AU2006350735A1 - A cigarette filter containing rosemary extract and a method of reducing DNA damage caused by harmful agents in cigarette smoke by use of said filter - Google Patents

Description

WO 2008/060286 PCT/US2006/044704 A CIGARETTE FILTER CONTAINING ROSEMARY EXTRACT AND A METHOD OF REDUCING DNA DAMAGE CAUSED BY HARMFUL AGENTS IN CIGARETTE SMOKE BY USE OF SAID FILTER 5 1. Field of the Invention The invention relates to a cigarette filter containing rosemary extract and a method of reducing DNA damage caused by various harmful agents in cigarette smoke. More specifically, the present invention relates to the use of said filter to 10 reduce DNA damage caused by benzo(a)pyrenes in human cells by the reduction of the human lung benzo(a)pyrene diol epoxide-dG (BPDE-dG) adduct. 2. Background 15 The human lung benzo(a)pyrene diol epoxide-dG (BPDE-dG) adduct concentrates in bronchial cells. This adduct now is recognized as a critical event in tumorigenesis by benzo(a)pyrenes. Cigarette smoke is a significant contributor to BPDE-dG formation. 20 Tobacco use is by far the most widespread link between exposure to known carcinogens and death from cancer, and is therefore a model for understanding mechanisms of cancer induction. Benzo(a)pyrene (BP) is a highly carcinogenic polycyclic aromatic hydrocarbon (PAH) present in emission 25 exhausts, charbroiled food and in small quantity in cigarette smoke, typically less than 10 ng per cigarette. BP is one of more than 60 carcinogens in cigarette smoke that is involved in the aetiology of lung cancer. It is metabolically activated into benzo(a)pyrene-7,8-diol-9,10-epoxide (BPDE) 30 which reacts with DNA predominantly at the N 2 -position of guanine to produce primarily N 2 -guanine lesions, e.g. benzo (a)pyrene-7, 8-diol-9, 10-epoxide-N 2 -deoxyguanosine

(BPDE

dG) adduct. The presence of BPDE-DNA adducts in human tissues 1 WO 2008/060286 PCT/US2006/044704 has been conclusively established and BPDE-dG adduct concentrated exclusively in bronchial cells and thus implicated in the initiation of human lung cancer. Rosemary (Rosmnarinus officinalis Labiatae) herb and oil, 5 rosemary extracts, carnosic acid and carnosol are commonly used as spice and flavoring agents in food processing for their desirable flavor and high antioxidant activity. However, prior to the instant invention, there was no recognition that the use of a rosemary extract in a cigarette 10 filter would reduce the DNA damage caused in human cells by benzo(a)pyrenes specifically, the human lung benzo(a)pyrene diol epoxide-dG (BPDE-dG) adduct which adduct now is recognized as a critical event in tumorigenesis by benzo(a)pyrenes. 15 3. Summary of the Invention BP is considered to be a significant carcinogen involved in lung cancer induction in smokers and, as is shown in this study, reactive oxygen species contribute substantially in the 20 formation of the critical lung tumorigenic adduct. While it is both critical to prevent addiction to tobacco and to enhance the efficacy of smoking cessation and reduction programs, these approaches have had little impact. The prevention of the formation of BPDE-dG adduct is one approach 25 which may lead to decreasing lung cancer risk in addicted smokers. The invention relates to a cigarette filter containing rosemary extract and a method of reducing DNA damage caused by harmful agents in cigarette smoke. More specifically, the 30 present invention provides for the use of said filter to ' reduce DNA damage caused by benzo(a)pyrenes in human cells by the reduction of the human lung benzo(a)pyrene diol epoxide-dG (BPDE-dG) adduct. 2 WO 2008/060286 PCT/US2006/044704 It has been found that the amount of (-)-anti- BPDE-dG adduct increases linearly with concentration of cigarette smoke in the presence of (+)-BP-7,8-diol. Catalase and superoxide dismutase inhibit its formation by more than 80%. 5 When MCF-7 cells are treated for 2 hours with the (+)-BP-7,8 diol, cigarette smoke increases dose dependently the formation of (-)-anti-BPDE-dG and decreases the CYPs dependent formation of (+)-syn-BPDE, the adduct. I have treated cells for up to one day with 10 benzo(a)pyrene and then exposed them for 2 hours with cigarette smoke. During these 2 hours, I have discovered that there is twice the increase in the adduct formation in cells treated with cigarette smoke in comparison to levels in non treated cells due to CYPs activity. Thus, I have found that 15 cigarette smoke activates by reactive oxygen species which it contains the second step of benzo(a)pyrene metabolic way leading to the formation of BPDE-dG adduct. Cigarette smoke thus may in this way responsible for the formation of the critical lung tumorigenic adduct. 20 Finally, I have found that modified cigarette filter containing rosemary extract decreases by more than 70% of the BPDE-dG adducts level due to the cigarette smoke in MCF-7 cells. This discovery, I believe is a significant advance in decreasing lung cancer risk in addicted smokers. 25 4. Brief Description of the Figures, Scheme and Table: Figure 1. Principal metabolic pathway and DNA binding of the carcinogen benzo(a)pyrene. Benzo(a)pyrene is a tobacco carcinogen that may be converted in vivo enzymatically or by 30 oxygen reactive species to yield DNA-reactive dihydrodiol epoxides. Stereoselective generation of the mutagenic (+)-r 7,t-8-dihydroxy-t-9,10-oxy-7,8,9,10-tetrahydro-BP [(+)-anti BPDE] from (-)-BP-7,8-dihydrodiol is catalyzed by cytochrome 3 WO 2008/060286 PCT/US2006/044704 P450-dependent monooxygenases (P450) or reactive oxygen species. Subsequent reaction of this electrophilic intermediate with genomic DNA produce stable adduct between dihydrodiol epoxide and the exocyclic amino group of 5 guanosine. This kind of DNA lesion may be converted into mutations within the following replication cycle unless repair of this adduct is produced. Figure 2. Results obtained by using a cell-free system concomitant with DNA adduction: 6 mg calf thymus DNA in 2 ml 10 water was added to 5 ml CSS with different dilutions and reacted for 2 hours at room temperature with (+)-BP-7,8-diol (final concentration 3.6 pM). DNA was hydrolyzed and the released BP-tetrol I were measured as outlined in Materials and Methods. 15 Figure 3. (a) Stereochemistry of BP-7,8-diol epoxidation by peroxyl radicals and cytochrome P450 to reactive species (anti-BPDE and syn-BPDE) that can bind to DNA, and (b) acid hydrolysis of DNA to BP-tetrols measured in this study. The 20 hydrolysis of (-)-anti-BPDE-dG and (-)-Syn-BPDE leads to the formation of BP-tetrol 1-2 and BP-tetrol II-1 which however are unstable and are converted into BP-tetrol I-land BP-tetrol II-2. Figure 4. Results obtained using MFC-7 cells. 10 x 106 25 cells/150 cm 2 flask in a total volume of 20 ml were treated for 2 hrs with (+)-BP-7,8-diol (0.2 y.IM) alone or in presence of different dilutions of CSS DNA was isolated, hydrolyzed and the released BP-tetrols were measured and the binding levels determined as outlined in Materials and Methods. Two distinct 30 peaks were observed on the chromatograms corresponding to BP tetrol I and BP-tetrol II derived from (-)-anti-BPDE-dG and (+)-syn-BPDE-dG respectively (ref s. 32-34). Values represent the means plus Std of two independent experiments with 3-4 HPLC runs. Figure 4a, upper panel, increases of 4 WO 2008/060286 PCT/US2006/044704 (-)-anti-BPDE-dG adducts with CSS dilution; Figure 4b, lower panel, increases of 1/(+)-syn-BPDE-dG adduct with CSS dilution. 5 Figure 5. BPDE-dG binding in MCF-7 cells af ter exposure to BP 2.5 pM or BP 2.5 pM + CS solution (dilution 20 times) for the time indicated. Cigarette smoke solution was added the last 2 hours during the exposure to BP (Scheme 1). Analysis of BPDE-dG was performed as described in Materials 10 and Methods. Values represent the means of two independent experiments with -4-6 HPLC runs plus Standard. The BPDE-dG value were 11.7 ± 0.5 (mean ± s.d.) Og of adducts per mg DNA after 12 hours of incubation and 17.6 ± 0.4, 26.1 ± 0.9 after 18 hours and 24 hours respectively. The CYP spontaneous 15 metabolism increased theses values to 17.2 ± 0.5, 27.8 ± 0.8 and 42.2 ± 1.0 two hours after the reference time at 12, 18 and 24 hours respectively. The addition of cigarette smoke solution (CSS) induced a much more dramatic change during the same two hours period leading to a final BPDE-dG value of 36.9 20 ± 1.2, 56.7 ± 0.9 and 80.2 ± 1.2 (mean ± s.d.) Og of adducts per mg after 12, 18 and 24 hours respectively. Figure 6. BPDE-dG binding in MCF-7 cells after exposure to BP 2.5 pM or BP 2.5 pM + CS solution obtained from standard 25 filter and filter containing rosemary extract. The cigarette smoke solution was added for the last 2 hours during the exposure to BP for the time indicated (Scheme 1). Analysis of BPDE-dG was performed as described in Materials and Methods. The HPLC runs show that there is only one peak on 30 chromatograms which correspond to BP-tetrol I derived from (+) -anti-BPDE-dG. Values represent the means of two independent experiments with 4-6 HPLC runs plus Std. Scheme 1. MCF-7 cells were treated with BP for 12 hrs and 18 hrs following with cigarette smoke for another 2 hours 5 WO 2008/060286 PCT/US2006/044704 together with BP (experiments A and B respectively). The goal of this experiment was to activate at different times the BP to produce BP-7,8-diol and after treat the cells with cigarette smoke and follow its effect during the last 2 hours. 5 The control represents cells treated only with BP. Table 1. Effect of scavengers on BPDE-dG level caused by cigarette smoke in a cell-free system 10 % BPDE-dG relative Treatment to standard CS Standard CSS 100 + Superoxide Dismutase SOD (20 pg) 16 15 + Catalase (4 pg) 12 + Inactivated Catalase (4ig) 100 Romarin filtered CS5 instead Standard CSS 42 The standard CSS system includes 2 ml calf thymus DNA (3 20 mg/ml), 600 il 30 p1M (+) BaP-7,8-diol and 5 ml of diluted CSS with PBS (1:19) at pH 7.4, and was incubated at room temperature fir 2h. Each value was obtained from three independent experiments performed in duplicate. The average error was about 12% in each duplicate experiment. The BPDE-dG 25 value of the standard was 56 ± 6.3 (mean ± s.d.) adducts per mg DNA. 6 WO 2008/060286 PCT/US2006/044704 5. Detailed Description Cigarette smoking is causally associated with a large number of human cancers. Tobacco use is by far the most widespread link between exposure to known carcinogens and 5 death from cancer, and is therefore a model for understanding mechanisms of cancer induction. Benzo(a)pyrene (BP) is a highly carcinogenic polycyclic aromatic hydrocarbon (PAH) present in emission exhausts, charbroiled food and in small quantity in cigarette smoke, 10 typically less than 10 ng per cigarette. BP is one of more than 60 carcinogens in cigarette smoke that is involved in the aetiology of lung cancer. It is metabolically activated into benzo(a)pyrene-7,8-diol-9,10-epoxide (BPDE) which reacts with DNA predominantly at the N 2 -position of guanine to produce 15 primarily N 2 -guanine lesions, e.g. benzo(a)pyrene-7,8-diol 9, 10-epoxide-N2 -deoxyguanosine (BPDE-dG) adduct. The presence of BPDE-DNA adducts in human tissues has been conclusively established and BPDE-dG adduct concentrated exclusively in bronchial cells and is thus implicated in the 20 initiation of human lung cancer. This carcinogen is metabolized by phase I enzymes to a large number of metabolites including phenols, arene oxides, quinones, dihydrodiols, and diol epoxides. An overview of BP metabolic way leading to the formation of (+)-anti-BPDE-dG 25 adduct is presented in Fig. 1. In more detail, the ultimate carcinogen (+)-anti-BPDE is formed from BP by two rounds of cytochrome P450-mediated oxidation. The first step of this oxidation leads preferentially to (-)-7,8-dihydro-7,8-dihydrobenzo(a)pyrene 30 [(-)BP -7,8-dioll. The diol is further oxidised primarily to the highly mutagenic (+)-r-7, t-8-dihydroxy-t-9,10-oxy 7,8, 9,10-tetrahydro-BP [(+)-anti-BPDE]. Numerous studies have clearly identified the [(+)-anti-BPDE] as the primary 7 WO 2008/060286 PCT/US2006/044704 carcinogenic metabolite of BP exhibiting enhanced mutagenic activity in vitro and in vivo. Most previous studies of genetic variation in metabolism of lung carcinogens have focused on metabolic activation by various cytochromes P450s, 5 although expression of these enzymes in lung is generally low) . The activation of BP-7,8-diol by lung epithelial cells is not caused solely by classic CYPs/GSTs dependent biotransformation processes, but also involves several metabolic routes other than CYPs. These include, 10 lipooxygenase, lipid-peroxidation products and peroxidase dependent pathways, COX-l 'and COX-2. Increasing evidence suggests the causal significance of tobacco free radicals in lung cancer induction in smokers. Each puff of smoke forms over 10 trillion free radicals 15 present in smoke, which may contribute to both tumor initiation as well as promotion of various forms of human cancer caused by repeated attacks from ROS on cellular macromolecules. The major free radical species are postulated to be an equilibrium mixture of semiquinones, hydroquinones 20 and quinones. It is suggested that this free radical complex causes redox cycling that generates superoxide anion from molecular oxygen and leads to the formation of hydrogen peroxide and hydroxyl radical. These reactive species cause DNA nicking and single-strand breaks in DNA of cultured 25 rodent and human cells. Quinone-associated redox cycling may also be involved in these effects; hydroquinone and catechol are believed to play a major role. I have discovered that cigarette smoke can activate by its oxygen generated radicals the second step of the BP 30 metabolic- pathway leading to the formation of BPDE-dG adduct, presumably by metabolism of the formed in the cells (-)-BP 7,8-diol to (+)-r-7,t-8-dihydroxy-t-9, 10-oxy-7,8,9,10 tetrahydro-BP [(+)-anti-BPDE] (Fig. 1). 8 WO 2008/060286 PCT/US2006/044704 I have also discovered that this activation is at least twice higher than this obtained with CYPs machinery. Further, I have discovered that ROS from the cigarette smoke may be in part responsible for the increased BPDE-dG 5 adduct formation. T have also found that a filter containing a formulated rosemary powder can reduce considerably the BPDE-dG level due CS oxygen generated radical, and that my discoveries can be used for cigarette filters which reduce the formation of 10 carcinogenic BPDE-dG adduct in bronchial epithelial cells. My invention provides (i) a means for determining the relative contribution of ROS in cigarette smoke on the activation of BP-7,8-diol in comparison with cytochrome P450; (ii) a means for establishing whether cigarette smoke's ROS 15 promotes the carcinogenic process by contributing to the metabolism of BP-7,8-diol resulting in an increase in the formation of the critical lung BPDE-dG; (iii) a filter containing a scavenger of cigarette free radicals to significantly decrease the formation of BPDE-dG ; and (iv) use 20 of said filter to significantly decrease the function of BPDE dG adducts. 7. Examples Chemicals. Proteinase K (EC 3.4.21.64, from Tritirachium 25 album) was purchased from Sigma (St. Louis, MO), RNase T1 (EC 3.1.21.3, from Aspergillus oryzae) and RNase (DNase free, heterogeneous mixture of ribonucleases from bovine pancreas) were obtained from Boehringer Mannheim (Mannheim, Germany) . Phosphate-buffered saline (PBS) contained 3.0 mM KCl, 1.5 mM 30 KH 2

HPO

4 , 140 mM NaCl, 8.0 mM Na 2

HPO

4 , (pH 7.4), HPLC-grade water, MeOH, ether and ethanol for spectroscopy from E. Merck, Darmstadt, Germany. If not stated otherwise, the others chemicals were purchased from Sigma (L'Isle d'Abeau Chesnes, 9 WO 2008/060286 PCT/US2006/044704 France), Boehringer Ingelheim (Heidelberg, Germany) and Boehringer Mannheim (Mannheim, Germany). All BP metabolite standards were obtained from National Cancer Institute, Chemical Carcinogen Reference Standard Repository Midwest 5 Research Institute (Kansas City, Mo) . Apparatus. High-performance liquid chromatography (HPLC) was carried out with a Hewlett-Packard high pressure isocratic and gradient systems (Waldborn, Germany) equipped with a Shimadzu RF-1OAXL fluorescence detector linked to a Hewlett 10 Packard integrator. Preparation of Cigarette Smoke/PBS Solution (CSS). Smoking was performed according to Pryor et al without the Cambridge filter. Essentially the same smoke collecting method has been used earlier by Nakayama et al. The smoke 15 from burning 8 cm of one cigarette (Marlboro) during 3.8 min with the help of constant vacuum generated from a water pump was bubbled through 10 ml of phosphate-buffered saline (PBS) solution which traps both the gas-phase and tar cigarette smoke chemicals. As there were no water-insoluble tar 20 compounds present on the walls of the wash bottles, a major part of the water-soluble compounds from the smoke of a single cigarette was contained in the 10 ml PBS solution. This aqueous solution named cigarette smoke solution (CSS) was reacted immediately with exogenous DNA or added to MCF-7 cells 25 in culture in the presence of benzo(a)pyrene or its proximate metabolite (+)-BaP-7,8-diol. Different dilutions of CSS were used (see below). Incorporation of a Rosemary Powder Extract into the cigarette Filter. The filter of the conventional cigarette 30 was removed and 40 mg of a rosemary powder extract, was introduced in the place free from the filter near to the cigarette itself. After this operation, the filter was reinstalled. The effect of this filter was evaluated by mass 10 WO 2008/060286 PCT/US2006/044704 spectrometry. Briefly the cigarette smoke was bubbled in an organic solution containing 3,3,5, 5-tetramethyl-l-pyrroline-N oxide (TMPO) a spin trap adduct. The amount of hydroxyl radical adduct was then quantified using liquid 5 chromatography, mass spectrometry. Under the smoking conditions used a 30% decrease in the hydroxyl radical was observed. Reaction of Exogenous DNA with (+)-BP-7,8-Diol in Presence of Diluted Cigarette Smoking Solution (CSS). 2 ml 10 calf thymus DNA (3 mg/ml) was added to 5 ml diluted 20 times CSS and reacted for 2 hours at room temperature with (+)-BP 7,8-diol (final concentration 3.6 pM) according to the following reaction: DNA + [ (+)-BP-7, 8-diol]+CSS-+ (-)-anti-BPDE-N 2 -dG 15 The level of the resulting (-)-anti BPDE-dG adduct was measured (see below) . As control an experiment without CSS was performed. Cell Culture Conditions and Treatment. The human mammary carcinoma cell line MCF-7 was grown in 150-cm 2 cell culture 20 flasks in a total volume of 20 ml minimal essential medium E MEM supplemented with 10% FCS, 15 mM Hepes buffer, and antibiotics (200 units/ml penicillin, 200 tg/ml streptomycin, and 25 pg/ml ampicillin) . Cells were maintained and treated at 37 0 C in 5% C0 2 /95% air atmosphere. 25 After MCF-7 cells had covered 90% of the surface area of the flasks, (2-3 days after splitting of a confluent culture), the medium was replaced with 20 ml of fresh medium containing 10% serum. Twenty four hours later, near-confluent cells e.g. more than 90% of cells in GO/G1 phase were treated with DMSO 30 alone or with carcinogen (see below) dissolved in DMSO and cigarette smoke/PBS (CSS see above). The final concentration of DMSO did not exceed 0.1% of the total incubation volume. 11 WO 2008/060286 PCT/US2006/044704 Control samples included in each incubation set were treated with DMSO alone. a) Treatment of MCF-7 Cells with (+) -BP--7,8-Diol and Cigarette Smoke. Cells were treated for 2 hours with (+)-BP 5 7,8-diol (0.2 pM) alone or in presence of different dilutions of CSS. The (+)-BaP-7,8-diol was activated by ROOO generated from the CS and cell CYP's to form (-)-anti-BPDE-dG and (+) syn-BPDE-dG respectively. Their levels were measured by the formation of BP-tetrol 1-1 and BP-tetrol 11-2 (see below and 10 Fig. 3). b) Time/Dose Exposure Experiments with BP. To characterize time/dose exposure to BP and BPDE-dG level, cells (l0xlO cells /150 cm 2 flask, total volume of 20 ml) were treated with medium containing final concentration of 1.25, 15 2.5 and 5.0 pM each for 6,12,18 and 24 hours (two flasks/dose/time point). BPDE-dG adduct formed in the cells increase linearly in a dose-and time-dependent manner to as was shown also by others (30). On the basis of the results obtained we choose 2.5 y as working concentration for BP. 20 c) Treatment of MCF-7 Cells with BP and Cigarette Smoke. To see the effect of CS concentration, the experience A of scheme N 0 1 was performed with different CSS dilutions (1:79; 1:39; 1:19; 1:9 vol/vol). On the basis of the results obtained from this experience I choose 1:19 (vol/vol) dilution 25 as working CS concentration. Thus, the cells (see above "Cell Culture and Treatment") were treated with BP (2.5 pM) and CSS (dilution 1:19 vol/vol) according to Scheme 1 (See Figure 6 Scheme 1) . All incubation sets were repeated 2-3 times with 30 duplicate samples. At the end of treatment, cells were examined microscopically for morphological changes, then harvested by trypsinization with 0.05% trypsin-EDTA (0.05% 12 WO 2008/060286 PCT/US2006/044704 trypsin, 0.14 M NaCl, 3 M KCl, 0.1 M Na 2

HPO

4 , 1.5 M K 2

HPO

4 , 0.5 M EDTA). After addition of an equal volume of medium containing 10% FCS, the cells were centrifuged at 1000 g, washed three times with PBS, and the cell pellet then stored 5 frozen at -201C. The viability of the cells treated with BP and cigarette smoke or (+)-BP-7,8-diol and cigarette smoke was roughly 90% at the time of harvesting as determined by a Trypan blue exclusion assay. The doses used did not show any cytotoxicity as measured by lactate dehydrogenase activity 10 assay (ELISA Kit, Boehringer, Mannheim). DNA Preparation and Hydrolysis. DNA isolation from MCF-7 cell pellets was carried out by treatment with RNase, proteinase K, salting procedure (31) and chloroform. Briefly, the cell pellets were resuspended in EDTA-sodium dodecyl 15 sulfate (SDS) buffer [10 mM Tris buffer, 1 mM Na 2 EDTA, 1% SDS (w/v) , pH 8] incubated for 1 h at 37 0 C with RNase TI (2000 U/ml) and RNase A (DNase free; 100 pg/ml) on a shaker (100 rpm). Then proteinase K (300 ig/ml) was added and the incubation continued overnight at 37 0 C. After digestion, 6M 20 NaCI was added to have final concentration of IM followed by a centrifugation at 10000 g. DNA in the supernal was precipitated with 2 vol. ethanol, washed with 70%, 100% ethanol, ether, dried and dissolved in 10 mM Tris buffer. Again, RNase A (100 pg/ml) and RNase Ti (2000 U/ml) were added 25 and the solution incubated at 371C for 1 h. followed by proteinase K (100 yg/ml) for another 2 hours at 370C. The solution was extracted once with chloroform, centrifuged and the solution was made im NaCl. DNA was precipitated with 2 vol. cold ethanol. 30 The portion of DNA to be hydrolyzed was rinsed with 100% ethanol to remove unbound BP-tetrols. The DNA, free of unbound BP-tetrols, was dissolved in water and the DNA concentration was determined by A 260 m.. The purity was ascertained by the ratios at A 260

/A

280 and A 2 60

/A

230 . The amount 13 WO 2008/060286 PCT/US2006/044704 of DNA for analysis was hydrolyzed as described previously by incubation at 90 0 C for 4 hour in a final concentration of 0.1 N HCl. This releases tetrols (Fig. 3) from BPDE-DNA adducts with > 90% recovery. The volume of the hydrolysate for 5 injection was made 700 pil containing 5-10 pig DNA. Determinations of BPDE-N 2 -dG adduct level. The adduct levels were determined by HPLC-FD as previously described [32,331 using r-7,c-9,t-8,t-10-tetrahydroxy-7,8,9,10 tetrahydrobenzo(a)pyrene (BP-tetrol II-1) as an internal 10 standard [341. The hydrolysate was loaded onto a Latex pre column module (HD-Germany) containing 5 pm Ci 8 reverse-phase materiel (Nucleosil 100) equilibrated with 10% MeOH and washed for 20 min with 12 ml 10% MeOH. Subsequently, the pre-column was switched by a Valco Instruments switching valve to flow 15 over a 4.6 mm x 25 cm 5 pm C 18 reverse-phase (Nucleosil 100) analytical column (Alltech GmbH, Unterhaching, Germany) . The products obtained by hydrolysis were eluted with the following MeOH/H 2 0 gradient: 50%, 0-17 min; 50 to 60%, 17-32 min; 60%, 32-42 min; 60 to 100%, 42-57 min. Retention times of the BP 20 tetrols were: BP tetrol I-1 (trans-anti-BP-tetrol) (35.2 min); BP-tetrol II-1 (trans-syn-BP-tetrol), internal standard (36.9 min); BP tetrol 11-2 (cis-syn-BP-tetrol)(42.3 min). Fluorescence was assessed at an excitation wavelength of 344 nm and emission wavelength of 398 nm. As I did not detect the 25 formation of BP tetrol II-1 in separate analysis of MCF-7 samples, I used it as internal standard (2 pg added to each HPLC run) for verification of the relative retention time. The detection limit was 0.5 pg of BP tetrol I-1 and BP-tetrol II-l. The level of each BP-tetrol was determined by using a 30 standard curve generated from the fluorescence peak area of authentic BP-tetrol standard analyzed just before the analysis of MCF-7 samples. The BP-tetrol-I-1 detected is derived after hydrolysis of (+)-anti-BPDE-DNA adduct. The hydrolysis of ( )-anti-BPDE-dG leads to the formation of BP-tetrol 1-2, which 14 WO 2008/060286 PCT/US2006/044704 however is unstable and is converted in BP-tetrol I-1 (Fig. 3) (38). Thus, the level of the formed (-)--anti-BPDE-dG was measured by the quantity of BP-tetrol I-1 found on HPLC runs. Based on the finding that BPDE reacting with DNA produce 5 primarily BPDE-N 2 -dG (7), I assumed that BP-tetrol-I-1 level corresponds to this of BPDE-N 2 -dG. The level of BPDE bound to MCF-7 DNA was quantified in duplicates. The adduct level was calculated from the equitation 1 pmol/mg DNA / 3.125 = 1 adduct per 106 nucleotide. The HPLC runs were quantitatively 10 reproducible, and variability between the two assays was lower than 5%. The mechanism of mutagenesis by BP is sufficiently well defined and used as a "molecular signature" to establish the causal nature between particular genetic events in development 15 of tumors and carcinogenic exposure (the "smoking gun") . The "BP molecular signature" has major implication for pinpointing the tobacco smoke as the cause of human lung cancer, and for the elaboration of specific strategies to minimize tobacco smoking, or introduce preventive measures. Specific agents 20 used in cancer chemoprevention appear to act by inhibiting carcinogen damage to DNA, mutagenesis, tumor promotion and/or tumor progression. I have explored the relative role of CS on the biotransformation of BP-7,8-diol to BPDE capable of forming 25 stable DNA adduct in human cells. Numerous studies have demonstrated that stable PAH-DNA adducts can lead to mutations through mis-incorporation of nucleotides or deletion. CS is an aerosol of complex chemical composition containing both organic and inorganic compounds, of which 4800 have been 30 identified so far. Both vapor phase and particulate phase of smoke are known to possess free radicals. While the gas phase radicals are generally short-lived the radicals in the particulate phase are relatively stable and consist of a hydroquinone, semiquinone, quinone complex, this complex is an 15 WO 2008/060286 PCT/US2006/044704 active redox system capable of reducing molecular oxygen to produce superoxide, eventually leading to hydrogen peroxide and hydroxyl radicals. In addition, at least 60 different CS carcinogens have been implicated in tumor initiation and 5 promotion; the most potent carcinogens agent contained in CS are BP and NNK (4- (methylnitrosamino) -1- (3-pyridyl) -1 butanone). The Effect of Cigarette Smoke on (+)-anti-BPDE-dG Using a Cell-Free System Concomitant with DNA Adduction. To elucidate 10 the mechanism of BPDE-dG formation dependent from active oxygen generated from cigarette smoke, I looked for this adduct in cell-free in vitro system concomitant with DNA adduction. The CSS solution containing the gas-phase and tar cigarette smoke radicals was immediately reacted with DNA in 15 the presence of (+)-BP-7,8-diol (see protocol above). The results from this experiment show that CS can oxidize the (+) BP-7,8 diol to (-)-anti-BPDE which in turn form the (-)-anti BPDE-dG adduct. The amount of (-)-anti-BPDE-dG increased linearly and dose dependently (See Fig. 2). 20 Previously it was found that large amounts of active oxygen such as H202 and 02~ were generated from cigarette smoke after trapping the smoke in PBS. This active oxygen generated from cigarette smoke might be responsible for the observed formation of (-)-anti-BPDE-dG. To verify this, I checked the 25 effect of catalase and superoxide dismutase (SOD) on the (-) anti-BPDE-dG produced, and found that the both enzymes inhibited the formation of the adduct. Inactivated catalase showed no effect (Table 1). From these results I concluded that cigarette smoke can oxidize (+)-BP-7,8-diol, thus forming 30 (-)-aneti-BPDE-dG, and that such capacity can be explained mainly by the action of oxygen generated from cigarette smoke. The Effect of Cigarette Smoke on (-)-anti-BPDE-dG Adduct Formed in MCF-7 Cells Treated with (+)-BP-7,8-diol. Two 16 WO 2008/060286 PCT/US2006/044704 independent pathways have been shown to participate in the metabolism of BP-7,8-diol to BPDE (Fig.3). The cytochrome P450 dependent metabolism of the (+)-enantiomer leads preferentially to (+) -syn-BPDE whereas the pathway involving 5 haem-containing proteins in conjunction with a peroxide (e.g. lipid peroxide) preferentially results in (-)-anti-BPDE. The (-)--BP-7,8-diol on the other hand, may be metabolized by both pathways and results in the formation of (+)-anti-BPDE, the ultimate form of BP, and (-)-syn-BPDE. The different pathways 10 can be distinguished by HPLC analysis since the tetrols derived from anti- and syn-BPDE respectively are clearly separated under my conditions. To investigate further the role of cigarette smoke dependent epoxidation of (+)-BP-7,8-diol leading to the 15 formation of (-)-anti-BPDE that form with DNA (-)-anti-BPDE-dG adduct, human mammary cell line MCF-7 was used. The reason for which I used MCF-7 cells to see the effect of cigarette smoke ROS on the activation of (+)-BP-7, 8 diol was that these cells have little peroxidase activity. The cells were treated 20 with the (+)-BP-7,8--diol, a stereochemical probe which can distinguish the adducts formed by ROS and CYPs dependent ways (Fig. 3). Two distinct peaks were observed on the chromatograms corresponding to BP-tetrol I and BP-tetrol II derived from (-)-anti-BPDE-dG and (+)-syn-BPDE-dG respectively 25 refss. 32-34). Cigarette smoke increased linearly and dose dependently the ROS dependent formation of (-)-anti-BPDE-dG (Fig. 4a) and decreased the CYPs dependent formation of (+) syn-BPDE-dG adduct measured by the formation of BP-tetrol II. This decrease is also dose dependant and the inverse of DNA 30 adducts increased linearly with cigarette smoke concentration (4b). The inhibitory effect of CS on CYPs dependent formation of (+)-syn-BPDE-dG and increased formation of (-)-anti-BPDE-dG adduct confirm the role of the oxygen generated from the cigarette smoke in the formation of (-)-anti-BPDE-dG adduct. 17 WO 2008/060286 PCT/US2006/044704 Other studies showed that induced CYPs activity was impaired by the oxidative challenge. The mechanism underlying such a phenomenon could be a down-regulation of cytochrome P4501A1 gene. Having little peroxidase activity may lead MCF 5 cells under "stress" conditions to increased DNA damage and reduced repair capacity. Consequently this may cause an increase of BPDE-DNA adducts independently from BP-7,8-diol activation. The Effect of Cigarette Smoke on BPDE-dG Adduct Formed in 10 Cells Treated with BP. Previous studies with MCF-7 cell cultures revealed that these cells possess inducible P4501B1 and P4501A1 activity. The presence of P450 catalyzed metabolic turnover of BP and the absence of detectable peroxidase activity in MCF-7 cells, allowed the evaluation of 15 the role of cigarette smoke oxygen radicals on BP activation in human cell cultures. MCF-7 cells have high CYP1Al enzyme activity for the metabolic activation of BP leading to the formation of (-)-BP-7,8-diol and consequently to (+)-anti BPDE-dG (Fig. 1). The level of adduct formation at 6 hours 20 was considerably lower than that observed after 12 and 24 hours of exposure. After treatment with 2.5 pM BP for 6 hours approximately. 2000 pg adducts per mg DNA were formed, whereas more than 11000 pg and more than 20000 pg adducts per mg DNA were present after 12 hours and 24 hours respectively 25 (Wilcoxon Rank Sum Test gives p=0.0022). The cells were treated for 12 and 18 hours with BP to induce the formation of (-)-BP-7,8 diol which is substrate for ROS. Indirect confirmation for the preferentially formation of (-)-BP-7,8-diol is the absence of BP-tetrol II derived from 30 syn-BPDE on HPLC runs which precursor is (+)-BP-7,8-diol (Fig.3). The cells were then exposed for 2 hours with CSS of cigarette smoke together with BP. The HPLC runs show that there is only one peak on chromatograms which correspond to BP-tetrol I derived from (+)-anti-BPDE-dG. The difference 18 WO 2008/060286 PCT/US2006/044704 between cells treated with CSS and those non treated (controls) is presented on Fig. 5. As mentioned above the cell line used in this study maintained the capability to lower the CYPlAl expression after oxidative challenge by CS. 5 The suppression of cytochrome P450 presumably lowers activation of BP to (-)-BP-7,8-diol and (+)-anti-BPDE. Thus the increased difference by CS is due to the increased metabolism of (-)-BaP-7,8 diol by ROS generated from CS. Wilcoxon Rank Sum Test gives p=0.0022 for treated with CS vs 10 controls for 14 hours and 20 hours respectively. Recently Dramatic damage by BP of DNA occurs in human bronchial epithelial cells forming BPDE-dG adduct which could be considered as "critical" for the initiation of human lung cancer bronchial epithelial cells. Thus, active oxygen 15 species generated in cigarette smoke could play an important role in the formation of this "critical" adduct in bronchial epithelial cells (Fig. 1). The Effect of Filter Containing Rosemary Extract on the Formation of BPDE-dG Adduct. Rosemary (Rosmarinus officinalis 20 Labiatae) herb and oil are commonly used as spice and flavoring agents in food processing for its desirable flavor and high antioxidant activity. Topical application of rosemary extract, carnasol or ursolic acid to mouse skin inhibited the covalent binding of benzo(a)pyrene to epidermal 25 DNA, tumor initiation by 7,12-dimethylbenz(a)antracene (DMBA), TPA-induced tumor promotion, ornitine decarboxylase activity and inflammation. Rosemary extracts were proved to be efficient not only in the promotion phase but also in the initiation phase. Rosemary extracts, carnosic acid and 30 carnosol strongly inhibit phase I enzyme, CYP 450 activities and induce the expression of the phase II enzyme, glutathione S-transferase (GST) and quinone reductase activities. Carnosol inhibits nitric oxide (NO) production in activated 19 WO 2008/060286 PCT/US2006/044704 macrophage. The antioxidant property had been referred to as the mechanistic basis of their protective effects. With the aim of removing free radicals and reactive oxygen species in the cigarette smoke a small amount of 5 rosemary powder was incorporated in a standard filter (see Materials). The decrease in free radicals in the condensate induced by the filters incorporating a rosemary extract was estimated by the quantitation of the hydroxyl radical content of CSS with a spin trap (TMPO) using LC-ESI-MS/MS. Under the 10 smoking conditions used a 30% decrease in the hydroxyl radical was observed. Due to the efficiency of this filter to reduce the level of the free radicals in cigarette smoke, as compared to a comparable standard Marlboro filter without the additive, I compared the effect of CS passed through this filter in 15 comparison to the standard filter on the formation of BPDE-dG using MCF-7 cells. The results presented in Fig. 6 were obtained when the MCF-7 cells were treated with BP. Two groups of experiments were performed (A and B). The cells were treated with BP for 20 12 and 18 hours respectively following with CSS from the two filters for another 2 hours together with BP (Scheme 1). To evaluate the CYPs dependent increase of the adduct during these last 2 hours, two controls for each group were performed : 12 and 14 hours for group A, 18 and 20 hours for group B. 25 The CSS from the standard filter double the binding level obtained for 14 and 20 hours. However, the rosemary filter strongly impedes the increase obtained by the standard filter, more than 70% in the two groups (Fig. 6). ). The modified filter scavengers ROS and 30 consequently decreases the activation of (-)-BP-7,8-diol (Fig. 3). Aside from the reduction of the free radicals, rosemary powder may have also other mechanisms to reduce BPDE-dG formation. 20 WO 2008/060286 PCT/US2006/044704 Using whole rosemary extract (6 pg.ml") also inhibits CYPlAl activity and DNA adduct formation by 80% after 6 hours co-incubation with 1.5 pM BP in human bronchial epithelial cells (BEAS-2B) . Thus, using filters which decrease the 5 amount of the free radicals to reduce the formation of the critical tumorogenic adduct are a significant benefit for the addicted smokers. My inventive rosemary cigarette filter therefore is a promising candidate for chemopreventive programs with the aim 10 to reduce BPDE-dG in bronchial epithelial cells. It will be understood that the above description of the present invention is susceptible to various modifications, changes and adaptations, and the same are intended to be comprehended within the meaning and range of equivalents of the 15 appended claims. The most obvious modification, for example, is the use of various gel materials as the electroresponsive composition of matter. It will thus be seen that the objects set forth above, among those made apparent from the preceding description, are 20 efficiently attained and, since certain changes may be made in carrying out the above method (process) without departing from the spirit and scope of the invention, it is intended that all matter contained in the above description shall be interpreted as illustrative and not in a limiting sense. 25 It is also to be understood that the following claims are intended to cover all of the generic and specific features of the invention herein described and all statements of the scope of the invention which, as a matter of language, might be said to fall there between. 21

Claims (10)

1. A method for reducing human lung benzo(a)pyrene diol epoxide-dG (BPDE-dG) adducts from cigarette smoke generated by smoking a cigarette having a filter, said method 5 comprising the steps of passing the cigarette smoke through the filter wherein said filter is impregnated by an extract of a plant from the Labiatae family wherein said extract comprises polyphenolcompounds or derivatives thereof.

2. The method according to claim 1, wherein the plant 10 is rosemary.

3. The method according to claim 1 wherein the extract is generated by extraction with an alcoholic solvent or an aqueous alcoholic solvent.

4. A method for reducing human lung benzo(a)pyrene diol 15 epoxide-dG (BPDE-dG) adducts from cigarette smoke generated by smoking a cigarette having a filter, said method comprising the steps of passing the cigarette smoke through the filter wherein said filter is impregnated by a mixture comprising at least one polyphenol compound or its 20 derivative.

5. The method according to claim 4, wherein the mixture comprises at least one polyphenol compound or a derivative thereof selected from the group consisting of carnosol, rosmanol, rosmarinic acid, and carnosic acid. 25

6. The method according to claim 5, wherein the mixture comprises carnosol, carnosic acid, rosmarinic acid, and rosemanol.

7. The method according to claim 6, wherein the mixture comprises carnosic acid or carnosol. 22 WO 2008/060286 PCT/US2006/044704

8. The method according to claim 7, wherein the filter comprises from 0.5 g to 0.1 mg of at least one polyphenol compound or its derivative.

9. The method according to claim 7, wherein the filter 5 comprises 0.01 g of at least one polyphenol compound or its derivative.

10. The method according to claim 7, wherein the at least one polyphenol or its derivative is coupled to a polymeric carrier or is in a microcapsule matrix or is added to the 10 fibers of a filter. 23