1
|
Cerdà A, Keesstra SD, Rodrigo-Comino J, Novara A, Pereira P, Brevik E, Giménez-Morera A, Fernández-Raga M, Pulido M, di Prima S, Jordán A. Runoff initiation, soil detachment and connectivity are enhanced as a consequence of vineyards plantations. J Environ Manage 2017; 202:268-275. [PMID: 28735211 DOI: 10.1016/j.jenvman.2017.07.036] [Citation(s) in RCA: 17] [Impact Index Per Article: 2.4] [Reference Citation Analysis] [What about the content of this article? (0)] [Affiliation(s)] [Abstract] [Key Words] [MESH Headings] [Track Full Text] [Subscribe] [Scholar Register] [Received: 04/30/2017] [Revised: 07/14/2017] [Accepted: 07/15/2017] [Indexed: 06/07/2023]
Abstract
Rainfall-induced soil erosion is a major threat, especially in agricultural soils. In the Mediterranean belt, vineyards are affected by high soil loss rates, leading to land degradation. Plantation of new vines is carried out after deep ploughing, use of heavy machinery, wheel traffic, and trampling. Those works result in soil physical properties changes and contribute to enhanced runoff rates and increased soil erosion rates. The objective of this paper is to assess the impact of the plantation of vineyards on soil hydrological and erosional response under low frequency - high magnitude rainfall events, the ones that under the Mediterranean climatic conditions trigger extreme soil erosion rates. We determined time to ponding, Tp; time to runoff, Tr; time to runoff outlet, Tro; runoff rate, and soil loss under simulated rainfall (55 mm h-1, 1 h) at plot scale (0.25 m2) to characterize the runoff initiation and sediment detachment. In recent vine plantations (<1 year since plantation; R) compared to old ones (>50 years; O). Slope gradient, rock fragment cover, soil surface roughness, bulk density, soil organic matter content, soil water content and plant cover were determined. Plantation of new vineyards largely impacted runoff rates and soil erosion risk at plot scale in the short term. Tp, Tr and Tro were much shorter in R plots. Tr-Tp and Tro-Tr periods were used as connectivity indexes of water flow, and decreased to 77.5 and 33.2% in R plots compared to O plots. Runoff coefficients increased significantly from O (42.94%) to R plots (71.92%) and soil losses were approximately one order of magnitude lower (1.8 and 12.6 Mg ha-1 h-1 for O and R plots respectively). Soil surface roughness and bulk density are two key factors that determine the increase in connectivity of flows and sediments in recently planted vineyards. Our results confirm that plantation of new vineyards strongly contributes to runoff initiation and sediment detachment, and those findings confirms that soil erosion control strategies should be applied immediately after or during the plantation of vines.
Collapse
Affiliation(s)
- A Cerdà
- Soil Erosion and Degradation Research Group, Department of Geography, Valencia University, Blasco Ibàñez, 28, 46010 Valencia, Spain.
| | - S D Keesstra
- Soil Physics and Land Management Group, Wageningen University, Droevendaalsesteeg 4 6708PB, Wageningen, The Netherlands; Civil, Surveying and Environmental Engineering, The University of Newcastle, Callaghan 2308, Australia.
| | - J Rodrigo-Comino
- Department of Physical Geography, Trier University, D-54286 Trier, Germany; Instituto de Geomorfología y Suelos, Department of Geography, Málaga University, Campus of Teatinos S/n, 29071 Málaga, Spain.
| | - A Novara
- Dipartimento di Scienze Agrarie e Forestali, University of Palermo, Italy.
| | - P Pereira
- Department of Environmental Policy, Mykolas Romeris University, Ateities g. 20, LT-08303 Vilnius, Lithuania.
| | - E Brevik
- Department of Natural Sciences, Dickinson State University, EEUU, United States.
| | - A Giménez-Morera
- Departamento de Economi´;a y Ciencias Sociales, Escuela Polite´cnica Superior de Alcoy, Universidad Polite´cnica de Valencia, Paseo Del Viaducto, 1, 03801 Alcoy, Alicante, Spain.
| | | | - M Pulido
- GeoEnvironmental Research Group, University of Extremadura, Faculty of Philosophy and Letters, Avda. de La Universidad S/n, 10071 Cáceres, Spain.
| | - S di Prima
- Dipartimento di Agraria, Università Degli Studi di Sassari, Viale Italia 39, 07100 Sassari, Italy.
| | - A Jordán
- MED_Soil Research Group, Department of Crystallography, Mineralogy and Agricultural Chemistry, University of Seville, Profesor García González, 1, 41012 Sevilla, Spain.
| |
Collapse
|
2
|
Masselink R, Temme AJAM, Giménez R, Casalí J, Keesstra SD. Assessing hillslope-channel connectivity in an agricultural catchment using rare-earth oxide tracers and random forests models. ACTA ACUST UNITED AC 2017. [DOI: 10.18172/cig.3169] [Citation(s) in RCA: 44] [Impact Index Per Article: 6.3] [Reference Citation Analysis] [What about the content of this article? (0)] [Abstract] [Track Full Text] [Journal Information] [Subscribe] [Scholar Register] [Indexed: 11/18/2022]
Abstract
Soil erosion from agricultural areas is a large problem, because of off-site effects like the rapid filling of reservoirs. To mitigate the problem of sediments from agricultural areas reaching the channel, reservoirs and other surface waters, it is important to understand hillslope-channel connectivity and catchment connectivity. To determine the functioning of hillslope-channel connectivity and the continuation of transport of these sediments in the channel, it is necessary to obtain data on sediment transport from the hillslopes to the channels. Simultaneously, the factors that influence sediment export out of the catchment need to be studied. For measuring hillslope-channel sediment connectivity, Rare-Earth Oxide (REO) tracers were applied to a hillslope in an agricultural catchment in Navarre, Spain, preceding the winter of 2014-2015. The results showed that during the winter no sediment transport from the hillslope to the channel was detected.To test the implication of the REO results at the catchment scale, two contrasting conceptual models for sediment connectivity were assessed using a Random Forest (RF) machine learning method. The RF method was applied using a 15-year period of measured sediment output at the catchment scale. One model proposes that small events provide sediment for large events, while the other proposes that only large events cause sediment detachment and small events subsequently remove these sediments from near and in the channel. For sediment yield prediction of small events, variables related to large preceding events were the most important. The model for large events underperformed and, therefore, we could not draw any immediate conclusions whether small events influence the amount of sediment exported during large events. Both REO tracers and RF method showed that low intensity events do not contribute any sediments from the hillslopes to the channel in the Latxaga catchment. Sediment dynamics are dominated by sediment mobilisation during large (high intensity) events. Sediments are for a large part exported during those events, but the system shows a memory of the occurrence of these large events, suggesting that large amounts of sediments are deposited in and near the channel after these events. These sediments are gradually removed by small events. To better understand the delivery of sediments to the channel and how large and small events influence each other more field data on hillslope-channel connectivity and within-channel sediment dynamics is necessary.
Collapse
|