Biofilms comprising a pure and a mixed culture of sulphate-reducing bacteria (SRB) were grown in continuous culture. When exposed to 20 or 200 pM Cd, both cultures accumulated C d but the mixed culture accumulated more and continued to accumulate Cd during the experiment, whereas accumulation by the pure cultures ceased after 4-6 d. Unlike the pure culture, the mixed culture also accumulated both protein and carbohydrate throughout the experiment proportionally to Cd which showed that accumulation required the production of biof ilm material. Electron microscopy showed the presence of polysaccharide and particulates in both pure and mixed cultures, irrespective of the presence of Cd. However, energy-dispersive X-ray analysis (EDXA) showed that accumulation of Cd in the form of CdS occurred in biofilms exposed to Cd while back-scattered electron imaging of sections indicated that the accumulation of Cd was localized in a superficial layer of the biofilm. The mechanism of uptake, therefore, appeared to be entrapment and/or precipitation of CdS at the biofilm surface. The relatively low Cd uptake by the pure culture biofilm was attributed to its less efficient growth and polysaccharide production. These results indicate that mixed SRB cultures are more effective than pure cultures for metal removal and underlines significant differences between the biology of pure and mixed cultures.

No abstract

Sulfate-reducing bacterial biofilms were grown in continuous culture. When exposed to medium containing 20 or 200 WM Cu, biofilms accumulated Cu. Energy-dispersive X-ray analysis (EDXA) showed that accumulation of Cu occurred in the form of sulfides while EDXA mapping of Cu and S in biofilm sections indicated that they were not uniformly distributed but located in the surface of the biofilm. While the polymer content of biofilm exposed to 20 WM Cu did not appear to increase relative to control Cu-free biofilms, biofilms exposed to 200 WM Cu accumulated carbohydrate and smaller amounts of protein throughout the incubation period. The mechanism of uptake, therefore, appeared to be precipitation of Cu sulfides at the biofilm surface or in the liquid phase followed by entrapment of precipitated Cu sulfide by the exopolymer-enhanced biofilm. ß

No abstract

Biomass from several fungal species removed thorium from solution in 1M HNO(3), pH 0-1. Thorium uptake was saturable with increasing thorium concentration, although the equilibria did not correspond to a simple ad sorption isotherm. Thorium uptake was altered by the biomass concentration, the uptake per unit biomass being reduced at high biomass concentrations. The presence of Al(3+) and Fe(3+) only slightly inhibited uptake of thorium while Ca(2+), Mg(2+), and Na(+) had no effect. Thus fungal biomass appears capable of removing thorium from solution under chemical conditions existing in acid waste liquors. Thorium uptake was increased by pretreatment using detergent and also, in the case of filamentous fungi, varied with the culture conditions, which implies that the thorium uptake characteristics of fungal biomass are able to be manipulated by these or similar means for optimum performance.