Biochemical characterization of the DNA polymerase activity present in isolated nuclei from mussel tissues: a possible system for the evaluation of the rate of DNA repair

Improving knowledge on genotoxicity dynamics in somatic and germ cells of crayfish (Procambarus clarkii)

The harmful effects of pesticides can be extended beyond the exposure time scale. Appraisals combining exposure and long-term post-exposure periods appear as an unavoidable approach in pesticide risk assessment, thus allowing a better understanding of the real impact of agrochemicals in non-target organisms. This study aimed to evaluate the progression of genetic damage in somatic and germ tissues of the crayfish Procambarus clarkii, also seeking for gender-specificities, following exposure (7 days) to penoxsulam (23 μg L^-1 ) and a post-exposure (70 days) period. The same approach was applied to the model genotoxicant ethyl methanesulfonate (EMS; 5 mg L^-1 ) as a complementary mean to improve knowledge on genotoxicity dynamics (induction vs. recovery). Penoxsulam induced DNA damage in all tested tissues, disclosing tissue- and gender-specificities, where females showed to be more vulnerable than males in the gills, while males demonstrated higher susceptibility in what concerns internal organs, that is, hepatopancreas and gonad. Crayfish were unable to recover from the DNA damage induced by EMS in gills and hepatopancreas (both genders) as well as in spermatozoa. The genotoxicity in the hepatopancreas was only perceptible in the post-exposure period. Oxidative DNA lesions were identified in hepatopancreas and spermatozoa of EMS-exposed crayfish. The spermatozoa proved to be the most vulnerable cell type. It became clear that the characterization of the genotoxic hazard of a given agent must integrate a complete set of information, addressing different types of DNA damage, tissue- and gender-specificities, as well as a long-term appraisal of temporal progression of damage.

Persistence of DNA damage in the freshwater mussel Unio pictorum upon exposure to ethyl methanesulphonate and hydrogen peroxide

An important endpoint in assessing pollution-related toxicity is genotoxicity. To obtain insight into the time-course of oxidative- and alkylation-induced DNA damage in the freshwater mussel, Unio pictorum, mussels were exposed for 24 hr to concentration gradients of pro-oxidant hydrogen peroxide (H(2)O(2)) and a mono-functional alkylating agent, ethyl methanesulfonate (EMS). DNA damage was assessed in haemocytes immediately upon exposure and over the recovery period of up to 72 days by means of comet and micronucleus assays. Following exposure to H(2)O(2), DNA damage as detected by the comet assay returned to control values after one day, except for the mussels exposed to the highest dose when damage was detectable for the next 3 days. In contrast, alkylation-induced DNA damage was detectable even after 72 days of recovery in de-chlorinated water, with a dose-response relationship observable throughout the whole recovery period. Micronucleus frequency was the highest on Day 3 after exposure to EMS; it decreased considerably by Day 7 and returned almost to the control levels 19 days after exposure, while no significant induction of micronuclei was observed in mussels exposed to H(2)O(2). Although the comet assay is considered a biomarker of recent genotoxic exposure, detecting DNA damage of shorter longevity than with the micronucleus assay, results presented here show that in the case of alkylation damage the comet assay reveals genotoxic exposure of U. pictorum in a dose-dependent manner even after 2 months.

Detection of DNA strand breaks in isolated mussel (Mytilus edulis L. ) digestive gland cells using the "Comet" assay

Isolated mussel (Mytilus edulis L.) digestive gland cells were analyzed using the single-cell gel electrophoresis or "comet" assay to assess the ability of potential aquatic contaminants to induce DNA strand breaks (SBs) and to investigate the potential application of this technique as part of an aquatic biomonitoring regime. Freshly prepared cell suspensions from digestive gland were exposed in vitro to hydrogen peroxide (H2O2, 0-200 microM), 3-chloro-4-(dichloromethyl)-5-hydroxy-2[5H]-furanone (MX, 0-200 microM), benzo[a]pyrene (BaP, 0-200 microM), 1-nitropyrene (1-NP, 0-250 microM) and nitrofurantoin (NF, 0-1000 microM) for 1 h in the dark at 15 degreesC in the presence of the DNA repair inhibitor cytosine-beta-D-arabinofuranoside (araC). DNA strand breakage was measured using the comet assay. There were significant concentration-dependent increases in the percentage of DNA in the comet tail (mean values+/-SD) for all doses compared with controls (P<0.05) with H2O2 (up to 61.4+/-5.1% at 100 microM), MX (up to 34. 3+/-2.2% at 200 microM), BaP (up to 24.7+/-5.1 at 100 microM), 1-NP (up to 54.7+/-5.0% at 200 microM), and NF (up to 68.1+/-4.5% at 500 microM). There was a decrease (P<0.05) in viability (eosin Y exclusion) of exposed compared with control cells at 200 microM H2O2 and BaP only. This study has demonstrated the potential of the comet assay to detect DNA strand breakage at subcytotoxic concentrations of a range of agents, some of which require metabolic activation. This may provide a sensitive, but nonspecific, molecular biomarker of genotoxicity.

The analysis of DNA adduct formation, removal and persistence in the common mussel Mytilus edulis exposed to 4-nitroquinoline 1-oxide

32P-postlabelling was used for the detailed analysis of 4-nitroquinoline 1-oxide (4-NQO) induced DNA adduct formation, removal and persistence in the marine shellfish Mytilus spp. The results had a number of important implications concerning the use of such DNA adducts as dosimeters of environmental genotoxin exposures. Our studies indicated that the maintenance of the Mytilus specimens under controlled laboratory conditions can result in the induction of 'stress-related adducts' seemingly related to the nature of the experimental set-up. The studies also indicated that the absorption and activation of genotoxins in this species appear to affect the rate of adduct formation, and that the maximum levels of adducts may not necessarily be induced immediately after the cessation of a genotoxin exposure. In addition, Mytilus specimens were shown to possess a significant capacity to remove these genotoxin-induced DNA adducts. The removal of these adducts appeared to be biphasic in nature, with the rapid removal of a large proportion of adducts occurring within 48 h of the cessation of the exposure, followed by a slow rate of adduct removal over the remaining period of the studies. Despite the relatively efficient removal of the majority of these genotoxin-induced DNA adducts, a proportion remained up to 56 days after the initial exposure. The persistence of these genotoxin-DNA adducts, combined with the information on the rates of adduct removal, indicated that under well-defined conditions, such adducts could serve as suitable biomarkers of environmental contamination.

The application of the 32P-postlabelling assay to aquatic biomonitoring

The aquatic environment is known to contain a variety of natural and anthropogenic compounds that are capable of interacting with the genetic material of aquatic organisms. The increases in the levels of these anthropogenic contaminants, associated with widespread industrialisation, has led to the requirement for reliable methodologies to monitor their potential impact upon exposed aquatic organisms. Of the molecular techniques currently available, the 32P-postlabelling assay for the detection of DNA adducts offers considerable potential for the qualitative and quantitative assessment of genotoxin exposure. Here we describe several studies in which the technique was adapted for evaluation in two marine bioindicator species the common mussel Mytilus edulis and the flatfish Limanda limanda. Laboratory studies in which M. edulis specimens were exposed to 2-aminofluorene and 4-nitroquinoline 1-oxide confirmed the species' capacity to form genotoxin-related adducts. However, in further studies, no exposure-related adducts could be detected in M. edulis specimens placed in mesocosms containing environmentally realistic levels of anthropogenic contaminants. Biologically significant levels of adducts were detected in L. limanda specimens exposed to sediment bound contaminants under controlled conditions, although the levels did not appear to be statistically significant. An in situ study in which adduct levels were determined in L. limanda specimens from two sites of contrasting contamination levels proved to be more conclusive. The results were both biologically and statistically significant, suggesting that adduct levels could well be related to the levels of sediment-bound contaminants. Together the studies confirmed that the determination of the levels of DNA adducts could be used as indicators of the exposure of aquatic organisms to environmental genotoxins.