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Application of a Slow-Release Fertilizer for Oil Bioremediation in Beach Sediment

R. Xua, N. L. A. Laub, K. L. Ngb and J. P. Obbarda,*

a Department of Chemical and Biomolecular Engineering, 4 Engineering Drive 4, National University of Singapore, Singapore 117576
b Tropical Marine Science Institute, 14 Kent Ridge Road, Singapore 119223



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Fig. 1. Concentrations of NH+4–N, NO3–N, and PO3–4–P in sediment pore water extracts during the 105-d period experiment. Error bars represent ±1 standard deviation unit. C, control samples; Os, Osmocote-treated samples.

 


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Fig. 2. Dehydrogenase activity of microbial biomass in oil-spiked control (C) and Osmocote-treated (Os) sediments. Error bars represent ±1 standard deviation unit.

 


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Fig. 3. First-order decline in total recoverable petroleum hydrocarbons (TRPH). Error bars represent ±1 standard deviation unit. C, control samples; Os, Osmocote-treated samples.

 


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Fig. 4. First-order decline in total n-alkanes. Error bars represent ±1 standard deviation unit. C, control samples; Os, Osmocote-treated samples. C/CH, hopane-normalized concentration of total n-alkanes.

 


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Fig. 5. First-order decline in total target polycyclic aromatic hydrocarbons (PAHs) (i.e., two- to six-ring PAHs and C1 to C4 alkyl homologs of two- and three-ring PAHs). Error bars represent ±1 standard deviation unit. C, control samples; Os, Osmocote-treated samples. C/CH, hopane-normalized concentration of total n-alkanes.

 





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