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En el instante 23 de junio de 2026, 15:51:43 UTC,
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Modificado el valor del campo
spatial_coverage
a[{'bbox': '{"type": "Polygon", "coordinates": [[[-18.16, 27.64], [4.32, 27.64], [4.32, 43.79], [-18.16, 43.79], [-18.16, 27.64]]]}', 'centroid': '{"type": "Point", "coordinates": [-6.92, 35.715]}', 'text': 'España', 'uri': 'http://datos.gob.es/recurso/sector-publico/territorio/Pais/España'}]
en Efficient irrigation management can contribute to reduce soil CO2 emissions in agriculture
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| 93 | "name": "de145167-102c-59fb-94f3-e2aac85e3eec", | 93 | "name": "de145167-102c-59fb-94f3-e2aac85e3eec", | ||
| 94 | "notes": "Irrigation water restrictions in the Mediterranean area | 94 | "notes": "Irrigation water restrictions in the Mediterranean area | ||
| 95 | have created a growing interest in water conservation. Apart from | 95 | have created a growing interest in water conservation. Apart from | ||
| 96 | environmental and economic benefits by water savings, regulated | 96 | environmental and economic benefits by water savings, regulated | ||
| 97 | deficit irrigation (RDI) may contribute to reduce soil CO2 emissions | 97 | deficit irrigation (RDI) may contribute to reduce soil CO2 emissions | ||
| 98 | and enhance C sequestration in soils, by decreasing microbial activity | 98 | and enhance C sequestration in soils, by decreasing microbial activity | ||
| 99 | in response to decreased soil moisture levels. An experiment was | 99 | in response to decreased soil moisture levels. An experiment was | ||
| 100 | established in an orchard for one year to inves\u0002tigate the | 100 | established in an orchard for one year to inves\u0002tigate the | ||
| 101 | effects of three irrigation strategies on soil CO2 emissions, soil C | 101 | effects of three irrigation strategies on soil CO2 emissions, soil C | ||
| 102 | pool dynamics and aggregate content and stability. Three irrigation | 102 | pool dynamics and aggregate content and stability. Three irrigation | ||
| 103 | treatments were assayed: full irrigation (FI), RDI1, irrigated as FI | 103 | treatments were assayed: full irrigation (FI), RDI1, irrigated as FI | ||
| 104 | except for the postharvest period where 50% of FI was applied; and | 104 | except for the postharvest period where 50% of FI was applied; and | ||
| 105 | severe RDI (RDI2), irrigated as RDI1, except for two periods in which | 105 | severe RDI (RDI2), irrigated as RDI1, except for two periods in which | ||
| 106 | irrigation was suppressed. Soil CO2 emissions were monitored every 15 | 106 | irrigation was suppressed. Soil CO2 emissions were monitored every 15 | ||
| 107 | d. Soil sampling was carried out every three months. Soil | 107 | d. Soil sampling was carried out every three months. Soil | ||
| 108 | fractionation was also carried out (b50, 50\u2013250, 250\u2013850, | 108 | fractionation was also carried out (b50, 50\u2013250, 250\u2013850, | ||
| 109 | 850\u20132000) to assess the weight, C content and aggregate stability | 109 | 850\u20132000) to assess the weight, C content and aggregate stability | ||
| 110 | of each fraction. The application of deficit caused a significant | 110 | of each fraction. The application of deficit caused a significant | ||
| 111 | decrease in CO2 emission rates, mainly in RDI2, with rates of, in | 111 | decrease in CO2 emission rates, mainly in RDI2, with rates of, in | ||
| 112 | average, 35 mg CO2-C m\u22122 h\u22121 lower than that of FI during | 112 | average, 35 mg CO2-C m\u22122 h\u22121 lower than that of FI during | ||
| 113 | the period when deficit was applied. Cumulative CO2-C released for one | 113 | the period when deficit was applied. Cumulative CO2-C released for one | ||
| 114 | year showed a total release of 410 g CO2-C m\u22122 in FI, 355 g CO2-C | 114 | year showed a total release of 410 g CO2-C m\u22122 in FI, 355 g CO2-C | ||
| 115 | m\u22122 in RDI1, and 251 g CO2-C m\u22122 in RDI2. Soil organic C, | 115 | m\u22122 in RDI1, and 251 g CO2-C m\u22122 in RDI2. Soil organic C, | ||
| 116 | recal\u0002citrant C and organic functional groups showed no | 116 | recal\u0002citrant C and organic functional groups showed no | ||
| 117 | significant differences among treatments. The labile organic fractions | 117 | significant differences among treatments. The labile organic fractions | ||
| 118 | increased under FI in summer, likely due to increments in microbial | 118 | increased under FI in summer, likely due to increments in microbial | ||
| 119 | biomass C and enzyme activities. Irrigation treatments did not have a | 119 | biomass C and enzyme activities. Irrigation treatments did not have a | ||
| 120 | strong effect on the amount and stability of aggregates, but increased | 120 | strong effect on the amount and stability of aggregates, but increased | ||
| 121 | SOC content in the coarse fraction under RDI2. No effect of irrigation | 121 | SOC content in the coarse fraction under RDI2. No effect of irrigation | ||
| 122 | was observed in inorganic C content", | 122 | was observed in inorganic C content", | ||
| 123 | "notes_translated": { | 123 | "notes_translated": { | ||
| 124 | "es": "Irrigation water restrictions in the Mediterranean area | 124 | "es": "Irrigation water restrictions in the Mediterranean area | ||
| 125 | have created a growing interest in water conservation. Apart from | 125 | have created a growing interest in water conservation. Apart from | ||
| 126 | environmental and economic benefits by water savings, regulated | 126 | environmental and economic benefits by water savings, regulated | ||
| 127 | deficit irrigation (RDI) may contribute to reduce soil CO2 emissions | 127 | deficit irrigation (RDI) may contribute to reduce soil CO2 emissions | ||
| 128 | and enhance C sequestration in soils, by decreasing microbial activity | 128 | and enhance C sequestration in soils, by decreasing microbial activity | ||
| 129 | in response to decreased soil moisture levels. An experiment was | 129 | in response to decreased soil moisture levels. An experiment was | ||
| 130 | established in an orchard for one year to inves\u0002tigate the | 130 | established in an orchard for one year to inves\u0002tigate the | ||
| 131 | effects of three irrigation strategies on soil CO2 emissions, soil C | 131 | effects of three irrigation strategies on soil CO2 emissions, soil C | ||
| 132 | pool dynamics and aggregate content and stability. Three irrigation | 132 | pool dynamics and aggregate content and stability. Three irrigation | ||
| 133 | treatments were assayed: full irrigation (FI), RDI1, irrigated as FI | 133 | treatments were assayed: full irrigation (FI), RDI1, irrigated as FI | ||
| 134 | except for the postharvest period where 50% of FI was applied; and | 134 | except for the postharvest period where 50% of FI was applied; and | ||
| 135 | severe RDI (RDI2), irrigated as RDI1, except for two periods in which | 135 | severe RDI (RDI2), irrigated as RDI1, except for two periods in which | ||
| 136 | irrigation was suppressed. Soil CO2 emissions were monitored every 15 | 136 | irrigation was suppressed. Soil CO2 emissions were monitored every 15 | ||
| 137 | d. Soil sampling was carried out every three months. Soil | 137 | d. Soil sampling was carried out every three months. Soil | ||
| 138 | fractionation was also carried out (b50, 50\u2013250, 250\u2013850, | 138 | fractionation was also carried out (b50, 50\u2013250, 250\u2013850, | ||
| 139 | 850\u20132000) to assess the weight, C content and aggregate stability | 139 | 850\u20132000) to assess the weight, C content and aggregate stability | ||
| 140 | of each fraction. The application of deficit caused a significant | 140 | of each fraction. The application of deficit caused a significant | ||
| 141 | decrease in CO2 emission rates, mainly in RDI2, with rates of, in | 141 | decrease in CO2 emission rates, mainly in RDI2, with rates of, in | ||
| 142 | average, 35 mg CO2-C m\u22122 h\u22121 lower than that of FI during | 142 | average, 35 mg CO2-C m\u22122 h\u22121 lower than that of FI during | ||
| 143 | the period when deficit was applied. Cumulative CO2-C released for one | 143 | the period when deficit was applied. Cumulative CO2-C released for one | ||
| 144 | year showed a total release of 410 g CO2-C m\u22122 in FI, 355 g CO2-C | 144 | year showed a total release of 410 g CO2-C m\u22122 in FI, 355 g CO2-C | ||
| 145 | m\u22122 in RDI1, and 251 g CO2-C m\u22122 in RDI2. Soil organic C, | 145 | m\u22122 in RDI1, and 251 g CO2-C m\u22122 in RDI2. Soil organic C, | ||
| 146 | recal\u0002citrant C and organic functional groups showed no | 146 | recal\u0002citrant C and organic functional groups showed no | ||
| 147 | significant differences among treatments. The labile organic fractions | 147 | significant differences among treatments. The labile organic fractions | ||
| 148 | increased under FI in summer, likely due to increments in microbial | 148 | increased under FI in summer, likely due to increments in microbial | ||
| 149 | biomass C and enzyme activities. Irrigation treatments did not have a | 149 | biomass C and enzyme activities. Irrigation treatments did not have a | ||
| 150 | strong effect on the amount and stability of aggregates, but increased | 150 | strong effect on the amount and stability of aggregates, but increased | ||
| 151 | SOC content in the coarse fraction under RDI2. No effect of irrigation | 151 | SOC content in the coarse fraction under RDI2. No effect of irrigation | ||
| 152 | was observed in inorganic C content" | 152 | was observed in inorganic C content" | ||
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