Enhanced rates of phenanthrene biodegradation were observed in rhizosphere
soils (17.2 and 15.5 mg/kg/d for initial and re-spiked additions, respectiv
ely) planted with slender oat (A vena barbata Pott ex Link) compared with u
nplanted bulk soil controls (12.4 and 10.7 mg/kg/d). Soil microbial populat
ions were characterized using a modified most probable number (MPN) method
to determine quantitative shifts in heterotrophic and phenanthrene degrader
communities while principal component analysis (PCA) of fatty acid methyl
ester (FAME) data from isolated phenanthrene degraders was used to identify
qualitative differences and degrader community diversity. The average hete
rotrophic bacterial population over time was about three times larger in rh
izosphere soil than in bulk soil while phenanthrene degrading populations i
ncreased by as much as an order of magnitude between 24 and 28 days after p
lanting (DAP). Thus, phenanthrene degraders were selectively enriched in rh
izosphere soil compared with bulk soil. The greatest selection for degrader
s occurred during the later-stages of plant development from 24 to 32 DAP.
A PCA plot of the FAME data from phenanthrene degrader isolates indicated t
hat the rhizosphere degraders were less diverse than bulk soil degraders. T
hese results give us some insight into the mechanisms responsible for enhan
ced biodegradation and selective degrader enrichment in rhizosphere soils.