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en High-rate biological denitrification in the cyclic rotating-bed biological reactor: Effect of COD=NO 3 , nitrate concentration and salinity and the phylogenetic analysis of denitrifiers -
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) en High-rate biological denitrification in the cyclic rotating-bed biological reactor: Effect of COD=NO 3 , nitrate concentration and salinity and the phylogenetic analysis of denitrifiers
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| 86 | "notes": "The effects of COD=NO 3 ratio, nitrate concentration and | 96 | "notes": "The effects of COD=NO 3 ratio, nitrate concentration and | ||
| 87 | salinity was tested on the performance of the CRBR in denitrification | 97 | salinity was tested on the performance of the CRBR in denitrification | ||
| 88 | with catechol as carbon source. The maximum nitrate reduction attained | 98 | with catechol as carbon source. The maximum nitrate reduction attained | ||
| 89 | atCOD=NO 3 ratio of 1. The CRBR operated at optimum COD=NO3 ratio | 99 | atCOD=NO 3 ratio of 1. The CRBR operated at optimum COD=NO3 ratio | ||
| 90 | could completely denitrify the nitrate at inlet concentration up to | 100 | could completely denitrify the nitrate at inlet concentration up to | ||
| 91 | 1250 mg/L without nitrite accumulation. The maximum denitrifica tion | 101 | 1250 mg/L without nitrite accumulation. The maximum denitrifica tion | ||
| 92 | rate in the CRBR was 3:56 kgNO 3 =m3 d with a nitrate reduction | 102 | rate in the CRBR was 3:56 kgNO 3 =m3 d with a nitrate reduction | ||
| 93 | efficiency of 99% when the bioreactor was operated at inlet nitrate | 103 | efficiency of 99% when the bioreactor was operated at inlet nitrate | ||
| 94 | loading rate of 3:6 kgNO 3 =m3 d. The denitrification performance of | 104 | loading rate of 3:6 kgNO 3 =m3 d. The denitrification performance of | ||
| 95 | the CRBR was not affected significantly by NaCl concentrations up to | 105 | the CRBR was not affected significantly by NaCl concentrations up to | ||
| 96 | 20 g/L. 16S rRNA fragment and phylogenetic analysis identified | 106 | 20 g/L. 16S rRNA fragment and phylogenetic analysis identified | ||
| 97 | Pseudomonas resinovorans, Stenotrophomonas maltophilia and Bacillus | 107 | Pseudomonas resinovorans, Stenotrophomonas maltophilia and Bacillus | ||
| 98 | cereus as the most abundant denitrifiers in biomass. Accordingly, the | 108 | cereus as the most abundant denitrifiers in biomass. Accordingly, the | ||
| 99 | CRBR is a high-rate bioreactor and appropriate technology for | 109 | CRBR is a high-rate bioreactor and appropriate technology for | ||
| 100 | treatment of nitrate-laden industrial wastewaters containing phenolic | 110 | treatment of nitrate-laden industrial wastewaters containing phenolic | ||
| 101 | compounds and salinity.", | 111 | compounds and salinity.", | ||
| 102 | "notes_translated": { | 112 | "notes_translated": { | ||
| 103 | "es": "The effects of COD=NO 3 ratio, nitrate concentration and | 113 | "es": "The effects of COD=NO 3 ratio, nitrate concentration and | ||
| 104 | salinity was tested on the performance of the CRBR in denitrification | 114 | salinity was tested on the performance of the CRBR in denitrification | ||
| 105 | with catechol as carbon source. The maximum nitrate reduction attained | 115 | with catechol as carbon source. The maximum nitrate reduction attained | ||
| 106 | atCOD=NO 3 ratio of 1. The CRBR operated at optimum COD=NO3 ratio | 116 | atCOD=NO 3 ratio of 1. The CRBR operated at optimum COD=NO3 ratio | ||
| 107 | could completely denitrify the nitrate at inlet concentration up to | 117 | could completely denitrify the nitrate at inlet concentration up to | ||
| 108 | 1250 mg/L without nitrite accumulation. The maximum denitrifica tion | 118 | 1250 mg/L without nitrite accumulation. The maximum denitrifica tion | ||
| 109 | rate in the CRBR was 3:56 kgNO 3 =m3 d with a nitrate reduction | 119 | rate in the CRBR was 3:56 kgNO 3 =m3 d with a nitrate reduction | ||
| 110 | efficiency of 99% when the bioreactor was operated at inlet nitrate | 120 | efficiency of 99% when the bioreactor was operated at inlet nitrate | ||
| 111 | loading rate of 3:6 kgNO 3 =m3 d. The denitrification performance of | 121 | loading rate of 3:6 kgNO 3 =m3 d. The denitrification performance of | ||
| 112 | the CRBR was not affected significantly by NaCl concentrations up to | 122 | the CRBR was not affected significantly by NaCl concentrations up to | ||
| 113 | 20 g/L. 16S rRNA fragment and phylogenetic analysis identified | 123 | 20 g/L. 16S rRNA fragment and phylogenetic analysis identified | ||
| 114 | Pseudomonas resinovorans, Stenotrophomonas maltophilia and Bacillus | 124 | Pseudomonas resinovorans, Stenotrophomonas maltophilia and Bacillus | ||
| 115 | cereus as the most abundant denitrifiers in biomass. Accordingly, the | 125 | cereus as the most abundant denitrifiers in biomass. Accordingly, the | ||
| 116 | CRBR is a high-rate bioreactor and appropriate technology for | 126 | CRBR is a high-rate bioreactor and appropriate technology for | ||
| 117 | treatment of nitrate-laden industrial wastewaters containing phenolic | 127 | treatment of nitrate-laden industrial wastewaters containing phenolic | ||
| 118 | compounds and salinity." | 128 | compounds and salinity." | ||
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| 222 | "text": "Espa\u00f1a", | 232 | "text": "Espa\u00f1a", | ||
| 223 | "uri": | 233 | "uri": | ||
| 224 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 234 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
| 225 | } | 235 | } | ||
| 226 | ], | 236 | ], | ||
| 227 | "spatial_uri": | 237 | "spatial_uri": | ||
| 228 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | 238 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | ||
| 229 | "state": "active", | 239 | "state": "active", | ||
| 230 | "study_variables": { | 240 | "study_variables": { | ||
| 231 | "es": "" | 241 | "es": "" | ||
| 232 | }, | 242 | }, | ||
| 233 | "tag_uri": [ | 243 | "tag_uri": [ | ||
| 234 | 244 | ||||
| 235 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 245 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 236 | ], | 246 | ], | ||
| 237 | "tags": [ | 247 | "tags": [ | ||
| 238 | { | 248 | { | ||
| 239 | "display_name": "gestion_sostenible", | 249 | "display_name": "gestion_sostenible", | ||
| 240 | "id": "ab71cc3e-3c99-4f3f-a20f-d4e8016c3b55", | 250 | "id": "ab71cc3e-3c99-4f3f-a20f-d4e8016c3b55", | ||
| 241 | "name": "gestion_sostenible", | 251 | "name": "gestion_sostenible", | ||
| 242 | "state": "active", | 252 | "state": "active", | ||
| 243 | "vocabulary_id": null | 253 | "vocabulary_id": null | ||
| 244 | }, | 254 | }, | ||
| 245 | { | 255 | { | ||
| 246 | "display_name": "marino", | 256 | "display_name": "marino", | ||
| 247 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | 257 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | ||
| 248 | "name": "marino", | 258 | "name": "marino", | ||
| 249 | "state": "active", | 259 | "state": "active", | ||
| 250 | "vocabulary_id": null | 260 | "vocabulary_id": null | ||
| 251 | } | 261 | } | ||
| 252 | ], | 262 | ], | ||
| 253 | "thematic_area": [ | 263 | "thematic_area": [ | ||
| 254 | "espacios_protegidos" | 264 | "espacios_protegidos" | ||
| 255 | ], | 265 | ], | ||
| 256 | "theme_es": [ | 266 | "theme_es": [ | ||
| 257 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 267 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 258 | ], | 268 | ], | ||
| 259 | "title": "High-rate biological denitrification in the cyclic | 269 | "title": "High-rate biological denitrification in the cyclic | ||
| 260 | rotating-bed biological reactor: Effect of COD=NO 3 , nitrate | 270 | rotating-bed biological reactor: Effect of COD=NO 3 , nitrate | ||
| 261 | concentration and salinity and the phylogenetic analysis of | 271 | concentration and salinity and the phylogenetic analysis of | ||
| 262 | denitrifiers", | 272 | denitrifiers", | ||
| 263 | "title_translated": { | 273 | "title_translated": { | ||
| 264 | "es": "High-rate biological denitrification in the cyclic | 274 | "es": "High-rate biological denitrification in the cyclic | ||
| 265 | rotating-bed biological reactor: Effect of COD=NO 3 , nitrate | 275 | rotating-bed biological reactor: Effect of COD=NO 3 , nitrate | ||
| 266 | concentration and salinity and the phylogenetic analysis of | 276 | concentration and salinity and the phylogenetic analysis of | ||
| 267 | denitrifiers" | 277 | denitrifiers" | ||
| 268 | }, | 278 | }, | ||
| 269 | "topic": | 279 | "topic": | ||
| 270 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 280 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 271 | "type": "dataset", | 281 | "type": "dataset", | ||
| 272 | "url": | 282 | "url": | ||
| 273 | //iepnb.es:443/catalogo/dataset/3d7510bd-6255-5672-b3c7-9388c37e0f19", | 283 | //iepnb.es:443/catalogo/dataset/3d7510bd-6255-5672-b3c7-9388c37e0f19", | ||
| 274 | "version_notes": { | 284 | "version_notes": { | ||
| 275 | "es": "" | 285 | "es": "" | ||
| 276 | } | 286 | } | ||
| 277 | } | 287 | } |