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a2026-06-25
en The impact of river fragmentation on the population persistence of native and alien mink: An ecological trap for the endangered European mink. -
Modificado el valor del campo
modified
del recurso Acceso al recurso a2026-06-25
(anteriormente2026-06-23
) en The impact of river fragmentation on the population persistence of native and alien mink: An ecological trap for the endangered European mink.
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| 82 | "notes": "The genetic diversity of feral and ranch American mink was | 96 | "notes": "The genetic diversity of feral and ranch American mink was | ||
| 83 | studied in order to detect gene flux among rivers, investigate the | 97 | studied in order to detect gene flux among rivers, investigate the | ||
| 84 | processes of invasion, and determine the possible effects of river | 98 | processes of invasion, and determine the possible effects of river | ||
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| 89 | differentiation between feral and ranch mink was suggested. These | 103 | differentiation between feral and ranch mink was suggested. These | ||
| 90 | results confirm that the mink population established on Butr\u00f3n | 104 | results confirm that the mink population established on Butr\u00f3n | ||
| 91 | River at the beginning of the 1990s may be the origin of almost all | 105 | River at the beginning of the 1990s may be the origin of almost all | ||
| 92 | the feral mink population within the study area. Additionally, the | 106 | the feral mink population within the study area. Additionally, the | ||
| 93 | occurrence of American and European mink was used to analyse the | 107 | occurrence of American and European mink was used to analyse the | ||
| 94 | effect of fragmentation on the population viability. The size and | 108 | effect of fragmentation on the population viability. The size and | ||
| 95 | composition of the home range of male European mink was considered to | 109 | composition of the home range of male European mink was considered to | ||
| 96 | model minimum viable units for presence/absence. Forty-two minimum | 110 | model minimum viable units for presence/absence. Forty-two minimum | ||
| 97 | viable units were randomly distributed among rivers in order to | 111 | viable units were randomly distributed among rivers in order to | ||
| 98 | analyse the effect of fragmentation on mink occurrence. Barriers were | 112 | analyse the effect of fragmentation on mink occurrence. Barriers were | ||
| 99 | mapped and classified as slight, moderate or absolute, depending on | 113 | mapped and classified as slight, moderate or absolute, depending on | ||
| 100 | the effect on mink movement, and were introduced into the models. The | 114 | the effect on mink movement, and were introduced into the models. The | ||
| 101 | presence of European and American mink depended on the non-fragmented | 115 | presence of European and American mink depended on the non-fragmented | ||
| 102 | main river stretches and the number of tributaries free from barriers. | 116 | main river stretches and the number of tributaries free from barriers. | ||
| 103 | Results showed that fragmented rivers can be temporarily occupied but | 117 | Results showed that fragmented rivers can be temporarily occupied but | ||
| 104 | the likelihood of death means that these areas are only sink patches | 118 | the likelihood of death means that these areas are only sink patches | ||
| 105 | for mink.", | 119 | for mink.", | ||
| 106 | "notes_translated": { | 120 | "notes_translated": { | ||
| 107 | "en": "The genetic diversity of feral and ranch American mink was | 121 | "en": "The genetic diversity of feral and ranch American mink was | ||
| 108 | studied in order to detect gene flux among rivers, investigate the | 122 | studied in order to detect gene flux among rivers, investigate the | ||
| 109 | processes of invasion, and determine the possible effects of river | 123 | processes of invasion, and determine the possible effects of river | ||
| 110 | barriers. Tissue samples of 78 feral American mink from 5 different | 124 | barriers. Tissue samples of 78 feral American mink from 5 different | ||
| 111 | river catchments and 18 ranch mink, collected between 2007 and 2011 in | 125 | river catchments and 18 ranch mink, collected between 2007 and 2011 in | ||
| 112 | Biscay, northern Spain, were genotyped at 21 microsatellite loci. Lack | 126 | Biscay, northern Spain, were genotyped at 21 microsatellite loci. Lack | ||
| 113 | of genetic differentiation of feral mink among the sites and high | 127 | of genetic differentiation of feral mink among the sites and high | ||
| 114 | differentiation between feral and ranch mink was suggested. These | 128 | differentiation between feral and ranch mink was suggested. These | ||
| 115 | results confirm that the mink population established on Butr\u00f3n | 129 | results confirm that the mink population established on Butr\u00f3n | ||
| 116 | River at the beginning of the 1990s may be the origin of almost all | 130 | River at the beginning of the 1990s may be the origin of almost all | ||
| 117 | the feral mink population within the study area. Additionally, the | 131 | the feral mink population within the study area. Additionally, the | ||
| 118 | occurrence of American and European mink was used to analyse the | 132 | occurrence of American and European mink was used to analyse the | ||
| 119 | effect of fragmentation on the population viability. The size and | 133 | effect of fragmentation on the population viability. The size and | ||
| 120 | composition of the home range of male European mink was considered to | 134 | composition of the home range of male European mink was considered to | ||
| 121 | model minimum viable units for presence/absence. Forty-two minimum | 135 | model minimum viable units for presence/absence. Forty-two minimum | ||
| 122 | viable units were randomly distributed among rivers in order to | 136 | viable units were randomly distributed among rivers in order to | ||
| 123 | analyse the effect of fragmentation on mink occurrence. Barriers were | 137 | analyse the effect of fragmentation on mink occurrence. Barriers were | ||
| 124 | mapped and classified as slight, moderate or absolute, depending on | 138 | mapped and classified as slight, moderate or absolute, depending on | ||
| 125 | the effect on mink movement, and were introduced into the models. The | 139 | the effect on mink movement, and were introduced into the models. The | ||
| 126 | presence of European and American mink depended on the non-fragmented | 140 | presence of European and American mink depended on the non-fragmented | ||
| 127 | main river stretches and the number of tributaries free from barriers. | 141 | main river stretches and the number of tributaries free from barriers. | ||
| 128 | Results showed that fragmented rivers can be temporarily occupied but | 142 | Results showed that fragmented rivers can be temporarily occupied but | ||
| 129 | the likelihood of death means that these areas are only sink patches | 143 | the likelihood of death means that these areas are only sink patches | ||
| 130 | for mink.", | 144 | for mink.", | ||
| 131 | "es": "The genetic diversity of feral and ranch American mink was | 145 | "es": "The genetic diversity of feral and ranch American mink was | ||
| 132 | studied in order to detect gene flux among rivers, investigate the | 146 | studied in order to detect gene flux among rivers, investigate the | ||
| 133 | processes of invasion, and determine the possible effects of river | 147 | processes of invasion, and determine the possible effects of river | ||
| 134 | barriers. Tissue samples of 78 feral American mink from 5 different | 148 | barriers. Tissue samples of 78 feral American mink from 5 different | ||
| 135 | river catchments and 18 ranch mink, collected between 2007 and 2011 in | 149 | river catchments and 18 ranch mink, collected between 2007 and 2011 in | ||
| 136 | Biscay, northern Spain, were genotyped at 21 microsatellite loci. Lack | 150 | Biscay, northern Spain, were genotyped at 21 microsatellite loci. Lack | ||
| 137 | of genetic differentiation of feral mink among the sites and high | 151 | of genetic differentiation of feral mink among the sites and high | ||
| 138 | differentiation between feral and ranch mink was suggested. These | 152 | differentiation between feral and ranch mink was suggested. These | ||
| 139 | results confirm that the mink population established on Butr\u00f3n | 153 | results confirm that the mink population established on Butr\u00f3n | ||
| 140 | River at the beginning of the 1990s may be the origin of almost all | 154 | River at the beginning of the 1990s may be the origin of almost all | ||
| 141 | the feral mink population within the study area. Additionally, the | 155 | the feral mink population within the study area. Additionally, the | ||
| 142 | occurrence of American and European mink was used to analyse the | 156 | occurrence of American and European mink was used to analyse the | ||
| 143 | effect of fragmentation on the population viability. The size and | 157 | effect of fragmentation on the population viability. The size and | ||
| 144 | composition of the home range of male European mink was considered to | 158 | composition of the home range of male European mink was considered to | ||
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| 146 | viable units were randomly distributed among rivers in order to | 160 | viable units were randomly distributed among rivers in order to | ||
| 147 | analyse the effect of fragmentation on mink occurrence. Barriers were | 161 | analyse the effect of fragmentation on mink occurrence. Barriers were | ||
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| 149 | the effect on mink movement, and were introduced into the models. The | 163 | the effect on mink movement, and were introduced into the models. The | ||
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| 151 | main river stretches and the number of tributaries free from barriers. | 165 | main river stretches and the number of tributaries free from barriers. | ||
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| 269 | "state": "active", | 283 | "state": "active", | ||
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| 278 | { | 292 | { | ||
| 279 | "display_name": "otros-recursos-que-incluyen-informacion-", | 293 | "display_name": "otros-recursos-que-incluyen-informacion-", | ||
| 280 | "id": "2b3610b7-85fe-495c-990a-40e99a432df1", | 294 | "id": "2b3610b7-85fe-495c-990a-40e99a432df1", | ||
| 281 | "name": "otros-recursos-que-incluyen-informacion-", | 295 | "name": "otros-recursos-que-incluyen-informacion-", | ||
| 282 | "state": "active", | 296 | "state": "active", | ||
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| 286 | "thematic_area": [ | 300 | "thematic_area": [ | ||
| 287 | "especies_silvestres" | 301 | "especies_silvestres" | ||
| 288 | ], | 302 | ], | ||
| 289 | "theme_es": [ | 303 | "theme_es": [ | ||
| 290 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 304 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 291 | ], | 305 | ], | ||
| 292 | "title": "The impact of river fragmentation on the population | 306 | "title": "The impact of river fragmentation on the population | ||
| 293 | persistence of native and alien mink: An ecological trap for the | 307 | persistence of native and alien mink: An ecological trap for the | ||
| 294 | endangered European mink.", | 308 | endangered European mink.", | ||
| 295 | "title_translated": { | 309 | "title_translated": { | ||
| 296 | "en": "", | 310 | "en": "", | ||
| 297 | "es": "The impact of river fragmentation on the population | 311 | "es": "The impact of river fragmentation on the population | ||
| 298 | persistence of native and alien mink: An ecological trap for the | 312 | persistence of native and alien mink: An ecological trap for the | ||
| 299 | endangered European mink." | 313 | endangered European mink." | ||
| 300 | }, | 314 | }, | ||
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| 303 | "type": "dataset", | 317 | "type": "dataset", | ||
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| 305 | //iepnb.es:443/catalogo/dataset/32031405-8793-5059-8b65-be392ad09b65", | 319 | //iepnb.es:443/catalogo/dataset/32031405-8793-5059-8b65-be392ad09b65", | ||
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| 309 | "es": "" | 323 | "es": "" | ||
| 310 | } | 324 | } | ||
| 311 | } | 325 | } |