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En el instante 23 de junio de 2026, 16:12:18 UTC,
-
Modificado el valor del campo
spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-2.34, 37.38], [-0.69, 37.38], [-0.69, 38.76], [-2.34, 38.76], [-2.34, 37.38]]]}', 'centroid': '{"type": "Point", "coordinates": [-1.515, 38.07]}', 'text': 'Región de Murcia', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia'}]
en Remote sensing of underwater vegetation using single-beam acoustics
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| 94 | "notes": "A single-beam, acoustic, ground-discrimination system (QTC | 94 | "notes": "A single-beam, acoustic, ground-discrimination system (QTC | ||
| 95 | VIEW, Series V) was used to study the distribution of underwater | 95 | VIEW, Series V) was used to study the distribution of underwater | ||
| 96 | macrophytes in a shallow-water coastal system, employing frequencies | 96 | macrophytes in a shallow-water coastal system, employing frequencies | ||
| 97 | of 50 and 200 kHz. The study was conducted in Mar Menor, SE Spain, | 97 | of 50 and 200 kHz. The study was conducted in Mar Menor, SE Spain, | ||
| 98 | where the expansion of Caulerpa prolifera has contributed to the | 98 | where the expansion of Caulerpa prolifera has contributed to the | ||
| 99 | silting up of the superficial sediments. A direct relationship was | 99 | silting up of the superficial sediments. A direct relationship was | ||
| 100 | identified between algal biomass and sediment-fines content. Acoustic | 100 | identified between algal biomass and sediment-fines content. Acoustic | ||
| 101 | information on sediment grain size and data on algal biomass were | 101 | information on sediment grain size and data on algal biomass were | ||
| 102 | obtained in muddy and sandy sediments, including vegetated and | 102 | obtained in muddy and sandy sediments, including vegetated and | ||
| 103 | non-vegetated seabed. Non-vegetated muddy areas were created by diving | 103 | non-vegetated seabed. Non-vegetated muddy areas were created by diving | ||
| 104 | and handpicking the algae. The multivariate acoustic data were | 104 | and handpicking the algae. The multivariate acoustic data were | ||
| 105 | analysed under the null hypotheses that there were no acoustic | 105 | analysed under the null hypotheses that there were no acoustic | ||
| 106 | differences between bare seabeds with contrasting superficial sediment | 106 | differences between bare seabeds with contrasting superficial sediment | ||
| 107 | types or among low, medium, and high algal-biomass areas, having in | 107 | types or among low, medium, and high algal-biomass areas, having in | ||
| 108 | mind that grain size can act as a confounding factor. Both null | 108 | mind that grain size can act as a confounding factor. Both null | ||
| 109 | hypotheses were rejected, and the results showed that 200 kHz was | 109 | hypotheses were rejected, and the results showed that 200 kHz was | ||
| 110 | better than 50 kHz in distinguishing cover levels of algal biomass. | 110 | better than 50 kHz in distinguishing cover levels of algal biomass. | ||
| 111 | The relationship between the 200-kHz acoustic data and algal biomass | 111 | The relationship between the 200-kHz acoustic data and algal biomass | ||
| 112 | suggests utility in modelling the latter using the former.", | 112 | suggests utility in modelling the latter using the former.", | ||
| 113 | "notes_translated": { | 113 | "notes_translated": { | ||
| 114 | "es": "A single-beam, acoustic, ground-discrimination system (QTC | 114 | "es": "A single-beam, acoustic, ground-discrimination system (QTC | ||
| 115 | VIEW, Series V) was used to study the distribution of underwater | 115 | VIEW, Series V) was used to study the distribution of underwater | ||
| 116 | macrophytes in a shallow-water coastal system, employing frequencies | 116 | macrophytes in a shallow-water coastal system, employing frequencies | ||
| 117 | of 50 and 200 kHz. The study was conducted in Mar Menor, SE Spain, | 117 | of 50 and 200 kHz. The study was conducted in Mar Menor, SE Spain, | ||
| 118 | where the expansion of Caulerpa prolifera has contributed to the | 118 | where the expansion of Caulerpa prolifera has contributed to the | ||
| 119 | silting up of the superficial sediments. A direct relationship was | 119 | silting up of the superficial sediments. A direct relationship was | ||
| 120 | identified between algal biomass and sediment-fines content. Acoustic | 120 | identified between algal biomass and sediment-fines content. Acoustic | ||
| 121 | information on sediment grain size and data on algal biomass were | 121 | information on sediment grain size and data on algal biomass were | ||
| 122 | obtained in muddy and sandy sediments, including vegetated and | 122 | obtained in muddy and sandy sediments, including vegetated and | ||
| 123 | non-vegetated seabed. Non-vegetated muddy areas were created by diving | 123 | non-vegetated seabed. Non-vegetated muddy areas were created by diving | ||
| 124 | and handpicking the algae. The multivariate acoustic data were | 124 | and handpicking the algae. The multivariate acoustic data were | ||
| 125 | analysed under the null hypotheses that there were no acoustic | 125 | analysed under the null hypotheses that there were no acoustic | ||
| 126 | differences between bare seabeds with contrasting superficial sediment | 126 | differences between bare seabeds with contrasting superficial sediment | ||
| 127 | types or among low, medium, and high algal-biomass areas, having in | 127 | types or among low, medium, and high algal-biomass areas, having in | ||
| 128 | mind that grain size can act as a confounding factor. Both null | 128 | mind that grain size can act as a confounding factor. Both null | ||
| 129 | hypotheses were rejected, and the results showed that 200 kHz was | 129 | hypotheses were rejected, and the results showed that 200 kHz was | ||
| 130 | better than 50 kHz in distinguishing cover levels of algal biomass. | 130 | better than 50 kHz in distinguishing cover levels of algal biomass. | ||
| 131 | The relationship between the 200-kHz acoustic data and algal biomass | 131 | The relationship between the 200-kHz acoustic data and algal biomass | ||
| 132 | suggests utility in modelling the latter using the former." | 132 | suggests utility in modelling the latter using the former." | ||
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| 267 | atos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia" | 238 | atos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia" | ||
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| 273 | "study_variables": { | 244 | "study_variables": { | ||
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| 276 | "tag_uri": [ | 247 | "tag_uri": [ | ||
| 277 | 248 | ||||
| 278 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 249 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 279 | ], | 250 | ], | ||
| 280 | "tags": [ | 251 | "tags": [ | ||
| 281 | { | 252 | { | ||
| 282 | "display_name": "analisis_espacial", | 253 | "display_name": "analisis_espacial", | ||
| 283 | "id": "7af4b5b1-a152-48cb-b581-a321fbe3ff88", | 254 | "id": "7af4b5b1-a152-48cb-b581-a321fbe3ff88", | ||
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| 289 | "display_name": "diversidad", | 260 | "display_name": "diversidad", | ||
| 290 | "id": "34ab7b9c-f2e0-47ad-aab4-69c31e8d0e14", | 261 | "id": "34ab7b9c-f2e0-47ad-aab4-69c31e8d0e14", | ||
| 291 | "name": "diversidad", | 262 | "name": "diversidad", | ||
| 292 | "state": "active", | 263 | "state": "active", | ||
| 293 | "vocabulary_id": null | 264 | "vocabulary_id": null | ||
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| 297 | "id": "4a120a32-4ed4-4b61-9193-1d46da5f3b4e", | 268 | "id": "4a120a32-4ed4-4b61-9193-1d46da5f3b4e", | ||
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| 300 | "vocabulary_id": null | 271 | "vocabulary_id": null | ||
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| 304 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | 275 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | ||
| 305 | "name": "marino", | 276 | "name": "marino", | ||
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| 307 | "vocabulary_id": null | 278 | "vocabulary_id": null | ||
| 308 | }, | 279 | }, | ||
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| 310 | "display_name": "sensores_remotos_teledeteccion", | 281 | "display_name": "sensores_remotos_teledeteccion", | ||
| 311 | "id": "1b91e619-fdaa-4fc8-9e06-20443950d6fa", | 282 | "id": "1b91e619-fdaa-4fc8-9e06-20443950d6fa", | ||
| 312 | "name": "sensores_remotos_teledeteccion", | 283 | "name": "sensores_remotos_teledeteccion", | ||
| 313 | "state": "active", | 284 | "state": "active", | ||
| 314 | "vocabulary_id": null | 285 | "vocabulary_id": null | ||
| 315 | } | 286 | } | ||
| 316 | ], | 287 | ], | ||
| 317 | "thematic_area": [ | 288 | "thematic_area": [ | ||
| 318 | "espacios_protegidos" | 289 | "espacios_protegidos" | ||
| 319 | ], | 290 | ], | ||
| 320 | "theme_es": [ | 291 | "theme_es": [ | ||
| 321 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 292 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 322 | ], | 293 | ], | ||
| 323 | "title": "Remote sensing of underwater vegetation using single-beam | 294 | "title": "Remote sensing of underwater vegetation using single-beam | ||
| 324 | acoustics", | 295 | acoustics", | ||
| 325 | "title_translated": { | 296 | "title_translated": { | ||
| 326 | "es": "Remote sensing of underwater vegetation using single-beam | 297 | "es": "Remote sensing of underwater vegetation using single-beam | ||
| 327 | acoustics" | 298 | acoustics" | ||
| 328 | }, | 299 | }, | ||
| 329 | "topic": | 300 | "topic": | ||
| 330 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 301 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 331 | "type": "dataset", | 302 | "type": "dataset", | ||
| 332 | "url": | 303 | "url": | ||
| 333 | //iepnb.es:443/catalogo/dataset/20c1fe6f-c0e9-5e5e-a1f2-bc66ca52435c", | 304 | //iepnb.es:443/catalogo/dataset/20c1fe6f-c0e9-5e5e-a1f2-bc66ca52435c", | ||
| 334 | "version_notes": { | 305 | "version_notes": { | ||
| 335 | "es": "" | 306 | "es": "" | ||
| 336 | } | 307 | } | ||
| 337 | } | 308 | } |