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. 2001 Jul;67(7):3208–3215. doi: 10.1128/AEM.67.7.3208-3215.2001

FIG. 3.

FIG. 3

The degradation of 500-μg g−1 2,4-D and the appearance of 2,4-D-degrading microbial populations with time in weeks, as detected in pilot field scale bioreactors containing Brazito soil amended with 2,4-D only (Treatment 1) (a); 2,4-D and 60 μg of cadmium g−1 (Treatment 2) (b); 2,4-D and 104 CFU of R. eutropha JMP134 g−1 (Treatment 3) (c); 2,4-D, 60 μg of cadmium g−1, and 104 CFU of R. eutropha JMP134 g−1 (Treatment 4) (d); 2,4-D, 60 μg of cadmium g−1, 104 CFU of R. eutropha JMP134 g−1, and 104 CFU of cadmium-resistant Pseudomonas strain H1 g−1 (Treatment 7) (e). The original number of 2,4-D degraders was fewer than 102 CFU g−1 of soil prior to bioaugmentation. Treatment 5 (2,4-D and Pseudomonas strain H1) and Treatment 6 (2,4-D, 60 μg of cadmium g−1, and Pseudomonas strain H1) are not shown.