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en Nutrient Bioaccumulation in Phragmites australis: Management Tool for Reduction of Pollution in the Mar Menor -
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del recurso Distribución HTML a2026-06-25
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) en Nutrient Bioaccumulation in Phragmites australis: Management Tool for Reduction of Pollution in the Mar Menor
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| 91 | "name": "41a7622d-be04-5283-9cb3-6c1ea8bbd809", | 101 | "name": "41a7622d-be04-5283-9cb3-6c1ea8bbd809", | ||
| 92 | "notes": "We studied nutrient removal by Phragmites australis in the | 102 | "notes": "We studied nutrient removal by Phragmites australis in the | ||
| 93 | Albujn rambla, the main drainage system that discharges into the Mar | 103 | Albujn rambla, the main drainage system that discharges into the Mar | ||
| 94 | Menor, a Mediterranean coastal lagoon of high conservation interest, | 104 | Menor, a Mediterranean coastal lagoon of high conservation interest, | ||
| 95 | but highly threatened by point and nonpoint pollution derived from | 105 | but highly threatened by point and nonpoint pollution derived from | ||
| 96 | tourism and agricultural activities. We measured aerial biomass and N | 106 | tourism and agricultural activities. We measured aerial biomass and N | ||
| 97 | and P concentrations in both aboveground and belowground tissues of | 107 | and P concentrations in both aboveground and belowground tissues of | ||
| 98 | common reed during an annual cycle that included two cutting events | 108 | common reed during an annual cycle that included two cutting events | ||
| 99 | and two periods of reed growth (one at the end of summer after cutting | 109 | and two periods of reed growth (one at the end of summer after cutting | ||
| 100 | and another at the beginning of spring, following their natural | 110 | and another at the beginning of spring, following their natural | ||
| 101 | cycle). The temporal variation of N and P concentrations was related | 111 | cycle). The temporal variation of N and P concentrations was related | ||
| 102 | to the phenology of the plant and cutting events. The maximum nutrient | 112 | to the phenology of the plant and cutting events. The maximum nutrient | ||
| 103 | concentrations were recorded in young stems in the initial stages of | 113 | concentrations were recorded in young stems in the initial stages of | ||
| 104 | the autumn growing season (35.86 mg N g(-1) and 2.38 mg P g(-1)). The | 114 | the autumn growing season (35.86 mg N g(-1) and 2.38 mg P g(-1)). The | ||
| 105 | phosphorus dynamics showed evidence of translocation processes related | 115 | phosphorus dynamics showed evidence of translocation processes related | ||
| 106 | with growth activity, although no evidence of N translocation was | 116 | with growth activity, although no evidence of N translocation was | ||
| 107 | found. In November and in summer, when aerial growth ceases because of | 117 | found. In November and in summer, when aerial growth ceases because of | ||
| 108 | the hard conditions, the P concentration in rhizomes was higher than | 118 | the hard conditions, the P concentration in rhizomes was higher than | ||
| 109 | in stems, while in spring and in September, the period of maximal | 119 | in stems, while in spring and in September, the period of maximal | ||
| 110 | growth, the reverse relation was found. The highest total amounts of | 120 | growth, the reverse relation was found. The highest total amounts of | ||
| 111 | the two elements in the aboveground biomass (0.54 Tm N ha(-1) and 0.25 | 121 | the two elements in the aboveground biomass (0.54 Tm N ha(-1) and 0.25 | ||
| 112 | Tm P ha(-1)) were reached in July, coinciding with the highest biomass | 122 | Tm P ha(-1)) were reached in July, coinciding with the highest biomass | ||
| 113 | (3.72 kg DW m(-2)), which then decreased to approximately half in | 123 | (3.72 kg DW m(-2)), which then decreased to approximately half in | ||
| 114 | August. Nutrient content in the aboveground tissues was highly | 124 | August. Nutrient content in the aboveground tissues was highly | ||
| 115 | dependent on the ammonium and nitrate water concentrations. In | 125 | dependent on the ammonium and nitrate water concentrations. In | ||
| 116 | addition, the N content was inversely related to the C-org/N of | 126 | addition, the N content was inversely related to the C-org/N of | ||
| 117 | sediments, while the P content was influenced positively by the | 127 | sediments, while the P content was influenced positively by the | ||
| 118 | phosphorous concentration of the water. Common reed of the Albujn | 128 | phosphorous concentration of the water. Common reed of the Albujn | ||
| 119 | rambla corresponds to the assimilation type, adapted to nutrient-rich | 129 | rambla corresponds to the assimilation type, adapted to nutrient-rich | ||
| 120 | habitats, which is characterized by a pronounced external N cycle and | 130 | habitats, which is characterized by a pronounced external N cycle and | ||
| 121 | P internal reserves. Based on the results obtained, we propose a | 131 | P internal reserves. Based on the results obtained, we propose a | ||
| 122 | management plan for common reed to help control eutrophication of the | 132 | management plan for common reed to help control eutrophication of the | ||
| 123 | Mar Menor lagoon. This would bring forward reed cutting to the | 133 | Mar Menor lagoon. This would bring forward reed cutting to the | ||
| 124 | beginning of summer, instead of August, coinciding with the time of | 134 | beginning of summer, instead of August, coinciding with the time of | ||
| 125 | maximum aerial biomass, greater nutrient retention, and lower risk of | 135 | maximum aerial biomass, greater nutrient retention, and lower risk of | ||
| 126 | strong precipitation.", | 136 | strong precipitation.", | ||
| 127 | "notes_translated": { | 137 | "notes_translated": { | ||
| 128 | "es": "We studied nutrient removal by Phragmites australis in the | 138 | "es": "We studied nutrient removal by Phragmites australis in the | ||
| 129 | Albujn rambla, the main drainage system that discharges into the Mar | 139 | Albujn rambla, the main drainage system that discharges into the Mar | ||
| 130 | Menor, a Mediterranean coastal lagoon of high conservation interest, | 140 | Menor, a Mediterranean coastal lagoon of high conservation interest, | ||
| 131 | but highly threatened by point and nonpoint pollution derived from | 141 | but highly threatened by point and nonpoint pollution derived from | ||
| 132 | tourism and agricultural activities. We measured aerial biomass and N | 142 | tourism and agricultural activities. We measured aerial biomass and N | ||
| 133 | and P concentrations in both aboveground and belowground tissues of | 143 | and P concentrations in both aboveground and belowground tissues of | ||
| 134 | common reed during an annual cycle that included two cutting events | 144 | common reed during an annual cycle that included two cutting events | ||
| 135 | and two periods of reed growth (one at the end of summer after cutting | 145 | and two periods of reed growth (one at the end of summer after cutting | ||
| 136 | and another at the beginning of spring, following their natural | 146 | and another at the beginning of spring, following their natural | ||
| 137 | cycle). The temporal variation of N and P concentrations was related | 147 | cycle). The temporal variation of N and P concentrations was related | ||
| 138 | to the phenology of the plant and cutting events. The maximum nutrient | 148 | to the phenology of the plant and cutting events. The maximum nutrient | ||
| 139 | concentrations were recorded in young stems in the initial stages of | 149 | concentrations were recorded in young stems in the initial stages of | ||
| 140 | the autumn growing season (35.86 mg N g(-1) and 2.38 mg P g(-1)). The | 150 | the autumn growing season (35.86 mg N g(-1) and 2.38 mg P g(-1)). The | ||
| 141 | phosphorus dynamics showed evidence of translocation processes related | 151 | phosphorus dynamics showed evidence of translocation processes related | ||
| 142 | with growth activity, although no evidence of N translocation was | 152 | with growth activity, although no evidence of N translocation was | ||
| 143 | found. In November and in summer, when aerial growth ceases because of | 153 | found. In November and in summer, when aerial growth ceases because of | ||
| 144 | the hard conditions, the P concentration in rhizomes was higher than | 154 | the hard conditions, the P concentration in rhizomes was higher than | ||
| 145 | in stems, while in spring and in September, the period of maximal | 155 | in stems, while in spring and in September, the period of maximal | ||
| 146 | growth, the reverse relation was found. The highest total amounts of | 156 | growth, the reverse relation was found. The highest total amounts of | ||
| 147 | the two elements in the aboveground biomass (0.54 Tm N ha(-1) and 0.25 | 157 | the two elements in the aboveground biomass (0.54 Tm N ha(-1) and 0.25 | ||
| 148 | Tm P ha(-1)) were reached in July, coinciding with the highest biomass | 158 | Tm P ha(-1)) were reached in July, coinciding with the highest biomass | ||
| 149 | (3.72 kg DW m(-2)), which then decreased to approximately half in | 159 | (3.72 kg DW m(-2)), which then decreased to approximately half in | ||
| 150 | August. Nutrient content in the aboveground tissues was highly | 160 | August. Nutrient content in the aboveground tissues was highly | ||
| 151 | dependent on the ammonium and nitrate water concentrations. In | 161 | dependent on the ammonium and nitrate water concentrations. In | ||
| 152 | addition, the N content was inversely related to the C-org/N of | 162 | addition, the N content was inversely related to the C-org/N of | ||
| 153 | sediments, while the P content was influenced positively by the | 163 | sediments, while the P content was influenced positively by the | ||
| 154 | phosphorous concentration of the water. Common reed of the Albujn | 164 | phosphorous concentration of the water. Common reed of the Albujn | ||
| 155 | rambla corresponds to the assimilation type, adapted to nutrient-rich | 165 | rambla corresponds to the assimilation type, adapted to nutrient-rich | ||
| 156 | habitats, which is characterized by a pronounced external N cycle and | 166 | habitats, which is characterized by a pronounced external N cycle and | ||
| 157 | P internal reserves. Based on the results obtained, we propose a | 167 | P internal reserves. Based on the results obtained, we propose a | ||
| 158 | management plan for common reed to help control eutrophication of the | 168 | management plan for common reed to help control eutrophication of the | ||
| 159 | Mar Menor lagoon. This would bring forward reed cutting to the | 169 | Mar Menor lagoon. This would bring forward reed cutting to the | ||
| 160 | beginning of summer, instead of August, coinciding with the time of | 170 | beginning of summer, instead of August, coinciding with the time of | ||
| 161 | maximum aerial biomass, greater nutrient retention, and lower risk of | 171 | maximum aerial biomass, greater nutrient retention, and lower risk of | ||
| 162 | strong precipitation." | 172 | strong precipitation." | ||
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| 332 | Management Tool for Reduction of Pollution in the Mar Menor", | 342 | Management Tool for Reduction of Pollution in the Mar Menor", | ||
| 333 | "title_translated": { | 343 | "title_translated": { | ||
| 334 | "es": "Nutrient Bioaccumulation in Phragmites australis: | 344 | "es": "Nutrient Bioaccumulation in Phragmites australis: | ||
| 335 | Management Tool for Reduction of Pollution in the Mar Menor" | 345 | Management Tool for Reduction of Pollution in the Mar Menor" | ||
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