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en Determinants of wintering waterbird changes in a Mediterranean coastal lagoon affected by eutrophication -
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) en Determinants of wintering waterbird changes in a Mediterranean coastal lagoon affected by eutrophication
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| 96 | "notes": "Southern Mediterranean lagoons are among the more | 106 | "notes": "Southern Mediterranean lagoons are among the more | ||
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| 98 | tourism, urbanization) leading to eutrophication. We analyse the | 108 | tourism, urbanization) leading to eutrophication. We analyse the | ||
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| 100 | environmental variables (nutrient load, fish production, jellyfish | 110 | environmental variables (nutrient load, fish production, jellyfish | ||
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| 103 | trophic status of the wetland. We use GLMs to relate the biomass of | 113 | trophic status of the wetland. We use GLMs to relate the biomass of | ||
| 104 | the five most abundant and representative waterbird species to these | 114 | the five most abundant and representative waterbird species to these | ||
| 105 | variables, accounting for the potential influence of external factors | 115 | variables, accounting for the potential influence of external factors | ||
| 106 | affecting their population at higher biogeographical scales. A | 116 | affecting their population at higher biogeographical scales. A | ||
| 107 | significant effect of such factors was only found for Great Cormorant, | 117 | significant effect of such factors was only found for Great Cormorant, | ||
| 108 | which biased the positive response of the piscivore guild to nutrient | 118 | which biased the positive response of the piscivore guild to nutrient | ||
| 109 | load (NLD). Red-breasted Merganser appeared relatively insensitive to | 119 | load (NLD). Red-breasted Merganser appeared relatively insensitive to | ||
| 110 | nutrient enrichment, although declined in the long term. The remaining | 120 | nutrient enrichment, although declined in the long term. The remaining | ||
| 111 | species responded positively. NLD being a significant predictor of | 121 | species responded positively. NLD being a significant predictor of | ||
| 112 | their biomass when a 2-year lag was allowed, although this variable | 122 | their biomass when a 2-year lag was allowed, although this variable | ||
| 113 | alone had a low explanatory power except for the Coot. When | 123 | alone had a low explanatory power except for the Coot. When | ||
| 114 | homogeneous temporal phases were defined, grebes could be identified | 124 | homogeneous temporal phases were defined, grebes could be identified | ||
| 115 | as early warners of eutrophication, and Coot as late-stage ones. The | 125 | as early warners of eutrophication, and Coot as late-stage ones. The | ||
| 116 | increase of piscivores along a period of declining fish catches could | 126 | increase of piscivores along a period of declining fish catches could | ||
| 117 | reflect a shift in fish community composition or structure that | 127 | reflect a shift in fish community composition or structure that | ||
| 118 | favours their feeding preferences.", | 128 | favours their feeding preferences.", | ||
| 119 | "notes_translated": { | 129 | "notes_translated": { | ||
| 120 | "es": "Southern Mediterranean lagoons are among the more | 130 | "es": "Southern Mediterranean lagoons are among the more | ||
| 121 | vulnerable systems regarding human activities (e.g. agriculture, | 131 | vulnerable systems regarding human activities (e.g. agriculture, | ||
| 122 | tourism, urbanization) leading to eutrophication. We analyse the | 132 | tourism, urbanization) leading to eutrophication. We analyse the | ||
| 123 | relationship of water-birds with locally measured or modelled | 133 | relationship of water-birds with locally measured or modelled | ||
| 124 | environmental variables (nutrient load, fish production, jellyfish | 134 | environmental variables (nutrient load, fish production, jellyfish | ||
| 125 | blooms) related with this process, in the Mar Menor lagoon (Murcia, SE | 135 | blooms) related with this process, in the Mar Menor lagoon (Murcia, SE | ||
| 126 | Spain), and discuss the potential value of birds as indicators of the | 136 | Spain), and discuss the potential value of birds as indicators of the | ||
| 127 | trophic status of the wetland. We use GLMs to relate the biomass of | 137 | trophic status of the wetland. We use GLMs to relate the biomass of | ||
| 128 | the five most abundant and representative waterbird species to these | 138 | the five most abundant and representative waterbird species to these | ||
| 129 | variables, accounting for the potential influence of external factors | 139 | variables, accounting for the potential influence of external factors | ||
| 130 | affecting their population at higher biogeographical scales. A | 140 | affecting their population at higher biogeographical scales. A | ||
| 131 | significant effect of such factors was only found for Great Cormorant, | 141 | significant effect of such factors was only found for Great Cormorant, | ||
| 132 | which biased the positive response of the piscivore guild to nutrient | 142 | which biased the positive response of the piscivore guild to nutrient | ||
| 133 | load (NLD). Red-breasted Merganser appeared relatively insensitive to | 143 | load (NLD). Red-breasted Merganser appeared relatively insensitive to | ||
| 134 | nutrient enrichment, although declined in the long term. The remaining | 144 | nutrient enrichment, although declined in the long term. The remaining | ||
| 135 | species responded positively. NLD being a significant predictor of | 145 | species responded positively. NLD being a significant predictor of | ||
| 136 | their biomass when a 2-year lag was allowed, although this variable | 146 | their biomass when a 2-year lag was allowed, although this variable | ||
| 137 | alone had a low explanatory power except for the Coot. When | 147 | alone had a low explanatory power except for the Coot. When | ||
| 138 | homogeneous temporal phases were defined, grebes could be identified | 148 | homogeneous temporal phases were defined, grebes could be identified | ||
| 139 | as early warners of eutrophication, and Coot as late-stage ones. The | 149 | as early warners of eutrophication, and Coot as late-stage ones. The | ||
| 140 | increase of piscivores along a period of declining fish catches could | 150 | increase of piscivores along a period of declining fish catches could | ||
| 141 | reflect a shift in fish community composition or structure that | 151 | reflect a shift in fish community composition or structure that | ||
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| 238 | 37.38]]]}", | 248 | 37.38]]]}", | ||
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| 246 | "text": "Regi\u00f3n de Murcia", | 256 | "text": "Regi\u00f3n de Murcia", | ||
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| 248 | atos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia" | 258 | atos.gob.es/recurso/sector-publico/territorio/Autonomia/Region-Murcia" | ||
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| 258 | 268 | ||||
| 259 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | 269 | tp://inspire.ec.europa.eu/metadata-codelist/TopicCategory/environment" | ||
| 260 | ], | 270 | ], | ||
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| 262 | { | 272 | { | ||
| 263 | "display_name": "amenazas", | 273 | "display_name": "amenazas", | ||
| 264 | "id": "9532991a-ec15-4a7c-b7f9-8ec12fcd335d", | 274 | "id": "9532991a-ec15-4a7c-b7f9-8ec12fcd335d", | ||
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| 271 | "id": "074e8d16-47c0-4913-88d6-220cfb4a4e94", | 281 | "id": "074e8d16-47c0-4913-88d6-220cfb4a4e94", | ||
| 272 | "name": "aves", | 282 | "name": "aves", | ||
| 273 | "state": "active", | 283 | "state": "active", | ||
| 274 | "vocabulary_id": null | 284 | "vocabulary_id": null | ||
| 275 | }, | 285 | }, | ||
| 276 | { | 286 | { | ||
| 277 | "display_name": "contaminacion", | 287 | "display_name": "contaminacion", | ||
| 278 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | 288 | "id": "49a55c88-74b7-4e72-ab38-19a1e2b3904f", | ||
| 279 | "name": "contaminacion", | 289 | "name": "contaminacion", | ||
| 280 | "state": "active", | 290 | "state": "active", | ||
| 281 | "vocabulary_id": null | 291 | "vocabulary_id": null | ||
| 282 | }, | 292 | }, | ||
| 283 | { | 293 | { | ||
| 284 | "display_name": "diversidad", | 294 | "display_name": "diversidad", | ||
| 285 | "id": "34ab7b9c-f2e0-47ad-aab4-69c31e8d0e14", | 295 | "id": "34ab7b9c-f2e0-47ad-aab4-69c31e8d0e14", | ||
| 286 | "name": "diversidad", | 296 | "name": "diversidad", | ||
| 287 | "state": "active", | 297 | "state": "active", | ||
| 288 | "vocabulary_id": null | 298 | "vocabulary_id": null | ||
| 289 | }, | 299 | }, | ||
| 290 | { | 300 | { | ||
| 291 | "display_name": "eutrofizacion", | 301 | "display_name": "eutrofizacion", | ||
| 292 | "id": "5fcdd244-0f78-4801-be7d-5a67c5bb55ec", | 302 | "id": "5fcdd244-0f78-4801-be7d-5a67c5bb55ec", | ||
| 293 | "name": "eutrofizacion", | 303 | "name": "eutrofizacion", | ||
| 294 | "state": "active", | 304 | "state": "active", | ||
| 295 | "vocabulary_id": null | 305 | "vocabulary_id": null | ||
| 296 | }, | 306 | }, | ||
| 297 | { | 307 | { | ||
| 298 | "display_name": "impacto_ambiental", | 308 | "display_name": "impacto_ambiental", | ||
| 299 | "id": "ae13116e-bbc3-450c-a498-d779feb6c792", | 309 | "id": "ae13116e-bbc3-450c-a498-d779feb6c792", | ||
| 300 | "name": "impacto_ambiental", | 310 | "name": "impacto_ambiental", | ||
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| 302 | "vocabulary_id": null | 312 | "vocabulary_id": null | ||
| 303 | }, | 313 | }, | ||
| 304 | { | 314 | { | ||
| 305 | "display_name": "lagunas-costeras-salobres-saladas", | 315 | "display_name": "lagunas-costeras-salobres-saladas", | ||
| 306 | "id": "92dd4d50-2752-4df9-8eeb-64128064bda8", | 316 | "id": "92dd4d50-2752-4df9-8eeb-64128064bda8", | ||
| 307 | "name": "lagunas-costeras-salobres-saladas", | 317 | "name": "lagunas-costeras-salobres-saladas", | ||
| 308 | "state": "active", | 318 | "state": "active", | ||
| 309 | "vocabulary_id": null | 319 | "vocabulary_id": null | ||
| 310 | }, | 320 | }, | ||
| 311 | { | 321 | { | ||
| 312 | "display_name": "marino", | 322 | "display_name": "marino", | ||
| 313 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | 323 | "id": "004084d1-68d8-46ca-842a-c10278540bc9", | ||
| 314 | "name": "marino", | 324 | "name": "marino", | ||
| 315 | "state": "active", | 325 | "state": "active", | ||
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| 317 | } | 327 | } | ||
| 318 | ], | 328 | ], | ||
| 319 | "thematic_area": [ | 329 | "thematic_area": [ | ||
| 320 | "espacios_protegidos" | 330 | "espacios_protegidos" | ||
| 321 | ], | 331 | ], | ||
| 322 | "theme_es": [ | 332 | "theme_es": [ | ||
| 323 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 333 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 324 | ], | 334 | ], | ||
| 325 | "title": "Determinants of wintering waterbird changes in a | 335 | "title": "Determinants of wintering waterbird changes in a | ||
| 326 | Mediterranean coastal lagoon affected by eutrophication", | 336 | Mediterranean coastal lagoon affected by eutrophication", | ||
| 327 | "title_translated": { | 337 | "title_translated": { | ||
| 328 | "es": "Determinants of wintering waterbird changes in a | 338 | "es": "Determinants of wintering waterbird changes in a | ||
| 329 | Mediterranean coastal lagoon affected by eutrophication" | 339 | Mediterranean coastal lagoon affected by eutrophication" | ||
| 330 | }, | 340 | }, | ||
| 331 | "topic": | 341 | "topic": | ||
| 332 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 342 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 333 | "type": "dataset", | 343 | "type": "dataset", | ||
| 334 | "url": | 344 | "url": | ||
| 335 | //iepnb.es:443/catalogo/dataset/cebc061b-e219-5fc6-80f9-8bfdbf26ad43", | 345 | //iepnb.es:443/catalogo/dataset/cebc061b-e219-5fc6-80f9-8bfdbf26ad43", | ||
| 336 | "version_notes": { | 346 | "version_notes": { | ||
| 337 | "es": "" | 347 | "es": "" | ||
| 338 | } | 348 | } | ||
| 339 | } | 349 | } |