L groups and in one control female. NITROMETHANE - 16-MONTH STUDY IN GUPPIES: Although the cause of death could not be confirmed in many cases, mortality in the 70 mg/L groups appeared to indicate that this level of nitromethane exposure was chronically toxic. This is confirmed by the similar survival rate of guppies from all treatments following removal from treatment aquaria and placement in stop-exposure. Due to the high mortality of fish in the 70 mg/L core study groups, these fish were removed from treatment (day 396) and fixed for histological analyses after approximately 57 weeks on study. The controls and other exposed groups were sacrificed at 70 weeks. Nominal exposure concentrations of 10, 30, and 70 mg/L provided actual exposure concentrations of 9.9, 28.7, and 66.4 mg/L nitromethane, respectively. There were no treatment-related differences between the control and exposed groups in body lengths or weights. 13-MONTH STUDY IN MEDAKA: Nitromethane in the aquaria supported a substantial microfaunal growth which, without frequent cleaning, affected water quality and treatment concentrations. To maintain acceptable water quality and treatment concentrations potentially affected by the rapid microfaunal growth, the study aquaria were brushed once and siphoned three times each day. Due to this frequent activity, a number of fish probably died due to mechanical injury. Unfortunately, the cause of death could not be confirmed in many cases; the mortality from this activity is believed to have been approximately uniform among treatments and should not have affected the comparison of survival between treatments. Based on mortality in this study and the previous life-span evaluation, the life phase of this study was terminated approximately 13.5 months after hatching. Nominal exposure concentrations of 10, 20, and 40 mg/L resulted in actual exposure concentrations of 9.3, 20.8, and 41.7 mg/L nitromethane, respectively. No differences between control and exposed groups were found in body lengths or weights at the 9-month interim evaluation. Due to mortality, unequal numbers of fish were distributed among the core study and stop-exposure aquaria at 9 months. Differences in lengths and weights were found at 13 months. The biological significance of this finding is unknown. At 9 months, a single cholangiocarcinoma occurred in a 40 mg/L male. Hepatocellular adenomas occurred in two 20 mg/L males and in one 40 mg/L female. In the core study, one cholangioma occurred in a 20 mg/L male, and cholangiocarcinomas were seen in a few exposed males, but none occurred in control males. 1,2,3-TRICHLOROPROPANE - 16-MONTH STUDY IN GUPPIES: The survival of exposed guppies was less than that of the control group at 9 months. Reduced survival was evident at 6 months in the 18.0 mg/L groups and at 7 months in the 4.5 and 9.0 mg/L groups. Survival was significantly reduced in the 18.0 mg/L core study group within 1 month of the 9-month interim evaluation, and mortality in this group was 42.6% between 9 months and study termination. Nominal exposure concentrations of 4.5, 9.0, and 18.0 mg/L resulted in actual exposure concentrations of 4.4, 8.8, and 18.2 mg/L 1,2,3-trichloropropane, respectively. Guppies in the 18.0 mg/L core study group were significantly longer and weighed more than the controls. Fish in the 18.0 mg/L stop-exposure group also weighed more than the controls. Mortality of fish during the study resulted in unequal numbers of individuals distributed to core study and stop-exposure aquaria at 9 months. This appears to have influenced the length and weight of fish measured at study termination (i.e., the smaller tank population allowed the fish to grow more). Observed differences in weight and length between controls and 18.0 mg/L fish was most likely an artifact of the reduced numbers of fish in the 18.0 mg/L aquaria. At 9 months, multiple hepatocellular adenomas occurred in one 4.5 mg/L male, and one hepatocellular adenoma occurred in a control male. In the core study, increased incidences of cholangiocellular (bile duct) and hepatocellular neoplasms occurred in exposed groups of males and females. Cholangioma and cholangiocarcinoma were seen in several exposed males and females. In the stop-exposure study, increased incidences of hepatocellular neoplasms occurred in 18.0 mg/L males and increased incidences of cholangiocellular (bile duct) neoplasms occurred in 18.0 mg/L females. (ABSTRACT TRUNCATED)

Protective effect of diphenyl diselenide on acute liver damage induced by 2-nitropropane in rats

The effect of diphenyl diselenide, (PhSe)2, administration on 2-nitropropane (2-NP)-induced hepatic damage was examined in male rats. Rats were pre-treated with a single dose of diphenyl diselenide (10, 50 or 100 micromol/kg). Afterward, they received only one dose of 2-NP (100 mg/kg body weight dissolved in olive oil). The parameters that indicate tissue damage such as plasma alanine aminotransferase (ALT), aspartate aminotransferase (AST), gamma-glutamyl transferase (GGT), alpha-fetoprotein (AFP), creatinine and urea were determined. Since toxicity induced by 2-NP is related to oxidative stress, lipid peroxidation was also evaluated. Diphenyl diselenide (100 micromol/kg) significantly reduced plasma ALT, gamma-GGT, AFP levels when compared to 2-NP group. Treatment with diphenyl diselenide, at all doses, effectively protects the increase of lipid peroxidation when compared to 2-NP group. Histological examination revealed that 2-NP treatment causes a moderate swelling and degenerative alterations on hepatocytes and diphenyl diselenide (100 micromol/kg) protects against these alterations. Diphenyl diselenide (50 and 100 micromol/kg) significantly decreased the urea level. This study evidences the protective effect of diphenyl diselenide by 2-NP-induced acute hepatic damage.

Use of the Japanese medaka (Oryzias latipes) and guppy (Poecilia reticulata) in carcinogenesis testing under national toxicology program protocols

A need exists for whole animal toxicity, mutagenesis, and carcinogenesis models that are alternative to the traditional rodent test models and that are economical, sensitive, and scientifically acceptable. Among small fish models, the Japanese medaka (Oryzias latipes) is preeminent for investigating effects of carcinogenic and/or toxic waterborne hazards to humans. The guppy (Poecilia reticulata), although less widely used, is valuable as a comparison species. Both species are easy to maintain and handle in the laboratory and there is a large body of background information on their responsiveness to a range of classes of carcinogens. There are considerable data on the occurrence of background diseases and on spontaneous neoplastic lesions, both of which occur relatively rarely. With few modifications, the medaka and guppy are amenable to carcinogenicity testing under the rigid standards established by the National Toxicology Program (NTP) for rodent tests. The advantages of the small fish in carcinogenesis studies are best realized in long-term studies that involve environmentally realistic exposures. Studies to identify chronic effects can be conducted in about 12 months, near the life span of medaka in our laboratory. Practically, 9-month studies are optimal but shorter study cycles and a variety of exposure/growout and initiation/promotion scenarios are available. Studies on 3 compounds tested in medaka under NTP protocols are under review and preliminary analysis indicates that chronic carcinogenicity bioassays with medaka, guppy, and potentially with other small fish species are feasible and scientifically valid.

OGG1 mRNA expression and incision activity in rats are higher in foetal tissue than in adult liver tissue while 8-oxo-2'-deoxyguanosine levels are unchanged

This study was set up to investigate the relationships between the formation and removal of DNA damage in form of 8-oxodeoxyguanosine (8-oxodG) in neonatal (day 16 of gestation) as compared to adult rats. The hypothesis addressed was whether the rapidly dividing foetal tissue has an enhanced requirement of DNA repair providing protection against potentially mutagenic DNA damages such as 8-oxodG. The activity of the primary 8-oxodG-repair protein OGG1 was measured by a DNA incision assay and the expression of OGG1 mRNA was measured by Real-Time PCR normalised to 18S rRNA. The tissue level of 8-oxodG was measured by HPLC-ECD. We found a 2-3-fold increased incision activity in the foetal control tissue, together with a 3-15-fold increase in mRNA of OGG1 as compared to liver tissue from adult rats. The levels of 8-oxodG in the foetal tissue were unaltered as compared to the adult groups. To increase the levels of 8-oxodG, the rats received an injection (i.p.) of the hepatotoxin 2-nitropropane. The compound induced significant levels of 8-oxodG in male rat livers 5h after the injection and in the foetuses 24h after the injection, while the female rats showed no increase in 8-oxodG. The incision activity was slightly depressed in both male and female liver tissue and in the foetal tissue 5h after the injection, but significantly increased from 5 to 24h after the injection. However, it did not reach levels significantly above the control levels. In conclusion, this study confirms that foetal tissue has increased levels of OGG1 mRNA and correspondingly an enhanced incision activity on an 8-oxodG substrate in a crude tissue extract.

Evaluation of carcinogenic responses in the Eker rat following short-term exposure to selected nephrotoxins and carcinogens

This study examined the response of the Eker rat to nephrotoxic compounds and to genotoxic nonrenal carcinogens. Groups of male Eker rats received either no treatment; a vehicle treatment; treatment with a noncarcinogenic nephrotoxin (aluminum nitrilotriacetate, 2 mg/kg/day of aluminum, intraperitoneally, 3 days per week or cyclosporine A, 30 mg/kg/day, orally by gavage, 7 days/week); or treatment with a genotoxic nonrenal carcinogen (furan, 8 mg/kg/day, orally by gavage, 5 days/week or 2,4-diaminotoluene, 6.5 mg/kg/day, orally by gavage, 7 days/week or 2-nitropropane, 89 mg/kg/day, orally by gavage, 3 days/week). Duration of treatment was 4 and/or 6 months. Tissues from the Eker rats were evaluated microscopically and numbers of proliferative renal lesions were counted. Administration of nephrotoxic compounds (Al-NTA and cyclosporine) significantly increased the number of preneoplastic and neoplastic renal lesions in the Eker rat compared to concurrent vehicle controls. The genotoxic nonrenal carcinogens had no consistent effect on numbers of preneoplastic or neoplastic renal lesions and did not produce neoplasms in the expected target organ (liver).

Evaluation of the TOPKAT system for predicting the carcinogenicity of chemicals

The TOPKAT computer-based system for predicting chemical carcinogens was evaluated by determining its ability to predict the carcinogenicity of chemicals tested by the National Toxicology Program. TOPKAT was not effective in identifying potential rodent carcinogens and noncarcinogens in the data set analyzed. The chemicals in the TOPKAT database of known carcinogens and noncarcinogens that the software identifies as most "similar" to unknown chemicals are illustrated using six examples. These "similar" chemicals generally bear no apparent relationship to the chemical of interest with regard to metabolism or potential mechanism of carcinogenicity. Environ. Mol. Mutagen. 37:55-69, 2001 Published 2001 Wiley-Liss, Inc.

Use of rat liver slices for the study of oxidative DNA damage in comparison with isolated rat liver nuclei and HepG2 human hepatoma cells

Tissue slices are a useful biological system for lipid peroxidation studies but their use for DNA damage studies is not well characterized. Hence, the present study investigates DNA damage in rat liver slices, in comparison with isolated rat liver nuclei and HepG2 human hepatoma cells, incubated with ferric nitrilotriacetate (Fe(III)-NTA), bromotrichloromethane (BrCCl(3)), bromobenzene (BrB) or 2-nitropropane (2-NP) at 37 degrees C for 2 hr. DNA damage was measured in slices, cells or nuclei after centrifugation as formation of as 8-hydroxy-2'-deoxyguanosine (8-OH-dGu) and loss of double-stranded (dsDNA) due to strand breakage using a fluorometric analysis of DNA unwinding (FADU). Lipid peroxidation was measured as thiobarbituric acid-reactive substances (TBARS) released into the medium. The results show that in liver slices and isolated nuclei, Fe/NTA (1 mM/4 mM) induced high levels of TBARS but low levels of 8-OH-dGu, whereas the oxidant induced low levels of TBARS and no formation of 8-OH-dGu in HepG2 cells. In all three systems, inclusion of ascorbate caused dose-dependent formation of 8-OH-dGu, and the levels were similar between liver slices and HepG2 cells but were far higher in isolated nuclei. In liver slices the FADU assay was not applicable due to limited solubilization of DNA from the slice, whereas the assay detected significant loss of dsDNA in HepG2 cells and slight loss in isolated nuclei induced by Fe/NTA with or without ascorbate. Liver slices incubated with 1 mm BrCCl(3), BrB or 2-NP had elevated TBARS but had little or no formation of 8-OH-dGu; none of these oxidants induced lipid peroxidation or DNA damage in HepG2 cells. When liver slices obtained from rats injected with diethylmaleate (to deplete GSH) were incubated with BrCCl(3), BrB or 2-NP, levels of TBARS and 8-OH-dGu increased markedly. Similarly, HepG2 cells with decreased GSH showed marked elevation of TBARS and loss of dsDNA induced by these oxidants, although no formation of 8-OH-dGu was detected. The present study demonstrates the usefulness and limitations of liver slices for DNA damage studies and the importance of cellular GSH in the protection of DNA against environmental toxicants.

Analysis of nitrite/nitrate in biological fluids: denitrification of 2-nitropropane in F344 rats

2-Nitropropane (2-NP), a rat hepatocarcinogen, is denitrified to nitrite and acetone by rat liver microsomes; the denitrification rate is increased using microsomes from phenobarbital (PB)-pretreated rats. To obtain evidence that denitrification of 2-NP also occurs in vivo, we attempted to determine nitrite and nitrate levels in blood sera and urines of 2-NP-treated (1.5 mmol/kg, ip, once) rats with and without PB pretreatment (80 mg/kg, ip, once daily, 3 days), using enzymatic reduction followed by the standard Griess reaction. However, due to various interfering factors, including pigment from methemoglobinemia, we found the assay had to be modified as follows: (a) reduction of nitrate to nitrite was accomplished using NADPH and nitrate reductase, (b) excess NADPH, proteins, and interfering pigments were precipitated using zinc acetate and Na(2)CO(3), and (c) the Griess reagents were prepared in 3 N HCl rather than 5% H(3)PO(4). With these modifications it became possible to show that 2-NP is indeed metabolized to nitrite in vivo and that the metabolism is increased by PB pretreatment. Two hours after 2-NP administration, rat blood serum nitrate plus nitrite levels were approximately 1600 microM (PB-pretreated) and 940 microM (vehicle-pretreated controls). The PB-pretreated and control rats, respectively, excreted 250 and 120 micromol nitrate/nitrite in the 24-h urine post 2-NP treatment. The modifications described make the method more specific, reproducible, and more widely applicable.

[Inhibitory effect of green tea infusion of hepatotoxicity]

We first showed a drinking of green tea infusion can inhibit chemically induced possible hepatic tissue damages in animal experiments, although it has been shown that oral administration of green tea extract can inhibit some organ toxicities. In this review, our data are summarized and a possibility of the effectiveness in humans is discussed. Male rats or mice in the series of experiments were given 2% green tea infusion as a drinking water 1 or 2 weeks before the chemical treatment and until the termination. In the study of rats, green tea effectively inhibited the hepatotoxicity induced by a single intraperitoneal injection or by repeated gavage administration of 2-nitropropane, and a single intraperitoneal injection of galactosamine. However, any possible effects were not observed when green tea was given, on the hepatotoxicity by a single or repeated gavage administration of carbon tetrachloride. In the study of mice, green tea inhibited the hepatotoxicity induced by administration of pentachlorophenol in diet. In conclusion, 2% green tea infusion can prevent the hepatotoxicity by at least some chemicals in experimental animals. It is inferred that the amount of green tea taken by animals in this experiment might be equivalent to the daily intake in Japanese general population, by calculation based on the content of epigallocatechin gallate, a major component of green tea, and the species differences between experimental animals and humans, suggesting the preventive effectiveness in humans.

Protective effects of green tea on hepatotoxicity, oxidative DNA damage and cell proliferation in the rat liver induced by repeated oral administration of 2-nitropropane

To evaluate the benefit of green tea in mitigating hazards caused by repeated exposure of 2-nitropropane (2NP), we examined the effects of the tea on toxic indices, oxidative DNA damage and cell proliferation in the liver of 2NP-treated rats. Male Fischer 344 rats were administered, by gastric intubation, a total of six doses of 60 mg/kg 2NP(L), or alternatively two doses of 90 mg/kg and then four doses of 120 mg/kg 2NP(H) during 2 weeks. Green tea infusion was given to the rats as drinking water 1 week before the 2NP treatments and throughout the experiment. Significant elevation of hepatotoxic indices was evident in the 2NP(H)-treated group, such as an increase of serum glutamic-oxaloacetic transaminase (GOT) activity and of hepatic lipid peroxidation, together with a decrease in hepatic glycogen and serum triglyceride, and degenerative changes in the hepatocytes. A dose-related increase was observed in oxidative DNA damage and cell proliferation in the liver. Green tea effectively inhibited all of above changes induced by 2NP treatment, suggesting that tea intake may be effective for preventing the hepatic injuries after chronic exposure to 2NP.

Experimental study of oxidative DNA damage

Animal experiments allow the study of oxidative DNA damage in target organs and the elucidation of dose-response relationships of carcinogenic and other harmful chemicals and conditions as well as the study of interactions of several factors. So far the effects of more than 50 different chemical compounds have been studied in animal experiments mainly in rats and mice, and generally with measurement of 8-oxodG with HPLC-EC. A large number of well-known carcinogens induce 8-oxodG formation in liver and/or kidneys. Moreover several animal studies have shown a close relationship between induction of dative DNA damage and tumour formation. In principle the level of oxidative DNA damage in an organ or cell may be studied by measurement of modified bases in extracted DNA by immunohistochemical visualisation, and from assays of strand breakage before and after treatment with repair enzymes. However, this level is a balance between the rates of damage and repair. Until the repair rates and capacity can be adequately assessed the rate of damage can only be estimated from the urinary excretion of repair products albeit only as an average of the entire body. A number of model compounds have been used to induce oxidative DNA damage in experimental animals. The hepatocarcinogen 2-nitropropane induces up to 10-fold increases in 8-oxodG levels in rat liver DNA. The level of 8-oxodG is also increased in kidneys and bone marrow but not in the testis. By means of 2-nitropropane we have shown correspondence between the increases in 8-oxodG in target organs and the urinary excretion of 8-oxodG and between 8-oxodG formation and the comet assay in bone marrow as well potent preventive effects of extracts of Brussels sprouts. Others have shown similar effects of green tea extracts and its components. Drawbacks of the use of 2-nitropropane as a model for oxidative DNA damage relate particularly to formation of 8-aminoguanine derivatives that may interfere with HPLC-EC assays and have unknown consequences. Other model compounds for induction of oxidative DNA damage, such as ferric nitriloacetate, iron dextran, potassium bromate and paraquat, are less potent and/or more organ specific. Inflammation and activation of an inflammatory response by phorbol esters or E. coli lipopolysaccharide (LPS) induce oxidative DNA damage in many target cells and enhance benzene-induced DNA damage in mouse bone marrow. Experimental studies provide powerful tools to investigate agents inducing and preventing oxidative damage to DNA and its role in carcinogenesis. So far, most animal experiments have concerned 8-oxodG and determination of additional damaged bases should be employed. An ideal animal model for prevention of oxidative DNA damage has yet to he developed.

2-Nitropropane-induced lipid peroxidation: antitoxic effects of melatonin

The degree of lipid peroxidation (LPO) as indicated by the levels of thiobarbituric acid reactive substances, malondialdehyde (MDA) and 4-hydroxyalkenals (4-HDA), and the activity of sorbitol dehydrogenase (SDH) in serum as parameters of hepatotoxicity were studied in rats treated with a single intraperitoneal (i.p.) injection of the hepatocarcinogen 2-nitropropane (2-NP). Since melatonin, the main secretory product of the pineal gland, has been shown to protect against a number of toxic agents, it was given 30 min before 2-NP to test its protective effect against 2-NP toxicity. Significant increases in LPO in liver (P<0.0001), lung (P<0.05) and kidney (P<0.0001) were observed 24 h after 4 mmol/kg 2-NP while serum SDH activity was increased 470-fold. All parameters showed time (0, 4, 8, 24 h) and dose (0, 1, 2, 3, 4 mmol/kg) dependency. The induction of LPO by 2-NP was significantly reduced in lung and kidney when melatonin (2.5, 5 or 10 mg/kg) was given prior to 2-NP administration. The elevation in serum SDH caused by 2-NP was also reduced when melatonin was given. These findings show that 2-NP induces LPO and that pharmacological levels of melatonin can reduce the toxicity of this hepatocarcinogen.

Prevention of oxidative DNA damage in rats by brussels sprouts

The alleged cancer preventive effects of cruciferous vegetables could be related to protection from mutagenic oxidative DNA damage. We have studied the effects of Brussels sprouts, some non-cruciferous vegetables and isolated glucosinolates on spontaneous and induced oxidative DNA damage in terms of 8-oxo-7,8-dihydro-2'-deoxyguanosine (8-oxodG) in groups of 6-8 male Wistar rats. Excess oxidative DNA damage was induced by 2-nitropropane (2-NP 100 mg/kg). Four days oral administration of 3 g of cooked Brussels sprouts homogenate reduced the spontaneous urinary 8-oxodG excretion by 31% (p<0.05) whereas raw sprouts, beans and endive (1:1), isolated indolyl glucosinolates and breakdown products had no significant effect. An aqueous extract of cooked Brussels sprouts (corresponding to 6.7 g vegetable per day for 4 days) decreased the spontaneous 8-oxodG excretion from 92 +/- 12 to 52 +/- 15 pmol/24 h (p<0.05). After 2-NP administration the 8-oxodG excretion was increased to 132 +/- 26 pmol/24 h (p<0.05) whereas pretreatment with the sprouts extract reduced this to 102 +/- 30 pmol/24 h (p<0.05). The spontaneous level of 8-oxodG in nuclear DNA from liver and bone marrow was not significantly affected by the sprouts extract whereas the level decreased by 27% in the kidney (p<0.05). In the liver 2-NP increased the 8-oxodG levels in nuclear DNA 8.7 and 3.8 times (p<0.05) 6 and 24 h after dose, respectively. The sprouts extract reduced this increase by 57% (p<0.05) at 6 h whereas there was no significant effect at 24 h. In the kidneys 2-NP increased the 8-oxodG levels 2.2 and 1.2 times (p<0.05) 6 and 24 h after dose, respectively. Pretreatment with the sprouts extract abolished these increases (p<0.05). Similarly, in the bone marrow the extract protected completely (p<0.05) against a 4.9-fold 2-NP induced increase (p<0.05) in the 8-oxodG level. These findings demonstrate that cooked Brussels sprouts contain bioactive substance(s) with a potential for reducing the physiological as well as oxidative stress induced oxidative DNA damage in rats. This could explain the suggested cancer preventive effect of cruciferous vegetables. The correspondence between the urinary excretion and 8-oxodG levels in 2-NP target organs supports its being the main repair product that reflects the rate of guanine oxidation in DNA.

Sulfotransferase-mediated genotoxicity of propane 2-nitronate in cultured ovine seminal vesicle cells

2-Nitropropane (2-NP) is a well-known genotoxin and carcinogen in rat liver. Several metabolic pathways, particularly cytochrome P450-, peroxidase- and sulfotransferase-dependent ones, have been suggested to lead to the formation of DNA-reactive species from 2-NP. Because rat liver cells express most types of xenobiotic-metabolizing enzymes, the role of specific pathways in the metabolic activation of 2-NP is difficult to assess in these cells. We have therefore investigated the genotoxicity of 2-NP and its anionic form, propane 2-nitronate (P2N), in cultured ovine seminal vesicle (OSV) cells. OSV cells lack cytochrome P450-dependent monooxygenase activity, but express prostaglandin-H-synthase (PHS) and, as we found out, phenol sulfotransferase. The induction of DNA repair synthesis and specific DNA modifications served as indicators for the genotoxicity of 2-NP and P2N. Both forms strongly induced repair, P2N being more active than 2-NP. The secondary nitroalkanes nitrocyclopentane and nitrocyclohexane also induced repair, whereas 1-nitropropane and the reduction product of 2-NP, acetone oxime, did not. P2N also elicited the formation of the characteristic DNA modifications 'DX1' and 8-aminodeoxyguanosine and increased the level of 8-oxodeoxyguanosine residues in the DNA. Pretreatment of OSV cells with indomethacin, an inhibitor of PHS, affected neither the induction of repair nor the formation of the DNA modifications, and P2N was not a reducing substrate for the PHS-peroxidase activity. In contrast, the sulfotransferase inhibitor pentachlorophenol strongly reduced genotoxicity. The results show that cytochrome P450-dependent monooxygenases are not required for the metabolic conversion of secondary nitroalkanes or their nitronates into DNA-damaging products, nor is PHS involved in the metabolic activation. Instead, the data corroborate an essential role of sulfotransferase(s) in the genotoxicity and carcinogenicity of secondary nitroalkanes. Moreover, it is demonstrated for the first time that these compounds can be genotoxic in cells other than hepatocytes or hepatoma cells. This implies that in species other than the rat, organs other than the liver can be targets for the genotoxicity, and possibly carcinogenicity, of secondary nitroalkanes.

Inhibition of 2-nitropropane-induced rat liver DNA and RNA damage by benzyl selenocyanate

We observed that pretreatment of male F344 rats with benzyl selenocyanate, a versatile organoselenium chemopreventive agent in several animal model systems, decreases the levels of DNA and RNA modifications produced in the liver by the hepatocarcinogen 2-nitropropane. To clarify the mechanisms involved, we pretreated male F344 rats with either benzyl selenocyanate, its sulfur analog benzyl thiocyanate, phenobarbital or cobalt protoporphyrin IX; the latter is a depletor of P450. We then determined (1) the ability of liver microsomes to denitrify 2-nitropropane, (2) effects on 2-nitropropane-induced liver DNA and RNA modifications and (3) amount of nitrate excreted in rat urine following administration of the carcinogen. Pretreatment with benzyl selenocyanate or phenobarbital increased the denitrification activity of liver microsomes by 217 and 765%, respectively, increased liver P4502B1 by 31- and 435-fold, respectively, decreased the levels of 2-nitropropane-induced modifications in liver DNA (29-70% and 17-30%, respectively) and RNA (67-85% and 30-50%, respectively), and increased the 24-h urinary excretion of nitrate by 157 and 209%, respectively. Pretreatment with benzyl thiocyanate had no significant effect on any of these parameters. Pretreatment with cobalt protoporphyrin IX decreased liver P4502B 1 by 87%, decreased the denitrification activity of liver microsomes by 76%, decreased the 24 h urinary excretion of nitrate by 88.5%, but increased the extent of 2-nitropropane-induced liver nucleic acid modifications by 17-67%. These results indicate that the metabolic sequence from 2-nitropropane to the reactive species causing DNA and RNA modifications does not involve the removal of the nitro group. Moreover, they suggest that benzyl selenocyanate inhibits 2-NP-induced liver nucleic acid modifications in part by increasing its detoxication through induction of denitrification, although it is evident that other mechanisms must also be involved.

Denitrification of the genotoxicant 2-nitropropane: relationship to its mechanism of toxicity

1. The stabilities of the industrial chemical and constituent of cigarette smoke 2-nitropropane (2-NP) and its aci tautomer propane 2-nitronate (P2N) towards hepatic enzymes and proteins such as serum proteins and oxyhaemoglobin were investigated in vitro in biological (hepatocytes and subcellular liver fractions) and model systems (serum proteins, oxyhaemoglobin, methylene blue). 2. Denitrification of 2-NP, P2N and 2-deutero 2-nitropropane (2H-NP) occurred in murine hepatocytes significantly faster than in rat cells. For 2-NP the rates were 1271 +/- 167 versus 820 +/- 125 pmol nitrite x min-1 x 10(6) cells-1. 3. A similar observation was made in microsomes, where 2-NP denitrification was 1460 +/- 110 (mouse) versus 480 +/- 80 pmol nitrite x min-1 x mg protein-1 (rat). 4. The major NO2(-)-forming activity was found to be localized in the microsomal fraction. 5. Conversion of 2-NP into P2N, either chemically or enzymatically, was a prerequisite for rapid denitrification. 6. Serum proteins and oxyhaemoglobin proved to be capable of denitrifying P2N (198 +/- 24 pmol nitrite x min-1 x mg protein-1 and 7.1 +/- 1.0 nmol nitrite x min-1 x nmol HbO2(-1) respectively), but were much less active towards 2-NP (24 +/- 2 pmol nitrite x min-1 x mg protein-1 and none respectively). 7. Methylene blue decomposed 2-NP and P2N at rates of 11 +/- 3 and 192 +/- 4 pmol nitrite x min-1 x nmol, methylene blue-1 respectively. The dye also enhanced NO2- formation from P2N and 2-NP in the presence of hepatocytes or serum proteins, with a concomitant enhancement of both 2-NP and P2N toxicity. 8. The results presented report species differences in the denitrification rate of 2-NP and highlight the crucial nitro-aci tautomerism of 2-NP as a pivotal determinant of 2-NP toxicity.

2-Nitropropane-induced DNA damage in rat bone marrow

DNA damage detected by the comet assay (single cell gel electrophoresis) and 8-oxo-7,8-dihydro-2'-deoxyguanosine (8-oxodG) formation in DNA in the bone marrow has been studied in groups of 6 male Wistar rats treated with a single i.p. injection of the carcinogen 2-nitropropane (2-NP, 100 mg/kg body weight) or vehicle. Twenty-four hours after 2-NP the average tail length in the comet assay in bone marrow cells was increased from 1.46 +/- 0.27 to 9.61 +/- 1.56 microm (mean /- SD, p < 0.01), and 8-oxodG levels in the DNA were increased from 1.04 +/- 0.50 to 5.14 +/- 2.42 per 10(5) dG (p < 0.01). There was a close correlation between the comet tail length and the 8-oxodG level (r = 0.89, p < 0.05). The results indicate that 2-NP inflicts DNA damage in the bone marrow cells and thus could be leukemogenic.

DNA-protein cross-links produced by various chemicals in cultured human lymphoma cells

Chemicals such as cis-platinum, formaldehyde, chromate, copper, and certain arsenic compounds have been shown to produce DNA-protein cross-links in human in vitro cell systems at high doses, such as those in the cytotoxic range. Thus far there have only been a limited number of other chemicals evaluated for their ability to produce cross-links. The purpose of the work described here was to evaluate whether select industrial chemicals can form DNA-protein cross-links in human cells in vitro. We evaluated acetaldehyde, acrolein, diepoxybutane, paraformaldehyde, 2-furaldehyde, propionaldehyde, chloroacetaldehyde, sodium arsenite, and a deodorant tablet [Mega Blue; hazardous component listed as tris(hydroxymethyl)nitromethane]. Short- and long-term cytotoxicity was evaluated and used to select appropriate doses for in vitro testing. DNA-protein cross-linking was evaluated at no fewer than three doses and two cell lysate washing temperatures (45 and 65 degrees C) in Epstein-Barr virus (EBV) human Burkitt's lymphoma cells. The two washing temperatures were used to assess the heat stability of the DNA-protein cross-link, 2-Furaldehyde, acetaldehyde, and propionaldehyde produced statistically significant increases in DNA-protein cross-links at washing temperatures of 45 degrees C, but not 65 degrees C, and at or above concentrations of 5, 17.5, and 75 mM, respectively. Acrolein, diepoxybutane, paraformaldehyde, and Mega Blue produced statistically significant increases in DNA-protein cross-links washed at 45 and 65 degrees C at or above concentrations of 0.15 mM, 12.5 mM, 0.003%, and 0.1%, respectively. Sodium arsenite and chloroacetaldehyde did not produce significantly increased DNA-protein cross-links at either temperature nor at any dose tested. Excluding paraformaldehyde and 2-furaldehyde treatments, significant increases in DNA-protein cross-links were observed only at doses that resulted in complete cell death within 4 d following dosing. This work demonstrates that DNA-protein cross-links can be formed in vitro following exposure to a variety of industrial compounds and that most cross-links are formed at cytotoxic concentrations.

Chronic inhalation exposure of rats to nitromethane

Male and female Long-Evans rats were housed in inhalation chambers and exposed to vapors of nitromethane (NM) at either 100 or 200 ppm. The animals were exposed 7 hr per day, 5 days per week for 2 years. Control groups of rats were also housed in a similar inhalation chamber, but NM was not introduced into the chamber. The animals were observed daily for signs of pharmacologic or toxicologic effect and body weights were recorded periodically. At the 2-year termination of the exposure period, clinical laboratory examinations (serum chemistry and hematology) were performed on selected animals and all surviving animals were sacrificed. All animals were necropsied and subjected to a thorough histopathologic examination. During the study there were no pharmacologic effects from exposure to NM at either 100 or 200 ppm. There was no effect on mortality on either sex at either exposure level. Body weights of male rats exposed to NM were not significantly different from those of control rats, but the body weights of female rats of both exposure groups were slightly less than their controls. There was no effect of exposure of rats of either sex to either level of NM on hematology. There were no clinically significant effects on serum chemistry. There were no effects of exposure to NM on organ weights. There were no significant differences in the nonneoplastic or neoplastic pathology related to exposure to NM.

Catalysis of nitro-aci tautomerism of the genotoxicant 2-nitropropane by cytosol from rodent and human liver

2-Nitropropane (2-NP) is a genotoxicant and hepatocarcinogen in rodents. Conversion to propane 2-nitronate (P2N), the anion of the tautomeric aci form of 2-NP, seems to be a pivotal part of the mechanism by which 2-NP causes its toxicity. We tested the hypothesis that the tautomeric equilibrium is influenced by enzymes in the liver, the target organ of 2-NP toxicity. Rat or mouse hepatocytes were incubated with 2-NP, P2N or the 2-NP isotopomer 2-deutero 2-nitropropane (2H-2-NP), which equilibrates with P2N much more slowly than 2-NP. Tautomers were analyzed by HPLC. The rates of conversion of 2-NP to P2N expressed as nmol P2N x (10(6) cells/ml)-1 x min-1 were 4.0 and 4.2 in the presence of hepatocytes from rats or mice, respectively, and 2.6 in the absence of cells. Production of 2-NP to P2N expressed as nmol 2-NP x (10(6) cells/ml)-1 x min-1 was increased from 6.1 in the absence of cells to 11.9 or 9.9 in the presence of hepatocytes from rats or mice, respectively. The rate of formation of P2N from 2H-2-NP as compared to 2-NP was characterised by a primary isotope effect of 3.4 and 3.8 in hepatocytes from rats and mice, respectively, contrasting with a value of 9.6 measured in medium omitting cells. When 2-NP was incubated with subfractions of rodent or human liver homogenate, production of P2N by cytosol was between 7.3 (mouse liver) and 28.1 times (human liver) higher than that observed in microsomes. Similarly generation of 2-NP from P2N by cytosol exceeded that in microsomes by a factor of two. Tautomerism in heat-activated cytosol, mitochondria or microsomes was not different from that in buffer only. The results suggest that the nitro-aci tautomerism of secondary nitroalkanes is catalysed by a hepatic enzyme which resides predominantly in the cytosol and may thus contribute to the generation of the toxic species via which 2-NP exerts its toxicity.

Preventive effects of green tea against liver oxidative DNA damage and hepatotoxicity in rats treated with 2-nitropropane

Male rats were given 2% green tea as their drinking water for 2 wk before a single ip injection of the carcinogen 2-nitropropane (2NP) (100 mg/kg body weight) and liver nuclear 8-hydroxydeoxyguanosine (8-OHdG) levels and hepatotoxicity parameters were determined 6 or 15 hr thereafter. The increase of 8-OHdG adducts in liver nuclear DNA caused by 2NP was depressed 50% at both time points with the green tea pretreatment. The time-dependent elevations of serum aminotransferases and lactate dehydrogenase values by 2NP were also effectively prevented. However, green tea had no obvious effects on the falls in serum lipid peroxide and triglyceride levels associated with carcinogen exposure. Increases of hepatic lipid peroxide levels with 2NP were depressed 100 and 30%, at 6 and 15 hr, respectively, by green tea and the decrease in hepatic glycogen content at 6 hr was clearly alleviated. Histopathological examination revealed effective protection against induction of hepatic degenerative changes by 2NP at 15 hr. Drinking crude catechin extract solution with the same concentration of (-)epigallocatechin gallate as green tea provided protection at 6 hr, but with only half the effectiveness. These findings demonstrate that green tea can effectively block oxidative DNA damage to the liver as well as hepatotoxicity in rats treated with 2NP.

Secondary nitroalkanes: induction of DNA repair in rat hepatocytes, activation by aryl sulfotransferase and hepatocarcinogenicity of 2-nitrobutane and 3-nitropentane in male F344 rats

The secondary nitroalkanes, 2-nitropropane, 2-nitrobutane, 3-nitropentane, 2-nitroheptane, nitrocyclopentane and nitrocyclohexane, as well as the primary nitroalkanes, 1-nitropropane, 1-nitrobutane, 1-nitropentane and 1-nitroheptane, were examined for their ability to induce DNA repair in rat hepatocytes and to serve as substrates for activation by partially purified rat liver aryl sulfotransferase in vitro. All of the secondary, but none of the primary nitroalkanes examined, induced significant DNA repair in rat hepatocytes. Also, the nitronates of all of the secondary nitroalkanes, but none of the primary nitroalkanes, served as substrates for the aryl sulfotransferase-catalysed production of 8-aminoguanosine and 8-oxoguanosine from guanosine in vitro. In a carcinogenicity assay using male F344 rats, the secondary nitroalkanes, 2-nitrobutane and 3-nitropentane, produced a highly significant incidence of hepatocarcinoma with metastases to the lungs, whereas the primary nitroalkane, 1-nitrobutane, was not carcinogenic. While a low incidence of hepatocarcinoma was also produced by cyclopentanone oxime, the results were not statistically significant. Since the secondary nitroalkane, 2-nitropropane, in contrast to the primary nitroalkane, 1-nitropropane, was also previously shown to be hepatocarcinogenic in rats, it is probable that secondary nitroalkanes constitute a hitherto unrecognized class of chemical carcinogens.

Changes in the urinary excretion level of 8-hydroxyguanine by exposure to reactive oxygen-generating substances

A simple means of measuring of 8-hydroxyguanine (8-OHGua) levels in urine was developed. Rat and human urine samples were purified by means of strong cation exchange chromatography (Amberlite CG-120), followed by cellulose partition chromatography (Whatman CF-11). Thereafter, 8-OHGua was determined by means of high performance liquid chromatography (HPLC) using an electro-chemical detector. The level of 8-OHGua in rat urine increased by a factor of 2 to 4 after an intraperitoneal administration of 2-nitropropane (25 mg/kg), paraquat (11.3 mg/kg), or hydroquinone (11 mg/kg). On the other hand, the urine of smokers and persons exposed to air polluted with car exhaust also contained 1.9 and 3.8 fold more 8-OHGua, respectively, than that of control nonsmokers. These results indicated that the amount of 8-OHGua in urine is useful marker for monitoring the level of in vivo oxidative stress.

Induction of gamma GT- and GST-P positive foci in the liver of rats treated with 2-nitropropane or propane 2-nitronate

2-Nitropropane (2-NP) or its anionic form propane 2-nitronate (P2-N) were tested as initiators in a sequential model of rat hepatocarcinogenesis, at the end of which preneoplastic foci were histologically detected. Six intraperitoneal (i.p.) injections of 25, 50 or 100 mg 2-NP or P2-N/kg body weight resulted in the appearance of liver gamma-glutamyltranspeptidase (gamma GT)- and glutathione S-transferase (GST-P)-positive foci, whose number and size increased with the dose of initiator. 2-NP and P2-N were equally effective. The potency of the highest dose (6 x 100 mg/kg body wt) was comparable to that of a single injection of diethylnitrosamine (100 or 200 mg/kg body wt). This work provides a short-term (70 days) and convenient model for further studies on 2-NP carcinogenicity.

Propane 2-nitronate is the major genotoxic form of 2-nitropropane

The mutagenicity of 2-nitropropane in Salmonella typhimurium (strain TA100) was proportional to the pH (range 6.1-9.1) of the medium used for pre-incubation of the agent and for incubation of the agent with the Salmonella. The mutagenicity correlated with an enhanced rate of tautomerase to propane 2-nitronate at relatively high pH as measured by high performance liquid chromatography. Both the mutagenicity in Salmonella typhimurium (strains TA100 and TA102) and the rate of tautomerisation to the nitronate was lower with 2-deutero-2-nitropropane than with non-deuterated 2-nitropropane. Furthermore, 2-deutero-2-nitropropane was less potent in the induction of unscheduled DNA synthesis in rat hepatocytes over a 4-h period. Propane 2-nitronate therefore appears to be pivotal in the causation of the genetic toxicity of 2-nitropropane. The presence of hepatocytes enhanced nitronate production from 2-nitropropane suggesting a contribution from hepatic enzymes in the tautomerisation reaction.

2-Nitropropane-induced liver DNA and RNA base modifications: differences between Sprague-Dawley rats and New Zealand white rabbits

2-Nitropropane (2-NP), a hepatocarcinogen in male Sprague-Dawley rats but not, under the same conditions, in male New Zealand White rabbits, induces characteristic base modifications in rat liver DNA and RNA including increases in 8-oxoguanine and the formation of 8-aminoguanine. We compared the levels of these modifications in the two animal species at 6, 18 and 42 h after a single i.p. treatment with 1.12 mmol/kg 2-NP. Significantly less nucleic acid base modifications were found to be produced in rabbit liver than in rat liver. Thus, the relative resistance of the rabbit to the hepatocarcinogenicity of 2-NP correlates with decreased levels of 2-NP-induced liver DNA and RNA base damage.

DNA modification and repair by 2-nitropropane is extensive in hepatocytes of rats compared to those of humans and mice

Hepatocytes from rats, mice or humans were exposed to either 2-nitropropane or propane 2-nitronate and the extent of unscheduled DNA synthesis (UDS) was measured. At a concentration of 2-nitropropane (0.1 mM) that produced a marked induction of UDS in rat hepatocytes, a negative or minimal response was seen in hepatocytes from mice and humans. A 10-fold higher concentration of 2-nitropropane was required in mouse hepatocytes for an equivalent UDS response to that seen in rat-liver cells. All three species showed UDS after exposure of hepatocytes to propane 2-nitronate at 0.1 mM although the effect in human cells was variable. In rat hepatocytes the induction of UDS by 2-nitropropane was not inhibited by the antioxidant dimethyl sulphoxide (1%). In these cells, 2-nitropropane produced an electrochemically active modified deoxynucleoside, similar to that reported to be formed in livers of rats which had received 2-nitropropane in vivo. A smaller but significant production of this altered deoxynucleoside was found in mouse hepatocytes but not in human hepatocytes treated identically. The level of 8-oxo-7,8-dihydrode-oxyguanosine was not increased in hepatocytes from any of the three species exposed to 2-NP under the same conditions. It is suggested that the UDS caused by 2-nitropropane may be in response to damage other than that produced by oxygen radicals.

8-Aminoguanine: a base modification produced in rat liver nucleic acids by the hepatocarcinogen 2-nitropropane

2-Nitropropane (2-NP), an important industrial chemical and a hepatocarcinogen in rats, had previously been found to produce several modifications of nucleosides in rat liver RNA and DNA that are discernible using HPLC with electrochemical detection. While one of these modifications has been identified as an increase in the levels of 8-oxoguanosine and 8-oxo-2'-deoxyguanosine in RNA and DNA, respectively, the others had not been identified. We now present evidence that a major modification in rat liver nucleic acids due to the administration of 2-NP is the amination of guanine at C8, apparently a completely novel in vivo reaction. 8-Aminoguanosine, isolated from hydrolysates of liver RNA from 2-NP-treated rats, cochromatographed with synthetic or commercially-obtained standard on reverse-phase as well as cation-exchange HPLC, and its UV spectral characteristics at acidic, neutral, and basic pH were identical to those of the standard. Acid hydrolysis produced 8-aminoguanine, which had a retention time and fragmentation pattern identical to that of the standard on gas chromatography-mass spectrometry of the trimethylsilyl derivatives. Evidence for the presence of 8-aminodeoxyguanosine in liver DNA of rats treated with 2-NP was also obtained by cochromatography with synthetic standard on HPLC. Hydroxylamine-O-sulfonic acid was found to react with RNA and DNA to give 8-oxo- and 8-amino-substituted guanines. We propose, as a working hypothesis, that 2-NP may be metabolized to hydroxylamine-O-sulfonate or acetate, which yield the reactive nitrenium ion, NH2+, capable of aminating cellular macromolecules in vivo.

Radical intermediates during the oxidation of nitropropanes. The formation of NO2 from 2-nitropropane, its reactivity with nucleosides, and implications for the genotoxicity of 2-nitropropane

The chemistry of the nonenzymatic oxidation of the rat liver carcinogen, 2-nitropropane, and its anionic form, propane-2-nitronate, was investigated using pulse radiolysis and EPR/spin trapping with 3,5-dibromo-4-nitrosobenzenesulfonic acid as the trapping agent. The results suggest that, following initial oxidation to a secondary alkyl radical, propane-2-nitronate is effectively degraded in a peroxidative chain reaction with the intermediary formation of peroxyl and NO2.radicals. The latter radical was shown to react appreciably fast with ribonucleosides, deoxyribonucleosides, and guanosine nucleotides. It is proposed that nonenzymatic formation of NO2.radicals after enzymatic oxidation of propane-2-nitronate to the corresponding secondary alkyl radical accounts for the induction of DNA damage observed after exposure of rats to 2-nitropropane.

Propane 2-nitronate is more rapidly denitrified and is more genotoxic than 2-nitropropane in cultured rat hepatoma cells

We have investigated the importance of nitronate formation from 2-nitropropane (2-NP) for the oxidative metabolism and the genotoxicity of 2-NP in 2sFou rat hepatoma cells. Treatment of the cells with 2-NP for up to 3 h resulted in the time-dependent appearance of nitrite in the culture medium and in a weak induction of DNA repair synthesis. Both nitrite formation and repair induction were markedly enhanced in cells exposed to the anionic form of 2-NP, propane 2-nitronate. These observations suggest that propane 2-nitronate, rather than 2-NP itself, is oxidized by the liver cells to yield a DNA-damaging product. The results also indicate that the nitro/nitronate equilibration in intact liver cells is slow, suggesting that nitronate formation represents the rate-limiting step in the metabolic activation of 2-NP.

Evaluation of secondary nitroalkanes, their nitronates, primary nitroalkanes, nitrocarbinols, and other aliphatic nitro compounds in the Ames Salmonella assay

The secondary nitroalkanes 2-nitropropane, 2-nitrobutane, 3-nitropentane and nitrocyclopentane, as well as their anionic forms (nitronates); the primary nitroalkanes 1-nitropropane, 1-nitrobutane, and 1-nitropentane and their respective nitronates; the nitrocarbinols 2-nitro-1-propanol, 2-nitro-1-butanol, 3-nitro-2-butanol, and 3-nitro-2-pentanol and their respective nitronates; 2-methyl-2-nitropropane, and 2-nitroso-2-nitropropane were tested in the Ames Salmonella assay using strains TA98, TA100 and TA102. Nitronates of the secondary nitroalkanes 2-nitropropane, 2-nitrobutane, 3-nitropentane, and nitrocyclopentane were significantly mutagenic in Salmonella strains TA100 and TA102 at 10-80 mumoles/plate, but the parent compounds were mutagenic at only a single dose level or were not mutagenic at all in the same dose range. The primary nitroalkanes and the nitrocarbinols were not mutagenic, or only marginally so, at the concentrations tested. The nitronates of the primary nitroalkanes and the nitrocarbinols reprotonated too rapidly under the conditions of the assay for adequate evaluation of mutagenicity. 2-Methyl-2-nitropropane was not mutagenic in strains TA100 and TA102; 2-nitroso-2-nitropropane was also not mutagenic in strains TA100 and TA102, but induced an equivocal mutagenic response in TA98. The positive Salmonella mutation data for the nitronates of the secondary nitroalkanes studied correlate very well with the very slow rate of reprotonation of secondary nitroalkane nitronates at pH 7.7 (Conaway et al. (1991) Cancer Res., 51, 3143), and provide further evidence that nitronates of secondary nitroalkanes, rather than the neutral parent forms with which they may be in equilibrium, are the more proximate mutagenic species.

DNA fragmentation by 2-nitropropane in rat tissues, and effects of the modulation of biotransformation processes

The occurrence and persistence of DNA fragmentation, as detected by the alkaline elution technique, have been studied in rats treated with single oral doses of the hepatocarcinogen 2-nitropropane (2-NP). A progressive increase of liver DNA fragmentation was observed at doses ranging from 0.5 to 8 mmol/kg; single strand breaks reached the maximum frequency 6 h after administration, and were partially reduced after 36 h. In contrast, DNA fragmentation was absent in lung, kidney, bone marrow and brain of rats given 8 mmol/kg. The role of cytochrome P-450 in the activation of 2-NP is indicated by the increase of liver DNA damage in rats pretreated with phenobarbital or beta-naphtoflavone, and by its reduction produced by methoxsalen. Both administration of GSH and GSH depletion did not result in clearcut modifications of the genotoxic effect of 2-NP for the liver.

Nitroreduction is not involved in the genotoxicity of 2-nitropropane in cultured mammalian cells

We have investigated the importance of nitroreduction for the genotoxicity of the carcinogen 2-nitropropane (2-NP) in primary cultures of rat hepatocytes and in V79 Chinese hamster cells. Induction of DNA repair synthesis was used as an indicator of genotoxic effects in hepatocytes. Genotoxicity in V79 cells was determined as induction of DNA repair, micronuclei and mutations to 6-thioguanine (TG) resistance. Both hepatocytes and V79 cells were found capable of reducing and oxidizing 2-NP. Reduction of 2-NP was indicated by the formation of acetone oxime, the tautomeric form of 2-nitrosopropane, the first reduction product of 2-NP. Oxidation of 2-NP was indicated by the production of acetone and nitrite. 2-NP strongly elicited repair in hepatocytes, but acetone oxime and the products of a possible further nitroreduction, isopropyl hydroxylamine (IPHA) and 2-aminopropane did not. None of the reduction products caused repair synthesis in V79 cells. However, in these cells IPHA and 2-NP increased the frequency of TG-resistant mutants. IPHA also markedly induced micronuclei. This was not seen with 2-NP. Acetone oxime was not genotoxic in V79 cells. The observations suggest that reduced metabolites are responsible neither for the induction of DNA repair synthesis by 2-NP in hepatocytes nor for the induction of gene mutations by 2-NP in V79 cells.

Investigation of the chemical basis of nitroalkane toxicity: tautomerism and decomposition of propane 1- and 2-nitronate under physiological conditions

Unlike primary nitroalkanes, such as 1-nitropropane, the secondary nitroalkane 2-nitropropane is geno- and hepatotoxic. Nitroalkanes exist in equilibrium with alkane nitronates. In order to investigate the relationship between nitroalkane toxicity and generation and stability of nitronates, propane 1- or 2-nitronate (4-6 mM) were incubated in buffer (pH 3.8 -7.4) in the absence or presence of cysteine. Equilibrium formation and degradation were studied by 1H-NMR spectroscopy and ion pair HPLC chromatography. Propane 1-nitronate generated 1-nitropropane rapidly and almost quantitatively. In the case of propane 2-nitronate equilibrium at pH 7.4 was reached within 8 h, when 48% of initial nitronate had tautomerised to 2-nitropropane. The pKa of the reaction 2-nitropropane less than--greater than propane 2-nitronate measured by HPLC was 7.63. Equilibrium formation, hydrolysis and reduction of nitronates were pH-dependent and, in the case of propane 2-nitronate, yielded mainly acetone, nitrite and acetone oxime, apart from 2-nitropropane. Hydrolysis of propane 2-nitronate (4 mM) to nitrite was modulated by cysteine (4 mM) and p-methoxyphenol (0.4 mM). At pH 7.4 they increased nitrite generation by 300 and 28%, respectively, at pH 4.8 they decreased nitrite formation by 91 and 82%, respectively, probably by scavenging radical intermediates. Differences between nitroalkanes in terms of content of nitronate tautomer at equilibrium are probably an important chemical determinant of their toxic potential.

Sex and organ differences in oxidative DNA and RNA damage due to treatment of Sprague-Dawley rats with acetoxime or 2-nitropropane

The hepatocarcinogens 2-nitropropane and acetoxime have previously been found to induce a specific and qualitatively identical pattern of base damage in rat liver DNA and RNA, including the induction of increased levels of 8-hydroxyguanine. Because both 2-nitropropane and acetoxime are weaker carcinogens in female rats than male rats, we examined the ability of these chemicals to induce this pattern of damage in liver and kidney nucleic acids of male and female Sprague-Dawley rats 6 and 18 h after administration. Significantly lower levels of 8-hydroxydeoxyguanosine, 8-hydroxyguanosine and other presumed modified nucleosides discernible by high-performance liquid chromatography with electrochemical detection were found in liver nucleic acids of female rats at both time points. In addition, minimal alteration of nucleic acids was observed in the kidney, which is not a target organ for the carcinogenicity of either 2-nitropropane (2-NP) or acetoxime (ACO). These results support the hypothesis that the specific DNA alterations observed are relevant to the hepatocarcinogenicity of 2-NP and ACO.

Dose-dependent emergence of preneoplastic foci in rat livers after exposure to 2-nitropropane

Male and female Sprague-Dawley rats, 4-6 days old were exposed for 3 weeks (6 h/day, 5 days/week) to 2-nitropropane vapours of 0, 25, 40, 50, 80 and 125 ppm. One week later polychlorinated biphenyls (Clophen A50, 10 mg/kg body weight) were administered for promotion twice a week for 8 weeks. Thirteen weeks after starting the experiments the logarithms of the numbers of preneoplastic liver foci deficient in adenosine-5'-triphosphatase were found to be linearly related to the exposure concentrations of 2-nitropropane. Male rats exhibited an approximately four times lower foci incidence than females.

Oxidative DNA and RNA damage in rat liver due to acetoxime: similarity to effects of 2-nitropropane

Acetoxime (ACO) and 2-nitropropane (2-NP), both industrially important chemicals and known hepatocarcinogens in rats, induced increased levels of 8-hydroxy-guanine in liver DNA and RNA of male Sprague-Dawley and F344 rats after either oral or i.p. administration. Both compounds also produced qualitatively the same patterns of other apparent modifications of liver DNA and RNA nucleosides, discernible by HPLC with electrochemical detection. Six hours after administration, the effects of 2-NP on liver nucleic acids were more pronounced in F344 rats than in Sprague-Dawley rats, suggesting that 2-NP may prove to be a stronger carcinogen in the F344 strain. The effects of ACO, a weaker carcinogen than 2-NP, were less than those of the nitroalkane in both rat strains. These results suggest that the hepatocarcinogenicity of ACO, like that of 2-NP, may depend on increased generation of reactive oxygen species capable of producing DNA and RNA base damage in rat liver. In addition, the data support the hypothesis that the hepatocarcinogenicity of ACO depends on its partial in vivo N-oxidation to 2-NP.

The reaction of alkylnitronates with glutathione

Nitroalkanes are agents of occupational importance, and 2-nitropropane has been shown to be mutagenic and hepatotoxic. Here the reaction of alkylnitronates, such as propyl-2-nitronate, with glutathione and other thiol nucleophiles has been studied by using TLC, HPLC, and spectroscopic methods. Propyl-2-nitronate, but not 2-nitropropane, reacted with glutathione in acidic media. The reaction yielded an inseparable mixture of oxidized glutathione and a product that was identified as S-nitrosoglutathione. S-Nitrosoglutathione is known to be generated by reaction of nitrous acid with glutathione and furnishes a characteristic UV spectrum, but its NMR and mass spectral properties are described here for the first time. The 1H NMR spectrum of S-nitrosoglutathione showed in principle the resonance signals of glutathione except that the cysteine beta-protons gave two broad signals shifted downfield by 1 ppm as compared to the resonance frequencies of the glutathione cysteine beta-protons. The interpretation of the spectrum was aided by investigation of the properties of S-nitroso-N-acetylcysteine, the product of the reaction of N-acetylcysteine with propyl-2-nitronate. The nitronates of primary nitroalkanes, such as nitromethane, nitroethane, or 1-nitropropane, did not react with glutathione. The reaction between propyl-2-nitronate and glutathione did not occur at pH values greater than 5; therefore, the relevance of these findings to the disposition of propyl-2-nitronate in vivo is unclear.

Genotoxicity of 1- and 2-nitropropane in the rat

2-Nitropropane (2-NP) is a rat liver carcinogen, whilst the 1-isomer is non-carcinogenic in rodents. Although DNA repair tests in the rat liver discriminated clearly between the carcinogenic and the non-carcinogenic isomer, uniformly negative results have been published for the mouse bone marrow micronucleus test (BMMN test) with both isomers. Therefore, the latter assay did not discriminate between the carcinogenic and the non-carcinogenic isomer. To investigate whether this is due to endpoint specificity or organospecificity of 2-NP, studies were carried out in the rat in which micronucleus induction (bone marrow and liver) and unscheduled DNA synthesis (UDS) induction (liver) were measured after oral treatment with either nitropropane isomer. 2-NP induced UDS in the liver whilst the 1-isomer was negative, thus confirming the published studies. In the BMMN test, occasional small increases in the incidence of micronuclei were found for both compounds, but results were interpreted as negative after considering the control background data and the lack of reproducibility. By contrast, the liver micronucleus test revealed a clastogenic effect of 2-NP in the liver. This indicates that 2-NP induces chromosome aberrations as well as DNA repair in vivo, but it seems to act organospecifically. For 1-NP a slightly increased incidence of micronuclei was found in the liver, which was accompanied by a markedly increased mitotic index. It therefore remains questionable as to whether this increased micronucleus frequency for 1-NP is an indicator of a clastogenic effect, or whether it is caused by an increased cell proliferation induced by 1-NP. Consequently, it is too early to conclude whether the liver micronucleus assay is able to discriminate between the carcinogenic and non-carcinogenic isomer. However, the results provide further evidence that bone marrow assays are insufficient for the detection of all genotoxic carcinogens in vivo. This indicates the need for analysing a second tissue, particularly when negative bone marrow results have been obtained with in vitro genotoxins.