Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months
Abstract Heavy metal content analysis of River Torsa in India did not indicate any alarming level of toxicity for human consumption but revealed variation at the ppb level in different months. The variation in recoverable nickel and zinc resistant copiotrophic (or eutrophic) bacterial counts was exp...
Ausführliche Beschreibung
Gespeichert in:
| Autor*in: |
Bhadra, Bhaskar [verfasserIn] |
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| Format: |
E-Artikel |
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| Sprache: |
Englisch |
| Erschienen: |
2007 |
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| Schlagwörter: |
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| Anmerkung: |
© Springer-Verlag 2007 |
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| Übergeordnetes Werk: |
Enthalten in: Archives of microbiology - Berlin : Springer, 1930, 188(2007), 3 vom: 12. Apr., Seite 215-224 |
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| Übergeordnetes Werk: |
volume:188 ; year:2007 ; number:3 ; day:12 ; month:04 ; pages:215-224 |
| Links: |
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| DOI / URN: |
10.1007/s00203-007-0236-7 |
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| Katalog-ID: |
SPR001793160 |
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| 100 | 1 | |a Bhadra, Bhaskar |e verfasserin |4 aut | |
| 245 | 1 | 0 | |a Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months |
| 264 | 1 | |c 2007 | |
| 336 | |a Text |b txt |2 rdacontent | ||
| 337 | |a Computermedien |b c |2 rdamedia | ||
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| 500 | |a © Springer-Verlag 2007 | ||
| 520 | |a Abstract Heavy metal content analysis of River Torsa in India did not indicate any alarming level of toxicity for human consumption but revealed variation at the ppb level in different months. The variation in recoverable nickel and zinc resistant copiotrophic (or eutrophic) bacterial counts was explained by the variation of the zinc content (34.0–691.3 ppb) of the river water in different sampling months. Growth studies conducted with some purified nickel and/or zinc resistant strains revealed that pre-exposure of the cells to ppb levels of $ Zn^{2+} $, comparable to the indigenous zinc ion concentration of the river, could induce the nickel or zinc resistance. A minimum concentration of 5–10 μM $ Zn^{2+ } $(325–650 ppb) was found effective in inducing the Nickel resistance of the isolates. Zinc resistance of the isolates was tested by pre-exposing the cells to 4 μM $ Zn^{2+ } $(260 ppb). The lag phase was reduced by 6–8 h in all the cases. Biochemical characteristics and phylogenetic analysis based on 16S rDNA sequence indicated that some of the Torsa River isolates, having inducible nickel and zinc resistance, are members of the genus Pseudomonas, Acinetobacter, Bacillus, Enterobacter, Serratia and Moraxella. | ||
| 650 | 4 | |a Inducible metal resistance |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Torsa River |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Ni resistance |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a Zn resistance |7 (dpeaa)DE-He213 | |
| 650 | 4 | |a River water bacteria |7 (dpeaa)DE-He213 | |
| 700 | 1 | |a Nanda, Ashis Kumar |4 aut | |
| 700 | 1 | |a Chakraborty, Ranadhir |4 aut | |
| 773 | 0 | 8 | |i Enthalten in |t Archives of microbiology |d Berlin : Springer, 1930 |g 188(2007), 3 vom: 12. Apr., Seite 215-224 |w (DE-627)253390079 |w (DE-600)1458451-7 |x 1432-072X |7 nnns |
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| 912 | |a GBV_ILN_2064 | ||
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| 912 | |a GBV_ILN_2070 | ||
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| 912 | |a GBV_ILN_2088 | ||
| 912 | |a GBV_ILN_2093 | ||
| 912 | |a GBV_ILN_2106 | ||
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10.1007/s00203-007-0236-7 doi (DE-627)SPR001793160 (SPR)s00203-007-0236-7-e DE-627 ger DE-627 rakwb eng Bhadra, Bhaskar verfasserin aut Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months 2007 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2007 Abstract Heavy metal content analysis of River Torsa in India did not indicate any alarming level of toxicity for human consumption but revealed variation at the ppb level in different months. The variation in recoverable nickel and zinc resistant copiotrophic (or eutrophic) bacterial counts was explained by the variation of the zinc content (34.0–691.3 ppb) of the river water in different sampling months. Growth studies conducted with some purified nickel and/or zinc resistant strains revealed that pre-exposure of the cells to ppb levels of $ Zn^{2+} $, comparable to the indigenous zinc ion concentration of the river, could induce the nickel or zinc resistance. A minimum concentration of 5–10 μM $ Zn^{2+ } $(325–650 ppb) was found effective in inducing the Nickel resistance of the isolates. Zinc resistance of the isolates was tested by pre-exposing the cells to 4 μM $ Zn^{2+ } $(260 ppb). The lag phase was reduced by 6–8 h in all the cases. Biochemical characteristics and phylogenetic analysis based on 16S rDNA sequence indicated that some of the Torsa River isolates, having inducible nickel and zinc resistance, are members of the genus Pseudomonas, Acinetobacter, Bacillus, Enterobacter, Serratia and Moraxella. Inducible metal resistance (dpeaa)DE-He213 Torsa River (dpeaa)DE-He213 Ni resistance (dpeaa)DE-He213 Zn resistance (dpeaa)DE-He213 River water bacteria (dpeaa)DE-He213 Nanda, Ashis Kumar aut Chakraborty, Ranadhir aut Enthalten in Archives of microbiology Berlin : Springer, 1930 188(2007), 3 vom: 12. Apr., Seite 215-224 (DE-627)253390079 (DE-600)1458451-7 1432-072X nnns volume:188 year:2007 number:3 day:12 month:04 pages:215-224 https://dx.doi.org/10.1007/s00203-007-0236-7 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_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_252 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 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_4325 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 188 2007 3 12 04 215-224 |
| spelling |
10.1007/s00203-007-0236-7 doi (DE-627)SPR001793160 (SPR)s00203-007-0236-7-e DE-627 ger DE-627 rakwb eng Bhadra, Bhaskar verfasserin aut Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months 2007 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2007 Abstract Heavy metal content analysis of River Torsa in India did not indicate any alarming level of toxicity for human consumption but revealed variation at the ppb level in different months. The variation in recoverable nickel and zinc resistant copiotrophic (or eutrophic) bacterial counts was explained by the variation of the zinc content (34.0–691.3 ppb) of the river water in different sampling months. Growth studies conducted with some purified nickel and/or zinc resistant strains revealed that pre-exposure of the cells to ppb levels of $ Zn^{2+} $, comparable to the indigenous zinc ion concentration of the river, could induce the nickel or zinc resistance. A minimum concentration of 5–10 μM $ Zn^{2+ } $(325–650 ppb) was found effective in inducing the Nickel resistance of the isolates. Zinc resistance of the isolates was tested by pre-exposing the cells to 4 μM $ Zn^{2+ } $(260 ppb). The lag phase was reduced by 6–8 h in all the cases. Biochemical characteristics and phylogenetic analysis based on 16S rDNA sequence indicated that some of the Torsa River isolates, having inducible nickel and zinc resistance, are members of the genus Pseudomonas, Acinetobacter, Bacillus, Enterobacter, Serratia and Moraxella. Inducible metal resistance (dpeaa)DE-He213 Torsa River (dpeaa)DE-He213 Ni resistance (dpeaa)DE-He213 Zn resistance (dpeaa)DE-He213 River water bacteria (dpeaa)DE-He213 Nanda, Ashis Kumar aut Chakraborty, Ranadhir aut Enthalten in Archives of microbiology Berlin : Springer, 1930 188(2007), 3 vom: 12. Apr., Seite 215-224 (DE-627)253390079 (DE-600)1458451-7 1432-072X nnns volume:188 year:2007 number:3 day:12 month:04 pages:215-224 https://dx.doi.org/10.1007/s00203-007-0236-7 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_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_252 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 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_4325 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 188 2007 3 12 04 215-224 |
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10.1007/s00203-007-0236-7 doi (DE-627)SPR001793160 (SPR)s00203-007-0236-7-e DE-627 ger DE-627 rakwb eng Bhadra, Bhaskar verfasserin aut Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months 2007 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2007 Abstract Heavy metal content analysis of River Torsa in India did not indicate any alarming level of toxicity for human consumption but revealed variation at the ppb level in different months. The variation in recoverable nickel and zinc resistant copiotrophic (or eutrophic) bacterial counts was explained by the variation of the zinc content (34.0–691.3 ppb) of the river water in different sampling months. Growth studies conducted with some purified nickel and/or zinc resistant strains revealed that pre-exposure of the cells to ppb levels of $ Zn^{2+} $, comparable to the indigenous zinc ion concentration of the river, could induce the nickel or zinc resistance. A minimum concentration of 5–10 μM $ Zn^{2+ } $(325–650 ppb) was found effective in inducing the Nickel resistance of the isolates. Zinc resistance of the isolates was tested by pre-exposing the cells to 4 μM $ Zn^{2+ } $(260 ppb). The lag phase was reduced by 6–8 h in all the cases. Biochemical characteristics and phylogenetic analysis based on 16S rDNA sequence indicated that some of the Torsa River isolates, having inducible nickel and zinc resistance, are members of the genus Pseudomonas, Acinetobacter, Bacillus, Enterobacter, Serratia and Moraxella. Inducible metal resistance (dpeaa)DE-He213 Torsa River (dpeaa)DE-He213 Ni resistance (dpeaa)DE-He213 Zn resistance (dpeaa)DE-He213 River water bacteria (dpeaa)DE-He213 Nanda, Ashis Kumar aut Chakraborty, Ranadhir aut Enthalten in Archives of microbiology Berlin : Springer, 1930 188(2007), 3 vom: 12. Apr., Seite 215-224 (DE-627)253390079 (DE-600)1458451-7 1432-072X nnns volume:188 year:2007 number:3 day:12 month:04 pages:215-224 https://dx.doi.org/10.1007/s00203-007-0236-7 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_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_252 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 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_4325 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 188 2007 3 12 04 215-224 |
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10.1007/s00203-007-0236-7 doi (DE-627)SPR001793160 (SPR)s00203-007-0236-7-e DE-627 ger DE-627 rakwb eng Bhadra, Bhaskar verfasserin aut Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months 2007 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2007 Abstract Heavy metal content analysis of River Torsa in India did not indicate any alarming level of toxicity for human consumption but revealed variation at the ppb level in different months. The variation in recoverable nickel and zinc resistant copiotrophic (or eutrophic) bacterial counts was explained by the variation of the zinc content (34.0–691.3 ppb) of the river water in different sampling months. Growth studies conducted with some purified nickel and/or zinc resistant strains revealed that pre-exposure of the cells to ppb levels of $ Zn^{2+} $, comparable to the indigenous zinc ion concentration of the river, could induce the nickel or zinc resistance. A minimum concentration of 5–10 μM $ Zn^{2+ } $(325–650 ppb) was found effective in inducing the Nickel resistance of the isolates. Zinc resistance of the isolates was tested by pre-exposing the cells to 4 μM $ Zn^{2+ } $(260 ppb). The lag phase was reduced by 6–8 h in all the cases. Biochemical characteristics and phylogenetic analysis based on 16S rDNA sequence indicated that some of the Torsa River isolates, having inducible nickel and zinc resistance, are members of the genus Pseudomonas, Acinetobacter, Bacillus, Enterobacter, Serratia and Moraxella. Inducible metal resistance (dpeaa)DE-He213 Torsa River (dpeaa)DE-He213 Ni resistance (dpeaa)DE-He213 Zn resistance (dpeaa)DE-He213 River water bacteria (dpeaa)DE-He213 Nanda, Ashis Kumar aut Chakraborty, Ranadhir aut Enthalten in Archives of microbiology Berlin : Springer, 1930 188(2007), 3 vom: 12. Apr., Seite 215-224 (DE-627)253390079 (DE-600)1458451-7 1432-072X nnns volume:188 year:2007 number:3 day:12 month:04 pages:215-224 https://dx.doi.org/10.1007/s00203-007-0236-7 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_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_252 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 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_4325 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 188 2007 3 12 04 215-224 |
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10.1007/s00203-007-0236-7 doi (DE-627)SPR001793160 (SPR)s00203-007-0236-7-e DE-627 ger DE-627 rakwb eng Bhadra, Bhaskar verfasserin aut Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months 2007 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier © Springer-Verlag 2007 Abstract Heavy metal content analysis of River Torsa in India did not indicate any alarming level of toxicity for human consumption but revealed variation at the ppb level in different months. The variation in recoverable nickel and zinc resistant copiotrophic (or eutrophic) bacterial counts was explained by the variation of the zinc content (34.0–691.3 ppb) of the river water in different sampling months. Growth studies conducted with some purified nickel and/or zinc resistant strains revealed that pre-exposure of the cells to ppb levels of $ Zn^{2+} $, comparable to the indigenous zinc ion concentration of the river, could induce the nickel or zinc resistance. A minimum concentration of 5–10 μM $ Zn^{2+ } $(325–650 ppb) was found effective in inducing the Nickel resistance of the isolates. Zinc resistance of the isolates was tested by pre-exposing the cells to 4 μM $ Zn^{2+ } $(260 ppb). The lag phase was reduced by 6–8 h in all the cases. Biochemical characteristics and phylogenetic analysis based on 16S rDNA sequence indicated that some of the Torsa River isolates, having inducible nickel and zinc resistance, are members of the genus Pseudomonas, Acinetobacter, Bacillus, Enterobacter, Serratia and Moraxella. Inducible metal resistance (dpeaa)DE-He213 Torsa River (dpeaa)DE-He213 Ni resistance (dpeaa)DE-He213 Zn resistance (dpeaa)DE-He213 River water bacteria (dpeaa)DE-He213 Nanda, Ashis Kumar aut Chakraborty, Ranadhir aut Enthalten in Archives of microbiology Berlin : Springer, 1930 188(2007), 3 vom: 12. Apr., Seite 215-224 (DE-627)253390079 (DE-600)1458451-7 1432-072X nnns volume:188 year:2007 number:3 day:12 month:04 pages:215-224 https://dx.doi.org/10.1007/s00203-007-0236-7 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_170 GBV_ILN_171 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_252 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_2057 GBV_ILN_2059 GBV_ILN_2061 GBV_ILN_2064 GBV_ILN_2065 GBV_ILN_2068 GBV_ILN_2070 GBV_ILN_2086 GBV_ILN_2088 GBV_ILN_2093 GBV_ILN_2106 GBV_ILN_2107 GBV_ILN_2108 GBV_ILN_2110 GBV_ILN_2111 GBV_ILN_2112 GBV_ILN_2113 GBV_ILN_2116 GBV_ILN_2118 GBV_ILN_2119 GBV_ILN_2122 GBV_ILN_2129 GBV_ILN_2143 GBV_ILN_2144 GBV_ILN_2147 GBV_ILN_2148 GBV_ILN_2152 GBV_ILN_2153 GBV_ILN_2188 GBV_ILN_2190 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_4325 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 188 2007 3 12 04 215-224 |
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Enthalten in Archives of microbiology 188(2007), 3 vom: 12. Apr., Seite 215-224 volume:188 year:2007 number:3 day:12 month:04 pages:215-224 |
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Enthalten in Archives of microbiology 188(2007), 3 vom: 12. Apr., Seite 215-224 volume:188 year:2007 number:3 day:12 month:04 pages:215-224 |
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Bhadra, Bhaskar @@aut@@ Nanda, Ashis Kumar @@aut@@ Chakraborty, Ranadhir @@aut@@ |
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<?xml version="1.0" encoding="UTF-8"?><collection xmlns="http://www.loc.gov/MARC21/slim"><record><leader>01000caa a22002652 4500</leader><controlfield tag="001">SPR001793160</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20230519130815.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">201001s2007 xx |||||o 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1007/s00203-007-0236-7</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)SPR001793160</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(SPR)s00203-007-0236-7-e</subfield></datafield><datafield tag="040" ind1=" " ind2=" "><subfield code="a">DE-627</subfield><subfield code="b">ger</subfield><subfield code="c">DE-627</subfield><subfield code="e">rakwb</subfield></datafield><datafield tag="041" ind1=" " ind2=" "><subfield code="a">eng</subfield></datafield><datafield tag="100" ind1="1" ind2=" "><subfield code="a">Bhadra, Bhaskar</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2007</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 2007</subfield></datafield><datafield tag="520" ind1=" " ind2=" "><subfield code="a">Abstract Heavy metal content analysis of River Torsa in India did not indicate any alarming level of toxicity for human consumption but revealed variation at the ppb level in different months. The variation in recoverable nickel and zinc resistant copiotrophic (or eutrophic) bacterial counts was explained by the variation of the zinc content (34.0–691.3 ppb) of the river water in different sampling months. Growth studies conducted with some purified nickel and/or zinc resistant strains revealed that pre-exposure of the cells to ppb levels of $ Zn^{2+} $, comparable to the indigenous zinc ion concentration of the river, could induce the nickel or zinc resistance. A minimum concentration of 5–10 μM $ Zn^{2+ } $(325–650 ppb) was found effective in inducing the Nickel resistance of the isolates. Zinc resistance of the isolates was tested by pre-exposing the cells to 4 μM $ Zn^{2+ } $(260 ppb). The lag phase was reduced by 6–8 h in all the cases. Biochemical characteristics and phylogenetic analysis based on 16S rDNA sequence indicated that some of the Torsa River isolates, having inducible nickel and zinc resistance, are members of the genus Pseudomonas, Acinetobacter, Bacillus, Enterobacter, Serratia and Moraxella.</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Inducible metal resistance</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Torsa River</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Ni resistance</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">Zn resistance</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="650" ind1=" " ind2="4"><subfield code="a">River water bacteria</subfield><subfield code="7">(dpeaa)DE-He213</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Nanda, Ashis Kumar</subfield><subfield code="4">aut</subfield></datafield><datafield tag="700" ind1="1" ind2=" "><subfield code="a">Chakraborty, Ranadhir</subfield><subfield code="4">aut</subfield></datafield><datafield tag="773" ind1="0" ind2="8"><subfield code="i">Enthalten in</subfield><subfield code="t">Archives of microbiology</subfield><subfield code="d">Berlin : Springer, 1930</subfield><subfield code="g">188(2007), 3 vom: 12. 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| author |
Bhadra, Bhaskar |
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Bhadra, Bhaskar misc Inducible metal resistance misc Torsa River misc Ni resistance misc Zn resistance misc River water bacteria Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months |
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Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months Inducible metal resistance (dpeaa)DE-He213 Torsa River (dpeaa)DE-He213 Ni resistance (dpeaa)DE-He213 Zn resistance (dpeaa)DE-He213 River water bacteria (dpeaa)DE-He213 |
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Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months |
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Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months |
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Bhadra, Bhaskar Nanda, Ashis Kumar Chakraborty, Ranadhir |
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fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of torsa river in different months |
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Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months |
| abstract |
Abstract Heavy metal content analysis of River Torsa in India did not indicate any alarming level of toxicity for human consumption but revealed variation at the ppb level in different months. The variation in recoverable nickel and zinc resistant copiotrophic (or eutrophic) bacterial counts was explained by the variation of the zinc content (34.0–691.3 ppb) of the river water in different sampling months. Growth studies conducted with some purified nickel and/or zinc resistant strains revealed that pre-exposure of the cells to ppb levels of $ Zn^{2+} $, comparable to the indigenous zinc ion concentration of the river, could induce the nickel or zinc resistance. A minimum concentration of 5–10 μM $ Zn^{2+ } $(325–650 ppb) was found effective in inducing the Nickel resistance of the isolates. Zinc resistance of the isolates was tested by pre-exposing the cells to 4 μM $ Zn^{2+ } $(260 ppb). The lag phase was reduced by 6–8 h in all the cases. Biochemical characteristics and phylogenetic analysis based on 16S rDNA sequence indicated that some of the Torsa River isolates, having inducible nickel and zinc resistance, are members of the genus Pseudomonas, Acinetobacter, Bacillus, Enterobacter, Serratia and Moraxella. © Springer-Verlag 2007 |
| abstractGer |
Abstract Heavy metal content analysis of River Torsa in India did not indicate any alarming level of toxicity for human consumption but revealed variation at the ppb level in different months. The variation in recoverable nickel and zinc resistant copiotrophic (or eutrophic) bacterial counts was explained by the variation of the zinc content (34.0–691.3 ppb) of the river water in different sampling months. Growth studies conducted with some purified nickel and/or zinc resistant strains revealed that pre-exposure of the cells to ppb levels of $ Zn^{2+} $, comparable to the indigenous zinc ion concentration of the river, could induce the nickel or zinc resistance. A minimum concentration of 5–10 μM $ Zn^{2+ } $(325–650 ppb) was found effective in inducing the Nickel resistance of the isolates. Zinc resistance of the isolates was tested by pre-exposing the cells to 4 μM $ Zn^{2+ } $(260 ppb). The lag phase was reduced by 6–8 h in all the cases. Biochemical characteristics and phylogenetic analysis based on 16S rDNA sequence indicated that some of the Torsa River isolates, having inducible nickel and zinc resistance, are members of the genus Pseudomonas, Acinetobacter, Bacillus, Enterobacter, Serratia and Moraxella. © Springer-Verlag 2007 |
| abstract_unstemmed |
Abstract Heavy metal content analysis of River Torsa in India did not indicate any alarming level of toxicity for human consumption but revealed variation at the ppb level in different months. The variation in recoverable nickel and zinc resistant copiotrophic (or eutrophic) bacterial counts was explained by the variation of the zinc content (34.0–691.3 ppb) of the river water in different sampling months. Growth studies conducted with some purified nickel and/or zinc resistant strains revealed that pre-exposure of the cells to ppb levels of $ Zn^{2+} $, comparable to the indigenous zinc ion concentration of the river, could induce the nickel or zinc resistance. A minimum concentration of 5–10 μM $ Zn^{2+ } $(325–650 ppb) was found effective in inducing the Nickel resistance of the isolates. Zinc resistance of the isolates was tested by pre-exposing the cells to 4 μM $ Zn^{2+ } $(260 ppb). The lag phase was reduced by 6–8 h in all the cases. Biochemical characteristics and phylogenetic analysis based on 16S rDNA sequence indicated that some of the Torsa River isolates, having inducible nickel and zinc resistance, are members of the genus Pseudomonas, Acinetobacter, Bacillus, Enterobacter, Serratia and Moraxella. © Springer-Verlag 2007 |
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3 |
| title_short |
Fluctuation in recoverable nickel and zinc resistant copiotrophic bacteria explained by the varying zinc ion content of Torsa River in different months |
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https://dx.doi.org/10.1007/s00203-007-0236-7 |
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Nanda, Ashis Kumar Chakraborty, Ranadhir |
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10.1007/s00203-007-0236-7 |
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2024-07-04T00:25:54.651Z |
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| score |
7.39979 |