Loading…
Hexadecane mineralization and denitrification in two diesel fuel-contaminated soils
The effect of nitrate, ammonium and urea on the mineralization of [ 14C]hexadecane (C 16H 34) and on denitrification was evaluated in two soils contaminated with diesel fuel. In soil A, addition of N fertilizers did not stimulate or inhibit background hexadecane mineralization (4.3 mg C 16H 34 kg −1...
Saved in:
Published in: | FEMS microbiology ecology 2000, Vol.32 (1), p.17-23 |
---|---|
Main Authors: | , |
Format: | Article |
Language: | English |
Subjects: | |
Online Access: | Get full text |
Tags: |
Add Tag
No Tags, Be the first to tag this record!
|
cited_by | |
---|---|
cites | |
container_end_page | 23 |
container_issue | 1 |
container_start_page | 17 |
container_title | FEMS microbiology ecology |
container_volume | 32 |
creator | Roy, Réal Greer, Charles W. |
description | The effect of nitrate, ammonium and urea on the mineralization of [
14C]hexadecane (C
16H
34) and on denitrification was evaluated in two soils contaminated with diesel fuel. In soil A, addition of N fertilizers did not stimulate or inhibit background hexadecane mineralization (4.3 mg C
16H
34 kg
−1 day
−1). In soil B, only NaNO
3 stimulated hexadecane mineralization (0.91 mg C
16H
34 kg
−1 day
−1) compared to soil not supplemented with any nitrogen nutrient (0.17 mg C
16H
34 kg
−1 day
−1). Hexadecane mineralization was not stimulated in this soil by NH
4NO
3 (0.13 mg C
16H
34 kg
−1 day
−1), but the addition of NH
4Cl or urea suppressed hexadecane mineralization (0.015 mg C
16H
34 kg
−1 day
−1). Addition of 2 kPa C
2H
2 did not inhibit the mineralization process in either soil. Denitrification occurred in both soils studied when supplemented with NaNO
3 and NH
4NO
3, but was not detected with other N sources. Denitrification started after a longer lag in soil A (10 days) than in soil B (4 days). In soil A microcosms supplemented with NaNO
3 or NH
4NO
3, rates of denitrification were 20.6 and 13.6 mg NO
3
− kg
−1 day
−1, respectively, and in soil B, they were 18.5 and 12.5 mg NO
3
− kg
−1 day
−1, respectively. We conclude that denitrification may lead to a substantial loss of nitrate, making it unavailable to the mineralizing bacterial population. Nitrous oxide was an important end-product accounting for 30–100% of total denitrification. These results indicate the need for preliminary treatability studies before implementing full-scale treatment processes incorporating commercial fertilizers. |
doi_str_mv | 10.1016/S0168-6496(99)00103-8 |
format | article |
fullrecord | <record><control><sourceid>proquest_elsev</sourceid><recordid>TN_cdi_proquest_miscellaneous_17599684</recordid><sourceformat>XML</sourceformat><sourcesystem>PC</sourcesystem><els_id>S0168649699001038</els_id><sourcerecordid>17599684</sourcerecordid><originalsourceid>FETCH-LOGICAL-e351t-e0f46a555299b866488dd329e34f37cc1b55b502016296af776ca512dd7414cc3</originalsourceid><addsrcrecordid>eNo9kE1LAzEQhoMoWKs_QdiT6CGabD42OYkUtULBQ_Uc0mQWImmim1TFX--2FS8zMDwzvPMgdE7JNSVU3izHorDkWl5qfUUIJQyrAzShouNYak4P0eQfOUYnpbyNkGCcTNByDt_Wg7MJmnVIMNgYfmwNOTU2-cZDCnUIfXD7WUhN_cqND1AgNv0GInY5VTuu2gq-KTnEcoqOehsLnP31KXp9uH-ZzfHi-fFpdrfAwAStGEjPpRVCtFqvlJRcKe9Zq4HxnnXO0ZUQK0HaMXqrpe27TjoraOt9xyl3jk3Rxf7u-5A_NlCqWYfiIMbxmbwphnZCa6n4CN7uQRjTfAYYTHEBkgMfBnDV-BwMJWYr0-xkmq0po7XZyTSK_QL7GWkU</addsrcrecordid><sourcetype>Aggregation Database</sourcetype><iscdi>true</iscdi><recordtype>article</recordtype><pqid>17599684</pqid></control><display><type>article</type><title>Hexadecane mineralization and denitrification in two diesel fuel-contaminated soils</title><source>Oxford Academic Journals (Open Access)</source><creator>Roy, Réal ; Greer, Charles W.</creator><creatorcontrib>Roy, Réal ; Greer, Charles W.</creatorcontrib><description>The effect of nitrate, ammonium and urea on the mineralization of [
14C]hexadecane (C
16H
34) and on denitrification was evaluated in two soils contaminated with diesel fuel. In soil A, addition of N fertilizers did not stimulate or inhibit background hexadecane mineralization (4.3 mg C
16H
34 kg
−1 day
−1). In soil B, only NaNO
3 stimulated hexadecane mineralization (0.91 mg C
16H
34 kg
−1 day
−1) compared to soil not supplemented with any nitrogen nutrient (0.17 mg C
16H
34 kg
−1 day
−1). Hexadecane mineralization was not stimulated in this soil by NH
4NO
3 (0.13 mg C
16H
34 kg
−1 day
−1), but the addition of NH
4Cl or urea suppressed hexadecane mineralization (0.015 mg C
16H
34 kg
−1 day
−1). Addition of 2 kPa C
2H
2 did not inhibit the mineralization process in either soil. Denitrification occurred in both soils studied when supplemented with NaNO
3 and NH
4NO
3, but was not detected with other N sources. Denitrification started after a longer lag in soil A (10 days) than in soil B (4 days). In soil A microcosms supplemented with NaNO
3 or NH
4NO
3, rates of denitrification were 20.6 and 13.6 mg NO
3
− kg
−1 day
−1, respectively, and in soil B, they were 18.5 and 12.5 mg NO
3
− kg
−1 day
−1, respectively. We conclude that denitrification may lead to a substantial loss of nitrate, making it unavailable to the mineralizing bacterial population. Nitrous oxide was an important end-product accounting for 30–100% of total denitrification. These results indicate the need for preliminary treatability studies before implementing full-scale treatment processes incorporating commercial fertilizers.</description><identifier>ISSN: 0168-6496</identifier><identifier>EISSN: 1574-6941</identifier><identifier>DOI: 10.1016/S0168-6496(99)00103-8</identifier><language>eng</language><publisher>Elsevier B.V</publisher><subject>Ammonium ; ammonium salts ; Bacteria ; Bacterium ; Denitrification ; Hexadecane ; Nitrate ; Nitrous oxide ; Soil ; urea</subject><ispartof>FEMS microbiology ecology, 2000, Vol.32 (1), p.17-23</ispartof><rights>2000</rights><lds50>peer_reviewed</lds50><oa>free_for_read</oa><woscitedreferencessubscribed>false</woscitedreferencessubscribed></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,777,781,4010,27904,27905,27906</link.rule.ids></links><search><creatorcontrib>Roy, Réal</creatorcontrib><creatorcontrib>Greer, Charles W.</creatorcontrib><title>Hexadecane mineralization and denitrification in two diesel fuel-contaminated soils</title><title>FEMS microbiology ecology</title><description>The effect of nitrate, ammonium and urea on the mineralization of [
14C]hexadecane (C
16H
34) and on denitrification was evaluated in two soils contaminated with diesel fuel. In soil A, addition of N fertilizers did not stimulate or inhibit background hexadecane mineralization (4.3 mg C
16H
34 kg
−1 day
−1). In soil B, only NaNO
3 stimulated hexadecane mineralization (0.91 mg C
16H
34 kg
−1 day
−1) compared to soil not supplemented with any nitrogen nutrient (0.17 mg C
16H
34 kg
−1 day
−1). Hexadecane mineralization was not stimulated in this soil by NH
4NO
3 (0.13 mg C
16H
34 kg
−1 day
−1), but the addition of NH
4Cl or urea suppressed hexadecane mineralization (0.015 mg C
16H
34 kg
−1 day
−1). Addition of 2 kPa C
2H
2 did not inhibit the mineralization process in either soil. Denitrification occurred in both soils studied when supplemented with NaNO
3 and NH
4NO
3, but was not detected with other N sources. Denitrification started after a longer lag in soil A (10 days) than in soil B (4 days). In soil A microcosms supplemented with NaNO
3 or NH
4NO
3, rates of denitrification were 20.6 and 13.6 mg NO
3
− kg
−1 day
−1, respectively, and in soil B, they were 18.5 and 12.5 mg NO
3
− kg
−1 day
−1, respectively. We conclude that denitrification may lead to a substantial loss of nitrate, making it unavailable to the mineralizing bacterial population. Nitrous oxide was an important end-product accounting for 30–100% of total denitrification. These results indicate the need for preliminary treatability studies before implementing full-scale treatment processes incorporating commercial fertilizers.</description><subject>Ammonium</subject><subject>ammonium salts</subject><subject>Bacteria</subject><subject>Bacterium</subject><subject>Denitrification</subject><subject>Hexadecane</subject><subject>Nitrate</subject><subject>Nitrous oxide</subject><subject>Soil</subject><subject>urea</subject><issn>0168-6496</issn><issn>1574-6941</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2000</creationdate><recordtype>article</recordtype><recordid>eNo9kE1LAzEQhoMoWKs_QdiT6CGabD42OYkUtULBQ_Uc0mQWImmim1TFX--2FS8zMDwzvPMgdE7JNSVU3izHorDkWl5qfUUIJQyrAzShouNYak4P0eQfOUYnpbyNkGCcTNByDt_Wg7MJmnVIMNgYfmwNOTU2-cZDCnUIfXD7WUhN_cqND1AgNv0GInY5VTuu2gq-KTnEcoqOehsLnP31KXp9uH-ZzfHi-fFpdrfAwAStGEjPpRVCtFqvlJRcKe9Zq4HxnnXO0ZUQK0HaMXqrpe27TjoraOt9xyl3jk3Rxf7u-5A_NlCqWYfiIMbxmbwphnZCa6n4CN7uQRjTfAYYTHEBkgMfBnDV-BwMJWYr0-xkmq0po7XZyTSK_QL7GWkU</recordid><startdate>2000</startdate><enddate>2000</enddate><creator>Roy, Réal</creator><creator>Greer, Charles W.</creator><general>Elsevier B.V</general><scope>7T7</scope><scope>7TV</scope><scope>8FD</scope><scope>C1K</scope><scope>F1W</scope><scope>FR3</scope><scope>H97</scope><scope>L.G</scope><scope>P64</scope></search><sort><creationdate>2000</creationdate><title>Hexadecane mineralization and denitrification in two diesel fuel-contaminated soils</title><author>Roy, Réal ; Greer, Charles W.</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-e351t-e0f46a555299b866488dd329e34f37cc1b55b502016296af776ca512dd7414cc3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2000</creationdate><topic>Ammonium</topic><topic>ammonium salts</topic><topic>Bacteria</topic><topic>Bacterium</topic><topic>Denitrification</topic><topic>Hexadecane</topic><topic>Nitrate</topic><topic>Nitrous oxide</topic><topic>Soil</topic><topic>urea</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Roy, Réal</creatorcontrib><creatorcontrib>Greer, Charles W.</creatorcontrib><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Pollution Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Engineering Research Database</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 3: Aquatic Pollution & Environmental Quality</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Biotechnology and BioEngineering Abstracts</collection><jtitle>FEMS microbiology ecology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Roy, Réal</au><au>Greer, Charles W.</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Hexadecane mineralization and denitrification in two diesel fuel-contaminated soils</atitle><jtitle>FEMS microbiology ecology</jtitle><date>2000</date><risdate>2000</risdate><volume>32</volume><issue>1</issue><spage>17</spage><epage>23</epage><pages>17-23</pages><issn>0168-6496</issn><eissn>1574-6941</eissn><abstract>The effect of nitrate, ammonium and urea on the mineralization of [
14C]hexadecane (C
16H
34) and on denitrification was evaluated in two soils contaminated with diesel fuel. In soil A, addition of N fertilizers did not stimulate or inhibit background hexadecane mineralization (4.3 mg C
16H
34 kg
−1 day
−1). In soil B, only NaNO
3 stimulated hexadecane mineralization (0.91 mg C
16H
34 kg
−1 day
−1) compared to soil not supplemented with any nitrogen nutrient (0.17 mg C
16H
34 kg
−1 day
−1). Hexadecane mineralization was not stimulated in this soil by NH
4NO
3 (0.13 mg C
16H
34 kg
−1 day
−1), but the addition of NH
4Cl or urea suppressed hexadecane mineralization (0.015 mg C
16H
34 kg
−1 day
−1). Addition of 2 kPa C
2H
2 did not inhibit the mineralization process in either soil. Denitrification occurred in both soils studied when supplemented with NaNO
3 and NH
4NO
3, but was not detected with other N sources. Denitrification started after a longer lag in soil A (10 days) than in soil B (4 days). In soil A microcosms supplemented with NaNO
3 or NH
4NO
3, rates of denitrification were 20.6 and 13.6 mg NO
3
− kg
−1 day
−1, respectively, and in soil B, they were 18.5 and 12.5 mg NO
3
− kg
−1 day
−1, respectively. We conclude that denitrification may lead to a substantial loss of nitrate, making it unavailable to the mineralizing bacterial population. Nitrous oxide was an important end-product accounting for 30–100% of total denitrification. These results indicate the need for preliminary treatability studies before implementing full-scale treatment processes incorporating commercial fertilizers.</abstract><pub>Elsevier B.V</pub><doi>10.1016/S0168-6496(99)00103-8</doi><tpages>7</tpages><oa>free_for_read</oa></addata></record> |
fulltext | fulltext |
identifier | ISSN: 0168-6496 |
ispartof | FEMS microbiology ecology, 2000, Vol.32 (1), p.17-23 |
issn | 0168-6496 1574-6941 |
language | eng |
recordid | cdi_proquest_miscellaneous_17599684 |
source | Oxford Academic Journals (Open Access) |
subjects | Ammonium ammonium salts Bacteria Bacterium Denitrification Hexadecane Nitrate Nitrous oxide Soil urea |
title | Hexadecane mineralization and denitrification in two diesel fuel-contaminated soils |
url | http://sfxeu10.hosted.exlibrisgroup.com/loughborough?ctx_ver=Z39.88-2004&ctx_enc=info:ofi/enc:UTF-8&ctx_tim=2025-01-21T06%3A56%3A23IST&url_ver=Z39.88-2004&url_ctx_fmt=infofi/fmt:kev:mtx:ctx&rfr_id=info:sid/primo.exlibrisgroup.com:primo3-Article-proquest_elsev&rft_val_fmt=info:ofi/fmt:kev:mtx:journal&rft.genre=article&rft.atitle=Hexadecane%20mineralization%20and%20denitrification%20in%20two%20diesel%20fuel-contaminated%20soils&rft.jtitle=FEMS%20microbiology%20ecology&rft.au=Roy,%20R%C3%A9al&rft.date=2000&rft.volume=32&rft.issue=1&rft.spage=17&rft.epage=23&rft.pages=17-23&rft.issn=0168-6496&rft.eissn=1574-6941&rft_id=info:doi/10.1016/S0168-6496(99)00103-8&rft_dat=%3Cproquest_elsev%3E17599684%3C/proquest_elsev%3E%3Cgrp_id%3Ecdi_FETCH-LOGICAL-e351t-e0f46a555299b866488dd329e34f37cc1b55b502016296af776ca512dd7414cc3%3C/grp_id%3E%3Coa%3E%3C/oa%3E%3Curl%3E%3C/url%3E&rft_id=info:oai/&rft_pqid=17599684&rft_id=info:pmid/&rfr_iscdi=true |