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En el instante 23 de junio de 2026, 16:12:36 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 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 | 99 | "notes": "The potential negative influence of the seaweed Caulerpa | ||
| 100 | prolifera on the seagrass Cymodocea nodosa was explored in a | 100 | prolifera on the seagrass Cymodocea nodosa was explored in a | ||
| 101 | Mediterranean coastal lagoon (Mar Menor, Spain) where the alga | 101 | Mediterranean coastal lagoon (Mar Menor, Spain) where the alga | ||
| 102 | suddenly and rapidly spread four decades ago. An extensive field | 102 | suddenly and rapidly spread four decades ago. An extensive field | ||
| 103 | sampling was carried out across the lagoon to characterise the | 103 | sampling was carried out across the lagoon to characterise the | ||
| 104 | distribution and abundance of both macrophytes at different spatial | 104 | distribution and abundance of both macrophytes at different spatial | ||
| 105 | scales, as well as sediment characteristics. Generalised linear and | 105 | scales, as well as sediment characteristics. Generalised linear and | ||
| 106 | additive models were performed at the whole-lagoon scale, for deep and | 106 | additive models were performed at the whole-lagoon scale, for deep and | ||
| 107 | shallow bottoms, independently, to explore factors influencing C. | 107 | shallow bottoms, independently, to explore factors influencing C. | ||
| 108 | nodosa distribution and abundance. A high-spatial-resolution | 108 | nodosa distribution and abundance. A high-spatial-resolution | ||
| 109 | macrophyte distribution map was also generated by integrating | 109 | macrophyte distribution map was also generated by integrating | ||
| 110 | underwater imaging, direct visualisations and orthophotographs. This | 110 | underwater imaging, direct visualisations and orthophotographs. This | ||
| 111 | map showed that both macrophytes largely dominated the ecosystem but | 111 | map showed that both macrophytes largely dominated the ecosystem but | ||
| 112 | with opposing depth patterns of abundance that mainly reflected their | 112 | with opposing depth patterns of abundance that mainly reflected their | ||
| 113 | specific light requirements. C. nodosa was dominant at shallow depths | 113 | specific light requirements. C. nodosa was dominant at shallow depths | ||
| 114 | but also grew intermingled with a dense C. prolifera bed over large | 114 | but also grew intermingled with a dense C. prolifera bed over large | ||
| 115 | areas of the deep seafloor with highly anoxic muddy sediments. Models | 115 | areas of the deep seafloor with highly anoxic muddy sediments. Models | ||
| 116 | did not reveal overall negative relationships between the macrophytes, | 116 | did not reveal overall negative relationships between the macrophytes, | ||
| 117 | indicating that C. prolifera was not the main driver of C. nodosa | 117 | indicating that C. prolifera was not the main driver of C. nodosa | ||
| 118 | distribution and abundance in this coastal lagoon. Findings | 118 | distribution and abundance in this coastal lagoon. Findings | ||
| 119 | highlighted the absence of a negative direct or indirect influence of | 119 | highlighted the absence of a negative direct or indirect influence of | ||
| 120 | C. prolifera on C. nodosa, as supported by the fact that the | 120 | C. prolifera on C. nodosa, as supported by the fact that the | ||
| 121 | distributions of both macrophytes were similar to those reported in | 121 | distributions of both macrophytes were similar to those reported in | ||
| 122 | the 1980s, just a few years after C. prolifera had spread in the | 122 | the 1980s, just a few years after C. prolifera had spread in the | ||
| 123 | lagoon. We conclude, therefore, that C. prolifera is not progressively | 123 | lagoon. We conclude, therefore, that C. prolifera is not progressively | ||
| 124 | replacing C. nodosa in this ecosystem, where both species have | 124 | replacing C. nodosa in this ecosystem, where both species have | ||
| 125 | coexisted for decades.", | 125 | coexisted for decades.", | ||
| 126 | "notes_translated": { | 126 | "notes_translated": { | ||
| 127 | "es": "The potential negative influence of the seaweed Caulerpa | 127 | "es": "The potential negative influence of the seaweed Caulerpa | ||
| 128 | prolifera on the seagrass Cymodocea nodosa was explored in a | 128 | prolifera on the seagrass Cymodocea nodosa was explored in a | ||
| 129 | Mediterranean coastal lagoon (Mar Menor, Spain) where the alga | 129 | Mediterranean coastal lagoon (Mar Menor, Spain) where the alga | ||
| 130 | suddenly and rapidly spread four decades ago. An extensive field | 130 | suddenly and rapidly spread four decades ago. An extensive field | ||
| 131 | sampling was carried out across the lagoon to characterise the | 131 | sampling was carried out across the lagoon to characterise the | ||
| 132 | distribution and abundance of both macrophytes at different spatial | 132 | distribution and abundance of both macrophytes at different spatial | ||
| 133 | scales, as well as sediment characteristics. Generalised linear and | 133 | scales, as well as sediment characteristics. Generalised linear and | ||
| 134 | additive models were performed at the whole-lagoon scale, for deep and | 134 | additive models were performed at the whole-lagoon scale, for deep and | ||
| 135 | shallow bottoms, independently, to explore factors influencing C. | 135 | shallow bottoms, independently, to explore factors influencing C. | ||
| 136 | nodosa distribution and abundance. A high-spatial-resolution | 136 | nodosa distribution and abundance. A high-spatial-resolution | ||
| 137 | macrophyte distribution map was also generated by integrating | 137 | macrophyte distribution map was also generated by integrating | ||
| 138 | underwater imaging, direct visualisations and orthophotographs. This | 138 | underwater imaging, direct visualisations and orthophotographs. This | ||
| 139 | map showed that both macrophytes largely dominated the ecosystem but | 139 | map showed that both macrophytes largely dominated the ecosystem but | ||
| 140 | with opposing depth patterns of abundance that mainly reflected their | 140 | with opposing depth patterns of abundance that mainly reflected their | ||
| 141 | specific light requirements. C. nodosa was dominant at shallow depths | 141 | specific light requirements. C. nodosa was dominant at shallow depths | ||
| 142 | but also grew intermingled with a dense C. prolifera bed over large | 142 | but also grew intermingled with a dense C. prolifera bed over large | ||
| 143 | areas of the deep seafloor with highly anoxic muddy sediments. Models | 143 | areas of the deep seafloor with highly anoxic muddy sediments. Models | ||
| 144 | did not reveal overall negative relationships between the macrophytes, | 144 | did not reveal overall negative relationships between the macrophytes, | ||
| 145 | indicating that C. prolifera was not the main driver of C. nodosa | 145 | indicating that C. prolifera was not the main driver of C. nodosa | ||
| 146 | distribution and abundance in this coastal lagoon. Findings | 146 | distribution and abundance in this coastal lagoon. Findings | ||
| 147 | highlighted the absence of a negative direct or indirect influence of | 147 | highlighted the absence of a negative direct or indirect influence of | ||
| 148 | C. prolifera on C. nodosa, as supported by the fact that the | 148 | C. prolifera on C. nodosa, as supported by the fact that the | ||
| 149 | distributions of both macrophytes were similar to those reported in | 149 | distributions of both macrophytes were similar to those reported in | ||
| 150 | the 1980s, just a few years after C. prolifera had spread in the | 150 | the 1980s, just a few years after C. prolifera had spread in the | ||
| 151 | lagoon. We conclude, therefore, that C. prolifera is not progressively | 151 | lagoon. We conclude, therefore, that C. prolifera is not progressively | ||
| 152 | replacing C. nodosa in this ecosystem, where both species have | 152 | replacing C. nodosa in this ecosystem, where both species have | ||
| 153 | coexisted for decades." | 153 | coexisted for decades." | ||
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| 366 | prolifera and the seagrass Cymodocea nodosa in a Mediterranean | 337 | prolifera and the seagrass Cymodocea nodosa in a Mediterranean | ||
| 367 | lagoon", | 338 | lagoon", | ||
| 368 | "title_translated": { | 339 | "title_translated": { | ||
| 369 | "es": "Long-term coexistence between the macroalga Caulerpa | 340 | "es": "Long-term coexistence between the macroalga Caulerpa | ||
| 370 | prolifera and the seagrass Cymodocea nodosa in a Mediterranean lagoon" | 341 | prolifera and the seagrass Cymodocea nodosa in a Mediterranean lagoon" | ||
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| 377 | "version_notes": { | 348 | "version_notes": { | ||
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| 379 | } | 350 | } | ||
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