The mutagenic hazards of aquatic sediments: a review

Uptake, metabolism, mutant frequencies and mutational spectra in lambda transgenic medaka embryos exposed to benzo[alpha]pyrene dosed sediments

The goal of this study was to provide data supporting the use of lambda transgenic medaka (Oryzias latipes) embryos to evaluate mutagens in sediments. Embryos incubated directly on sediments dosed with the reference mutagen, benzo[alpha]pyrene (BaP), were examined for BaP uptake and metabolism. Mutant frequency and mutational spectrum were assessed in the cII transgene recovered from adult medaka livers exposed as embryos. Embryos rapidly accumulated 14C-BaP and metabolized BaP to polar metabolites, indicating sediment-sorbed BaP is available for bioaccumulation and medaka embryos are capable of bioactivating this mutagen. Exposure of embryos to BaP dosed sediments significantly induced cII transgene mutant frequencies with mutations predominantly being in G:C base pairs, consistent with known mechanisms of BaP mutagenesis in transgenic mice and fish.

Anguilla anguilla L. Genotoxic responses after in situ exposure to freshwater wetland (Pateira de Fermentelos, Portugal)

Pateira de Fermentelos is a Cértima River enlargement, close to its river mouth (by the Agueda River), where the introduction of agricultural chemicals such as fertilisers and pesticides, domestic sewage, as well as heavy metals from electroplating industries, results in increased water pollution. The present research work concerns a 48 h in situ exposure of caged eels (Anguilla anguilla L.) at the Pateira de Fermentelos. Five exposure sites were selected, i.e., site A, site B, site C, site D and site E in order to study its water genotoxicity potential, measured in gill, blood, liver and kidney as DNA strand breaks. Eels were also exposed at a reference site by the Cértima River spring. Bottom water samples were collected for further physical-chemical analysis. Site A exposure, significantly decreased gill, blood and liver DNA integrity. Gill and liver DNA integrity was also significantly decreased at site B. At site C only blood DNA integrity was significantly decreased. The present field in situ study demonstrated that the three exposure sites close to the Pateira initial part, such as A, B and C are polluted by pro and/or genotoxic compounds. The genotoxic effects induced in A. anguilla L. suggest a different contamination of the exposure sites A, B and C, in genotoxic chemicals. Thus, according to its genotoxic potential the exposure sites A, B and C, may be ordered as follows site A>site B>site C. No genotoxic effects on A. anguilla L. were observed at site E as DNA strand breaks increase.

Genotoxicity and toxicity assessment in urban hydrographic basins

The genotoxicity and cytotoxicity of water in small urban basins was evaluated by the Salmonella/microsome assay and micronucleus test in V79 cells. The results showed that the cytotoxic effect was the most significant response in areas with medium to heavy urban occupation for both assays evaluated. Water samples from these areas include different concentrations of chloroform, bromodichloromethane, toluene, ethylbenzene, m,p-xylene and 1,4-dichlorobenzene. As to genotoxic damage, the presence of mainly direct-acting frameshift mutagens was detected in areas with less urban concentration and showed genotoxic activity in V79 cells in more heavily urbanized areas. Water organic extracts, evaluated using a microsuspension procedure, showed frameshift mutagenic activity in the presence of hepatic metabolization that increased as the population density grow. Chronic toxicity studies of sediment samples with the microcrustacean Daphnia magna showed that, while survival was not highly affected, reproductive inhibition was found in 92% of the observations. A retrospective diagnosis of water quality using traditional physicochemical parameters that defined the differential contribution of urban wastes at the three sites was associated with the biological assays. It became clear that the biological assays were of significant benefit in the diagnosis of risks of contamination of hydrographic basins by pollutants from urban non-point sources.

The effects of 3-methylcholanthrene on lymphocyte proliferation in the common carp (Cyprinus carpio L.)

The sensitivity of lymphocyte proliferation as bioindicator of pollution stress was evaluated in the common carp (Cyrinus carpio L.). The time course response of peripheral blood leukocyte proliferation in response or not to mitogens was measured from 1 to 7 days after peritoneal injection of 3-methylcholantrene (3-MC), and compared to the time course response of a highly sensitive biomarker, induction of cytochrome P450. 3-Methylcholanthrene (40 mg kg(-1)) inhibited both B- and T-lymphocyte proliferation in response to lipopolysaccharide (LPS) and concanavalin A (Con A). Studies with alpha-naphtofiavone, suggest the lack of metabolic processes. 3-Methylcholanthrene alone strongly stimulated resting peripheral blood leukocytes (PBLs) proliferation. This effect was not transient. The induction of lymphocyte proliferation paralleled the increase in cytochrome P450 content in the liver. The specificity of polycyclic aromatic hydrocarbon (PAH)-induced lymphocyte proliferation suggests that this immune activity may be an early marker of exposure to PAHs in aquatic environments. The capacity of 3-MC to induce rapid lymphocyte proliferation may be related to PAH-induced rapid clonal expansion in mammals. These results strongly suggested that the underlying mechanism might be the same in both models. More studies are needed in fish to explain this phenomenon and may be helpful in understanding the occurrence of neoplastic epizootics in fish associated with PAH exposition.

Mutagens in contaminated soil: a review

The intentional and accidental discharges of toxic pollutants into the lithosphere results in soil contamination. In some cases (e.g., wood preserving wastes, coal-tar, airborne combustion by-products), the contaminated soil constitutes a genotoxic hazard. This work is a comprehensive review of published information on soil mutagenicity. In total, 1312 assessments of genotoxic activity from 118 works were examined. The majority of the assessments (37.6%) employed the Salmonella mutagenicity test with strains TA98 and/or TA100. An additional 37.6% of the assessments employed a variety of plant species (e.g., Tradescantia clone 4430, Vicia faba, Zea mays, Allium cepa) to assess mutagenic activity. The compiled data on Salmonella mutagenicity indicates significant differences (p<0.0001) in mean potency (revertents per gram dry weight) between industrial, urban, and rural/agricultural sites. Additional analyses showed significant empirical relationships between S9-activated TA98 mutagenicity and soil polycyclic aromatic hydrocarbon (PAH) concentration (r2=0.19 to 0.25, p<0.0001), and between direct-acting TA98 mutagenicity and soil dinitropyrene (DNP) concentration (r2=0.87, p<0.0001). The plant assay data revealed excellent response ranges and significant differences between heavily contaminated, industrial, rural/agricultural, and reference sites, for the anaphase aberration in Allium cepa (direct soil contact) and the waxy locus mutation assay in Zea mays (direct soil contact). The Tradescantia assays appeared to be less responsive, particularly for exposures to aqueous soil leachates. Additional data analyses showed empirical relationships between anaphase aberrations in Allium, or mutations in Arabidopsis, and the 137Cs contamination of soils. Induction of micronuclei in Tradescantia is significantly related to the soil concentration of several metals (e.g., Sb, Cu, Cr, As, Pb, Cd, Ni, Zn). Review of published remediation exercises showed effective removal of genotoxic petrochemical wastes within one year. Remediation of more refractory genotoxic material (e.g., explosives, creosote) frequently showed increases in mutagenic hazard that remained for extended periods. Despite substantial contamination and mutagenic hazards, the risk of adverse effect (e.g., mutation, cancer) in humans or terrestrial biota is difficult to quantify.