Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ

Abstract A bacterium that uses 2-chloroethanol as sole energy and carbon source coupled to denitrification was isolated from 1,2-dichloroethane-contaminated soil. Its 16 S rDNA sequence showed 98% similarity with the type strain of Pseudomonas stutzeri (DSM 5190) and the isolate was tentatively iden...
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Autor*in:	Dijk, J. A. [verfasserIn] Stams, A. J. M. Schraa, G. Ballerstedt, H. de Bont, J. A. M. Gerritse, J.

Format:	E-Artikel
Sprache:	Englisch

Erschienen:	2003

Schlagwörter:	Pseudomonas Putida Dehalogenase Chloroacetate Pseudomonas Stutzeri Denitrify Condition

Anmerkung:	© Springer-Verlag 2003

Übergeordnetes Werk:	Enthalten in: Applied microbiology and biotechnology - Berlin : Springer, 1975, 63(2003), 1 vom: 27. Mai, Seite 68-74
Übergeordnetes Werk:	volume:63 ; year:2003 ; number:1 ; day:27 ; month:05 ; pages:68-74

Links:	Volltext

DOI / URN:	10.1007/s00253-003-1346-z

Katalog-ID:	SPR002932369

Internformat


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245	1	0	\|a Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ
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520			\|a Abstract A bacterium that uses 2-chloroethanol as sole energy and carbon source coupled to denitrification was isolated from 1,2-dichloroethane-contaminated soil. Its 16 S rDNA sequence showed 98% similarity with the type strain of Pseudomonas stutzeri (DSM 5190) and the isolate was tentatively identified as Pseudomonas stutzeri strain JJ. Strain JJ oxidized 2-chloroethanol completely to $ CO_{2} $ with $ NO_{3} $− or $ O_{2} $ as electron acceptor, with a preference for $ O_{2} $ if supplied in combination. Optimum growth on 2-chloroethanol with nitrate occurred at 30 °C with a µmax of 0.14 $ h^{−1} $ and a yield of 4.4 g protein per mol 2-chloroethanol metabolized. Under aerobic conditions, the µmax was 0.31 $ h^{−1} $. $ NO_{2} $− also served as electron acceptor, but reduction of Fe(OH)3, $ MnO_{2} $, $ SO_{4} $2−, fumarate or $ ClO_{3} $− was not observed. Another chlorinated compound used as sole energy and carbon source under aerobic and denitrifying conditions was chloroacetate. Various different bacterial strains, including some closely related Pseudomonas stutzeri strains, were tested for their ability to grow on 2-chloroethanol as sole energy and carbon source under aerobic and denitrifying conditions, respectively. Only three strains, Pseudomonas stutzeri strain LMD 76.42, Pseudomonas putida US2 and Xanthobacter autotrophicus GJ10, grew aerobically on 2-chloroethanol. This is the first report of oxidation of 2-chloroethanol under denitrifying conditions by a pure bacterial culture.
650		4	\|a Pseudomonas Putida \|7 (dpeaa)DE-He213
650		4	\|a Dehalogenase \|7 (dpeaa)DE-He213
650		4	\|a Chloroacetate \|7 (dpeaa)DE-He213
650		4	\|a Pseudomonas Stutzeri \|7 (dpeaa)DE-He213
650		4	\|a Denitrify Condition \|7 (dpeaa)DE-He213
700	1		\|a Stams, A. J. M. \|4 aut
700	1		\|a Schraa, G. \|4 aut
700	1		\|a Ballerstedt, H. \|4 aut
700	1		\|a de Bont, J. A. M. \|4 aut
700	1		\|a Gerritse, J. \|4 aut
773	0	8	\|i Enthalten in \|t Applied microbiology and biotechnology \|d Berlin : Springer, 1975 \|g 63(2003), 1 vom: 27. Mai, Seite 68-74 \|w (DE-627)265509564 \|w (DE-600)1464336-4 \|x 1432-0614 \|7 nnns
773	1	8	\|g volume:63 \|g year:2003 \|g number:1 \|g day:27 \|g month:05 \|g pages:68-74
856	4	0	\|u https://dx.doi.org/10.1007/s00253-003-1346-z \|z lizenzpflichtig \|3 Volltext
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912			\|a GBV_ILN_31
912			\|a GBV_ILN_32
912			\|a GBV_ILN_39
912			\|a GBV_ILN_40
912			\|a GBV_ILN_60
912			\|a GBV_ILN_62
912			\|a GBV_ILN_63
912			\|a GBV_ILN_69
912			\|a GBV_ILN_70
912			\|a GBV_ILN_73
912			\|a GBV_ILN_74
912			\|a GBV_ILN_90
912			\|a GBV_ILN_95
912			\|a GBV_ILN_100
912			\|a GBV_ILN_101
912			\|a GBV_ILN_105
912			\|a GBV_ILN_110
912			\|a GBV_ILN_120
912			\|a GBV_ILN_138
912			\|a GBV_ILN_150
912			\|a GBV_ILN_151
912			\|a GBV_ILN_152
912			\|a GBV_ILN_161
912			\|a GBV_ILN_165
912			\|a GBV_ILN_170
912			\|a GBV_ILN_171
912			\|a GBV_ILN_187
912			\|a GBV_ILN_206
912			\|a GBV_ILN_213
912			\|a GBV_ILN_224
912			\|a GBV_ILN_230
912			\|a GBV_ILN_250
912			\|a GBV_ILN_267
912			\|a GBV_ILN_281
912			\|a GBV_ILN_285
912			\|a GBV_ILN_293
912			\|a GBV_ILN_370
912			\|a GBV_ILN_381
912			\|a GBV_ILN_602
912			\|a GBV_ILN_636
912			\|a GBV_ILN_702
912			\|a GBV_ILN_2001
912			\|a GBV_ILN_2003
912			\|a GBV_ILN_2004
912			\|a GBV_ILN_2005
912			\|a GBV_ILN_2006
912			\|a GBV_ILN_2007
912			\|a GBV_ILN_2008
912			\|a GBV_ILN_2009
912			\|a GBV_ILN_2010
912			\|a GBV_ILN_2011
912			\|a GBV_ILN_2014
912			\|a GBV_ILN_2015
912			\|a GBV_ILN_2020
912			\|a GBV_ILN_2021
912			\|a GBV_ILN_2025
912			\|a GBV_ILN_2026
912			\|a GBV_ILN_2027
912			\|a GBV_ILN_2031
912			\|a GBV_ILN_2034
912			\|a GBV_ILN_2037
912			\|a GBV_ILN_2038
912			\|a GBV_ILN_2039
912			\|a GBV_ILN_2044
912			\|a GBV_ILN_2048
912			\|a GBV_ILN_2049
912			\|a GBV_ILN_2050
912			\|a GBV_ILN_2055
912			\|a GBV_ILN_2056
912			\|a GBV_ILN_2057
912			\|a GBV_ILN_2059
912			\|a GBV_ILN_2061
912			\|a GBV_ILN_2064
912			\|a GBV_ILN_2068
912			\|a GBV_ILN_2070
912			\|a GBV_ILN_2086
912			\|a GBV_ILN_2093
912			\|a GBV_ILN_2106
912			\|a GBV_ILN_2107
912			\|a GBV_ILN_2110
912			\|a GBV_ILN_2113
912			\|a GBV_ILN_2118
912			\|a GBV_ILN_2119
912			\|a GBV_ILN_2129
912			\|a GBV_ILN_2143
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912			\|a GBV_ILN_2147
912			\|a GBV_ILN_2153
912			\|a GBV_ILN_2188
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912			\|a GBV_ILN_2336
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912			\|a GBV_ILN_2522
912			\|a GBV_ILN_2548
912			\|a GBV_ILN_4012
912			\|a GBV_ILN_4035
912			\|a GBV_ILN_4037
912			\|a GBV_ILN_4046
912			\|a GBV_ILN_4112
912			\|a GBV_ILN_4125
912			\|a GBV_ILN_4126
912			\|a GBV_ILN_4242
912			\|a GBV_ILN_4246
912			\|a GBV_ILN_4249
912			\|a GBV_ILN_4251
912			\|a GBV_ILN_4305
912			\|a GBV_ILN_4306
912			\|a GBV_ILN_4307
912			\|a GBV_ILN_4313
912			\|a GBV_ILN_4322
912			\|a GBV_ILN_4323
912			\|a GBV_ILN_4324
912			\|a GBV_ILN_4326
912			\|a GBV_ILN_4333
912			\|a GBV_ILN_4334
912			\|a GBV_ILN_4335
912			\|a GBV_ILN_4336
912			\|a GBV_ILN_4338
912			\|a GBV_ILN_4393
912			\|a GBV_ILN_4700
951			\|a AR
952			\|d 63 \|j 2003 \|e 1 \|b 27 \|c 05 \|h 68-74

Indexfelder

author_variant	j a d ja jad a j m s ajm ajms g s gs h b hb b j a m d bjam bjamd j g jg
matchkey_str	article:14320614:2003----::neoioiainfclrehnlnedntiyncniinbpe
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publishDate	2003
allfields	10.1007/s00253-003-1346-z doi (DE-627)SPR002932369 (SPR)s00253-003-1346-z-e DE-627 ger DE-627 rakwb eng Dijk, J. A. verfasserin aut Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ 2003 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2003 Abstract A bacterium that uses 2-chloroethanol as sole energy and carbon source coupled to denitrification was isolated from 1,2-dichloroethane-contaminated soil. Its 16 S rDNA sequence showed 98% similarity with the type strain of Pseudomonas stutzeri (DSM 5190) and the isolate was tentatively identified as Pseudomonas stutzeri strain JJ. Strain JJ oxidized 2-chloroethanol completely to $ CO_{2} $ with $ NO_{3} $− or $ O_{2} $ as electron acceptor, with a preference for $ O_{2} $ if supplied in combination. Optimum growth on 2-chloroethanol with nitrate occurred at 30 °C with a µmax of 0.14 $ h^{−1} $ and a yield of 4.4 g protein per mol 2-chloroethanol metabolized. Under aerobic conditions, the µmax was 0.31 $ h^{−1} $. $ NO_{2} $− also served as electron acceptor, but reduction of Fe(OH)3, $ MnO_{2} $, $ SO_{4} $2−, fumarate or $ ClO_{3} $− was not observed. Another chlorinated compound used as sole energy and carbon source under aerobic and denitrifying conditions was chloroacetate. Various different bacterial strains, including some closely related Pseudomonas stutzeri strains, were tested for their ability to grow on 2-chloroethanol as sole energy and carbon source under aerobic and denitrifying conditions, respectively. Only three strains, Pseudomonas stutzeri strain LMD 76.42, Pseudomonas putida US2 and Xanthobacter autotrophicus GJ10, grew aerobically on 2-chloroethanol. This is the first report of oxidation of 2-chloroethanol under denitrifying conditions by a pure bacterial culture. Pseudomonas Putida (dpeaa)DE-He213 Dehalogenase (dpeaa)DE-He213 Chloroacetate (dpeaa)DE-He213 Pseudomonas Stutzeri (dpeaa)DE-He213 Denitrify Condition (dpeaa)DE-He213 Stams, A. J. M. aut Schraa, G. aut Ballerstedt, H. aut de Bont, J. A. M. aut Gerritse, J. aut Enthalten in Applied microbiology and biotechnology Berlin : Springer, 1975 63(2003), 1 vom: 27. Mai, Seite 68-74 (DE-627)265509564 (DE-600)1464336-4 1432-0614 nnns volume:63 year:2003 number:1 day:27 month:05 pages:68-74 https://dx.doi.org/10.1007/s00253-003-1346-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_165 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_267 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2110 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 63 2003 1 27 05 68-74
spelling	10.1007/s00253-003-1346-z doi (DE-627)SPR002932369 (SPR)s00253-003-1346-z-e DE-627 ger DE-627 rakwb eng Dijk, J. A. verfasserin aut Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ 2003 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2003 Abstract A bacterium that uses 2-chloroethanol as sole energy and carbon source coupled to denitrification was isolated from 1,2-dichloroethane-contaminated soil. Its 16 S rDNA sequence showed 98% similarity with the type strain of Pseudomonas stutzeri (DSM 5190) and the isolate was tentatively identified as Pseudomonas stutzeri strain JJ. Strain JJ oxidized 2-chloroethanol completely to $ CO_{2} $ with $ NO_{3} $− or $ O_{2} $ as electron acceptor, with a preference for $ O_{2} $ if supplied in combination. Optimum growth on 2-chloroethanol with nitrate occurred at 30 °C with a µmax of 0.14 $ h^{−1} $ and a yield of 4.4 g protein per mol 2-chloroethanol metabolized. Under aerobic conditions, the µmax was 0.31 $ h^{−1} $. $ NO_{2} $− also served as electron acceptor, but reduction of Fe(OH)3, $ MnO_{2} $, $ SO_{4} $2−, fumarate or $ ClO_{3} $− was not observed. Another chlorinated compound used as sole energy and carbon source under aerobic and denitrifying conditions was chloroacetate. Various different bacterial strains, including some closely related Pseudomonas stutzeri strains, were tested for their ability to grow on 2-chloroethanol as sole energy and carbon source under aerobic and denitrifying conditions, respectively. Only three strains, Pseudomonas stutzeri strain LMD 76.42, Pseudomonas putida US2 and Xanthobacter autotrophicus GJ10, grew aerobically on 2-chloroethanol. This is the first report of oxidation of 2-chloroethanol under denitrifying conditions by a pure bacterial culture. Pseudomonas Putida (dpeaa)DE-He213 Dehalogenase (dpeaa)DE-He213 Chloroacetate (dpeaa)DE-He213 Pseudomonas Stutzeri (dpeaa)DE-He213 Denitrify Condition (dpeaa)DE-He213 Stams, A. J. M. aut Schraa, G. aut Ballerstedt, H. aut de Bont, J. A. M. aut Gerritse, J. aut Enthalten in Applied microbiology and biotechnology Berlin : Springer, 1975 63(2003), 1 vom: 27. Mai, Seite 68-74 (DE-627)265509564 (DE-600)1464336-4 1432-0614 nnns volume:63 year:2003 number:1 day:27 month:05 pages:68-74 https://dx.doi.org/10.1007/s00253-003-1346-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_165 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_267 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2110 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 63 2003 1 27 05 68-74
allfields_unstemmed	10.1007/s00253-003-1346-z doi (DE-627)SPR002932369 (SPR)s00253-003-1346-z-e DE-627 ger DE-627 rakwb eng Dijk, J. A. verfasserin aut Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ 2003 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2003 Abstract A bacterium that uses 2-chloroethanol as sole energy and carbon source coupled to denitrification was isolated from 1,2-dichloroethane-contaminated soil. Its 16 S rDNA sequence showed 98% similarity with the type strain of Pseudomonas stutzeri (DSM 5190) and the isolate was tentatively identified as Pseudomonas stutzeri strain JJ. Strain JJ oxidized 2-chloroethanol completely to $ CO_{2} $ with $ NO_{3} $− or $ O_{2} $ as electron acceptor, with a preference for $ O_{2} $ if supplied in combination. Optimum growth on 2-chloroethanol with nitrate occurred at 30 °C with a µmax of 0.14 $ h^{−1} $ and a yield of 4.4 g protein per mol 2-chloroethanol metabolized. Under aerobic conditions, the µmax was 0.31 $ h^{−1} $. $ NO_{2} $− also served as electron acceptor, but reduction of Fe(OH)3, $ MnO_{2} $, $ SO_{4} $2−, fumarate or $ ClO_{3} $− was not observed. Another chlorinated compound used as sole energy and carbon source under aerobic and denitrifying conditions was chloroacetate. Various different bacterial strains, including some closely related Pseudomonas stutzeri strains, were tested for their ability to grow on 2-chloroethanol as sole energy and carbon source under aerobic and denitrifying conditions, respectively. Only three strains, Pseudomonas stutzeri strain LMD 76.42, Pseudomonas putida US2 and Xanthobacter autotrophicus GJ10, grew aerobically on 2-chloroethanol. This is the first report of oxidation of 2-chloroethanol under denitrifying conditions by a pure bacterial culture. Pseudomonas Putida (dpeaa)DE-He213 Dehalogenase (dpeaa)DE-He213 Chloroacetate (dpeaa)DE-He213 Pseudomonas Stutzeri (dpeaa)DE-He213 Denitrify Condition (dpeaa)DE-He213 Stams, A. J. M. aut Schraa, G. aut Ballerstedt, H. aut de Bont, J. A. M. aut Gerritse, J. aut Enthalten in Applied microbiology and biotechnology Berlin : Springer, 1975 63(2003), 1 vom: 27. Mai, Seite 68-74 (DE-627)265509564 (DE-600)1464336-4 1432-0614 nnns volume:63 year:2003 number:1 day:27 month:05 pages:68-74 https://dx.doi.org/10.1007/s00253-003-1346-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_165 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_267 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2110 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 63 2003 1 27 05 68-74
allfieldsGer	10.1007/s00253-003-1346-z doi (DE-627)SPR002932369 (SPR)s00253-003-1346-z-e DE-627 ger DE-627 rakwb eng Dijk, J. A. verfasserin aut Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ 2003 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2003 Abstract A bacterium that uses 2-chloroethanol as sole energy and carbon source coupled to denitrification was isolated from 1,2-dichloroethane-contaminated soil. Its 16 S rDNA sequence showed 98% similarity with the type strain of Pseudomonas stutzeri (DSM 5190) and the isolate was tentatively identified as Pseudomonas stutzeri strain JJ. Strain JJ oxidized 2-chloroethanol completely to $ CO_{2} $ with $ NO_{3} $− or $ O_{2} $ as electron acceptor, with a preference for $ O_{2} $ if supplied in combination. Optimum growth on 2-chloroethanol with nitrate occurred at 30 °C with a µmax of 0.14 $ h^{−1} $ and a yield of 4.4 g protein per mol 2-chloroethanol metabolized. Under aerobic conditions, the µmax was 0.31 $ h^{−1} $. $ NO_{2} $− also served as electron acceptor, but reduction of Fe(OH)3, $ MnO_{2} $, $ SO_{4} $2−, fumarate or $ ClO_{3} $− was not observed. Another chlorinated compound used as sole energy and carbon source under aerobic and denitrifying conditions was chloroacetate. Various different bacterial strains, including some closely related Pseudomonas stutzeri strains, were tested for their ability to grow on 2-chloroethanol as sole energy and carbon source under aerobic and denitrifying conditions, respectively. Only three strains, Pseudomonas stutzeri strain LMD 76.42, Pseudomonas putida US2 and Xanthobacter autotrophicus GJ10, grew aerobically on 2-chloroethanol. This is the first report of oxidation of 2-chloroethanol under denitrifying conditions by a pure bacterial culture. Pseudomonas Putida (dpeaa)DE-He213 Dehalogenase (dpeaa)DE-He213 Chloroacetate (dpeaa)DE-He213 Pseudomonas Stutzeri (dpeaa)DE-He213 Denitrify Condition (dpeaa)DE-He213 Stams, A. J. M. aut Schraa, G. aut Ballerstedt, H. aut de Bont, J. A. M. aut Gerritse, J. aut Enthalten in Applied microbiology and biotechnology Berlin : Springer, 1975 63(2003), 1 vom: 27. Mai, Seite 68-74 (DE-627)265509564 (DE-600)1464336-4 1432-0614 nnns volume:63 year:2003 number:1 day:27 month:05 pages:68-74 https://dx.doi.org/10.1007/s00253-003-1346-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_165 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_267 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2110 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 63 2003 1 27 05 68-74
allfieldsSound	10.1007/s00253-003-1346-z doi (DE-627)SPR002932369 (SPR)s00253-003-1346-z-e DE-627 ger DE-627 rakwb eng Dijk, J. A. verfasserin aut Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ 2003 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2003 Abstract A bacterium that uses 2-chloroethanol as sole energy and carbon source coupled to denitrification was isolated from 1,2-dichloroethane-contaminated soil. Its 16 S rDNA sequence showed 98% similarity with the type strain of Pseudomonas stutzeri (DSM 5190) and the isolate was tentatively identified as Pseudomonas stutzeri strain JJ. Strain JJ oxidized 2-chloroethanol completely to $ CO_{2} $ with $ NO_{3} $− or $ O_{2} $ as electron acceptor, with a preference for $ O_{2} $ if supplied in combination. Optimum growth on 2-chloroethanol with nitrate occurred at 30 °C with a µmax of 0.14 $ h^{−1} $ and a yield of 4.4 g protein per mol 2-chloroethanol metabolized. Under aerobic conditions, the µmax was 0.31 $ h^{−1} $. $ NO_{2} $− also served as electron acceptor, but reduction of Fe(OH)3, $ MnO_{2} $, $ SO_{4} $2−, fumarate or $ ClO_{3} $− was not observed. Another chlorinated compound used as sole energy and carbon source under aerobic and denitrifying conditions was chloroacetate. Various different bacterial strains, including some closely related Pseudomonas stutzeri strains, were tested for their ability to grow on 2-chloroethanol as sole energy and carbon source under aerobic and denitrifying conditions, respectively. Only three strains, Pseudomonas stutzeri strain LMD 76.42, Pseudomonas putida US2 and Xanthobacter autotrophicus GJ10, grew aerobically on 2-chloroethanol. This is the first report of oxidation of 2-chloroethanol under denitrifying conditions by a pure bacterial culture. Pseudomonas Putida (dpeaa)DE-He213 Dehalogenase (dpeaa)DE-He213 Chloroacetate (dpeaa)DE-He213 Pseudomonas Stutzeri (dpeaa)DE-He213 Denitrify Condition (dpeaa)DE-He213 Stams, A. J. M. aut Schraa, G. aut Ballerstedt, H. aut de Bont, J. A. M. aut Gerritse, J. aut Enthalten in Applied microbiology and biotechnology Berlin : Springer, 1975 63(2003), 1 vom: 27. Mai, Seite 68-74 (DE-627)265509564 (DE-600)1464336-4 1432-0614 nnns volume:63 year:2003 number:1 day:27 month:05 pages:68-74 https://dx.doi.org/10.1007/s00253-003-1346-z lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OLC-PHA GBV_ILN_11 GBV_ILN_20 GBV_ILN_22 GBV_ILN_23 GBV_ILN_24 GBV_ILN_31 GBV_ILN_32 GBV_ILN_39 GBV_ILN_40 GBV_ILN_60 GBV_ILN_62 GBV_ILN_63 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 GBV_ILN_101 GBV_ILN_105 GBV_ILN_110 GBV_ILN_120 GBV_ILN_138 GBV_ILN_150 GBV_ILN_151 GBV_ILN_152 GBV_ILN_161 GBV_ILN_165 GBV_ILN_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_206 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_267 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 GBV_ILN_381 GBV_ILN_602 GBV_ILN_636 GBV_ILN_702 GBV_ILN_2001 GBV_ILN_2003 GBV_ILN_2004 GBV_ILN_2005 GBV_ILN_2006 GBV_ILN_2007 GBV_ILN_2008 GBV_ILN_2009 GBV_ILN_2010 GBV_ILN_2011 GBV_ILN_2014 GBV_ILN_2015 GBV_ILN_2020 GBV_ILN_2021 GBV_ILN_2025 GBV_ILN_2026 GBV_ILN_2027 GBV_ILN_2031 GBV_ILN_2034 GBV_ILN_2037 GBV_ILN_2038 GBV_ILN_2039 GBV_ILN_2044 GBV_ILN_2048 GBV_ILN_2049 GBV_ILN_2050 GBV_ILN_2055 GBV_ILN_2056 GBV_ILN_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2110 GBV_ILN_2113 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2232 GBV_ILN_2336 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4012 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 GBV_ILN_4126 GBV_ILN_4242 GBV_ILN_4246 GBV_ILN_4249 GBV_ILN_4251 GBV_ILN_4305 GBV_ILN_4306 GBV_ILN_4307 GBV_ILN_4313 GBV_ILN_4322 GBV_ILN_4323 GBV_ILN_4324 GBV_ILN_4326 GBV_ILN_4333 GBV_ILN_4334 GBV_ILN_4335 GBV_ILN_4336 GBV_ILN_4338 GBV_ILN_4393 GBV_ILN_4700 AR 63 2003 1 27 05 68-74
language	English
source	Enthalten in Applied microbiology and biotechnology 63(2003), 1 vom: 27. Mai, Seite 68-74 volume:63 year:2003 number:1 day:27 month:05 pages:68-74
sourceStr	Enthalten in Applied microbiology and biotechnology 63(2003), 1 vom: 27. Mai, Seite 68-74 volume:63 year:2003 number:1 day:27 month:05 pages:68-74
format_phy_str_mv	Article
institution	findex.gbv.de
topic_facet	Pseudomonas Putida Dehalogenase Chloroacetate Pseudomonas Stutzeri Denitrify Condition
isfreeaccess_bool	false
container_title	Applied microbiology and biotechnology
authorswithroles_txt_mv	Dijk, J. A. @@aut@@ Stams, A. J. M. @@aut@@ Schraa, G. @@aut@@ Ballerstedt, H. @@aut@@ de Bont, J. A. M. @@aut@@ Gerritse, J. @@aut@@
publishDateDaySort_date	2003-05-27T00:00:00Z
hierarchy_top_id	265509564
id	SPR002932369
language_de	englisch
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author	Dijk, J. A.
spellingShingle	Dijk, J. A. misc Pseudomonas Putida misc Dehalogenase misc Chloroacetate misc Pseudomonas Stutzeri misc Denitrify Condition Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ
authorStr	Dijk, J. A.
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topic_title	Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ Pseudomonas Putida (dpeaa)DE-He213 Dehalogenase (dpeaa)DE-He213 Chloroacetate (dpeaa)DE-He213 Pseudomonas Stutzeri (dpeaa)DE-He213 Denitrify Condition (dpeaa)DE-He213
topic	misc Pseudomonas Putida misc Dehalogenase misc Chloroacetate misc Pseudomonas Stutzeri misc Denitrify Condition
topic_unstemmed	misc Pseudomonas Putida misc Dehalogenase misc Chloroacetate misc Pseudomonas Stutzeri misc Denitrify Condition
topic_browse	misc Pseudomonas Putida misc Dehalogenase misc Chloroacetate misc Pseudomonas Stutzeri misc Denitrify Condition
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title	Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ
ctrlnum	(DE-627)SPR002932369 (SPR)s00253-003-1346-z-e
title_full	Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ
author_sort	Dijk, J. A.
journal	Applied microbiology and biotechnology
journalStr	Applied microbiology and biotechnology
lang_code	eng
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author_browse	Dijk, J. A. Stams, A. J. M. Schraa, G. Ballerstedt, H. de Bont, J. A. M. Gerritse, J.
container_volume	63
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author-letter	Dijk, J. A.
doi_str_mv	10.1007/s00253-003-1346-z
title_sort	anaerobic oxidation of 2-chloroethanol under denitrifying conditions by pseudomonas stutzeri strain jj
title_auth	Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ
abstract	Abstract A bacterium that uses 2-chloroethanol as sole energy and carbon source coupled to denitrification was isolated from 1,2-dichloroethane-contaminated soil. Its 16 S rDNA sequence showed 98% similarity with the type strain of Pseudomonas stutzeri (DSM 5190) and the isolate was tentatively identified as Pseudomonas stutzeri strain JJ. Strain JJ oxidized 2-chloroethanol completely to $ CO_{2} $ with $ NO_{3} $− or $ O_{2} $ as electron acceptor, with a preference for $ O_{2} $ if supplied in combination. Optimum growth on 2-chloroethanol with nitrate occurred at 30 °C with a µmax of 0.14 $ h^{−1} $ and a yield of 4.4 g protein per mol 2-chloroethanol metabolized. Under aerobic conditions, the µmax was 0.31 $ h^{−1} $. $ NO_{2} $− also served as electron acceptor, but reduction of Fe(OH)3, $ MnO_{2} $, $ SO_{4} $2−, fumarate or $ ClO_{3} $− was not observed. Another chlorinated compound used as sole energy and carbon source under aerobic and denitrifying conditions was chloroacetate. Various different bacterial strains, including some closely related Pseudomonas stutzeri strains, were tested for their ability to grow on 2-chloroethanol as sole energy and carbon source under aerobic and denitrifying conditions, respectively. Only three strains, Pseudomonas stutzeri strain LMD 76.42, Pseudomonas putida US2 and Xanthobacter autotrophicus GJ10, grew aerobically on 2-chloroethanol. This is the first report of oxidation of 2-chloroethanol under denitrifying conditions by a pure bacterial culture. © Springer-Verlag 2003
abstractGer	Abstract A bacterium that uses 2-chloroethanol as sole energy and carbon source coupled to denitrification was isolated from 1,2-dichloroethane-contaminated soil. Its 16 S rDNA sequence showed 98% similarity with the type strain of Pseudomonas stutzeri (DSM 5190) and the isolate was tentatively identified as Pseudomonas stutzeri strain JJ. Strain JJ oxidized 2-chloroethanol completely to $ CO_{2} $ with $ NO_{3} $− or $ O_{2} $ as electron acceptor, with a preference for $ O_{2} $ if supplied in combination. Optimum growth on 2-chloroethanol with nitrate occurred at 30 °C with a µmax of 0.14 $ h^{−1} $ and a yield of 4.4 g protein per mol 2-chloroethanol metabolized. Under aerobic conditions, the µmax was 0.31 $ h^{−1} $. $ NO_{2} $− also served as electron acceptor, but reduction of Fe(OH)3, $ MnO_{2} $, $ SO_{4} $2−, fumarate or $ ClO_{3} $− was not observed. Another chlorinated compound used as sole energy and carbon source under aerobic and denitrifying conditions was chloroacetate. Various different bacterial strains, including some closely related Pseudomonas stutzeri strains, were tested for their ability to grow on 2-chloroethanol as sole energy and carbon source under aerobic and denitrifying conditions, respectively. Only three strains, Pseudomonas stutzeri strain LMD 76.42, Pseudomonas putida US2 and Xanthobacter autotrophicus GJ10, grew aerobically on 2-chloroethanol. This is the first report of oxidation of 2-chloroethanol under denitrifying conditions by a pure bacterial culture. © Springer-Verlag 2003
abstract_unstemmed	Abstract A bacterium that uses 2-chloroethanol as sole energy and carbon source coupled to denitrification was isolated from 1,2-dichloroethane-contaminated soil. Its 16 S rDNA sequence showed 98% similarity with the type strain of Pseudomonas stutzeri (DSM 5190) and the isolate was tentatively identified as Pseudomonas stutzeri strain JJ. Strain JJ oxidized 2-chloroethanol completely to $ CO_{2} $ with $ NO_{3} $− or $ O_{2} $ as electron acceptor, with a preference for $ O_{2} $ if supplied in combination. Optimum growth on 2-chloroethanol with nitrate occurred at 30 °C with a µmax of 0.14 $ h^{−1} $ and a yield of 4.4 g protein per mol 2-chloroethanol metabolized. Under aerobic conditions, the µmax was 0.31 $ h^{−1} $. $ NO_{2} $− also served as electron acceptor, but reduction of Fe(OH)3, $ MnO_{2} $, $ SO_{4} $2−, fumarate or $ ClO_{3} $− was not observed. Another chlorinated compound used as sole energy and carbon source under aerobic and denitrifying conditions was chloroacetate. Various different bacterial strains, including some closely related Pseudomonas stutzeri strains, were tested for their ability to grow on 2-chloroethanol as sole energy and carbon source under aerobic and denitrifying conditions, respectively. Only three strains, Pseudomonas stutzeri strain LMD 76.42, Pseudomonas putida US2 and Xanthobacter autotrophicus GJ10, grew aerobically on 2-chloroethanol. This is the first report of oxidation of 2-chloroethanol under denitrifying conditions by a pure bacterial culture. © Springer-Verlag 2003
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title_short	Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ
url	https://dx.doi.org/10.1007/s00253-003-1346-z
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author2	Stams, A. J. M. Schraa, G. Ballerstedt, H. de Bont, J. A. M. Gerritse, J.
author2Str	Stams, A. J. M. Schraa, G. Ballerstedt, H. de Bont, J. A. M. Gerritse, J.
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doi_str	10.1007/s00253-003-1346-z
up_date	2024-07-03T16:09:28.214Z
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A.</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2003</subfield></datafield><datafield tag="336" ind1=" " ind2=" "><subfield code="a">Text</subfield><subfield code="b">txt</subfield><subfield code="2">rdacontent</subfield></datafield><datafield tag="337" ind1=" " ind2=" "><subfield code="a">Computermedien</subfield><subfield code="b">c</subfield><subfield code="2">rdamedia</subfield></datafield><datafield tag="338" ind1=" " ind2=" "><subfield code="a">Online-Ressource</subfield><subfield code="b">cr</subfield><subfield code="2">rdacarrier</subfield></datafield><datafield tag="500" ind1=" " ind2=" "><subfield code="a">© Springer-Verlag 2003</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract A bacterium that uses 2-chloroethanol as sole energy and carbon source coupled to denitrification was isolated from 1,2-dichloroethane-contaminated soil. Its 16 S rDNA sequence showed 98% similarity with the type strain of Pseudomonas stutzeri (DSM 5190) and the isolate was tentatively identified as Pseudomonas stutzeri strain JJ. Strain JJ oxidized 2-chloroethanol completely to $ CO_{2} $ with $ NO_{3} $− or $ O_{2} $ as electron acceptor, with a preference for $ O_{2} $ if supplied in combination. Optimum growth on 2-chloroethanol with nitrate occurred at 30 °C with a µmax of 0.14 $ h^{−1} $ and a yield of 4.4 g protein per mol 2-chloroethanol metabolized. Under aerobic conditions, the µmax was 0.31 $ h^{−1} $. $ NO_{2} $− also served as electron acceptor, but reduction of Fe(OH)3, $ MnO_{2} $, $ SO_{4} $2−, fumarate or $ ClO_{3} $− was not observed. Another chlorinated compound used as sole energy and carbon source under aerobic and denitrifying conditions was chloroacetate. Various different bacterial strains, including some closely related Pseudomonas stutzeri strains, were tested for their ability to grow on 2-chloroethanol as sole energy and carbon source under aerobic and denitrifying conditions, respectively. Only three strains, Pseudomonas stutzeri strain LMD 76.42, Pseudomonas putida US2 and Xanthobacter autotrophicus GJ10, grew aerobically on 2-chloroethanol. 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Anaerobic oxidation of 2-chloroethanol under denitrifying conditions by Pseudomonas stutzeri strain JJ

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