Monitoring of nitrate leaching during flush flooding events in a coarse-textured floodplain soil
Author
dc.contributor.author
Salazar Guerrero, Osvaldo
Author
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Vargas, Juan
es_CL
Author
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Nájera de Ferrari, Francisco
es_CL
Author
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Seguel Seguel, Oscar
es_CL
Author
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Casanova Pinto, Manuel
es_CL
Admission date
dc.date.accessioned
2014-12-22T18:07:40Z
Available date
dc.date.available
2014-12-22T18:07:40Z
Publication date
dc.date.issued
2014
Cita de ítem
dc.identifier.citation
Agricultural Water Management Volume 146, December 2014, Pages 218–227
en_US
Identifier
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doi:10.1016/j.agwat.2014.08.014
Identifier
dc.identifier.uri
https://repositorio.uchile.cl/handle/2250/120257
General note
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Artículo de publicación SCOPUS
en_US
Abstract
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The demand for foods in central Chile is increasing and arable land is expanding rapidly onto floodplain soils, which are being cleared for maize cultivation. After harvest, a significant amount of residual nitrogen (N) may be still present in the soil in autumn–winter, when a high risk of nitrate leaching (NL) is expected due to occasional flooding events. Determining nitrate (NO3−) movement through the vadose zone is essential for studying the impact of agricultural practices on surface water quality. This study focused on understanding the processes of NO3− leaching in a floodplain environment and compared the effectiveness of four different methods: soil coring (T0), an observation well (T1), ceramic suction cup lysimeters (T2) and a capillary lysimeter (FullStop™ wetting front detector) (T3) for monitoring NL using an infiltration cylinder to simulate the conditions generated during flush flooding events during autumn–winter season in a typical coarse-textured alluvial floodplain soil. The comparison showed that T0 and T3 can be used for monitoring NL during flush flooding events during autumn–winter season in stratified coarse-textured floodplain soils, whereas T1 and T2 are not appropriate for these site conditions. A correlation was found between NO3 and soluble salt (Cl− concentration and EC) only in the first measurements after the dry summer period. The results of this study suggest that most of the surplus N could be leached by excessive irrigation during the crop growing season (spring–summer), while a lower amount of residual N may still be present in the soil in autumn–winter available to be lost by NL during flush flooding events. Overall the two monitored flushing events could have leached around 6% of the total NO3–N load. There was no significant effect of sampler devices on saturated hydraulic conductivity.
en_US
Patrocinador
dc.description.sponsorship
Department of Soil and Engineering at the University of Chile
FONDECYT