Risk assessment of dietary exposures to compounds that are genotoxic and carcinogenic--an overview.

The process of risk assessment of dietary exposures to genotoxic carcinogens is summarised. Exposures to six genotoxic carcinogens in food (acrylamide, aflatoxin B1, benzo(a)pyrene, dimethylnitrosamine, ethyl carbamate, PhIP) have been used to illustrate the process. The margin of exposure (MOE) approach is seen as a useful method to be used in the risk characterisation step of assessing exposures to genotoxic carcinogens. This approach combines information on animal potency and human exposure, and can be used to indicate levels of concern and also the ranking between various exposures to such agents. Both the T25 and the BMDL10 methods may be used as a reference point. Should a specific MOE value be developed as a cut-off between levels of concern and levels of low concern, the value using T25 data is proposed to be 2.5-times higher than using BMDL10 data. Linear low-dose extrapolation using either T25 or BMDL10, may also be applied. However, it should be understood that this approach should not be interpreted as giving a precise estimate of human risk. For exposures to mutagens in food lacking carcinogenicity data, it is proposed to apply the MOE approach to the lowest effective dose (LED) for in vivo genotoxicity.

The scientific basis of tobacco product regulation.

This report presents the conclusions and recommendations of TobReg from its fourth meeting, where the Study Group deliberated on a number of topics in the field of tobacco product regulation and produced the following advisory notes and recommendations: an advisory note on smokeless tobacco products: health effects, implications for harm reduction and research needs; an advisory note on 'fire safer' cigarettes: approaches to reduced ignition propensity; a recommendation on mandated lowering of toxicants in cigarette smoke: tobacco-specific nitrosamines and selected other constituents; and a recommendation on cigarette machine smoking regimens. The four sections of this report address these four issues, and the Study Group's recommendations are set out at the end of each section. Its overall recommendations are summarized in section 5.

Importance of size and composition of particles for effects on cells in vitro.

A primary goal of current research on particle-induced health effects is to reveal the critical characteristics that determine their biological effects. Experimental studies have shown that smaller particles induce stronger biological effects than larger particles of similar composition, due to their larger surface area to mass ratio. However, correlation for variations in surface area could not account for variation in biological reactivity among particles of differential composition. Hence, the importance of size and surface area does not override the importance of particle composition. Moreover, different particle characteristics appear to be involved in different biological effects in vitro. Our studies show that mineral particle-induced apoptosis mostly seems to depend on particle size, whereas composition and surface reactivity appeared to be most important for the proinflammatory potential of the particles. The ability of the particles to generate reactive oxygen species in vitro was not correlated with either inflammatory markers or apoptosis, suggesting that other mechanisms are at play. A single, specific component of the mineral particles, explaining the differences in response, has not been identified. In European-wide studies such as the Respiratory Allergy and Inflammation due to Air Pollution (RAIAP) study, particles have been sampled in different locations to study season- and site-dependent variations in responses particles, such as markers of inflammatory and allergic reactions in cells and animals. The data indicate that coarse particles can induce at least as strong inflammatory responses as fine particles. The allergic responses tended to be more associated with the organic fraction (PAH) of particles, whereas the inflammatory reactions seemed to be more associated with metals and endotoxin. Overall, coarse PM was found to have an inflammatory potential similar to fine PM on an equal mass basis. Even though one has to take into account different concentrations in ambient air as well as differences in respiratory system deposition of the size fractions, the potential of coarse particles to induce pulmonary effects should not be neglected.

Approaches to the risk assessment of genotoxic carcinogens in food: a critical appraisal.

The present paper examines the particular difficulties presented by low levels of food-borne DNA-reactive genotoxic carcinogens, some of which may be difficult to eliminate completely from the diet, and proposes a structured approach for the evaluation of such compounds. While the ALARA approach is widely applicable to all substances in food that are both carcinogenic and genotoxic, it does not take carcinogenic potency into account and, therefore, does not permit prioritisation based on potential risk or concern. In the absence of carcinogenicity dose-response data, an assessment based on comparison with an appropriate threshold of toxicological concern may be possible. When carcinogenicity data from animal bioassays are available, a useful analysis is achieved by the calculation of margins of exposure (MOEs), which can be used to compare animal potency data with human exposure scenarios. Two reference points on the dose-response relationship that can be used for MOE calculation were examined; the T25 value, which is derived from linear extrapolation, and the BMDL10, which is derived from mathematical modelling of the dose-response data. The above approaches were applied to selected food-borne genotoxic carcinogens. The proposed approach is applicable to all substances in food that are DNA-reactive genotoxic carcinogens and enables the formulation of appropriate semi-quantitative advice to risk managers.

Risk assessment of substances that are both genotoxic and carcinogenic report of an International Conference organized by EFSA and WHO with support of ILSI Europe.

The European Food Safety Authority (EFSA) and the World Health Organization (WHO), with the support of the International Life Sciences Institute, European Branch (ILSI Europe), organized an international conference on 16-18 November 2005 to discuss how regulatory and advisory bodies evaluate the potential risks of the presence in food of substances that are both genotoxic and carcinogenic. The objectives of the conference were to discuss the possible approaches for risk assessment of such substances, how the approaches may be interpreted and whether they meet the needs of risk managers. ALARA (as low as reasonably achievable) provides advice based solely on hazard identification and does not take into account either potency or human exposure. The use of quantitative low-dose extrapolation of dose-response data from an animal bioassay raises numerous scientific uncertainties related to the selection of mathematical models and extrapolation down to levels of human exposure. There was consensus that the margin of exposure (MOE) was the preferred approach because it is based on the available animal dose-response data, without extrapolation, and on human exposures. The MOE can be used for prioritisation of risk management actions but the conference recognised that it is difficult to interpret it in terms of health risk.

Developmental pattern of 3-methylcholanthrene-inducible mutagenic activation of N-2-fluorenylacetamide, 2-fluorenamine, and 2,4-diaminoanisole in the rabbit.

The effects of 3-methylcholanthrene (MCA) on mutagenic activation of the carcinogenic arylamines N-2-fluorenylacetamide (FAA), 2-fluorenamine (FA), and 2,4-diaminoanisole (2,4-DAA) by liver homogenates were studied postnatally in Dutch rabbits. These effects were compared with the developmental profiles of cytochrome P448 and aryl hydrocarbon hydroxylase (AHH) activity. Mutagenic activation of FA and 2,4-DAA was increased by MCA as early as 2 days after birth, whereas induction of FAA mutagenicity appeared 6 days after birth. Thereafter, induction of all three arylamines closely paralleled induction of cytochrome P448, which was maintained into adulthood. In contrast, induction of AHH activity by MCA was highest at 2 days of age and decreased to control levels 20 days after birth.

Particulate matter properties and health effects: consistency of epidemiological and toxicological studies.

Identifying the ambient particulate matter (PM) fractions or constituents, critically involved in eliciting adverse health effects, is crucial to the implementation of more cost-efficient abatement strategies to improve air quality. This review focuses on the importance of different particle properties for PM-induced effects, and whether there is consistency in the results from epidemiological and experimental studies. An evident problem for such comparisons is that epidemiological and experimental data on the effects of specific components of ambient PM are limited. Despite this, some conclusions can be drawn. With respect to the importance of the PM size-fractions, experimental and epidemiological studies are somewhat conflicting, but there seems to be a certain consistency in that the coarse fraction (PM10-2.5) has an effect that should not be neglected. Better exposure characterization may improve the consistency between the results from experimental and epidemiological studies, in particular for ultrafine particles. Experimental data indicate that surface area is an important metric, but composition may play an even greater role in eliciting effects. The consistency between epidemiological and experimental findings for specific PM-components appears most convincing for metals, which seem to be important for the development of both pulmonary and cardiovascular disease. Metals may also be involved in PM-induced allergic sensitization, but the epidemiological evidence for this is scarce. Soluble organic compounds appear to be implicated in PM-induced allergy and cancer, but the data from epidemiological studies are insufficient for any conclusions. The present review suggests that there may be a need for improvements in research designs. In particular, there is a need for better exposure assessments in epidemiological investigations, whereas experimental data would benefit from an improved comparability of studies. Combined experimental and epidemiological investigations may also help answer some of the unresolved issues.

Metabolism and activation of 2-acetylaminofluorene in isolated rat hepatocytes.

The metabolism of 2-acetylaminofluorene (AAF) as well as the activation of AAF to covalently bound and mutagenic intermediates were studied in isolated rat hepatocytes. The cell system readily formed oxidized, deacetylated, and conjugated AAF metabolites. Pretreatments of animals with the inducer beta-naphthoflavone led to increases in phenolic and conjugated as well as covalently protein-bound products. Addition of 4-nitrophenol, a substrate for conjugation, increased the levels of free phenols and inhibited the formation of water-soluble metabolites. At the same time, the rates of covalent protein binding were decreased. Formation of 9-hydroxy-2-acetylaminofluorene could also be demonstrated. The pathway leading to this alicyclic hydroxylated AAF metabolite was not induced by prior beta-naphthoflavone treatment, nor was it inhibited by 4-nitrophenol addition. The cells converted AAF as well as aminofluorene and 2,4-diaminoanisole to mutagenic intermediates which were released into the incubation medium. 2-Aminofluorene was considerably more mutagenic than was AAF in this system. Addition of microsomes increased the mutagenicity of AAF, but not that of 2-aminofluorene or 2,4-diaminoanisole, presumably by deacetylation of N-hydroxy-2-acetylaminofluorene to N-hydroxy-2-aminofluorene.

Deacetylation to 2-aminofluorene as a major initial reaction in the microsomal metabolism of 2-acetylaminofluorene to mutagenic products in preparations from rabbit lung and liver.

The rabbit pulmonary and hepatic microsomal pathways for the metabolism of 2-acetylaminofluorene (AAF) and 2-aminofluorene (AF) to mutagenic products were investigated by means of high performance liquid chromatography and the Salmonella mutagenicity assay. Mutagenic activity approached a maximum with increasing concentrations of AAF incubated with hepatic microsomal preparations and Salmonella; with pulmonary microsomal preparations, mutagenic activity was proportional to the concentration of AAF over the range examined. The mutagenic activities of AF exhibited typical saturation kinetics with both hepatic and pulmonary microsomal preparations. Approximately 7 times more AF than N-hydroxy-2-acetylaminofluorene (N-hydroxy-AAF) was formed in incubations of AAF (0.5 mM) with hepatic microsomal preparations. When AAF was incubated with pulmonary microsomal preparations, formation of AF, but not N-hydroxy-AAF, was detected. The inclusion of paraoxon in the pulmonary incubations blocked the formation of AF but did not lead to the recovery of any N-hydroxy-AAF. We conclude that the metabolism of AAF to mutagenic products in pulmonary microsomal preparations from rabbits is initiated primarily, if not entirely, by deacetylation of AAF to AF. The mutagenic activity of AAF with the pulmonary microsomal preparations is limited by the deacetylase activity which, like mutagenic activity, exhibits a linear relationship with the concentration of AAF. On the basis of the rates of formation of AF and N-hydroxy-AAF and their mutagenic activities, we estimate that about 60% of the hepatic metabolism of AAF to mutagenic products is dependent upon deacetylation of AAF and subsequent oxidation of the AF formed.

Human exposure and internal dose assessments of acrylamide in food.

This review provides a framework contributing to the risk assessment of acrylamide in food. It is based on the outcome of the ILSI Europe FOSIE process, a risk assessment framework for chemicals in foods and adds to the overall framework by focusing especially on exposure assessment and internal dose assessment of acrylamide in food. Since the finding that acrylamide is formed in food during heat processing and preparation of food, much effort has been (and still is being) put into understanding its mechanism of formation, on developing analytical methods and determination of levels in food, and on evaluation of its toxicity and potential toxicity and potential human health consequences. Although several exposure estimations have been proposed, a systematic review of key information relevant to exposure assessment is currently lacking. The European and North American branches of the International Life Sciences Institute, ILSI, discussed critical aspects of exposure assessment, parameters influencing the outcome of exposure assessment and summarised data relevant to the acrylamide exposure assessment to aid the risk characterisation process. This paper reviews the data on acrylamide levels in food including its formation and analytical methods, the determination of human consumption patterns, dietary intake of the general population, estimation of maximum intake levels and identification of groups of potentially high intakes. Possible options and consequences of mitigation efforts to reduce exposure are discussed. Furthermore the association of intake levels with biomarkers of exposure and internal dose, considering aspects of bioavailability, is reviewed, and a physiologically-based toxicokinetic (PBTK) model is described that provides a good description of the kinetics of acrylamide in the rat. Each of the sections concludes with a summary of remaining gaps and uncertainties.

Induction of liver microsomal cytochrome P-450 and associated monooxygenases by octachlorostyrene in inbred strains of mice. Lack of correlation with the murine Ah locus.

Single intraperitoneal injections of octachlorostyrene (OCS) and hexachlorobenzene in genetically polycyclic aromatic hydrocarbon "responsive' C57/BL/6 (B6) mice led to a time- and dose-dependent increase in the levels of liver microsomal cytochromes P-450 and b5 as well as in the activities of NADPH cytochrome P-450 (cytochrome c) reductase, ethylmorphine (EM) N-demethylase, 4-nitroanisole (PNA) O-demethylase and acetanilide 4-hydroxylase (AcA hydroxylase). No, or only a very moderate, increase in the activity of aryl hydrocarbon hydroxylase was seen after OCS and HCB, respectively. Pretreatments with phenobarbital (PB) or 3-methylcholanthrene (MC) both increased AcA hydroxylase activity to a similar degree, whereas pretreatment with polychlorinated biphenyls (Aroclor 1254) had an effect equal to the sum of PB and MC. Judged from sodium dodecylsulfate polyacrylamide gel electrophoresis studies, OCS and HCB predominantly increased a microsomal polypeptide of apparent mol. wt 52,000, similar to PB. A reduced response was seen after OCS or HCB treatment of aromatic hydrocarbon "non-responsive' DBA/2 (D2) mice compared to B6 mice, both with respect to AcA hydroxylase as well as EM demethylase and PNA demethylase activities. OCS treatment of B6D2F1 mice resulted in a doubling of AcA hydroxylase activity, but in mice of the (B6D2)D2 backcross no distinct subgrouping of individual AcA hydroxylase activities were apparent. These results demonstrate that OCS is an inducer of the PB-type in mice and that induction of AcA hydroxylase by OCS is not regulated by the Ah locus.

Cytotoxic effects of N-acetyl-p-benzoquinone imine, a common arylating intermediate of paracetamol and N-hydroxyparacetamol.

The cytotoxic effects of N-acetyl-p-benzoquinone imine (NAPQI), a postulated ultimate reactive metabolite of paracetamol (pHAA), was studied in suspensions of isolated rat hepatocytes. Incubation of cells for 10-300 min with 0.1-0.5 mM NAPQI led to concentration dependent cell damage, as determined by increased trypan blue exclusion, lactate dehydrogenase release and glutathione (GSH) depletion. NAPQI and N-hydroxyparacetamol (N-OH-pHAA), a postulated proximate metabolite of pHAA, caused cytotoxic effects in the same concentration range. In contrast, no toxic effects of pHAA (less than or equal to 20 mM) could be demonstrated. With the short half-life of NAPQI, less than 0.5% of the NAPQI added is expected to be left in the incubation medium after a 2 min incubated period. Nevertheless, 10-120 min (depending on the concentration of NAPQI) elapsed before the cells responded with increased membrane permeability. Clearly, the initial damage caused by NAPQI must be followed by subsequent cellular steps before toxicity becomes apparent. The addition of N-acetylcysteine, GSH or ascorbate during the NAPQI exposure period fully protected the hepatocytes from NAPQI damage. Lesser effects were demonstrated when these agents were added after the 5 min NAPQI exposure period. The results presented in this study further support the hypothesis that NAPQI is the ultimate reactive formed from pHAA.

Metabolism in vitro of tris(2,3-dibromopropyl)-phosphate: oxidative debromination and bis(2,3-dibromopropyl)phosphate formation as correlates of mutagenicity and covalent protein binding.

Tris(2,3-dibromopropyl)phosphate (Tris-BP) was found to be metabolized by liver microsomes obtained from untreated and phenobarbital-pretreated rats. Metabolites of Tris-BP, whose formation was dependent on NADPH and oxygen, included bromide ion and bis(2,3-dibromopropyl)phosphate (Bis-BP). The rates of formation of these metabolites were markedly increased in liver microsomes isolated from phenobarbital-pretreated rats compared to microsomes from untreated rats. In the presence of either SKF 525-A or metyrapone, the formation rates of bromide ion and Bis-BP were decreased, whereas alpha-naphthoflavone had no effect. The effects of the various treatments on bromide release and Bis-BP formation paralleled those that have been previously observed with respect to the activation of Tris-BP to mutagenic and covalently protein bound metabolites. Furthermore, rates of oxidative debromination of several Tris-BP analogs directly correlated with their respective mutagenicities. Addition of glutathione (GSH) to microsomal incubations of Tris-BP increased bromide release substantially over control, values but had no effect on Bis-BP formation. On the other hand, the addition of GSH to microsomes decreased covalent binding and mutagenicity of Tris-BP with increased formation of water soluble metabolites. GC/MS analysis of ethyl acetate extracts from incubations of rat liver microsomes with Tris-BP identified 2-bromoacrolein (2-BA) as a metabolite. Introducing deuterium at the carbon atom number 1 of the propyl moiety of Tris-BP had no effect on either bromide release or mutagenicity, whereas the analog labelled at carbon atom 3 showed significant isotope effects on both activities. In contrast, deuterium substitution at carbon atom 2 gave a significant isotope effect on bromide release, but not on mutagenicity. The data indicate that Tris-BP can be metabolized by rat liver microsomes to Bis-BP and 2-bromoacrolein catalyzed by cytochrome P-450 in a process liberating bromide ions. Further, the results are consistent with oxidation at the terminal carbon atom of Tris-BP thereby forming 2-bromoacrolein, which is postulated to be the metabolite mainly responsible for Tris-BP mutagenicity.

Risk assessment of acrylamide in foods.

Daily mean intakes of acrylamide present in foods and coffee in a limited Norwegian exposure assessment study have been estimated to be 0.49 and 0.46 microg per kg body weight in males and females, respectively. Testicular mesotheliomas and mammary gland adenomas have consistently been found in 2-year drinking water rat cancer studies with acrylamide. Acrylamide also shows initiating activity in mouse skin after systemic administration. Since acrylamide is converted to the mutagenic metabolite glycidamide and forms adducts to hemoglobin in rodents and humans, the tumorigenic endpoints in rats were assumed to be an expression of acrylamide genotoxicity. Using the default linear extrapolation methods LED10 and T25, the lifetime cancer hazard after lifelong exposure to 1 microg acrylamide per kg body weight per day, scaled to humans, was calculated to be, on average, 1.3 x 10-3. Using this hazard level and correlating it with the exposure estimates, a lifetime cancer risk related to daily intake of acrylamide in foods for 70 years in males was calculated to be 0.6 x 10-3, implying that 6 out of 10,000 individuals may develop cancer due to acrylamide. For females, the risk values were slightly lower. It must be emphasized that this risk assessment is conservative. A number of processes may result in nonlinearity of the dose-response relationships for acrylamide carcinogenicity in the low-dose region, including detoxication reactions, cell cycle arrest, DNA repair, apoptosis, and immune surveillance. Thus, the true risk levels related to acrylamide intake may be considerably lower.

Development and implementation of the IPCS conceptual framework for evaluating mode of action of chemical carcinogens.

The framework developed by the International Programme on Chemical Safety (IPCS) for assessing the mode of action of tumour induction of chemicals in experimental animals has been illustrated with d-limonene, sodium saccharin, di(2-ethylhexyl)phthalate (DEHP) and sulfamethazine as examples. d-Limonene causes renal tumours only in male rats through a response associated with alpha(2u)-globulin. Sodium saccharin induces urinary bladder tumours only in male rats through formation of a urinary precipitate causing erosion of the bladder surface and extensive regenerative hyperplasia. DEHP causes liver tumours in rats and mice through activation of the receptor PPAR alpha leading to peroxisome proliferation and hepatocellular proliferation. Sulfamethazine induces thyroid follicular cell tumours in rats and mice through a mechanism involving altered thyroid hormone homeostasis.

In vitro and in vivo covalent binding of the kidney toxicant and carcinogen tris(2,3-dibromopropyl)-phosphate.

The nephrotoxicant and nephrocarcinogen tris(2,3-dibromopropyl)-phosphate (Tris-BP) is activated to products which bind covalently to microsomal protein by a cytochrome P-450 dependent oxidation reaction. Binding to rat liver microsomes proceeds 15 times faster than with kidney microsomes. The binding in liver microsomes is markedly increased by phenobarbital pretreatment, the apparent Vmax of the reaction is 175 pmol/mg microsomal protein/min with control microsomes and 1053 pmol/mg protein/min with induced microsomes. Binding with kidney microsomes is doubled after pretreatment with polychlorinated biphenyls. 2,3-Dibromopropanol (2,3-DBP), a hydrolysis product of Tris-BP, is also activated to covalently protein-bound products, but at a much slower rate than Tris-BP. Administration of Tris-BP to rats leads to its covalent binding to proteins in liver and kidney, with 5 time higher binding levels in kidney than in liver, correlating with its relative organotoxic potential in single dose experiments. Binding to proteins in the kidney was increased by pretreatment of animals with polychlorinated biphenyls. A covalent interaction of Tris-BP could also be demonstrated to DNA, both when DNA was added to liver microsomal incubations in vitro and to DNA extracted from liver and kidney after administration of Tris-BP in vivo. The binding levels were 4 times higher to kidney DNA than to liver DNA.

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.

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.

Mutagenicity and irreversible binding of the hepatocarcinogen, 2,4-diaminotoluene.

Mutagenicity of 2,4-diaminotoluene (DAT) in the Salmonella mutagenicity assay was increased with liver fractions from phenobarbital (PB) or beta-naphthoflavone (BNF) treated rats. Substitutions of the hydrogens in the methyl group of 2,4-DAT with deuterium resulted in a decrease in mutagenicity. Incubation of rat liver microsomes with tritiated 2,4-DAT in the presence of NADPH led to the formation of irreversibly bound products to microsomal protein. The rates of binding were not increased using microsomes from PB or BNF-treated rats and was not altered by deuterium substitution in the methyl group. Addition of superoxide dismutase, glutathione (GSH) or rat liver supernatant reduced 2,4-DAT irreversible binding, whereas 2,4-DAT mutagenicity was unaffected by superoxide dismutase addition. Injection of tritiated 2,4-DAT 100 mg/kg to rats lead to its irreversible binding to liver protein and ribosomal RNA and to kidney protein in vivo, again protein binding was not increased after prior treatment with PB or BNF. No irreversible interaction of tritiated 2,4-DAT with DNA either in vitro or in vivo could be demonstrated.

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.