| Literature DB >> 24778463 |
Olivia Torres-Bugarín1, María Guadalupe Zavala-Cerna1, Arnulfo Nava2, Aurelio Flores-García3, María Luisa Ramos-Ibarra4.
Abstract
The use of biomarkers as tools to evaluate genotoxicity is increasing recently. Methods that have been used previously to evaluate genomic instability are frequently expensive, complicated, and invasive. The micronuclei (MN) and nuclear abnormalities (NA) technique in buccal cells offers a great opportunity to evaluate in a clear and precise way the appearance of genetic damage whether it is present as a consequence of occupational or environmental risk. This technique is reliable, fast, relatively simple, cheap, and minimally invasive and causes no pain. So, it is well accepted by patients; it can also be used to assess the genotoxic effect derived from drug use or as a result of having a chronic disease. Furthermore the beneficial effects derived from changes in life style or taking additional supplements can also be evaluated. In the present paper, we aim to focus on the explanation of MN test and its usefulness as a biomarker; we further give details about procedures to perform and interpret the results of the test and review some factors that could have an influence on the results of the technique.Entities:
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Year: 2014 PMID: 24778463 PMCID: PMC3932264 DOI: 10.1155/2014/956835
Source DB: PubMed Journal: Dis Markers ISSN: 0278-0240 Impact factor: 3.434
The use of micronuclei and nuclear abnormalities as markers for labor and environmental risk.
| Labor/environmental risk | Age (years) | MN | CC | KR | PN | KL | NBUDs | BNC | CA stained | Country reference |
|---|---|---|---|---|---|---|---|---|---|---|
| Banana harvester (pesticide) | 1000 (ND) |
Costa Rica, 2004 [ | ||||||||
| Exposed ( | 16–50 | 0.03 | 0.003 | 0.04* | 0.03 | 0.08 | 0.02 | 0.04 | ||
| Nonexposed ( | 33.2 | 0.03 | 0.003 | 0.06 | 0.04 | 0.1 | 0.02 | 0.04 | ||
|
| ||||||||||
| Floriculture (pesticide) | 1000 (1) |
Mexico,
2000 [ | ||||||||
| Exposed ( | 18–63 | 10.01 ± 0.03* | 19 ± 0.0 | 2 ± 0.0* | 4 ± 0.0* | 8 ± 0.0* | 0.7 ± 0.0 | 25 ± 0.0 | ||
| Nonexposed ( | 0.3 ± 0.02 | 19 ± 0.0 | 0.5 ± 0.0 | 2 ± 0.0 | 3 ± 0.0 | 0.1 ± 0.0 | 16 ± 0.0 | |||
|
| ||||||||||
| Pesticide production | 2000 (6) |
India,
2006 [ | ||||||||
| Exposed ( | 35.1 ± 5.2 | 1.2 ± 0.7* | ND | ND | ND | ND | ND | ND | ||
| Nonexposed ( | 33.4 ± 5.5 | 0.3 ± 0.2 | ||||||||
|
| ||||||||||
| Nurses (cytostatic drugs) | 1000 (2) |
Cuba,
2004 [ | ||||||||
| Exposed | 39 | 7.3* | 7.0* | ND | 5.09* | 9.1* | ND | 8.09* | ||
| Nonexposed | 4.5 | 1.5 | 4.1 | 1.8 | 4.6 | |||||
|
| ||||||||||
| Cone beam computed tomography | 2000 (1) |
Brazil,
2010 [ | ||||||||
| Before exposure ( | 26.8 ± 5 | 0.04 ± 0.05 | ND | 7.4 ± 46 (KR, PN, KL) | ND | ND | ||||
| After exposure ( | 0.05 ± 0.06 | 17.8 ± 5.4* (KR, PN, KL) | ||||||||
|
| ||||||||||
| Chemical products | 1000 (2) |
Cuba,
2005 [ | ||||||||
| Nonexposed ( | 36.2 ± 5.9 | 5.6 | 4.2 | 7.4 | 4.5 | ND | 9.2 | |||
| Carbon dioxide ( | 52.2 ± 7.0 | 5.4 | 6.5* | 5.5 | 5.6 | 5.2 | ||||
| Ammonia ( | 35.7 ± 5.7 | 8.1* | 8.3* | 7.7 | 7.6 | 10.0* | ||||
| Welding vapor (Fe, Zn, Ni, and Cr) ( | 40.7 ± 8.7 | 8.6* | 9.5 | ND | 8.5 | 10.0* | 13.2* | |||
|
| ||||||||||
| Welder (Fe, Zn, Ni, and Cr vapor) | 1000 (2) |
Colombia,
2011 [ | ||||||||
| Exposed ( | ND | 0.5 ± 0.1* | ND | ND | ND | ND | 0.2 ± 0.04* | 13.7 ± 0.7* | ||
| Nonexposed ( | 0.2 ± 0.07 | 0.05 ± 0.02 | 5.6 ± 0.3 | |||||||
|
| ||||||||||
| Children with metal crowns (nickel) | 1000 (2) |
Mexico,
2013 [ | ||||||||
| Day 1 ( | 4–11 | 4.6 ± 0.15 | ND | ND | ND | ND | ND | ND | ||
| Day 45 ( | 6.2 ± 1.7 | 6.7 ± 0.16* | ||||||||
|
| ||||||||||
| Lead battery factory workers (smokers) | 1000 (2) |
India,
2011 [ | ||||||||
| Exposed ( | 38.0 + 7.0 | 10.1* | ND | 18.8* | 46.0 | 6.8 | ND | |||
| Nonexposed ( | 42.2 + 8.0 | 3.6 ± 0.1 | 8.6 ± 0.4 | 32.4 ± 0.6 | 3.7 ± 0.4 | |||||
|
| ||||||||||
| Chrome plating workers (hexavalent Cr) | 1500 (3) |
India,
2011 [ | ||||||||
| Smokers exposed ( | 43.4 ± 3.7 | 4.5 ± 1.1* | ND | 36.2 ± 5.9 | 5.1 ± 0.4 | 128.9 ± 8.4 | 7.1 ± 1.5 | 7.2 ± 0.8 | ||
| Exposed ( | 37.6 ± 2.9 | 3.1 ± 1.1* | 52.2 ± 7.0 | 3.6 ± 0.3 | 87 ± 4.2 | 5.0 ± 0.7 | 6.9 ± 0.9 | |||
| Smokers nonexposed ( | 42.5 ± 2.2 | 1.4 ± 0.4 | 9.1 ± 2.9 | 2.6 ± 0.2 | 39.2 ± 2.4 | 2.5 ± 1.4 | 4.7 ± 0.8 | |||
| Nonexposed ( | 40.2 ± 3.7 | 1.0 ± 0.2 | 6.0 ± 1.56 | 1.8 ± 0.7 | 26.3 ± 2.5 | 3.2 ± 1.5 | 3.4 ± 0.9 | |||
|
| ||||||||||
| Urban soil (arsenic and lead) | 1000 (ND) |
Mexico,
2013 [ | ||||||||
| Exposed ( | 4–10 | 2.2 ± 1.6* | ND | ND | ND | ND | ND | ND | ||
| Nonexposed ( | 1.06 ± 0.74 | |||||||||
|
| ||||||||||
| Glass workers (arsenic) | 18–34 | 0.4 ± 0.1 | ND | ND | ND | ND | ND | ND | 2000 (1) |
India,
2006 [ |
| Exposed ( | 35–68 | 1.1 ± 0.1* | ||||||||
| Nonexposed ( | 18–34 | 0.1 ± 0.04 | ||||||||
| 35–68 | 0.2 ± 0.05 | |||||||||
|
| ||||||||||
| Outdoor painters | 3000 (1) |
Mexico,
2000 [ | ||||||||
| Exposed ( | 25–60 | 1.1 ± 0.02* | ND | ND | ND | ND | ND | ND | ||
| Nonexposed ( | 0.3 ± 0.01 | |||||||||
|
| ||||||||||
| Commercial painters | 3000 (1) |
India,
2010 [ | ||||||||
| Exposed ( | 20–50 | 17.7 ± 3.2 | ND | 23.8 ± 4.2* | ND | 21.3 ± 4.5* | 10.4 ± 3.4* | 25.7 ± 4.5* | ||
| Nonexposed ( | 2.5 ± 1.3 | 2.7 ± 0.6 | 2.7 ± 0.8 | 0.6 ± 0.4 | 2.3 ± 0.9 | |||||
|
| ||||||||||
| Shoe workers (toluene and others) | 1000 (1) |
Mexico,
2009 [ | ||||||||
| Exposed ( | 18–65 | 0.1∗♦ | 5.0♦ | 0.0♦ | 1.0♦ | 0.2♦ | 0.1♦ | 0.3♦ | ||
| Nonexposed ( | 0.0♦ | 6.1♦ | 0.0♦ | 0.7♦ | 0.0♦ | 0.0♦ | 0.2♦ | |||
|
| ||||||||||
| Tannery workers | 2000 (2) |
India,
2011 [ | ||||||||
| Exposed ( | 37.4 ± 8.6 | 7.1 ± 1.1* | ND | ND | ND | ND | ND | ND | ||
| Nonexposed ( | 37.6 ± 8.4 | 4.0 ± 1.6 | ||||||||
|
| ||||||||||
| Power plant processing poultry litter workers | 2000 (3) |
Austria, 2012 [ | ||||||||
| Exposed ( | 41.2 ± 9.4 | No difference | No difference | * | * | No difference | No difference | No difference | ||
| Nonexposed ( | 41.1 ± 8.1 | |||||||||
|
| ||||||||||
| Formaldehyde | 1000 (1) |
Portugal, 2010 [ | ||||||||
| Pathology laboratory ( | 33.8 ± 8.2 | 0.6 ± 1.7 | ND | ND | ND | ND | ND | ND | ||
| Formaldehyde-based resins production factory ( | 1.2 ± 1.5* | |||||||||
| Nonexposed ( | 35.7 ± 9.4 | 0.1 ± 0.4 | ||||||||
|
| ||||||||||
| Hairdressers | 2000 (3) |
Brazil,
2010 [ | ||||||||
| Exposed ( | 37.4 ± 2.0 | 2.0 ± 3.6* | ND | ND | ND | ND | 9.0 ± 3.8 | 8.5 ± 5.0 | ||
| Nonexposed ( | 37.0 ± 12.0 | 0.3 ± 1.0 | 5.9 ± 2.6 | 5.2 ± 4.7 | ||||||
|
| ||||||||||
| Thermoelectric plant workers | 1000 (1) |
Portugal, 2012 [ | ||||||||
| Exposed ( | 36.2 ± 9.6 | 1.8 ± 1.6* | ND | 82.4‰ (karyorrhexis, pyknosis, and karyolysis)* | ND | ND | ||||
| Office nonexposed ( | 42.1 ± 7.6 | 0.2 ± 0.4 | 58.3‰ (karyorrhexis, pyknosis, and karyolysis) | |||||||
|
| ||||||||||
| Calcite factory workers | 1000 (2) |
Turkey,
2010 [ | ||||||||
| Smokers + CaCO3 ( | 30.7 ± 0.7 | 11.4 ± 1.1 | 3.0 ± 0.2 | 1.9 ± 0.4 | 15.1 ± 1.5 | 11.2 ± 0.8 | ||||
| Nonsmokers + CaCO3 ( | 4.6 ± 1.1 | ND | 2.2 ± 0.2 | ND | 3.1 ± 0.4 | 4.0 ± 1.5 | 6.9 ± 0.8 | |||
| Smokers Nonexposed ( | 30.6 ± 1.2 | 25.5 ± 1.1 | 1.1 ± 0.2 | 1.2 ± 0.4 | 3.5 ± 1.5 | 4.7 ± 0.8 | ||||
| Nonsmokers ( | 15.1 ± 1.1 | 1.0 ± 0.2 | 1.3 ± 0.4 | 5.2 ± 1.5 | 3.4 ± 0.8 | |||||
|
| ||||||||||
| Fisher folks/mine tailings | 1000 (1) |
Philippines,
2010 [ | ||||||||
| Exposed ( | 8–70 | 7.7 ± 2.9* | ND | ND | ND | ND | ND | ND | ||
| Nonexposed ( | 2.2 ± 1.5 | |||||||||
|
| ||||||||||
| Mechanic and car painters | 3000 (1) |
Brazil, 2000 [ | ||||||||
| Exposed ( | 15–50 | 8.2 ± 4.3* | ND | ND | ND | ND | ND | ND | ||
| Nonexposed ( | 2.1 ± 1.6 | |||||||||
|
| ||||||||||
| Firefighter | ND | ND | 1000 (3) |
India,
2005 [ | ||||||
| Exposed ( | 43.2 | 3.9 ± 0.1* | 24.1 ± 1.4* | 2.8 ± 0.4* | 152.6 ± 10.1* | 5.6 ± 0.4* | ||||
| Nonexposed/office ( | 44 | 1.2 ± 0.01 | 6.45 ± 0.76 | 0.62 ± 0.13 | 21.5 ± 2.2 | 1.7 ± 0.2 | ||||
|
| ||||||||||
| Fire breathers | 1000 (4) |
Mexico,
1998 [ | ||||||||
| Exposed ( | 0.8 ± 0.7 | 2.4 ± 2.9* | 0.4 ± 0.6* | 0.7 ± 0.8* | 0.8 ± 0.9 | 4.2 ± 2.3* | ||||
| Exposed + smokers ( | 28–54 | 0.7 ± 0.5 | 2.9 ± 1.1 | 4.4 ± 0.8 | 1.3 ± 0.4 | 0 | 0.4 ± 0.5 | 5.8 ± 1.1 | ||
| Nonexposed ( | 1.1 ± 0.9 | 1.3 ± 1.6 | 0.1 ± 0.1 | 0.7 ± 1.4 | 0.7 ± 0.8 | 2.7 ± 1.7 | ||||
|
| ||||||||||
| Fuel dispenser | 1000 (1) |
Turkey,
2003 [ | ||||||||
| Smokers ( | 1.6 ± 0.08* | 0.5 ± 0.09 | 0.4 ± 0.1 | 2.3 ± 0.4 | ||||||
| Nonsmokers ( | 1.1 ± 0.06 | 0.3 ± 0.09 | 0.3 ± 0.0 | 1.7 ± 0.05 | ||||||
| Nonexposed | ND | ND | ND | |||||||
| Smokers ( | 0.6 ± 0.03 | 1.8 ± 0.1 | 1.7 ± 0.1 | 0.8 ± 0.0 | ||||||
| Nonsmokers ( | 0.2 ± 0.02 | 1.3 ± 0.1 | 1.5 ± 0.1 | 0.6 ± 0.0 | ||||||
|
| ||||||||||
| Fuel dispenser | 1000 (2) |
India,
2010 [ | ||||||||
| Smokers ( | 17–35 | 9.8 ± 2.0* | ND | 19.8 ± 03* | 41.2 ± 0.5 | ND | 7.8 ± 1.0* | |||
| Nonsmokers ( | 7.1 ± 3.1 | 7.8 ± 0.5 | 32.8 ± 0.2 | 4.8 ± 1.0 | ||||||
| Nonexposed | ||||||||||
| Smokers ( | 2.9 ± 0.01 | 9.6 ± 1.1 | 29.4 ± 0.5 | 3.4 ± 0.4 | ||||||
| Nonsmokers ( | 2.1 ± 0.02 | 7.6 ± 0.7 | 24.4 ± 1.1 | 2.8 ± 0.1 | ||||||
|
| ||||||||||
| Fuel dispenser (benzene) | 1000 (5) |
India,
2011 [ | ||||||||
| ( | ND | ND | ||||||||
| 1.500 | 37.5 ± 6.3 | 5.1 ± 0.3* | 1.1 ± 0.3* | 2.2 ± 0.1* | 1.0 ± 0.0 | 3.0 ± 0.01* | ||||
| 1.100 | 34.8 ± 6.2 | 2.7 ± 0.4 | 0.03 ± 0.1 | 0 | 0 | 1.04 ± 0.2 | ||||
MN: micronuclei; CC: condensed chromatin; KR: karyorrhexis, PN: pyknosis; KL: karyolysis; NBUDs: nuclear buds; BN: binucleated cells; AC: analyzed cells; ND: no data. All values are represented as mean ± SD, except for values marked with ♦represent median. *Statistical difference when compared with reference group.
Figure 3Typical and atypical nuclear buds (NBUDs). Photomicrographs stained with acridine orange viewed at 1000 magnification under fluorescence with an IVFL filter (450–490 nm). Binocular Microscope Carl Zeiss (Axiostar Plus).