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Modificado el valor del campo
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en Long-term coexistence between the macroalga Caulerpa prolifera and the seagrass Cymodocea nodosa in a Mediterranean lagoon -
Modificado el valor del campo
modified
del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Long-term coexistence between the macroalga Caulerpa prolifera and the seagrass Cymodocea nodosa in a Mediterranean lagoon
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| 99 | "notes": "The potential negative influence of the seaweed Caulerpa | 109 | "notes": "The potential negative influence of the seaweed Caulerpa | ||
| 100 | prolifera on the seagrass Cymodocea nodosa was explored in a | 110 | prolifera on the seagrass Cymodocea nodosa was explored in a | ||
| 101 | Mediterranean coastal lagoon (Mar Menor, Spain) where the alga | 111 | Mediterranean coastal lagoon (Mar Menor, Spain) where the alga | ||
| 102 | suddenly and rapidly spread four decades ago. An extensive field | 112 | suddenly and rapidly spread four decades ago. An extensive field | ||
| 103 | sampling was carried out across the lagoon to characterise the | 113 | sampling was carried out across the lagoon to characterise the | ||
| 104 | distribution and abundance of both macrophytes at different spatial | 114 | distribution and abundance of both macrophytes at different spatial | ||
| 105 | scales, as well as sediment characteristics. Generalised linear and | 115 | scales, as well as sediment characteristics. Generalised linear and | ||
| 106 | additive models were performed at the whole-lagoon scale, for deep and | 116 | additive models were performed at the whole-lagoon scale, for deep and | ||
| 107 | shallow bottoms, independently, to explore factors influencing C. | 117 | shallow bottoms, independently, to explore factors influencing C. | ||
| 108 | nodosa distribution and abundance. A high-spatial-resolution | 118 | nodosa distribution and abundance. A high-spatial-resolution | ||
| 109 | macrophyte distribution map was also generated by integrating | 119 | macrophyte distribution map was also generated by integrating | ||
| 110 | underwater imaging, direct visualisations and orthophotographs. This | 120 | underwater imaging, direct visualisations and orthophotographs. This | ||
| 111 | map showed that both macrophytes largely dominated the ecosystem but | 121 | map showed that both macrophytes largely dominated the ecosystem but | ||
| 112 | with opposing depth patterns of abundance that mainly reflected their | 122 | with opposing depth patterns of abundance that mainly reflected their | ||
| 113 | specific light requirements. C. nodosa was dominant at shallow depths | 123 | specific light requirements. C. nodosa was dominant at shallow depths | ||
| 114 | but also grew intermingled with a dense C. prolifera bed over large | 124 | but also grew intermingled with a dense C. prolifera bed over large | ||
| 115 | areas of the deep seafloor with highly anoxic muddy sediments. Models | 125 | areas of the deep seafloor with highly anoxic muddy sediments. Models | ||
| 116 | did not reveal overall negative relationships between the macrophytes, | 126 | did not reveal overall negative relationships between the macrophytes, | ||
| 117 | indicating that C. prolifera was not the main driver of C. nodosa | 127 | indicating that C. prolifera was not the main driver of C. nodosa | ||
| 118 | distribution and abundance in this coastal lagoon. Findings | 128 | distribution and abundance in this coastal lagoon. Findings | ||
| 119 | highlighted the absence of a negative direct or indirect influence of | 129 | highlighted the absence of a negative direct or indirect influence of | ||
| 120 | C. prolifera on C. nodosa, as supported by the fact that the | 130 | C. prolifera on C. nodosa, as supported by the fact that the | ||
| 121 | distributions of both macrophytes were similar to those reported in | 131 | distributions of both macrophytes were similar to those reported in | ||
| 122 | the 1980s, just a few years after C. prolifera had spread in the | 132 | the 1980s, just a few years after C. prolifera had spread in the | ||
| 123 | lagoon. We conclude, therefore, that C. prolifera is not progressively | 133 | lagoon. We conclude, therefore, that C. prolifera is not progressively | ||
| 124 | replacing C. nodosa in this ecosystem, where both species have | 134 | replacing C. nodosa in this ecosystem, where both species have | ||
| 125 | coexisted for decades.", | 135 | coexisted for decades.", | ||
| 126 | "notes_translated": { | 136 | "notes_translated": { | ||
| 127 | "es": "The potential negative influence of the seaweed Caulerpa | 137 | "es": "The potential negative influence of the seaweed Caulerpa | ||
| 128 | prolifera on the seagrass Cymodocea nodosa was explored in a | 138 | prolifera on the seagrass Cymodocea nodosa was explored in a | ||
| 129 | Mediterranean coastal lagoon (Mar Menor, Spain) where the alga | 139 | Mediterranean coastal lagoon (Mar Menor, Spain) where the alga | ||
| 130 | suddenly and rapidly spread four decades ago. An extensive field | 140 | suddenly and rapidly spread four decades ago. An extensive field | ||
| 131 | sampling was carried out across the lagoon to characterise the | 141 | sampling was carried out across the lagoon to characterise the | ||
| 132 | distribution and abundance of both macrophytes at different spatial | 142 | distribution and abundance of both macrophytes at different spatial | ||
| 133 | scales, as well as sediment characteristics. Generalised linear and | 143 | scales, as well as sediment characteristics. Generalised linear and | ||
| 134 | additive models were performed at the whole-lagoon scale, for deep and | 144 | additive models were performed at the whole-lagoon scale, for deep and | ||
| 135 | shallow bottoms, independently, to explore factors influencing C. | 145 | shallow bottoms, independently, to explore factors influencing C. | ||
| 136 | nodosa distribution and abundance. A high-spatial-resolution | 146 | nodosa distribution and abundance. A high-spatial-resolution | ||
| 137 | macrophyte distribution map was also generated by integrating | 147 | macrophyte distribution map was also generated by integrating | ||
| 138 | underwater imaging, direct visualisations and orthophotographs. This | 148 | underwater imaging, direct visualisations and orthophotographs. This | ||
| 139 | map showed that both macrophytes largely dominated the ecosystem but | 149 | map showed that both macrophytes largely dominated the ecosystem but | ||
| 140 | with opposing depth patterns of abundance that mainly reflected their | 150 | with opposing depth patterns of abundance that mainly reflected their | ||
| 141 | specific light requirements. C. nodosa was dominant at shallow depths | 151 | specific light requirements. C. nodosa was dominant at shallow depths | ||
| 142 | but also grew intermingled with a dense C. prolifera bed over large | 152 | but also grew intermingled with a dense C. prolifera bed over large | ||
| 143 | areas of the deep seafloor with highly anoxic muddy sediments. Models | 153 | areas of the deep seafloor with highly anoxic muddy sediments. Models | ||
| 144 | did not reveal overall negative relationships between the macrophytes, | 154 | did not reveal overall negative relationships between the macrophytes, | ||
| 145 | indicating that C. prolifera was not the main driver of C. nodosa | 155 | indicating that C. prolifera was not the main driver of C. nodosa | ||
| 146 | distribution and abundance in this coastal lagoon. Findings | 156 | distribution and abundance in this coastal lagoon. Findings | ||
| 147 | highlighted the absence of a negative direct or indirect influence of | 157 | highlighted the absence of a negative direct or indirect influence of | ||
| 148 | C. prolifera on C. nodosa, as supported by the fact that the | 158 | C. prolifera on C. nodosa, as supported by the fact that the | ||
| 149 | distributions of both macrophytes were similar to those reported in | 159 | distributions of both macrophytes were similar to those reported in | ||
| 150 | the 1980s, just a few years after C. prolifera had spread in the | 160 | the 1980s, just a few years after C. prolifera had spread in the | ||
| 151 | lagoon. We conclude, therefore, that C. prolifera is not progressively | 161 | lagoon. We conclude, therefore, that C. prolifera is not progressively | ||
| 152 | replacing C. nodosa in this ecosystem, where both species have | 162 | replacing C. nodosa in this ecosystem, where both species have | ||
| 153 | coexisted for decades." | 163 | coexisted for decades." | ||
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| 335 | ], | 345 | ], | ||
| 336 | "title": "Long-term coexistence between the macroalga Caulerpa | 346 | "title": "Long-term coexistence between the macroalga Caulerpa | ||
| 337 | prolifera and the seagrass Cymodocea nodosa in a Mediterranean | 347 | prolifera and the seagrass Cymodocea nodosa in a Mediterranean | ||
| 338 | lagoon", | 348 | lagoon", | ||
| 339 | "title_translated": { | 349 | "title_translated": { | ||
| 340 | "es": "Long-term coexistence between the macroalga Caulerpa | 350 | "es": "Long-term coexistence between the macroalga Caulerpa | ||
| 341 | prolifera and the seagrass Cymodocea nodosa in a Mediterranean lagoon" | 351 | prolifera and the seagrass Cymodocea nodosa in a Mediterranean lagoon" | ||
| 342 | }, | 352 | }, | ||
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| 344 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | 354 | "http://inspire.ec.europa.eu/metadata-codelist/TopicCategory/biota", | ||
| 345 | "type": "dataset", | 355 | "type": "dataset", | ||
| 346 | "url": | 356 | "url": | ||
| 347 | //iepnb.es:443/catalogo/dataset/1ce5c56d-61f0-5bc9-8d21-c45c485079de", | 357 | //iepnb.es:443/catalogo/dataset/1ce5c56d-61f0-5bc9-8d21-c45c485079de", | ||
| 348 | "version_notes": { | 358 | "version_notes": { | ||
| 349 | "es": "" | 359 | "es": "" | ||
| 350 | } | 360 | } | ||
| 351 | } | 361 | } |