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spatial_coverage
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en Reducing nitrogen contamination from agricultural subsurface drainage with denitrification bioreactors and controlled drainage
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| 90 | "notes": "Reactive nitrogen leaving agricultural fields through | 90 | "notes": "Reactive nitrogen leaving agricultural fields through | ||
| 91 | subsurface drainage systems enters aquatic systems and contributes to | 91 | subsurface drainage systems enters aquatic systems and contributes to | ||
| 92 | eutrophication, habitat degradation and loss of biodiversity. | 92 | eutrophication, habitat degradation and loss of biodiversity. | ||
| 93 | Denitrification bioreactors, in combination with controlled drainage, | 93 | Denitrification bioreactors, in combination with controlled drainage, | ||
| 94 | are proposed as a means of reducing nitrogen emitted through | 94 | are proposed as a means of reducing nitrogen emitted through | ||
| 95 | subsurface agricultural drainage systems, but their suitability in | 95 | subsurface agricultural drainage systems, but their suitability in | ||
| 96 | colder climates where soils and drainage systems freeze during winter | 96 | colder climates where soils and drainage systems freeze during winter | ||
| 97 | is poorly understood. This study presents the first field scale | 97 | is poorly understood. This study presents the first field scale | ||
| 98 | evaluation of denitrification bioreactors under cold climate | 98 | evaluation of denitrification bioreactors under cold climate | ||
| 99 | conditions during a three-year period in Quebec, Canada. Under a | 99 | conditions during a three-year period in Quebec, Canada. Under a | ||
| 100 | three-year crop rotation, about 55% of the total annual subsurface | 100 | three-year crop rotation, about 55% of the total annual subsurface | ||
| 101 | drainage water passed through bioreactors, which significantly lowered | 101 | drainage water passed through bioreactors, which significantly lowered | ||
| 102 | the total-nitrogen (72%) and nitrate-nitrogen (99%) median | 102 | the total-nitrogen (72%) and nitrate-nitrogen (99%) median | ||
| 103 | concentrations in thesubsurface drainage outflows. Loadings of | 103 | concentrations in thesubsurface drainage outflows. Loadings of | ||
| 104 | nitrate-nitrogen from the test fields to surface drainage ditches were | 104 | nitrate-nitrogen from the test fields to surface drainage ditches were | ||
| 105 | reduced by 99%, equivalent to about 11 kg nitrate-nitrogen ha 1 year 1 | 105 | reduced by 99%, equivalent to about 11 kg nitrate-nitrogen ha 1 year 1 | ||
| 106 | removal in the test area and approximately 7 g nitrate-nitrogen | 106 | removal in the test area and approximately 7 g nitrate-nitrogen | ||
| 107 | removal m 3 bioreactor volume d 1. Aquatic environmental criteria | 107 | removal m 3 bioreactor volume d 1. Aquatic environmental criteria | ||
| 108 | non-compliance events declined by 96% for nitrate-nitrogen and by 50% | 108 | non-compliance events declined by 96% for nitrate-nitrogen and by 50% | ||
| 109 | for total-nitrogen during the three-year study. This study | 109 | for total-nitrogen during the three-year study. This study | ||
| 110 | demonstrates that denitrification bioreactors, combined with | 110 | demonstrates that denitrification bioreactors, combined with | ||
| 111 | controlled drainage, are an effective in-field technology for nitrogen | 111 | controlled drainage, are an effective in-field technology for nitrogen | ||
| 112 | removal from agri cultural subsurface drainage water that will improve | 112 | removal from agri cultural subsurface drainage water that will improve | ||
| 113 | water quality under cold climate conditions.", | 113 | water quality under cold climate conditions.", | ||
| 114 | "notes_translated": { | 114 | "notes_translated": { | ||
| 115 | "es": "Reactive nitrogen leaving agricultural fields through | 115 | "es": "Reactive nitrogen leaving agricultural fields through | ||
| 116 | subsurface drainage systems enters aquatic systems and contributes to | 116 | subsurface drainage systems enters aquatic systems and contributes to | ||
| 117 | eutrophication, habitat degradation and loss of biodiversity. | 117 | eutrophication, habitat degradation and loss of biodiversity. | ||
| 118 | Denitrification bioreactors, in combination with controlled drainage, | 118 | Denitrification bioreactors, in combination with controlled drainage, | ||
| 119 | are proposed as a means of reducing nitrogen emitted through | 119 | are proposed as a means of reducing nitrogen emitted through | ||
| 120 | subsurface agricultural drainage systems, but their suitability in | 120 | subsurface agricultural drainage systems, but their suitability in | ||
| 121 | colder climates where soils and drainage systems freeze during winter | 121 | colder climates where soils and drainage systems freeze during winter | ||
| 122 | is poorly understood. This study presents the first field scale | 122 | is poorly understood. This study presents the first field scale | ||
| 123 | evaluation of denitrification bioreactors under cold climate | 123 | evaluation of denitrification bioreactors under cold climate | ||
| 124 | conditions during a three-year period in Quebec, Canada. Under a | 124 | conditions during a three-year period in Quebec, Canada. Under a | ||
| 125 | three-year crop rotation, about 55% of the total annual subsurface | 125 | three-year crop rotation, about 55% of the total annual subsurface | ||
| 126 | drainage water passed through bioreactors, which significantly lowered | 126 | drainage water passed through bioreactors, which significantly lowered | ||
| 127 | the total-nitrogen (72%) and nitrate-nitrogen (99%) median | 127 | the total-nitrogen (72%) and nitrate-nitrogen (99%) median | ||
| 128 | concentrations in thesubsurface drainage outflows. Loadings of | 128 | concentrations in thesubsurface drainage outflows. Loadings of | ||
| 129 | nitrate-nitrogen from the test fields to surface drainage ditches were | 129 | nitrate-nitrogen from the test fields to surface drainage ditches were | ||
| 130 | reduced by 99%, equivalent to about 11 kg nitrate-nitrogen ha 1 year 1 | 130 | reduced by 99%, equivalent to about 11 kg nitrate-nitrogen ha 1 year 1 | ||
| 131 | removal in the test area and approximately 7 g nitrate-nitrogen | 131 | removal in the test area and approximately 7 g nitrate-nitrogen | ||
| 132 | removal m 3 bioreactor volume d 1. Aquatic environmental criteria | 132 | removal m 3 bioreactor volume d 1. Aquatic environmental criteria | ||
| 133 | non-compliance events declined by 96% for nitrate-nitrogen and by 50% | 133 | non-compliance events declined by 96% for nitrate-nitrogen and by 50% | ||
| 134 | for total-nitrogen during the three-year study. This study | 134 | for total-nitrogen during the three-year study. This study | ||
| 135 | demonstrates that denitrification bioreactors, combined with | 135 | demonstrates that denitrification bioreactors, combined with | ||
| 136 | controlled drainage, are an effective in-field technology for nitrogen | 136 | controlled drainage, are an effective in-field technology for nitrogen | ||
| 137 | removal from agri cultural subsurface drainage water that will improve | 137 | removal from agri cultural subsurface drainage water that will improve | ||
| 138 | water quality under cold climate conditions." | 138 | water quality under cold climate conditions." | ||
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| 269 | "type": "Point" | ||||
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| 271 | "text": "Espa\u00f1a", | 242 | "text": "Espa\u00f1a", | ||
| 272 | "uri": | 243 | "uri": | ||
| 273 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 244 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
| 274 | } | 245 | } | ||
| 275 | ], | 246 | ], | ||
| 276 | "spatial_uri": | 247 | "spatial_uri": | ||
| 277 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | 248 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | ||
| 278 | "state": "active", | 249 | "state": "active", | ||
| 279 | "study_variables": { | 250 | "study_variables": { | ||
| 280 | "es": "" | 251 | "es": "" | ||
| 281 | }, | 252 | }, | ||
| 282 | "tag_uri": [ | 253 | "tag_uri": [ | ||
| 283 | 254 | ||||
| 284 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 255 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 285 | ], | 256 | ], | ||
| 286 | "tags": [ | 257 | "tags": [ | ||
| 287 | { | 258 | { | ||
| 288 | "display_name": "contaminacion", | 259 | "display_name": "contaminacion", | ||
| 289 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | 260 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | ||
| 290 | "name": "contaminacion", | 261 | "name": "contaminacion", | ||
| 291 | "state": "active", | 262 | "state": "active", | ||
| 292 | "vocabulary_id": null | 263 | "vocabulary_id": null | ||
| 293 | }, | 264 | }, | ||
| 294 | { | 265 | { | ||
| 295 | "display_name": "gestion_sostenible", | 266 | "display_name": "gestion_sostenible", | ||
| 296 | "id": "ab71cc3e-3c99-4f3f-a20f-d4e8016c3b55", | 267 | "id": "ab71cc3e-3c99-4f3f-a20f-d4e8016c3b55", | ||
| 297 | "name": "gestion_sostenible", | 268 | "name": "gestion_sostenible", | ||
| 298 | "state": "active", | 269 | "state": "active", | ||
| 299 | "vocabulary_id": null | 270 | "vocabulary_id": null | ||
| 300 | }, | 271 | }, | ||
| 301 | { | 272 | { | ||
| 302 | "display_name": "marino", | 273 | "display_name": "marino", | ||
| 303 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | 274 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | ||
| 304 | "name": "marino", | 275 | "name": "marino", | ||
| 305 | "state": "active", | 276 | "state": "active", | ||
| 306 | "vocabulary_id": null | 277 | "vocabulary_id": null | ||
| 307 | }, | 278 | }, | ||
| 308 | { | 279 | { | ||
| 309 | "display_name": "tierras-de-regadio", | 280 | "display_name": "tierras-de-regadio", | ||
| 310 | "id": "ad1f4f78-f7c0-40dd-a0a7-6b1b9b844ed9", | 281 | "id": "ad1f4f78-f7c0-40dd-a0a7-6b1b9b844ed9", | ||
| 311 | "name": "tierras-de-regadio", | 282 | "name": "tierras-de-regadio", | ||
| 312 | "state": "active", | 283 | "state": "active", | ||
| 313 | "vocabulary_id": null | 284 | "vocabulary_id": null | ||
| 314 | } | 285 | } | ||
| 315 | ], | 286 | ], | ||
| 316 | "thematic_area": [ | 287 | "thematic_area": [ | ||
| 317 | "espacios_protegidos" | 288 | "espacios_protegidos" | ||
| 318 | ], | 289 | ], | ||
| 319 | "theme_es": [ | 290 | "theme_es": [ | ||
| 320 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 291 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 321 | ], | 292 | ], | ||
| 322 | "title": "Reducing nitrogen contamination from agricultural | 293 | "title": "Reducing nitrogen contamination from agricultural | ||
| 323 | subsurface drainage with denitrification bioreactors and controlled | 294 | subsurface drainage with denitrification bioreactors and controlled | ||
| 324 | drainage", | 295 | drainage", | ||
| 325 | "title_translated": { | 296 | "title_translated": { | ||
| 326 | "es": "Reducing nitrogen contamination from agricultural | 297 | "es": "Reducing nitrogen contamination from agricultural | ||
| 327 | subsurface drainage with denitrification bioreactors and controlled | 298 | subsurface drainage with denitrification bioreactors and controlled | ||
| 328 | drainage" | 299 | drainage" | ||
| 329 | }, | 300 | }, | ||
| 330 | "topic": | 301 | "topic": | ||
| 331 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 302 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 332 | "type": "dataset", | 303 | "type": "dataset", | ||
| 333 | "url": | 304 | "url": | ||
| 334 | //iepnb.es:443/catalogo/dataset/df43db66-3f29-51ec-9f0f-b363198fe5ae", | 305 | //iepnb.es:443/catalogo/dataset/df43db66-3f29-51ec-9f0f-b363198fe5ae", | ||
| 335 | "version_notes": { | 306 | "version_notes": { | ||
| 336 | "es": "" | 307 | "es": "" | ||
| 337 | } | 308 | } | ||
| 338 | } | 309 | } |