TY - JOUR
T1 - Bioremediation of petroleum hydrocarbon contaminated soil
T2 - Effects of strategies and microbial community shift
AU - Grace Liu, Pao Wen
AU - Chang, Tsung Chain
AU - Whang, Liang Ming
AU - Kao, Chun Hsuan
AU - Pan, Po Tseng
AU - Cheng, Sheng Shung
N1 - Funding Information:
The authors like to express their gratitude to the financial support from the National Science Counsil ( NSC 98-2221-E-273-001-MY3 ). Also our special thanks go to Professor Chiu-Chung Young at the National Chung Hsing University for diesel-degrading bacteria, Professor Jo-Shu Chang at the National Cheng Kung University and Yu-Hung Wei at Yuan Ze University for providing the rhamnolipid biosurfactant.
PY - 2011/12
Y1 - 2011/12
N2 - Biodegradation of petroleum hydrocarbon oil (14,000 mg kg-1) were investigated in six biopiles batches, differing in the remediation strategy: bioaugmentation (selected consortium and kitchen waste were introduced), biostimulation (added with rhamnolipid, high-level, or low-level nutrient), and bioaugmentation plus biostimulation (added both with rhamnolipid and bacterial consortia). After the 140-day operation, the kitchen waste (KW) and the low-level nutrient (NEL) batches achieved the highest total petroleum hydrocarbon degradation efficiency (>80%). The result of the hydrocarbon analysis revealed that the bioaugmentation approaches were the most effective ones in removing aromatic component (64% and 68%), and KW and NEL were the only two approaches that can remove the polar component with positive efficiency, 11% and 21%, respectively. The terminal-restriction fragment length polymorphism percentage (T-RFLP) abundance applied with nonmetric multidimensional scaling indicated a similarity of the bacterial communities during the early fastest remediation stage. The results of the oligonucleotide array targeting the ribosomal internal transcribed spacer (ITS) region, along with the hydrocarbon fractional analysis, indicated a successive degradation completed by the bacterial-fungi consortia. Before Day 70, the bacterial community was dominant in decomposing the saturated and partially aromatic hydrocarbons. After Day 70, the fungal community found to be dynamic and responsible for degradation of the polar hydrocarbons composing of recalcitrant metabolites.
AB - Biodegradation of petroleum hydrocarbon oil (14,000 mg kg-1) were investigated in six biopiles batches, differing in the remediation strategy: bioaugmentation (selected consortium and kitchen waste were introduced), biostimulation (added with rhamnolipid, high-level, or low-level nutrient), and bioaugmentation plus biostimulation (added both with rhamnolipid and bacterial consortia). After the 140-day operation, the kitchen waste (KW) and the low-level nutrient (NEL) batches achieved the highest total petroleum hydrocarbon degradation efficiency (>80%). The result of the hydrocarbon analysis revealed that the bioaugmentation approaches were the most effective ones in removing aromatic component (64% and 68%), and KW and NEL were the only two approaches that can remove the polar component with positive efficiency, 11% and 21%, respectively. The terminal-restriction fragment length polymorphism percentage (T-RFLP) abundance applied with nonmetric multidimensional scaling indicated a similarity of the bacterial communities during the early fastest remediation stage. The results of the oligonucleotide array targeting the ribosomal internal transcribed spacer (ITS) region, along with the hydrocarbon fractional analysis, indicated a successive degradation completed by the bacterial-fungi consortia. Before Day 70, the bacterial community was dominant in decomposing the saturated and partially aromatic hydrocarbons. After Day 70, the fungal community found to be dynamic and responsible for degradation of the polar hydrocarbons composing of recalcitrant metabolites.
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U2 - 10.1016/j.ibiod.2011.09.002
DO - 10.1016/j.ibiod.2011.09.002
M3 - Article
AN - SCOPUS:80053362536
VL - 65
SP - 1119
EP - 1127
JO - International Biodeterioration and Biodegradation
JF - International Biodeterioration and Biodegradation
SN - 0964-8305
IS - 8
ER -