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En el instante 23 de junio de 2026, 16:14:24 UTC,
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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 Fish Assemblage Response to Eutrophic-Mediated Environmental Stress Events in the Mar Menor Coastal Lagoon (SE of Spain)
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| 8 | "author": "Zamora-L\u00f3pez, A., Guerrero-G\u00f3mez, A., Torralva, | 8 | "author": "Zamora-L\u00f3pez, A., Guerrero-G\u00f3mez, A., Torralva, | ||
| 9 | M., Zamora-Mar\u00edn, J.M., Guill\u00e9n-Beltr\u00e1n, A., | 9 | M., Zamora-Mar\u00edn, J.M., Guill\u00e9n-Beltr\u00e1n, A., | ||
| 10 | L\u00f3pez-Mart\u00ednez de la Plaza, P. y Oliva-Paterna, F.J.", | 10 | L\u00f3pez-Mart\u00ednez de la Plaza, P. y Oliva-Paterna, F.J.", | ||
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| 12 | "author_name": "Zamora-L\u00f3pez, A., Guerrero-G\u00f3mez, A., | 12 | "author_name": "Zamora-L\u00f3pez, A., Guerrero-G\u00f3mez, A., | ||
| 13 | Torralva, M., Zamora-Mar\u00edn, J.M., Guill\u00e9n-Beltr\u00e1n, A., | 13 | Torralva, M., Zamora-Mar\u00edn, J.M., Guill\u00e9n-Beltr\u00e1n, A., | ||
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| 39 | "created": "2024-11-05", | 39 | "created": "2024-11-05", | ||
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| 42 | "email": "antonio.zamora2@um.es", | 42 | "email": "antonio.zamora2@um.es", | ||
| 43 | "name": "Zamora-L\u00f3pez, A., Guerrero-G\u00f3mez, A., | 43 | "name": "Zamora-L\u00f3pez, A., Guerrero-G\u00f3mez, A., | ||
| 44 | Torralva, M., Zamora-Mar\u00edn, J.M., Guill\u00e9n-Beltr\u00e1n, A., | 44 | Torralva, M., Zamora-Mar\u00edn, J.M., Guill\u00e9n-Beltr\u00e1n, A., | ||
| 45 | L\u00f3pez-Mart\u00ednez de la Plaza, P. y Oliva-Paterna, F.J." | 45 | L\u00f3pez-Mart\u00ednez de la Plaza, P. y Oliva-Paterna, F.J." | ||
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| 50 | "dcat_type": "http://id.loc.gov/vocabulary/marcgt/art", | 50 | "dcat_type": "http://id.loc.gov/vocabulary/marcgt/art", | ||
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| 72 | "license_title": "Creative Commons Attribution", | 72 | "license_title": "Creative Commons Attribution", | ||
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| 74 | "lineage_source": [ | 74 | "lineage_source": [ | ||
| 75 | "Biology and life sciences forum", | 75 | "Biology and life sciences forum", | ||
| 76 | "vol 13", | 76 | "vol 13", | ||
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| n | 82 | "metadata_modified": "2026-06-23T15:01:27.701005", | n | 82 | "metadata_modified": "2026-06-23T16:14:24.048878", |
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| 86 | "miteco_data_population": { | 86 | "miteco_data_population": { | ||
| 87 | "es": "" | 87 | "es": "" | ||
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| 89 | "miteco_data_territory": { | 89 | "miteco_data_territory": { | ||
| 90 | "es": "" | 90 | "es": "" | ||
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| 92 | "miteco_dataset_type": | 92 | "miteco_dataset_type": | ||
| 93 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | 93 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | ||
| 94 | "miteco_geo_level": "1", | 94 | "miteco_geo_level": "1", | ||
| 95 | "modified": "2026-06-23", | 95 | "modified": "2026-06-23", | ||
| 96 | "name": "040d4856-b83f-5f07-ad34-1077c0a79a3a", | 96 | "name": "040d4856-b83f-5f07-ad34-1077c0a79a3a", | ||
| 97 | "notes": "In the last two decades, the extensive development of | 97 | "notes": "In the last two decades, the extensive development of | ||
| 98 | intensive irrigated agriculture around the Mar Menor coastal lagoon | 98 | intensive irrigated agriculture around the Mar Menor coastal lagoon | ||
| 99 | (SE Iberian Peninsula) has disturbed the characteristics of this | 99 | (SE Iberian Peninsula) has disturbed the characteristics of this | ||
| 100 | initially oligotrophic ecosystem. The organic pollution that flows | 100 | initially oligotrophic ecosystem. The organic pollution that flows | ||
| 101 | into the lagoon from agriculture and, to a lesser extent, from urban | 101 | into the lagoon from agriculture and, to a lesser extent, from urban | ||
| 102 | wastewater, has triggered the eutrophication of the system, resulting | 102 | wastewater, has triggered the eutrophication of the system, resulting | ||
| 103 | in dystrophic crises and mass mortality events of aquatic fauna. In | 103 | in dystrophic crises and mass mortality events of aquatic fauna. In | ||
| 104 | order to explore temporal changes in the ecological quality of the | 104 | order to explore temporal changes in the ecological quality of the | ||
| 105 | shallow areas of the Mar Menor, fish assemblage parameters have been | 105 | shallow areas of the Mar Menor, fish assemblage parameters have been | ||
| 106 | obtained and integrated into a multimetric fish index (modified-EMFI). | 106 | obtained and integrated into a multimetric fish index (modified-EMFI). | ||
| 107 | A total of 18 sampling sites around the lagoon perimeter were | 107 | A total of 18 sampling sites around the lagoon perimeter were | ||
| 108 | seasonally assessed. Seasonal sampling was carried out in three | 108 | seasonally assessed. Seasonal sampling was carried out in three | ||
| 109 | two-years periods: (a) the reference period (2002\u20132004); (b) the | 109 | two-years periods: (a) the reference period (2002\u20132004); (b) the | ||
| 110 | critical eutrophic first period (2018\u20132019); and (c) the critical | 110 | critical eutrophic first period (2018\u20132019); and (c) the critical | ||
| 111 | eutrophic second period with multispecies mass mortality events | 111 | eutrophic second period with multispecies mass mortality events | ||
| 112 | (2020\u20132021). The effect of sampling-site confinement (three | 112 | (2020\u20132021). The effect of sampling-site confinement (three | ||
| 113 | levels of water-renewal time) and the degree of anthropic pressure on | 113 | levels of water-renewal time) and the degree of anthropic pressure on | ||
| 114 | shallow areas were evaluated. Despite the magnitude of the | 114 | shallow areas were evaluated. Despite the magnitude of the | ||
| 115 | eutrophication impact on the lagoon, the shallow areas\u2019 | 115 | eutrophication impact on the lagoon, the shallow areas\u2019 | ||
| 116 | ecological quality (according to the modified-EMFI) did not show a | 116 | ecological quality (according to the modified-EMFI) did not show a | ||
| 117 | drastic drop. Nevertheless, significantly lower values were detected | 117 | drastic drop. Nevertheless, significantly lower values were detected | ||
| 118 | in the critical eutrophic second period. The level of confinement | 118 | in the critical eutrophic second period. The level of confinement | ||
| 119 | showed effects on the ecological quality of the shallow areas, | 119 | showed effects on the ecological quality of the shallow areas, | ||
| 120 | although the effects associated with the degree of anthropic pressure | 120 | although the effects associated with the degree of anthropic pressure | ||
| 121 | at site-approach were not significant. These results suggest that the | 121 | at site-approach were not significant. These results suggest that the | ||
| 122 | shallow areas of the lagoon, beyond their usual function as | 122 | shallow areas of the lagoon, beyond their usual function as | ||
| 123 | recruitment areas for juvenile fish, could be playing a complementary | 123 | recruitment areas for juvenile fish, could be playing a complementary | ||
| 124 | role as fish refuge habitats and buffering against the long-term | 124 | role as fish refuge habitats and buffering against the long-term | ||
| 125 | eutrophication process that is affecting the lagoon. However, fish | 125 | eutrophication process that is affecting the lagoon. However, fish | ||
| 126 | assemblages in shallow areas could be undergoing significant changes | 126 | assemblages in shallow areas could be undergoing significant changes | ||
| 127 | in their structure and composition. We understand that the loss of the | 127 | in their structure and composition. We understand that the loss of the | ||
| 128 | taxonomic and functional integrity of the shallow-area fish assemblage | 128 | taxonomic and functional integrity of the shallow-area fish assemblage | ||
| 129 | has repercussions on the dynamics of the fish populations present | 129 | has repercussions on the dynamics of the fish populations present | ||
| 130 | throughout the lagoon, and can compromise the recovery of this | 130 | throughout the lagoon, and can compromise the recovery of this | ||
| 131 | ecosystem.", | 131 | ecosystem.", | ||
| 132 | "notes_translated": { | 132 | "notes_translated": { | ||
| 133 | "es": "In the last two decades, the extensive development of | 133 | "es": "In the last two decades, the extensive development of | ||
| 134 | intensive irrigated agriculture around the Mar Menor coastal lagoon | 134 | intensive irrigated agriculture around the Mar Menor coastal lagoon | ||
| 135 | (SE Iberian Peninsula) has disturbed the characteristics of this | 135 | (SE Iberian Peninsula) has disturbed the characteristics of this | ||
| 136 | initially oligotrophic ecosystem. The organic pollution that flows | 136 | initially oligotrophic ecosystem. The organic pollution that flows | ||
| 137 | into the lagoon from agriculture and, to a lesser extent, from urban | 137 | into the lagoon from agriculture and, to a lesser extent, from urban | ||
| 138 | wastewater, has triggered the eutrophication of the system, resulting | 138 | wastewater, has triggered the eutrophication of the system, resulting | ||
| 139 | in dystrophic crises and mass mortality events of aquatic fauna. In | 139 | in dystrophic crises and mass mortality events of aquatic fauna. In | ||
| 140 | order to explore temporal changes in the ecological quality of the | 140 | order to explore temporal changes in the ecological quality of the | ||
| 141 | shallow areas of the Mar Menor, fish assemblage parameters have been | 141 | shallow areas of the Mar Menor, fish assemblage parameters have been | ||
| 142 | obtained and integrated into a multimetric fish index (modified-EMFI). | 142 | obtained and integrated into a multimetric fish index (modified-EMFI). | ||
| 143 | A total of 18 sampling sites around the lagoon perimeter were | 143 | A total of 18 sampling sites around the lagoon perimeter were | ||
| 144 | seasonally assessed. Seasonal sampling was carried out in three | 144 | seasonally assessed. Seasonal sampling was carried out in three | ||
| 145 | two-years periods: (a) the reference period (2002\u20132004); (b) the | 145 | two-years periods: (a) the reference period (2002\u20132004); (b) the | ||
| 146 | critical eutrophic first period (2018\u20132019); and (c) the critical | 146 | critical eutrophic first period (2018\u20132019); and (c) the critical | ||
| 147 | eutrophic second period with multispecies mass mortality events | 147 | eutrophic second period with multispecies mass mortality events | ||
| 148 | (2020\u20132021). The effect of sampling-site confinement (three | 148 | (2020\u20132021). The effect of sampling-site confinement (three | ||
| 149 | levels of water-renewal time) and the degree of anthropic pressure on | 149 | levels of water-renewal time) and the degree of anthropic pressure on | ||
| 150 | shallow areas were evaluated. Despite the magnitude of the | 150 | shallow areas were evaluated. Despite the magnitude of the | ||
| 151 | eutrophication impact on the lagoon, the shallow areas\u2019 | 151 | eutrophication impact on the lagoon, the shallow areas\u2019 | ||
| 152 | ecological quality (according to the modified-EMFI) did not show a | 152 | ecological quality (according to the modified-EMFI) did not show a | ||
| 153 | drastic drop. Nevertheless, significantly lower values were detected | 153 | drastic drop. Nevertheless, significantly lower values were detected | ||
| 154 | in the critical eutrophic second period. The level of confinement | 154 | in the critical eutrophic second period. The level of confinement | ||
| 155 | showed effects on the ecological quality of the shallow areas, | 155 | showed effects on the ecological quality of the shallow areas, | ||
| 156 | although the effects associated with the degree of anthropic pressure | 156 | although the effects associated with the degree of anthropic pressure | ||
| 157 | at site-approach were not significant. These results suggest that the | 157 | at site-approach were not significant. These results suggest that the | ||
| 158 | shallow areas of the lagoon, beyond their usual function as | 158 | shallow areas of the lagoon, beyond their usual function as | ||
| 159 | recruitment areas for juvenile fish, could be playing a complementary | 159 | recruitment areas for juvenile fish, could be playing a complementary | ||
| 160 | role as fish refuge habitats and buffering against the long-term | 160 | role as fish refuge habitats and buffering against the long-term | ||
| 161 | eutrophication process that is affecting the lagoon. However, fish | 161 | eutrophication process that is affecting the lagoon. However, fish | ||
| 162 | assemblages in shallow areas could be undergoing significant changes | 162 | assemblages in shallow areas could be undergoing significant changes | ||
| 163 | in their structure and composition. We understand that the loss of the | 163 | in their structure and composition. We understand that the loss of the | ||
| 164 | taxonomic and functional integrity of the shallow-area fish assemblage | 164 | taxonomic and functional integrity of the shallow-area fish assemblage | ||
| 165 | has repercussions on the dynamics of the fish populations present | 165 | has repercussions on the dynamics of the fish populations present | ||
| 166 | throughout the lagoon, and can compromise the recovery of this | 166 | throughout the lagoon, and can compromise the recovery of this | ||
| 167 | ecosystem." | 167 | ecosystem." | ||
| 168 | }, | 168 | }, | ||
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