Fluorescence study of (+/-)-trans-7,8-dihydroxy-7,8-dihydrobenzo(a)pyrene metabolism in vitro and binding to DNA

DNA–carcinogen interaction: covalent DNA-adducts of benzo(a)pyrene 7, 8-dihydrodiol 9, 10-epoxides studied by biochemical and biophysical techniques

Exposure to various chemicals, either due to occupation or lifestyle, is considered to be a major contributing factor to tumour formation in man (Higginson, 1969; Doll and Peto, 1981). An important and prevalent class of potent carcinogenic compounds present in he environment is polycyclic aromatic hydrocarbons (PAHs), which are found in various petroleum and combustion products derived from heat and power generation and motor vehicle exhausts (Baum, 1978). Furthermore, since PAHs are generally formed by pyrolysis of organic matters such as tobacco smoking and certain procedures of food preparation, the PAH exposure to humans is extensive.

DNA–carcinogen interaction: covalent DNA-adducts of benzo(a)pyrene 7, 8-dihydrodiol 9, 10-epoxides studied by biochemical and biophysical techniques

Exposure to various chemicals, either due to occupation or lifestyle, is considered to be a major contributing factor to tumour formation in man (Higginson, 1969; Doll & Peto, 1981). An important and prevalent class of potent carcinogenic compounds present in the environment is polycyclic aromatic hydrocarbons (PAHs), which are found in various petroleum and combustion products derived from heat and power generation and motor vehicle exhausts (Baum, 1978). Furthermore, since PAHs are generally formed by pyrolysis of organic matters such as tobacco smoking and certain procedures of food preparation, the PAH exposure to humans is extensive

DNA–carcinogen interaction: covalent DNA-adducts of benzo(a)pyrene 7, 8-dihydrodiol 9, 10-epoxides studied by biochemical and biophysical techniques

Exposure to various chemicals, either due to occupation or lifestyle, is considered to be a major contributing factor to tumour formation in man (Higginson, 1969; Doll & Peto, 1981). An important and prevalent class of potent carcinogenic compounds present in the environment is polycyclic aromatic hydrocarbons (PAHs), which are found in various petroleum and combustion products derived from heat and power generation and motor vehicle exhausts (Baum, 1978). Furthermore, since PAHs are generally formed by pyrolysis of organic matters such as tobacco smoking and certain procedures of food preparation, the PAH exposure to humans is extensive.

DNA–carcinogen interaction: covalent DNA-adducts of benzo(a)pyrene 7, 8-dihydrodiol 9, 10-epoxides studied by biochemical and biophysical techniques

Exposure to various chemicals, either due to occupation or lifestyle, is considered to be a major contributing factor to tumour formation in man (Higginson, 1969; Doll and Peto, 1981). An important and prevalent class of potent carcinogeniccompounds present in the environment is polycyclic aromatic hydrocarbons(PAHs), which are found in various petroleum and combustion products derived from heat and power generation and motor vehicle exhausts (Baum, 1978). Furthermore, since PAHs are generally formed by pyrolysis of organic matters such as tobacco smoking and certain procedures of food preparation, the PAH exposure to humans is extensive.

Comparison of the solid-matrix luminescence properties of benzo(a)pyrene-DNA adducts on alpha-cyclodextrin/NaCl and trehalose/NaCl matrices

The solid-matrix luminescence properties of (+/-)-trans-7,8-dihydroxy-anti-9, 10-epoxy-7,8,9,10-tetrahydrobenzo(a)pyrene-DNA ([+/-]-anti-BPDE-DNA) adducts were compared on alpha-cyclodextrin (CD)/NaCl and trehalose/NaCl solid matrices. Both the optimum composition for the solid matrices and the best solvent system were obtained experimentally for acquiring the maximum room-temperature fluorescence (RTF) and room-temperature phosphorescence (RTP) signals for the (+/-)-anti-BPDE-DNA. Most of the solid-matrix RTF and RTP data were obtained at 296 K and 93 K for (+/-)-anti-BPDE-DNA adducts adsorbed on 1% alpha-CD/NaCl and 80% trehalose/NaCl. The RTF signals were strong for (+/-)-BPDE-DNA adducts on both solid matrices, but RTP was only obtained on the trehalose/NaCl solid matrices with the 80% trehalose yielding the strongest RTP signal for (+/-)-anti-BPDE-DNA. The fluorescence lifetime data for (+/-)-anti-BPDE-DNA gave two components on 1% alpha-CD/NaCl. For 80% trehalose/NaCl, three components were revealed, but two components were obtained with 80% trehalose/NaCl after ether extraction of the solid matrix. The third component was ascribed to the formation of the tetrols from (+/-)-anti-BPDE-DNA adducts during the drying step in the sample preparation of 80% trehalose/NaCl. The results give the first reported data on the solid-matrix luminescence of the (+/-)-anti-BPDE-DNA adducts. These results should be of considerable interest not only from an analytical viewpoint but as a new means of studying the luminescence characteristics of the adducts.

Carcinogenic optical rotation

It is suggested that viral nucleic acid inserts in vulnerable regions of host cell DNA contribute to cell transformation by introducing 43 degrees of optical rotation at 425 nm, and that a carcinogenic event caused by DNA inserts and adducts is spurious electron ejection from important adenine molecules that may be far from insert/adduct sites.

Probing the microenvironment of benzo[a]pyrene diol epoxide-DNA adducts by triplet excited state quenching methods

Triplet flash photolysis techniques, coupled with quenching of the triplets by molecular oxygen, are utilized as probes of the microenvironment of polycyclic aromatic molecules bound covalently and non-covalently to DNA. The triplet-oxygen quenching properties of the following adducts in aqueous solutions at 25 +/- 1 degrees C were investigated: covalent adducts derived from the reaction of (+/-)-7 beta,8 alpha-dihydroxy-9 alpha,10 alpha-epoxy-7,8,9, 10-tetrahydrobenzo[a]pyrene (BaPDE) and of (+/-)-9,10-epoxy-7,8,9,10-tetrahydrobenzo[a]pyrene (BaPE) with DNA, and non-covalent intercalation complexes of acridine orange (AO) and DNA. In all cases the quenching follows the Stern-Volmer quenching law with a quenching constant of KTO2 approximately equal to 10(9) M-1 X S-1 for the covalent BaPDE-DNA and BaPE-DNA complexes in aqueous solution. This value of KTO2 is characteristic of free molecules (not bound to DNA) and indicates that the pyrene chromophore is totally accessible to oxygen, and is thus not located at an intercalation-type of binding site in these covalent adducts. In contrast, the AO-DNA complexes are characterized by values of KTO2 approximately equal to 10(8) M-1 X S-1 indicating that the intercalated AO molecules are about ten times less accessible to molecular oxygen than free AO molecules. The KTO2 values for the covalent BaPDE-DNA and BaPE-DNA adducts decrease when the DNA concentration is increased in the 1 X 10(-4)-3 X 10(-3) M range (expressed in nucleotide concentration). This effect is attributed to intermolecular DNA-DNA interactions in which segments of adjacent DNA molecules tend to cover the pyrene chromophores on other strands, thus decreasing their accessibility to oxygen. In contrast the values of KTO2 for the non-covalent AO-DNA intercalation complexes are independent of DNA concentration, as expected for interior binding sites.