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en Recovery of eutrophized marine ecosystems using the European flat oyster, Ostrea edulis -
Modificado el valor del campo
modified
del recurso Distribución HTML a2026-06-25
(anteriormente2026-06-23
) en Recovery of eutrophized marine ecosystems using the European flat oyster, Ostrea edulis
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| 8 | "author": "Albentosa, M., Akinyemi, M.I., Vera, M., Ibarrola, I., | 8 | "author": "Albentosa, M., Akinyemi, M.I., Vera, M., Ibarrola, I., | ||
| 9 | Filgueira, R., Galimany, E., da Costa, F., Pardo, B.G., Vazquez-Luis, | 9 | Filgueira, R., Galimany, E., da Costa, F., Pardo, B.G., Vazquez-Luis, | ||
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| 43 | "name": "Albentosa, M., Akinyemi, M.I., Vera, M., Ibarrola, I., | 43 | "name": "Albentosa, M., Akinyemi, M.I., Vera, M., Ibarrola, I., | ||
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| 65 | "eutrofizacion", | 75 | "eutrofizacion", | ||
| 66 | "plan_de_recuperacion", | 76 | "plan_de_recuperacion", | ||
| 67 | "restauracion", | 77 | "restauracion", | ||
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| 75 | "lineage_source": [ | 85 | "lineage_source": [ | ||
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| 77 | Oyster Retoration Alliance (NORA) 4TH Conference \u2010 Reconnecting | 87 | Oyster Retoration Alliance (NORA) 4TH Conference \u2010 Reconnecting | ||
| 78 | Across Europe", | 88 | Across Europe", | ||
| 79 | "vol 33", | 89 | "vol 33", | ||
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| 100 | "name": "319c9d86-d121-569b-9a1b-0bf6f74b2ac2", | 110 | "name": "319c9d86-d121-569b-9a1b-0bf6f74b2ac2", | ||
| 101 | "notes": "The development of tourism and intensification of | 111 | "notes": "The development of tourism and intensification of | ||
| 102 | agriculture has released large amounts of nitrogen and phosphorus into | 112 | agriculture has released large amounts of nitrogen and phosphorus into | ||
| 103 | the Mar Menor coastal lagoon in South-east Spain, resulting in a | 113 | the Mar Menor coastal lagoon in South-east Spain, resulting in a | ||
| 104 | phytoplankton bloom in 2016. This bloom turned the clear and | 114 | phytoplankton bloom in 2016. This bloom turned the clear and | ||
| 105 | transparent waters turbid and greenish, and killed approximately 85% | 115 | transparent waters turbid and greenish, and killed approximately 85% | ||
| 106 | of benthic macrophytes.Nutrient bioextraction by flat oysters, Ostrea | 116 | of benthic macrophytes.Nutrient bioextraction by flat oysters, Ostrea | ||
| 107 | edulis, has been proposed for remediation of these eutrophication | 117 | edulis, has been proposed for remediation of these eutrophication | ||
| 108 | events and water quality recovery.This research aims to quantify the | 118 | events and water quality recovery.This research aims to quantify the | ||
| 109 | clearance rate and investigate the genetic origin of Mar Menor oysters | 119 | clearance rate and investigate the genetic origin of Mar Menor oysters | ||
| 110 | under eutrophized conditions for potential applications to | 120 | under eutrophized conditions for potential applications to | ||
| 111 | bioremediation projects. Oligotrophic and eutrophic conditions were | 121 | bioremediation projects. Oligotrophic and eutrophic conditions were | ||
| 112 | replicated in the laboratory, and oyster feeding behaviour (i.e. | 122 | replicated in the laboratory, and oyster feeding behaviour (i.e. | ||
| 113 | clearance rates, ingestion rates, absorption efficiency and absorption | 123 | clearance rates, ingestion rates, absorption efficiency and absorption | ||
| 114 | rates) were studied using a flow-through system.The genetic | 124 | rates) were studied using a flow-through system.The genetic | ||
| 115 | characterization of oysters showed no significant difference between | 125 | characterization of oysters showed no significant difference between | ||
| 116 | individuals from the Mar Menor and individuals collected from a nearby | 126 | individuals from the Mar Menor and individuals collected from a nearby | ||
| 117 | Mediterranean bed (Tabarca Island).Based on the physiological results | 127 | Mediterranean bed (Tabarca Island).Based on the physiological results | ||
| 118 | observed, oysters were grouped into high-feeder (HF) and low-feeder | 128 | observed, oysters were grouped into high-feeder (HF) and low-feeder | ||
| 119 | (LF) categories according to their clearance rate, that was 3-fold | 129 | (LF) categories according to their clearance rate, that was 3-fold | ||
| 120 | higher in the HF group. Different responses in feeding behaviour were | 130 | higher in the HF group. Different responses in feeding behaviour were | ||
| 121 | observed under eutrophic conditions in both oyster groups. Constraints | 131 | observed under eutrophic conditions in both oyster groups. Constraints | ||
| 122 | in the absorption capacity of LF oysters seemed to be related to their | 132 | in the absorption capacity of LF oysters seemed to be related to their | ||
| 123 | reduced filtering activity. Lower body condition of LF oysters was | 133 | reduced filtering activity. Lower body condition of LF oysters was | ||
| 124 | evidenced by their negative scope for growth value.From this work, | 134 | evidenced by their negative scope for growth value.From this work, | ||
| 125 | several conclusions can be drawn for future restoration/bioextraction | 135 | several conclusions can be drawn for future restoration/bioextraction | ||
| 126 | actions: (i) the recovery of half of the oyster population that | 136 | actions: (i) the recovery of half of the oyster population that | ||
| 127 | existed in the past would act as an effective top-down control on the | 137 | existed in the past would act as an effective top-down control on the | ||
| 128 | phytoplankton community; (ii) using clearance rate measurements is | 138 | phytoplankton community; (ii) using clearance rate measurements is | ||
| 129 | recommended to select oysters as broodstock; and (iii) Mediterranean | 139 | recommended to select oysters as broodstock; and (iii) Mediterranean | ||
| 130 | oysters could be used as broodstock in the event that Mar Menor | 140 | oysters could be used as broodstock in the event that Mar Menor | ||
| 131 | oysters fail to reproduce.", | 141 | oysters fail to reproduce.", | ||
| 132 | "notes_translated": { | 142 | "notes_translated": { | ||
| 133 | "es": "The development of tourism and intensification of | 143 | "es": "The development of tourism and intensification of | ||
| 134 | agriculture has released large amounts of nitrogen and phosphorus into | 144 | agriculture has released large amounts of nitrogen and phosphorus into | ||
| 135 | the Mar Menor coastal lagoon in South-east Spain, resulting in a | 145 | the Mar Menor coastal lagoon in South-east Spain, resulting in a | ||
| 136 | phytoplankton bloom in 2016. This bloom turned the clear and | 146 | phytoplankton bloom in 2016. This bloom turned the clear and | ||
| 137 | transparent waters turbid and greenish, and killed approximately 85% | 147 | transparent waters turbid and greenish, and killed approximately 85% | ||
| 138 | of benthic macrophytes.Nutrient bioextraction by flat oysters, Ostrea | 148 | of benthic macrophytes.Nutrient bioextraction by flat oysters, Ostrea | ||
| 139 | edulis, has been proposed for remediation of these eutrophication | 149 | edulis, has been proposed for remediation of these eutrophication | ||
| 140 | events and water quality recovery.This research aims to quantify the | 150 | events and water quality recovery.This research aims to quantify the | ||
| 141 | clearance rate and investigate the genetic origin of Mar Menor oysters | 151 | clearance rate and investigate the genetic origin of Mar Menor oysters | ||
| 142 | under eutrophized conditions for potential applications to | 152 | under eutrophized conditions for potential applications to | ||
| 143 | bioremediation projects. Oligotrophic and eutrophic conditions were | 153 | bioremediation projects. Oligotrophic and eutrophic conditions were | ||
| 144 | replicated in the laboratory, and oyster feeding behaviour (i.e. | 154 | replicated in the laboratory, and oyster feeding behaviour (i.e. | ||
| 145 | clearance rates, ingestion rates, absorption efficiency and absorption | 155 | clearance rates, ingestion rates, absorption efficiency and absorption | ||
| 146 | rates) were studied using a flow-through system.The genetic | 156 | rates) were studied using a flow-through system.The genetic | ||
| 147 | characterization of oysters showed no significant difference between | 157 | characterization of oysters showed no significant difference between | ||
| 148 | individuals from the Mar Menor and individuals collected from a nearby | 158 | individuals from the Mar Menor and individuals collected from a nearby | ||
| 149 | Mediterranean bed (Tabarca Island).Based on the physiological results | 159 | Mediterranean bed (Tabarca Island).Based on the physiological results | ||
| 150 | observed, oysters were grouped into high-feeder (HF) and low-feeder | 160 | observed, oysters were grouped into high-feeder (HF) and low-feeder | ||
| 151 | (LF) categories according to their clearance rate, that was 3-fold | 161 | (LF) categories according to their clearance rate, that was 3-fold | ||
| 152 | higher in the HF group. Different responses in feeding behaviour were | 162 | higher in the HF group. Different responses in feeding behaviour were | ||
| 153 | observed under eutrophic conditions in both oyster groups. Constraints | 163 | observed under eutrophic conditions in both oyster groups. Constraints | ||
| 154 | in the absorption capacity of LF oysters seemed to be related to their | 164 | in the absorption capacity of LF oysters seemed to be related to their | ||
| 155 | reduced filtering activity. Lower body condition of LF oysters was | 165 | reduced filtering activity. Lower body condition of LF oysters was | ||
| 156 | evidenced by their negative scope for growth value.From this work, | 166 | evidenced by their negative scope for growth value.From this work, | ||
| 157 | several conclusions can be drawn for future restoration/bioextraction | 167 | several conclusions can be drawn for future restoration/bioextraction | ||
| 158 | actions: (i) the recovery of half of the oyster population that | 168 | actions: (i) the recovery of half of the oyster population that | ||
| 159 | existed in the past would act as an effective top-down control on the | 169 | existed in the past would act as an effective top-down control on the | ||
| 160 | phytoplankton community; (ii) using clearance rate measurements is | 170 | phytoplankton community; (ii) using clearance rate measurements is | ||
| 161 | recommended to select oysters as broodstock; and (iii) Mediterranean | 171 | recommended to select oysters as broodstock; and (iii) Mediterranean | ||
| 162 | oysters could be used as broodstock in the event that Mar Menor | 172 | oysters could be used as broodstock in the event that Mar Menor | ||
| 163 | oysters fail to reproduce." | 173 | oysters fail to reproduce." | ||
| 164 | }, | 174 | }, | ||
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