Effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment
Purpose The aim of this study was to evaluate polychlorinated biphenyl (PCB) removal in relation to the associated bacterial community composition in Ohio River sediments (USA) using field and laboratory approaches. Materials and methods PCB removal was studied in different sediment layers applying...
Ausführliche Beschreibung
Autor*in: |
D’Angelo, Elisa [verfasserIn] Nunez, Andres [verfasserIn] |
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Format: |
E-Artikel |
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Sprache: |
Englisch |
Erschienen: |
2010 |
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Schlagwörter: |
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Übergeordnetes Werk: |
Enthalten in: Journal of soils and sediments - Berlin : Springer, 2001, 10(2010), 6 vom: 21. Apr., Seite 1186-1199 |
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Übergeordnetes Werk: |
volume:10 ; year:2010 ; number:6 ; day:21 ; month:04 ; pages:1186-1199 |
Links: |
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DOI / URN: |
10.1007/s11368-010-0218-2 |
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Katalog-ID: |
SPR018948529 |
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520 | |a Purpose The aim of this study was to evaluate polychlorinated biphenyl (PCB) removal in relation to the associated bacterial community composition in Ohio River sediments (USA) using field and laboratory approaches. Materials and methods PCB removal was studied in different sediment layers applying dialysis equilibrators in the field for 4 months. In parallel, dissolved chemical constituents and bacterial community composition using the 16S rDNA cloning–sequencing approach were determined within the appropriate sediment layers. The effects of several bioremediation treatments on PCB removal and bacterial community composition were evaluated in laboratory experiments. Sediments spiked with 245-2’4’5’ hexachlorobiphenyl were incubated under different conditions for up to 250 days, including alternating anaerobic–aerobic conditions, amendments with electron donors, $ FeSO_{4} $, and incubations at different temperatures (10°C, 25°C, 40°C). Results and discussion PCB levels remained stable in the sediment layers under field conditions. Surface sediments (0–26 cm) had elevated levels of nitrate+nitrite and sulfate, while subsurface sediments (27–35 cm) were characterized by high concentrations of ammonium, methane, and dissolved organic carbon. Oxic/anoxic conditions were also reflected in the bacterial community, with aerobic bacteria in the Bulkholderiales order enriched in the surface sediments, and anaerobic bacteria in the Clostridiales, Syntrophobacteriales, and Desulfobacterales orders more prevalent in the subsurface sediments. Although the chemical status was favorable and the potential degraders were present, PCB transformation did not take place under the prevailing environmental conditions. Under laboratory conditions, PCB transformation was positively influenced by lowered redox conditions with or without amendments with $ FeSO_{4} $, electron donors, or alternating anaerobic–aerobic conditions. The main PCB transformation process in all anaerobic treatments at 25°C was reductive dechlorination of 245-2’4’5’ hexachlorobiphenyl to 24-2’4’5’ pentachlorobiphenyl and 24-2’4’ tetrachlorobiphenyl, which occurred at rates between 60–85% in 177 days. Exposing sediments to air for an additional period of 100 days in the sequential anaerobic–aerobic treatment did not result in additional mineralization of PCBs. Temperature, electron donors, and redox conditions significantly affected the abundance of bacteria in the Bacteroidales, Hydrogenophilales, Pseudomonales, Myxococcales, Syntrophobacterales, Acidobacterales, Caldilineales, and Clostridiales orders. The PCB dechlorinator Dehalococcoides and other dechlorinating bacteria were detected in anaerobic sediments, including Desulfitobacterium, Desulfuromonas, Anaeromyxobacter, Geobacter, and Desulfomonile. The data suggested that shifts in the bacterial communities due to abiotic conditions affected PCB transformation, either directly (degraders) or indirectly (bacterial syntrophic associations with degraders). Conclusions The data indicated that elevated redox status and low temperature conditions accounted for stable PCB concentrations under field conditions in Ohio River sediments. In laboratory experiments, PCB removal increased under anaerobic conditions at 25°C, but was not affected by other varying conditions. Depending on the environmental conditions, several bacterial groups involved in the stepwise degradation of natural organic matter to dechlorinating substrates acetate and hydrogen were prevalent in sediments, including Clostridiales, Caldilineales, Syntrophobacterales, Bacteroidales, and Acidobacteriales. Measurements of the prevailing bacterial community composition and chemical–physical properties important for PCB degradation could be valuable prior to developing PCB bioremediation strategies in sediments. | ||
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10.1007/s11368-010-0218-2 doi (DE-627)SPR018948529 (SPR)s11368-010-0218-2-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl D’Angelo, Elisa verfasserin aut Effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment 2010 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The aim of this study was to evaluate polychlorinated biphenyl (PCB) removal in relation to the associated bacterial community composition in Ohio River sediments (USA) using field and laboratory approaches. Materials and methods PCB removal was studied in different sediment layers applying dialysis equilibrators in the field for 4 months. In parallel, dissolved chemical constituents and bacterial community composition using the 16S rDNA cloning–sequencing approach were determined within the appropriate sediment layers. The effects of several bioremediation treatments on PCB removal and bacterial community composition were evaluated in laboratory experiments. Sediments spiked with 245-2’4’5’ hexachlorobiphenyl were incubated under different conditions for up to 250 days, including alternating anaerobic–aerobic conditions, amendments with electron donors, $ FeSO_{4} $, and incubations at different temperatures (10°C, 25°C, 40°C). Results and discussion PCB levels remained stable in the sediment layers under field conditions. Surface sediments (0–26 cm) had elevated levels of nitrate+nitrite and sulfate, while subsurface sediments (27–35 cm) were characterized by high concentrations of ammonium, methane, and dissolved organic carbon. Oxic/anoxic conditions were also reflected in the bacterial community, with aerobic bacteria in the Bulkholderiales order enriched in the surface sediments, and anaerobic bacteria in the Clostridiales, Syntrophobacteriales, and Desulfobacterales orders more prevalent in the subsurface sediments. Although the chemical status was favorable and the potential degraders were present, PCB transformation did not take place under the prevailing environmental conditions. Under laboratory conditions, PCB transformation was positively influenced by lowered redox conditions with or without amendments with $ FeSO_{4} $, electron donors, or alternating anaerobic–aerobic conditions. The main PCB transformation process in all anaerobic treatments at 25°C was reductive dechlorination of 245-2’4’5’ hexachlorobiphenyl to 24-2’4’5’ pentachlorobiphenyl and 24-2’4’ tetrachlorobiphenyl, which occurred at rates between 60–85% in 177 days. Exposing sediments to air for an additional period of 100 days in the sequential anaerobic–aerobic treatment did not result in additional mineralization of PCBs. Temperature, electron donors, and redox conditions significantly affected the abundance of bacteria in the Bacteroidales, Hydrogenophilales, Pseudomonales, Myxococcales, Syntrophobacterales, Acidobacterales, Caldilineales, and Clostridiales orders. The PCB dechlorinator Dehalococcoides and other dechlorinating bacteria were detected in anaerobic sediments, including Desulfitobacterium, Desulfuromonas, Anaeromyxobacter, Geobacter, and Desulfomonile. The data suggested that shifts in the bacterial communities due to abiotic conditions affected PCB transformation, either directly (degraders) or indirectly (bacterial syntrophic associations with degraders). Conclusions The data indicated that elevated redox status and low temperature conditions accounted for stable PCB concentrations under field conditions in Ohio River sediments. In laboratory experiments, PCB removal increased under anaerobic conditions at 25°C, but was not affected by other varying conditions. Depending on the environmental conditions, several bacterial groups involved in the stepwise degradation of natural organic matter to dechlorinating substrates acetate and hydrogen were prevalent in sediments, including Clostridiales, Caldilineales, Syntrophobacterales, Bacteroidales, and Acidobacteriales. Measurements of the prevailing bacterial community composition and chemical–physical properties important for PCB degradation could be valuable prior to developing PCB bioremediation strategies in sediments. 16S rRNA (dpeaa)DE-He213 Bioindicators (dpeaa)DE-He213 Reductive dechlorination (dpeaa)DE-He213 Syntrophic associations (dpeaa)DE-He213 Nunez, Andres verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 10(2010), 6 vom: 21. Apr., Seite 1186-1199 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:10 year:2010 number:6 day:21 month:04 pages:1186-1199 https://dx.doi.org/10.1007/s11368-010-0218-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 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_183 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 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_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 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 58.52 ASE AR 10 2010 6 21 04 1186-1199 |
spelling |
10.1007/s11368-010-0218-2 doi (DE-627)SPR018948529 (SPR)s11368-010-0218-2-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl D’Angelo, Elisa verfasserin aut Effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment 2010 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The aim of this study was to evaluate polychlorinated biphenyl (PCB) removal in relation to the associated bacterial community composition in Ohio River sediments (USA) using field and laboratory approaches. Materials and methods PCB removal was studied in different sediment layers applying dialysis equilibrators in the field for 4 months. In parallel, dissolved chemical constituents and bacterial community composition using the 16S rDNA cloning–sequencing approach were determined within the appropriate sediment layers. The effects of several bioremediation treatments on PCB removal and bacterial community composition were evaluated in laboratory experiments. Sediments spiked with 245-2’4’5’ hexachlorobiphenyl were incubated under different conditions for up to 250 days, including alternating anaerobic–aerobic conditions, amendments with electron donors, $ FeSO_{4} $, and incubations at different temperatures (10°C, 25°C, 40°C). Results and discussion PCB levels remained stable in the sediment layers under field conditions. Surface sediments (0–26 cm) had elevated levels of nitrate+nitrite and sulfate, while subsurface sediments (27–35 cm) were characterized by high concentrations of ammonium, methane, and dissolved organic carbon. Oxic/anoxic conditions were also reflected in the bacterial community, with aerobic bacteria in the Bulkholderiales order enriched in the surface sediments, and anaerobic bacteria in the Clostridiales, Syntrophobacteriales, and Desulfobacterales orders more prevalent in the subsurface sediments. Although the chemical status was favorable and the potential degraders were present, PCB transformation did not take place under the prevailing environmental conditions. Under laboratory conditions, PCB transformation was positively influenced by lowered redox conditions with or without amendments with $ FeSO_{4} $, electron donors, or alternating anaerobic–aerobic conditions. The main PCB transformation process in all anaerobic treatments at 25°C was reductive dechlorination of 245-2’4’5’ hexachlorobiphenyl to 24-2’4’5’ pentachlorobiphenyl and 24-2’4’ tetrachlorobiphenyl, which occurred at rates between 60–85% in 177 days. Exposing sediments to air for an additional period of 100 days in the sequential anaerobic–aerobic treatment did not result in additional mineralization of PCBs. Temperature, electron donors, and redox conditions significantly affected the abundance of bacteria in the Bacteroidales, Hydrogenophilales, Pseudomonales, Myxococcales, Syntrophobacterales, Acidobacterales, Caldilineales, and Clostridiales orders. The PCB dechlorinator Dehalococcoides and other dechlorinating bacteria were detected in anaerobic sediments, including Desulfitobacterium, Desulfuromonas, Anaeromyxobacter, Geobacter, and Desulfomonile. The data suggested that shifts in the bacterial communities due to abiotic conditions affected PCB transformation, either directly (degraders) or indirectly (bacterial syntrophic associations with degraders). Conclusions The data indicated that elevated redox status and low temperature conditions accounted for stable PCB concentrations under field conditions in Ohio River sediments. In laboratory experiments, PCB removal increased under anaerobic conditions at 25°C, but was not affected by other varying conditions. Depending on the environmental conditions, several bacterial groups involved in the stepwise degradation of natural organic matter to dechlorinating substrates acetate and hydrogen were prevalent in sediments, including Clostridiales, Caldilineales, Syntrophobacterales, Bacteroidales, and Acidobacteriales. Measurements of the prevailing bacterial community composition and chemical–physical properties important for PCB degradation could be valuable prior to developing PCB bioremediation strategies in sediments. 16S rRNA (dpeaa)DE-He213 Bioindicators (dpeaa)DE-He213 Reductive dechlorination (dpeaa)DE-He213 Syntrophic associations (dpeaa)DE-He213 Nunez, Andres verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 10(2010), 6 vom: 21. Apr., Seite 1186-1199 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:10 year:2010 number:6 day:21 month:04 pages:1186-1199 https://dx.doi.org/10.1007/s11368-010-0218-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 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_183 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 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_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 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 58.52 ASE AR 10 2010 6 21 04 1186-1199 |
allfields_unstemmed |
10.1007/s11368-010-0218-2 doi (DE-627)SPR018948529 (SPR)s11368-010-0218-2-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl D’Angelo, Elisa verfasserin aut Effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment 2010 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The aim of this study was to evaluate polychlorinated biphenyl (PCB) removal in relation to the associated bacterial community composition in Ohio River sediments (USA) using field and laboratory approaches. Materials and methods PCB removal was studied in different sediment layers applying dialysis equilibrators in the field for 4 months. In parallel, dissolved chemical constituents and bacterial community composition using the 16S rDNA cloning–sequencing approach were determined within the appropriate sediment layers. The effects of several bioremediation treatments on PCB removal and bacterial community composition were evaluated in laboratory experiments. Sediments spiked with 245-2’4’5’ hexachlorobiphenyl were incubated under different conditions for up to 250 days, including alternating anaerobic–aerobic conditions, amendments with electron donors, $ FeSO_{4} $, and incubations at different temperatures (10°C, 25°C, 40°C). Results and discussion PCB levels remained stable in the sediment layers under field conditions. Surface sediments (0–26 cm) had elevated levels of nitrate+nitrite and sulfate, while subsurface sediments (27–35 cm) were characterized by high concentrations of ammonium, methane, and dissolved organic carbon. Oxic/anoxic conditions were also reflected in the bacterial community, with aerobic bacteria in the Bulkholderiales order enriched in the surface sediments, and anaerobic bacteria in the Clostridiales, Syntrophobacteriales, and Desulfobacterales orders more prevalent in the subsurface sediments. Although the chemical status was favorable and the potential degraders were present, PCB transformation did not take place under the prevailing environmental conditions. Under laboratory conditions, PCB transformation was positively influenced by lowered redox conditions with or without amendments with $ FeSO_{4} $, electron donors, or alternating anaerobic–aerobic conditions. The main PCB transformation process in all anaerobic treatments at 25°C was reductive dechlorination of 245-2’4’5’ hexachlorobiphenyl to 24-2’4’5’ pentachlorobiphenyl and 24-2’4’ tetrachlorobiphenyl, which occurred at rates between 60–85% in 177 days. Exposing sediments to air for an additional period of 100 days in the sequential anaerobic–aerobic treatment did not result in additional mineralization of PCBs. Temperature, electron donors, and redox conditions significantly affected the abundance of bacteria in the Bacteroidales, Hydrogenophilales, Pseudomonales, Myxococcales, Syntrophobacterales, Acidobacterales, Caldilineales, and Clostridiales orders. The PCB dechlorinator Dehalococcoides and other dechlorinating bacteria were detected in anaerobic sediments, including Desulfitobacterium, Desulfuromonas, Anaeromyxobacter, Geobacter, and Desulfomonile. The data suggested that shifts in the bacterial communities due to abiotic conditions affected PCB transformation, either directly (degraders) or indirectly (bacterial syntrophic associations with degraders). Conclusions The data indicated that elevated redox status and low temperature conditions accounted for stable PCB concentrations under field conditions in Ohio River sediments. In laboratory experiments, PCB removal increased under anaerobic conditions at 25°C, but was not affected by other varying conditions. Depending on the environmental conditions, several bacterial groups involved in the stepwise degradation of natural organic matter to dechlorinating substrates acetate and hydrogen were prevalent in sediments, including Clostridiales, Caldilineales, Syntrophobacterales, Bacteroidales, and Acidobacteriales. Measurements of the prevailing bacterial community composition and chemical–physical properties important for PCB degradation could be valuable prior to developing PCB bioremediation strategies in sediments. 16S rRNA (dpeaa)DE-He213 Bioindicators (dpeaa)DE-He213 Reductive dechlorination (dpeaa)DE-He213 Syntrophic associations (dpeaa)DE-He213 Nunez, Andres verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 10(2010), 6 vom: 21. Apr., Seite 1186-1199 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:10 year:2010 number:6 day:21 month:04 pages:1186-1199 https://dx.doi.org/10.1007/s11368-010-0218-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 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_183 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 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_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 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 58.52 ASE AR 10 2010 6 21 04 1186-1199 |
allfieldsGer |
10.1007/s11368-010-0218-2 doi (DE-627)SPR018948529 (SPR)s11368-010-0218-2-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl D’Angelo, Elisa verfasserin aut Effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment 2010 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The aim of this study was to evaluate polychlorinated biphenyl (PCB) removal in relation to the associated bacterial community composition in Ohio River sediments (USA) using field and laboratory approaches. Materials and methods PCB removal was studied in different sediment layers applying dialysis equilibrators in the field for 4 months. In parallel, dissolved chemical constituents and bacterial community composition using the 16S rDNA cloning–sequencing approach were determined within the appropriate sediment layers. The effects of several bioremediation treatments on PCB removal and bacterial community composition were evaluated in laboratory experiments. Sediments spiked with 245-2’4’5’ hexachlorobiphenyl were incubated under different conditions for up to 250 days, including alternating anaerobic–aerobic conditions, amendments with electron donors, $ FeSO_{4} $, and incubations at different temperatures (10°C, 25°C, 40°C). Results and discussion PCB levels remained stable in the sediment layers under field conditions. Surface sediments (0–26 cm) had elevated levels of nitrate+nitrite and sulfate, while subsurface sediments (27–35 cm) were characterized by high concentrations of ammonium, methane, and dissolved organic carbon. Oxic/anoxic conditions were also reflected in the bacterial community, with aerobic bacteria in the Bulkholderiales order enriched in the surface sediments, and anaerobic bacteria in the Clostridiales, Syntrophobacteriales, and Desulfobacterales orders more prevalent in the subsurface sediments. Although the chemical status was favorable and the potential degraders were present, PCB transformation did not take place under the prevailing environmental conditions. Under laboratory conditions, PCB transformation was positively influenced by lowered redox conditions with or without amendments with $ FeSO_{4} $, electron donors, or alternating anaerobic–aerobic conditions. The main PCB transformation process in all anaerobic treatments at 25°C was reductive dechlorination of 245-2’4’5’ hexachlorobiphenyl to 24-2’4’5’ pentachlorobiphenyl and 24-2’4’ tetrachlorobiphenyl, which occurred at rates between 60–85% in 177 days. Exposing sediments to air for an additional period of 100 days in the sequential anaerobic–aerobic treatment did not result in additional mineralization of PCBs. Temperature, electron donors, and redox conditions significantly affected the abundance of bacteria in the Bacteroidales, Hydrogenophilales, Pseudomonales, Myxococcales, Syntrophobacterales, Acidobacterales, Caldilineales, and Clostridiales orders. The PCB dechlorinator Dehalococcoides and other dechlorinating bacteria were detected in anaerobic sediments, including Desulfitobacterium, Desulfuromonas, Anaeromyxobacter, Geobacter, and Desulfomonile. The data suggested that shifts in the bacterial communities due to abiotic conditions affected PCB transformation, either directly (degraders) or indirectly (bacterial syntrophic associations with degraders). Conclusions The data indicated that elevated redox status and low temperature conditions accounted for stable PCB concentrations under field conditions in Ohio River sediments. In laboratory experiments, PCB removal increased under anaerobic conditions at 25°C, but was not affected by other varying conditions. Depending on the environmental conditions, several bacterial groups involved in the stepwise degradation of natural organic matter to dechlorinating substrates acetate and hydrogen were prevalent in sediments, including Clostridiales, Caldilineales, Syntrophobacterales, Bacteroidales, and Acidobacteriales. Measurements of the prevailing bacterial community composition and chemical–physical properties important for PCB degradation could be valuable prior to developing PCB bioremediation strategies in sediments. 16S rRNA (dpeaa)DE-He213 Bioindicators (dpeaa)DE-He213 Reductive dechlorination (dpeaa)DE-He213 Syntrophic associations (dpeaa)DE-He213 Nunez, Andres verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 10(2010), 6 vom: 21. Apr., Seite 1186-1199 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:10 year:2010 number:6 day:21 month:04 pages:1186-1199 https://dx.doi.org/10.1007/s11368-010-0218-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 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_183 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 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_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 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 58.52 ASE AR 10 2010 6 21 04 1186-1199 |
allfieldsSound |
10.1007/s11368-010-0218-2 doi (DE-627)SPR018948529 (SPR)s11368-010-0218-2-e DE-627 ger DE-627 rakwb eng 550 ASE 58.52 bkl D’Angelo, Elisa verfasserin aut Effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment 2010 Text txt rdacontent Computermedien c rdamedia Online-Ressource cr rdacarrier Purpose The aim of this study was to evaluate polychlorinated biphenyl (PCB) removal in relation to the associated bacterial community composition in Ohio River sediments (USA) using field and laboratory approaches. Materials and methods PCB removal was studied in different sediment layers applying dialysis equilibrators in the field for 4 months. In parallel, dissolved chemical constituents and bacterial community composition using the 16S rDNA cloning–sequencing approach were determined within the appropriate sediment layers. The effects of several bioremediation treatments on PCB removal and bacterial community composition were evaluated in laboratory experiments. Sediments spiked with 245-2’4’5’ hexachlorobiphenyl were incubated under different conditions for up to 250 days, including alternating anaerobic–aerobic conditions, amendments with electron donors, $ FeSO_{4} $, and incubations at different temperatures (10°C, 25°C, 40°C). Results and discussion PCB levels remained stable in the sediment layers under field conditions. Surface sediments (0–26 cm) had elevated levels of nitrate+nitrite and sulfate, while subsurface sediments (27–35 cm) were characterized by high concentrations of ammonium, methane, and dissolved organic carbon. Oxic/anoxic conditions were also reflected in the bacterial community, with aerobic bacteria in the Bulkholderiales order enriched in the surface sediments, and anaerobic bacteria in the Clostridiales, Syntrophobacteriales, and Desulfobacterales orders more prevalent in the subsurface sediments. Although the chemical status was favorable and the potential degraders were present, PCB transformation did not take place under the prevailing environmental conditions. Under laboratory conditions, PCB transformation was positively influenced by lowered redox conditions with or without amendments with $ FeSO_{4} $, electron donors, or alternating anaerobic–aerobic conditions. The main PCB transformation process in all anaerobic treatments at 25°C was reductive dechlorination of 245-2’4’5’ hexachlorobiphenyl to 24-2’4’5’ pentachlorobiphenyl and 24-2’4’ tetrachlorobiphenyl, which occurred at rates between 60–85% in 177 days. Exposing sediments to air for an additional period of 100 days in the sequential anaerobic–aerobic treatment did not result in additional mineralization of PCBs. Temperature, electron donors, and redox conditions significantly affected the abundance of bacteria in the Bacteroidales, Hydrogenophilales, Pseudomonales, Myxococcales, Syntrophobacterales, Acidobacterales, Caldilineales, and Clostridiales orders. The PCB dechlorinator Dehalococcoides and other dechlorinating bacteria were detected in anaerobic sediments, including Desulfitobacterium, Desulfuromonas, Anaeromyxobacter, Geobacter, and Desulfomonile. The data suggested that shifts in the bacterial communities due to abiotic conditions affected PCB transformation, either directly (degraders) or indirectly (bacterial syntrophic associations with degraders). Conclusions The data indicated that elevated redox status and low temperature conditions accounted for stable PCB concentrations under field conditions in Ohio River sediments. In laboratory experiments, PCB removal increased under anaerobic conditions at 25°C, but was not affected by other varying conditions. Depending on the environmental conditions, several bacterial groups involved in the stepwise degradation of natural organic matter to dechlorinating substrates acetate and hydrogen were prevalent in sediments, including Clostridiales, Caldilineales, Syntrophobacterales, Bacteroidales, and Acidobacteriales. Measurements of the prevailing bacterial community composition and chemical–physical properties important for PCB degradation could be valuable prior to developing PCB bioremediation strategies in sediments. 16S rRNA (dpeaa)DE-He213 Bioindicators (dpeaa)DE-He213 Reductive dechlorination (dpeaa)DE-He213 Syntrophic associations (dpeaa)DE-He213 Nunez, Andres verfasserin aut Enthalten in Journal of soils and sediments Berlin : Springer, 2001 10(2010), 6 vom: 21. Apr., Seite 1186-1199 (DE-627)373325134 (DE-600)2125896-X 1614-7480 nnns volume:10 year:2010 number:6 day:21 month:04 pages:1186-1199 https://dx.doi.org/10.1007/s11368-010-0218-2 lizenzpflichtig Volltext GBV_USEFLAG_A SYSFLAG_A GBV_SPRINGER SSG-OPC-GGO SSG-OPC-ASE 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_65 GBV_ILN_69 GBV_ILN_70 GBV_ILN_73 GBV_ILN_74 GBV_ILN_90 GBV_ILN_95 GBV_ILN_100 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_183 GBV_ILN_187 GBV_ILN_213 GBV_ILN_224 GBV_ILN_230 GBV_ILN_250 GBV_ILN_281 GBV_ILN_285 GBV_ILN_293 GBV_ILN_370 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_2360 GBV_ILN_2446 GBV_ILN_2470 GBV_ILN_2472 GBV_ILN_2507 GBV_ILN_2522 GBV_ILN_2548 GBV_ILN_4035 GBV_ILN_4037 GBV_ILN_4046 GBV_ILN_4112 GBV_ILN_4125 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 58.52 ASE AR 10 2010 6 21 04 1186-1199 |
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Enthalten in Journal of soils and sediments 10(2010), 6 vom: 21. Apr., Seite 1186-1199 volume:10 year:2010 number:6 day:21 month:04 pages:1186-1199 |
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16S rRNA Bioindicators Reductive dechlorination Syntrophic associations |
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Journal of soils and sediments |
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D’Angelo, Elisa @@aut@@ Nunez, Andres @@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">SPR018948529</controlfield><controlfield tag="003">DE-627</controlfield><controlfield tag="005">20220111064041.0</controlfield><controlfield tag="007">cr uuu---uuuuu</controlfield><controlfield tag="008">201006s2010 xx |||||o 00| ||eng c</controlfield><datafield tag="024" ind1="7" ind2=" "><subfield code="a">10.1007/s11368-010-0218-2</subfield><subfield code="2">doi</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(DE-627)SPR018948529</subfield></datafield><datafield tag="035" ind1=" " ind2=" "><subfield code="a">(SPR)s11368-010-0218-2-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="082" ind1="0" ind2="4"><subfield code="a">550</subfield><subfield code="q">ASE</subfield></datafield><datafield tag="084" ind1=" " ind2=" "><subfield code="a">58.52</subfield><subfield code="2">bkl</subfield></datafield><datafield tag="100" ind1="1" ind2=" "><subfield code="a">D’Angelo, Elisa</subfield><subfield code="e">verfasserin</subfield><subfield code="4">aut</subfield></datafield><datafield tag="245" ind1="1" ind2="0"><subfield code="a">Effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment</subfield></datafield><datafield tag="264" ind1=" " ind2="1"><subfield code="c">2010</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="520" ind1=" " ind2=" "><subfield code="a">Purpose The aim of this study was to evaluate polychlorinated biphenyl (PCB) removal in relation to the associated bacterial community composition in Ohio River sediments (USA) using field and laboratory approaches. Materials and methods PCB removal was studied in different sediment layers applying dialysis equilibrators in the field for 4 months. In parallel, dissolved chemical constituents and bacterial community composition using the 16S rDNA cloning–sequencing approach were determined within the appropriate sediment layers. The effects of several bioremediation treatments on PCB removal and bacterial community composition were evaluated in laboratory experiments. Sediments spiked with 245-2’4’5’ hexachlorobiphenyl were incubated under different conditions for up to 250 days, including alternating anaerobic–aerobic conditions, amendments with electron donors, $ FeSO_{4} $, and incubations at different temperatures (10°C, 25°C, 40°C). Results and discussion PCB levels remained stable in the sediment layers under field conditions. Surface sediments (0–26 cm) had elevated levels of nitrate+nitrite and sulfate, while subsurface sediments (27–35 cm) were characterized by high concentrations of ammonium, methane, and dissolved organic carbon. Oxic/anoxic conditions were also reflected in the bacterial community, with aerobic bacteria in the Bulkholderiales order enriched in the surface sediments, and anaerobic bacteria in the Clostridiales, Syntrophobacteriales, and Desulfobacterales orders more prevalent in the subsurface sediments. Although the chemical status was favorable and the potential degraders were present, PCB transformation did not take place under the prevailing environmental conditions. Under laboratory conditions, PCB transformation was positively influenced by lowered redox conditions with or without amendments with $ FeSO_{4} $, electron donors, or alternating anaerobic–aerobic conditions. The main PCB transformation process in all anaerobic treatments at 25°C was reductive dechlorination of 245-2’4’5’ hexachlorobiphenyl to 24-2’4’5’ pentachlorobiphenyl and 24-2’4’ tetrachlorobiphenyl, which occurred at rates between 60–85% in 177 days. Exposing sediments to air for an additional period of 100 days in the sequential anaerobic–aerobic treatment did not result in additional mineralization of PCBs. Temperature, electron donors, and redox conditions significantly affected the abundance of bacteria in the Bacteroidales, Hydrogenophilales, Pseudomonales, Myxococcales, Syntrophobacterales, Acidobacterales, Caldilineales, and Clostridiales orders. The PCB dechlorinator Dehalococcoides and other dechlorinating bacteria were detected in anaerobic sediments, including Desulfitobacterium, Desulfuromonas, Anaeromyxobacter, Geobacter, and Desulfomonile. The data suggested that shifts in the bacterial communities due to abiotic conditions affected PCB transformation, either directly (degraders) or indirectly (bacterial syntrophic associations with degraders). Conclusions The data indicated that elevated redox status and low temperature conditions accounted for stable PCB concentrations under field conditions in Ohio River sediments. In laboratory experiments, PCB removal increased under anaerobic conditions at 25°C, but was not affected by other varying conditions. Depending on the environmental conditions, several bacterial groups involved in the stepwise degradation of natural organic matter to dechlorinating substrates acetate and hydrogen were prevalent in sediments, including Clostridiales, Caldilineales, Syntrophobacterales, Bacteroidales, and Acidobacteriales. 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D’Angelo, Elisa |
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D’Angelo, Elisa ddc 550 bkl 58.52 misc 16S rRNA misc Bioindicators misc Reductive dechlorination misc Syntrophic associations Effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment |
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550 ASE 58.52 bkl Effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment 16S rRNA (dpeaa)DE-He213 Bioindicators (dpeaa)DE-He213 Reductive dechlorination (dpeaa)DE-He213 Syntrophic associations (dpeaa)DE-He213 |
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Effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment |
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Effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment |
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D’Angelo, Elisa |
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10.1007/s11368-010-0218-2 |
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550 |
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verfasserin |
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effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment |
title_auth |
Effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment |
abstract |
Purpose The aim of this study was to evaluate polychlorinated biphenyl (PCB) removal in relation to the associated bacterial community composition in Ohio River sediments (USA) using field and laboratory approaches. Materials and methods PCB removal was studied in different sediment layers applying dialysis equilibrators in the field for 4 months. In parallel, dissolved chemical constituents and bacterial community composition using the 16S rDNA cloning–sequencing approach were determined within the appropriate sediment layers. The effects of several bioremediation treatments on PCB removal and bacterial community composition were evaluated in laboratory experiments. Sediments spiked with 245-2’4’5’ hexachlorobiphenyl were incubated under different conditions for up to 250 days, including alternating anaerobic–aerobic conditions, amendments with electron donors, $ FeSO_{4} $, and incubations at different temperatures (10°C, 25°C, 40°C). Results and discussion PCB levels remained stable in the sediment layers under field conditions. Surface sediments (0–26 cm) had elevated levels of nitrate+nitrite and sulfate, while subsurface sediments (27–35 cm) were characterized by high concentrations of ammonium, methane, and dissolved organic carbon. Oxic/anoxic conditions were also reflected in the bacterial community, with aerobic bacteria in the Bulkholderiales order enriched in the surface sediments, and anaerobic bacteria in the Clostridiales, Syntrophobacteriales, and Desulfobacterales orders more prevalent in the subsurface sediments. Although the chemical status was favorable and the potential degraders were present, PCB transformation did not take place under the prevailing environmental conditions. Under laboratory conditions, PCB transformation was positively influenced by lowered redox conditions with or without amendments with $ FeSO_{4} $, electron donors, or alternating anaerobic–aerobic conditions. The main PCB transformation process in all anaerobic treatments at 25°C was reductive dechlorination of 245-2’4’5’ hexachlorobiphenyl to 24-2’4’5’ pentachlorobiphenyl and 24-2’4’ tetrachlorobiphenyl, which occurred at rates between 60–85% in 177 days. Exposing sediments to air for an additional period of 100 days in the sequential anaerobic–aerobic treatment did not result in additional mineralization of PCBs. Temperature, electron donors, and redox conditions significantly affected the abundance of bacteria in the Bacteroidales, Hydrogenophilales, Pseudomonales, Myxococcales, Syntrophobacterales, Acidobacterales, Caldilineales, and Clostridiales orders. The PCB dechlorinator Dehalococcoides and other dechlorinating bacteria were detected in anaerobic sediments, including Desulfitobacterium, Desulfuromonas, Anaeromyxobacter, Geobacter, and Desulfomonile. The data suggested that shifts in the bacterial communities due to abiotic conditions affected PCB transformation, either directly (degraders) or indirectly (bacterial syntrophic associations with degraders). Conclusions The data indicated that elevated redox status and low temperature conditions accounted for stable PCB concentrations under field conditions in Ohio River sediments. In laboratory experiments, PCB removal increased under anaerobic conditions at 25°C, but was not affected by other varying conditions. Depending on the environmental conditions, several bacterial groups involved in the stepwise degradation of natural organic matter to dechlorinating substrates acetate and hydrogen were prevalent in sediments, including Clostridiales, Caldilineales, Syntrophobacterales, Bacteroidales, and Acidobacteriales. Measurements of the prevailing bacterial community composition and chemical–physical properties important for PCB degradation could be valuable prior to developing PCB bioremediation strategies in sediments. |
abstractGer |
Purpose The aim of this study was to evaluate polychlorinated biphenyl (PCB) removal in relation to the associated bacterial community composition in Ohio River sediments (USA) using field and laboratory approaches. Materials and methods PCB removal was studied in different sediment layers applying dialysis equilibrators in the field for 4 months. In parallel, dissolved chemical constituents and bacterial community composition using the 16S rDNA cloning–sequencing approach were determined within the appropriate sediment layers. The effects of several bioremediation treatments on PCB removal and bacterial community composition were evaluated in laboratory experiments. Sediments spiked with 245-2’4’5’ hexachlorobiphenyl were incubated under different conditions for up to 250 days, including alternating anaerobic–aerobic conditions, amendments with electron donors, $ FeSO_{4} $, and incubations at different temperatures (10°C, 25°C, 40°C). Results and discussion PCB levels remained stable in the sediment layers under field conditions. Surface sediments (0–26 cm) had elevated levels of nitrate+nitrite and sulfate, while subsurface sediments (27–35 cm) were characterized by high concentrations of ammonium, methane, and dissolved organic carbon. Oxic/anoxic conditions were also reflected in the bacterial community, with aerobic bacteria in the Bulkholderiales order enriched in the surface sediments, and anaerobic bacteria in the Clostridiales, Syntrophobacteriales, and Desulfobacterales orders more prevalent in the subsurface sediments. Although the chemical status was favorable and the potential degraders were present, PCB transformation did not take place under the prevailing environmental conditions. Under laboratory conditions, PCB transformation was positively influenced by lowered redox conditions with or without amendments with $ FeSO_{4} $, electron donors, or alternating anaerobic–aerobic conditions. The main PCB transformation process in all anaerobic treatments at 25°C was reductive dechlorination of 245-2’4’5’ hexachlorobiphenyl to 24-2’4’5’ pentachlorobiphenyl and 24-2’4’ tetrachlorobiphenyl, which occurred at rates between 60–85% in 177 days. Exposing sediments to air for an additional period of 100 days in the sequential anaerobic–aerobic treatment did not result in additional mineralization of PCBs. Temperature, electron donors, and redox conditions significantly affected the abundance of bacteria in the Bacteroidales, Hydrogenophilales, Pseudomonales, Myxococcales, Syntrophobacterales, Acidobacterales, Caldilineales, and Clostridiales orders. The PCB dechlorinator Dehalococcoides and other dechlorinating bacteria were detected in anaerobic sediments, including Desulfitobacterium, Desulfuromonas, Anaeromyxobacter, Geobacter, and Desulfomonile. The data suggested that shifts in the bacterial communities due to abiotic conditions affected PCB transformation, either directly (degraders) or indirectly (bacterial syntrophic associations with degraders). Conclusions The data indicated that elevated redox status and low temperature conditions accounted for stable PCB concentrations under field conditions in Ohio River sediments. In laboratory experiments, PCB removal increased under anaerobic conditions at 25°C, but was not affected by other varying conditions. Depending on the environmental conditions, several bacterial groups involved in the stepwise degradation of natural organic matter to dechlorinating substrates acetate and hydrogen were prevalent in sediments, including Clostridiales, Caldilineales, Syntrophobacterales, Bacteroidales, and Acidobacteriales. Measurements of the prevailing bacterial community composition and chemical–physical properties important for PCB degradation could be valuable prior to developing PCB bioremediation strategies in sediments. |
abstract_unstemmed |
Purpose The aim of this study was to evaluate polychlorinated biphenyl (PCB) removal in relation to the associated bacterial community composition in Ohio River sediments (USA) using field and laboratory approaches. Materials and methods PCB removal was studied in different sediment layers applying dialysis equilibrators in the field for 4 months. In parallel, dissolved chemical constituents and bacterial community composition using the 16S rDNA cloning–sequencing approach were determined within the appropriate sediment layers. The effects of several bioremediation treatments on PCB removal and bacterial community composition were evaluated in laboratory experiments. Sediments spiked with 245-2’4’5’ hexachlorobiphenyl were incubated under different conditions for up to 250 days, including alternating anaerobic–aerobic conditions, amendments with electron donors, $ FeSO_{4} $, and incubations at different temperatures (10°C, 25°C, 40°C). Results and discussion PCB levels remained stable in the sediment layers under field conditions. Surface sediments (0–26 cm) had elevated levels of nitrate+nitrite and sulfate, while subsurface sediments (27–35 cm) were characterized by high concentrations of ammonium, methane, and dissolved organic carbon. Oxic/anoxic conditions were also reflected in the bacterial community, with aerobic bacteria in the Bulkholderiales order enriched in the surface sediments, and anaerobic bacteria in the Clostridiales, Syntrophobacteriales, and Desulfobacterales orders more prevalent in the subsurface sediments. Although the chemical status was favorable and the potential degraders were present, PCB transformation did not take place under the prevailing environmental conditions. Under laboratory conditions, PCB transformation was positively influenced by lowered redox conditions with or without amendments with $ FeSO_{4} $, electron donors, or alternating anaerobic–aerobic conditions. The main PCB transformation process in all anaerobic treatments at 25°C was reductive dechlorination of 245-2’4’5’ hexachlorobiphenyl to 24-2’4’5’ pentachlorobiphenyl and 24-2’4’ tetrachlorobiphenyl, which occurred at rates between 60–85% in 177 days. Exposing sediments to air for an additional period of 100 days in the sequential anaerobic–aerobic treatment did not result in additional mineralization of PCBs. Temperature, electron donors, and redox conditions significantly affected the abundance of bacteria in the Bacteroidales, Hydrogenophilales, Pseudomonales, Myxococcales, Syntrophobacterales, Acidobacterales, Caldilineales, and Clostridiales orders. The PCB dechlorinator Dehalococcoides and other dechlorinating bacteria were detected in anaerobic sediments, including Desulfitobacterium, Desulfuromonas, Anaeromyxobacter, Geobacter, and Desulfomonile. The data suggested that shifts in the bacterial communities due to abiotic conditions affected PCB transformation, either directly (degraders) or indirectly (bacterial syntrophic associations with degraders). Conclusions The data indicated that elevated redox status and low temperature conditions accounted for stable PCB concentrations under field conditions in Ohio River sediments. In laboratory experiments, PCB removal increased under anaerobic conditions at 25°C, but was not affected by other varying conditions. Depending on the environmental conditions, several bacterial groups involved in the stepwise degradation of natural organic matter to dechlorinating substrates acetate and hydrogen were prevalent in sediments, including Clostridiales, Caldilineales, Syntrophobacterales, Bacteroidales, and Acidobacteriales. Measurements of the prevailing bacterial community composition and chemical–physical properties important for PCB degradation could be valuable prior to developing PCB bioremediation strategies in sediments. |
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title_short |
Effect of environmental conditions on polychlorinated biphenyl transformations and bacterial communities in a river sediment |
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https://dx.doi.org/10.1007/s11368-010-0218-2 |
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Nunez, Andres |
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score |
7.398467 |