HVRII of mtDNA in cord blood cells of newborn children and in their saliva 10 years later.

Comparison of hypervariable region II nucleotide sequences of mitochondrial DNA obtained from cord blood cells and saliva cells of the same individual at birth and after ten years revealed a few differences at the so-called mutation hot spots (three transitions and three indels within the C-tract). The personal identity of samples was proved by short tandem repeat profiling. Comparison of individuals living in two regions that differ by air pollution, however, did not reveal statistically significantly increased number of mutations in the population from the region of poorer environmental conditions, although indicating such tendency.

Genetic variability of HVRII mtDNA in cord blood and respiratory morbidity in children.

Genetic polymorphisms were examined using direct sequencing of the hypervariable region II (HVRII) in the D-loop of mtDNA in the cord blood of 355 children living in two areas of the Czech Republic - the industrial district of Teplice and the agricultural district of Prachatice. The incidence of the most frequent nucleotide variants of HVRII, C150T (10.1%), T152C (19.7%), T195C (19.7%) and 309.nC (41.4% for 309.2C and 13.8% for 309.3C), and the respiratory morbidity at the ages of 0-2 years and 2-6 years were investigated, considering many other factors such as locality, gender, ethnicity, heating by coal in household, maternal age, asthma bronchiale, allergic rhinitis, pollinosis, conjunctivitis and maternal tobacco exposure during and after pregnancy. We found that the T195C transversion in HVRII is connected with an increased risk of early childhood (0-2 years) bronchitis (RR 1.38, p=0.034, 95% CI 1.04-1.85) and with increased risk of otitis media in children aged 2-6 years (RR 1.62, p=0.032, 95% CI 1.04-2.53). Another polymorphism, 309.nC, is associated with an increased risk of bronchitis in children aged 2-6 years (RR 1.46, p=0.030, 95% CI 1.04-2.06). The results indicate that genetic polymorphisms in mtDNA may be an important factor not only for various types of cancers and neurodegenerative diseases, but also for respiratory morbidity in children.

In vitro genotoxicity of PAH mixtures and organic extract from urban air particles part I: acellular assay.

Acellular assay of calf thymus DNA+/-rat liver microsomal S9 fraction coupled with (32)P-postlabelling was used to study the genotoxic potential of organic compounds bound onto PM10 particles collected in three European cities-Prague (CZ), Kosice (SK) and Sofia (BG) during summer and winter periods. B[a]P alone induced DNA adduct levels ranging from 4.8 to 768 adducts/10(8) nucleotides in the concentration dependent manner. However, a mixture of 8 c-PAHs with equimolar doses of B[a]P induced 3.7-757 adducts/10(8) nucleotides, thus suggesting the inhibition of DNA adduct forming activity by interaction among various PAHs. Comparison of DNA adduct levels induced by various EOMs indicates higher variability among seasons than among localities. DNA adduct levels for Prague collection site varied from 19 to 166 adducts/10(8) nucleotides, for Kosice from 22 to 85 and for Sofia from 6 to 144 adducts/10(8) nucleotides. Bioactivation with S9 microsomal fraction caused 2- to 7-fold increase in DNA adduct levels compared to -S9 samples, suggesting a crucial role of indirectly acting genotoxic EOM components, such as PAHs. We have demonstrated for the first time a significant positive correlation between B[a]P content in EOMs and total DNA adduct levels detected in the EOM treated samples (R=0.83; p=0.04). These results suggest that B[a]P content in EOM is an important factor for the total genotoxic potential of EOM and/or B[a]P is a good indicator of the presence of other genotoxic compounds causing DNA adducts. Even stronger correlation between the content of genotoxic compounds in EOMs and total DNA adduct levels detected (R=0.94; p=0.005) was found when eight c-PAHs were taken into the consideration. Our findings support a hypothesis that a relatively limited number of EOM components is responsible for a major part of its genotoxicity detectable as DNA adducts by (32)P-postlabelling.