Abstract:We performed field experiment with 10 g l −1 concentration of Brilliant Blue solutes in 100 l of water sprinkling on 1 × 1 m surface of the Dystric Cambisol. Consequently, four vertical profiles were exposed at experimental plot after 2 hours (CUT 2), 24 hours (CUT 24), 27 hours (CUT 27) and after 504 hours (CUT 504) in order to analyse spatiotemporal interactions among the BB solution (Na-salts), soil exchangeable complex and fine earth soil (%) samples extracted from both the high and low coloured zones loca… Show more
“…It was found that the application of BB dye solution abruptly increased the pH (H 2 O) values in all profiles (CUT 2-CUT 504) of the experimental plot, and that the comparison with REF profiles revealed the gradual drop in pH (H 2 O) from CUT 2 to CUT 504 profiles. Bebej et al (2017) have documented also the changes of Na + concentration (cmol c kg −1 ) in the soil exchangeable complex extracted from the zones of macropore PF of CUT 2 -CUT 504 profiles, analogous with those described for pH (H 2 O).…”
Section: Discussionmentioning
confidence: 65%
“…objects (SPW < 20 mm) with small V v is located in this line, but high S V value is observed here (ten intercepts is visible in this line) Dye pattern profiles and corresponding dye pattern coverages (bottom) of CUT 2 (a), CUT 24 (b), CUT 27 (c) and CUT 504 (d) profiles (adapted fromBebej et al, 2017).…”
mentioning
confidence: 67%
“…On the other hand, the morphometric parameters of stained objects seemed to be sensitive enough to track these processes. Bebej et al (2017) have reported the physical-chemical changes caused by the application of Brilliant Blue dye (pH = 7) on acidic soils (pH < 4.0) from the same experiment. It was found that the application of BB dye solution abruptly increased the pH (H 2 O) values in all profiles (CUT 2-CUT 504) of the experimental plot, and that the comparison with REF profiles revealed the gradual drop in pH (H 2 O) from CUT 2 to CUT 504 profiles.…”
Section: Discussionmentioning
confidence: 99%
“…The results of all above mentioned independent and indirect methods of dye solution flow were summarised and evaluated by Bebej et al (2017). It was also found that according to the USDA soil taxonomy, the soil samples taken from both the experimental and the REF plots were classified as sandy clay loam (usually, samples from 0.1 to 0.5 m depth), and sandy loam (samples below 0.5 m), and no significant texture differences were found between the experimental and the REF plots.…”
Section: Experiments Setupmentioning
confidence: 99%
“…The silicate analyses of fine earth soil samples taken from the soil profiles of REF plots showed no differences in chemical and mineralogical composition of soil. Considering the skeleton composition, its volumetric content, soil textures and chemical composition of fine earth we can propose that the working hypothesis about the spatial representativeness of soil pedon body within the REF and the experimental plots is valid, and that the observed changes in dye pattern profiles will minimally reflect spatial variations existing within the pedon body under investigation (Bebej et al, 2017).…”
The application of Brilliant Blue FCF tracer enables to identify flow types in multi-domain porous systems of soils via analyses of morphologic parameters of stained objects occurring in dye pattern profiles, as they represent the footprint of flow processes which occurred in soil during both the infiltration and the redistribution of dye solution. We analysed the vertical dye pattern profiles exposed for different time lengths, and revealed temporal evolution of dye solution redistribution leading to changes in flow types. The field experiment was performed with the Brilliant Blue tracer (the 10 g l−1 concentration) applied on 1m x 1m surface of the Dystric Cambisol. The top litter horizon had been removed before 100 l of the tracer was applied. Four vertical profiles were excavated on the experimental plot (always 20 cm apart) at different times after the irrigation had been finished: 2 hours (CUT 2), 24 hours (CUT 24), 27 hours (CUT 27) and 504 hours (CUT 504). The analyses of the dyed patterns profiles showed the spatio-temporal changes in the dye coverage, surface area density, average BB concentration, and stained path width, which allowed us to specify three stages of dye solution redistribution history: (i) a stage of preferential macropore flow, (ii) a stage of strong interaction between macropore-domain and soil matrix leading to the generation of heterogeneous matrix flow and fingering flow types, and (iii) a final stage of dye redistribution within the soil body connected with leaching of BB caused by meteoric water. With increasing time, the macropore flow types convert to mostly matrix-dominated FTs in the upper part of the soil profile. These results were supported by soil hydrological modelling, which implied that more than 70% of the soil moisture profiles variability among CUT 2–CUT 504 could be explained by the time factor.
“…It was found that the application of BB dye solution abruptly increased the pH (H 2 O) values in all profiles (CUT 2-CUT 504) of the experimental plot, and that the comparison with REF profiles revealed the gradual drop in pH (H 2 O) from CUT 2 to CUT 504 profiles. Bebej et al (2017) have documented also the changes of Na + concentration (cmol c kg −1 ) in the soil exchangeable complex extracted from the zones of macropore PF of CUT 2 -CUT 504 profiles, analogous with those described for pH (H 2 O).…”
Section: Discussionmentioning
confidence: 65%
“…objects (SPW < 20 mm) with small V v is located in this line, but high S V value is observed here (ten intercepts is visible in this line) Dye pattern profiles and corresponding dye pattern coverages (bottom) of CUT 2 (a), CUT 24 (b), CUT 27 (c) and CUT 504 (d) profiles (adapted fromBebej et al, 2017).…”
mentioning
confidence: 67%
“…On the other hand, the morphometric parameters of stained objects seemed to be sensitive enough to track these processes. Bebej et al (2017) have reported the physical-chemical changes caused by the application of Brilliant Blue dye (pH = 7) on acidic soils (pH < 4.0) from the same experiment. It was found that the application of BB dye solution abruptly increased the pH (H 2 O) values in all profiles (CUT 2-CUT 504) of the experimental plot, and that the comparison with REF profiles revealed the gradual drop in pH (H 2 O) from CUT 2 to CUT 504 profiles.…”
Section: Discussionmentioning
confidence: 99%
“…The results of all above mentioned independent and indirect methods of dye solution flow were summarised and evaluated by Bebej et al (2017). It was also found that according to the USDA soil taxonomy, the soil samples taken from both the experimental and the REF plots were classified as sandy clay loam (usually, samples from 0.1 to 0.5 m depth), and sandy loam (samples below 0.5 m), and no significant texture differences were found between the experimental and the REF plots.…”
Section: Experiments Setupmentioning
confidence: 99%
“…The silicate analyses of fine earth soil samples taken from the soil profiles of REF plots showed no differences in chemical and mineralogical composition of soil. Considering the skeleton composition, its volumetric content, soil textures and chemical composition of fine earth we can propose that the working hypothesis about the spatial representativeness of soil pedon body within the REF and the experimental plots is valid, and that the observed changes in dye pattern profiles will minimally reflect spatial variations existing within the pedon body under investigation (Bebej et al, 2017).…”
The application of Brilliant Blue FCF tracer enables to identify flow types in multi-domain porous systems of soils via analyses of morphologic parameters of stained objects occurring in dye pattern profiles, as they represent the footprint of flow processes which occurred in soil during both the infiltration and the redistribution of dye solution. We analysed the vertical dye pattern profiles exposed for different time lengths, and revealed temporal evolution of dye solution redistribution leading to changes in flow types. The field experiment was performed with the Brilliant Blue tracer (the 10 g l−1 concentration) applied on 1m x 1m surface of the Dystric Cambisol. The top litter horizon had been removed before 100 l of the tracer was applied. Four vertical profiles were excavated on the experimental plot (always 20 cm apart) at different times after the irrigation had been finished: 2 hours (CUT 2), 24 hours (CUT 24), 27 hours (CUT 27) and 504 hours (CUT 504). The analyses of the dyed patterns profiles showed the spatio-temporal changes in the dye coverage, surface area density, average BB concentration, and stained path width, which allowed us to specify three stages of dye solution redistribution history: (i) a stage of preferential macropore flow, (ii) a stage of strong interaction between macropore-domain and soil matrix leading to the generation of heterogeneous matrix flow and fingering flow types, and (iii) a final stage of dye redistribution within the soil body connected with leaching of BB caused by meteoric water. With increasing time, the macropore flow types convert to mostly matrix-dominated FTs in the upper part of the soil profile. These results were supported by soil hydrological modelling, which implied that more than 70% of the soil moisture profiles variability among CUT 2–CUT 504 could be explained by the time factor.
AbstractIn agricultural land use, organic residues such as compost, digestate, and sewage sludge are discussed as costeffective soil conditioner that may improve the water holding capacity and crop available soil moisture. The objective of this study is to determine the effect of application of digestates with different compositions in maize, sugar beet and winter wheat, compost of shrub debris and sewage sludge on shrinkage behaviour and contact angle of till-derived loamy topsoil of a Haplic Luvisol under agricultural use. Novelty is the simultaneous determination of contact angle and shrinkage of soils amended with digestates composed of different composition in maize, sugar beet and winter wheat, compost of shrub debris and sewage sludge. The results suggest that the application of organic residues impacts the air capacity, while the contact angles remained in the subcritical range between > 0° and < 90°. The relationship between CA values and moisture ratios, ϑ, during proportional shrinkage was positive and linear (r2 of 0.98) and negative during residual- and zero-shrinkage (r2 of 0.93).
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