Weighted risk assessment of critical source areas for soil phosphorus losses through surface runoff mechanisms

被引:13
|
作者
Hayes, Emma [1 ]
Higgins, Suzanne [2 ]
Geris, Josie [3 ]
Nicholl, Gillian [2 ]
Mullan, Donal [1 ]
机构
[1] Queens Univ Belfast, Sch Nat & Built Environm, Geog, Belfast, North Ireland
[2] Agrifood & Biosci Inst, Belfast, North Ireland
[3] Univ Aberdeen, Sch Geosci, Northern Rivers Inst, Aberdeen, Scotland
关键词
Gridded soil sampling; Soil phosphorus; Ordinary kriging; Hydrological modelling; Water quality; HYDROLOGICALLY SENSITIVE AREAS; NUTRIENT MANAGEMENT; WATER-QUALITY; OVERLAND-FLOW; FIELD; IDENTIFICATION; AGRICULTURE; VARIABILITY; GRASSLANDS; MITIGATION;
D O I
10.1016/j.catena.2023.107027
中图分类号
P [天文学、地球科学];
学科分类号
07 ;
摘要
In intensive livestock areas, soils commonly contain elevated nutrients above the agronomic optimum which increases the risk of nutrient losses and contributing to poor ecological status waterbodies. Large within-field variability in soil nutrient content exists, and at-risk phosphorus (P) hotspots are rarely quantified due to suboptimal soil sampling regimes. This study aims to address this issue by developing and evaluating an improved classification of P transfer risk at a sub-field scale through a weighted risk assessment model that combines gridded soil sampling data with modelled in-field surface runoff pathways. Within-field soil P variability was quantified at six field-scale sites in Northern Ireland using two different sampling techniques; traditional bulked field soil sampling (i.e. bulk analysis of W pattern sampling) and gridded sampling (at 35 m resolution) alongside interpolation. Results show that traditional bulked sampling failed to account for the subfield scale spatial variability in soil P content. This may contribute to the poor chemical and ecological status of surface waters by frequently under-predicting soil nutrient content, and failing to identify potential contributing sources of soil P losses. In contrast, higher intensity gridded sampling and interpolation revealed wide in-field spatial variability in soil P content, facilitating the identification of contributing sources of P losses to poor water quality and aiding in the characterisation of risk for nutrient losses to waterways. Hydrological modelling of in-field runoff pathways indicated several P sources potentially contributing to runoff-based P losses. Our weighted risk assessment model was successful in identifying P hotspots and transfer potential to water courses, illustrating that a similar approach could be applied anywhere in the world where excess P poses a problem for water quality. Model validation took place using instream water quality sampling data, which showed that higher risk weighting model results correlated to poorer water quality conditions. This methodology could be a useful management tool to help countries meet their national water quality targets.
引用
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页数:12
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