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| f | 1 | { | f | 1 | { |
| 2 | "access_rights": | 2 | "access_rights": | ||
| 3 | .europa.eu/metadata-codelist/LimitationsOnPublicAccess/noLimitations", | 3 | .europa.eu/metadata-codelist/LimitationsOnPublicAccess/noLimitations", | ||
| 4 | "alternate_identifier": "DOI: 10.1016/j.jenvman.2023.117292", | 4 | "alternate_identifier": "DOI: 10.1016/j.jenvman.2023.117292", | ||
| 5 | "applicable_legislation": [ | 5 | "applicable_legislation": [ | ||
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| 8 | "author": "Diaz-Garcia, C., Martinez-Sanchez, J.J. y Alvarez-Rogel, | 8 | "author": "Diaz-Garcia, C., Martinez-Sanchez, J.J. y Alvarez-Rogel, | ||
| 9 | J.", | 9 | J.", | ||
| 10 | "author_email": "cdiazg@illinois.edu", | 10 | "author_email": "cdiazg@illinois.edu", | ||
| 11 | "author_name": "Diaz-Garcia, C., Martinez-Sanchez, J.J. y | 11 | "author_name": "Diaz-Garcia, C., Martinez-Sanchez, J.J. y | ||
| 12 | Alvarez-Rogel, J.", | 12 | Alvarez-Rogel, J.", | ||
| 13 | "classification_variables": { | 13 | "classification_variables": { | ||
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| 17 | "https://www.boe.es/eli/es/res/2013/02/19/(4)" | 17 | "https://www.boe.es/eli/es/res/2013/02/19/(4)" | ||
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| 36 | "contact_url": "https://organismo.example.org/", | 36 | "contact_url": "https://organismo.example.org/", | ||
| 37 | "created": "2024-11-05", | 37 | "created": "2024-11-05", | ||
| 38 | "creator": [ | 38 | "creator": [ | ||
| 39 | { | 39 | { | ||
| 40 | "email": "cdiazg@illinois.edu", | 40 | "email": "cdiazg@illinois.edu", | ||
| 41 | "name": "Diaz-Garcia, C., Martinez-Sanchez, J.J. y | 41 | "name": "Diaz-Garcia, C., Martinez-Sanchez, J.J. y | ||
| 42 | Alvarez-Rogel, J." | 42 | Alvarez-Rogel, J." | ||
| 43 | } | 43 | } | ||
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| 58 | "identifier": "de7545bc-ef39-5ac8-89ac-2ee5701b607b", | 58 | "identifier": "de7545bc-ef39-5ac8-89ac-2ee5701b607b", | ||
| 59 | "isopen": true, | 59 | "isopen": true, | ||
| 60 | "keyword_iepnb": [ | 60 | "keyword_iepnb": [ | ||
| 61 | "agricultura", | 61 | "agricultura", | ||
| 62 | "contaminacion", | 62 | "contaminacion", | ||
| 63 | "desalacion", | 63 | "desalacion", | ||
| 64 | "mitigacion", | 64 | "mitigacion", | ||
| 65 | "tecnologia" | 65 | "tecnologia" | ||
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| 69 | "license_id": "cc-by", | 69 | "license_id": "cc-by", | ||
| 70 | "license_title": "Creative Commons Attribution", | 70 | "license_title": "Creative Commons Attribution", | ||
| 71 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | 71 | "license_url": "http://www.opendefinition.org/licenses/cc-by", | ||
| 72 | "lineage_source": [ | 72 | "lineage_source": [ | ||
| 73 | "Journal of Environmental Management", | 73 | "Journal of Environmental Management", | ||
| 74 | "vol 331" | 74 | "vol 331" | ||
| 75 | ], | 75 | ], | ||
| 76 | "maintainer": "", | 76 | "maintainer": "", | ||
| 77 | "maintainer_name": "", | 77 | "maintainer_name": "", | ||
| 78 | "metadata_created": "2026-06-23T14:48:40.936242", | 78 | "metadata_created": "2026-06-23T14:48:40.936242", | ||
| n | 79 | "metadata_modified": "2026-06-23T15:51:40.577529", | n | 79 | "metadata_modified": "2026-06-23T15:57:57.941838", |
| 80 | "metadata_profile": [ | 80 | "metadata_profile": [ | ||
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| 83 | "miteco_data_population": { | 83 | "miteco_data_population": { | ||
| 84 | "es": "" | 84 | "es": "" | ||
| 85 | }, | 85 | }, | ||
| 86 | "miteco_data_territory": { | 86 | "miteco_data_territory": { | ||
| 87 | "es": "" | 87 | "es": "" | ||
| 88 | }, | 88 | }, | ||
| 89 | "miteco_dataset_type": | 89 | "miteco_dataset_type": | ||
| 90 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | 90 | //publications.europa.eu/resource/authority/dataset-type/STATISTICAL", | ||
| 91 | "miteco_geo_level": "1", | 91 | "miteco_geo_level": "1", | ||
| 92 | "modified": "2026-06-23", | 92 | "modified": "2026-06-23", | ||
| 93 | "name": "de7545bc-ef39-5ac8-89ac-2ee5701b607b", | 93 | "name": "de7545bc-ef39-5ac8-89ac-2ee5701b607b", | ||
| 94 | "notes": "Leachates from intensive agriculture containing high | 94 | "notes": "Leachates from intensive agriculture containing high | ||
| 95 | nitrate have been identified as a major cause of the severe | 95 | nitrate have been identified as a major cause of the severe | ||
| 96 | eutrophication crisis that impacts Mar Menor (SE Spain), the largest | 96 | eutrophication crisis that impacts Mar Menor (SE Spain), the largest | ||
| 97 | hypersaline coastal lagoon in the Medi-terranean basin. A best | 97 | hypersaline coastal lagoon in the Medi-terranean basin. A best | ||
| 98 | management practice for removing NO3--N is denitrifying bioreactors. | 98 | management practice for removing NO3--N is denitrifying bioreactors. | ||
| 99 | This is the first study to assess the efficiency of citrus woodchips | 99 | This is the first study to assess the efficiency of citrus woodchips | ||
| 100 | bioreactors in treating agricultural leachates that flow to the Mar | 100 | bioreactors in treating agricultural leachates that flow to the Mar | ||
| 101 | Menor via surface discharges. Denitrification capacity, woodchip | 101 | Menor via surface discharges. Denitrification capacity, woodchip | ||
| 102 | degradation (by weight loss), formation of potentially harmful | 102 | degradation (by weight loss), formation of potentially harmful | ||
| 103 | compounds, and greenhouse gas (GHG) emissions were assessed. Three | 103 | compounds, and greenhouse gas (GHG) emissions were assessed. Three | ||
| 104 | bioreactors (6 m x 0.98 m x 1.2 m) filled with citrus woodchips (3 | 104 | bioreactors (6 m x 0.98 m x 1.2 m) filled with citrus woodchips (3 | ||
| 105 | m(3) d(-1) per bioreactor) through which the untreated ditch water | 105 | m(3) d(-1) per bioreactor) through which the untreated ditch water | ||
| 106 | over 1.5 years. Bioreactors were operated at 8 h, 16 h, and 24 h | 106 | over 1.5 years. Bioreactors were operated at 8 h, 16 h, and 24 h | ||
| 107 | hydraulic residence time respectively, in each bioreactor. The main | 107 | hydraulic residence time respectively, in each bioreactor. The main | ||
| 108 | characteristics of the ditch water were: pH approximate to 7.5-8.0, | 108 | characteristics of the ditch water were: pH approximate to 7.5-8.0, | ||
| 109 | electrical conductivity approximate to 5-8 dS m-1, dissolved organic | 109 | electrical conductivity approximate to 5-8 dS m-1, dissolved organic | ||
| 110 | carbon approximate to 6-10 mg L-1, and NO3--N approximate to 22-45 mg | 110 | carbon approximate to 6-10 mg L-1, and NO3--N approximate to 22-45 mg | ||
| 111 | L-1. Bioreactors were highly efficient in reducing NO3--N. The average | 111 | L-1. Bioreactors were highly efficient in reducing NO3--N. The average | ||
| 112 | RNO3 in effluents was for the complete experimental period 8 g N m(-3) | 112 | RNO3 in effluents was for the complete experimental period 8 g N m(-3) | ||
| 113 | d(-1), 10.9 g N m(-3) d(-1), and 12.6 g N m(-3) d(-1) for 8, 16 and 24 | 113 | d(-1), 10.9 g N m(-3) d(-1), and 12.6 g N m(-3) d(-1) for 8, 16 and 24 | ||
| 114 | h residence time, respectively. Nitrate reduction efficiency was | 114 | h residence time, respectively. Nitrate reduction efficiency was | ||
| 115 | modulated by seasonal changes in temperature, with an increasing | 115 | modulated by seasonal changes in temperature, with an increasing | ||
| 116 | efficiency in warmer periods (maximum approximate to 85-90% for all | 116 | efficiency in warmer periods (maximum approximate to 85-90% for all | ||
| 117 | hydraulic residence time) and decreasing in colder ones (minimum | 117 | hydraulic residence time) and decreasing in colder ones (minimum | ||
| 118 | approximate to 12%, 23% and 41% for hydraulic residence time 8, 16 and | 118 | approximate to 12%, 23% and 41% for hydraulic residence time 8, 16 and | ||
| 119 | 24 h respectively). Woodchips degradation was greatest during the | 119 | 24 h respectively). Woodchips degradation was greatest during the | ||
| 120 | first six months (average approximate to 29% weight loss) in the | 120 | first six months (average approximate to 29% weight loss) in the | ||
| 121 | material above the water level, attributable to aerobic mineralization | 121 | material above the water level, attributable to aerobic mineralization | ||
| 122 | of the organic carbon, while weight loss was approximate to 11% in | 122 | of the organic carbon, while weight loss was approximate to 11% in | ||
| 123 | woodchip media continuously below the water level. Dissolved organic | 123 | woodchip media continuously below the water level. Dissolved organic | ||
| 124 | carbon, sulfide, ammonium, and soluble phosphorus concentrations in | 124 | carbon, sulfide, ammonium, and soluble phosphorus concentrations in | ||
| 125 | the effluents were mostly low, although some peaks in concentrations | 125 | the effluents were mostly low, although some peaks in concentrations | ||
| 126 | occurred. Design consideration must be taken to avoid environmental | 126 | occurred. Design consideration must be taken to avoid environmental | ||
| 127 | impacts due to the occasional presence of harmful compounds in the | 127 | impacts due to the occasional presence of harmful compounds in the | ||
| 128 | effluents.", | 128 | effluents.", | ||
| 129 | "notes_translated": { | 129 | "notes_translated": { | ||
| 130 | "es": "Leachates from intensive agriculture containing high | 130 | "es": "Leachates from intensive agriculture containing high | ||
| 131 | nitrate have been identified as a major cause of the severe | 131 | nitrate have been identified as a major cause of the severe | ||
| 132 | eutrophication crisis that impacts Mar Menor (SE Spain), the largest | 132 | eutrophication crisis that impacts Mar Menor (SE Spain), the largest | ||
| 133 | hypersaline coastal lagoon in the Medi-terranean basin. A best | 133 | hypersaline coastal lagoon in the Medi-terranean basin. A best | ||
| 134 | management practice for removing NO3--N is denitrifying bioreactors. | 134 | management practice for removing NO3--N is denitrifying bioreactors. | ||
| 135 | This is the first study to assess the efficiency of citrus woodchips | 135 | This is the first study to assess the efficiency of citrus woodchips | ||
| 136 | bioreactors in treating agricultural leachates that flow to the Mar | 136 | bioreactors in treating agricultural leachates that flow to the Mar | ||
| 137 | Menor via surface discharges. Denitrification capacity, woodchip | 137 | Menor via surface discharges. Denitrification capacity, woodchip | ||
| 138 | degradation (by weight loss), formation of potentially harmful | 138 | degradation (by weight loss), formation of potentially harmful | ||
| 139 | compounds, and greenhouse gas (GHG) emissions were assessed. Three | 139 | compounds, and greenhouse gas (GHG) emissions were assessed. Three | ||
| 140 | bioreactors (6 m x 0.98 m x 1.2 m) filled with citrus woodchips (3 | 140 | bioreactors (6 m x 0.98 m x 1.2 m) filled with citrus woodchips (3 | ||
| 141 | m(3) d(-1) per bioreactor) through which the untreated ditch water | 141 | m(3) d(-1) per bioreactor) through which the untreated ditch water | ||
| 142 | over 1.5 years. Bioreactors were operated at 8 h, 16 h, and 24 h | 142 | over 1.5 years. Bioreactors were operated at 8 h, 16 h, and 24 h | ||
| 143 | hydraulic residence time respectively, in each bioreactor. The main | 143 | hydraulic residence time respectively, in each bioreactor. The main | ||
| 144 | characteristics of the ditch water were: pH approximate to 7.5-8.0, | 144 | characteristics of the ditch water were: pH approximate to 7.5-8.0, | ||
| 145 | electrical conductivity approximate to 5-8 dS m-1, dissolved organic | 145 | electrical conductivity approximate to 5-8 dS m-1, dissolved organic | ||
| 146 | carbon approximate to 6-10 mg L-1, and NO3--N approximate to 22-45 mg | 146 | carbon approximate to 6-10 mg L-1, and NO3--N approximate to 22-45 mg | ||
| 147 | L-1. Bioreactors were highly efficient in reducing NO3--N. The average | 147 | L-1. Bioreactors were highly efficient in reducing NO3--N. The average | ||
| 148 | RNO3 in effluents was for the complete experimental period 8 g N m(-3) | 148 | RNO3 in effluents was for the complete experimental period 8 g N m(-3) | ||
| 149 | d(-1), 10.9 g N m(-3) d(-1), and 12.6 g N m(-3) d(-1) for 8, 16 and 24 | 149 | d(-1), 10.9 g N m(-3) d(-1), and 12.6 g N m(-3) d(-1) for 8, 16 and 24 | ||
| 150 | h residence time, respectively. Nitrate reduction efficiency was | 150 | h residence time, respectively. Nitrate reduction efficiency was | ||
| 151 | modulated by seasonal changes in temperature, with an increasing | 151 | modulated by seasonal changes in temperature, with an increasing | ||
| 152 | efficiency in warmer periods (maximum approximate to 85-90% for all | 152 | efficiency in warmer periods (maximum approximate to 85-90% for all | ||
| 153 | hydraulic residence time) and decreasing in colder ones (minimum | 153 | hydraulic residence time) and decreasing in colder ones (minimum | ||
| 154 | approximate to 12%, 23% and 41% for hydraulic residence time 8, 16 and | 154 | approximate to 12%, 23% and 41% for hydraulic residence time 8, 16 and | ||
| 155 | 24 h respectively). Woodchips degradation was greatest during the | 155 | 24 h respectively). Woodchips degradation was greatest during the | ||
| 156 | first six months (average approximate to 29% weight loss) in the | 156 | first six months (average approximate to 29% weight loss) in the | ||
| 157 | material above the water level, attributable to aerobic mineralization | 157 | material above the water level, attributable to aerobic mineralization | ||
| 158 | of the organic carbon, while weight loss was approximate to 11% in | 158 | of the organic carbon, while weight loss was approximate to 11% in | ||
| 159 | woodchip media continuously below the water level. Dissolved organic | 159 | woodchip media continuously below the water level. Dissolved organic | ||
| 160 | carbon, sulfide, ammonium, and soluble phosphorus concentrations in | 160 | carbon, sulfide, ammonium, and soluble phosphorus concentrations in | ||
| 161 | the effluents were mostly low, although some peaks in concentrations | 161 | the effluents were mostly low, although some peaks in concentrations | ||
| 162 | occurred. Design consideration must be taken to avoid environmental | 162 | occurred. Design consideration must be taken to avoid environmental | ||
| 163 | impacts due to the occasional presence of harmful compounds in the | 163 | impacts due to the occasional presence of harmful compounds in the | ||
| 164 | effluents." | 164 | effluents." | ||
| 165 | }, | 165 | }, | ||
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| 167 | "num_tags": 6, | 167 | "num_tags": 6, | ||
| 168 | "organization": { | 168 | "organization": { | ||
| 169 | "approval_status": "approved", | 169 | "approval_status": "approved", | ||
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| 188 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | 188 | "name": "\u00c1rea de Banco de Datos de la Naturaleza. | ||
| 189 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | 189 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | ||
| 190 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 190 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
| 191 | Demogr\u00e1fico", | 191 | Demogr\u00e1fico", | ||
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| 199 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | 199 | Direcci\u00f3n General Biodiversidad, Bosques y Desertificaci\u00f3n. | ||
| 200 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | 200 | Ministerio para la Transici\u00f3n Ecol\u00f3gica y el Reto | ||
| 201 | Demogr\u00e1fico", | 201 | Demogr\u00e1fico", | ||
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| 205 | "publisher_url": "https://www.miteco.gob.es/", | 205 | "publisher_url": "https://www.miteco.gob.es/", | ||
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| 336 | "title_translated": { | 336 | "title_translated": { | ||
| 337 | "es": "Woodchip bioreactors for saline leachates denitrification | 337 | "es": "Woodchip bioreactors for saline leachates denitrification | ||
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