Our study was aimed at investigating some factors affecting the use of a carbofuran-degrading bacterium as an inoculant to remove carbofuran residues from contaminated soil. Soil samples inoculated with a liquid cell suspension of strain C28 to give an initial density ranging from 10(3) to 10(7) cfu g(-1) (dry weight of soil) significantly improved pesticide removal. When the soil was inoculated with a granular formulation of strain C28 to give theoretical cell densities of 5 x 10(3), 5 x 10(4) and 5 x 10(5) cfu g(-1) (dry wt of soil), a significant increase in the rate of carbofuran degradation, as compared to uninoculated samples, was seen only for the highest inoculum size. The rate of carbofuran degradation in non-inoculated samples was significantly reduced by chloroform fumigation, but inoculation of natural and chloroform-fumigated soil with equivalent cell densities of strain C28 in both liquid and granular formulation led to a significant increase in the rate of carbofuran breakdown. The effect of soil glucose amendment on pesticide degradation by strain C28, in a liquid or solid formulation, depended on the concentration of the sugar and on inoculant density. A low concentration of glucose significantly reduced the lag phase before pesticide degradation by a low density inoculant. A high concentration, however, led to a significant reduction of the degradation rate for all inoculum sizes. Mixing the soil after inoculation was essential to obtain rapid degradation of the pesticide. When theoretically-equivalent cell densities were introduced in 0.1 and 1 g of microgranules, no significant difference in the rate of pesticide degradation was observed in these experiments. (C) 1997 Elsevier Science Ltd.