Soil parameters are key factors to predict metal bioavailability to snails based on chemical extractant data.
Although soil characteristics modulate metal mobility and bioavailability to organisms, they are often ignored in the risk assessment of metal transfer. This paper aims to determine the ability of chemical methods to assess and predict cadmium (Cd), lead (Pb) and zinc (Zn) environmental bioavailability to the land snail Cantareus aspersus. Snails were exposed in the laboratory for 28 days to 17 soils from around a former smelter. The soils were selected for their range of pH, organic matter, clay content, and Cd, Pb and Zn concentrations. The influence of soil properties on environmental availability (estimated using HF-HClO(4), EDTA, CaCl(2), NH(4)NO(3), NaNO(3), free ion activity and total dissolved metal concentration in soil solution) and on environmental bioavailability (modelled using accumulation kinetics) was identified. Among the seven chemical methods, only the EDTA and the total soil concentration can be used to assess Cd and Pb environmental bioavailability to snails (r²(adj)=0.67 and 0.77, respectively). For Zn, none of the chemical methods were suitable. Taking into account the influence of the soil characteristics (pH and CEC) allows a better prediction of Cd and Pb environmental bioavailability (r²(adj)=0.82 and 0.83, respectively). Even though alone none of the chemical methods tested could assess Zn environmental bioavailability to snails, the addition of pH, iron and aluminium oxides allowed the variation of assimilation fluxes to be predicted. A conceptual and practical method to use soil characteristics for risk assessment is proposed based on these results. We conclude that as yet there is no universal chemical method to predict metal environmental bioavailability to snails, and that the soil factors having the greatest impact depend on the metal considered.
Department Chrono-Environment, UMR UFC/CNRS 6249 USC INRA, University of Franche-Comté, Place Leclerc, F-25030 Besançon Cedex, France.
B
B
Pauget
F
F
Gimbert
R
R
Scheifler
M
M
Coeurdassier
A
A
de Vaufleury
D000538:Aluminum Silicates; D000818:Animals; D001682:Biological Availability; D002104:Cadmium / Q000493:pharmacokinetics; D002623:Chemistry Techniques, Analytical; D000077215:Clay; D004492:Edetic Acid / Q000737:chemistry; D004781:Environmental Exposure; D004784:Environmental Monitoring / Q000379:methods; D006863:Hydrogen-Ion Concentration; D007854:Lead / Q000493:pharmacokinetics; D008670:Metals / Q000493:pharmacokinetics*; D012908:Snails / Q000378:metabolism*; D012987:Soil / Q000032:analysis / Q000737:chemistry*; D012989:Soil Pollutants / Q000493:pharmacokinetics*; D015032:Zinc / Q000493:pharmacokinetics
D000538:Aluminum Silicates; D008670:Metals; D012987:Soil; D012989:Soil Pollutants; D002104:Cadmium; D007854:Lead; D004492:Edetic Acid; D015032:Zinc; D000077215:Clay