Not only the Sahel (Haregeweyn et al., 2013), the deforested land (Borelli et al., 2013) the chinese Plateau areaffected by intense soil erosion rates (Zhao et al., 2013). Soil erosion affect agriculture land (Cerdà et al., 2009),and citrus orchards are being seeing as one of the crops with the highest erosion rates due to the managementsthat avoid the catch crops, weeds or litter. Example of the research carried out on citrus orchards is found in theMediterranean (Cerdà and Jurgensen, 2008; 2009; Cerdà et al., 2009a; 2009b; Cerdà et al., 2011; 2012) and inChina (Wu et al., 1997; Xu et al., 2010; Wang et al., 2011; Wu et al., 2011; Liu et al., 2011; Lü et al., 2011; Xu etal., 2012), and they confirm the non sustainable soil losses measured. The land management in citrus plantationsresults in soil degradation too (Lu et al., 1997; Lü et al., 2012; Xu et al., 2012). The use of cover crops to reducethe soil losses (Lavigne et al., 2012; Le Bellec et al., 2012) and the use of residues such as dried citrus peel hasbeen found successful. There is a need to find new plants or residues to protect the soils on citrus orchards.Agriculture produces a high amount of residues. The pruning can contribute with a valuable source of nutrientsand a good soil protection. The leaves of the trees, and some parts of the plants, once harvest can contribute toreduce the soil losses. Due to the mechanization of the agriculture, and the reduction of the draft animals (mainlyhorses, mules, donkeys and oxen) the straw is being a residue instead of a resource. The Valencia region is thelargest producer of citrus in Europe, and the largest exporter in the world. This citrus production region is locatedin the eastern cost of Spain where we can find the rice production area of the l’Albufera Lagoon paddy fields,the third largest production region in Spain. This means, a rice production region surrounded by the huge citrusproduction region. There, the rice straw is not used in the paddy fields after harvesting and the straw is being asa residue that damages the air quality when burnt, the water quality due to the decomposition and the methaneproduction, and is not accepted in the field by the farmers. This is a new problem as few years ago the rice strawwas use for animal feeding. Many attempts were developed in the last decade to remove and use the straw to avoidfires and water pollution (Iranzo et al., 2004; Silvestre et al., 2013).Our goal is to test if a residue such as the rice straw can be transformed as a resource: soil erosion control. Strawhas been seen as a very efficient to reduce the water losses in agriculture land (García Moreno et al., 2013), thesoil losses in fire affected land (Robichaud et al., 2013a; 2013b; Fernandez and Vega, 2014), and soil properties(García Orenes et al., 2009; 2010; Jordán et al., 2010; García Orenes 2012).Rainfall simulations under 55 mm h-1 rainfall intensity during one hour on 0,25 m2 plots were carried out on plotspaired plots: bare and covered with straw. The plots covered with straw had different straw mulch cover: from 10to 100 % cover and from 0,005 g m2 to 300 g m2. The results show a positive effect of the straw cover that showan exponential relation between the straw cover and weight with the sediment yield.AcknowledgementsThe research projects GL2008-02879/BTE, LEDDRA 243857 and RECARE supported this research.
|Numero di pagine||1|
|Stato di pubblicazione||Published - 2014|