Use of the random amplif|ed polymorphic DNA (RAPD) assay for the detection of DNA damage and mutations: possible implications of confounding factors

The aim of this study was to evaluate the potential of the random amplified polymorphic DNA (RAPD) assay to qualitatively detect the kinetics of benzo[a]pyrene (B[Ma]P)-induced DNA effects in the water flea Daphnia magna exposed to 25 and 50 µg l^-1 B[a]P for 7 and 6 days, respectively. Mortality was recorded on a daily basis in both experiments, and RAPD analysis was performed on samples collected every day following isolation of genomic DNA. The main changes occurring in RAPD profiles produced by the population of Daphnia magna exposed to 25 and 50µg l^-1 B[a]P was a decrease and increase in band intensity, respectively. Most of the changes occurring in the RAPD patterns were likely to be the result of B[a]P-induced DNA damage (B[a]P DNA adducts, oxidized bases, DNA breakages) and/or mutations (point mutations and large rearrangements). In addition, reproducible changes also occurred in the profiles generated by control Daphnia magna. The results lead us to suggest that, in addition to B[a]P-induced DNA damage and mutations, factors such as variation in gene expression, steady levels of genetic alterations and changes in metabolic processes could induce some changes in RAPD patterns. Nevertheless, our data suggest that DNA damage and mutations appear to be the main factors influencing RAPD patterns. This study also emphasizes that unexpected variation in control profiles is not always associated with artefacts.     

The random amplified polymorphic DNA (RAPD) assay to determine DNA alterations, repair and transgenerational effects in B(a)P exposed Daphnia magna

The random amplified polymorphic DNA (RAPD) is a useful assay for the detection of genotoxin-induced DNA damage and mutations. In this study, we have further evaluated the potential of this assay to measure benzo(a)pyrene [B(a)P]-induced DNA changes, and repair (in kinetic experiments) as well as transgenerational effects in the water fleas, Daphnia magna. The organisms, which reproduce parthenogenetically, were exposed to 50 microg L(-1) B(a)P for 3 or 6 days and were allowed to recover in clean medium for 12 or 9 days, respectively. Qualitative and quantitative changes were observed in RAPD profiles generated not only from the B(a)P exposed Daphnia but also from previously treated organisms during the recovery experiments. The fact that some of the RAPD changes disappeared at the end of both recovery experiments suggested that the DNA effects were fully repaired or reversed. In addition, some of the B(a)P-induced RAPD alterations detected in parental D. magna were also observed in the offspring patterns. This suggested that DNA alterations that occurred in germ cells were probably transmitted to the next cohorts. The present study shows that the RAPD method can be useful to qualitatively assess the kinetics of DNA changes, repair and transgenerational effects and such effects could potentially be linked to survival and reproductive success at higher levels of biological organisation. In addition, the water fleas have efficient capabilities to repair or reverse B(a)P-induced DNA effects. Finally, unrepaired or misrepaired genetic damage induced by genotoxins such as B(a)P could be transmitted to next generations in these parthenogenetically reproducing organisms.     

Evaluation of the random amplified polymorphic DNA (RAPD) assay for the detection of DNA damage and mutations

The random amplified polymorphic DNA (RAPD) assay and related techniques like the arbitrarily primed polymerase chain reaction (AP-PCR) have been shown to detect genotoxin-induced DNA damage and mutations. The changes occurring in RAPD profiles following genotoxic treatments include variation in band intensity as well as gain or loss of bands. However, the interpretation of the molecular events responsible for differences in the RAPD patterns is not an easy task since different DNA alterations can induce similar type of changes. In this study, we evaluated the effects of a number of DNA alterations on the RAPD profiles. Genomic DNA from different species was digested with restriction enzymes, ultrasonicated, treated with benzo[a]pyrene (B[a]P) diol epoxide (BPDE) and the resulting RAPD profiles were evaluated. In comparison to the enzymatic DNA digestions, sonication caused greater changes in the RAPD patterns and induced a dose-related disappearance of the high molecular weight amplicons. A DNA sample substantially modified with BPDE caused very similar changes but amplicons of low molecular weight were also affected. Appearance of new bands and increase in band intensity were also evident in the RAPD profiles generated by the BPDE-modified DNA. Random mutations occurring in mismatch repair-deficient strains did not cause any changes in the banding patterns whereas a single base change in 10-mer primers produced substantial differences. Finally, further research is required to better understand the potential and limitations of the RAPD assay for the detection of DNA damage and mutations.     

Evaluation of the random amplified polymorphic DNA (RAPD) assay for the detection of DNA damage and mutations

The random amplified polymorphic DNA (RAPD) assay and related techniques like the arbitrarily primed polymerase chain reaction (AP-PCR) have been shown to detect genotoxin-induced DNA damage and mutations. The changes occurring in RAPD profiles following genotoxic treatments include variation in band intensity as well as gain or loss of bands. However, the interpretation of the molecular events responsible for differences in the RAPD patterns is not an easy task since different DNA alterations can induce similar type of changes. In this study, we evaluated the effects of a number of DNA alterations on the RAPD profiles. Genomic DNA from different species was digested with restriction enzymes, ultrasonicated, treated with benzo[a]pyrene (B[a]P) diol epoxide (BPDE) and the resulting RAPD profiles were evaluated. In comparison to the enzymatic DNA digestions, sonication caused greater changes in the RAPD patterns and induced a dose-related disappearance of the high molecular weight amplicons. A DNA sample substantially modified with BPDE caused very similar changes but amplicons of low molecular weight were also affected. Appearance of new bands and increase in band intensity were also evident in the RAPD profiles generated by the BPDE-modified DNA. Random mutations occurring in mismatch repair-deficient strains did not cause any changes in the banding patterns whereas a single base change in 10-mer primers produced substantial differences. Finally, further research is required to better understand the potential and limitations of the RAPD assay for the detection of DNA damage and mutations.     

Benzo{a}pyrene-induced DNA damage in Mytilus galloprovincialis: measurement of bulky DNA adducts and DNA oxidative damage in terms of 8-oxo-7,8-dihydro-2´-deoxyguanosine formation

Bulky DNA adducts and 8-oxo-7,8-dihydro-2´-deoxyguanosine (8-oxodGuo) were measured in gill DNA of benzo[a]pyrene (B[a]P)-exposed mussels (50 mg kg^-1 dw day^-1), respectively by the ³²P-post-labelling technique and high performance liquid chromatography coupled to electrochemical detection assay. A time-course study was performed for both biomarkers and their potential use for marine biomonitoring discussed for the sentinel species studied. In gills, B[a]P-related DNA adducts were positively correlated with B[a     

DNA damage (comet assay) and 8-oxodGuo (HPLC-EC) in relation to oxidative stress in the freshwater bivalve Unio tumidus

The relationships between DNA damage and oxidative stress in the digestive gland, gills and haemocytes of the freshwater bivalve Unio tumidus were investigated. Two markers of genotoxicity were measured: DNA breaks by means of the comet assay, and oxidative DNA lesions by means of 8-oxo-7,8-dihydro-2′-deoxyguanosine (8-oxodGuo) measured using high-performance liquid chromatography (HPLC) coupled to electrochemical detection. Lipid peroxidation was evaluated by measuring malondialdehyde (MDA) tissue levels. Effects were studied after exposure of bivalves for 6 days to benzo[a]pyrene (B[a]P) (50 and 100 μg?l^?1) and ferric iron (20 and 40 mg?l^?1), applied alone or in combination. Lipid peroxidation in the digestive gland and gills resulted from exposure to Fe³⁺ or B[a]P whatever the concentrations tested. DNA oxidatively formed lesions were induced in the two tissues at a higher level after B[a]P exposure than after Fe³⁺ treatment. No significant dose–response relationship was found with the two compounds and no synergistic effect was observed between Fe³⁺ and B[a]P. The gills appeared less sensitive than the digestive gland to DNA lesions expressed as 8-oxodGuo and comet results. Good correlations were noted between 8-oxodGuo and comet. MDA and DNA damage did not correlate as well, although it was stronger in the digestive gland than in the gills. Production of mucus by the gills likely served to prevent lesions by reducing the bioavailability of the chemicals tested, which could explain that dose–effect relationships and synergistic effects were not observed.     

Inhibition of the benzo[<Emphasis Type="Italic">a</Emphasis>]pyrene-induced toxicity by allyl sulfides in human epidermal keratinocytes

Diallyl sulfide (DAS) and diallyl disulfide (DADS) at 25 g ml^–1decreased the benzo[a]pyrene (B[a]P)-induced colony growth inhibition of human epidermal keratinocytes. DAS and DADS decreased B[a]P-DNA and B[a]P-protein adducts by 65% and 49–55%, respectively. The B[a]P-induced ethoxyresorufin O-deethylase activity, a marker enzyme for cytochrome P450 1, was decreased from 3 to 1.7–1.9 nmol min^–1 mg^–1 microsomal protein by DAS and DADS treatments. The activity of glutathione S-transferase, a detoxifying enzyme for B[a]P, but was decreased by DADS, but was unaffected by DAS.     

Lack of contribution of covalent benzo[a]pyrene-7,8-quinone–DNA adducts in benzo[a]pyrene-induced mouse lung tumorigenesis

Benzo[a]pyrene (B[a]P) is a potent human and rodent lung carcinogen. This activity has been ascribed in part to the formation of anti-trans-7,8-dihydroxy-7,8-dihydroB[a]P-9,10-epoxide (BPDE)-DNA adducts. Other carcinogenic mechanisms have been proposed: (1) the induction of apurinic sites from radical cation processes, and (2) the metabolic formation of B[a]P-7,8-quinone (BPQ) that can form covalent DNA adducts or reactive oxygen species which can damage DNA. The studies presented here sought to examine the role of stable BPQ-DNA adducts in B[a]P-induced mouse lung tumorigenesis. Male strain A/J mice were injected intraperitoneally once with BPQ or trans-7,8-dihydroxy-7,8-dihydroB[a]P (BP-7,8-diol) at 30, 10, 3, or 0 mg/kg. Lungs and livers were harvested after 24 h, the DNA extracted and subjected to ³²P-postlabeling analysis. Additional groups of mice were dosed once with BPQ or BP-7,8-diol each at 30 mg/kg and tissues harvested 48 and 72 h later, or with B[a]P (50 mg/kg, a tumorigenic dose) and tissues harvested 72 h later. No BPQ or any other DNA adducts were observed in lung or liver tissues 24, 48, or 72 h after the treatment with 30 mg/kg BPQ. BP-7,8-diol gave BPDE-DNA adducts at all time points in both tissues and B[a]P treatment gave BPDE-DNA adducts in the lung. In each case, no BPQ-DNA adducts were detected. Mouse body weights significantly decreased over time after BPQ or BP-7,8-diol treatments suggesting that systemic toxicity was induced by both agents. Model studies with BPQ and N-acetylcysteine suggested that BPQ is rapidly inactivated by sulfhydryl-containing compounds and not available for DNA adduction. We conclude that under these treatment conditions BPQ does not form stable covalent DNA adducts in the lungs or livers of strain A/J mice, suggesting that stable BPQ-covalent adducts are not a part of the complex of mechanisms involved in B[a]P-induced mouse lung tumorigenesis.     

Mitochondrial DNA exhibits resistance to induced point and deletion mutations

The accumulation of somatic mitochondrial DNA (mtDNA) mutations contributes to the pathogenesis of human disease. Currently, mitochondrial mutations are largely considered results of inaccurate processing of its heavily damaged genome. However, mainly from a lack of methods to monitor mtDNA mutations with sufficient sensitivity and accuracy, a link between mtDNA damage and mutation has not been established. To test the hypothesis that mtDNA-damaging agents induce mtDNA mutations, we exposed Muta^TMMouse mice to benzo[a]pyrene (B[a]P) or N-ethyl-N-nitrosourea (ENU), daily for 28 consecutive days, and quantified mtDNA point and deletion mutations in bone marrow and liver using our newly developed Digital Random Mutation Capture (dRMC) and Digital Deletion Detection (3D) assays. Surprisingly, our results demonstrate mutagen treatment did not increase mitochondrial point or deletion mutation frequencies, despite evidence both compounds increase nuclear DNA mutations and demonstrated B[a]P adduct formation in mtDNA. These findings contradict models of mtDNA mutagenesis that assert the elevated rate of mtDNA mutation stems from damage sensitivity and abridged repair capacity. Rather, our results demonstrate induced mtDNA damage does not readily convert into mutation. These findings suggest robust mitochondrial damage responses repress induced mutations after mutagen exposure.     

Toward an understanding of the role of DNA adduct conformation in defining mutagenic mechanism based on studies of the major adduct (formed at N-dG) of the potent environmental carcinogen, benzo[a]pyrene

The process of carcinogenesis is initiated by mutagenesis, which often involves replication past damaged DNA. One question — what exactly is a DNA polymerase seeing when it incorrectly copies a damaged DNA base (e.g., inserting dATP opposite a dG adduct)? — has not been answered in any case. Herein, we reflect on this question, principally by considering the mutagenicity of one activated form of benzo[a]pyrene, (+)-anti-B[a]PDE, and its major adduct [+ta]-B[a]P-N²-dG. In previous work, [+ta]-B[a]P-N²-dG was shown to be capable of inducing>95% G→T mutations in one sequence context (5′-T C), and 95% G→A mutations in another (5′-A A). This raises the question — how can a single chemical entity induce different mutations depending upon DNA sequence context? Our current working hypothesis is that adduct conformational complexity causes adduct mutational complexity, where DNA sequence context can affect the former, thereby influencing the latter. Evidence supporting this hypothesis was discussed recently (Seo et al., Mutation Res. [in press]). Assuming this hypothesis is correct (at least in some cases), one goal is to consider what these mutagenic conformations might be. Based on molecular modeling studies, 16 possible conformations for [+ta]-B[a]P-N²-dG are proposed. A correlation between molecular modeling and mutagenesis work suggests a hypothesis (Hypothesis 3): a base displaced conformation with the dG moiety of the adduct in the major vs. minor groove gives G→T vs. G→A mutations, respectively. (Hypothesis 4, which is a generalized version of Hypothesis 3, is also proposed, and can potentially rationalize aspects of both [+ta]-B[a]P-N²-dG and AP-site mutagenesis, as well as the so-called “A-rule”.) Finally, there is a discussion of how conformational complexity might explain some unusual mutagenesis results that suggest [+ta]-B[a]P-N²-dG can become trapped in different conformations, and why we think it makes sense to interpret adduct mutagenesis results by modeling ds-DNA (at least in some cases), even though the mutagenic event must occur at a ss/ds-DNA junction in the presence of a DNA polymerase.     

Time course of metabolism of benzo[e]pyrene by hamster embryo cells and the effect of chemical modifiers

In cultures of hamster embryo cells, benzo[a]pyrene (B[a]P) is metabolized primarily in the bay region. In contrast, little or no bay region metabolism of the noncarcinogenic isomer benzo[e]pyrene (B[e]P) could be detected during 12–96-h incubations of hamster embryo cells with 4 μM [³H]B[e]P. The upper limit to 9,10-dihydro-9,10-dihydroxy-B[e]P formation is about 0.2% of the ethyl acetate-soluble metabolites ( <0.1% of the total metabolites). The major identified metabolites of B[e]P were 4,5-dihydro-4,5-dihydroxy B[e]P and the glucuronide conjugates of 3-OH-B[e]P and 4,5-dihydro-4,5-dihydroxy B[e]P. Simultaneous treatment of cells with either B[a]P or 7,8-benzoflavone (BF) did not induce bay region metabolism of [³H]B[e]P.     

Binding of benzo[a]pyrene at the 1,3,6 positions to nucleic acids in vivo on mouse skin and in vitro with rat liver microsomes and nuclei

Loss of tritium from specific positions in [³H,¹⁴C] aromatic hydrocarbons can elucidate their binding site(s) to DNA and RNA and indicate the mechanism of activation. Studies of tritium loss from [6-³H,¹⁴C]benzo[a]pyrene(B[a]P), [1,3-³H,¹⁴C]B[a]P, [1,3,6-³H,¹⁴C]B[a]P, [6,7-³H,¹⁴C]B[a]P, and [7-³H,¹⁴C]B[a]P were conducted in vitro using liver nuclei and microsomes from 3-methylcholanthrene-induced Sprague-Dawley rats and in vivo on the skin of Charles River CD-1 mice. The relative loss of tritium from $\text{[}{}^3\text{H}\text{,}{}^{14}\text{C}\text{]}\text{B}\text{[a]}\text{P}$ was measured after binding to skin DNA and RNA, to nuclear DNA, and to native and denatured calf thymus and rat liver DNA's and poly(G) by microsomal activation. In skin, nuclei, and microsomes plus native DNA, virtually all B[a]P binding occurred at positions 1,3 and 6; while with microsomes plus denatured DNA or poly(G), B[a]P showed no binding at the 6 position and a small amount at the 1 and 3 positions. In vivo and with nuclei, binding at the 6 position predominated. Little loss of tritium from the 7 position was seen; this was expected because binding at this position is not thought to occur. This confirms the interpretation of loss of tritium as an indication of binding at a given position. These results demonstrate that the use of microsomes to activate B[a]P is not a valid model system for delineating the in vivo mechanism of B[a]P activation, and support previous evidence for one-electron oxidation as the mechanism of activation of hydrocarbons in binding to nucleic acids.     

Determinants of anti-benzo[a]pyrene diol epoxide–DNA adduct formation in lymphomonocytes of the general population

We evaluated determinants of anti-benzo[a]pyrenediolepoxide-(B[a]PDE)–DNA adduct formation (adduct induced by the ultimate carcinogenic metabolite of B[a]P) in lymphomonocytes of subjects environmentally exposed to low doses of polycyclic aromatic hydrocarbons (PAHs) (B[a]P). Our study population consisted of 585 Caucasian subjects, all municipal workers living in North-East Italy and recruited during their periodic check-ups after informed consent. PAH (B[a]P) exposure was assessed by questionnaire. Anti-B[a]PDE–DNA levels were measured by HPLC fluorescence analysis.We found that cigarette smoking (smokers (22%) versus non-smokers, p < 0.0001), dietary intake of PAH-rich meals (≥52 (38%) versus <52 times/year, p < 0.0001), and outdoor exposure (≥4 (19%) versus <4 h/day; p = 0.0115) significantly influenced adduct levels. Indoor exposure significantly increased the frequency of positive subjects (≥0.5 adducts/10⁸ nucleotides; χ² for linear trend, p = 0.051). In linear multiple regression analysis the major determinants of increased DNA adduct levels (ln values) were smoking (t = 6.362, p < 0.0001) and diet (t = 4.035, p < 0.0001). In this statistical analysis, indoor and outdoor exposure like other factors of PAH exposure had no influence. In non-smokers, the influence of diet (p < 0.0001) and high indoor exposure (p = 0.016) on anti-B[a]PDE–DNA adduct formation became more evident, but not that of outdoor exposure, as was confirmed by linear multiple regression analysis (diet, t = 3.997, p < 0.0001 and high indoor exposure, t = 2.522, p = 0.012).This study indicates that anti-B[a]PDE–DNA adducts can be detected in the general population and are modulated by PAH (B[a]P) exposure not only with smoking – information already known from studies with limited number of subjects – but also with dietary habits and high indoor exposure. In non-smokers, these two factors are the principal determinants of DNA adduct formation. The information provided here seems to be important, since DNA adduct formation in surrogate tissue is an index of genotoxic exposure also in target organs (e.g., lung) and their increase may also be predictive of higher risk for PAH-related cancers.     

Resistance to Nucleotide Excision Repair of Bulky Guanine Adducts Opposite Abasic Sites in DNA Duplexes and Relationships between Structure and Function

The nucleotide excision repair of certain bulky DNA lesions is abrogated in some specific non-canonical DNA base sequence contexts, while the removal of the same lesions by the nucleotide excision repair mechanism is efficient in duplexes in which all base pairs are complementary. Here we show that the nucleotide excision repair activity in human cell extracts is moderate-to-high in the case of two stereoisomeric DNA lesions derived from the pro-carcinogen benzo[a]pyrene (cis- and trans-B[a]P-N ²-dG adducts) in a normal DNA duplex. By contrast, the nucleotide excision repair activity is completely abrogated when the canonical cytosine base opposite the B[a]P-dG adducts is replaced by an abasic site in duplex DNA. However, base excision repair of the abasic site persists. In order to understand the structural origins of these striking phenomena, we used NMR and molecular spectroscopy techniques to evaluate the conformational features of 11mer DNA duplexes containing these B[a]P-dG lesions opposite abasic sites. Our results show that in these duplexes containing the clustered lesions, both B[a]P-dG adducts adopt base-displaced intercalated conformations, with the B[a]P aromatic rings intercalated into the DNA helix. To explain the persistence of base excision repair in the face of the opposed bulky B[a]P ring system, molecular modeling results suggest how the APE1 base excision repair endonuclease, that excises abasic lesions, can bind productively even with the trans-B[a]P-dG positioned opposite the abasic site. We hypothesize that the nucleotide excision repair resistance is fostered by local B[a]P residue—DNA base stacking interactions at the abasic sites, that are facilitated by the absence of the cytosine partner base in the complementary strand. More broadly, this study sets the stage for elucidating the interplay between base excision and nucleotide excision repair in processing different types of clustered DNA lesions that are substrates of nucleotide excision repair or base excision repair mechanisms.     

Rat liver homogenate (S9)-mediated binding of benzo[a]pyren to DNA in V79 cells,V79 cell nuclei and aqueous solution

The role of the target cell in determining the structures and the amounts of hydrocarbon-DNA adducts formed after hydrocarbon activation by an exogenous metabolic ativation system was investigated by exposing intact cells of the Chinese hamster lung cell line V79, V79 cell nuclei and calf thymus DNA to benzo[a]pyrene (B[a]P) in the presenceof a rat liver homogenate activation system (S9). The DNA was isolated, enzymatically degraded to deoxyribonucleosides and the B[a]P-deoxyribonucleoside adducts analyzed by high-performance liquid chromatography. Two major adducts were present in all samples; one formed by reaction of r-7, t-8-dihydroxy-t-9, 10-epoxy-7, 8, 9, 10-tetrahydro-B[a]P (anti-B[a]PDE) with the 2-amino group of deoxyguanosine, the other formed by reaction of a metabolite of 9-hydroxybenzo[a]pyrene (9-OH-B[a]P) with an unidentified deoxyribonucleoside. The ratios of the anti-B[a]PDE-DNA adduct to the 9-OH-B[a]P-DNA adduct were: calf thymus DNA, 3 to 1: DNA from V79 nuclei, 8 to 1; DNA from intact V79 cells, 11 to 1. Similar several-fold increases in the proportion of anti-B[a]PDE-DNA adducts in V79 cells over those in calf thymus DNA were observed for a dose range of 1–10 μg B[a]P per ml. The relative extent of binding of the activated metabolite of 9-OH-B[a]P to DNA was also much lower in intact V79 cells than in calf thymus DNA after exposure to 9-OH-B[a]P in the presence of the S9 activation system.These results demonstrate that the relative abilities of various reactive bbenzo[a]pyrene metabolites formed by an exogenous activation system to reach DNA differ substantially. Therefore, assessment of the biological activity of hydrocarbons in mutation assays using exogenous activation systems must take into account not only the amounts of different reactive hydrocarbon metabolites formed but also the relative abilities of these metabolites to reach the DNA of the target cell.     

The role of base excision repair genes OGG1, APN1 and APN2 in benzo[a]pyrene-7,8-dione induced p53 mutagenesis

Lung cancer is primarily caused by exposure to tobacco smoke. Tobacco smoke contains numerous carcinogens, including polycyclic aromatic hydrocarbons (PAH). The most common PAH studied is benzo[a]pyrene (B[a]P). B[a]P is metabolically activated through multiple routes, one of which is catalyzed by aldo-keto reductase (AKR) to B[a]P-7,8-dione (BPQ). BPQ undergoes a futile redox cycle in the presence of NADPH to generate reactive oxygen species (ROS). ROS, in turn, damages DNA. Studies with a yeast p53 mutagenesis system found that the generation of ROS by PAH o-quinones may contribute to lung carcinogenesis because of similarities between the patterns (types of mutations) and spectra (location of mutations) and those seen in lung cancer. The patterns were dominated by G to T transversions, and the spectra in the experimental system have mutations at lung cancer hotspots. To address repair mechanisms that are responsible for BPQ induced damage we observed the effect of mutating two DNA repair genes OGG1 and APE1 (APN1 in yeast) and tested them in a yeast reporter system for p53 mutagenesis. There was an increase in both the mutant frequency and the number of G:C/T:A transversions in p53 treated with BPQ in ogg1 yeast but not in apn1 yeast. Knocking out APN2 increased mutagenesis in the apn1 cells. In addition, we did not find a strand bias on p53 treated with BPQ in ogg1 yeast. These studies suggest that Ogg1 is involved in repairing the oxidative damage caused by BPQ, Apn1 and Apn2 have redundant functions and that the stand bias seen in lung cancer may not be due to impaired repair of oxidative lesions.     

Improved measurement of dibenzo[a,l]pyrene-induced abasic sites by the aldehyde-reactive probe assay

Dibenzo[a,l]pyrene (DB[a,l]P) induces abundant amounts of depurinating adducts that spontaneously dissociate to form abasic sites in DNA. However, several previous studies that used the aldehyde-reactive probe (ARP) assay, could not verify abasic site formation by DB[a,l]P. Therefore, we examined whether a modification of the ARP assay would allow greater quantification of abasic sites. A previous study indicated that the abasic site quantification is improved by letting ARP trap the nascent abasic sites in cells, before extracting DNA for the assay. To test whether the addition of ARP to the DB[a,l]P–DNA adduct-forming reaction would improve abasic site quantification, we treated calf thymus DNA (0.625 mg/mL) with DB[a,l]P (80 μM) and 3-methylcholanthrene-treated rat liver microsomes with or without ARP (3 mM). The inclusion of ARP in the adduct-forming reaction resulted in significantly greater detection of abasic sites (62 lesions/10⁶ bp versus 3.7 lesions/10⁶ bp). DB[a,l]P also induces DNA strand breaks. The strand breaks may occur at abasic sites and by other mechanisms, such as oxidative damage. ARP/O-methoxyamine-abasic site conjugates are refractory to strand breakage, however, ARP or O-methoxyamine (3–10 mM) could only partially protect DB[a,l]P-induced DNA degradation, presumably by protecting the abasic sites, but not the other strand breaks. These results suggest that if DNA strand breakages occur at the abasic sites or at bases flanking them, and the fragments are lost during DNA extraction, abasic site estimation could be compromised. To obtain an independent line of evidence for abasic site formation in DB[a,l]P-treated cells, mouse Mβ16 fibroblasts were treated with DB[a,l]P and O-methoxyamine. O-Methoxyamine is known to potentiate cytotoxicity of abasic site-inducing chemicals by forming abasic site conjugates, which partially inhibits their repair. O-Methoxyamine was found to increase DB[a,l]P cytotoxicity in these cells, supporting the idea that DB[a,l]P formed abasic sites. In summary, the inclusion of ARP in the DB[a,l]P–DNA adduct-forming reaction traps and protects the nascent abasic sites, allowing an improved quantification of abasic sites.     

Modulations of benzo[a]pyrene-induced DNA adduct, cyclin D1 and PCNA in oral tissue by 1,4-phenylenebis(methylene)selenocyanate

Tobacco smoking is an important cause of human oral squamous cell carcinoma (SCC). Tobacco smoke contains multiple carcinogens include polycyclic aromatic hydrocarbons typified by benzo[a]pyrene (B[a]P). Surgery is the conventional treatment approach for SCC, but it remains imperfect. However, chemoprevention is a plausible strategy and we had previously demonstrated that 1,4-phenylenebis(methylene)selenocyanate (p-XSC) significantly inhibited tongue tumors-induced by the synthetic 4-nitroquinoline-N-oxide (not present in tobacco smoke). In this study, we demonstrated that p-XSC is capable of inhibiting B[a]P-DNA adduct formation, cell proliferation, cyclin D1 expression in human oral cells in vitro. In addition, we showed that dietary p-XSC inhibits B[a]P-DNA adduct formation, cell proliferation and cyclin D1 protein expression in the mouse tongue in vivo. The results of this study are encouraging to further evaluate the chemopreventive efficacy of p-XSC initially against B[a]P-induced tongue tumors in mice and ultimately in the clinic.