“…P-values b 0.05 are shown in bold font. direct soil contact has been reported also earlier (Gomot et al, 1989). In contrast to U, concentrations of Co, Mo, Ni, Pb and Zn in snail tissues did not depend on the presence of soil in our microcosm experiment.…”
Section: Uptake Of Elements To Snails and Earthwormssupporting
“…P-values b 0.05 are shown in bold font. direct soil contact has been reported also earlier (Gomot et al, 1989). In contrast to U, concentrations of Co, Mo, Ni, Pb and Zn in snail tissues did not depend on the presence of soil in our microcosm experiment.…”
Section: Uptake Of Elements To Snails and Earthwormssupporting
“…In this experiment, assimilation efficiency was similar to those recorded by Charrier and Daguzan (1980) and Lamotte and Stem (1987 (Pallant, 1974 (Desbuquois, 1991) and snails' density (Dan and Bailey, 1982;Gomot et al, 1989;Lucarz and Gomot, 1985) are known to influence the growth of H aspersa. In contrast to this experiment, farm snails are fed with a compound food and maintained in group at an optimum density.…”
“…They are characteristic of the soil surface layer, are saprophagous and phytophagous, and spend a large part of their biological cycle in contact with the soil [5]. Exchanges between soil and snails occur via both soil ingestion and absorption through the moist pedal sole (foot) [5][6][7]. They fully correspond to the criteria for relevant biological indicators [8]: Easy to sample and identify, they are distributed widely and accumulate some contaminants [9][10][11][12][13][14][15][16][17][18][19], and their ecological and physiological characteristics are well known [5].…”
Among soil invertebrates, terrestrial snails are herbivorous and detritivorous organisms exposed to polluted soils by both digestive and cutaneous routes. Using laboratory-reared snails (Helix aspersa aspersa), we describe how the effects of contaminants on survival and growth of snails can be evaluated in laboratory bioassays. A national ring test was performed to assess the effect of Cd added to the soil or to the food. The ecotoxicity of sewage sludge also was evaluated. The present results demonstrate that toxicity depends on both the pollutants and the exposure route. Cadmium was sixfold more toxic for snails exposed via food contamination (median effective concentration [EC50], 68-139 microg/g) than via soil contamination (EC50, 534-877 microg/g), whereas the opposite occurred with the sewage sludge (EC50, 55% of sludge in the food and 10% of waste in the soil). A logistic relationship linked growth inhibition and internal Cd concentrations, which can reach 2,000 microg/g in the viscera of snails exposed to 626 microg/g in the food. No clear trend was found between Cu, Zn, Pb, Cr, and Ni concentrations in the sludge and in snail tissues. These data enabled the development of an international standard, which should enhance the use of terrestrial gastropods for both fundamental research and routine risk assessment in the terrestrial environment.
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