Tissue distribution of DNA adducts in male Fischer rats exposed to 500 ppm of propylene oxide: quantitative analysis of 7-(2-hydroxypropyl)guanine by 32P-postlabelling

(32)P-postlabelling/HPLC analysis of various styrene-induced DNA adducts in mice

Styrene oxide (SO), a reactive metabolite of styrene, modifies DNA at several nucleophilic sites. In the present work we have determined the SO-DNA adducts in vitro and in vivo by two different versions of (32)P-postlabelling/HPLC assays. When anionexchange cartridges were used for adduct enrichment the β-isomer of 7-substituted guanines was detected in in vitro SO-treated DNA as well as in mice lungs exposed to styrene at 750 and 1500 mg m(-3) for 21 days (6 h day(-1), 7 days week(-1)). In the lungs, the adduct levels were 6.5 and 23 per 10(8) nucleotides for the two doses, respectively. When the nuclease P1 resistant adducts were studied by the (32)P-postlabelling/HPLC assay involving nuclease P1/prostatic acid phosphatase hydrolysis, the main adducts in in vitro-treated DNA were the α-isomer of N(2)-substituted guanine, β-isomers of 1-substituted adenine and 3-substituted uracil. β1-SO-adenine adduct was detected in the mice lung tissues after conversion of the 1-substituted adduct to the βN(6)-SO-adenine adduct by the Dimroth rearrangement. The 1-adenine adduct levels for the two doses were found to be 0.17 and 0.51 per 10(8) nucleotides. The current results show the potential of using the 7-guanine and 1-adenine adducts as biomarkers in biomonitoring of styrene exposure.

Is propylene oxide induced cell proliferation in rat nasal respiratory epithelium mediated by a severe depletion of water-soluble non-protein thiol?

Propylene oxide (PO) concentrations >or=300 ppm induced cell proliferation and tumors in rat nasal respiratory epithelium (NRE). Cell proliferation was suggested to result from depletion of glutathione (GSH) in NRE. In order to substantiate this hypothesis, cell proliferation - measured by bromodeoxyuridine incorporation into DNA of the epithelium lining middle septum, dorsal medial meatus, and medial and lateral surfaces of the nasoturbinate in transverse nasal sections taken immediately posterior to the upper incisor teeth - and water-soluble non-protein thiol (NPSH) in NRE were determined after exposing male Fischer 344 rats to 50 ppm, 100 ppm, 200 ppm, or 300 ppm PO (6 h/day, 3 days). Both parameters were also investigated after treating rats for 3 days with diethylmaleate (DEM; 2 x 250 mg/kg/day or 500 + 150 mg/kg/day) or buthionine sulfoximine (BSO; 500 mg/kg/day). Exposure to 50 ppm PO and treatment with 2 x2 50 mg/kg/day DEM resulted in NPSH levels approximating 50% and 80% of the level in untreated controls, respectively. Cell proliferation did not increase. After exposures to >or= 100 ppm PO or treatment with BSO or 500 + 150 mg/kg/day DEM, NPSH was depleted to <or=1/3 of the control level and cell proliferation increased 2.0-3.7-fold the control value. In conclusion, profound perturbation of the GSH status may represent a crucial step in PO induced rat nasal tumorigenicity.

Propylene oxide: genotoxicity profile of a rodent nasal carcinogen

Propylene oxide (PO) is a DNA-reactive genotoxic agent; that is, it reacts with DNA to produce lesions in the genetic material. PO also induces tumors in rodents, although only at high concentrations and at portals of entry. This review of PO's genotoxicity profile is organized according to endpoints measured, that is, nonmutational or mutational endpoints, and as to whether the results were from in vitro or in vivo studies. In addition to results of experimental studies, PO's genotoxicity for humans is assessed by reviewing results of published biomarker studies. The weight of evidence indicates that although it is genotoxic, PO's potency as a DNA-reactive mutagen is weak. Other aspects of PO's overall tissue toxicities are also reviewed, with attention to glutathione (GSH) depletion and its consequences, that is, cell proliferation, death, and necrosis. These toxic tissue responses occur in the same anatomical regions in rodents as do the PO-induced tumors. Furthermore, some of these tissue toxicities can produce effects that may either augment PO's DNA-reactive mutagenicity or be genotoxic in themselves, not dependent on PO's DNA reactivity. Although its DNA reactivity may be a necessary component of PO's overall genotoxicity and rodent carcinogenicity, it is likely not sufficient, and the associated tissue toxicities, which are rate-limiting, also seem to be required. This complex mode of action has implications for estimations of PO's cancer potential in humans, especially at low exposure concentrations.

A physiological toxicokinetic model for inhaled propylene oxide in rat and human with special emphasis on the nose

Chronic exposure to high concentrations of PO induced inflammation in the respiratory nasal mucosa (RNM) of rodents and, for concentrations >or= 300 ppm, caused nasal tumors. Considering the nose to be the most relevant target organ for PO-induced tumorigenicity, we developed a physiological toxicokinetic model for PO in rats and humans. It includes compartments for arterial, venous, and pulmonary blood, liver, muscle, fat, richly perfused tissues, lung, and nose. It simulates inhalation of PO, its distribution into tissues by blood flow, and its elimination by exhalation and metabolism. In nose, lung, and liver of rats, PO conjugation with glutathione (GSH), PO-induced GSH depletion, and formation of PO adducts to DNA are described. Also modeled are PO adducts to hemoglobin of rats and humans. Required partition coefficients and metabolic parameters were derived experimentally or from publications. In rats, simulated PO concentrations in blood and GSH levels in tissues agreed with measured data. If compared with reported values, levels of adducts with hemoglobin were underpredicted up to a factor of about 2. Adducts with DNA differed up to a factor of 3. Hemoglobin adducts predicted for PO-exposed workers were 1.5-1.9 times higher than the reported ones. Considering identical conditions of PO exposure, similar PO concentrations in RNM were modeled for rats and humans. Also, PO concentrations in blood, about 1/30th of those in RNM, were similar in both species. Since the model was evaluated on all available data in rats and humans, we consider it to be useful for estimating the risk from inhalation exposure to PO.

DNA damage and DNA adduct formation in rat tissues following oral administration of acrylamide

Acrylamide is present as a contaminant in the human diet in heated food products. It has been found to be carcinogenic in laboratory rats and has been classified as probably carcinogenic in humans. In order to clarify the possible involvement of a primary genotoxic mechanism in acrylamide-induced carcinogenicity, both the presence of DNA damage, measured by the comet assay, and the formation of N7-(2-carbamoyl-2-hydroxyethyl)guanine (N7-GA-Gua) and N3-(2-carbamoyl-2-hydroxyethyl)adenine (N3-GA-Ade), derived from reaction of the active metabolite glycidamide (GA) with the DNA, analyzed by LC/MS/MS, were assessed in selected rat tissues. Rats were administered with single oral doses of acrylamide (18, 36 or 54 mg/kg body weight (b.w.) and the organs (blood leukocytes, brain, bone marrow, liver, testes and adrenals) were sampled at different times after treatment. Results from GA-induced DNA adduct measurements indicated a relatively even organ distribution of the adducts in brain, testes and liver. Organ-specificity in acrylamide carcinogenesis can therefore not be explained by a selective accumulation of GA-DNA adducts in the target organs, at least not after a single dose exposure. The DNA adduct profiles and half-lives were similar in the different organs; except that the N3-GA-Ade adduct was more rapidly removed from tissues than the N7-GA-Gua adduct. Increased extent of DNA migration, as measured by the in vivo rat comet assay, was found in brain and testes, and these specific results seem to be in accordance with the known organ-specificity in acrylamide carcinogenesis in rat. Only weak and transient DNA damage was recorded in the liver, bone marrow and adrenals. The DNA-damaging effect of the compound observed in the blood leukocytes could be a simple biomarker of acrylamide exposure and genotoxicity.

DNA adducts derived from administration of acrylamide and glycidamide to mice and rats

Acrylamide (AA) is an important industrial chemical that is neurotoxic, mutagenic to somatic and germ cells, and carcinogenic in chronic rodent bioassays. Recent findings of AA in many common starchy foods have sparked renewed interest in determining toxic mechanisms and in understanding the cancer, neurotoxicity, and reproductive risks from typical human exposures. Dosing mice and rats with AA (50 mg/kg) led to presence of glycidamide (GA) in serum and tissues. Furthermore, GA-derived DNA adducts of adenine and guanine were formed in all tissues examined, including both target tissues identified in rodent carcinogenicity bioassays and in non-target tissues. Dosing rats and mice with an equimolar amount of GA typically produced higher levels of DNA adducts than observed with AA. Kinetics of DNA adduct formation and accumulation were measured following oral administration of a single dose of AA (50 mg/kg) or from repeat dosing (1 mg/kg/day), respectively. The formation of these DNA adducts is consistent with previously reported mutagenicity of AA and GA in vitro, which involved reaction of GA with adenine and guanine bases. These results provide strong support for a genotoxic mechanism of AA carcinogenicity in rodents. The kinetic/biomarker approaches described here may represent a meaningful way to extrapolate cancer risks to actual human exposures from food, which are much lower.

Dosimetry by means of DNA and hemoglobin adducts in propylene oxide-exposed rats

The main purpose of the study was to establish the relation between exposure dose of propylene oxide (PO) and dose in various tissues of male F344 rats exposed to the compound by inhalation. The animals were exposed to 0, 5, 25, 50, 300, or 500 ppm PO in the air for 3 days (6 h/day) or 4 weeks (6 h/day, 5 days/week). Blood, nasal respiratory epithelium, lung, and liver were collected. 2-Hydroxypropylvaline (HPVal) in hemoglobin was quantified using the N-alkyl Edman method and gas chromatography/tandem mass spectrometry. 7-(2-Hydroxypropyl)guanine (7-HPG) in DNA was quantified using (32)P postlabeling. The levels of 7-HPG in DNA of nasal respiratory epithelium and lung increased linearly with concentration as measured both after 3 days and 4 weeks of exposure. Similarly, 7-HPG in liver DNA and HPVal in hemoglobin showed a linear increase with PO concentration in the 3-day exposure group, whereas a deviation from linearity was observed above 300 ppm in the 4-week exposure group. The new results confirm previous observations of a dose difference between tissues with the highest dose present in the nasal respiratory epithelium. The measured adduct levels were used for calculation of adduct increments and corresponding tissue doses per unit of external exposure dose. For this purpose, the buildup of adducts was modeled considering the different kinetics of formation and elimination of adducts with DNA and hemoglobin, respectively, and also considering the increasing body weight of the animals. The half-life of 7-HPG in vivo, as well as tissue doses, could be solved from DNA adduct data at the 3rd and 26th days. Within the range of concentrations where the dose-response curves for adduct formation are linear, the relationship between exposure dose and resulting tissue doses could be based equally well on adduct data from the short-term exposure as on adduct data from the prolonged exposure.

Mutagenic activity of ethylene oxide and propylene oxide under XPG proficient and deficient conditions in relation to N-7-(2-hydroxyalkyl)guanine levels in Drosophila

Ethylene oxide (EO) and propylene oxide (PO) are direct acting mutagens with high Swain-Scott s-values, which indicate that they react preferentially with ring nitrogens in the DNA. We have previously described that in the X-linked recessive lethal (RL) assay in Drosophila postmeiotic male germ cells EO is, per unit exposure dose, 5-10 times more mutagenic than PO. Furthermore, at the higher dose range of EO tested, 62.5-1000 ppm, up to 20-fold enhanced mutation rates were measured in the absence of maternal nucleotide excision repair (NER) compared to repair proficient conditions. The lower dose range of EO tested, 2-7.8 ppm, still produced a small increased mutation rate but without a significant elevated effect when the NER system is being suppressed. The lowest dose of PO tested, 15.6 ppm, produced only in NER- condition an increased mutation rate. The aim of the present study was to compare the mutagenic effect of EO and PO in the RL assay under XPG proficient and deficient conditions with the formation of N-7-(2-hydroxyethyl)guanine (7-HEG) and N-7-(2-hydroxypropyl)guanine (7-HPG), respectively, the major DNA adducts formed. The formation of 7-HEG and 7-HPG was investigated in Drosophila males exposed to EO and PO as a measure of internal dose for exposures ranging from 2 to 1000 or 2000 ppm, respectively, for 24h. Analysis of 7-HEG and 7-HPG, using a highly sensitive 32P-postlabelling assay, showed a linear increase of adduct levels over the entire dose range. The non-linear dose-response relationship for mutations could therefore not be explained by a reduced inhalation or increased detoxification at higher exposure levels. In analogy with the four times higher reactivity of EO the level of N-7-guanine alkylation per ppm was for EO 3.5-fold higher than that for PO. Per unit N-7-guanine alkylation EO was found to be slightly more mutagenic than PO, whereas PO was the more potent clastogenic agent. While this research has not identified the DNA lesions that cause the increase in repair deficient flies, it supports the hypothesis that efficient error-free repair of some N-alkylation products can explain why these agents tend to be weakly genotoxic or even inactive in repair-competent (premeiotic) germ cells of the mouse and the Drosophila fly.

Molecular dosimetry of N7-(2-hydroxypropyl)guanine in tissues of F344 rats after inhalation exposure to propylene oxide

Propylene oxide (PO) is a high-volume chemical intermediate that causes a low incidence of nasal tumors in rodents exposed to high concentrations (> or =300 p.p.m.). PO reacts with DNA forming mainly N7-(2-hydroxypropyl)guanine (7-HPG). The exposure-dependent accumulation of 7-HPG in nasal respiratory epithelium (NRE), lung and liver was determined in male F344 rats exposed to PO (0, 5, 25, 50, 300 or 500 p.p.m.) by the inhalation route for 3 or 20 days (6 h/day; 5 days/week). These exposures ranged from low concentrations, such as those potentially occurring in the workplace, to high concentrations that proved to be carcinogenic in rodents. Analysis of 7-HPG in DNA by gas chromatography-high-resolution mass spectrometry (GC-HRMS) showed a linear response in 7-HPG for all three tissues after 3 days of exposure, and for NRE and lung after 20 days of exposure. A slightly sublinear response in 7-HPG was observed in liver after 20 days of exposure. For both exposure periods, the NRE had the highest concentration of 7-HPG, followed by lung and liver. The amount of 7-HPG in NRE was seven and 17 times higher than in lung and liver, respectively, for the 3 day exposures. For the 20 day exposures, the concentration of 7-HPG in NRE was six and 13 times higher than that in lung and liver, respectively, over the concentration range studied. These results demonstrate a much higher extent of DNA alkylation in the target tissue for carcinogenesis, than in non-target tissues. As PO-induced tumor formation was highly sublinear, occurring only at high vapor concentrations, whereas 7-HPG adducts were shown to be linearly dependent on airborne concentration, these results suggest that 7-HPG is not sufficient for PO nasal carcinogenesis and that other factors such as increased cell proliferation may be important in determining the tumor exposure response.

A toxicokinetic model for styrene and its metabolite styrene-7,8-oxide in mouse, rat and human with special emphasis on the lung

Styrene (ST) occurs ubiquitously in the environment and it is an important industrial chemical. After its uptake by the exposed mammalian organism, ST is oxidized to styrene-7,8-oxide (SO) by cytochrome P450 dependent monooxygenases. This reactive intermediate is further metabolized by epoxide hydrolase (EH) and glutathione S-transferase (GST). In long-term animal studies, ST induced lung tumors in mice but not in rats. Considering the lung to be the relevant target organ for ST induced carcinogenicity in mice, we extended a previously developed physiological toxicokinetic model in order to simulate the lung burden with ST and SO in the ST exposed mouse, rat and human. The new model describes oral and pulmonary uptake of ST, its distribution into various tissues, its exhalation and its metabolism to SO in lung and liver. It also simulates the distribution of the produced SO into the tissues and its EH and GST mediated metabolism in liver and in lung. In both organs the ST induced GSH consumption is described together with the formation of adducts to hemoglobin and to DNA of lymphocytes in ST exposed mice, rats and humans. The model includes compartments for arterial, venous and pulmonary blood, liver, muscle, fat, richly perfused tissues and lung. The latter organ is represented by two compartments, namely by the conducting and the alveolar zone. The physiological description of the pulmonary compartments relies on measured alveolar retentions, literature values of surface area of capillary endothelium, of the thickness of the tissue 'air-to-plasma', of the partition coefficient lung:blood and of metabolic parameters of ST and SO measured in pulmonary cell fractions of rodents and humans. Simulations of average pulmonary GSH levels in ST exposed rodents agree with measured data. The model predicts a significant GSH depletion (40%) in the conducting zone of mice exposed for 6 h to a ST concentration of only 20 ppm. In the conducting zone of rats, exposure to 200 ppm ST results in a loss of GSH of about 15% only. In humans, a pulmonary GSH reduction does not occur. The highest average pulmonary SO concentrations are predicted for mice, somewhat lower values for rats and by far the lowest ones for humans. Following steady state exposure to 20 ppm ST, the average SO concentration in mouse lungs is expected to be only three times higher than in rats. This difference diminishes to a factor of less than two at 70 ppm. In humans exposed to 20 ppm ST for 8 h, the average pulmonary SO burden of 0.016 micromol/kg is predicted to be about 17 and 50 times smaller than the corresponding values for rat and mouse. In agreement with reported values, pulmonary DNA adduct levels in rodents exposed to 160 ppm ST were simulated to be similar in rats and mice. In summary, there was no dramatic difference in the calculated average pulmonary SO burden between both animal species. However, pulmonary GSH loss was by far more expressed in ST exposed mice than rats. Since the model was validated on all available ST/SO data in mice, rats and humans, we consider it to be useful for estimating the risk resulting from exposure to ST.

Genotoxic effects of ethylene oxide, propylene oxide and epichlorohydrin in humans: update review (1990-2001)

Ethylene oxide (EtO), propylene oxide (PO) and epichlorohydrin (ECH) are important industrial chemicals widely used as intermediates for various synthetic products. EtO and PO are also environmental pollutants. In this review we summarize data published during the period 1990-2001 concerning both the genotoxic and carcinogenic effects of these epoxides in humans. The use of DNA and hemoglobin adducts as biomarkers of exposure and the role of polymorphism, as well as confounding factors, are discussed. We have also included recent in vitro data comprising genotoxic effects induced by EtO, PO and ECH in mammalian cells. The uncertainties regarding cancer risk estimation still persist, in spite of the large database collected.

Applications of mass spectrometry for quantitation of DNA adducts

DNA adducts are formed when electrophilic molecules or free radicals attack DNA. 32P-postlabeling has been the most commonly used assay for quantitation of DNA adducts due mainly to its excellent sensitivity that allows quantitation at concentrations as low as approximately 1 adduct per 10(9) normal bases. Such methods, however, do not have the specificity desired for accurate and reliable quantitation, and are prone to produce false positives and artifacts. In the last decade, mass spectrometry in combination with liquid and gas chromatography has presented itself as a good alternative to these techniques since it can satisfy the need for specificity and reliability through the use of stable isotope-labeled internal standards and highly specific detection modes such as selected reaction monitoring and high-resolution mass spectrometry. In this article, the contribution of mass spectrometry to the quantitation of DNA adducts is reviewed with special emphasis on unique applications of mass spectrometry in the area of DNA adduct quantitation and recent applications with improvements in sensitivity.

Exposure-dependent accumulation of N-(2-hydroxypropyl)valine in hemoglobin of F344 rats exposed to propylene oxide by the inhalation route

The detection of hemoglobin adducts by mass spectrometry is a very sensitive and specific measurement of the extent of covalent binding of electrophilic chemicals. The exposure-dependent accumulation of N-(2-hydroxypropyl)valine (N-HPVal) in globin of rats exposed to propylene oxide (PO) (0, 5, 25, 50, 300 or 500 ppm) by the inhalation route was measured to assess the utility of Hb adducts as biomarkers of exposure. Analysis of N-HPVal by gas-chromatography tandem mass spectrometry showed a linear exposure-dependent response for adduct accumulation in globin of rats exposed to PO for 3 days (6 h/day). After 20 days of exposure (6 h/day; 5 days/week), the exposure-response curve was slightly sub-linear. DNA adducts had been measured in several organs of the same animals in a companion study. The dose-response for accumulation of DNA adducts was similar to that obtained for Hb adducts. However, the number of DNA adducts varied by 17-fold between different tissues. The highest number of DNA adducts was found in respiratory nasal tissue, followed by lung and then liver. These data demonstrate that hemoglobin adducts provide a sensitive dosimeter for systemic exposure, but cannot be used to predict the extent of DNA binding in individual tissues. Furthermore, the exposure-response curve for both hemoglobin and DNA adduct accumulation does not reflect the tumor incidence curve for PO, providing evidence that the assessment of risk to cancer is more complex than simple biomarker measurements. When the present rat data were compared with recent N-HPVal measurements in humans, similar binding was found.

Kinetics of propylene oxide metabolism in microsomes and cytosol of different organs from mouse, rat, and humans

Kinetics of the metabolic inactivation of 1,2-epoxypropane (propylene oxide; PO) catalyzed by glutathione S-transferase (GST) and by epoxide hydrolase (EH) were investigated at 37 degrees C in cytosol and microsomes of liver and lung of B6C3F1 mice, F344 rats, and humans and of respiratory and olfactory nasal mucosa of F344 rats. In all of these tissues, GST and EH activities were detected. GST activity for PO was found in cytosolic fractions exclusively. EH activity for PO could be determined only in microsomes, with the exception of human livers where some cytosolic activity also occurred, representing 1-3% of the corresponding GST activity. For GST, the ratio of the maximum metabolic rate (V(max)) to the apparent Michaelis constant (K(m)) could be quantified for all tissues. In liver and lung, these ratios ranged from 12 (human liver) to 106 microl/min/mg protein (mouse lung). Corresponding values for EH ranged from 4.4 (mouse liver) to 46 (human lung). The lowest V(max) value for EH was found in mouse lung (7.1 nmol/min/mg protein); the highest was found in human liver (80 nmol/min/mg protein). K(m) values for EH-mediated PO hydrolysis in liver and lung ranged from 0.83 (human lung) to 3.7 mmol/L (mouse liver). With respect to liver and lung, the highest V(max)/K(m) ratios were obtained for GST in mouse and for EH in human tissues. GST activities were higher in lung than in liver of mouse and human and were alike in both rat tissues. Species-specific EH activities in lung were similar to those in liver. In rat nasal mucosa, GST and EH activities were much higher than in rat liver.

Specific DNA adducts induced by some mono-substituted epoxides in vitro and in vivo

Alkyl epoxides are important intermediates in the chemical industry. They are also formed in vivo during the detoxification of alkenes. Alkyl epoxides have shown genotoxicity in many toxicology assays which has been associated with their covalent binding to DNA. Here aspects of the formation and properties of DNA adducts, induced by some industrially important alkenes and mono-substituted epoxides are discussed. These include propylene oxide, epichlorohydrin, allyl glycidyl ether and the epoxy metabolites of styrene and butadiene. The major DNA adducts formed by epoxides are 7-substituted guanines, 1- and 3-substituted adenines and 3-substituted cytosines. In addition, styrene oxide and butadiene monoepoxide are able to modify exocyclic sites in the DNA bases, the sites being in the case of styrene oxide N(2)- and O(6)-positions of guanine, N(6)-adenine as well as N(4)-and O(2)-cytosine. In vivo the main adduct is the 7-substituted guanines. The 1-substituted adenines have also shown marked levels, and these adducts should also be targets in biomonitoring of human exposures. Due to its low mutagenicity, 7-substituted guanines are considered as a surrogate marker for other mutagenic lesions, e.g. those of 1-adenine or 3-uracil adducts.

Dna adducts, mutations, and cancer 2000

The main achievements in the DNA adduct field in the 1990s have been technical innovations of methods for specific adducts reaching sensitivities required for low levels encountered in humans. Over 20 specific adducts or closely related groups of adducts have been determined in humans. The sources of the DNA-binding agents are endogenous and exogenous or both. In some of these studies adduct levels have been correlated to metabolic or DNA repair genotypes. An example of DNA adduct studies in human target tissue is taken on UV photoproducts in skin in situ. Adduct-induced mutations, specific mutation spectra, and their relationship to cancer are discussed. The quantitative adduct techniques will enable comparisons of endogenous and exogenous adduct levels and will give important clues to the etiology of human cancer. Furthermore, adducts will provide an intermediary tool for genotyping studies, both for metabolic enzyme and for DNA repair system genotypes. As the common polymorphisms are likely to cause at most moderate increases in the risk of cancer, the intermediary adduct endpoint is a necessary proof of causal relationships. The present and future biomonitoring studies will cover many endpoints to link the mechanistic steps from DNA adducts to cancer via mutations and modulating host susceptibility factors.

Toxicokinetics of inhaled propylene in mouse, rat, and human

A physiological toxicokinetic (PT) model was developed for inhaled propylene gas (PE) in mouse, rat, and human. Metabolism was simulated to occur in the liver (90%) and in the richly perfused tissue group (10%). The partition coefficients tissue:air were determined in vitro using tissues of mice, rats, and humans. Most of the tissues have partition coefficients of around 0.5. Only adipose tissue displays a 10 times higher value. The partition coefficient blood:air in human is 0.44, about half of that in rodents. PE can accumulate in the organism only barely. For male B6C3F1 mice and male Fischer 344/N rats, parameters of PE metabolism were obtained from gas uptake experiments. Maximum rates of metabolism (V(maxmo)) were 110 micromol/h/kg in mice and 50.4 micromol/h/kg in rats. V(maxmo)/2 was reached in mice at 270 ppm and in rats at 400 ppm of atmospheric PE. Pretreatment of the animals with sodium diethyldithiocarbamate resulted in an almost complete inhibition of PE metabolism in both species. Preliminary toxicokinetic data on PE metabolism in humans were obtained in one volunteer who was exposed up to 4.5 h to constant concentrations of 5 and 25 ppm PE. The PT model was used to calculate PE blood concentrations at steady state. At 25 ppm, the blood values were comparable across species, with 0.19, 0.32, and 0.34 micromol/L for mouse, rat, and human, respectively. However, the corresponding rates of PE metabolism differed dramatically, being 8.3, 2.1, and 0.29 micromol/h/kg in mouse, rat, and human. For a repeated human exposure to 25 ppm PE in air (8 h/day, 5 days/week), PE concentrations in venous blood were simulated. The prediction demonstrates that PE is eliminated so rapidly that it cannot accumulate in the organism. For low exposure concentrations, it became obvious that the rate of uptake into blood by inhalation is limited by the blood flow through the lung and the rate of metabolism is limited by the blood flow through the metabolizing organs.

Nasal tumors in rats following long-term inhalation exposure to 1,4-dichlorobutene-2 (DCB)

This study was conducted to elucidate the time- and dose-response relationships of long-term, low-level 1,4-dichlorobutene-2 (DCB) inhalation exposure to nasal tumor induction in rats. Male Crl:CD BR rats were exposed 6 hours per day, 5 days week to 0, 0.1, 0.3, or 1.0 ppm DCB for up to 19 months; some rats were sacrificed at various time intervals during the study. After 19 months of exposure, surviving rats were held without treatment for an additional 5 months. Tissues from the respiratory tract, lymph nodes, and brain were evaluated microscopically. Compound-related non-neoplastic lesions were observed in the nasal cavities of rats in the 1.0 ppm group after three months of exposure and in the other two groups after twelve months of exposure. The lesions were progressive in severity and frequency. A statistically significant increase in benign nasal tumors (adenomas) occurred in rats from all three DCB-exposed groups. The adenomas occurred in the respiratory region of the nasal cavity and were first observed in the 1.0 ppm group at study month 10. Malignant nasal tumors occurred in the olfactory region of the nasal cavity and were statistically increased at 1.0 ppm.

32P-postlabelling of propylene oxide 1- and N(6)-substituted adenine and 3-substituted cytosine/uracil: formation and persistence in vitro and in vivo

Propylene oxide, a widely used monofunctional alkylating agent, has been shown to be genotoxic in in vitro test systems and induces tumors in the nasal tissues of experimental animals. Propylene oxide, like related alkylating agents, forms several different adducts with DNA bases, but predominantly at the 7-position of guanine. We have previously described the in vitro and in vivo formation and stability of this major adduct. The aim of the present study was to perform a similar investigation of other adducts of propylene oxide. 1-(2-Hydroxypropyl)adenine (1-HP-adenine) and 3-(2-hydroxypropyl)cytosine (3-HP-cytosine), as well as their rearrangement products to N(6)-(2-hydroxypropyl)adenine (N(6)-HP-adenine) and 3-(2-hydroxypropyl)uracil (3-HP-uracil), respectively, were analysed by a very sensitive (32)P-postlabelling method involving nuclease P1 enhancement and radioisotope detector-coupled HPLC separation. All four adducts could be detected in DNA treated in vitro with propylene oxide. The sum of the levels of 1- and N(6)-HP-adenine amounted to 3.5% and the sum of 3-HP-cytosine and 3-HP-uracil to 1.7%, respectively, of 7-(2-hydroxypropyl)guanine (7-HP-guanine). In male Fischer 344 rats exposed to 500 p.p.m. propylene oxide by inhalation for 20 days, 1-HP-adenine was detected in all analysed tissues, including nasal epithelium, lung and lymphocytes, whereas N(6)-HP-adenine was only found in the tissues of the nasal cavities. The highest level of 1-HP-adenine (2.0 mol/10(6) mol of normal nucleotides, i.e. 2% of 7-HP-guanine) was found in the respiratory nasal epithelium, which also represents the major target for tumour induction in the rat following inhalation of propylene oxide. The levels of this adduct in the lung and in the lymphocytes were considerably lower, amounting to 15 and 9%, respectively, of that of the respiratory nasal epithelium. In rats killed 3 days after cessation of exposure, practically no decrease in 1-HP-adenine was observed, indicating no or very slow repair. 3-HP-uracil could only be detected in the respiratory nasal epithelia of propylene-exposed rats and its concentration was as low as 0.02 mol/10(6) mol of normal nucleotides (0.02% of 7-HP-guanine). Since 3-HP-uracil was chemically much more stable than the latter, the obtained animal data suggest repair of the cytosine and/or uracil adducts. Incubation of propylene oxide-reacted DNA with a protein extract from mammalian cells indicated that an enzymatic repair mechanism exists for removal of 3-HP-cytosine, but not for 3-HP-uracil or 1- and N(6)-HP-adenine. Another finding was that uracil glycosylase is probably not involved. The level of 1-HP-adenine in the propylene oxide-exposed rats was approximately 50 times lower than that of 7-HP-guanine. Nevertheless, this adduct is conveniently analysed and has high chemical stability and recovery, which results in high sensitivity (detection limit 0.3 mol/10(9) mol of normal nucleotides using 10 microgram DNA). 1-HP-adenine might, therefore, be considered as an alternative to 7-HP-guanine for monitoring exposure to propylene oxide.

Methods for biological monitoring of propylene oxide exposure in Fischer 344 rats

Propylene oxide (PO) is used as an intermediate in the chemical industry. Human exposure to PO may occur in the work place. Propylene, an important industrial chemical and a component of, for example, car exhausts and cigarette smoke, is another source of PO exposure. Once taken up in the organism, this epoxide alkylates macromolecules, such as haemoglobin and DNA. The aim of the present investigation was to compare two methods for determination of in vivo dose, the steady state concentration of PO in blood of exposed rats and the level of haemoglobin adducts. Male Fischer 344 rats were exposed for 4 weeks (6 h/day, 5 days/week) to PO at a mean atmospheric concentration of 500 ppm (19.9 micromol/l). Immediately after the last exposure blood was collected in order to determine the steady state concentration of PO. Free PO was measured in blood samples of three animals by means of a head space method to be 37 +/- 2 micromol/l blood (mean +/- S.D.). Blood samples were also harvested for the measurement of haemoglobin adducts. N-2-Hydroxypropyl adducts with N-terminal valine in haemoglobin were quantified using the N-alkyl Edman method with globin containing adducts of deuterium-substituted PO as an internal standard and N-D,L-2-hydroxypropyl-Val-Leu-anilide as a reference compound. Tandem mass spectrometry was used for adduct quantification. The adduct levels were < 0.02 and 77.7 +/- 4.7 nmol/g globin (mean +/- S.D.) in control animals (n = 7) and in exposed animals (n = 34), respectively. The adduct levels expected at the end of exposure were calculated to be 71.7 +/- 4.1 nmol/g globin (mean +/- S.D.) using the measured steady state concentration of PO in blood and taking into account the growth of animals, the life span of erythrocytes, the exposure conditions and the second order rate constant for adduct formation. The good agreement between the estimated and measured adduct levels indicates that both end-points investigated are suitable for biological monitoring.