Coelomocyte biomarkers in the earthworm Eisenia fetida exposed to 2,4,6-trinitrotoluene (TNT)
Contamination by 2,4,6-trinitrotoluene (TNT) is a global environmental problem at sites of former explosive production, handling, or storage, and could have deleterious consequences for human and ecological health. We investigated its sublethal effects to Eisenia fetida, using two nonspecific biomar...
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2011
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| 024 | 7 | |2 cas |a trinitrotoluene, 118-96-7; Biological Markers; Trinitrotoluene, 118-96-7 | |
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| 100 | 1 | |a Fuchs, J. | |
| 245 | 1 | 0 | |a Coelomocyte biomarkers in the earthworm Eisenia fetida exposed to 2,4,6-trinitrotoluene (TNT) |
| 260 | |c 2011 | ||
| 270 | 1 | 0 | |m Casabé, N.; CONICET, Rivadavia 1917, Buenos Aires 1033, Argentina; email: nbcm@qb.fcen.uba.ar |
| 506 | |2 openaire |e Política editorial | ||
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| 520 | 3 | |a Contamination by 2,4,6-trinitrotoluene (TNT) is a global environmental problem at sites of former explosive production, handling, or storage, and could have deleterious consequences for human and ecological health. We investigated its sublethal effects to Eisenia fetida, using two nonspecific biomarkers. In coelomocytes of earthworms exposed 24, 48, or 72 h, we evaluated DNA damage (comet assay) and neutral red retention time (NRRT), using the filter paper contact test. Both percentage of damage (D%) and calculated damage index showed significant DNA damage at almost all concentrations, at all time points assayed. Along exposure time, two different patterns were observed. At the lower TNT concentrations (0.25-0.5 μg/cm 2 ) an increased DNA migration at 48 h, with a decrease close to initial levels after 72 h exposure, was observed. This decrease could be attributed to activation of the DNA repair system. At higher concentrations (1.0-2.0 μg/cm 2 ), the high DNA damage observed remained constant during the 72 h exposure, suggesting that the rate of DNA repair was not enough to compensate such damage. Analysis of NRRT results showed a significant interaction between time and treatment. After 48 h, a significant decrease was observed at 4.0 μg/cm 2 . After 72 h, NRRT presented a concentration-dependent decrease, significantly different with respect to control at 0.5, 1.0, 2.0, and 4.0 μg/cm 2 . The two assayed methods, performed on the same sample, showed clear responses to sublethal TNT exposure in E. fetida, providing sensitive unspecific biomarkers of cell injury and DNA damage. © 2010 Springer Science+Business Media B.V. |l eng | |
| 593 | |a Department of Biological Chemistry, Faculty of Exact and Natural Sciences, University of Buenos Aires, Pabellón 2, 4o piso, Buenos Aires 1428, Argentina | ||
| 593 | |a CONICET, Rivadavia 1917, Buenos Aires 1033, Argentina | ||
| 593 | |a Centre for Advanced Studies in Health Sciences, UAI -Av. Montes de Oca 745, Buenos Aires 1270, Argentina | ||
| 690 | 1 | 0 | |a 2,4,6-TRINITROTOLUENE (TNT) |
| 690 | 1 | 0 | |a BIOMARKERS |
| 690 | 1 | 0 | |a COELOMOCYTES |
| 690 | 1 | 0 | |a COMET ASSAY |
| 690 | 1 | 0 | |a EISENIA FETIDA |
| 690 | 1 | 0 | |a NEUTRAL RED RETENTION TIME |
| 690 | 1 | 0 | |a 2,4,6-TRINITROTOLUENE (TNT) |
| 690 | 1 | 0 | |a COELOMOCYTES |
| 690 | 1 | 0 | |a COMET ASSAY |
| 690 | 1 | 0 | |a EISENIA FETIDA |
| 690 | 1 | 0 | |a NEUTRAL RED RETENTION TIME |
| 690 | 1 | 0 | |a CONCENTRATION (PROCESS) |
| 690 | 1 | 0 | |a DAMAGE DETECTION |
| 690 | 1 | 0 | |a NUCLEIC ACIDS |
| 690 | 1 | 0 | |a DNA |
| 690 | 1 | 0 | |a TRINITROTOLUENE |
| 690 | 1 | 0 | |a BIOMARKER |
| 690 | 1 | 0 | |a CONCENTRATION (COMPOSITION) |
| 690 | 1 | 0 | |a DNA |
| 690 | 1 | 0 | |a EARTHWORM |
| 690 | 1 | 0 | |a SUBLETHAL EFFECT |
| 690 | 1 | 0 | |a TRINITROTOLUENE |
| 690 | 1 | 0 | |a ANALYTIC METHOD |
| 690 | 1 | 0 | |a ARTICLE |
| 690 | 1 | 0 | |a CALCULATION |
| 690 | 1 | 0 | |a CELL TYPE |
| 690 | 1 | 0 | |a CELL VIABILITY |
| 690 | 1 | 0 | |a CELOMOCYTE |
| 690 | 1 | 0 | |a COMET ASSAY |
| 690 | 1 | 0 | |a CONTAMINATION |
| 690 | 1 | 0 | |a CONTROLLED STUDY |
| 690 | 1 | 0 | |a DNA DAMAGE |
| 690 | 1 | 0 | |a DNA REPAIR |
| 690 | 1 | 0 | |a EARTHWORM |
| 690 | 1 | 0 | |a ENVIRONMENTAL EXPOSURE |
| 690 | 1 | 0 | |a ENVIRONMENTAL IMPACT ASSESSMENT |
| 690 | 1 | 0 | |a NATURAL RED RETENTION TIME |
| 690 | 1 | 0 | |a NONHUMAN |
| 690 | 1 | 0 | |a ANIMALS |
| 690 | 1 | 0 | |a BIOLOGICAL MARKERS |
| 690 | 1 | 0 | |a COMET ASSAY |
| 690 | 1 | 0 | |a ENVIRONMENTAL MONITORING |
| 690 | 1 | 0 | |a OLIGOCHAETA |
| 690 | 1 | 0 | |a TRINITROTOLUENE |
| 690 | 1 | 0 | |a EISENIA FETIDA |
| 700 | 1 | |a Piola, L. | |
| 700 | 1 | |a González, E.P. | |
| 700 | 1 | |a Oneto, M.L. | |
| 700 | 1 | |a Basack, S. | |
| 700 | 1 | |a Kesten, E. | |
| 700 | 1 | |a Casabé, N. | |
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