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Monitoring of biodegradative Pseudomonas putida strains in aquatic environments using molecular techniques
Monitoring strategies were developed to track non-genetically engineered Pseudomonas putida strains in the open environment. The strain E1 was used for four years for the biodegradation of phenolic compounds in industrial wastewater in Polva, Estonia. In this study we used the strain E2 which is a n...
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Published in: | Microbial ecology 1997-03, Vol.33 (2), p.124-133 |
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description | Monitoring strategies were developed to track non-genetically engineered Pseudomonas putida strains in the open environment. The strain E1 was used for four years for the biodegradation of phenolic compounds in industrial wastewater in Polva, Estonia. In this study we used the strain E2 which is a non-carbenicillin-resistant variant of the strain E1. Both strains have a deletion of approximately 34 kb in the TOL plasmid pWW0 which served as a basis for discrimination from indigenous bacteria by molecular analyses. Other targets used for PCR and DNA hybridization were the xylE gene and a sequence located in the left-handed region of to the transposon Tn4652. In laboratory tests we demonstrated that two cells inoculated into 20 ml of river water could be detected against a background of more than 10(7) colony forming units (CFUs) by a combination of growth on selective media and molecular analysis. Using the same combination of methods in a deliberate release experiment, detection of the released strain was possible only to 32 h after release. It is assumed that the released strains did not survive in the aquatic ecosystem, mainly due to the high dilution rate. The combination of cultivation on selective media and molecular analyses proved useful for tracking Pseudomonas putida strain E2 in an aquatic environment |
doi_str_mv | 10.1007/s002489900014 |
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The strain E1 was used for four years for the biodegradation of phenolic compounds in industrial wastewater in Polva, Estonia. In this study we used the strain E2 which is a non-carbenicillin-resistant variant of the strain E1. Both strains have a deletion of approximately 34 kb in the TOL plasmid pWW0 which served as a basis for discrimination from indigenous bacteria by molecular analyses. Other targets used for PCR and DNA hybridization were the xylE gene and a sequence located in the left-handed region of to the transposon Tn4652. In laboratory tests we demonstrated that two cells inoculated into 20 ml of river water could be detected against a background of more than 10(7) colony forming units (CFUs) by a combination of growth on selective media and molecular analysis. Using the same combination of methods in a deliberate release experiment, detection of the released strain was possible only to 32 h after release. It is assumed that the released strains did not survive in the aquatic ecosystem, mainly due to the high dilution rate. The combination of cultivation on selective media and molecular analyses proved useful for tracking Pseudomonas putida strain E2 in an aquatic environment</description><identifier>ISSN: 0095-3628</identifier><identifier>EISSN: 1432-184X</identifier><identifier>DOI: 10.1007/s002489900014</identifier><identifier>PMID: 9052646</identifier><identifier>CODEN: MCBEBU</identifier><language>eng</language><publisher>New York, NY: Springer-Verlag New York Inc</publisher><subject>AMBIENTE ACUATICO ; ANALYTICAL METHODS ; Animal, plant and microbial ecology ; AQUATIC ENVIRONMENT ; Bacteria ; Bacteriological methods and techniques used in bacteriology ; Bacteriology ; BIODECONTAMINACION ; Biodegradation ; Biological and medical sciences ; BIOREMEDIATION ; Biotechnology ; CONTROLE CONTINU ; Environment and pollution ; Freshwater ; Fundamental and applied biological sciences. Psychology ; Industrial applications and implications. Economical aspects ; Microbial ecology ; Microbiology ; Microorganisms ; MILIEU AQUATIQUE ; Miscellaneous ; MONITORING ; Phenols ; Plasmids ; Polymerase chain reaction ; Product category rules ; PSEUDOMONAS PUTIDA ; Sewage ; TECHNIQUE ANALYTIQUE ; TECNICAS ANALITICAS ; Transposons ; Various environments (extraatmospheric space, air, water) ; VIGILANCIA</subject><ispartof>Microbial ecology, 1997-03, Vol.33 (2), p.124-133</ispartof><rights>Copyright 1997 Springer-Verlag New York Inc.</rights><rights>1997 INIST-CNRS</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c519t-cdfa6dcf8a29064f941bf46e0d20d9f2faee91fdad5ed9d804da770df6ebc7c13</citedby></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://www.jstor.org/stable/pdf/4251478$$EPDF$$P50$$Gjstor$$H</linktopdf><linktohtml>$$Uhttps://www.jstor.org/stable/4251478$$EHTML$$P50$$Gjstor$$H</linktohtml><link.rule.ids>314,780,784,27924,27925,58238,58471</link.rule.ids><backlink>$$Uhttp://pascal-francis.inist.fr/vibad/index.php?action=getRecordDetail&idt=2604642$$DView record in Pascal Francis$$Hfree_for_read</backlink><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/9052646$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Wand, H</creatorcontrib><creatorcontrib>Laht, T</creatorcontrib><creatorcontrib>Peters, M</creatorcontrib><creatorcontrib>Becker, P.M</creatorcontrib><creatorcontrib>Stottmeister, U</creatorcontrib><creatorcontrib>Heinaru, A</creatorcontrib><title>Monitoring of biodegradative Pseudomonas putida strains in aquatic environments using molecular techniques</title><title>Microbial ecology</title><addtitle>Microb Ecol</addtitle><description>Monitoring strategies were developed to track non-genetically engineered Pseudomonas putida strains in the open environment. The strain E1 was used for four years for the biodegradation of phenolic compounds in industrial wastewater in Polva, Estonia. In this study we used the strain E2 which is a non-carbenicillin-resistant variant of the strain E1. Both strains have a deletion of approximately 34 kb in the TOL plasmid pWW0 which served as a basis for discrimination from indigenous bacteria by molecular analyses. Other targets used for PCR and DNA hybridization were the xylE gene and a sequence located in the left-handed region of to the transposon Tn4652. In laboratory tests we demonstrated that two cells inoculated into 20 ml of river water could be detected against a background of more than 10(7) colony forming units (CFUs) by a combination of growth on selective media and molecular analysis. Using the same combination of methods in a deliberate release experiment, detection of the released strain was possible only to 32 h after release. 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Economical aspects</topic><topic>Microbial ecology</topic><topic>Microbiology</topic><topic>Microorganisms</topic><topic>MILIEU AQUATIQUE</topic><topic>Miscellaneous</topic><topic>MONITORING</topic><topic>Phenols</topic><topic>Plasmids</topic><topic>Polymerase chain reaction</topic><topic>Product category rules</topic><topic>PSEUDOMONAS PUTIDA</topic><topic>Sewage</topic><topic>TECHNIQUE ANALYTIQUE</topic><topic>TECNICAS ANALITICAS</topic><topic>Transposons</topic><topic>Various environments (extraatmospheric space, air, water)</topic><topic>VIGILANCIA</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Wand, H</creatorcontrib><creatorcontrib>Laht, T</creatorcontrib><creatorcontrib>Peters, M</creatorcontrib><creatorcontrib>Becker, P.M</creatorcontrib><creatorcontrib>Stottmeister, U</creatorcontrib><creatorcontrib>Heinaru, A</creatorcontrib><collection>AGRIS</collection><collection>Pascal-Francis</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>ASFA: Aquatic Sciences and Fisheries Abstracts</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) 1: Biological Sciences & Living Resources</collection><collection>Aquatic Science & Fisheries Abstracts (ASFA) Professional</collection><collection>Bacteriology Abstracts (Microbiology B)</collection><collection>Ecology Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Pollution Abstracts</collection><collection>Water Resources Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>MEDLINE - Academic</collection><collection>Mechanical & Transportation Engineering Abstracts</collection><collection>Civil Engineering Abstracts</collection><jtitle>Microbial ecology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Wand, H</au><au>Laht, T</au><au>Peters, M</au><au>Becker, P.M</au><au>Stottmeister, U</au><au>Heinaru, A</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Monitoring of biodegradative Pseudomonas putida strains in aquatic environments using molecular techniques</atitle><jtitle>Microbial ecology</jtitle><addtitle>Microb Ecol</addtitle><date>1997-03-01</date><risdate>1997</risdate><volume>33</volume><issue>2</issue><spage>124</spage><epage>133</epage><pages>124-133</pages><issn>0095-3628</issn><eissn>1432-184X</eissn><coden>MCBEBU</coden><abstract>Monitoring strategies were developed to track non-genetically engineered Pseudomonas putida strains in the open environment. The strain E1 was used for four years for the biodegradation of phenolic compounds in industrial wastewater in Polva, Estonia. In this study we used the strain E2 which is a non-carbenicillin-resistant variant of the strain E1. Both strains have a deletion of approximately 34 kb in the TOL plasmid pWW0 which served as a basis for discrimination from indigenous bacteria by molecular analyses. Other targets used for PCR and DNA hybridization were the xylE gene and a sequence located in the left-handed region of to the transposon Tn4652. In laboratory tests we demonstrated that two cells inoculated into 20 ml of river water could be detected against a background of more than 10(7) colony forming units (CFUs) by a combination of growth on selective media and molecular analysis. Using the same combination of methods in a deliberate release experiment, detection of the released strain was possible only to 32 h after release. It is assumed that the released strains did not survive in the aquatic ecosystem, mainly due to the high dilution rate. The combination of cultivation on selective media and molecular analyses proved useful for tracking Pseudomonas putida strain E2 in an aquatic environment</abstract><cop>New York, NY</cop><pub>Springer-Verlag New York Inc</pub><pmid>9052646</pmid><doi>10.1007/s002489900014</doi><tpages>10</tpages></addata></record> |
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subjects | AMBIENTE ACUATICO ANALYTICAL METHODS Animal, plant and microbial ecology AQUATIC ENVIRONMENT Bacteria Bacteriological methods and techniques used in bacteriology Bacteriology BIODECONTAMINACION Biodegradation Biological and medical sciences BIOREMEDIATION Biotechnology CONTROLE CONTINU Environment and pollution Freshwater Fundamental and applied biological sciences. Psychology Industrial applications and implications. Economical aspects Microbial ecology Microbiology Microorganisms MILIEU AQUATIQUE Miscellaneous MONITORING Phenols Plasmids Polymerase chain reaction Product category rules PSEUDOMONAS PUTIDA Sewage TECHNIQUE ANALYTIQUE TECNICAS ANALITICAS Transposons Various environments (extraatmospheric space, air, water) VIGILANCIA |
title | Monitoring of biodegradative Pseudomonas putida strains in aquatic environments using molecular techniques |
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