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Published online 31 May 2006
Published in J Environ Qual 35:982-991 (2006)
DOI: 10.2134/jeq2005.0253
© 2006 American Society of Agronomy, Crop Science Society of America, and Soil Science Society of America
677 S. Segoe Rd., Madison, WI 53711 USA
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Utilization of Biosolids during the Phytoremediation of Hydrocarbon-Contaminated Soil

S. J. Dickinson and P. M. Rutherford*

College of Science and Management, University of Northern British Columbia, 3333 University Way, Prince George, BC, Canada V2N 4Z9


Figure 1
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Fig. 1. Gas chromatography–flame ionization detector (GC–FID) chromatograms of soil from low-amendment treatments showing the distribution of Canadian Council of Ministers of the Environment (CCME) F2 (nC10–nC16 petroleum hydrocarbon [PHC] fraction) and F3 (nC16–nC34 petroleum hydrocarbon fraction) compound classes at (A) t = 0 wk, (B) t = 32 wk, planted treatment, and (C) t = 32 wk, non-planted treatment. Dotted lines are retention times for nC10, nC16, and nC34 PHC standards, respectively. The arrow in (A) shows the biosolids-derived contribution to F3.

 





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