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) en The Stenohaline Seagrass Posidonia oceanica Can Persist in Natural Environments Under Fluctuating Hypersaline Conditions
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| 96 | "notes": "The Mediterranean endemic seagrass Posidonia oceanica is | 106 | "notes": "The Mediterranean endemic seagrass Posidonia oceanica is | ||
| 97 | generally regarded as a stenohaline species, highly sensitive to | 107 | generally regarded as a stenohaline species, highly sensitive to | ||
| 98 | salinity increments; however, in a few particular cases, natural | 108 | salinity increments; however, in a few particular cases, natural | ||
| 99 | populations can grow under salinity levels above its normal threshold | 109 | populations can grow under salinity levels above its normal threshold | ||
| 100 | of tolerance. One such case is a population of P. oceanica in the | 110 | of tolerance. One such case is a population of P. oceanica in the | ||
| 101 | southeastern coastal region of Spain, which is able to survive under | 111 | southeastern coastal region of Spain, which is able to survive under | ||
| 102 | the fluctuating influence of hypersaline waters coming from an | 112 | the fluctuating influence of hypersaline waters coming from an | ||
| 103 | adjacent coastal lagoon (Mar Menor). The present work examines the | 113 | adjacent coastal lagoon (Mar Menor). The present work examines the | ||
| 104 | physiological mechanisms underlying the species' ability to overcome | 114 | physiological mechanisms underlying the species' ability to overcome | ||
| 105 | this hypersaline stress and persist in the long term. To this end, the | 115 | this hypersaline stress and persist in the long term. To this end, the | ||
| 106 | physiological, morphological, and population statuses of plants from | 116 | physiological, morphological, and population statuses of plants from | ||
| 107 | the site of influence were compared to those from a reference site | 117 | the site of influence were compared to those from a reference site | ||
| 108 | where plants grew under normal conditions. P. oceanica leaves from the | 118 | where plants grew under normal conditions. P. oceanica leaves from the | ||
| 109 | influenced sites showed more negative water potentials than those from | 119 | influenced sites showed more negative water potentials than those from | ||
| 110 | the reference sites as a response to maintain a positive water balance | 120 | the reference sites as a response to maintain a positive water balance | ||
| 111 | under hypersaline conditions. However, these lower water potentials | 121 | under hypersaline conditions. However, these lower water potentials | ||
| 112 | were not explained by the accumulation of intracellular solutes since | 122 | were not explained by the accumulation of intracellular solutes since | ||
| 113 | their osmotic potential were similar to reference leaves and their | 123 | their osmotic potential were similar to reference leaves and their | ||
| 114 | ionic content generally lower. In addition, these leaves also | 124 | ionic content generally lower. In addition, these leaves also | ||
| 115 | accumulated higher concentrations of proline and soluble sugars but | 125 | accumulated higher concentrations of proline and soluble sugars but | ||
| 116 | these organic osmolytes are more likely acting as osmo-protectants, | 126 | these organic osmolytes are more likely acting as osmo-protectants, | ||
| 117 | rather than as osmoticums. These responses indicated that plants | 127 | rather than as osmoticums. These responses indicated that plants | ||
| 118 | growing at the influenced site have developed physiological strategies | 128 | growing at the influenced site have developed physiological strategies | ||
| 119 | to maintain lower ion concentration in their leaf tissues in order to | 129 | to maintain lower ion concentration in their leaf tissues in order to | ||
| 120 | avoid the alteration of ion homeostasis (i.e., ionic ratios), which | 130 | avoid the alteration of ion homeostasis (i.e., ionic ratios), which | ||
| 121 | can be toxic for plant metabolism. Photosynthesis and photochemistry | 131 | can be toxic for plant metabolism. Photosynthesis and photochemistry | ||
| 122 | were not adversely affected in leaves exposed to hypersalinity; in | 132 | were not adversely affected in leaves exposed to hypersalinity; in | ||
| 123 | fact, these processes showed a tendency to become enhanced, possibly | 133 | fact, these processes showed a tendency to become enhanced, possibly | ||
| 124 | to support the assimilation of anthropogenic nitrogen coming from the | 134 | to support the assimilation of anthropogenic nitrogen coming from the | ||
| 125 | lagoon waters. At the individual and population levels, P. oceanica | 135 | lagoon waters. At the individual and population levels, P. oceanica | ||
| 126 | plants growing under the influence of hypersaline waters exhibited a | 136 | plants growing under the influence of hypersaline waters exhibited a | ||
| 127 | marked reduction in shoot size compared to those at the reference | 137 | marked reduction in shoot size compared to those at the reference | ||
| 128 | site, while shoot density and population growth rates were similar to | 138 | site, while shoot density and population growth rates were similar to | ||
| 129 | those of the reference site and remained stable over time. This shoot | 139 | those of the reference site and remained stable over time. This shoot | ||
| 130 | size reduction involves a lower demand of metabolic resources | 140 | size reduction involves a lower demand of metabolic resources | ||
| 131 | necessary to maintain vegetative structures, which is mainly required | 141 | necessary to maintain vegetative structures, which is mainly required | ||
| 132 | for metabolic adjustments at the physiological level. We propose that | 142 | for metabolic adjustments at the physiological level. We propose that | ||
| 133 | this morphological adaptation serves as a stress-coping mechanism, | 143 | this morphological adaptation serves as a stress-coping mechanism, | ||
| 134 | helping the species to inhabit this unfavorable environment, as has | 144 | helping the species to inhabit this unfavorable environment, as has | ||
| 135 | been widely described for terrestrial plants subjected to long-term | 145 | been widely described for terrestrial plants subjected to long-term | ||
| 136 | environmental stress.", | 146 | environmental stress.", | ||
| 137 | "notes_translated": { | 147 | "notes_translated": { | ||
| 138 | "es": "The Mediterranean endemic seagrass Posidonia oceanica is | 148 | "es": "The Mediterranean endemic seagrass Posidonia oceanica is | ||
| 139 | generally regarded as a stenohaline species, highly sensitive to | 149 | generally regarded as a stenohaline species, highly sensitive to | ||
| 140 | salinity increments; however, in a few particular cases, natural | 150 | salinity increments; however, in a few particular cases, natural | ||
| 141 | populations can grow under salinity levels above its normal threshold | 151 | populations can grow under salinity levels above its normal threshold | ||
| 142 | of tolerance. One such case is a population of P. oceanica in the | 152 | of tolerance. One such case is a population of P. oceanica in the | ||
| 143 | southeastern coastal region of Spain, which is able to survive under | 153 | southeastern coastal region of Spain, which is able to survive under | ||
| 144 | the fluctuating influence of hypersaline waters coming from an | 154 | the fluctuating influence of hypersaline waters coming from an | ||
| 145 | adjacent coastal lagoon (Mar Menor). The present work examines the | 155 | adjacent coastal lagoon (Mar Menor). The present work examines the | ||
| 146 | physiological mechanisms underlying the species' ability to overcome | 156 | physiological mechanisms underlying the species' ability to overcome | ||
| 147 | this hypersaline stress and persist in the long term. To this end, the | 157 | this hypersaline stress and persist in the long term. To this end, the | ||
| 148 | physiological, morphological, and population statuses of plants from | 158 | physiological, morphological, and population statuses of plants from | ||
| 149 | the site of influence were compared to those from a reference site | 159 | the site of influence were compared to those from a reference site | ||
| 150 | where plants grew under normal conditions. P. oceanica leaves from the | 160 | where plants grew under normal conditions. P. oceanica leaves from the | ||
| 151 | influenced sites showed more negative water potentials than those from | 161 | influenced sites showed more negative water potentials than those from | ||
| 152 | the reference sites as a response to maintain a positive water balance | 162 | the reference sites as a response to maintain a positive water balance | ||
| 153 | under hypersaline conditions. However, these lower water potentials | 163 | under hypersaline conditions. However, these lower water potentials | ||
| 154 | were not explained by the accumulation of intracellular solutes since | 164 | were not explained by the accumulation of intracellular solutes since | ||
| 155 | their osmotic potential were similar to reference leaves and their | 165 | their osmotic potential were similar to reference leaves and their | ||
| 156 | ionic content generally lower. In addition, these leaves also | 166 | ionic content generally lower. In addition, these leaves also | ||
| 157 | accumulated higher concentrations of proline and soluble sugars but | 167 | accumulated higher concentrations of proline and soluble sugars but | ||
| 158 | these organic osmolytes are more likely acting as osmo-protectants, | 168 | these organic osmolytes are more likely acting as osmo-protectants, | ||
| 159 | rather than as osmoticums. These responses indicated that plants | 169 | rather than as osmoticums. These responses indicated that plants | ||
| 160 | growing at the influenced site have developed physiological strategies | 170 | growing at the influenced site have developed physiological strategies | ||
| 161 | to maintain lower ion concentration in their leaf tissues in order to | 171 | to maintain lower ion concentration in their leaf tissues in order to | ||
| 162 | avoid the alteration of ion homeostasis (i.e., ionic ratios), which | 172 | avoid the alteration of ion homeostasis (i.e., ionic ratios), which | ||
| 163 | can be toxic for plant metabolism. Photosynthesis and photochemistry | 173 | can be toxic for plant metabolism. Photosynthesis and photochemistry | ||
| 164 | were not adversely affected in leaves exposed to hypersalinity; in | 174 | were not adversely affected in leaves exposed to hypersalinity; in | ||
| 165 | fact, these processes showed a tendency to become enhanced, possibly | 175 | fact, these processes showed a tendency to become enhanced, possibly | ||
| 166 | to support the assimilation of anthropogenic nitrogen coming from the | 176 | to support the assimilation of anthropogenic nitrogen coming from the | ||
| 167 | lagoon waters. At the individual and population levels, P. oceanica | 177 | lagoon waters. At the individual and population levels, P. oceanica | ||
| 168 | plants growing under the influence of hypersaline waters exhibited a | 178 | plants growing under the influence of hypersaline waters exhibited a | ||
| 169 | marked reduction in shoot size compared to those at the reference | 179 | marked reduction in shoot size compared to those at the reference | ||
| 170 | site, while shoot density and population growth rates were similar to | 180 | site, while shoot density and population growth rates were similar to | ||
| 171 | those of the reference site and remained stable over time. This shoot | 181 | those of the reference site and remained stable over time. This shoot | ||
| 172 | size reduction involves a lower demand of metabolic resources | 182 | size reduction involves a lower demand of metabolic resources | ||
| 173 | necessary to maintain vegetative structures, which is mainly required | 183 | necessary to maintain vegetative structures, which is mainly required | ||
| 174 | for metabolic adjustments at the physiological level. We propose that | 184 | for metabolic adjustments at the physiological level. We propose that | ||
| 175 | this morphological adaptation serves as a stress-coping mechanism, | 185 | this morphological adaptation serves as a stress-coping mechanism, | ||
| 176 | helping the species to inhabit this unfavorable environment, as has | 186 | helping the species to inhabit this unfavorable environment, as has | ||
| 177 | been widely described for terrestrial plants subjected to long-term | 187 | been widely described for terrestrial plants subjected to long-term | ||
| 178 | environmental stress." | 188 | environmental stress." | ||
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| 308 | "name": "crecimiento", | 318 | "name": "crecimiento", | ||
| 309 | "state": "active", | 319 | "state": "active", | ||
| 310 | "vocabulary_id": null | 320 | "vocabulary_id": null | ||
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| 318 | }, | 328 | }, | ||
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| 355 | Natural Environments Under Fluctuating Hypersaline Conditions", | 365 | Natural Environments Under Fluctuating Hypersaline Conditions", | ||
| 356 | "title_translated": { | 366 | "title_translated": { | ||
| 357 | "es": "The Stenohaline Seagrass Posidonia oceanica Can Persist in | 367 | "es": "The Stenohaline Seagrass Posidonia oceanica Can Persist in | ||
| 358 | Natural Environments Under Fluctuating Hypersaline Conditions" | 368 | Natural Environments Under Fluctuating Hypersaline Conditions" | ||
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| 367 | } | 377 | } | ||
| 368 | } | 378 | } |