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en Population Dynamics of Two Resident Fish Species with Contrasting Habitat Preferences: Temporal Changes over Eutrophic Crises in the Mar Menor Coastal Lagoon (SE Iberian Peninsula) -
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) en Population Dynamics of Two Resident Fish Species with Contrasting Habitat Preferences: Temporal Changes over Eutrophic Crises in the Mar Menor Coastal Lagoon (SE Iberian Peninsula)
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| 43 | L\u00f3pez-Mart\u00ednez de la Plaza, P. y Torralva, M." | 43 | L\u00f3pez-Mart\u00ednez de la Plaza, P. y Torralva, M." | ||
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| 86 | "miteco_data_population": { | 96 | "miteco_data_population": { | ||
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| 92 | "miteco_dataset_type": | 102 | "miteco_dataset_type": | ||
| 93 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | 103 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | ||
| 94 | "miteco_geo_level": "1", | 104 | "miteco_geo_level": "1", | ||
| n | 95 | "modified": "2026-06-23", | n | 105 | "modified": "2026-06-25", |
| 96 | "name": "b5d32fdc-51e1-528c-bf77-c07c6d2e7b9c", | 106 | "name": "b5d32fdc-51e1-528c-bf77-c07c6d2e7b9c", | ||
| 97 | "notes": "The Mar Menor coastal lagoon is a paradigmatic example of | 107 | "notes": "The Mar Menor coastal lagoon is a paradigmatic example of | ||
| 98 | a transitional system under high human disturbance, which in the last | 108 | a transitional system under high human disturbance, which in the last | ||
| 99 | years has resulted in occasional fish kill due to extreme anoxic | 109 | years has resulted in occasional fish kill due to extreme anoxic | ||
| 100 | conditions. Here, we assess the abundance temporal trend of two | 110 | conditions. Here, we assess the abundance temporal trend of two | ||
| 101 | conservation-concern resident fish species with contrasting habitat | 111 | conservation-concern resident fish species with contrasting habitat | ||
| 102 | preferences: Pomatoschistus marmoratus, associated with sandy open | 112 | preferences: Pomatoschistus marmoratus, associated with sandy open | ||
| 103 | bottoms, and Syngnathus abaster, associated with vegetated bottoms. | 113 | bottoms, and Syngnathus abaster, associated with vegetated bottoms. | ||
| 104 | Both species have been historically abundant in the shallow areas of | 114 | Both species have been historically abundant in the shallow areas of | ||
| 105 | the Mar Menor. Temporal change was related to three dystrophic crisis | 115 | the Mar Menor. Temporal change was related to three dystrophic crisis | ||
| 106 | events, leading to a lagoon-scale mortality of deep seagrass meadow | 116 | events, leading to a lagoon-scale mortality of deep seagrass meadow | ||
| 107 | before spring 2016 and two fish kills occurring in autumn 2019 and | 117 | before spring 2016 and two fish kills occurring in autumn 2019 and | ||
| 108 | summer 2021. After deep seagrass meadow mortality (2017/19), S. | 118 | summer 2021. After deep seagrass meadow mortality (2017/19), S. | ||
| 109 | abaster showed an increased abundance (annual mean: 5 ind/100 m2 to 23 | 119 | abaster showed an increased abundance (annual mean: 5 ind/100 m2 to 23 | ||
| 110 | ind/100 m2), whereas abundance of P. marmoratus decreased (annual | 120 | ind/100 m2), whereas abundance of P. marmoratus decreased (annual | ||
| 111 | mean: 37 ind/100 m2 to 10 ind/100 m2) in comparison to reference | 121 | mean: 37 ind/100 m2 to 10 ind/100 m2) in comparison to reference | ||
| 112 | values (2002/04). At that point, shallow areas had experienced great | 122 | values (2002/04). At that point, shallow areas had experienced great | ||
| 113 | habitat changes, with an increase both in the mud portion of the | 123 | habitat changes, with an increase both in the mud portion of the | ||
| 114 | substrate (driven by the deep seagrass decomposition process), and in | 124 | substrate (driven by the deep seagrass decomposition process), and in | ||
| 115 | the vegetated surface (due to nutrient input), thus modifying the | 125 | the vegetated surface (due to nutrient input), thus modifying the | ||
| 116 | mesohabitat selected by the species. Before the first fish kill | 126 | mesohabitat selected by the species. Before the first fish kill | ||
| 117 | (autumn 2019), the abundance of both species markedly increased, | 127 | (autumn 2019), the abundance of both species markedly increased, | ||
| 118 | likely as a response to an anoxia-mediated refugee search by | 128 | likely as a response to an anoxia-mediated refugee search by | ||
| 119 | deep-habitat metapopulations. A slow recovery was detected after the | 129 | deep-habitat metapopulations. A slow recovery was detected after the | ||
| 120 | 2020 recruitment period for both species, reaching record values for | 130 | 2020 recruitment period for both species, reaching record values for | ||
| 121 | P. marmoratus (75 ind/100 m2) in summer 2021, possibly related again | 131 | P. marmoratus (75 ind/100 m2) in summer 2021, possibly related again | ||
| 122 | to the search for more oxygenated shallow areas, since shortly | 132 | to the search for more oxygenated shallow areas, since shortly | ||
| 123 | thereafter a new dystrophic crisis occurred (summer 2021). Since then, | 133 | thereafter a new dystrophic crisis occurred (summer 2021). Since then, | ||
| 124 | the abundance of both species has steeply decreased to less than 2 | 134 | the abundance of both species has steeply decreased to less than 2 | ||
| 125 | ind/100 m2, highlighting a critical threat to the long-term population | 135 | ind/100 m2, highlighting a critical threat to the long-term population | ||
| 126 | viability of these conservation-concern species. As supported here, | 136 | viability of these conservation-concern species. As supported here, | ||
| 127 | long-term monitoring programs provide insightful data on the response | 137 | long-term monitoring programs provide insightful data on the response | ||
| 128 | of fish species to acute human-related disturbance events, offering | 138 | of fish species to acute human-related disturbance events, offering | ||
| 129 | necessary information to guide the development of management and | 139 | necessary information to guide the development of management and | ||
| 130 | conservation actions.", | 140 | conservation actions.", | ||
| 131 | "notes_translated": { | 141 | "notes_translated": { | ||
| 132 | "es": "The Mar Menor coastal lagoon is a paradigmatic example of a | 142 | "es": "The Mar Menor coastal lagoon is a paradigmatic example of a | ||
| 133 | transitional system under high human disturbance, which in the last | 143 | transitional system under high human disturbance, which in the last | ||
| 134 | years has resulted in occasional fish kill due to extreme anoxic | 144 | years has resulted in occasional fish kill due to extreme anoxic | ||
| 135 | conditions. Here, we assess the abundance temporal trend of two | 145 | conditions. Here, we assess the abundance temporal trend of two | ||
| 136 | conservation-concern resident fish species with contrasting habitat | 146 | conservation-concern resident fish species with contrasting habitat | ||
| 137 | preferences: Pomatoschistus marmoratus, associated with sandy open | 147 | preferences: Pomatoschistus marmoratus, associated with sandy open | ||
| 138 | bottoms, and Syngnathus abaster, associated with vegetated bottoms. | 148 | bottoms, and Syngnathus abaster, associated with vegetated bottoms. | ||
| 139 | Both species have been historically abundant in the shallow areas of | 149 | Both species have been historically abundant in the shallow areas of | ||
| 140 | the Mar Menor. Temporal change was related to three dystrophic crisis | 150 | the Mar Menor. Temporal change was related to three dystrophic crisis | ||
| 141 | events, leading to a lagoon-scale mortality of deep seagrass meadow | 151 | events, leading to a lagoon-scale mortality of deep seagrass meadow | ||
| 142 | before spring 2016 and two fish kills occurring in autumn 2019 and | 152 | before spring 2016 and two fish kills occurring in autumn 2019 and | ||
| 143 | summer 2021. After deep seagrass meadow mortality (2017/19), S. | 153 | summer 2021. After deep seagrass meadow mortality (2017/19), S. | ||
| 144 | abaster showed an increased abundance (annual mean: 5 ind/100 m2 to 23 | 154 | abaster showed an increased abundance (annual mean: 5 ind/100 m2 to 23 | ||
| 145 | ind/100 m2), whereas abundance of P. marmoratus decreased (annual | 155 | ind/100 m2), whereas abundance of P. marmoratus decreased (annual | ||
| 146 | mean: 37 ind/100 m2 to 10 ind/100 m2) in comparison to reference | 156 | mean: 37 ind/100 m2 to 10 ind/100 m2) in comparison to reference | ||
| 147 | values (2002/04). At that point, shallow areas had experienced great | 157 | values (2002/04). At that point, shallow areas had experienced great | ||
| 148 | habitat changes, with an increase both in the mud portion of the | 158 | habitat changes, with an increase both in the mud portion of the | ||
| 149 | substrate (driven by the deep seagrass decomposition process), and in | 159 | substrate (driven by the deep seagrass decomposition process), and in | ||
| 150 | the vegetated surface (due to nutrient input), thus modifying the | 160 | the vegetated surface (due to nutrient input), thus modifying the | ||
| 151 | mesohabitat selected by the species. Before the first fish kill | 161 | mesohabitat selected by the species. Before the first fish kill | ||
| 152 | (autumn 2019), the abundance of both species markedly increased, | 162 | (autumn 2019), the abundance of both species markedly increased, | ||
| 153 | likely as a response to an anoxia-mediated refugee search by | 163 | likely as a response to an anoxia-mediated refugee search by | ||
| 154 | deep-habitat metapopulations. A slow recovery was detected after the | 164 | deep-habitat metapopulations. A slow recovery was detected after the | ||
| 155 | 2020 recruitment period for both species, reaching record values for | 165 | 2020 recruitment period for both species, reaching record values for | ||
| 156 | P. marmoratus (75 ind/100 m2) in summer 2021, possibly related again | 166 | P. marmoratus (75 ind/100 m2) in summer 2021, possibly related again | ||
| 157 | to the search for more oxygenated shallow areas, since shortly | 167 | to the search for more oxygenated shallow areas, since shortly | ||
| 158 | thereafter a new dystrophic crisis occurred (summer 2021). Since then, | 168 | thereafter a new dystrophic crisis occurred (summer 2021). Since then, | ||
| 159 | the abundance of both species has steeply decreased to less than 2 | 169 | the abundance of both species has steeply decreased to less than 2 | ||
| 160 | ind/100 m2, highlighting a critical threat to the long-term population | 170 | ind/100 m2, highlighting a critical threat to the long-term population | ||
| 161 | viability of these conservation-concern species. As supported here, | 171 | viability of these conservation-concern species. As supported here, | ||
| 162 | long-term monitoring programs provide insightful data on the response | 172 | long-term monitoring programs provide insightful data on the response | ||
| 163 | of fish species to acute human-related disturbance events, offering | 173 | of fish species to acute human-related disturbance events, offering | ||
| 164 | necessary information to guide the development of management and | 174 | necessary information to guide the development of management and | ||
| 165 | conservation actions." | 175 | conservation actions." | ||
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| 295 | "vocabulary_id": null | 305 | "vocabulary_id": null | ||
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| 301 | "state": "active", | 311 | "state": "active", | ||
| 302 | "vocabulary_id": null | 312 | "vocabulary_id": null | ||
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| 306 | "id": "5fcdd244-0f78-4801-be7d-5a67c5bb55ec", | 316 | "id": "5fcdd244-0f78-4801-be7d-5a67c5bb55ec", | ||
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| 329 | "state": "active", | 339 | "state": "active", | ||
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| 351 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | 361 | "http://datos.gob.es/kos/sector-publico/sector/medio-ambiente" | ||
| 352 | ], | 362 | ], | ||
| 353 | "title": "Population Dynamics of Two Resident Fish Species with | 363 | "title": "Population Dynamics of Two Resident Fish Species with | ||
| 354 | Contrasting Habitat Preferences: Temporal Changes over Eutrophic | 364 | Contrasting Habitat Preferences: Temporal Changes over Eutrophic | ||
| 355 | Crises in the Mar Menor Coastal Lagoon (SE Iberian Peninsula)", | 365 | Crises in the Mar Menor Coastal Lagoon (SE Iberian Peninsula)", | ||
| 356 | "title_translated": { | 366 | "title_translated": { | ||
| 357 | "es": "Population Dynamics of Two Resident Fish Species with | 367 | "es": "Population Dynamics of Two Resident Fish Species with | ||
| 358 | Contrasting Habitat Preferences: Temporal Changes over Eutrophic | 368 | Contrasting Habitat Preferences: Temporal Changes over Eutrophic | ||
| 359 | Crises in the Mar Menor Coastal Lagoon (SE Iberian Peninsula)" | 369 | Crises in the Mar Menor Coastal Lagoon (SE Iberian Peninsula)" | ||
| 360 | }, | 370 | }, | ||
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| 363 | "type": "dataset", | 373 | "type": "dataset", | ||
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| 366 | "version_notes": { | 376 | "version_notes": { | ||
| 367 | "es": "" | 377 | "es": "" | ||
| 368 | } | 378 | } | ||
| 369 | } | 379 | } |