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Bioremediation potential of PAHs in compost.

Research output: Contribution to conference - Without ISBN/ISSN Other

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Bioremediation potential of PAHs in compost. / Reid, Brian J.; Jones, Kevin C.; Semple, Kirk T. et al.
1999. 25-30 BIOREMEDIATION TECHNOLOGIES FOR POLYCYCLIC AROMATIC HYDROCARBON COMPOUNDS.

Research output: Contribution to conference - Without ISBN/ISSN Other

Harvard

Reid, BJ, Jones, KC, Semple, KT, Fermor, TR, Leeson, A (ed.) & Alleman, BC (ed.) 1999, 'Bioremediation potential of PAHs in compost.', BIOREMEDIATION TECHNOLOGIES FOR POLYCYCLIC AROMATIC HYDROCARBON COMPOUNDS, 1/01/00 pp. 25-30.

APA

Reid, B. J., Jones, K. C., Semple, K. T., Fermor, T. R., Leeson, A. (Ed.), & Alleman, BC. (Ed.) (1999). Bioremediation potential of PAHs in compost.. 25-30. BIOREMEDIATION TECHNOLOGIES FOR POLYCYCLIC AROMATIC HYDROCARBON COMPOUNDS.

Vancouver

Reid BJ, Jones KC, Semple KT, Fermor TR, Leeson A, (ed.), Alleman BC, (ed.). Bioremediation potential of PAHs in compost.. 1999. BIOREMEDIATION TECHNOLOGIES FOR POLYCYCLIC AROMATIC HYDROCARBON COMPOUNDS.

Author

Reid, Brian J. ; Jones, Kevin C. ; Semple, Kirk T. et al. / Bioremediation potential of PAHs in compost. BIOREMEDIATION TECHNOLOGIES FOR POLYCYCLIC AROMATIC HYDROCARBON COMPOUNDS.6 p.

Bibtex

@conference{7f43f632a6074dd6942207006f5cb000,
title = "Bioremediation potential of PAHs in compost.",
abstract = "This study investigated the potential for Phase 2 mushroom compost to degrade phenanthrene (a representative PAH) in both slurry and soil systems. Initially, induction of catabolic ability within the compost was assessed after increasing compost-phenanthrene contact times. This was achieved by monitoring the evolution of (CO2)-C-14 from the mineralization of freshly added C-14-9-phenanthrene to aqueous compost slurries in respirometers. A subsequent experiment to assess the potential of the compost to bioremediate aged phenanthrene (300 d) from soil was then conducted in aerated microcosms. The extent of mineralization using induced compost was compared to that where uninduced and no compost was used. The results suggested that with increasing compost-phenanthrene contact time there was an increase in catabolic capability. Initial, (0 d compost-phenanthrene contact time) mineralization was less than 2%. However after 7 weeks compost-phenanthrene contact time greater that 65% mineralization was observed. When remediation of aged phenanthrene from soil was attempted the induced compost produced the greatest extent of mineralization initially. However, after 21 d remediation time the cumulative extents of mineralization were similar in all microcosms.",
author = "Reid, {Brian J.} and Jones, {Kevin C.} and Semple, {Kirk T.} and Fermor, {Terry R.} and A Leeson and BC Alleman",
note = "5th International In Situ and On-Site Bioremediation Symposium, SAN DIEGO, CA, APR 19-22, 1999; BIOREMEDIATION TECHNOLOGIES FOR POLYCYCLIC AROMATIC HYDROCARBON COMPOUNDS ; Conference date: 01-01-1900",
year = "1999",
language = "English",
pages = "25--30",

}

RIS

TY - CONF

T1 - Bioremediation potential of PAHs in compost.

AU - Reid, Brian J.

AU - Jones, Kevin C.

AU - Semple, Kirk T.

AU - Fermor, Terry R.

A2 - Leeson, A

A2 - Alleman, BC

N1 - 5th International In Situ and On-Site Bioremediation Symposium, SAN DIEGO, CA, APR 19-22, 1999

PY - 1999

Y1 - 1999

N2 - This study investigated the potential for Phase 2 mushroom compost to degrade phenanthrene (a representative PAH) in both slurry and soil systems. Initially, induction of catabolic ability within the compost was assessed after increasing compost-phenanthrene contact times. This was achieved by monitoring the evolution of (CO2)-C-14 from the mineralization of freshly added C-14-9-phenanthrene to aqueous compost slurries in respirometers. A subsequent experiment to assess the potential of the compost to bioremediate aged phenanthrene (300 d) from soil was then conducted in aerated microcosms. The extent of mineralization using induced compost was compared to that where uninduced and no compost was used. The results suggested that with increasing compost-phenanthrene contact time there was an increase in catabolic capability. Initial, (0 d compost-phenanthrene contact time) mineralization was less than 2%. However after 7 weeks compost-phenanthrene contact time greater that 65% mineralization was observed. When remediation of aged phenanthrene from soil was attempted the induced compost produced the greatest extent of mineralization initially. However, after 21 d remediation time the cumulative extents of mineralization were similar in all microcosms.

AB - This study investigated the potential for Phase 2 mushroom compost to degrade phenanthrene (a representative PAH) in both slurry and soil systems. Initially, induction of catabolic ability within the compost was assessed after increasing compost-phenanthrene contact times. This was achieved by monitoring the evolution of (CO2)-C-14 from the mineralization of freshly added C-14-9-phenanthrene to aqueous compost slurries in respirometers. A subsequent experiment to assess the potential of the compost to bioremediate aged phenanthrene (300 d) from soil was then conducted in aerated microcosms. The extent of mineralization using induced compost was compared to that where uninduced and no compost was used. The results suggested that with increasing compost-phenanthrene contact time there was an increase in catabolic capability. Initial, (0 d compost-phenanthrene contact time) mineralization was less than 2%. However after 7 weeks compost-phenanthrene contact time greater that 65% mineralization was observed. When remediation of aged phenanthrene from soil was attempted the induced compost produced the greatest extent of mineralization initially. However, after 21 d remediation time the cumulative extents of mineralization were similar in all microcosms.

M3 - Other

SP - 25

EP - 30

T2 - BIOREMEDIATION TECHNOLOGIES FOR POLYCYCLIC AROMATIC HYDROCARBON COMPOUNDS

Y2 - 1 January 1900

ER -