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en Cymodocea nodosa vs. Caulerpa prolifera: Causes and consequences of a long term history of interaction in macrophyte meadows in the Mar Menor coastal lagoon (Spain, southwestern Mediterranean) -
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) en Cymodocea nodosa vs. Caulerpa prolifera: Causes and consequences of a long term history of interaction in macrophyte meadows in the Mar Menor coastal lagoon (Spain, southwestern Mediterranean)
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| 100 | "notes": "Seagrass communities are under direct threat as a result | 110 | "notes": "Seagrass communities are under direct threat as a result | ||
| 101 | of anthropogenic impact and competition with macroalgae. Present day | 111 | of anthropogenic impact and competition with macroalgae. Present day | ||
| 102 | macrophyte meadows in the Mar Menor are the result of successive | 112 | macrophyte meadows in the Mar Menor are the result of successive | ||
| 103 | colonization events, associated with changes in the hydrographical | 113 | colonization events, associated with changes in the hydrographical | ||
| 104 | conditions. In the last of these events, Caulerpa prolifera | 114 | conditions. In the last of these events, Caulerpa prolifera | ||
| 105 | (Forssk\u00e5l) J.V. Lamouroux colonized the lagoon in the early | 115 | (Forssk\u00e5l) J.V. Lamouroux colonized the lagoon in the early | ||
| 106 | 1970\u2019s following the widening and deepening of the El Estacio | 116 | 1970\u2019s following the widening and deepening of the El Estacio | ||
| 107 | inlet into a navigation channel, which caused a substantial decrease | 117 | inlet into a navigation channel, which caused a substantial decrease | ||
| 108 | in the salinity level and a lower annual water temperature range. The | 118 | in the salinity level and a lower annual water temperature range. The | ||
| 109 | seaweed C. prolifera expanded rapidly and replaced the previous | 119 | seaweed C. prolifera expanded rapidly and replaced the previous | ||
| 110 | seagrass meadows with monospecific algae meadows or with meadows mixed | 120 | seagrass meadows with monospecific algae meadows or with meadows mixed | ||
| 111 | with the seagrass Cymodocea nodosa (Ucria) Ascherson. This work | 121 | with the seagrass Cymodocea nodosa (Ucria) Ascherson. This work | ||
| 112 | analyzes the factors that explain the distribution of macrophyte | 122 | analyzes the factors that explain the distribution of macrophyte | ||
| 113 | meadows and their evolution, as well as subsequent sediment | 123 | meadows and their evolution, as well as subsequent sediment | ||
| 114 | alterations. The mean biomass of C. prolifera (Ca) in the deeper areas | 124 | alterations. The mean biomass of C. prolifera (Ca) in the deeper areas | ||
| 115 | of the Mar Menor increased from 1982 to 1987 and remained constant | 125 | of the Mar Menor increased from 1982 to 1987 and remained constant | ||
| 116 | thereafter until 2008, while the mean biomass of C. nodosa (Cy) showed | 126 | thereafter until 2008, while the mean biomass of C. nodosa (Cy) showed | ||
| 117 | a continuous decrease during the same period. The evolution of the | 127 | a continuous decrease during the same period. The evolution of the | ||
| 118 | Ca/Cy ratio showed a progressive expansion of C. prolifera | 128 | Ca/Cy ratio showed a progressive expansion of C. prolifera | ||
| 119 | monospecific meadows from north to south. The decline in the C. nodosa | 129 | monospecific meadows from north to south. The decline in the C. nodosa | ||
| 120 | meadows was more pronounced in the deeper areas and was especially | 130 | meadows was more pronounced in the deeper areas and was especially | ||
| 121 | verified in the inner or more confined areas. At present, monospecific | 131 | verified in the inner or more confined areas. At present, monospecific | ||
| 122 | C. nodosa meadows are restricted to the southern and western, | 132 | C. nodosa meadows are restricted to the southern and western, | ||
| 123 | shallowest areas of the lagoon. The negative relationship between | 133 | shallowest areas of the lagoon. The negative relationship between | ||
| 124 | Caulerpa prolifera and Cymodocea nodosa shown by multiple regressions | 134 | Caulerpa prolifera and Cymodocea nodosa shown by multiple regressions | ||
| 125 | suggests that there is a competition between the two species. A | 135 | suggests that there is a competition between the two species. A | ||
| 126 | complex interaction of factors could be responsible for the | 136 | complex interaction of factors could be responsible for the | ||
| 127 | equilibrium and evolution of the relationships between both species in | 137 | equilibrium and evolution of the relationships between both species in | ||
| 128 | the Mar Menor. In shallow waters, coarse sediments, high light levels | 138 | the Mar Menor. In shallow waters, coarse sediments, high light levels | ||
| 129 | and physiological adaptations could favour C. nodosa. In deeper areas, | 139 | and physiological adaptations could favour C. nodosa. In deeper areas, | ||
| 130 | light scarcity might limit C. nodosa biomass, but a negative effect of | 140 | light scarcity might limit C. nodosa biomass, but a negative effect of | ||
| 131 | C. prolifera through increasing the sediment silt content, sulphide | 141 | C. prolifera through increasing the sediment silt content, sulphide | ||
| 132 | production, organic matter and anoxia, cannot be ruled out.", | 142 | production, organic matter and anoxia, cannot be ruled out.", | ||
| 133 | "notes_translated": { | 143 | "notes_translated": { | ||
| 134 | "es": "Seagrass communities are under direct threat as a result of | 144 | "es": "Seagrass communities are under direct threat as a result of | ||
| 135 | anthropogenic impact and competition with macroalgae. Present day | 145 | anthropogenic impact and competition with macroalgae. Present day | ||
| 136 | macrophyte meadows in the Mar Menor are the result of successive | 146 | macrophyte meadows in the Mar Menor are the result of successive | ||
| 137 | colonization events, associated with changes in the hydrographical | 147 | colonization events, associated with changes in the hydrographical | ||
| 138 | conditions. In the last of these events, Caulerpa prolifera | 148 | conditions. In the last of these events, Caulerpa prolifera | ||
| 139 | (Forssk\u00e5l) J.V. Lamouroux colonized the lagoon in the early | 149 | (Forssk\u00e5l) J.V. Lamouroux colonized the lagoon in the early | ||
| 140 | 1970\u2019s following the widening and deepening of the El Estacio | 150 | 1970\u2019s following the widening and deepening of the El Estacio | ||
| 141 | inlet into a navigation channel, which caused a substantial decrease | 151 | inlet into a navigation channel, which caused a substantial decrease | ||
| 142 | in the salinity level and a lower annual water temperature range. The | 152 | in the salinity level and a lower annual water temperature range. The | ||
| 143 | seaweed C. prolifera expanded rapidly and replaced the previous | 153 | seaweed C. prolifera expanded rapidly and replaced the previous | ||
| 144 | seagrass meadows with monospecific algae meadows or with meadows mixed | 154 | seagrass meadows with monospecific algae meadows or with meadows mixed | ||
| 145 | with the seagrass Cymodocea nodosa (Ucria) Ascherson. This work | 155 | with the seagrass Cymodocea nodosa (Ucria) Ascherson. This work | ||
| 146 | analyzes the factors that explain the distribution of macrophyte | 156 | analyzes the factors that explain the distribution of macrophyte | ||
| 147 | meadows and their evolution, as well as subsequent sediment | 157 | meadows and their evolution, as well as subsequent sediment | ||
| 148 | alterations. The mean biomass of C. prolifera (Ca) in the deeper areas | 158 | alterations. The mean biomass of C. prolifera (Ca) in the deeper areas | ||
| 149 | of the Mar Menor increased from 1982 to 1987 and remained constant | 159 | of the Mar Menor increased from 1982 to 1987 and remained constant | ||
| 150 | thereafter until 2008, while the mean biomass of C. nodosa (Cy) showed | 160 | thereafter until 2008, while the mean biomass of C. nodosa (Cy) showed | ||
| 151 | a continuous decrease during the same period. The evolution of the | 161 | a continuous decrease during the same period. The evolution of the | ||
| 152 | Ca/Cy ratio showed a progressive expansion of C. prolifera | 162 | Ca/Cy ratio showed a progressive expansion of C. prolifera | ||
| 153 | monospecific meadows from north to south. The decline in the C. nodosa | 163 | monospecific meadows from north to south. The decline in the C. nodosa | ||
| 154 | meadows was more pronounced in the deeper areas and was especially | 164 | meadows was more pronounced in the deeper areas and was especially | ||
| 155 | verified in the inner or more confined areas. At present, monospecific | 165 | verified in the inner or more confined areas. At present, monospecific | ||
| 156 | C. nodosa meadows are restricted to the southern and western, | 166 | C. nodosa meadows are restricted to the southern and western, | ||
| 157 | shallowest areas of the lagoon. The negative relationship between | 167 | shallowest areas of the lagoon. The negative relationship between | ||
| 158 | Caulerpa prolifera and Cymodocea nodosa shown by multiple regressions | 168 | Caulerpa prolifera and Cymodocea nodosa shown by multiple regressions | ||
| 159 | suggests that there is a competition between the two species. A | 169 | suggests that there is a competition between the two species. A | ||
| 160 | complex interaction of factors could be responsible for the | 170 | complex interaction of factors could be responsible for the | ||
| 161 | equilibrium and evolution of the relationships between both species in | 171 | equilibrium and evolution of the relationships between both species in | ||
| 162 | the Mar Menor. In shallow waters, coarse sediments, high light levels | 172 | the Mar Menor. In shallow waters, coarse sediments, high light levels | ||
| 163 | and physiological adaptations could favour C. nodosa. In deeper areas, | 173 | and physiological adaptations could favour C. nodosa. In deeper areas, | ||
| 164 | light scarcity might limit C. nodosa biomass, but a negative effect of | 174 | light scarcity might limit C. nodosa biomass, but a negative effect of | ||
| 165 | C. prolifera through increasing the sediment silt content, sulphide | 175 | C. prolifera through increasing the sediment silt content, sulphide | ||
| 166 | production, organic matter and anoxia, cannot be ruled out." | 176 | production, organic matter and anoxia, cannot be ruled out." | ||
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| 352 | Mediterranean)", | 362 | Mediterranean)", | ||
| 353 | "title_translated": { | 363 | "title_translated": { | ||
| 354 | "es": "Cymodocea nodosa vs. Caulerpa prolifera: Causes and | 364 | "es": "Cymodocea nodosa vs. Caulerpa prolifera: Causes and | ||
| 355 | consequences of a long term history of interaction in macrophyte | 365 | consequences of a long term history of interaction in macrophyte | ||
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| 357 | Mediterranean)" | 367 | Mediterranean)" | ||
| 358 | }, | 368 | }, | ||
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