The bioaugmentation of petroleum-contaminated soil using Enterobacter cloacae was profiled from the evolution of microbial community, soil dehydrogenase activity, to the degradation of petroleum contaminants. The seeding and proliferation of inoculant and the consequential microbial community were monitored by denaturing gradient gel electrophoresis analysis of the amplification of V3 zone of 16S rDNA. Degradation process kinetics was characterized by the degradation ratio of nC17 to nC18. The dehydrogenase activity was also determined during the degradation process. An abrupt change in the microbial community after inoculation was illustrated as well as successive changes in response to degradation of the petroleum contaminants. Seeding with E. cloacae stimulated the growth of other degrading stains such as Pseudomonas sp. and Rhodothermus sp. The application of wheat straw as a representative lignin waste, at 5% (w/w), induced an increase in the total dehydrogenase activity from 0.50 to 0.79, an increase in the microbial content of 130% for bacteria and 84% for fungi, and an increase of the overall degradation ratio from 44% to 56% after 56 days of treatment. The above mentioned results have provided a microbial ecological insight being essential for the design and implementation of bioaugmentation processes.

2,4,6-Trinitrotoluene (TNT), an extensively used and versatile explosive, is harmful in soil and water. In the present study, four bacterial strains capable of degrading TNT have been isolated from contaminated sites and named as Thu-A, Thu-B, Thu-C, and Thu-Z. Thu-Z, which gave the highest degradation efficiency compared to the others, was assigned to the genus Pantoea according to its 16S rRNA gene. Similarities in both biochemical properties and morphology suggested that Thu-Z was a Pantoea sp. strain. Thu-Z was proved to be capable of using TNT as a sole nitrogen source by cleaving NO(2) from the nitroaromatic ring by direct aromatic ring reduction. Under nitrogen-limited conditions, 96.6 % N of TNT was consumed by Thu-Z for growth, which was determined in terms of NaNO(2). Trace nitro reduction metabolites such as 2,4-diamino-6-nitrotoluene (24Dam) and 2,6-diamino-4-nitrotoluene (26Dam) were identified in the presence of (NH(4))(2)SO(4). On the other hand, 4,4',6,6'-tetranitro-2,2'-azoxytoluene (22Azo) and 2,2',6,6'-tetranitro-4,4'-azoxytoluene (44Azo) were detected in the absence of (NH(4))(2)SO(4). These indicated the existence of a dual pathway for Thu-Z, while the direct aromatic ring reduction was predominant. Addition of a nitrogen source ((NH(4))(2)SO(4)) after inoculation stimulated the growth of Thu-Z and accelerated TNT degradation.

Soil microbial ecosystems are responsive to environmental changes that underpin the biological functions of the soil. The present study was conducted to profile variations in the microbial ecological system of remediated soil (R) and petroleum contaminated soil (P) based on comparisons with soil that had not been contaminated (N), using a cloning library of taxonomic genes (16S rRNA gene for bacteria and 18S rRNA gene for eukaryotes) and functional genes (nifH, amoA and narG). The results showed that N and R had a similar distribution in both the taxonomic genes and functional genes for bacteria and eukaryotes, which were dominated by Proteobacteria and Arthropoda, respectively. Phylogenetic analysis based on the nifH gene showed that the sequences from the three soils were clustered into six taxonomic groups, Actinobacteridae, and Alpha-, Beta-, Gamma- and Delta-proteobacteria, as well as an unclassified group. Evaluation of the amoA gene revealed that all sequences derived from the three samples belonged to Betaproteobacteria. The R and N soil had similar Shannon-Wiener diversity index (H') values, both of which were significantly higher than that of the P soil. The most abundant bacterial phylotype identified in the N and R soils were the same and were related to an uncultured bacterial clone (GAN-SB17, FN423475). None of the narG genes were found in the P soil. Similar results in terms of distribution, composition and the related index were obtained for nifH and amoA. These parameters may comprise a biological ecology index that may be applied to aid the design, implementation and evaluation of soil bioremediation.