Effects of formaldehyde exposure on the extractability of DNA from proteins in the rat nasal mucosa

Capturing Protein-Nucleic Acid Interactions by High-Intensity Laser-Induced Covalent Crosslinking

Interactions of DNA with structural proteins such as histones, regulatory proteins, and enzymes play a crucial role in major cellular processes such as transcription, replication and repair. The in vivo mapping and characterization of the binding sites of the involved biomolecules are of primary importance for a better understanding of genomic deployment that is implicated in tissue and developmental stage-specific gene expression regulation. The most powerful and commonly used approach to date is immunoprecipitation of chemically cross-linked chromatin (XChIP) coupled with sequencing analysis (ChIP-seq). While the resolution and the sensitivity of the high-throughput sequencing techniques have been constantly improved little progress has been achieved in the crosslinking step. Because of its low efficiency the use of the conventional UVC lamps remains very limited while the formaldehyde method was established as the "gold standard" crosslinking agent. Efficient biphotonic crosslinking of directly interacting nucleic acid-protein complexes by a single short UV laser pulse has been introduced as an innovative technique for overcoming limitations of conventionally used chemical and photochemical approaches. In this survey, the main available methods including the laser approach are critically reviewed for their ability to generate DNA-protein crosslinks in vitro model systems and cells.

An updated mode of action and human relevance framework evaluation for Formaldehyde-Related nasal tumors

Formaldehyde is a reactive aldehyde naturally present in all plant and animal tissues and a critical component of the one-carbon metabolism pathway. It is also a high production volume chemical used in the manufacture of numerous products. Formaldehyde is also one of the most well-studied chemicals with respect to environmental fate, biology, and toxicology-including carcinogenic potential, and mode of action (MOA). In 2006, a published MOA for formaldehyde-induced nasal tumors in rats concluded that nasal tumors were most likely driven by cytotoxicity and regenerative cell proliferation, with possible contributions from direct genotoxicity. In the past 15 years, new research has better informed the MOA with the publication of in vivo genotoxicity assays, toxicogenomic analyses, and development of ultra-sensitive methods to measure endogenous and exogenous formaldehyde-induced DNA adducts. Herein, we review and update the MOA for nasal tumors, with particular emphasis on the numerous studies published since 2006. These new studies further underscore the involvement of cytotoxicity and regenerative cell proliferation, and further inform the genotoxic potential of inhaled formaldehyde. The data lend additional support for the use of mechanistic data for the derivation of toxicity criteria and/or scientifically supported approaches for low-dose extrapolation for the risk assessment of formaldehyde.

Reassessment of MTBE cancer potency considering modes of action for MTBE and its metabolites

A 1999 California state agency cancer potency (CP) evaluation of methyl tert-butyl ether (MTBE) assumed linear risk extrapolations from tumor data were plausible because of limited evidence that MTBE or its metabolites could damage DNA, and based such extrapolations on data from rat gavage and rat and mouse inhalation studies indicating elevated tumor rates in male rat kidney, male rat Leydig interstitial cells, and female rat leukemia/lymphomas. More recent data bearing on MTBE cancer potency include a rodent cancer bioassay of MTBE in drinking water; several new studies of MTBE genotoxicity; several similar evaluations of MTBE metabolites, formaldehyde, and tert-butyl alcohol or TBA; and updated evaluations of carcinogenic mode(s) of action (MOAs) of MTBE and MTBE metabolite's. The lymphoma/leukemia data used in the California assessment were recently declared unreliable by the U.S. Environmental Protection Agency (EPA). Updated characterizations of MTBE CP, and its uncertainty, are currently needed to address a variety of decision goals concerning historical and current MTBE contamination. To this end, an extensive review of data sets bearing on MTBE and metabolite genotoxicity, cytotoxicity, and tumorigenicity was applied to reassess MTBE CP and related uncertainty in view of MOA considerations. Adopting the traditional approach that cytotoxicity-driven cancer MOAs are inoperative at very low, non-cytotoxic dose levels, it was determined that MTBE most likely does not increase cancer risk unless chronic exposures induce target-tissue toxicity, including in sensitive individuals. However, the corresponding expected (or plausible upper bound) CP for MTBE conditional on a hypothetical linear (e.g., genotoxic) MOA was estimated to be ∼2 × 10(-5) (or 0.003) per mg MTBE per kg body weight per day for adults exposed chronically over a lifetime. Based on this conservative estimate of CP, if MTBE is carcinogenic to humans, it is among the weakest 10% of chemical carcinogens evaluated by EPA.

Measurement of Endogenous versus Exogenous Formaldehyde-Induced DNA-Protein Crosslinks in Animal Tissues by Stable Isotope Labeling and Ultrasensitive Mass Spectrometry

DNA-protein crosslinks (DPC) arise from a wide range of endogenous and exogenous chemicals, such as chemotherapeutic drugs and formaldehyde. Importantly, recent identification of aldehydes as endogenous genotoxins in Fanconi anemia has provided new insight into disease causation. Because of their bulky nature, DPCs pose severe threats to genome stability, but previous methods to measure formaldehyde-induced DPCs were incapable of discriminating between endogenous and exogenous sources of chemical. In this study, we developed methods that provide accurate and distinct measurements of both exogenous and endogenous DPCs in a structurally specific manner. We exposed experimental animals to stable isotope-labeled formaldehyde ([(13)CD2]-formaldehyde) by inhalation and performed ultrasensitive mass spectrometry to measure endogenous (unlabeled) and exogenous ((13)CD2-labeled) DPCs. We found that exogenous DPCs readily accumulated in nasal respiratory tissues but were absent in tissues distant to the site of contact. This observation, together with the finding that endogenous formaldehyde-induced DPCs were present in all tissues examined, suggests that endogenous DPCs may be responsible for increased risks of bone marrow toxicity and leukemia. Furthermore, the slow rate of DPC repair provided evidence for the persistence of DPCs. In conclusion, our method for measuring endogenous and exogenous DPCs presents a new perspective for the potential health risks inflicted by endogenous formaldehyde and may inform improved disease prevention and treatment strategies. Cancer Res; 76(9); 2652-61. ©2016 AACR.

Formation, Accumulation, and Hydrolysis of Endogenous and Exogenous Formaldehyde-Induced DNA Damage

Formaldehyde is not only a widely used chemical with well-known carcinogenicity but is also a normal metabolite of living cells. It thus poses unique challenges for understanding risks associated with exposure. N(2-)hydroxymethyl-dG (N(2)-HOMe-dG) is the main formaldehyde-induced DNA mono-adduct, which together with DNA-protein crosslinks (DPCs) and toxicity-induced cell proliferation, play important roles in a mutagenic mode of action for cancer. In this study, N(2)-HOMe-dG was shown to be an excellent biomarker for direct adduction of formaldehyde to DNA and the hydrolysis of DPCs. The use of inhaled [(13)CD2]-formaldehyde exposures of rats and primates coupled with ultrasensitive nano ultra performance liquid chromatography-tandem mass spectrometry permitted accurate determinations of endogenous and exogenous formaldehyde DNA damage. The results show that inhaled formaldehyde only reached rat and monkey noses, but not tissues distant to the site of initial contact. The amounts of exogenous adducts were remarkably lower than those of endogenous adducts in exposed nasal epithelium. Moreover, exogenous adducts accumulated in rat nasal epithelium over the 28-days exposure to reach steady-state concentrations, followed by elimination with a half-life (t1/2) of 7.1 days. Additionally, we examined artifact formation during DNA preparation to ensure the accuracy of nonlabeled N(2)-HOMe-dG measurements. These novel findings provide critical new data for understanding major issues identified by the National Research Council Review of the 2010 Environmental Protection Agency's Draft Integrated Risk Information System Formaldehyde Risk Assessment. They support a data-driven need for reflection on whether risks have been overestimated for inhaled formaldehyde, whereas underappreciating endogenous formaldehyde as the primary source of exposure that results in bone marrow toxicity and leukemia in susceptible humans and rodents deficient in DNA repair.

The endogenous exposome

The concept of the Exposome is a compilation of diseases and one's lifetime exposure to chemicals, whether the exposure comes from environmental, dietary, or occupational exposures; or endogenous chemicals that are formed from normal metabolism, inflammation, oxidative stress, lipid peroxidation, infections, and other natural metabolic processes such as alteration of the gut microbiome. In this review, we have focused on the endogenous exposome, the DNA damage that arises from the production of endogenous electrophilic molecules in our cells. It provides quantitative data on endogenous DNA damage and its relationship to mutagenesis, with emphasis on when exogenous chemical exposures that produce identical DNA adducts to those arising from normal metabolism cause significant increases in total identical DNA adducts. We have utilized stable isotope labeled chemical exposures of animals and cells, so that accurate relationships between endogenous and exogenous exposures can be determined. Advances in mass spectrometry have vastly increased both the sensitivity and accuracy of such studies. Furthermore, we have clear evidence of which sources of exposure drive low dose biology that results in mutations and disease. These data provide much needed information to impact quantitative risk assessments, in the hope of moving towards the use of science, rather than default assumptions.

Determination of genotoxicity by the Comet assay applied to murine precision-cut lung slices

Precision-cut lung slices (PCLSs) are an organotypic lung model that is widely used in pharmacological, physiological, and toxicological studies. Genotoxicity testing, as a pivotal part of early risk assessment, is currently established in vivo in various organs including lung, brain, or liver, and in vitro in cell lines or primary cells. The aim of the present study was to provide the three-dimensional organ culture PCLS as a new ex vivo model for determination of genotoxicity using the Comet assay. Murine PCLS were exposed to increasing concentrations of ethyl methane sulfonate 'EMS' (0.03-0.4%) and formalin (0.5-5mM). Tissue was subsequently dissociated, and DNA single-strand breaks were quantified using the Comet assay. Number of viable dissociated lung cells was between 4×10(5) and 6.7×10(5)cells/slice. Even treatment with EMS did not induce toxicity compared to untreated tissue control. As expected, DNA single-strand breaks were increased dose-dependently and significantly after exposure to EMS. Here, tail length rose from 24μm to 75μm. In contrast, formalin resulted in a significant induction of DNA cross-links. The effects induced by EMS and formalin demonstrate the usefulness of PCLS as a new ex vivo lung model for genotoxicity testing in the early risk assessment of airborne substances in the future.

Distribution of DNA adducts caused by inhaled formaldehyde is consistent with induction of nasal carcinoma but not leukemia

Inhaled formaldehyde is classified as a known human and animal carcinogen, causing nasopharyngeal cancer. Additionally, limited epidemiological evidence for leukemia in humans is available; however, this is inconsistent across studies. Both genotoxicity and cytotoxicity are key events in formaldehyde nasal carcinogenicity in rats, but mechanistic data for leukemia are not well established. Formation of DNA adducts is a key event in initiating carcinogenesis. Formaldehyde can induce DNA monoadducts, DNA-DNA cross-links, and DNA protein cross-links. In this study, highly sensitive liquid chromatography-tandem mass spectrometry-selected reaction monitoringmethods were developed and [(13)CD(2)]-formaldehyde exposures utilized, allowing differentiation of DNA adducts and DNA-DNA cross-links originating from endogenous and inhalation-derived formaldehyde exposure. The results show that exogenous formaldehyde induced N(2)-hydroxymethyl-dG monoadducts and dG-dG cross-links in DNA from rat respiratory nasal mucosa but did not form [(13)CD(2)]-adducts in sites remote to the portal of entry, even when five times more DNA was analyzed. Furthermore, no N(6)-HO(13)CD(2)-dA adducts were detected in nasal DNA. In contrast, high amounts of endogenous formaldehyde dG and dA monoadducts were present in all tissues examined. The number of exogenous N(2)-HO(13)CD(2)-dG in 1- and 5-day nasal DNA samples from rats exposed to 10-ppm [(13)CD(2)]-formaldehyde was 1.28 +/- 0.49 and 2.43 +/- 0.78 adducts/10(7) dG, respectively, while 2.63 +/- 0.73 and 2.84 +/- 1.13 N(2)-HOCH(2)-dG adducts/10(7) dG and 3.95 +/- 0.26 and 3.61 +/- 0.95 N(6)-HOCH(2)-dA endogenous adducts/10(7) dA were present. This study provides strong evidence supporting a genotoxic and cytotoxic mode of action for the carcinogenesis of inhaled formaldehyde in respiratory nasal epithelium but does not support the biological plausibility that inhaled formaldehyde also causes leukemia.

Derivation of an inhalation reference concentration based upon olfactory neuronal loss in male rats following subchronic acetaldehyde inhalation

Acetaldehyde inhalation induces neoplastic and nonneoplastic responses in the rodent nasal cavity. This experiment further characterizes the dose-response relationship for nasal pathology, nasal epithelial cell proliferation, and DNA-protein cross-link formation in F-344 rats exposed subchronically to acetaldehyde. Animals underwent whole-body exposure to 0, 50, 150, 500, or 1500 ppm acetaldehyde for 6 h/day, 5 days/wk for up to 65 exposure days. Respiratory tract histopathology was evaluated after 4, 9, 14, 30, and 65 exposure days. Acetaldehyde exposure was not associated with reduced body weight gain or other evidence of systemic toxicity. Histologic evaluation of the nasal cavity showed an increased incidence of olfactory neuronal loss (ONL) following acute to subchronic exposure to > or = 150 ppm acetaldehyde and increased olfactory epithelial cell proliferation following exposure to 1500 ppm acetaldehyde. The severity of the ONL demonstrated dose- and temporal-dependent behaviors, with minimal effects noted at 150-500 ppm acetaldehyde and moderately severe lesions seen in the highest exposure group, with increased lesion severity and extent as the exposure duration increased. Acetaldehyde exposure was also associated with inflammation, hyperplasia, and squamous metaplasia of the respiratory epithelium. These responses were seen in animals exposed to > or = 500 ppm acetaldehyde. Acetaldehyde exposure was not associated with increased DNA-protein cross-link formation in the respiratory or olfactory epithelium. A model of acetaldehyde pharmacokinetics in the nose was used to derive an inhalation reference concentration (RfC) of 0.4 ppm, based on the no-observed-adverse-effect level (NOAEL) of 50 ppm for the nasal pathology seen in this study.

The implausibility of leukemia induction by formaldehyde: a critical review of the biological evidence on distant-site toxicity

Formaldehyde is a naturally occurring biological compound that is present in tissues, cells, and bodily fluids. It is also a potent nasal irritant, a cytotoxicant at high doses, and a nasal carcinogen in rats exposed to high airborne concentrations. The normal endogenous concentration of formaldehyde in the blood is approximately 0.1 mM in rats, monkeys, and humans, and it is 2- to 4-fold higher in the liver and nasal mucosa of the rat. Inhaled formaldehyde enters the one-carbon pool, and the carbon atom is rapidly incorporated into macromolecules throughout the body. Oxidation to formate catalyzed by glutathione-dependent and -independent dehydrogenases in nasal tissues is a major route of detoxication and generally precedes incorporation. The possibility that inhaled formaldehyde might induce various forms of distant-site toxicity has been proposed, but no convincing evidence for such toxicity has been obtained in experimental studies. This review summarizes the biological evidence that pertains to the issue of leukemia induction by formaldehyde, which includes: (1) the failure of inhaled formaldehyde to increase the formaldehyde concentration in the blood of rats, monkeys, or humans exposed to concentrations of 14.4, 6, or 1.9 ppm, respectively; (2) the lack of detectable protein adducts or DNA-protein cross-links (DPX) in the bone marrow of normal rats exposed to [3H]- and [14C]formaldehyde at concentrations as high as 15 ppm; (3) the lack of detectable protein adducts or DPX in the bone marrow of glutathione-depleted (metabolically inhibited) rats exposed to [3H]- and [14C]formaldehyde at concentrations as high as 10 ppm; (4) the lack of detectable DPX in the bone marrow of Rhesus monkeys exposed to [14C]formaldehyde at concentrations as high as 6 ppm; (5) the failure of formaldehyde to induce leukemia in any of seven long-term inhalation bioassays in rats, mice, or hamsters; and (6) the failure of formaldehyde to induce chromosomal aberrations in the bone marrow of rats exposed to airborne concentrations as high as 15 ppm or of mice injected intraperitoneally with formaldehyde at doses as high as 25 mg/kg. Biological evidence that might be regarded as supporting the possibility of leukemia induction by formaldehyde includes: (1) the detection of cytogenetic abnormalities in circulating lymphocytes in seven studies of human subjects exposed to ambient concentrations in the workplace (but not in seven other studies of human subjects or in rats exposed to 15 ppm); (2) the induction of leukemia in rats in a single questionable drinking water study with formaldehyde concentrations as high as 1.5 g/L (but not in three other drinking water studies with concentrations as high as 1.9 or 5 g/L); (3) the detection of chromosomal aberrations in the bone marrow of rats exposed to very low concentrations of formaldehyde (0.4 or 1.2 ppm) (but not in another study at concentrations as high as 15 ppm); and (4) an apparent increase in the fraction of protein-associated DNA (assumed to be due to DPX) in circulating lymphocytes of humans exposed to ambient concentrations in the workplace (1-3 ppm). This evidence is regarded as inconsequential for several reasons, including lack of reproducibility, inadequate reporting of experimental methods, inconsistency with other data, or insufficient analytical sensitivity, and therefore, it provides little justification for or against the possibility that inhaled formaldehyde may be a leukemogen. In contrast to these inconclusive findings, the abundance of negative evidence mentioned above is undisputed and strongly suggests that there is no delivery of inhaled formaldehyde to distant sites. Combined with the fact that formaldehyde naturally occurs throughout the body, and that multiple inhalation bioassays have not induced leukemia in animals, the negative findings provide convincing evidence that formaldehyde is not leukemogenic.

DNA-protein crosslinks and p53 protein expression in relation to occupational exposure to formaldehyde

BACKGROUND

Formaldehyde (FA) is classified as a probable human carcinogen.

AIMS

To examine DNA protein crosslinks (DPC) and p53, which are generally known to be involved in carcinogenesis, in peripheral blood lymphocytes of workers exposed to FA.

METHODS

DPC and p53 ("wild type" and mutant) were examined in peripheral blood lymphocytes of 186 workers exposed to FA (mean years of exposure = 16) and 213 unexposed workers. Every worker completed a questionnaire on demographic data, occupational and medical history, smoking, and hygiene.

RESULTS

The adjusted mean level of DPC in the exposed and the unexposed workers differed significantly. Adjustment was made for age, sex, years of education, smoking, and origin. Exposure to FA increased the risk of having a higher level of pantropic p53 above 150 pg/ml (OR 1.6, 95% CI 0.8 to 3.1). A significant positive correlation was found between the increase of pantropic p53 protein and mutant p53 protein, as well as between pantropic p53 >150 pg/ml and mutant p53 protein. In the exposed group a significantly higher proportion of p53 >150 pg/ml was found among workers with DPC >0.187 (55.7%) (0.187 = median level of DPC) than among workers with DPC < or =0.187 (33.3%). The risk of having pantropic p53 protein >150 pg/ml was determined mainly by levels of DPC. Workers with DPC above the median level had a significantly higher risk of having pantropic p53 >150 pg/ml (adjusted OR 2.5, 95% CI 1.2 to 5.4).

CONCLUSIONS

Results suggest that DPC and mutation in p53 may represent steps in FA carcinogenesis and a possible causal relation between DPC and mutation in p53. These biomarkers can be applied in the assessment of the development of cancer due to FA exposure.

Genomewide demarcation of RNA polymerase II transcription units revealed by physical fractionation of chromatin

Epigenetic modifications of chromatin serve an important role in regulating the expression and accessibility of genomic DNA. We report here a genomewide approach for fractionating yeast chromatin into two functionally distinct parts, one containing RNA polymerase II transcribed sequences, and the other comprising noncoding sequences and genes transcribed by RNA polymerases I and III. Noncoding regions could be further fractionated into promoters and segments lacking promoters. The observed separations were apparently based on differential crosslinking efficiency of chromatin in different genomic regions. The results reveal a genomewide molecular mechanism for marking promoters and genomic regions that have a license to be transcribed by RNA polymerase II, a previously unrecognized level of genomic complexity that may exist in all eukaryotes. Our approach has broad potential use as a tool for genome annotation and for the characterization of global changes in chromatin structure that accompany different genetic, environmental, and disease states.

Structure-activity relationships in the induction of DNA-protein cross-links by hematotoxic ring-opened benzene metabolites and related compounds in HL60 cells

Previous studies from our laboratory have demonstrated the formation of DNA-protein cross-links (DNAPC), a potentially cytotoxic and genotoxic lesion induced by many leukemogenic agents, in bone marrow cells of mice administered benzene, however, reactive benzene metabolites involved in DNAPC formation by benzene have not been characterized. The present studies examined DNA PC formation in HL60 cells treated with trans,trans-muconaldehyde (MUC), a hematotoxic ring-opened metabolite of benzene, as well as with MUC metabolites and structurally related compounds. Using a K(+)/SDS precipitation assay for DNAPC determination, concentration- and time-dependent increases in DNAPC formation were observed 2 and 4 h after treatment of HL60 cells with 50, 75 and 100 microM MUC. No increases in DNAPC levels were measured in HL60 cells 4 h after treatment with the MUC metabolites 6-hydroxy-trans,trans-2,4-hexadienal (HO-M-CHO), 6-oxo-trans,trans-2,4-hexadienoic acid (CHO-M-COOH), or trans,trans-muconic acid (HOOC-M-COOH), each at 100 microM. Significant increases in DNAPC levels were observed 4 h after treatment with 500 and 1000 microM HO-M-CHO, but not CHO-M-COOH. No effect on DNAPC levels was observed 4 h after treatment with 100 microM for trans, trans-2,4-hexadienal, trans-2-hexenal, hexanal, trans,trans-2, 4-hexadiene, glutaraldehyde, or acrolein. DNAPC induced by MUC and HO-M-CHO may be cytotoxic lesions, as increases in DNAPC levels by these compounds correlated with decreases in cell viability. Except for acrolein, compounds not inducing DNAPC at 100 microM also did not affect cell viability. These studies suggest that both aldehydic carbons of MUC contribute to DNAPC induction, and that the presence of alpha,beta-unsaturated double bonds conjugated with the aldehyde groups increases the ability of MUC to induce DNAPC relative to the saturated dialdehyde glutaraldehyde.

Mitogenic responses of rat nasal epithelium to hexamethylphosphoramide inhalation exposure

Hexamethylphosphoramide (HMPA) is a rat nasal carcinogen that induces squamous cell carcinomas in the anterior portions of the nasal cavity following chronic inhalation exposures as low as 50 ppb. These tumors may arise as a result of P-450-mediated release of formaldehyde (HCHO), a known rat nasal carcinogen. The goal of this research was to investigate early responses of the nasal epithelium to inhaled HMPA. Rats were exposed nose-only to approximately 3 ppm HMPA for 6 h, and killed 18, 48, 96 or 144 h post-exposure. In a separate study, rats were exposed nose-only for 6 h for 1, 2, 3, or 5 consecutive days and killed 18 or 96 h post-exposure. With both single and repeated doses of HMPA, there was no evidence of cytotoxicity in the anterior nose. Olfactory degeneration and necrosis of the dorsal meatus, Bowman's glands and tips of the ethmoid turbinates increased in severity with repeated exposures to HMPA. Cell proliferation was assessed in levels of nasal tissue that included regions of squamous, respiratory, transitional and olfactory epithelium. Regional induction of cell proliferation was measured by BrdU incorporation, and reported as the number of labeled cells/mm basement membrane. At 18 h after a single exposure, there was an increase in cell proliferation in squamous epithelium, which returned to control levels within 48 h. A transitory increase in cell proliferation was observed regions of respiratory and transitional epithelium, although the response of each tissue, in terms of magnitude and peak time of response post-exposure, also differed. Along the dorsal meatus in Level 9, olfactory labeling initially decreased, returned to control levels by 96 h, but again declined at 144 h post-exposure. In repeat dose studies, the squamous epithelium response was variable 18 h post-exposure. For respiratory and transitional epithelium, increased cell proliferation 18 h post-exposure was correlated with increased dose (exposure) of HMPA. Cell proliferation responses following two or more exposures returned to near control levels within 96 h post-exposure. In conclusion, HMPA induced cell proliferation, but not cytotoxicity, in the anterior nose at approximately 3 ppm. These data suggest that HMPA induces proliferative, perhaps mitogenic, responses in the nasal epithelium, and this response may facilitate the fixation of low level genetic damage induced by liberated HCHO.

DNA damage in the nasal passageway: a literature review

The purpose of this review is to provide a compilation of work examining DNA damage in the nasal cavity. There are numerous methods to identify and quantify damage to DNA and the diversity of methods and toxicologic endpoints is illustrated by the range of studies presented here. There are a large number of independent studies measuring endpoints in the upper respiratory tract; however, with regard to toxicant induced DNA damage in the nasal passageway, the effects of two compounds, 4-(N-Methyl-N-nitrosamino)-1-(3-pyridyl)-1-butanone (NNK) and formaldehyde (HCHO), appear to have been extensively characterized. The body of work on NNK and formaldehyde have provided insights into molecular mechanisms of DNA damage and repair and induced cell replication and its relationship to nasal cancer. With new technologies and molecular techniques, the sensitivity to enable evaluations of the minute quantities of nasal tissue available in test species and human biopsy impact the study of the nasal-toxicant interactions. As methods used to characterize DNA damage increase in sensitivity, the importance of both exogenous and endogenous sources of DNA damage, steady-state levels of cellular damage, repair, and resulting mutations, low-dose exposure assessments and inter-species extrapolation will become increasingly complex. Additional studies of DNA damage in the nasal passage will undoubtedly challenge future estimations of risk and impact what are perceived to be acceptable levels of exposure to known and predicted carcinogens. The aim of this paper is to provide to the interested scientist literature relevant to the effects of agents on nasal DNA, so that areas of insufficient information can be identified and used to further develop and expand the knowledge base for nasal DNA toxicant interactions.

Dosimetry, toxicity and carcinogenicity of inspired acetaldehyde in the rat

Acetaldehyde is a ubiquitous air pollutant. It is an important industrial chemical and is also produced during the combustion of wood or tobacco. In smoky indoor atmospheres concentrations of the aldehyde may reach 100 ppb. Acetaldehyde is metabolized to acetate (releasing hydrogen ion) by aldehyde dehydrogenase a process which, in most tissues, represents a detoxification pathway. In vitro, acetaldehyde forms DNA-DNA and DNA-protein crosslinks. It is a clastogen, and inducer of sister chromatid exchanges, and is, perhaps, a weak mutagen. Inhalation exposure to 1000 ppm may induce DNA-protein crosslink formation in nasal tissues in the rat in vivo. Inhalation toxicity studies have shown acetaldehyde vapor causes chronic tissue injury and tumor formation in nasal tissues at exposure concentrations of 750 ppm or higher, with nasal olfactory mucosa being more sensitive than respiratory mucosa. Dosimetric estimates suggest that marked tissue injury and carcinogenicity occurs only at inspired concentrations which are sufficiently high to overwhelm nasal aldehyde dehydrogenase detoxification capacity. The induction of squamous cell carcinomas in the respiratory mucosa by acetaldehyde displays many analogies to the induction of squamous cell carcinomas by formaldehyde. For both vapors, non-linear concentration response relationships are observed for DNA-protein crosslink formation, tissue injury, and carcinogenicity, suggesting these responses are associated. For both vapors it is possible to document an exposure concentration that produces nasal respiratory epithelial injury without increasing tumor incidence, suggesting that for respiratory mucosa-derived tumors, exposure to non-cytotoxic concentrations may pose limited carcinogenic risk. In addition to squamous cell carcinomas of the respiratory epithelium, acetaldehyde exposure also results in nasal olfactory injury and tumors (adenocarcinomas) in the rat. The studies performed to date have not demonstrated a no observable effect level for these responses, therefore, the precise role of cytotoxicity and regenerative cell proliferation in the carcinogenic process in olfactory tissues can not be evaluated. Acetaldehyde metabolism via aldehyde dehydrogenase results in the formation of two hydrogen ions. The olfactory mucosa is quite sensitive to acid and dosimetric estimates suggest that the intracellular acid production rates that may occur in olfactory mucosa during acetaldehyde exposure may be sufficiently high to cause tissue damage. Such acid-induced tissue damage may enhance the genotoxic and tumorigenic potential of acetaldehyde in olfactory mucosa, and may, therefore, represent an important process in the production of tumors in this tissue.

A brief review of formaldehyde carcinogenesis in relation to rat nasal pathology and human health risk assessment

The 1980 report that inhaled formaldehyde induced nasal squamous cell carcinomas in rats had a significant societal impact and resulted in extensive research in the fields of rodent nasal pathology and human cancer risk assessment. This article presents an overview of the evolution of these events. It is concluded that the nasal passages of humans and rats are fundamentally identical biological target organs. Nevertheless, in the case of human health risk assessment, minor differences between these species may be critically important. Special attention should be paid to interspecies differences in nasal dosimetry and local metabolism; thus, chemical toxicity data derived from rats require careful interpretation when used for human risk assessments. In the case of formaldehyde, it is recommended that low-concentration (< or = 2 ppm airborne exposure) extrapolation, where no tissue damage is observed, be uncoupled from the responses at high concentrations (> or = 6 ppm), where epithelial degeneration, regenerative cell replication, and inflammation appear to be essential driving forces in formaldehyde carcinogenesis. The presence of treatment-related nasal lesions in rats following exposure to chemicals should always be treated as an indication of a potential human health risk, whether exposure is by the inhalation, oral, or dermal route.

DNA-Protein Crosslinks and Sister Chromatid Exchanges as Biomarkers of Exposure to Formaldehyde

Formaldehyde is classified as a probable human carcinogen. DNA-protein crosslinks (DPCs) and sister chromatid exchanges (SCEs) may represent early lesions in the carcinogenic process. The authors examined the DPCs and SCEs in peripheral-blood lymphocytes of 12 and 13 workers exposed to formaldehyde and eight and 20 unexposed workers, respectively. The amounts of DPCs and SCEs in the exposed and the unexposed differed significantly after adjustment for smoking. There was a linear relationship between years of exposure and the amounts of DPC and SCE. The authors conclude that the data indicate a possible mechanism of carcinogenicity of formaldehyde, and that formaldehyde is mutagenic to humans. These results support the use of DPCs as a biomarker of occupational exposure to formaldehyde and to detect high-risk populations for secondary prevention.

DNA-protein crosslink formation in rat nasal epithelial cells by hexamethylphosphoramide and its correlation with formaldehyde production

Hexamethylphosphoramide (HMPA) is an aprotic polar solvent and nasal carcinogen in rats. The metabolism of HMPA to formaldehyde, another nasal carcinogen in rats, was found to be approximately 6 times greater in microsomes from olfactory tissues than from respiratory tissues (isolated from both male and female rats). HMPA was shown to induce formation of DNA-protein crosslinks (DPXLS) in isolated rat nasal epithelial cells. Using a filter binding assay, we demonstrated that microsomal activation is necessary for HMPA-induced crosslink formation between plasmid DNA and calf thymus histones, presumably through metabolic N-demethylation of HMPA and the formation of formaldehyde. Both formaldehyde production and DPXL formation were inhibited by pre-incubation of nasal mucosal extracts with metyrapone, an inhibitor of cytochrome P-450. Significant dose-dependent increases in DPXL formation were observed in respiratory and olfactory epithelial cells exposed to > or = 0.5 and 1 mM HMPA, respectively, for 3 h at 37 degrees C. This resulted in DPXL accumulation at 18-20% higher levels than untreated cells. Increases in DPXL formation in rat nasal epithelial cells cultured with 1 mM HMPA were inhibited by over 70% by co-administration of metyrapone. These data suggest that metabolic liberation of formaldehyde from HMPA is involved in the mechanism of HMPA-induced nasal carcinogenesis. Comparative studies showed formaldehyde to be more potent than HMPA in the induction of DPXL in nasal epithelium. However, induction of tumor formation after two years at 50 ppb HMPA and 6 ppm formaldehyde show the former to be active at several-fold lower concentrations. Therefore, other mechanisms are likely to be involved in HMPA nasal carcinogenesis.

DNA damage in lung cells in vivo and in vitro by 1,3-butadiene and nitrogen dioxide and their photochemical reaction products

A UV-irradiated mixture of 1,3-butadiene and nitrogen dioxide (NO2) was tested for its potency to induce DNA damage measured as single-strand breaks (SSB) in lungs of mice. Both gases were also tested separately. After 16 h exposure a UV-irradiated mixture of 40 ppm butadiene + 20 ppm NO2, but not 20 ppm butadiene + 10 ppm NO2 + UV, induced a significant increase in SSB as measured by the alkaline unwinding technique. There was no increase in the level of SSB using the alkaline elution technique during the same testing conditions. However, after 5 h exposure to 60 ppm butadiene + 30 ppm NO2 + UV both methods demonstrated a significant increase in SSB. Mice were also exposed to butadiene at 80 and 200 ppm for 16 h and at 500 ppm for 5 h. DNA damage was demonstrated in both liver and lung after 5 and 16 h (only at 200 ppm) of exposure using the unwinding technique. Using the alkaline elution assay, a significant increase in the level of SSB in lung and liver was found only after 5 h of exposure. When mice were exposed to 30 ppm NO2 for 16 h or 50 ppm for 5 h, a significant increase in SSB was found with the unwinding technique. Alveolar macrophages from mice were also exposed in vitro to the gas mixture and to butadiene and NO2 separately. In these experiments, the DNA damage was studied with the unwinding technique. A significant effect was demonstrated with 40 ppm butadiene + 20 ppm NO2 + UV. NO2 itself contributed to some extent to the increase. Reasons for the discrepancies between the unwinding and the alkaline elution techniques are discussed.

Formation and stability of acetaldehyde-induced crosslinks between poly-lysine and poly-deoxyguanosine

The amino acid residue and nucleoside specificity of acetaldehyde-induced DNA-protein crosslinks (DPXLs) were studied using a modified filter binding assay. A 40% inhibition of acetaldehyde-induced pUC13 plasmid DNA-calf thymus histone crosslink formation was achieved by addition of 50 mM lysine (free base), while arginine was unable to affect crosslink formation at concentrations to 150 mM. Polymers (5-mers) of lysine (poly-lys5) were able to substitute for histones in acetaldehyde-induced plasmid crosslink formation, being equally effective at equimolar concentrations. Homopolymers (6-mers) of deoxyguanosine (poly-dG6) (but not deoxyadenosine, deoxycytidine or thymidine) served as an efficient substrate for acetaldehyde-induced DPXL formation, using either calf thymus histones or poly-lys5 as the protein source. Acetaldehyde-induced crosslinks between poly-dG6 and poly-lys5 were formed rapidly, but were unstable at 37 degrees C (a half-life or 1.5-2 h). Stability of these crosslinks was unaffected by pH at a range of 5.5-9.0 at 37 degrees C for 2 h. Results presented here suggest that unstable complexes of deoxyguanosine and lysine constitute a major portion of the DPXLs formed by acetaldehyde in vitro.

The role of formaldehyde and S-chloromethylglutathione in the bacterial mutagenicity of methylene chloride

Methylene chloride was less mutagenic in Salmonella typhimurium TA100/NG-11 (glutathione-deficient) compared to TA100, indicating that glutathione is involved in the activation of methylene chloride to a mutagen in bacteria. In rodents, the pathway of methylene chloride metabolism utilizing glutathione produces formaldehyde via a postulated S-chloromethylglutathione conjugate (GSCH2Cl). Formaldehyde is known to cause DNA-protein cross-links, and GSCH2Cl may act as a monofunctional DNA alkylator by analogy with the glutathione conjugates of 1,2-dihaloalkanes. The lack of sensitivity of Salmonella TA100 towards formaldehyde (Schmid et al., Mutagenesis, 1 (1986) No. 6, 427-431) suggests that GSCH2Cl is responsible for methylene chloride mutagenicity in Salmonella. In Escherichia coli K12 (AB1157), formaldehyde was mutagenic only in the wild-type, a characteristic shared with cross-linking agents, whereas 1,2-dibromoethane (1,2-DBE) was more mutagenic in uvrA cells (AB1886). Methylene chloride, activated by S9 from mouse liver, was mutagenic only in wild-type cells, suggesting a mutagenic role for metabolically derived formaldehyde in E. coli. Mouse-liver S9 also enhanced the cell-killing effect of methylene chloride in the uvrA, and a recA/uvrA double mutant (AB2480) which is very sensitive to DNA damage. This pattern was consistent with formaldehyde damage. However, a mutagenic role in bacteria for the glutathione conjugate of methylene chloride cannot be ruled out by these E. coli experiments because S9 fractions did not increase 1,2-DBE mutagenicity, suggesting lack of cell wall penetration by this reactive species. Rat-liver S9 did not activate methylene chloride to a bacterial mutagen or enhance methylene chloride-induced cell-killing, which is consistent with the carcinogenicity difference between the species.

Efficiency of DNA-histone crosslinking induced by saturated and unsaturated aldehydes in vitro

Using a filter-binding assay based on precipitation of pUC13 plasmid DNA bound to calf-thymus histones, we have determined the efficiency of formation of DNA-protein crosslink formation induced by several aldehyde compounds in vitro. Formaldehyde, glutaraldehyde and acrolein were the most potent, causing 1 crosslink per 2.7 kbp of DNA at 1.5, 8 and 150 microM, respectively. All other compounds tested gave 1 crosslink per plasmid molecule in the mM concentration range as follows: acetaldehyde, 115 mM; propionaldehyde, 295 mM; butyraldehyde, 360 mM; crotonaldehyde, 8.5 mM; trans-2-pentenal, 6.3 mM. Significant decreases in the efficiency of DPXL formation were observed with monofunctional aldehydes of higher carbon chain length. For example, the concentration of formaldehyde needed to give 1 crosslink per molecule was almost 10(5) times less than that of acetaldehyde. Acetaldehyde differs from formaldehyde only by one saturated carbon. The presence of an unsaturated bond between the 2-3 carbons improved the potential for crosslink formation. For example, acrolein was over 500-fold more potent than propionaldehyde. Glutaraldehyde was almost as potent as formaldehyde, indicating that the bifunctional nature of this 5-carbon saturated aldehyde may be crucial to its high efficiency of DNA-protein crosslinking.

Ciliated respiratory epithelial surface changes after formaldehyde exposure

The investigation sought to identify alterations of specific ciliated epithelial surface components after exposure to formaldehyde (HCHO) levels that decrease respiratory ciliary function. Bovine tracheae were reacted with an analog of N-hydroxysuccinimidobiotin to label epithelial surface-accessible components before exposure to HCHO. The tracheae were then exposed to 0, 16, 33, and 66 micrograms HCHO/cm2 epithelial surface for 30 min. Cilia were isolated from the epithelium, separated into membrane and internal axonemal portions, analyzed on sodium dodecyl sulfate-polyacrylamide gel electrophoresis (SDS-PAGE), and either stained to detect proteins or transblotted to detect biotin-labeled components. Densitometric analysis of axoneme proteins showed a decrease in the total amount extracted with increased HCHO concentration, including axoneme-specific proteins, dynein, and tubulin. However, biotinylated proteins in the axoneme fractions proportionately increased. Membrane fractions showed little change in protein with increasing HCHO concentration. The majority of these is not biotin-labeled and thus not surface-accessible components. Biotinylated material in the membrane fractions showed a significant decrease with increased HCHO concentration, particularly of bands at 92, 98, and 105 kD. These data suggest that increasing HCHO exposure reduces both extractable ciliary axonemes and detergent-soluble surface components, possibly by stabilizing respiratory epithelial membranes. This process apparently strengthens association of certain surface components with the internal axoneme, thereby reducing subsequent solubilization in detergent.

Histochemical localization of formaldehyde dehydrogenase in the rat

Formaldehyde dehydrogenase (FDH) activity has been demonstrated biochemically in the olfactory and respiratory mucosae and in the liver of the rat, but the cellular localization of this enzyme has not been investigated. A histochemical procedure was developed to permit cellular localization of FDH. This allowed us to examine the relationship between distribution of FDH and formaldehyde-induced toxicity. Cold-processed glycol methacrylate embedded tissues were used to localize FDH activity in the rat respiratory tract, kidney, liver, and brain. Five- or ten-micrometer tissue sections were incubated in a reaction mixture containing formaldehyde (HCHO), glutathione (GSH), NAD+, nitroblue tetrazolium, pyrazole, and disulfiram. A blue formazan precipitate was formed at the site of FDH activity. Epithelial cell cytoplasm of both the respiratory and the olfactory mucosae of the nose stained for FDH, and olfactory sensory cell nuclei were also positive. Underlying Bowman's and seromucous glands were weakly positive. The lung had FDH activity located mainly in the Clara cells of the airways, with only diffuse weak activity in the lung parenchyma. Liver had activity in the cytoplasm of the hepatocytes, while in the kidney FDH was most prominent in the brush border of the P2 segment of the proximal tubules. Brain white matter stained strongly for FDH, while in gray matter only the neuropil exhibited weak activity. Corresponding tissue sections were stained for sulfhydryls; these sections indicated that GSH is likely to be present in all cells with FDH activity. For the respiratory tract these results demonstrate distinct differences between the location of FDH activity and previously reported nonspecific aldehyde dehydrogenase activity in the nose (M. S. Bogdanffy, H. W. Randall, and K. T. Morgan, 1986, Toxicol. Appl. Pharmacol. 82, 560-567). While high aldehyde dehydrogenase activities were found in tissues with low toxicities due to acetaldehyde exposure and vice versa, FDH activity was observed in tissues whether or not they exhibited a toxic response to inhaled HCHO. While not able to account for the localized toxicity of HCHO, the presence of FDH and glutathione in the epithelial layer of the nasal cavity presents a barrier to inhaled formaldehyde at low concentrations and may partially explain the observed nonlinearity of HCHO toxicity.

Inhibition and recovery of mammalian respiratory ciliary function after formaldehyde exposure

Formaldehyde (HCHO) has been reported to impair mucociliary clearance. The present investigation using rabbit and porcine tracheal explants in vitro examined (1) the impairment of ciliary activity, an essential component of mucociliary clearance; (2) the reversibility of ciliary dysfunction after HCHO exposure; and (3) the mechanism by which ciliary activity is reduced by HCHO. HCHO treatment of rabbit tracheal rings significantly decreased zones of active ciliated epithelium in direct proportion to concentration and exposure duration. There was also a significant concentration-dependent reduction of ciliary beat frequency. Removal of HCHO permitted recovery of zones of ciliary activity to normal beat frequencies; greater inhibitory concentrations of HCHO required greater time for return of function. Treatment of porcine tracheae with increasing concentrations of HCHO for time periods inhibitory to rabbit ciliary activity correspondingly reduced the yield of cilia extractable from treated epithelium. Furthermore, the specific activity of ATPase of extracted ciliary axonemes was diminished with increasing HCHO concentration, indicating loss of function. A recovery period following identical exposures of the porcine tracheae to the lower HCHO concentrations resulted in normal yields of functionally intact ciliary axonemes. Similarly, a recovery period after the highest HCHO concentration produced more functional axonemes than obtained from exposed tracheae without a recovery period, although less than normal yields. Therefore, ciliary dysfunction elicited by a defined range of HCHO concentrations is reversible. The yield and functional integrity of ciliary axonemes from epithelium exposed to HCHO with a recovery period are significantly greater than those without such a recovery period, suggesting an alteration and subsequent repair of epithelial surface components following HCHO exposure.

Covalent binding of [14C]-2,6-dimethylaniline to DNA of rat liver and ethmoid turbinate

The xylidide 2,6-dimethylaniline (2,6-DMA) has produced carcinomas and papillary adenomas in the nasal cavity of rats at high dietary doses (3000 ppm) in a 2-yr bioassay. The objective of the present study was to measure the covalent binding of 2,6-DMA to DNA of rat ethmoid turbinate tissues and, for comparison, to DNA of rat liver. The potent hepatocarcinogen 2-acetylaminofluorene (AAF) was studied as a positive control for adduct formation and covalent binding index (CBI) calculation. Both 2,6-DMA and AAF were administered as 14C-(ring)-labeled agents to naive rats and to rats pretreated for 9 d with unlabeled 2,6-DMA or AAF. The CBI value for 2,6-DMA adduct formation with ethmoid turbinate DNA was below the assay's sensitivity limit in nonpretreated rats, but increased to 41.9 in rats pretreated with unlabeled 2,6-DMA. It also increased from 0.6 in nonpretreated to 7.9 in liver of pretreated rats. The opposite pattern, however, was observed for AAF. In nonpretreated rats considerable adduct formation was observed in liver (CBI = 271.5) and modest values (CBI = 39.3) were calculated for ethmoid turbinate tissues. Pretreatment with unlabeled AAF caused a significant decrease in CBI values, to 18.3 for liver and less than 0.5 for ethmoid turbinate. The results suggest that there may be value in conducting DNA covalent binding assays in both naive animals and animals pretreated with the test article.

A mutagenicity assessment of acetaldehyde

Acetaldehyde has been shown in studies by several different laboratories to be a clastogen (chromosome-breaking) and inducer of sister-chromatid exchanges in cultured mammalian cells (Chinese hamster cells and human lymphocytes). Although there have been very few studies in intact mammals, the available evidence suggests that acetaldehyde produces similar cytogenetic effects in vivo. The production of cytogenetic abnormalities may be related to the ability of acetaldehyde to form DNA-DNA and/or DNA-protein cross-links. Acetaldehyde apparently has not been evaluated for its ability to cause gene mutations in cultured mammalian cells, but it has been shown to produce sex-linked recessive lethals in Drosophila. In general, bacteria tests have been negative. Although acetaldehyde is a genotoxic cross-linking agent, it does not appear to cause DNA strand breaks. There were no studies available regarding the potential of acetaldehyde to produce genetic damage in mammalian germ cells in vivo. Most mutagenicity testing on acetaldehyde has been motivated by attempts to define the proximate mutagen in ethanol metabolism.

Further studies of the metabolic incorporation and covalent binding of inhaled [3H]- and [14C]formaldehyde in Fischer-344 rats: effects of glutathione depletion

Glutathione (GSH) is required for the oxidation of formaldehyde (HCHO) to formate catalyzed by formaldehyde dehydrogenase (FDH). The effects of GSH depletion on the mechanisms of labeling of macromolecules in the rat nasal mucosa and bone marrow by 3HCHO and H14CHO were investigated. Male rats were exposed for 3 hr to atmospheres containing 3HCHO and H14CHO at concentrations of 0.9, 2, 4, 6, or 10 ppm, 1 day after a single 3-hr preexposure to the same concentration of unlabeled HCHO. Two hours prior to the second exposure, the animals were injected either with phorone (300 mg/kg, ip) or with corn oil. The concentration of nonprotein sulfhydryls in the nasal respiratory mucosa of phorone-injected rats was decreased to 10% of that of corn oil-injected rats. The metabolic incorporation of 3HCHO and H14CHO into DNA, RNA, and proteins in the respiratory and olfactory mucosa and bone marrow (femur) was significantly decreased, and DNA-protein crosslinking was significantly increased in the respiratory mucosa of phorone-injected relative to corn oil-injected rats at all HCHO concentrations. DNA-protein crosslinks were not detected in the respiratory mucosa of corn oil-injected rats at 0.9 ppm. Evidence was obtained for the formation of adducts of HCHO with the RNA from the nasal respiratory mucosa of phorone-injected rats at concentrations above 0.9 ppm. Covalent binding of HCHO to macromolecules in the bone marrow was not detected. These results indicate that the GSH-dependent oxidation of HCHO catalyzed by FDH is an important defense mechanism against the covalent reactions of HCHO with nucleic acids in the respiratory mucosa. Experiments using phorone-injected rats exposed to 10 ppm of [3H]- and [14C]formaldehyde showed that the DNA from the respiratory mucosa was enriched in 3H relative to 14C in comparison to the inhaled vapor. The enrichment is explained by an isotope effect in the oxidation of 3HCHO and H14CHO (H. d'A, Heck and M. Casanova (1987). Toxicol. Appl. Pharmacol. 89, 122-134), which results in 3H enrichment of the residual (unoxidized) HCHO that binds to DNA. A non-linear pharmacokinetic model is proposed that depicts the potential effects of FDH saturation on the relative concentrations of intracellular to extracellular HCHO.

Experimental toxicology of formaldehyde

Formaldehyde is a reactive chemical which undergoes spontaneous reactions with various cellular constituents. Mutagenicity data may be interpreted on the background of this behavior. Mice are better able to reduce the irritating effect of formaldehyde than rats and to reduce their ventilation rate when formaldehyde acts on the respiratory tract. Subacute exposure of rats to concentrations higher than 2 ppm inhibits mucociliary clearance of the nasal epithelium and leads to progressive histological and ultrastructural lesions at this site. The occurrence of squamous cell carcinomas of the nasal epithelium of rats after 2 years inhalation of 14.3 ppm formaldehyde (CIIT study) is probably the result of chronic and recurrent local toxicity; this is supported by species differences in susceptibility to the tissue damaging and carcinogenic effect of formaldehyde (rat, mouse, hamster). Data on formaldehyde-DNA interaction further support the argument that a direct risk extrapolation from the formaldehyde effects in rats to those expected for man is not possible.

Establishment of a rat nasal epithelial tumor cell line

A new cell line designated NAS 2BL has been established from a rat nasal tumor induced by inhalation of the direct-acting carcinogen methylmethane sulfonate. The cells are epithelial in morphology, have a generation time of 34 h, require 10% fetal bovine serum for optimal growth, and exhibit keratinization at confluence. The karyotype is aneuploid, with several marker chromosomes, and the cells are transformed by the criterion of nude mouse tumorigenicity.

Formaldehyde mutagenesis and formation of DNA-protein crosslinks in human lymphoblasts in vitro

Human lymphoblasts were exposed in vitro to various concentrations of formaldehyde (HCHO) in single and multiple treatment regimens to determine relative mutagenic efficiency. Single treatments of HCHO (0-150 microM X 2 h) resulted in a nonlinear increase in induced mutant fraction at the thymidine kinase locus with increasing slope at concentrations above 125 microM. Only HCHO exposures of 125 microM X 2 h or greater produced significant effects on the growth rate of the lymphoblasts. Cultures were also exposed to either three treatments of 50 microM X 2 h, five treatments of 30 microM X 2 h, or ten treatments of 15 microM X 2 h; multiple treatments were administered on different days. These multiple treatments resulted in increases in mutant fraction, although their combined effect was less than a single treatment of equivalent concentration X time (150 microM X 2 h). Exposure of lymphoblasts to four treatments of 150 microM X 2 h HCHO failed to induce mutations at the ouabain resistance locus. Cultures of lymphoblasts receiving a single treatment of HCHO (0-600 microM X 2 h) were analyzed by the alkaline elution technique to detect the presence of DNA-protein crosslinks. HCHO treatment resulted in a significant nonlinear increase in DNA-protein crosslinks at concentrations greater than 50 microM X 2 h, which correlated with the onset of significant toxicity in this cell line. Holding the culture for 24 h resulted in complete removal of the crosslinks. These data indicate that both the induction of mutations and the formation of DNA-protein crosslinks by HCHO are nonlinear functions in human lymphoblasts and occur at overlapping concentration ranges.

Endogenous formaldehyde does not produce detectable DNA-protein crosslinks in rat liver

Formaldehyde is an electrophilic molecule able to crosslink DNA and protein. It has been found to induce tumors in the nasal epithelium in rodents. The safety margin between the maximum tolerated FA concentration in the work place and the concentration found to be tumorigenic in animal studies is very small. Because FA is produced endogenously as a result of a variety of oxidative demethylations, the assessment of the tumor risk from exogenous FA exposure has to be related quantitatively to the level of DNA-protein crosslinks induced by endogenous FA generation. It is reported here that the high level of endogenous FA formed in the liver after a large dose of methanol or of aminopyrine did not lead to any observable increase in DNA-protein crosslinks. Using positive and negative control data from in vitro incubations of liver homogenate with FA or methanol it is estimated that the endogenous level of DNA damage in the liver must be more than three orders of magnitude below the damage observed at tumorigenic concentrations for the rat nose. The fact that FA is formed endogenously cannot, therefore, be used to claim that exogenous FA merely leads to a negligible increase in DNA damage.

Depletion of nasal mucosal glutathione by acrolein and enhancement of formaldehyde-induced DNA-protein cross-linking by simultaneous exposure to acrolein

Incubation of homogenates of rat nasal mucosa with acrolein resulted in the apparent formation of DNA-protein cross-links. However, inhalation exposure of male Fischer-344 rats to acrolein (2.0 ppm, 6 h) did not cause detectable DNA-protein cross-linking in the nasal respiratory mucosa. Simultaneous exposure of rats to both acrolein (2.0 ppm) and formaldehyde (6.0 ppm) for 6 h resulted in a significantly higher yield of DNA-protein cross-links than was obtained following exposure to formaldehyde (6.0 ppm) alone. Acrolein exposure at concentrations of 0.1, 0.5, 1.0, or 2.5 ppm resulted in a concentration-dependent depletion of nonprotein sulfhydryl groups in the nasal respiratory mucosa. A plausible explanation for the enhancement of DNA-protein cross-links by simultaneous exposure to formaldehyde and acrolein may be that depletion of glutathione by acrolein inhibited the oxidative metabolism of formaldehyde, leading to an increase of formaldehyde-induced DNA-protein cross-links.

Formaldehyde-induced sister chromatid exchanges in vitro and the influence of the exogenous metabolizing systems S9 mix and primary rat hepatocytes

Formaldehyde-induced sister chromatid exchanges (SCE) in vitro and the influence of the exogenous metabolizing systems, S9 mix and primary rat hepatocytes, were studied. The SCE-frequency in V79 cells was dose dependent. A three- to four-fold increase at non-toxic doses was observed. However, in the presence of an exogenous metabolizing system, the number of formaldehyde-induced SCE decreased. S9 mix as well as hepatocytes reduced the SCE frequency to nearly that of the control range. It could be demonstrated that the reduction was not due to an unspecific binding of formaldehyde to macromolecules of the added S9 mix. The decrease in genotoxic effects, due to rapid metabolisation of formaldehyde in vitro and in vivo, explains the differences between results obtained in the in vitro experiments--performed without metabolizing systems--and in vivo results.

The role of mechanistic data in dose-response modeling

The results from employing metabolized dose in the case of vinyl chloride demonstrate that the delivered dose concept can radically alter the shape of the dose-response curve in the observable response range. Simultaneously, it can eliminate the obvious bias in low-dose risk estimates that arises from use of an inappropriate dose measure, namely, the administered airborne vinyl chloride concentration. For formaldehyde, the data regarding covalent binding to respiratory mucosal DNA provide the best measure of target tissue exposure that is currently available. The results obtained with this dose measure demonstrate that incorporation of the delivered dose concept into any of the commonly used low-dose extrapolation procedures leads to a unilateral reduction in estimated cancer risk associated with the exposure of rats to low airborne formaldehyde concentrations. These findings strongly suggest that low-dose risk estimates obtained with the administered formaldehyde dose as the measure of exposure are biased conservatively, and that regulatory assessments of formaldehyde should consider the delivered formaldehyde dose to be the valid and relevant measure of exposure. Additional research is, of course, required to refine and elaborate the delivered dose concept, especially for human exposures. Nevertheless, this concept provides a convenient vehicle for incorporating mechanistic information directly into the quantitative risk assessment process in a meaningful and relevant manner. Clearly, risk estimates based on delivered dose reflect what is known of the underlying biological reality more faithfully than estimates that are based solely on unverified assumptions and the findings in chronic bioassays. Use of the delivered dose concept should be strongly encouraged, since it can help place quantitative risk assessment on a sound and scientifically defensible footing.

Differentiation between metabolic incorporation and covalent binding in the labeling of macromolecules in the rat nasal mucosa and bone marrow by inhaled [14C]- and [3H]formaldehyde

The mechanisms of labeling of macromolecules (DNA, RNA, and protein) in the respiratory and olfactory mucosa, and in the bone marrow (femur) of male Fischer-344 rats exposed to [14C]- and [3H]formaldehyde [( 14C]- and [3H]CH2O) were investigated. Animals were exposed for 6 hr to atmospheres containing [14C]- and [3H]CH2O at concentrations of 0.3, 2, 6, 10, or 15 ppm, 1 day following a single pre-exposure to the same concentration of unlabeled CH2O. The major route of nucleic acid labeling at all concentrations and in all tissues was metabolic incorporation; protein labeling in the respiratory mucosa was mainly due to covalent binding at the higher CH2O concentrations. Incorporation of [14C]CH2O into DNA in the respiratory mucosa was maximal at 6 ppm but decreased at higher concentrations, whereas labeling of DNA in the olfactory mucosa and bone marrow increased monotonically with concentration. Evidence for covalent binding of CH2O to respiratory mucosal DNA was obtained at CH2O concentrations equal to or greater than 2 ppm. The concentration of CH2O covalently bound to DNA at 6 ppm was 10.5-fold higher than at 2 ppm, indicating significant nonlinearity of DNA binding with respect to the inhaled formaldehyde concentration under these conditions. Covalent binding to proteins increased in an essentially linear manner with increases in the airborne concentration. No evidence was obtained for the formation of covalent adducts with macromolecules in the olfactory mucosa or bone marrow. The nonlinear increase in covalent binding to respiratory mucosal DNA with increasing CH2O concentrations may be explained either by a decrease in the efficiency of defense mechanisms or by an increase in the availability of reaction sites on the DNA resulting from increased cell turnover.