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Principle of the ultrasonic dispersion equipment. 

Principle of the ultrasonic dispersion equipment. 

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This study aimed to reveal differences in UV (ultraviolet) -absorbing dissolved organic carbon (DOC) between three prominent Austrian soil types: a Cambisol and a Chernozem developed from Tertiary marl, both under agricultural management, and a Podzol from a mixed coniferous beech forest stand. Topsoil samples (0–300 mm) were pre-treated, air-dried...

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Context 1
... ultrasonic dispersion equipment used in the present study is an adapted ultrasonic fatigue testing equipment (Mayer 2006). The probe is inserted into a soil water suspension and performs resonance vibrations at 19.1 kHz. This led to emission of pressure waves into the soil water suspension. The vibration amplitude was measured with an induction coil. Under well- defined geometrical conditions, the vibration organic matter (ISO11277 2009). Carbon and nitrogen were measured using dry combustion with a Carlo Erba NA 1500 (ISO10694 2009; ISO13878 1998) determined with flash combustion and chromatographic analysis of carbon dioxide. The difference between total carbon and inorganic carbon is expressed as organic carbon. Determination of calcium carbonate was in accordance with the Scheibler volumetric method (ISO10693 1995). SOM was calculated with C x 1.724 assuming average C-concentration of org organic matter of 58% (Blume et al. 2010). Each sample was air-dried, homogenously mixed and sieved to gain the aggregate fraction with size between 2000 μ m and 1000 μ m. This fraction is used to determine soil aggregate stability (SAS) according to OENorm L 1072 (2003). amplitude strongly correlates with the magnitude of the acoustic pressure waves emitted into the suspension that cause dispersion of soil particles (Kuttruff 1988; Millner 1987). The amplitude and resonance frequency was controlled and kept constant with very high accuracy in a closed- loop electronic circuit. Deviation of pre-selected and actual vibration amplitude was maximum ± 1%. The equipment can be run in pulsed mode to limit the temperature increase of the soil- water suspension. Commercially available equipment use ultrasonic power as a control parameter where the power setting is rather high and accuracy is low. Since ultrasonic power is derived from voltage and current signals, the efficiency of the ultrasonic transducer and other electrical and mechanical parameters of the system it is prone to errors. Subsequently, the power of these systems can be quantified with 10-20% accuracy only (Zhu et al. 2009; Schmidt et al. 1999). 2.4. Calibration procedure to determine power of the ultrasonic equipment The system operated close to the cavitation threshold of gas saturated de-ionized water, which is 0.5-0.6 μ m at 19.1 kHz frequency (Schomakers et al. 2011b). The following procedure was developed and applied to determine ultrasonic power at low vibration amplitudes. The probe was inserted in water (mass of water is m and specific heat capacity w is c ) and vibrates at constant amplitude. The The cylindrical probe used in this study had a diameter of 30 mm. The rather large diameter of the probe improves the homogeneity of the pressure field. During the experiments, the probe was dipped into de-ionized water. The insertion depth was four millimetres, which set the distance between probe and beaker bottom at about 50 mm ( Figure 1 ). This distance to the beaker bottom was chosen to avoid resonance of the acoustic waves in water (half wavelength of sound waves of 20 kHz frequency in water is 37 mm). increase of water temperature, Δ T during the time period Δ t was measured. Changes of thermal energy of water are caused by ultrasonic vibrations and by heat exchange with probe, beaker and ambient air. With the ultrasonic power, P and the heat exchange per second, us Δ Q Exchange / Δ t, change of thermal energy of water per second, m w c w Δ T/ Δ t is given by Eq. 1 in Schomakers et al. 2011b: A temperature gradient drives heat flow between water and environment due to convection or thermal conduction. Heat flow from thermic conduction (ultrasonic probe, beaker) and convection (ambient air) is proportional to the respective temperature difference. At the start of the power measurements, all mechanical components of the system are at room temperature. Only water measures a few degrees less: Δ Q Exchange / Δ t > 0 and the increase of thermal energy of water per unit time is the sum of ultrasonic power and heat flow into the water. During sonication, the water temperature increases until it is greater than the ambient temperature and Δ Q Exchange / Δ t < 0. When temperature of water and ambiance coincide Δ Q Exchange / Δ t = 0 and the ultrasonic power is directly correlated to the increase of water temperature. Ultrasonic power was determined at different vibration amplitudes for the used setup, i.e. an ultrasonic probe with diameter ø 30 mm, insertion depth 4 mm and vibration frequency 19.1 kHz. At vibration amplitude 1 μ m mean ultrasonic power was 2.9 W. At vibration amplitude 2 μ m it was 8.9 W, at 3 μ m the mean power was 14.9 W, at 4 μ m it was 20.8 W and at 5 μ m it was 26.8 W. Standard deviation was mean 0.9 ...
Context 2
... grams of air-dried soil (2 000-1 000 μ m) were placed in a plexiglass beaker (Ø 44 mm), 80 cm 3 of de-ionised water was added and the suspension was subsequently sonicated. To obtain a homogeneous distribution, the soil water suspension was stirred with a magnetic device (2 Hz, cylindrical shape with length 25 mm and thickness 8 mm), immediately prior and during the experiment ( Figure 1 ). The soil samples were subjected to a combination of ultrasonic dispersion, in accordance with OENorm L 1092 (2005). One treatment included a sonication time of 60 s at 2 μ m, the other treatment included a sonication time of 480 s at 5 μ m. With the ultrasonic power of 8.9 W and 26.8 W, respectively, the ultrasonic energies absorbed in 80 cm 3 were 0.53 kJ (i.e. 6.7 J cm -3 ) in the experiments at vibration amplitude 2 μ m, and 12.9 kJ (i.e. 161 J cm -3 ) in the experiments at vibration amplitude 5 μ m. Pulsed loading was applied to limit maximum temperature of the soil-water suspension to maximum 30 ...

Citations

... The concentration of SOC was obtained by the subtraction of the inorganic C content from total C and is expressed in kg m − 2 . A probe sonicator (SONOPLUS HD2200, BANDELIN electronic GmbH & Co., Berlin, Germany) was applied to extract DOC from a soil-water suspension (10 g soil in 100 ml MilliQ water) with 1 cm insert depth at 2 μm amplitude for 2 min as adapted from Schomakers et al. (2014). After filtration through 0.45 μm double filters (a folded filter and a nylon membrane filter), filtrates were measured for DOC with a UV-Vis diode array spectrophotometer (Agilent 8453, Agilent Technologies Inc., USA) using a 1 cm quartz cuvette. ...
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The aim of global carbon (C) neutrality brings soils and their potential for C storage into the spotlight. Improved agricultural management techniques such as minimum or no-tillage are thought to foster soil C sequestration. However, the underlying mechanisms are still not well understood. In this study, we investigated the inter-relations of soil organic C (SOC), fungal biomass, microbial necromass biomarkers, and aggregate stability in rhizosphere and bulk soil after thirteen years of reduced tillage intensities (reduced, minimum, and no-tillage). Overall, rhizosphere and bulk soil were indifferent in their response to reduced tillage. Reducing tillage intensity increased SOC and nitrogen stocks and dissolved organic C contents in the following order: minimum > no-tillage > reduced > conventional. Aggregate stability showed the strongest increase under no-tillage. Interestingly, ergosterol contents were highest under reduced and minimum tillage followed by no-tillage. The amino sugars muramic acid, galactosamine, and glucosamine – proxies for soil microbial-derived necromass – showed similar increases under all three tillage reduction systems. Structural equation modelling revealed that increased dissolved organic C contents under reduced tillage intensity facilitated SOC sequestration and aggregate stability through enhanced fungal biomass to necromass turnover. Thus, reducing soil tillage intensity is a valuable tool to facilitate microbial growth and hence to increase SOC sequestration in agricultural soils.
... This poses an important link between DOM occluded in soil aggregates and its role in aggregate stabilization. There is a large variety of sources for DOM in soil, ranging from plant root and microbial exudates to decomposed organic matter (Neff and Asner 2001;Bolan et al. 2011;Malik and Gleixner 2013;Schomakers et al. 2014). The organic compounds include, for example, simple carbohydrates and amino acids with low molecular weight, organic acids and proteins, amino sugars, or more complex polysaccharides, which show a wide range of degradability (Bolan et al. 2011). ...
... Accordingly, the determination of DOM release from soil aggregates could provide mechanistic insight into stabilization processes of this active fraction in soil and thus better represent potential SOC effects of different soil managements where aggregate-bound C is a key sensitive indicator (Six et al. 2000;Kiem et al. 2002;Wiesmeier et al. 2019). The application of ultrasonic energy effectively disperses soil aggregates, which leads to a continuous release of occluded DOM (Schomakers et al. 2011(Schomakers et al. , 2014. A level of ultrasonic energy application during a dispersion process can be used to infer mechanical stability of soil aggregates and subsequently occluded SOC (Kaiser and Berhe 2014). ...
... An ultrasonic energy of 60 J ml −1 was suggested to completely disperse soil macroaggregate (250 -2000 μm), while ≥ 440 J ml −1 are required for microaggregate separation (20 -250 μm). A study by Schomakers et al. (2014) reported that 6.7 J ml −1 was sufficient to release dissolved organic fractions obtained from plant and microbial origins in the soils. ...
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Purpose Since principles of conservation agriculture mimic the soil conditions of undisturbed natural soils, linking aggregation and dissolved organic matter (DOM) occlusion would therefore provide a targeted descriptor for soil health advances of innovative farming systems. This study aimed to assess structure-related DOM patterns of conservation farming systems and underlying bio-chemical drivers by using a novel method for the combined analysis of aggregate breakdown and DOM release. Methods Soil samples were collected from conventional farming, conservation farming and natural reference soil systems over a wide range of soil types. Ultrasonication aggregate breakdown combined with continuous UV–Vis measurement was used to characterize DOM release from soil. Measures of breakdown dynamics were related to soil physical and chemical properties to determine the strongest predictors of DOM release. Results The quantity of DOM released and aggregate stabilization showed a steady continuum starting from standard farming through conservation agriculture towards reference soil systems. DOM released from reference soils however was less complex and occluded in more stable soil aggregates than arable soils. The overall DOM release dynamics are shaped by agricultural management with site-specific modifiers driving aggregation and mineral-organic interactions in soils. Conclusions The simultaneous quantification of aggregate breakdown and DOM release captures key biophysical effects in structure-related DOM stabilization and revealed significant differences between land-use and agricultural management systems. The linkage of physical with functional soil organic matter descriptors provides an improved approach to monitor soil health advances in arable cropping systems.
... According to the researchers, the organic compounds leached during the leaching of pine bark with water are mainly sugars (hemicellulose and derivatives of cellulose), lipids, organic acids (phenolic acid, oleic acid, linolenic and linoleic acids, and other fatty acids), resin compounds, alcohols, oils, polyphenols, proteins, tannins, flavonoids, sterols, and others (Valentín et al. 2010;Deng et al. 2013;Schomakers et al. 2014;Yu et al. 2014). According to the author, as a result of atmospheric pollution, such organic pollutants as polycyclic aromatic hydrocarbons (PAHs), dioxins, or furans can penetrate the bark structure. ...
... These compounds are then extracted during the leaching process. An important group of organic compounds leached from biomass are humic compounds (Leenheer and Croué 2003;Schomakers et al. 2014) which influence, among others, the intensity of the color of the leachates formed during the leaching process. These compounds also contribute to the change of color mainly in surface waters (Świderska-Bróż and Kowal 2009). ...
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Water encountering biomass can affect the change in its chemical composition and properties through the leaching process. In the leaching process, leachates are formed, and their composition depends on the type of biomass and the time of exposure to the solvent (water). The aim of the study was to analyze the influence of time of contact of water with biomass on changing the chemical composition of the leachates formed during long-term (counted in days) leaching of pine bark (Pinus sylvestris). Long-term leaching contributes to a loss of organic and inorganic compounds, and in this study, an intensive extraction of biomass components was noted from the first day of leaching. Along with the extension of the leaching time, values for electrical conductivity, concentration of mineral fraction (ashes), concentration of volatile matter, and concentration of total organic carbon significantly increased in the leachates. However, no linear relationship between the extension of the leaching time and the increase in the concentration of chlorides, sulfates, nitrogen, phosphorus, and other elements in the leachates was observed. This study will allow to better understand the impact of vegetation communities on the aquatic and terrestrial ecosystems, as well as help to provide adequate conditions of storage of biomass for technological purposes. Graphical Abstract
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Ultrasonic power is the main variable that forms the basis for many soil disaggregation experiments. Thus, a procedure for the rapid determination of this variable has been developed and is described in this article. Calorimetric experiments serve to measure specific heat capacity and ultrasonic power. Ultrasonic power is determined experimentally for deionised water, 30% ethanol and sodium polytungstate with a density of 1.6 g cm⁻³ and 1.8 g cm⁻³. All experiments are performed with a pre-selected ultrasonic probe vibration amplitude. Under these conditions, it was found that the emitted ultrasonic power was comparable in the four fluids. It is suggested, however, to perform calibration experiments prior to dispersion experiments, since the used fluid, as well as the employed ultrasonic equipment, may influence the power output.