• Publikační typ
• abstrakt z konference MeSH

• MeSH
• barvení a značení metody   MeSH
• chromozomální aberace účinky léků   MeSH
• cytogenetické vyšetření metody   využití   MeSH
• fluorescenční mikroskopie metody   využití   MeSH
• klinické laboratorní techniky normy   využití   MeSH
• lidé MeSH
• lymfocyty imunologie   účinky léků   MeSH
• preventivní lékařství metody   MeSH
• řízení kvality MeSH
• statistika jako téma MeSH
• testy karcinogenity metody   využití   MeSH
• testy toxicity metody   využití   MeSH
• Check Tag
• lidé MeSH

The rationale for cytogenetic monitoring to determine if safe maximum allowable concentrations (MAC) of genotoxic chemicals are being maintained in a workplace is that exposure levels that do not increase chromosomal aberration frequencies are without harmful effects. Such monitoring, widely used in occupational health programs in the Czech Republic (CR), includes workers exposed to 1,3-butadiene (BD) or other chemicals. Studies of BD exposed workers in the years 1992, 1993, 1994, 1998, and 2004 compared mean frequencies of cells carrying chromosomal aberrations (frequency of aberrant cells=%AB.C.) in exposed workers with those in non-exposed matched controls in the same plant or in other individuals living in the region of the same petrochemical industry. Workers potentially exposed to acrylonitrile at this site were also evaluated in 2000, along with another unexposed matched control group. The %AB.C. values of exposed workers and their controls were also compared with reference values determined for normal individuals (ages 20-59 years) throughout the CR. Substantial discrepancies were noted between subjects in the region of the petrochemical industry (exposed workers and controls) for the years 2000 and 2004 and the reference CR-wide normal values that had been determined during an earlier time period. The matched non-exposed controls at the petrochemical industry site showed a mean %AB.C. value of 1.56+/-1.23% (N=25) in 1998; this rose to a mean of 2.65+/-2.29% (N=33) in 2000. In 2004, values for non-exposed matched controls at the industry site were 2.64+/-1.75% for males (N=25) and 2.38+/-1.74% (N=26) for females. However, the earlier determined CR-wide %AB.C. mean reference values for normal individuals were 1.77+/-1.16% (N=1305) for the interval 1977-1988 and 1.45+/-1.17% (N=2140) for the interval 1991-1999. As both reference values are substantially lower than those determined in 2000 and 2004 for the non-exposed matched controls at the petrochemical industry site, an analysis of the CR-wide mean normal individual reference values for this same 2000-2004 period was conducted. Unexpectedly, it was found that this reference value too had risen to 1.95+/-1.36% (N=1045) and was comparable to the concurrent matched control values at the petrochemical industry site where the monitoring studies were conducted. This substantial increase in %AB.C. values in 2000 and 2004, therefore, has occurred throughout the CR and is probably unrelated to chemicals uniquely present at the petrochemical industry site.

• MeSH
• akrylonitril škodlivé účinky   MeSH
• butadieny škodlivé účinky   MeSH
• časové faktory MeSH
• chemický průmysl MeSH
• chromozomální aberace MeSH
• dospělí MeSH
• financování organizované MeSH
• genetické techniky MeSH
• lidé středního věku MeSH
• lidé MeSH
• lymfocyty mikrobiologie   účinky záření   MeSH
• maximální přípustná koncentrace MeSH
• Check Tag
• dospělí MeSH
• lidé středního věku MeSH
• lidé MeSH
• mužské pohlaví MeSH
• ženské pohlaví MeSH
• Geografické názvy
• Česká republika MeSH

The human biomonitoring (HBM) is an integral part of Environmental Health Monitoring System in the Czech Republic since 1994. Selected biomarkers of the internal dose (heavy metals, PCBs) and cytogenetic analysis of peripheral lymphocytes as a biomarker of the exposure/effect to/of environmental genotoxic factors are systematically followed up in the blood and urine of adults (blood donors), in children aged 8 to 10 years, and in the breast milk of nursing mothers. Selected outputs documented the declining trend of blood lead levels, with the recent reference value of 80 mg/l for men, and the rising trend of blood selenium levels in adults, but not in children. PCBs and chlorinated pesticides in human milk show a long-term downward trend, but still higher than in neighbouring countries. The frequency of aberrant cells revealed a downward trend, but the increase obtained in the last monitored period needs to be explained. Further HBM activities are required to demonstrate the corresponding trends and to reduce human exposure and health risks.

• MeSH
• chromozomální aberace chemicky indukované   MeSH
• dítě MeSH
• environmentální zdraví MeSH
• hodnocení rizik MeSH
• lidé středního věku MeSH
• lidé MeSH
• mateřské mléko chemie   MeSH
• mladiství MeSH
• monitorování životního prostředí metody   MeSH
• polychlorované bifenyly krev   moč   MeSH
• předškolní dítě MeSH
• surveillance populace MeSH
• těžké kovy krev   moč   MeSH
• vystavení vlivu životního prostředí MeSH
• Check Tag
• dítě MeSH
• lidé středního věku MeSH
• lidé MeSH
• mladiství MeSH
• mužské pohlaví MeSH
• předškolní dítě MeSH
• ženské pohlaví MeSH
• Geografické názvy
• Česká republika MeSH

The capital city of Prague is one of the most polluted localities of the Czech Republic. Therefore, the effect of exposure to carcinogenic polycyclic aromatic hydrocarbons (c-PAHs) adsorbed onto respirable air particles (<2.5mum) on chromosomal aberrations was studied in a group of policemen (males, aged 22-50 years) working in the downtown area of Prague and spending daily >8h outdoors (N=53). Age- and sex-matched healthy volunteers spending >90% daily time indoors were chosen as controls (N=52). Ambient air particles (PM10, PM2.5) and c-PAHs were monitored using versatile air pollution sampler (VAPS), and personal exposure was evaluated using personal samplers during working shift. Chromosomal aberrations were analyzed by conventional cytogenetic analysis and fluorescent in situ hybridization (FISH). Urinary cotinine plasma levels of vitamins A, E and C, folate, total cholesterol, HDL, LDL cholesterols and triglycerides were also analyzed as possible effect modifiers. Genotypes CYP1A1*2A, CYP1A1*2C, GSTM1, GSTP1, GSTT1, EPHX1, NAT2, hOGG1, XRCC1, XPD, p53 BstI, p53 MspI, MTHFR677, and MS2656 were determined by PCR-based RFLP assays. The following levels of air pollution were recorded during the study period (mean from HiVol sampling): PM10 62.6microg/m(3), c-PAHs 24.7ng/m(3), B[a]P 3.50ng/m(3). The conventional cytogenetic analysis did not reveal any differences between the group of policemen exposed to the ambient air pollution and the control group. The cytogenetic analysis by FISH analysis used the whole chromosome painting probes for chromosomes #1 and #4 (Cambio, UK). It detected a significant increase in all studied endpoints in the policemen compared to controls (% AB.C.=0.33+/-0.25 versus 0.24+/-0.18, p<0.05, F(G)/100=1.72+/-1.57 versus 1.25+/-1.11, p<0.05, AB/1000 (aberrations/1000 cells)=5.58+/-4.62 versus 3.90+/-3.06, p<0.05). CYP1A1*2C (Ile/Ile), XPD 23 (Lys/Lys), and XPD 6 (CC) genotypes were associated with an increase of aberrant cells by conventional method. Factors associated with an increased level of translocations by FISH included age, smoking, B[a]P-like DNA adducts (corresponding to the exposure of c-PAHs), folate, polymorphisms of CYP1A1*2C, GSTP1, EPHX1, p53 MspI and MTHFR. Ambient air exposure to c-PAHs significantly increased FISH cytogenetic parameters in nonsmoking policemen. We may conclude that FISH indicates that the city policemen in Prague represent a group of increased genotoxic risk. This is the first study that has reported a relationship between DNA adducts (biomarker of exposure) and chromosomal aberrations by FISH (biomarker of effect).

• MeSH
• chromozomální aberace MeSH
• cytochrom P-450 CYP1A1 genetika   MeSH
• dospělí MeSH
• financování organizované MeSH
• genotyp MeSH
• glutathiontransferasa genetika   MeSH
• hybridizace in situ fluorescenční MeSH
• karcinogeny životního prostředí toxicita   MeSH
• látky znečišťující vzduch toxicita   MeSH
• lidé středního věku MeSH
• lidé MeSH
• malování chromozomů MeSH
• oprava DNA MeSH
• policie MeSH
• polycyklické aromatické uhlovodíky toxicita   MeSH
• polymorfismus genetický MeSH
• pracovní expozice MeSH
• Check Tag
• dospělí MeSH
• lidé středního věku MeSH
• lidé MeSH
• mužské pohlaví MeSH

The aim of our study was to identify occupational risk of irradiation exposure in the Czech nuclear power plant workers. We analyzed levels of chromosomal aberrations, a well-known biomarker of early biological effects and a predictor of cancer risk. We applied the conventional method of cytogenetic analysis and fluorescence in situ hybridization (FISH, whole chromosome painting for chromosomes 1 and 4, combined with a pancentromeric probe) to three groups: 123 subjects in the Temelin nuclear power plant (2 years in use), 114 subjects in the Dukovany nuclear power plant (20 years in use), and 53 matched controls from Ceske Budejovice. Nuclear power plant workers were divided into two groups: subjects with admittance into the monitored zone, and others. Following factors were also analyzed: GSTM1, GSTT1, GSTP1, XPD, XRCC1, hOGG1, p53, MTHFR, and MS gene polymorphisms, levels of vitamins A, C, E, and folate in plasma, and level of cotinine in urine. Long-term exposure to ionizing radiation in the monitored zone was 0.47+/-1.50 mSv (miliSievert) in the Temelin nuclear power plant and 5.74+/-9.57 mSv in the Dukovany nuclear power plant. Using the conventional cytogenetic analysis, we observed 1.90+/-0.95 and 1.82+/-1.19% AB.C. (percent of aberrant cells) in the Temelin nuclear power plant, and 2.39+/-1.01 and 2.33+/-1.04% AB.C. in the Dukovany nuclear power plant, for monitored zone workers and others, respectively. In the control group, we found 2.25+/-0.82% AB.C. Genomic frequency of translocations F(G)/100 measured by FISH was 1.89+/-1.40 and 2.01+/-1.68 in the Temelin nuclear power plant, and 2.48+/-1.93 and 2.14+/-1.62 in the Dukovany nuclear power plant for monitored zone workers and others, respectively. In the control group, F(G)/100 was 1.83+/-1.19. Following factors were identified as potential confounders by the conventional cytogenetic analysis: XPD-6, by the FISH: age, GSTP1 and p53Bst genotypes, long-term use of medication, alcohol consumption, and smoking. No association between the dose of irradiation and the level of chromosomal aberrations in any nuclear power plant was detected either by the conventional cytogenetic analysis or by FISH.

• MeSH
• chromozomální aberace MeSH
• elektrárny MeSH
• financování organizované MeSH
• hybridizace in situ fluorescenční MeSH
• kotinin moč   MeSH
• lidé MeSH
• pracovní expozice MeSH
• studie případů a kontrol MeSH
• Check Tag
• lidé MeSH
• mužské pohlaví MeSH
• Geografické názvy
• Česká republika MeSH

• Publikační typ
• abstrakt z konference MeSH

• Publikační typ
• abstrakt z konference MeSH

In the framework of the system of monitoring the environmental impact on population health, the concentration of lead, cadmium and selenium in blood and cadmium in urine was measured in adults (n = 670), children (n = 599) and umbilical blood (n = 549) using atomic absorption spectrophotometry. Furthermore, cytogenetic analysis of peripheral lymphocytes in all population groups under study was investigated. The median blood Pb level for the overall group of adults (47.8 micrograms/l, i.e. 0.23 mumol/1) was significantly higher in men (51.5 micrograms/l, i.e. 0.25 mumol/l). Smoking significantly influenced the blood Pb level in women. The 90th percentile in no group exceeded the value of 100 micrograms/l (0.48 mumol/l). The median blood Cd level in adults (0.9 microgram/l, i.e. 0.008 mumol/l) depends on smoking habit (1.25 micrograms/l, i.e. 0.01 mumol/l). The median urine Cd level was 0.585 microgram/g creatinine (0.59 mumol/mole creatinine) in adults and 0.37 microgram/g creatinine (0.37 mumol/mole creatinine) in children. The median blood Se level (53.5 micrograms/l, i.e. 0.68 mumol/l) was found to be higher in the group of non-smokers (57.5 micrograms/l, i.e 0.73 mumol/l). Lead and selenium level were significantly lower in the umbilical blood. Cytogenetic analysis results showed age-dependent average percentages of aberrant cells: 1.1% in umbilical blood, 1.27% in children and 1.71 in adults in line with the reference values for the Czech population.

• MeSH
• chromozomální aberace MeSH
• dítě MeSH
• dospělí MeSH
• interpretace statistických dat MeSH
• kadmium * krev   moč   MeSH
• lidé MeSH
• monitorování životního prostředí * MeSH
• olovo * krev   MeSH
• pupečník MeSH
• selen * krev   MeSH
• sexuální faktory MeSH
• surveillance populace * MeSH
• T-lymfocyty ultrastruktura   MeSH
• věkové faktory MeSH
• veřejné zdravotnictví normy   MeSH
• Check Tag
• dítě MeSH
• dospělí MeSH
• lidé MeSH
• mužské pohlaví MeSH
• ženské pohlaví MeSH
• Publikační typ
• práce podpořená grantem MeSH
• Geografické názvy
• Česká republika MeSH

• MeSH
• chemické látky znečišťující vodu analýza   škodlivé účinky   MeSH
• chromozomální aberace genetika   MeSH
• lidé MeSH
• lymfocyty účinky záření   MeSH
• mutageny analýza   MeSH
• průmyslový odpad analýza   škodlivé účinky   MeSH
• Salmonella typhimurium genetika   účinky léků   MeSH
• sladká voda analýza   MeSH
• Check Tag
• lidé MeSH