Evaluation of toxic and genotoxic potential of stabilized industrial waste and contaminated soils.

Artificial aqueous samples (eluates, percolates, immersion waters) were obtained from contaminated soils and stabilized industrial wastes. The toxicity and genotoxicity of these aqueous fractions have been evaluated in vivo in the aquatic larvae of the amphibian Xenopus laevis. Four biotests have been applied: a test of subchronic toxicity and three biomakers: (1) measurement of the activity of ethoxyresorufine-o-dealkylase in the liver, (2) detection of DNA adducts in the liver and the blood, and (3) measurement of the rate of micronuclei in the erythrocytes. Biological datas were completed through a chemical analysis. The main conclusions of this study are: The importance of integrating different toxicity criterias into a biological battery (phenotypic and genotypic criterias). Some aqueous extracts did not seem to be very toxic, whereas their genotoxic effects were rather significant [e.g. the stabilized Municipal Solid Waste (MSW) ashes]. The importance of coupling together chemical and biological approaches to refine the impact. Actually, some eluates (lixiviation or percolation) coming from polluted soils appeared to be very poorly loaded with pollutants, whereas the toxic and genotoxic impact of these complex matrices were rather noticeable. In addition, when applying the leaching standardized procedure, the hazardous potential of the two analysed soils may be underestimated if the results on percolates and on eluates have been compared. This study highligths the importance of coupling the tools of characterization and preparation of samples to be analysed according to the objectives to be reached.

[1]  G. Fiskesjö The Allium test as a standard in environmental monitoring. , 2008, Hereditas.

[2]  Y. Grosse,et al.  Differential DNA adduct formation and disappearance in three mouse tissues after treatment with the mycotoxin ochratoxin A. , 1993, Mutation research.

[3]  R. Gupta,et al.  32P-labeling test for DNA damage. , 1981, Proceedings of the National Academy of Sciences of the United States of America.

[4]  B. B. Panda,et al.  Monitoring and assessment of mercury pollution in the vicinity of a chloralkali plant. II Plant-availability, tissue-concentration and genotoxicity of mercury from agricultural soil contaminated with solid waste assessed in barley (Hordeum vulgare L.). , 1992, Environmental pollution.

[5]  Paul H. Brunner,et al.  The Flux of Metals Through Municipal Solid Waste Incinerators , 1986 .

[6]  A. Boudou,et al.  Genotoxicity and bioaccumulation of methyl mercury and mercuric chloride in vivo in the newt Pleurodeles waltl. , 1988, Mutagenesis.

[7]  C. Amrhein,et al.  Environmental biochemistry of chromium. , 1994, Reviews of environmental contamination and toxicology.

[8]  M. V. Reddy,et al.  Nuclease P1-mediated enhancement of sensitivity of 32P-postlabeling test for structurally diverse DNA adducts. , 1986, Carcinogenesis.

[9]  S. Felter,et al.  Hexavalent chromium-contaminated soils: options for risk assessment and risk management. , 1997, Regulatory toxicology and pharmacology : RTP.

[10]  Y. Grosse,et al.  Okadaic acid treatment induces DNA adduct formation in BHK21 C13 fibroblasts and HESV keratinocytes. , 1996, Mutation research.

[11]  P. Vasseur,et al.  The genotoxicity of iron and chromium in electroplating effluents. , 1996, Mutation research.

[12]  B. B. Panda,et al.  Allium micronucleus (MNC) assay to assess bioavailability, bioconcentration and genotoxicity of mercury from solid waste deposits of a chloralkali plant, and antagonism of L-cysteine. , 1989, The Science of the total environment.

[13]  B. B. Panda,et al.  Biomonitoring of low levels of mercurial derivatives in water and soil by Allium micronucleus assay. , 1988, Mutation research.