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| f | 1 | { | f | 1 | { |
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| 8 | "author": "Christianson, L.E.", | 8 | "author": "Christianson, L.E.", | ||
| 9 | "author_name": "Christianson, L.E.", | 9 | "author_name": "Christianson, L.E.", | ||
| 10 | "classification_variables": { | 10 | "classification_variables": { | ||
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| 19 | "name": "Organismo publicador del Cat\u00e1logo", | 19 | "name": "Organismo publicador del Cat\u00e1logo", | ||
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| 34 | "created": "2024-11-05", | 34 | "created": "2024-11-05", | ||
| 35 | "creator": [ | 35 | "creator": [ | ||
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| 56 | "contaminacion", | 56 | "contaminacion", | ||
| 57 | "eficiencia", | 57 | "eficiencia", | ||
| 58 | "medidas_de_gestion" | 58 | "medidas_de_gestion" | ||
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| 63 | "license_title": "Creative Commons Attribution", | 63 | "license_title": "Creative Commons Attribution", | ||
| 64 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | 64 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | ||
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| 68 | "metadata_created": "2026-06-23T14:48:36.557589", | 68 | "metadata_created": "2026-06-23T14:48:36.557589", | ||
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| 73 | "miteco_data_population": { | 73 | "miteco_data_population": { | ||
| 74 | "es": "" | 74 | "es": "" | ||
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| 76 | "miteco_data_territory": { | 76 | "miteco_data_territory": { | ||
| 77 | "es": "" | 77 | "es": "" | ||
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| 79 | "miteco_dataset_type": | 79 | "miteco_dataset_type": | ||
| 80 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | 80 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | ||
| 81 | "miteco_geo_level": "1", | 81 | "miteco_geo_level": "1", | ||
| 82 | "modified": "2026-06-23", | 82 | "modified": "2026-06-23", | ||
| 83 | "name": "dfba6e17-3220-5a6c-91d0-9ccbcd1c8283", | 83 | "name": "dfba6e17-3220-5a6c-91d0-9ccbcd1c8283", | ||
| 84 | "notes": "Denitrification drainage bioreactors are emerging as an | 84 | "notes": "Denitrification drainage bioreactors are emerging as an | ||
| 85 | innovative practice to address water quality concerns stemming from | 85 | innovative practice to address water quality concerns stemming from | ||
| 86 | nitrate leaching from drained agricultural lands. Although | 86 | nitrate leaching from drained agricultural lands. Although | ||
| 87 | installation of these systems has begun in farms in the Midwestern | 87 | installation of these systems has begun in farms in the Midwestern | ||
| 88 | United States, the understanding of their design and in-field | 88 | United States, the understanding of their design and in-field | ||
| 89 | performance remains deficient. This study utilized a set of | 89 | performance remains deficient. This study utilized a set of | ||
| 90 | pilot-scale drainage bioreactors to evaluate the impact of bioreactor | 90 | pilot-scale drainage bioreactors to evaluate the impact of bioreactor | ||
| 91 | geometry on reactor hydraulic properties and to determine nitrate | 91 | geometry on reactor hydraulic properties and to determine nitrate | ||
| 92 | removal under steady state conditions and during a simulated storm | 92 | removal under steady state conditions and during a simulated storm | ||
| 93 | event. Bioreactors with different cross-sectional geometries but | 93 | event. Bioreactors with different cross-sectional geometries but | ||
| 94 | similar depths and total volumes were evaluated. Percent reduction of | 94 | similar depths and total volumes were evaluated. Percent reduction of | ||
| 95 | the influent nitrate mass was linearly correlated to the theoretical | 95 | the influent nitrate mass was linearly correlated to the theoretical | ||
| 96 | hydraulic retention time (HRT) with 30 to 70% NO3--N removals observed | 96 | hydraulic retention time (HRT) with 30 to 70% NO3--N removals observed | ||
| 97 | within the four to eight h of retention time suggested for field | 97 | within the four to eight h of retention time suggested for field | ||
| 98 | installations. Tracer tests revealed that in-situ HRTs were | 98 | installations. Tracer tests revealed that in-situ HRTs were | ||
| 99 | substantially greater (i.e. at least 1.5 times as large) than | 99 | substantially greater (i.e. at least 1.5 times as large) than | ||
| 100 | theoretical HRTs.", | 100 | theoretical HRTs.", | ||
| 101 | "notes_translated": { | 101 | "notes_translated": { | ||
| 102 | "es": "Denitrification drainage bioreactors are emerging as an | 102 | "es": "Denitrification drainage bioreactors are emerging as an | ||
| 103 | innovative practice to address water quality concerns stemming from | 103 | innovative practice to address water quality concerns stemming from | ||
| 104 | nitrate leaching from drained agricultural lands. Although | 104 | nitrate leaching from drained agricultural lands. Although | ||
| 105 | installation of these systems has begun in farms in the Midwestern | 105 | installation of these systems has begun in farms in the Midwestern | ||
| 106 | United States, the understanding of their design and in-field | 106 | United States, the understanding of their design and in-field | ||
| 107 | performance remains deficient. This study utilized a set of | 107 | performance remains deficient. This study utilized a set of | ||
| 108 | pilot-scale drainage bioreactors to evaluate the impact of bioreactor | 108 | pilot-scale drainage bioreactors to evaluate the impact of bioreactor | ||
| 109 | geometry on reactor hydraulic properties and to determine nitrate | 109 | geometry on reactor hydraulic properties and to determine nitrate | ||
| 110 | removal under steady state conditions and during a simulated storm | 110 | removal under steady state conditions and during a simulated storm | ||
| 111 | event. Bioreactors with different cross-sectional geometries but | 111 | event. Bioreactors with different cross-sectional geometries but | ||
| 112 | similar depths and total volumes were evaluated. Percent reduction of | 112 | similar depths and total volumes were evaluated. Percent reduction of | ||
| 113 | the influent nitrate mass was linearly correlated to the theoretical | 113 | the influent nitrate mass was linearly correlated to the theoretical | ||
| 114 | hydraulic retention time (HRT) with 30 to 70% NO3--N removals observed | 114 | hydraulic retention time (HRT) with 30 to 70% NO3--N removals observed | ||
| 115 | within the four to eight h of retention time suggested for field | 115 | within the four to eight h of retention time suggested for field | ||
| 116 | installations. Tracer tests revealed that in-situ HRTs were | 116 | installations. Tracer tests revealed that in-situ HRTs were | ||
| 117 | substantially greater (i.e. at least 1.5 times as large) than | 117 | substantially greater (i.e. at least 1.5 times as large) than | ||
| 118 | theoretical HRTs." | 118 | theoretical HRTs." | ||
| 119 | }, | 119 | }, | ||
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| 121 | "num_tags": 7, | 121 | "num_tags": 7, | ||
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| 123 | "approval_status": "approved", | 123 | "approval_status": "approved", | ||
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| 129 | "name": "iepnb", | 129 | "name": "iepnb", | ||
| 130 | "state": "active", | 130 | "state": "active", | ||
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| 142 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | 142 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | ||
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| 144 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 144 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
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| 241 | "name": "agricultura", | 241 | "name": "agricultura", | ||
| 242 | "state": "active", | 242 | "state": "active", | ||
| 243 | "vocabulary_id": null | 243 | "vocabulary_id": null | ||
| 244 | }, | 244 | }, | ||
| 245 | { | 245 | { | ||
| 246 | "display_name": "aguas_residuales", | 246 | "display_name": "aguas_residuales", | ||
| 247 | "id": "1c05284d-393e-4a50-bfa9-8399d88dbe77", | 247 | "id": "1c05284d-393e-4a50-bfa9-8399d88dbe77", | ||
| 248 | "name": "aguas_residuales", | 248 | "name": "aguas_residuales", | ||
| 249 | "state": "active", | 249 | "state": "active", | ||
| 250 | "vocabulary_id": null | 250 | "vocabulary_id": null | ||
| 251 | }, | 251 | }, | ||
| 252 | { | 252 | { | ||
| 253 | "display_name": "contaminacion", | 253 | "display_name": "contaminacion", | ||
| 254 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | 254 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | ||
| 255 | "name": "contaminacion", | 255 | "name": "contaminacion", | ||
| 256 | "state": "active", | 256 | "state": "active", | ||
| 257 | "vocabulary_id": null | 257 | "vocabulary_id": null | ||
| 258 | }, | 258 | }, | ||
| 259 | { | 259 | { | ||
| 260 | "display_name": "eficiencia", | 260 | "display_name": "eficiencia", | ||
| 261 | "id": "af5c3707-639f-471d-aaeb-992567640951", | 261 | "id": "af5c3707-639f-471d-aaeb-992567640951", | ||
| 262 | "name": "eficiencia", | 262 | "name": "eficiencia", | ||
| 263 | "state": "active", | 263 | "state": "active", | ||
| 264 | "vocabulary_id": null | 264 | "vocabulary_id": null | ||
| 265 | }, | 265 | }, | ||
| 266 | { | 266 | { | ||
| 267 | "display_name": "marino", | 267 | "display_name": "marino", | ||
| 268 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | 268 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | ||
| 269 | "name": "marino", | 269 | "name": "marino", | ||
| 270 | "state": "active", | 270 | "state": "active", | ||
| 271 | "vocabulary_id": null | 271 | "vocabulary_id": null | ||
| 272 | }, | 272 | }, | ||
| 273 | { | 273 | { | ||
| 274 | "display_name": "medidas_de_gestion", | 274 | "display_name": "medidas_de_gestion", | ||
| 275 | "id": "c82d981c-d4ad-45e5-8229-afe383d5ea3d", | 275 | "id": "c82d981c-d4ad-45e5-8229-afe383d5ea3d", | ||
| 276 | "name": "medidas_de_gestion", | 276 | "name": "medidas_de_gestion", | ||
| 277 | "state": "active", | 277 | "state": "active", | ||
| 278 | "vocabulary_id": null | 278 | "vocabulary_id": null | ||
| 279 | }, | 279 | }, | ||
| 280 | { | 280 | { | ||
| 281 | "display_name": "tierras-de-regadio", | 281 | "display_name": "tierras-de-regadio", | ||
| 282 | "id": "ad1f4f78-f7c0-40dd-a0a7-6b1b9b844ed9", | 282 | "id": "ad1f4f78-f7c0-40dd-a0a7-6b1b9b844ed9", | ||
| 283 | "name": "tierras-de-regadio", | 283 | "name": "tierras-de-regadio", | ||
| 284 | "state": "active", | 284 | "state": "active", | ||
| 285 | "vocabulary_id": null | 285 | "vocabulary_id": null | ||
| 286 | } | 286 | } | ||
| 287 | ], | 287 | ], | ||
| 288 | "thematic_area": [ | 288 | "thematic_area": [ | ||
| 289 | "espacios_protegidos" | 289 | "espacios_protegidos" | ||
| 290 | ], | 290 | ], | ||
| 291 | "theme_es": [ | 291 | "theme_es": [ | ||
| 292 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 292 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 293 | ], | 293 | ], | ||
| 294 | "title": "Design and performance of denitrification bioreactors for | 294 | "title": "Design and performance of denitrification bioreactors for | ||
| 295 | agricultural drainage", | 295 | agricultural drainage", | ||
| 296 | "title_translated": { | 296 | "title_translated": { | ||
| 297 | "es": "Design and performance of denitrification bioreactors for | 297 | "es": "Design and performance of denitrification bioreactors for | ||
| 298 | agricultural drainage" | 298 | agricultural drainage" | ||
| 299 | }, | 299 | }, | ||
| 300 | "topic": | 300 | "topic": | ||
| 301 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 301 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 302 | "type": "dataset", | 302 | "type": "dataset", | ||
| 303 | "url": | 303 | "url": | ||
| 304 | //iepnb.es:443/catalogo/dataset/dfba6e17-3220-5a6c-91d0-9ccbcd1c8283", | 304 | //iepnb.es:443/catalogo/dataset/dfba6e17-3220-5a6c-91d0-9ccbcd1c8283", | ||
| 305 | "version_notes": { | 305 | "version_notes": { | ||
| 306 | "es": "" | 306 | "es": "" | ||
| 307 | } | 307 | } | ||
| 308 | } | 308 | } |