“…Chen et al, 2014;Colica et al, 2014;Fischer et al, 2010;Katznelson, 1989;Kidron et al, 1999;Malam Issa et al, 2009;Mazor et al, 1996;Rossi et al, 2012) was mentioned as one reason for the decreasing infiltration and higher water repellency. However, cyanobacteria always dominated the crusts studied there.…”
Section: Water Repellency and Infiltrationmentioning
confidence: 99%
“…On the other hand, investigations showed a promoted run-off by soil crusts (e.g. Kidron et al, 1999;Malam Issa et al, 2009). Run-off generation on soils with biological soil crusts was also caused by hydrophobic polymers and extracelluar secretions (Fischer et al, 2013), which reduced the size of pores formed by cyanobacteria (Mazor et al, 1996;Verrecchia et al, 1995) and induced run-off (Malam Issa et al, 2009).…”
Section: Water Retentionmentioning
confidence: 99%
“…They modify the water run-off infiltration balance (Kidron and Yair, 1997) and alter water re-distribution on different scales (Eldridge et al, 2002;Kidron, 2014). Increased porosity, enhanced aggregate stability and an improved physical structure have been reported to cause higher infiltration (Mager and Thomas, 2011;Menon et al, 2011;Rossi et al, 2012), while water repellency and clogging of pores led to a reduced infiltration (Kidron et al, 1999;Malam Issa et al, 2009). Also an influence of soil crusts on infiltration can be masked by soil properties like structure or texture.…”
Investigations were done on two former open-cast lignite mining sites under reclamation, an artificial sand dune in Welzow Süd, and a forest plantation in Schlabendorf Süd (Brandenburg, Germany). The aim was to associate the topsoil hydrological characteristics of green algae dominated as well as moss and soil lichen dominated biological soil crusts during crustal succession with their water retention and the repellency index on sandy soils under temperate climate and different reliefs.The investigation of the repellency index showed on the one hand an increase due to the cross-linking of sand particles by green algae which resulted in clogging of pores. On the other hand, the occurrence of moss plants led to a decrease of the repellency index due to absorption caused by bryophytes. The determination of the water retention curves showed an increase of the water holding capacity, especially in conjunction with the growth of green algae layer. The pore-related van Genuchten parameter indicate a clay-like behaviour of the developed soil crusts. Because of the inhomogeneous distribution of lichens and mosses as well as the varying thickness of green algae layers, the water retention differed between the study sites and between samples of similar developmental stages. However, similar tendencies of water retention and water repellency related to the soil crust formation were observed.Biological soil crusts should be considered after disturbances in the context of reclamation measures, because the initial development of green algae biocrusts lead to an increasing repellency index, while the occurrence of mosses and a gain in organic matter enhance the water holding capacity. Thus, the succession of biocrusts and their small-scale succession promote the development of soil and ecosystem.
“…Chen et al, 2014;Colica et al, 2014;Fischer et al, 2010;Katznelson, 1989;Kidron et al, 1999;Malam Issa et al, 2009;Mazor et al, 1996;Rossi et al, 2012) was mentioned as one reason for the decreasing infiltration and higher water repellency. However, cyanobacteria always dominated the crusts studied there.…”
Section: Water Repellency and Infiltrationmentioning
confidence: 99%
“…On the other hand, investigations showed a promoted run-off by soil crusts (e.g. Kidron et al, 1999;Malam Issa et al, 2009). Run-off generation on soils with biological soil crusts was also caused by hydrophobic polymers and extracelluar secretions (Fischer et al, 2013), which reduced the size of pores formed by cyanobacteria (Mazor et al, 1996;Verrecchia et al, 1995) and induced run-off (Malam Issa et al, 2009).…”
Section: Water Retentionmentioning
confidence: 99%
“…They modify the water run-off infiltration balance (Kidron and Yair, 1997) and alter water re-distribution on different scales (Eldridge et al, 2002;Kidron, 2014). Increased porosity, enhanced aggregate stability and an improved physical structure have been reported to cause higher infiltration (Mager and Thomas, 2011;Menon et al, 2011;Rossi et al, 2012), while water repellency and clogging of pores led to a reduced infiltration (Kidron et al, 1999;Malam Issa et al, 2009). Also an influence of soil crusts on infiltration can be masked by soil properties like structure or texture.…”
Investigations were done on two former open-cast lignite mining sites under reclamation, an artificial sand dune in Welzow Süd, and a forest plantation in Schlabendorf Süd (Brandenburg, Germany). The aim was to associate the topsoil hydrological characteristics of green algae dominated as well as moss and soil lichen dominated biological soil crusts during crustal succession with their water retention and the repellency index on sandy soils under temperate climate and different reliefs.The investigation of the repellency index showed on the one hand an increase due to the cross-linking of sand particles by green algae which resulted in clogging of pores. On the other hand, the occurrence of moss plants led to a decrease of the repellency index due to absorption caused by bryophytes. The determination of the water retention curves showed an increase of the water holding capacity, especially in conjunction with the growth of green algae layer. The pore-related van Genuchten parameter indicate a clay-like behaviour of the developed soil crusts. Because of the inhomogeneous distribution of lichens and mosses as well as the varying thickness of green algae layers, the water retention differed between the study sites and between samples of similar developmental stages. However, similar tendencies of water retention and water repellency related to the soil crust formation were observed.Biological soil crusts should be considered after disturbances in the context of reclamation measures, because the initial development of green algae biocrusts lead to an increasing repellency index, while the occurrence of mosses and a gain in organic matter enhance the water holding capacity. Thus, the succession of biocrusts and their small-scale succession promote the development of soil and ecosystem.
“…The modifications in hydrological surface properties are due to a multitude of factors associated with the BSCs, including texture (Fischer et al, 2013), surface roughness (Rodríguez-Caballero et al, 2012), vesicular porosity and capillary barriers , pore clogging and swelling of organic crust components (Fischer et al, 2010;Kidron et al, 1999) as well as water repellency (WR) (Drahorad et al, 2013b;Fischer et al, 2010). Recently the importance of the single factors have not been characterized systematically, as the complex interactions between them make it difficult to state general claims on their importance.…”
Abstract:The biological soil crusts (BSCs) in the NW Negev cause local water redistribution by increasing surface runoff. The effects of pore clogging and swelling of organic and inorganic crust components were intensively investigated in earlier studies. However, the effect of water repellency (WR) was not addressed systematically yet. This study investigates subcritical WR of BSCs in three different study sites in the NW Negev. For this purpose, three common methods to determine soil WR were used: (i) the repellency index (RI) method (ii) the water drop penetration time (WDPT) test and (iii) the Wilhelmy plate method (WPM). Furthermore, the potential influence of WR on local water redistribution is discussed and the applied methods are compared. We found the BSC to be subcritically water repellent. The degree of WR may only affect water redistribution on a microscale and has little influence on the ecosystem as a whole. The RI method was clearly the most appropriate to use, whereas the WDPT and the WPM failed to detect subcritical WR.
“…Scanning electron microscopy shows sufficient openings in sandy loam soils for water flow (Belnap and Gardner 1993), but concentration of silt and clay particles in the crust, in combination with swelling, may restrict infiltration even in sandy soils when they are wet (Verrecchia et al 1995). Some authors speculate that the hydrophobic nature of some crustal components contributes to soil surface sealing (Bond 1964;Dulieu et al 1977;Walker 1979;Rutin 1983;Jungerius and van de Meulen 1988); however, others have shown crustal organisms at some sites are highly hydrophilic (Kidron et al 1999).…”
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