Yuan-Wan Sun

1,4-Phenylenebis(Methylene)Selenocyanate, but Not Selenomethionine, Inhibits Androgen Receptor and Akt Signaling in Human Prostate Cancer Cells

The lack of treatment for worried-well patients with high-grade prostatic intraepithelial neoplasia combined with issues of recurrence and hormone resistance in prostate cancer survivors remains a major public health obstacle. The long latency of prostate cancer development provides an opportunity to intervene with agents of known mechanisms at various stages of disease progression. A number of signaling cascades have been shown to play important roles in prostate cancer development and progression, including the androgen receptor (AR) and phosphatidylinositol 3-kinase/Akt signaling pathways. Crosstalk between these two pathways is also thought to contribute to progression and hormone-refractory prostate disease. Our initial investigations show that the naturally occurring organoselenium compound selenomethionine (SM) and the synthetic 1,4-phenylenebis(methylene)selenocyanate (p-XSC) can inhibit human prostate cancer cell viability; however, in contrast to SM, p-XSC is active at physiologically relevant doses. In the current investigation, we show that p-XSC, but not an equivalent dose of SM, alters molecular targets and induces apoptosis in androgen-responsive LNCaP and androgen-independent LNCaP C4-2 human prostate cancer cells. p-XSC effectively inhibits AR expression and transcriptional activity in both cell lines. p-XSC also decreases Akt phosphorylation as well as Akt-specific phosphorylation of the AR. Inhibition of Akt, however, does not fully attenuate p-XSC–mediated downregulation of AR activity, suggesting that inhibition of AR signaling by p-XSC does not occur solely through alterations in the phosphatidylinositol 3-kinase/Akt survival pathway. Our data suggest that p-XSC inhibits multiple signaling pathways in prostate cancer, likely accounting for the downstream effects on proliferation and apoptosis. Cancer Prev Res; 3(8); 975–84. ©2010 AACR.

Mutagenesis and carcinogenesis induced by dibenzo[a,l]pyrene in the mouse oral cavity: a potential new model for oral cancer

Cancer of the oral cavity is a serious disease, affecting about 30,000 individuals in US annually. There are several animal models of oral cancer, but each has certain disadvantages. As a new model, we investigated whether topical application of the tobacco smoke carcinogen, dibenzo[a,l]pyrene (DB[a,l]P) is mutagenic and carcinogenic in the oral cavity of the B6C3F1 lacI and B6C3F1 mouse, respectively. B6C3F1 lacI mice received DB[a,l]P (0, 3, 6, 12 nmol) 3× per week. B6C3F1 mice received the same doses and also 24 nmol. At 38 weeks mutagenesis was measured in oral tissues in lacI mice. For the high dose group, the mutant fraction (MF) in upper mucosa and tongue increased about twofold relative to that in vehicle‐alone. The increases were statistically significant. The mutational profile in the DB[a,l]P‐induced mutants was compared with that induced by benzo[a]pyrene (BaP) in oral tissue. BaP is mutagenic in many tissues when administered by gavage. The mutational profile for DB[a,l]P was more similar to that reported for p53 mutations in head and neck cancers than was that of BaP. At 47 weeks, oral squamous cell carcinomas (OSCC) were found in 31% of the high‐dose B6C3F1 group. Elevations of p53 and COX‐2 protein were observed in tumor and dysplastic tissue. As DB[a,l]P induces mutations and tumors in the oral cavity, and has a mutational profile in oral tissue similar to that found in p53 in human OSCC, the treatment protocol described here may represent a new and relevant model for cancer of the oral cavity.

FOXO3 Encodes a Carcinogen-Activated Transcription Factor Frequently Deleted in Early-Stage Lung Adenocarcinoma

The FOXO family of transcription factors elicits cell cycle arrest, apoptosis, and resistance to various physiologic and pathologic stresses relevant to sporadic cancer, such as DNA damage and oxidative stress. Although implicated as tumor suppressors, FOXO genetic inactivation has not been observed in human cancer. In an investigation of the two major types of non-small cell lung cancer, here, we identify the FOXO3 gene as a novel target of deletion in human lung adenocarcinoma (LAC). Biallelic or homozygous deletion (HD) of FOXO3 was detected in 8 of 33 (24.2%) mostly early-stage LAC of smokers. Another 60.6% of these tumors had losses of FOXO3 not reaching the level of HD (hereafter referred to as sub-HD). In contrast, no HD of FOXO3 was observed in 19 lung squamous cell carcinoma. Consistent with the deletion of FOXO3 were corresponding decreases in its mRNA and protein levels in LAC. The potential role of FOXO3 loss in LAC was also investigated. The carcinogen (+)-anti-7,8-dihydroxy-9,10-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (BPDE) is strongly implicated as a cause of human lung cancer. Here, we show that FOXO3a is functionally activated and augments the level of caspase-dependent apoptosis in cells exposed to this DNA-damaging carcinogen. These results implicate FOXO3 as a suppressor of LAC carcinogenesis, a role frequently lost through gene deletion.

Identification and quantification of DNA adducts in the oral tissues of mice treated with the environmental carcinogen dibenzo[a,l]pyrene by HPLC-MS/MS.

Tobacco smoking is one of the leading causes for oral cancer. Dibenzo[a,l]pyrene (DB[a,l]P), an environmental pollutant and a tobacco smoke constituent, is the most carcinogenic polycyclic aromatic hydrocarbon (PAH) tested to date in several animal models (target organs: skin, lung, ovary, and mammary tissues). We have recently demonstrated that DB[a,l]P is also capable of inducing oral cancer in mice; however, its metabolic activation to the ultimate genotoxic metabolite dibenzo[a,l]pyrene-11,12-dihydrodiol-13,14-epoxide (DB[a,l]PDE) in mouse oral cavity has not been examined. Here we developed a liquid chromatography-tandem mass spectrometry (LC-MS/MS) method to detect and quantify (±)-anti-DB[a,l]PDE-dA adducts in oral tissues of mice treated with DB[a,l]P. [(15)N(5)]-(±)-anti-DB[a,l]PDE-N(6)-dA adducts were synthesized as internal standards. The stereoisomeric adducts were characterized by MS, NMR, and CD analysis. The detection limit of the method is 8 fmol with 100 μg of digested DNA as the matrix. Two adducts were detected and identified as (-)-anti-cis and (-)-anti-trans-DB[a,l]PDE-dA in the oral tissues of mice following the direct application of DB[a,l]P (240 nmol per day, for 2 days) into the oral cavity, indicating that DB[a,l]P is predominantly metabolized into (-)-anti-DB[a,l]PDE in this target organ. We also compared the formation and removal of adducts as a function of time, following the direct application of DB[a,l]P (24 nmol, 3 times per week for 5 weeks) into the oral cavity of mice. Adducts were quantified at 48 h, 1, 2, and 4 weeks after the last dose. Maximal levels of adducts occurred at 48 h, followed by a gradual decrease. The levels (fmol/μg DNA) of (-)-anti-trans adducts (4.03 ± 0.27 to 1.77 ± 0.25) are significantly higher than (-)-anti-cis-DB[a,l]PDE-dA adduct (1.63 ± 0.42 to 0.72 ± 0.04) at each time point (p < 0.005). The results presented here indicate that the formation and persistence of (-)-anti-DB[a,l]PDE-dA adducts may, in part, contribute to the initiation of DB[a,l]P-induced oral carcinogenesis.

Mechanisms of oral carcinogenesis induced by dibenzo[a,l]pyrene: An environmental pollutant and a tobacco smoke constituent

We previously reported that dibenzo[a,l]pyrene (DB[a,l]P), the most potent known environmental carcinogen among polycyclic aromatic hydrocarbons (PAH) congeners, is carcinogenic in the oral tissues of mice. We have now developed a new mouse model which employs the oral application of the fjord region diol epoxide, (±)‐anti−11,12‐dihydroxy‐13,14‐epoxy‐11,12,13,14‐tetrahydrodibenzo[a,l]pyrene (DB[a,l]PDE), a metabolite of the tobacco smoke constituent DB[a,l]P, and we show its specific induction of oral squamous cell carcinoma (OSCC) in both tongue and other oral tissues. Groups of B6C3F1 mice (20/group) received 6 or 3 nmol of (±)‐anti‐DB[a,l]PDE administered into the oral cavity; 3 times per week for 38 weeks. Additional groups received the vehicle alone or were left untreated. Mice were sacrificed 42 weeks after the first carcinogen administration. The high dose induced 74 and 100% OSCC in the tongue and other oral tissues, respectively; the corresponding values at the lower dose were 45 and 89%. Using immunohistochemistry, we showed that DB[a,l]PDE resulted in overexpression of p53 and COX‐2 proteins in malignant tissues when compared to normal oral tissues and tongues. Consistent with the carcinogenicity, we demonstrated powerful mutagenicity in cII gene in B6C3F1 (Big Blue) mouse tongue. The mutational profile in lacI reporter gene is similar to those detected in human head and neck cancer, and p53 mutations were observed in mouse oral tumor tissues. Taken together, we conclude that the formation of diol epoxides plays a major role among the mechanisms by which DB[a,l]P exerts its oral mutagenicity and tumorigenicity.

Simultaneous detection of deoxyadenosine and deoxyguanosine adducts in the tongue and other oral tissues of mice treated with Dibenzo[a,l]pyrene.

We were the first to demonstrate that direct application of the environmental pollutant and tobacco smoke constituent dibenzo[a,l]pyrene (DB[a,l]P) into the oral cavity of mice induced squamous cell carcinoma (SCC) in oral tissues but not in the tongue; however, the mechanisms that can account for the varied carcinogenicity remain to be determined. Furthermore, we also showed that not only dA adducts, but also dG adducts can account for the mutagenic activity of DB[a,l]P in the oral tissues in vivo. In this study, we initially focused on DB[a,l]P-induced genotoxic effects in both oral and tongue tissues. Therefore, to fully assess the contribution of these DNA adducts in the initiation stage of carcinogenesis induced by DB[a,l]P, an LC-MS/MS method to simultaneously detect and quantify DB[a,l]PDE-dG and -dA adducts was developed. Mice were orally administered with DB[a,l]P (24 nmole, 3 times per week for 5 weeks) or its fjord region diol epoxide, (±)-anti-11,12-dihydroxy-13,14-epoxy-11,12,13,14-tetrahydrodibenzo[a,l]pyrene (DB[a,l]PDE, 12 nmole, single application); animals were sacrificed at 2, 7, 14, and 28 days after the last dose of carcinogen administration. Oral and tongue tissues were obtained and DNA were isolated followed by enzymatic hydrolysis. Following the development of an isotope dilution LC-MS/MS method, we successfully detected (−)-anti-cis- and (−)-anti-trans-DB[a,l]PDE-N2-dG, as well as (−)-anti-cis- and (−)-anti-trans-DB[a,l]PDE-N6-dA in oral and tongue tissues of mice treated with DB[a,l]P. Levels of (−)-anti-trans-DB[a,l]PDE-N6-dA were ≥2 folds higher than (−)-anti-cis-DB[a,l]PDE-N6-dA adduct and those of dG adducts in the oral tissues and tongue at all time points selected after the cessation of DB[a,l]P treatment. Levels of dG adducts were comparable in both tissues. Collectively, our results support that DB[a,l]P is predominantly metabolized to (−)-anti-DB[a,l]PDE, and the levels and persistence of (−)-anti-trans-DB[a,l]PDE-N6-dA may, in part, explain the carcinogenicity of DB[a,l]P in the oral tissues but not in the tongue.

CK0403, a 9‑aminoacridine, is a potent anti‑cancer agent in human breast cancer cells

3‑({4‑[4‑(Acridin‑9‑ylamino)phenylthio]phenyl}(3‑hydroxypropyl)amino)propan‑1‑ol (CK0403) is a sulfur‑containing 9‑anilinoacridine analogue of amsacrine and was found to be more potent than its analogue 2-({4-[4-(acridin-9-ylamino)phenylthio]phenyl}(2‑hydroxyethyl)amino)ethan‑1‑ol (CK0402) and amsacrine in the inhibition of the topoisomerase II‑catalyzed decatenation reaction. A previous study by our group reported that CK0402 was effective against numerous breast cancer cell lines, and the combination of CK0402 with herceptin enhanced its activity in HER2(+) SKBR‑3 cells. In order to identify novel chemotherapeutic agents with enhanced potency, the present study explored the potential of CK0403 in the treatment of breast cancer. First, the growth inhibitory activity of CK0403 in the breast cancer cell lines MCF‑7, MDA‑MB‑231, BT474 and SKBR‑3, as well as in the non‑cancerous MCF‑10A cell line, was examined using a sulforhodamine B assay. The results showed that CK0403 exerted more potent growth inhibitory activity than CK0402 in all of the breast cancer cell lines except MCF‑7. SKBR‑3 and MDA‑MB‑231 were the most sensitive cell lines tested, and the combination of CK0403 with herceptin in HER2(+) SKBR‑3 cells enhanced the growth inhibitory activity of CK0403. Analysis of cell cycle alterations induced by CK0403 in SKBR‑3 cells revealed that, similarly to CK0402, CK0403 induced G2/M‑phase arrest with a decreased S- and G0/G1-phase ratio. In addition, it was shown that CK0403 induced apoptosis more effectively than CK0402 in SKBR‑3 cells. Further analysis of autophagy protein 5 (Atg5) indicated that CK0403 induced more cleaved Atg5 than CK0402 and other chemotherapeutic agents tested. Of note, although still relatively potent, CK0403 exhibited reduced growth inhibitory activity under hypoxic conditions, which can induce autophagy. Collectively, the present results supported that CK0403 is highly potent and more effective than CK0402 against estrogen receptor-negative and HER2‑overexpressing breast cancer cell lines, suggesting its future application for chemotherapy in breast cancer.

Mechanisms underlying the varied mammary carcinogenicity of the environmental pollutant 6-nitrochrysene and its metabolites (-)-[R,R]- and (+)-[S,S]-1,2-dihydroxy-1,2-dihydro-6-nitrochrysene in the rat.

The mechanisms that can account for the remarkable mammary carcinogenicity of the environmental pollutant 6-nitrochrysene (6-NC) in the rat remain elusive. In our previous studies, we identified several 6-NC-derived DNA adducts in the rat mammary gland; one major adduct was derived from (±)-trans-1,2-dihydroxy-1,2-dihydro-6-nitrochrysene (1,2-DHD-6-NC). In the present study, we resolved the racemic (±)-1,2-DHD-6-NC into (-)-[R,R]- and (+)-[S,S]-1,2-DHD-6-NC and compared their in vivo mutagenicity and carcinogenicity in the mammary glands of female transgenic (BigBlue F344 × Sprague-Dawley)F1 rats harboring lacI/cII and Sprague-Dawley rats, respectively. Both [R,R]- and [S,S]-isomers exerted similar mutagenicity and carcinogenicity but were less potent than 6-NC. Additional in vivo and in vitro studies were then performed to explore possible mechanisms that can explain the higher potency of 6-NC than 1,2-DHD-6-NC. Using ELISA, we found that neither 6-NC nor 1,2-DHD-6-NC increased the levels of several inflammatory cytokines in plasma obtained from rats 24 h after treatment. In MCF-7 cells, as determined by immunoblotting, the effects of 6-NC and 1,2-DHD-6-NC on protein expression (p53, Akt, p38, JNK, c-myc, bcl-2, PCNA, and ERβ) were comparable; however, the expressions of AhR and ERα proteins were decreased by 6-NC but not 1,2-DHD-6-NC. The expression of both receptors was decreased in mammary tissues of rats treated with 6-NC. Our findings suggest that the differential effects of 6-NC and 1,2-DHD-6-NC on AhR and ERα could potentially account for the higher carcinogenicity of 6-NC in the rat mammary gland.

Stereoselective metabolism of the environmental mammary carcinogen 6-nitrochrysene to trans-1,2-dihydroxy-1,2-dihydro-6-nitrochrysene by aroclor 1254-treated rat liver microsomes and their comparative mutation profiles in a laci mammary epithelial cell line.

The environmental pollutant 6-nitrochrysene (6-NC) is a powerful mammary carcinogen and mutagen in rats. Our previous studies have shown that 6-NC is metabolized to trans-1,2-dihydroxy-1,2-dihydro-6-nitrochrysene (1,2-DHD-6-NC) in rats and in several in vitro systems, including human breast tissue, and the latter is the proximate carcinogenic form in the rat mammary gland. Because optically active enantiomers of numerous polynuclear aromatic hydrocarbon (PAH) metabolites including chrysene have different biological activities, we hypothesized that the stereochemical course of 6-NC metabolism might play a significant role in the carcinogenic/mutagenic activities of the parent 6-NC. The goal of this study is to evaluate the effect of stereochemistry on the mutagenicity of 1,2-DHD-6-NC using the cII gene of lacI mammary epithelial cells in vitro. Resolution of (+/-)-1,2-DHD-6-NC was obtained by either nonchiral or chiral stationary phase HPLC methods. We determined that the ratio of (-)-[R,R]- and (+)-[S,S]-1,2-DHD-6-NC formed in the metabolism of 6-NC by rat liver microsomes is 88:12. The mutation fractions and mutation spectra of [R,R] and [S,S]-enantiomers were examined. Our results showed that the [R,R]-isomer is a significantly (p < 0.01) more potent mutagen than the [S,S]-isomer. The major types of mutation induced by the [R,R]-enantiomer are AT > GC, AT > TA, and GC > TA substitutions, and these are similar to those obtained from 6-NC in vivo in the mammary glands of rats treated with 6-NC. The mutation spectra of the [S,S]-isomer were similar to the [R,R]-isomer, but a higher percentage of AT > GC substitutions in the [R,R]-isomer was noted. On the basis of the results of the present study, we hypothesize that [R,R]-1,2-DHD-6-NC is the proximate carcinogen of 6-NC in the rat mammary gland in vivo and will test this hypothesis in a future study.

Comparative tumorigenicity and DNA damage induced by dibenzo[def,p]chrysene and its metabolites in the mouse ovary

Ovarian cancer ranked second in incidence among gynecologic cancers, but it causes more deaths than any other gynecologic cancer; at present there is no curative treatment beyond surgery. Animal models that employ carcinogens found in the human environment can provide a realistic platform to understand the mechanistic basis for disease development and to design rational chemopreventive/therapeutic strategies. We and others have shown that the administration of the environmental pollutant and tobacco smoke constituent dibenzo[ def,p]chrysene (DBP) to mice by several routes of exposure can induce tumors in multiple sites including the ovary. In the present study we compared, for the first time, the tumorigenicity and DNA damage induced by DBP and its metabolites DBP-dihydrodiol (DBPDHD) and DBP-dihydrodiol epoxide (DBPDE) in the mouse ovary. Compounds were dissolved in dimethyl sulfoxide (DMSO) as the vehicle and administered by topical application into the mouse oral cavity three times per week for 38 weeks. No tumors were observed in mice treated with DMSO. At equal dose (24 nmol/30 μL DMSO), the incidence of ovarian tumors induced by DBPDHD was higher (60.7%), although not significantly, than that induced by DBP (44.8%). Similarly the levels of DNA damage induced by DBPDHD in the ovary were higher than those observed with DBP. We did not observe any histological abnormality in the ovary of mice treated with DBPDE, which is consistent with lack of DNA damage. Our results suggested that both DBP and DBPDHD can be metabolized in the mouse ovary leading to the formation of DBPDE that can damage DNA, which is a prerequisite step in the initiation stage of carcinogenesis.