Impact of PAH Exposure on Accumulation of Translesion DNA Polymerases in Mouse Colon Jacki L. Coburn Mentor: Dr. Andrew B. Buermeyer Colorectal Cancer • In the U.S., 70,270 men and 68,857 women were diagnosed with colorectal cancer in 2006. • The same year, 26,801 men and 26,395 women died of colorectal cancer in the U.S. • Exposure to polycyclic aromatic hydrocarbons (PAHs) is associated with increased risk of developing colon cancer. Benzo[a]pyrene (B[a]P) • Volatilized during combustion of organic compounds • Present in coal tar and diesel exhaust • Highly mutagenic and carcinogenic Routes of Exposure Inhalation (air pollution, use of tobacco products) Dermal contact (soot and coal tar derivative products) Ingestion (contaminated water, cooked meat products and vegetable oils) Levels of B[a]P Found in Selected Foods* Sample PPB (ng/g) BBQ Steak, Very Well Done 4.75 BBQ Chicken (bone and skin), Well Done 4.57 BBQ Hamburger, Medium 0.56 Pumpkin Pie 0.47 Fast Food French Fry 0.22 Tomato (Fresh) 0.19 *Kazerouni N., Sinha R., Hsu C.-H., Greenberg A., Rothman N.Analysis of 200 food items for benzo[a]pyrene and estimation of its intake in an epidemiologic study(2001)ハ Food and Chemical Toxicology,ハ39ハ(5),ハpp.ハ423-436. B[a]P is converted to its diol epoxide (BPDE) through cellular enzymatic action. Cytochrome P4501A1 Epoxide Hydrolase Benzo[a]pyrene (+)-benzo[a]pyrene7,8-dihyrodiol-9,10epoxide BPDE bonds with DNA to form a bulky adduct BPDE Lesion on DNA Image courtesy of Zephyris B[a]P-Adducted Guanine Image courtesy of Peter Hoffman Impact of B[a]P Adduct on DNA Synthesis • Replication stalls at B[a]P adduct site • Translesion polymerases (TLPs) are recruited for synthesis • Polymerase (Pol) - B[a]P adducts • Polymerase (Pol) - UV photodamage The ProblemWith TLPs • Specialized TLPs preferentially add correct bases at specific lesion sites, but replicate in an errorprone manner downstream from the lesion. Why? • Larger active site • Lack of proof-reading ability Pol almost exclusively inserts C opposite B[a]P-adducted G, while Pol inserts bases at random, and Polι preferentially inserts G. ? Rechkoblit,O et al. J. Biol. Chem. 2002;277:30488-30494 ©2002 by American Society for Biochemistry and Molecular Biology Regulation of TLPs • Pol is known to be stabilized by UV radiation and ubiquitin-tagged for destruction by proteasomes • Regulation of Pol is not as well understood • How specific TLPs are recruited for bypass of specific lesions is unknown • Local concentration of TLPs may be important in selection process Hypothesis Pol levels are higher in BPDE-induced target cells because Pol can accurately bypass bulky adduct lesions such as those formed by PAHs. Predictions • Pol levels will be greater in BPDE-treated target cells than in negative control target cells. • Levels of Pol will increase relative to Pol levels when induced by BPDE. • Levels of Pol will be very low, if not undetectable. • Pol levels will peak shortly after dosing, then slowly taper off Research Questions • What is the normal, uninduced level of Polη and Pol in the target cells? • How do Polη and Pol levels in the target cells change with increasing dosages of BPDE? • How many hours after dosing does the Pol level peak? Experimental Design Test subjects are Pol/Polη proficient wild-type laboratory mice, with one negative control group and test groups given different doses of BPDE. Negative Control (No BPDE) Mice are harvested at different times following exposure to BPDE 0 hr 8 hr 2 hr 4 hr 12 hr 24 hr Quantitative Western Blots Pol Lysate Pol Lysate Pol Lysate Lysate Lysate Pol K/O Cell Pol Pol Pol Pol Lysate Pol Lysate Pol Lysate Lysate Lysate Pol K/O Cell Pol Pol Chemiluminescence Pol Chemiluminescence Standard Curves Interpolating Polymerase Levels in Mouse Extracts Negative Control BPDE BPDE BPDE (No BPDE Pol Chemiluminescence Mouse Colon Extracts Pure Pol Mouse Colon Pol Negative Control (No BPDE Pol BPDE BPDE BPDE Chemiluminescence Mouse Colon Extracts Pure Pol Mouse Colon Pol Expected Relationships Temporal Variation of Polymerase Levels after BPDE Dosing Predicted BPDE-Induced Accumulation of Pol Pol Pol Pol Undetectable Undetectable Polymerase Level Polymerase Level Pol Time Increasing Dose of BPDE Detection of Pol 250 250 250 150 150 150 150 100 100 100 75 75 75 50 50 50 Ladder 6.25 g HeLa 12.5 g HeLa 25 g HeLa 50 g HeLa Signals at 90 kDa detected by a mouse monoclonal Pol antibody. Ladder 40 ng 80 ng Pol Pol Ladder Full-length purified protein does not co-migrate with signal in HeLa (100 kDa) Detection of Polη 250 250 250 250 150 150 150 150 100 100 100 100 75 75 75 75 50 50 Polη signal is very weak in HeLa and may not be detectable in mouse tissues 50 50 Non-specific signal from secondary antibody comigrates with Polη Benefits of this research • First quantification of Pol and Polη in normal and B[a]P induced cells • Understanding of dose-response relationship and temporal variance of Pol BPDE in target cells • Will inform research on the mechanism of TLP recruitment. • Will inform research on normal cellular responses triggered by exposure to PAHs such as B[a]P What’s Next • Quantify full-length protein fraction of purified Pol and Polη • Test rabbit Pol and Polη antibodies to avoid nonspecific interference from secondary antibodies in the mouse extracts. • Create standard curves • Dose mice and analyze extracts Acknowledgements • • • • • • • • Dr. Andrew B. Buermeyer Dr. John Hays and the Hays Lab HHMI Cripps Scholarship Fund Joshua T. Robinson Dr. Vidya Schalk URISC Dr. Anthony C. Zable References • • • • • • • • Shou M, Gonzalez FJ, Gelboin HV. Stereoselective epoxidation and hydration at the K-region of polycyclic aromatic hydrocarbons by cDNA-expressed cytochromes P450 1A1, 1A2, and epoxide hydrolase. Biochemistry. 1996 December 10;35(49):15807-13 G. Mastrangelo, E. Fadda, V. Marzia. Polycyclic aromatic hydrocarbons and cancer in man, Environ. Health perspect., 104 (1996) 1166-1170 A. Ramesh, S.A. Walker, D.B. Hood, M.D. Guillen, K. Schneider, E.H. Weyand. Bioavailability and risk assessment of orally ingested polycyclic aromatic hydrocarbons, Int. Journal Toxicol. 23 (2004) 301-333. 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