Influence of PAHs in ambient air on chromosomal aberrations in exposed subjects: international study - EXPAH

Prenatal PAH exposure is associated with chromosome-specific aberrations in cord blood

Chromosomal aberrations are associated with increased cancer risk in adults. Previously, we demonstrated that stable aberrations involving chromosomes 1-6 in cord blood are associated with prenatal exposure to polycyclic aromatic hydrocarbons (PAHs) measured in air and are disproportionate to genomic content. We now examine whether the association with air PAHs is chromosome-specific and extends to smaller chromosomes. Using whole chromosome paints for chromosomes 1-6, 11, 12, 14 and 19, and a 6q sub-telomere specific probe, we scored 48 cord bloods (1500 metaphases per sample) from newborns monitored prenatally for airborne PAH exposure in the Columbia Center for Children's Environmental Health cohort. Frequencies of stable aberrations were calculated as incident aberrations per 100 cell equivalents scored, and examined for association with airborne PAHs. Aberrations in chromosome 6 occurred more frequently than predicted by genomic content (p<0.008). Levels of both prenatal airborne PAHs and stable aberration frequency in chromosomes 1-6 decreased to half the levels reported previously in the same cohort (mean PAH decreased from 3.6 to 1.8ng/m(3); mean stable aberration frequency from 0.56 to 0.24, SD=0.19). The mean stable aberration frequency was 0.45 (SD=0.15) in chromosomes 11-19. After adjusting for gender, ethnicity, and household smokers, the mean stable aberration frequency increased with increasing PAH exposure: with a doubling of prenatal PAH exposure, the mean stable aberration frequency for the chromosome1-6 group increased by a factor of 1.49 (95% CI: 0.84, 2.66; p=0.17); for chromosomes 11-19 mean stable aberration frequency increased by 2.00 (95% CI: 1.11, 3.62; p=0.02); for chromosome 6 alone, it increased by 3.16 (95% CI: 0.93, 10.77; p=0.06); there was no increase for chromosomes 1-5 (p>0.8). Aberrations in chromosomes 11, 12, 14, 19 and 6 were associated with prenatal exposure to PAHs in air, even at lower levels of PAH in air. The observed chromosome-specific effects of prenatal airborne PAHs raise concern about potential cancer risk.

Chromosomal aberrations by fluorescence in situ hybridization (FISH)--Biomarker of exposure to carcinogenic PAHs

The fluorescence in situ hybridization (FISH) technique with whole chromosome painting for chromosomes #1 and #4 was used to study the impact of air pollution containing higher concentrations of carcinogenic polycyclic aromatic hydrocarbons (c-PAHs) in three European cities, Prague (Czech Republic), Kosice (Slovakia) and Sofia (Bulgaria). In each site were followed an exposed group, who were police officers or bus drivers who work usually through busy streets for at least 8h, and a reference group, who spent more than 90% of their daily time indoors. In Prague, a significant increase was observed in percentage of aberrant cells (% AB.C.) in the police officers compared to the reference group (0.33+/-0.25 versus 0.24+/-0.18, p<0.05). In Kosice, the exposed group differed from reference in the endpoints F(G)/100 1.52+/-1.18 versus 1.12+/-1.30, p<0.05; % AB.C. 0.30+/-0.19 versus 0.21+/-0.20, p<0.05; t/1000 3.91+/-3.18 versus 2.84+/-3.10, p<0.05. In Sofia were followed two exposed groups: police officers and bus drivers. All FISH endpoints were significantly higher in police officers compared to reference group (F(G)/100 1.60+/-0.99 versus 0.82+/-0.79, p<0.01; % AB.C. 0.25+/-0.14 versus 0.13+/-0.13, p<0.01; t/1000 4.19+/-2.65 versus 2.13+/-2.05, p<0.05; rcp 1.46+/-1.07 versus 0.70+/-0.76, p<0.05). In bus drivers compared to reference there was an increase in % AB.C. (0.25+/-0.18 versus 0.13+/-0.13, p<0.05). This is the first study when FISH method was used to analyze the impact of environmental air pollution. According to the original hypothesis it is expected that the most important group of chemicals responsible for the biological activity of air pollution represent c-PAHs.