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) en The case of Mar Menor eutrophication: State of the art and description of tested Nature-Based Solutions
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| 4 | "alternate_identifier": "DOI: 10.1016/j.ecoleng.2020.106086", | 4 | "alternate_identifier": "DOI: 10.1016/j.ecoleng.2020.106086", | ||
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| 55 | "dataset_scope": "non_spatial_dataset", | 55 | "dataset_scope": "non_spatial_dataset", | ||
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| 63 | "description": "Grupo de conjuntos de datos del Mar Menor.", | ||||
| 64 | "display_name": "Mar Menor", | ||||
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| 69 | "title": "Mar Menor" | ||||
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| 100 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | 110 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | ||
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| n | 102 | "modified": "2026-06-23", | n | 112 | "modified": "2026-06-25", |
| 103 | "name": "ffac4631-1644-586b-b72a-c6ad8a277cea", | 113 | "name": "ffac4631-1644-586b-b72a-c6ad8a277cea", | ||
| 104 | "notes": "The Mar Menor (SE Spain), the largest hypersaline coastal | 114 | "notes": "The Mar Menor (SE Spain), the largest hypersaline coastal | ||
| 105 | lagoon of the Mediterranean basin, suffers a severe eutrophication | 115 | lagoon of the Mediterranean basin, suffers a severe eutrophication | ||
| 106 | crisis due to the nutrients that receives from the Campo de Cartagena | 116 | crisis due to the nutrients that receives from the Campo de Cartagena | ||
| 107 | watershed, mainly nitrate from intensive agriculture. This paper | 117 | watershed, mainly nitrate from intensive agriculture. This paper | ||
| 108 | updates the state of the art in relation with nutrient discharges to | 118 | updates the state of the art in relation with nutrient discharges to | ||
| 109 | the Mar Menor, and summarizes results from different tested | 119 | the Mar Menor, and summarizes results from different tested | ||
| 110 | Nature-Based Solution (NBS). Specifically, we show i) results from a | 120 | Nature-Based Solution (NBS). Specifically, we show i) results from a | ||
| 111 | pilot plant with woodchip bioreactors for nitrate-enriched brine | 121 | pilot plant with woodchip bioreactors for nitrate-enriched brine | ||
| 112 | denitrification, and ii) the first results obtained in a pilot plant | 122 | denitrification, and ii) the first results obtained in a pilot plant | ||
| 113 | with bioreactors and constructed wetlands for treatment of | 123 | with bioreactors and constructed wetlands for treatment of | ||
| 114 | agricultural drainage water and leachates, as well as other effluents. | 124 | agricultural drainage water and leachates, as well as other effluents. | ||
| 115 | Nutrient discharges to the lagoon are highly variable and occur via | 125 | Nutrient discharges to the lagoon are highly variable and occur via | ||
| 116 | drainage network, drains, stormwater pipes, direct groundwater | 126 | drainage network, drains, stormwater pipes, direct groundwater | ||
| 117 | discharges from the Quaternary aquifer, and others. For instance, | 127 | discharges from the Quaternary aquifer, and others. For instance, | ||
| 118 | between January 2017 and January 2018 measured daily superficial | 128 | between January 2017 and January 2018 measured daily superficial | ||
| 119 | discharge (floods excluded) ofN-NO3 \u2212 amounted from 119 kg | 129 | discharge (floods excluded) ofN-NO3 \u2212 amounted from 119 kg | ||
| 120 | d\u22121 to 1084 kg d\u22121. Estimations subsurface discharges ranged | 130 | d\u22121 to 1084 kg d\u22121. Estimations subsurface discharges ranged | ||
| 121 | 815 to 3836 kg N-NO3 \u2212 d\u22121 in 2018\u20132020. Field studies | 131 | 815 to 3836 kg N-NO3 \u2212 d\u22121 in 2018\u20132020. Field studies | ||
| 122 | in coastal wetlands (e.g. inflow \u224820\u201330 mg N-NO3 \u2212 | 132 | in coastal wetlands (e.g. inflow \u224820\u201330 mg N-NO3 \u2212 | ||
| 123 | L\u22121, removal \u224880\u201390%) and results from pilot plants | 133 | L\u22121, removal \u224880\u201390%) and results from pilot plants | ||
| 124 | with bioreactors (e.g. inflow \u224830\u201340 mg N-NO3 \u2212 | 134 | with bioreactors (e.g. inflow \u224830\u201340 mg N-NO3 \u2212 | ||
| 125 | L\u22121, re\u0002moval \u224890\u201395%) and constructed wetlands | 135 | L\u22121, re\u0002moval \u224890\u201395%) and constructed wetlands | ||
| 126 | (e.g. inflow \u224830\u201340 mg N-NO3 \u2212 L\u22121, removal | 136 | (e.g. inflow \u224830\u201340 mg N-NO3 \u2212 L\u22121, removal | ||
| 127 | \u224860\u201370%), showed the good performance of these systems for | 137 | \u224860\u201370%), showed the good performance of these systems for | ||
| 128 | nutrient retention. Four strategies are considered for reducing | 138 | nutrient retention. Four strategies are considered for reducing | ||
| 129 | nu\u0002trient inputs into the Mar Menor, which include a combination | 139 | nu\u0002trient inputs into the Mar Menor, which include a combination | ||
| 130 | of nature-based solutions and best management practices. (i) Reducing | 140 | of nature-based solutions and best management practices. (i) Reducing | ||
| 131 | the leaching of nitrate to the aquifer and export of nutrients and | 141 | the leaching of nitrate to the aquifer and export of nutrients and | ||
| 132 | sediments following heavy rains by improving fertilization, and | 142 | sediments following heavy rains by improving fertilization, and | ||
| 133 | irrigation routines, and soil conservation measures in the | 143 | irrigation routines, and soil conservation measures in the | ||
| 134 | agricultural fields. (ii) Development of effective and scalable tools | 144 | agricultural fields. (ii) Development of effective and scalable tools | ||
| 135 | for denitrification of nitrate-rich brine produced by on\u0002farm | 145 | for denitrification of nitrate-rich brine produced by on\u0002farm | ||
| 136 | desalination plants. (iii) Capture and treatment of polluted water | 146 | desalination plants. (iii) Capture and treatment of polluted water | ||
| 137 | discharged to the Mar Menor via hy\u0002drologic networks, subsurface | 147 | discharged to the Mar Menor via hy\u0002drologic networks, subsurface | ||
| 138 | flow, drainage ditches, and others. (iv) Preservation and restoration | 148 | flow, drainage ditches, and others. (iv) Preservation and restoration | ||
| 139 | of coastal wetlands.", | 149 | of coastal wetlands.", | ||
| 140 | "notes_translated": { | 150 | "notes_translated": { | ||
| 141 | "es": "The Mar Menor (SE Spain), the largest hypersaline coastal | 151 | "es": "The Mar Menor (SE Spain), the largest hypersaline coastal | ||
| 142 | lagoon of the Mediterranean basin, suffers a severe eutrophication | 152 | lagoon of the Mediterranean basin, suffers a severe eutrophication | ||
| 143 | crisis due to the nutrients that receives from the Campo de Cartagena | 153 | crisis due to the nutrients that receives from the Campo de Cartagena | ||
| 144 | watershed, mainly nitrate from intensive agriculture. This paper | 154 | watershed, mainly nitrate from intensive agriculture. This paper | ||
| 145 | updates the state of the art in relation with nutrient discharges to | 155 | updates the state of the art in relation with nutrient discharges to | ||
| 146 | the Mar Menor, and summarizes results from different tested | 156 | the Mar Menor, and summarizes results from different tested | ||
| 147 | Nature-Based Solution (NBS). Specifically, we show i) results from a | 157 | Nature-Based Solution (NBS). Specifically, we show i) results from a | ||
| 148 | pilot plant with woodchip bioreactors for nitrate-enriched brine | 158 | pilot plant with woodchip bioreactors for nitrate-enriched brine | ||
| 149 | denitrification, and ii) the first results obtained in a pilot plant | 159 | denitrification, and ii) the first results obtained in a pilot plant | ||
| 150 | with bioreactors and constructed wetlands for treatment of | 160 | with bioreactors and constructed wetlands for treatment of | ||
| 151 | agricultural drainage water and leachates, as well as other effluents. | 161 | agricultural drainage water and leachates, as well as other effluents. | ||
| 152 | Nutrient discharges to the lagoon are highly variable and occur via | 162 | Nutrient discharges to the lagoon are highly variable and occur via | ||
| 153 | drainage network, drains, stormwater pipes, direct groundwater | 163 | drainage network, drains, stormwater pipes, direct groundwater | ||
| 154 | discharges from the Quaternary aquifer, and others. For instance, | 164 | discharges from the Quaternary aquifer, and others. For instance, | ||
| 155 | between January 2017 and January 2018 measured daily superficial | 165 | between January 2017 and January 2018 measured daily superficial | ||
| 156 | discharge (floods excluded) ofN-NO3 \u2212 amounted from 119 kg | 166 | discharge (floods excluded) ofN-NO3 \u2212 amounted from 119 kg | ||
| 157 | d\u22121 to 1084 kg d\u22121. Estimations subsurface discharges ranged | 167 | d\u22121 to 1084 kg d\u22121. Estimations subsurface discharges ranged | ||
| 158 | 815 to 3836 kg N-NO3 \u2212 d\u22121 in 2018\u20132020. Field studies | 168 | 815 to 3836 kg N-NO3 \u2212 d\u22121 in 2018\u20132020. Field studies | ||
| 159 | in coastal wetlands (e.g. inflow \u224820\u201330 mg N-NO3 \u2212 | 169 | in coastal wetlands (e.g. inflow \u224820\u201330 mg N-NO3 \u2212 | ||
| 160 | L\u22121, removal \u224880\u201390%) and results from pilot plants | 170 | L\u22121, removal \u224880\u201390%) and results from pilot plants | ||
| 161 | with bioreactors (e.g. inflow \u224830\u201340 mg N-NO3 \u2212 | 171 | with bioreactors (e.g. inflow \u224830\u201340 mg N-NO3 \u2212 | ||
| 162 | L\u22121, re\u0002moval \u224890\u201395%) and constructed wetlands | 172 | L\u22121, re\u0002moval \u224890\u201395%) and constructed wetlands | ||
| 163 | (e.g. inflow \u224830\u201340 mg N-NO3 \u2212 L\u22121, removal | 173 | (e.g. inflow \u224830\u201340 mg N-NO3 \u2212 L\u22121, removal | ||
| 164 | \u224860\u201370%), showed the good performance of these systems for | 174 | \u224860\u201370%), showed the good performance of these systems for | ||
| 165 | nutrient retention. Four strategies are considered for reducing | 175 | nutrient retention. Four strategies are considered for reducing | ||
| 166 | nu\u0002trient inputs into the Mar Menor, which include a combination | 176 | nu\u0002trient inputs into the Mar Menor, which include a combination | ||
| 167 | of nature-based solutions and best management practices. (i) Reducing | 177 | of nature-based solutions and best management practices. (i) Reducing | ||
| 168 | the leaching of nitrate to the aquifer and export of nutrients and | 178 | the leaching of nitrate to the aquifer and export of nutrients and | ||
| 169 | sediments following heavy rains by improving fertilization, and | 179 | sediments following heavy rains by improving fertilization, and | ||
| 170 | irrigation routines, and soil conservation measures in the | 180 | irrigation routines, and soil conservation measures in the | ||
| 171 | agricultural fields. (ii) Development of effective and scalable tools | 181 | agricultural fields. (ii) Development of effective and scalable tools | ||
| 172 | for denitrification of nitrate-rich brine produced by on\u0002farm | 182 | for denitrification of nitrate-rich brine produced by on\u0002farm | ||
| 173 | desalination plants. (iii) Capture and treatment of polluted water | 183 | desalination plants. (iii) Capture and treatment of polluted water | ||
| 174 | discharged to the Mar Menor via hy\u0002drologic networks, subsurface | 184 | discharged to the Mar Menor via hy\u0002drologic networks, subsurface | ||
| 175 | flow, drainage ditches, and others. (iv) Preservation and restoration | 185 | flow, drainage ditches, and others. (iv) Preservation and restoration | ||
| 176 | of coastal wetlands." | 186 | of coastal wetlands." | ||
| 177 | }, | 187 | }, | ||
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| 179 | "num_tags": 7, | 189 | "num_tags": 7, | ||
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| 202 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 212 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
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