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En el instante 23 de junio de 2026, 16:00:38 UTC,
-
Modificado el valor del campo
spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-18.16, 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, 27.64]]]}', 'centroid': '{"type": "Point", "coordinates": [-6.92, 35.715]}', 'text': 'España', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Pais/España'}]
en Spatio-temporal impacts of roads on the persistence of populations: analytic and numerical approaches.
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| 71 | "miteco_data_population": { | 71 | "miteco_data_population": { | ||
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| 81 | "name": "ba8e23a9-97ec-572d-bca9-f355313d3826", | 81 | "name": "ba8e23a9-97ec-572d-bca9-f355313d3826", | ||
| 82 | "notes": "Roads can have drastic impacts on wildlife populations. | 82 | "notes": "Roads can have drastic impacts on wildlife populations. | ||
| 83 | Although there is wide recognition of the negative impacts caused by | 83 | Although there is wide recognition of the negative impacts caused by | ||
| 84 | roads and a wealth of practical studies, there is a lack of | 84 | roads and a wealth of practical studies, there is a lack of | ||
| 85 | theoretical work that can be used to predict the impact of road | 85 | theoretical work that can be used to predict the impact of road | ||
| 86 | networks or to implement mitigation measures. Here, using | 86 | networks or to implement mitigation measures. Here, using | ||
| 87 | Skellam\u2019s diffusion model, we develop analytic and numerical | 87 | Skellam\u2019s diffusion model, we develop analytic and numerical | ||
| 88 | approaches to analyze the impact of road networks on the survival of | 88 | approaches to analyze the impact of road networks on the survival of | ||
| 89 | populations. Our models show that the viability of a population is | 89 | populations. Our models show that the viability of a population is | ||
| 90 | determined not only by road density but also by the size and shape of | 90 | determined not only by road density but also by the size and shape of | ||
| 91 | patches. Accordingly, we studied the minimum size of a patch to | 91 | patches. Accordingly, we studied the minimum size of a patch to | ||
| 92 | sustain a population with given diffusion and growth parameters. We | 92 | sustain a population with given diffusion and growth parameters. We | ||
| 93 | provide simple formulas to estimate the minimum patch size, and | 93 | provide simple formulas to estimate the minimum patch size, and | ||
| 94 | illustrate the importance of shape with square and rectangular | 94 | illustrate the importance of shape with square and rectangular | ||
| 95 | patches. Our models also allow the estimation of time to extinction | 95 | patches. Our models also allow the estimation of time to extinction | ||
| 96 | after road \u2026\n Palabras clave: Population", | 96 | after road \u2026\n Palabras clave: Population", | ||
| 97 | "notes_translated": { | 97 | "notes_translated": { | ||
| 98 | "en": "Roads can have drastic impacts on wildlife populations. | 98 | "en": "Roads can have drastic impacts on wildlife populations. | ||
| 99 | Although there is wide recognition of the negative impacts caused by | 99 | Although there is wide recognition of the negative impacts caused by | ||
| 100 | roads and a wealth of practical studies, there is a lack of | 100 | roads and a wealth of practical studies, there is a lack of | ||
| 101 | theoretical work that can be used to predict the impact of road | 101 | theoretical work that can be used to predict the impact of road | ||
| 102 | networks or to implement mitigation measures. Here, using | 102 | networks or to implement mitigation measures. Here, using | ||
| 103 | Skellam\u2019s diffusion model, we develop analytic and numerical | 103 | Skellam\u2019s diffusion model, we develop analytic and numerical | ||
| 104 | approaches to analyze the impact of road networks on the survival of | 104 | approaches to analyze the impact of road networks on the survival of | ||
| 105 | populations. Our models show that the viability of a population is | 105 | populations. Our models show that the viability of a population is | ||
| 106 | determined not only by road density but also by the size and shape of | 106 | determined not only by road density but also by the size and shape of | ||
| 107 | patches. Accordingly, we studied the minimum size of a patch to | 107 | patches. Accordingly, we studied the minimum size of a patch to | ||
| 108 | sustain a population with given diffusion and growth parameters. We | 108 | sustain a population with given diffusion and growth parameters. We | ||
| 109 | provide simple formulas to estimate the minimum patch size, and | 109 | provide simple formulas to estimate the minimum patch size, and | ||
| 110 | illustrate the importance of shape with square and rectangular | 110 | illustrate the importance of shape with square and rectangular | ||
| 111 | patches. Our models also allow the estimation of time to extinction | 111 | patches. Our models also allow the estimation of time to extinction | ||
| 112 | after road \u2026", | 112 | after road \u2026", | ||
| 113 | "es": "Roads can have drastic impacts on wildlife populations. | 113 | "es": "Roads can have drastic impacts on wildlife populations. | ||
| 114 | Although there is wide recognition of the negative impacts caused by | 114 | Although there is wide recognition of the negative impacts caused by | ||
| 115 | roads and a wealth of practical studies, there is a lack of | 115 | roads and a wealth of practical studies, there is a lack of | ||
| 116 | theoretical work that can be used to predict the impact of road | 116 | theoretical work that can be used to predict the impact of road | ||
| 117 | networks or to implement mitigation measures. Here, using | 117 | networks or to implement mitigation measures. Here, using | ||
| 118 | Skellam\u2019s diffusion model, we develop analytic and numerical | 118 | Skellam\u2019s diffusion model, we develop analytic and numerical | ||
| 119 | approaches to analyze the impact of road networks on the survival of | 119 | approaches to analyze the impact of road networks on the survival of | ||
| 120 | populations. Our models show that the viability of a population is | 120 | populations. Our models show that the viability of a population is | ||
| 121 | determined not only by road density but also by the size and shape of | 121 | determined not only by road density but also by the size and shape of | ||
| 122 | patches. Accordingly, we studied the minimum size of a patch to | 122 | patches. Accordingly, we studied the minimum size of a patch to | ||
| 123 | sustain a population with given diffusion and growth parameters. We | 123 | sustain a population with given diffusion and growth parameters. We | ||
| 124 | provide simple formulas to estimate the minimum patch size, and | 124 | provide simple formulas to estimate the minimum patch size, and | ||
| 125 | illustrate the importance of shape with square and rectangular | 125 | illustrate the importance of shape with square and rectangular | ||
| 126 | patches. Our models also allow the estimation of time to extinction | 126 | patches. Our models also allow the estimation of time to extinction | ||
| 127 | after road \u2026\n Palabras clave: Population" | 127 | after road \u2026\n Palabras clave: Population" | ||
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| 244 | [ | ||||
| 245 | -18.16, | ||||
| 246 | 43.79 | ||||
| 247 | ], | ||||
| 248 | [ | ||||
| 249 | -18.16, | ||||
| 250 | 27.64 | ||||
| 251 | ] | ||||
| 252 | ] | ||||
| 253 | ], | ||||
| 254 | "type": "Polygon" | ||||
| 255 | }, | ||||
| 256 | "centroid": { | ||||
| 257 | "coordinates": [ | ||||
| 258 | -6.92, | ||||
| 259 | 35.715 | ||||
| 260 | ], | ||||
| 261 | "type": "Point" | ||||
| 262 | }, | ||||
| 263 | "text": "Espa\u00f1a", | 234 | "text": "Espa\u00f1a", | ||
| 264 | "uri": | 235 | "uri": | ||
| 265 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | 236 | ttp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a" | ||
| 266 | } | 237 | } | ||
| 267 | ], | 238 | ], | ||
| 268 | "spatial_resolution_in_meters": "", | 239 | "spatial_resolution_in_meters": "", | ||
| 269 | "spatial_uri": | 240 | "spatial_uri": | ||
| 270 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | 241 | tp://datos.gob.es/recurso/sector-publico/territorio/Pais/Espa\u00f1a", | ||
| 271 | "state": "active", | 242 | "state": "active", | ||
| 272 | "study_variables": { | 243 | "study_variables": { | ||
| 273 | "es": "" | 244 | "es": "" | ||
| 274 | }, | 245 | }, | ||
| 275 | "tag_uri": [ | 246 | "tag_uri": [ | ||
| 276 | 247 | ||||
| 277 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 248 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 278 | ], | 249 | ], | ||
| 279 | "tags": [ | 250 | "tags": [ | ||
| 280 | { | 251 | { | ||
| 281 | "display_name": "aspectos-globales-sobre-fragmentacion-de", | 252 | "display_name": "aspectos-globales-sobre-fragmentacion-de", | ||
| 282 | "id": "2379c860-0540-450a-9a23-72454ee80469", | 253 | "id": "2379c860-0540-450a-9a23-72454ee80469", | ||
| 283 | "name": "aspectos-globales-sobre-fragmentacion-de", | 254 | "name": "aspectos-globales-sobre-fragmentacion-de", | ||
| 284 | "state": "active", | 255 | "state": "active", | ||
| 285 | "vocabulary_id": null | 256 | "vocabulary_id": null | ||
| 286 | }, | 257 | }, | ||
| 287 | { | 258 | { | ||
| 288 | "display_name": "fragmentacion", | 259 | "display_name": "fragmentacion", | ||
| 289 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | 260 | "id": "627f9c0a-a199-4c69-b563-0c8d626e3194", | ||
| 290 | "name": "fragmentacion", | 261 | "name": "fragmentacion", | ||
| 291 | "state": "active", | 262 | "state": "active", | ||
| 292 | "vocabulary_id": null | 263 | "vocabulary_id": null | ||
| 293 | }, | 264 | }, | ||
| 294 | { | 265 | { | ||
| 295 | "display_name": "poblacion", | 266 | "display_name": "poblacion", | ||
| 296 | "id": "e104a1ee-9489-4d5e-bb7b-7ecfe1899b23", | 267 | "id": "e104a1ee-9489-4d5e-bb7b-7ecfe1899b23", | ||
| 297 | "name": "poblacion", | 268 | "name": "poblacion", | ||
| 298 | "state": "active", | 269 | "state": "active", | ||
| 299 | "vocabulary_id": null | 270 | "vocabulary_id": null | ||
| 300 | } | 271 | } | ||
| 301 | ], | 272 | ], | ||
| 302 | "thematic_area": [ | 273 | "thematic_area": [ | ||
| 303 | "especies_silvestres" | 274 | "especies_silvestres" | ||
| 304 | ], | 275 | ], | ||
| 305 | "theme_es": [ | 276 | "theme_es": [ | ||
| 306 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 277 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 307 | ], | 278 | ], | ||
| 308 | "title": "Spatio-temporal impacts of roads on the persistence of | 279 | "title": "Spatio-temporal impacts of roads on the persistence of | ||
| 309 | populations: analytic and numerical approaches.", | 280 | populations: analytic and numerical approaches.", | ||
| 310 | "title_translated": { | 281 | "title_translated": { | ||
| 311 | "en": "", | 282 | "en": "", | ||
| 312 | "es": "Spatio-temporal impacts of roads on the persistence of | 283 | "es": "Spatio-temporal impacts of roads on the persistence of | ||
| 313 | populations: analytic and numerical approaches." | 284 | populations: analytic and numerical approaches." | ||
| 314 | }, | 285 | }, | ||
| 315 | "topic": | 286 | "topic": | ||
| 316 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 287 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 317 | "type": "dataset", | 288 | "type": "dataset", | ||
| 318 | "url": | 289 | "url": | ||
| 319 | //iepnb.es:443/catalogo/dataset/ba8e23a9-97ec-572d-bca9-f355313d3826", | 290 | //iepnb.es:443/catalogo/dataset/ba8e23a9-97ec-572d-bca9-f355313d3826", | ||
| 320 | "version": "", | 291 | "version": "", | ||
| 321 | "version_notes": { | 292 | "version_notes": { | ||
| 322 | "en": "", | 293 | "en": "", | ||
| 323 | "es": "" | 294 | "es": "" | ||
| 324 | } | 295 | } | ||
| 325 | } | 296 | } |