328 research outputs found

    Green fallow soil vs. intensive soil cultivation – a study of soil structure along the slope gradient affected by erosion process

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    Article Details: Received: 2019-09-19 | Accepted: 2019-10-01 | Available online: 2019-09-30https://doi.org/10.15414/afz.2019.22.03.76-83 The type of slope and its interaction with soil management practices are one of the most important factors affecting soil structure along the slope gradient. In this study, the effects of fallow in greening and intensive soil cultivation both located on slopes on changes soil properties especially soil structure were evaluated. Soil samples were collected from two fields (neighbouring fields) between Trakovice and Bučany villages (Slovakia). The terrain of both fields was sloping with a WN – ES orientation and a slope of <8°. Field 1 is used as arable land with intensive cultivation of crops (IC). In field 2, the fallow in greening (G) was established in 2012 and in 2018 soil samples were taken in five zones of both slopes as follows: on the summit slope, shoulder, back slope, toe slope and flat. Results showed that structure coefficient (K) was strongly affected by both land use (p = 0.0000) and slope position (p = 0.0206)as well as by the interaction of land use and slope position (p = 0.0010). The statistically significantly highest structure coefficient of water-stable aggregates (Kwsa) and opposite the lowest macro-aggregate destruction (PAD) were found for G compared to IC. In G, the index of crusting (Ic) increased by 9% compared to IC. The critical level of soil organic matter (St) was strongly affected by both land use (p = 0.0114) and slope position (p = 0.0000). The values of St were statistically significantly influenced by interaction of land use and slope position. When land use and slope position were assessed together, positive significant correlations were observed between silt and carbonate contents and Ic. On the other hand, the St values were strong effected soil organic matter (SOM) quantity and quality. In IC, positive correlations between CL (r = 0.773, P <0.01) and K were observed. Ic correlated with silt (r = 0.650, P <0.05), carbonates (r = 0.704, P <0.05) and lower humus stability. A higher silt and carbonate contents as well as highercontent of SOM and better humus quality resulted in higher St values. In G, the K values positive correlated with silt and carbonate contents. Higher humus quality and stability improved soil structure evaluated on the base of Kwsa.Keywords: intensive cultvation, greening, fallow, slope gradient, soil structure ReferencesAMÉZKETA, E. (1999) Soil aggregate stability: a review. In J. of Sustain. Agric., vol. 14, no. 2–3, pp. 83–151. doi: http://dx.doi.org/10.1300/J064v14n02_08BA, L.T. et al. (2016) Effect of cropping system on physical properties of clay soil under intensive rice cultivation. In Land Degrad. Dev., vol. 27, pp. 973–982. doi: https://doi.org/10.1002/ldr.2321BARTLOVÁ, J. et al. 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(2015) Impact of long-term mineral and organic fertilizer application on the water stability, wettability and porosity of aggregates obtained from two loamy soils. In Eur. J. Soil Sci., vol. 66, pp. 1–12. doi: https://doi.org/10.1111/ejss.12242DZIADOWIEC, H. and GONET, S. S. (1999) Methodical guidebook for soil organic matter studies. Prace Komisji Naukowych Polskiego Towarzystwa Gleboznawczego, N. 120, Komisja chemii gleb, Zespół Materii Organicznej Gleb, N II/16 (in Polish).EFTHIMIOU N. (2018) The importance of soil data availability on erosion modeling. In Catena, vol. 165, pp. 551–566. doi:https://doi.org/10.1016/j.catena.2018.03.002FOTH, H.D. (1990) Fundamentals of soil science. New York: John Wiley and Sons, pp. 360. ISBN 0-471-52279-1.FULAJTÁR, E. (2006) Physical properties of soil (in Slovak). Bratislava: VÚPOP, pp.142. ISBN 80-89128-20-3.FULAJTÁR, E. and SAKSA, M. (2018) Loess soils of the Trnava Hilly Land. In ŚWITONIAK, M. and CHARZYŃSKI, P. Soil Sequences Atlas IV. Toruń: Nicolaus Copernicus University, pp. 123–137. ISBN 978-83-951878-2-7.HRIVŇAKOVÁ, K. et al. (2011) Uniform methods of soil analyses (in Slovak) VUPOP: Bratislava.KOBZA, J. et al. (2017) Current state and development of land degradation processes based on soil monitoring in Slovakia. In Agriculture (Poľnohospodárstvo), vol. 63, no. 2, pp. 74–85. doi: https://doi.org/10.1515/agri-2017-0007KÖRSCHNER M. et al. (1990) Heisswasserlőslicher C und N im Boden als Kriterium fűr das N-Nachliferungsvermőgen. In Mikrobiologie, vol. 145, pp. 305–311.LAL, R. and SHUKLA, M.K. (2004) Principles of soil physics. New York: Marcel Dekker. ISBN 0-8247-5324-0.LOGINOW, W. et al. (1987) Fractionation of organic carbon based on susceptibility to oxidation. In Pol. J. Soil Sci., vol. 20, pp. 47–52.MAÏGA-YALEU, S. et al. (2013) Soil crusting impact on soil organic carbon losses by water erosion. In Catena, vol. 107, pp. 26–34. doi: http://dx.doi.org/10.1016/j.catena.2013.03.006MONTGOMERY, D.R. (2007) Soil erosion and agricultural sustainability. In PNAS, vol. 104, pp. 13268–13272. doi: https://doi.org/10.1073/pnas.0611508104MORENO-RAMÓN, H. et al. (2014) Coffee husk mulch on soil erosion and runoff: experiences under rainfall simulation experiment. In Solid Earth, vol. 5, pp. 851–862. doi: https://doi.org/10.5194/se-5-851-2014MORGAN, R.P.C. (2005) Soil Erosion and Conservation. 3rd ed. London: Blackwell Publishing, pp. 299.NOVÁK, P. and VALLA, M. (2002) Other degradation forms of soil. In Pedologické dny, 2002, pp. 137–142.PANAGOS, P. et al. (2015) Rainfall erosivity in Europe. In Sci. Total Environ., vol. 511, pp. 801–814. doi: http://dx.doi.org/10.1016/j.scitotenv.2015.01.008PARADELO, R. et al. (2013) Water-dispersible clay in bare fallow soils after 80 years of continuous fertilizer addition. In Geoderma, vol. 200–201, pp. 40–44. doi: https://doi.org/10.1016/j.geoderma.2013.01.014PIERI, C. (1992) Fertility of Soils: A Future for Farming in the West African Savannah. Berlin: Springer-Verlag, pp. 347. ISBN 978-3-642-84322-8.PIRES, L.P. et al. (2017) Soil structure changes induced by tillage systems. In Soil Tilage Research, vol. 165, pp. 66–79. doi: https://doi.org/10.1016/j.still.2016.07.010SHEIN, E. V. (2005) Course of Soil Physics. Moscow: MGU, pp. 432. ISBN 5-211-05021-5 (in Russian).SIX, J. et al. (2004) A history of research on the link between (micro)aggregates, soil biota, and soil organic matter dynamics. In Soil Till Res., vol. 79, pp. 7–31. doi: https://doi.org/10.1016/j.still.2004.03.008ŠIMANSKÝ, V. (2011) Soil structure of Haplic Luvisol as influenced by tillage and crop residues ploughing. In Acta fytotechnica et zootechnica, vol. 14, no 1, pp. 27–29.ŠIMANSKÝ, V. and JONCZAK, J. (2016) Water-stable aggregates as a key element in the stabilization of soil organic matter in the Chernozems. In Carpathian Journal of Earth and Environmental Sciences, vol. 11(2), pp. 511–517.ŠIMANSKÝ, V. et al. 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In Geoderma, vol. 342, pp. 75–84. doi: https://doi.org/10.1016/j.geoderma.2019.02.020ŠIMANSKÝ, V. et al. (2019a) Slope position and management practices as factors influencing selected properties of topsoil. In Soil Science Annual (in press).ŠPIČKA, A. et al. (1964) Soil properties and processing. Praha: SZN (in Czech).VADJUNINA, A.F. and KORCHAGINA, Z.A. (1986) Methods of Study of Soil Physical Properties. Moscow: Agropromizdat (inRussian).WIESMEIER, M. et al. (2012) Aggregate stability and physical protection of soil organic carbon in semi-arid steppe soils. In European Journal of Soil Science, vol. 63, pp. 22–31. doi: https://doi.org/10.1111/j.1365-2389.2011.01418.xZHANG, B. and HORN, H. (2001) Mechanisms of aggregate stabilization in Ultisols from subtropical China. In Geoderma, vol. 99, pp. 123–145. doi: https://doi.org/10.1016/S0016-7061(00)00069-

    Spatial Variability of Actual Soil Moisture, pH and Bulk Soil Electrical Conductivity within the Area of the Former Oleszek Mill Pond Basin

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    Celem badań było określenie zróżnicowania przestrzennego wilgotności aktualnej (Wa), pH i przewodności elektrycznej (ECa) w powierzchniowych poziomach glebowych w niecce byłego stawu młyńskiego Oleszek. Młyny wodne to jedne z pierwszych budowli hydrotechnicznych w Polsce. Pojawiły się już na przełomie XI i XII wieku, natomiast upowszechniły się w XIII wieku. Budowa i funkcjonowanie młynów wodnych znacznie wpłynęła na przekształcenie środowiska przyrodniczego w ich otoczeniu, przede wszystkim na zmiany rzeźby terenu i warunków wodnych. Badania obejmowały pomiary Wa, pH i ECa w powierzchniowej warstwie gleby (0–30 cm). Pomiary wykonano za pomocą metody TDR aparatem Field Operated Meter – Easy Test FOM/mts w 49 punktach zlokalizowanych w obrębie niecki byłego stawu młyńskiego Oleszek. Zróżnicowanie wyników  Wa, pH i ECa wskazuje na znaczną zmienność przestrzenną powierzchniowej warstwy osadów zakumulowanych w niecce byłego stawu młyńskiego. Powierzchniowa warstwa osadów budujących analizowaną nieckę nie wykazuje jednak różnic w odniesieniu do podziału niecki na część proksymalną, środkową i dystalną. Zaobserwowane różnice mają postać punktowo występujących wartości ekstremalnych związanych z mikrorzeźbą powstałą po zakończeniu funkcjonowania stawu (wały brzegowe), lub wywołane są z lokalnymi czynnikami silnie modyfikującymi powierzchnię równiny biogenicznej w obrębie niecki takimi jak wysięki wód w strefie krawędziowej niecki

    Land use changes and landscape pattern dynamics of a peatland area under diversified human impact: the Grójec Valley (Central Poland)

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    The paper aims to assess the land use changes and the dynamics of the landscape pattern of the Grójec Valley in the scope of diverse anthropogenic impacts. The study site is located in the border of the Koło Basin and Kujawy Lakeland, Central Poland. This area was originally covered with wetlands. Since the beginning of the 20th century it has been influenced by intensive agricultural use, peat extraction and open-pit mining. The research is based on cartographic materials from 1941, 1981 and 2012. The most relevant finding was that in the first study period (1941–1981) the most common changes in land use (transformation of wetlands into grasslands with shrubs) took place. These were caused mainly by a change in hydrological conditions due to drainage for agricultural use (meadows and pastures) and peat extraction. The study confirmed that these land use changes significantly influenced the landscape structure in each of the analysed parameters (patch density and size, edge, shape and diversity metrics)

    Physiologically based pharmacokinetic-quantitative systems toxicology and safety (PBPK-QSTS) modeling approach applied to predict the variability of amitriptyline pharmacokinetics and cardiac safety in populations and in individuals

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    The physiologically based pharmacokinetic (PBPK) models allow for predictive assessment of variability in population of interest. One of the future application of PBPK modeling is in the field of precision dosing and personalized medicine. The aim of the study was to develop PBPK model for amitriptyline given orally, predict the variability of cardiac concentrations of amitriptyline and its main metabolite-nortriptyline in populations as well as individuals, and simulate the influence of those xenobiotics in therapeutic and supratherapeutic concentrations on human electrophysiology. The cardiac effect with regard to QT and RR interval lengths was assessed. The Emax model to describe the relationship between amitriptyline concentration and heart rate (RR) length was proposed. The developed PBPK model was used to mimic 29 clinical trials and 19 cases of amitriptyline intoxication. Three clinical trials and 18 cases were simulated with the use of PBPK-QSTS approach, confirming lack of cardiotoxic effect of amitriptyline in therapeutic doses and the increase in heart rate along with potential for arrhythmia development in case of amitriptyline overdose. The results of our study support the validity and feasibility of the PBPK-QSTS modeling development for personalized medicine

    SOIL ORGANIC MATTER STATUS IN AGRICULTURAL SOIL SEQUENCE OF FORMER SHORELINE OF DISAPPEARING SUMOWSKIE LAKES, NORTH-EASTERN POLAND

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    The aim of the study has been to define the stocks and the basic properties of soil organic matter in agricultural-used soil sequence located in the former shoreline of disappearing lakes. The study area is located in the catchment of the Sumowskie Lakes, the Brodnica Lake District, North-Eastern Poland. The investigations involved preparation of five soil pits located in the south-western part of the former Sumowskie Lake bottom and on the southern slope of the adjacent kame hill. The greatest soil transformation is reflected in the quality and quantity of the soil organic matter. Indexes of organic matter quality and TOC stocks are significantly changing along the studied transect. The strongly humidified organic matter is found in mursh horizons. Gyttja layers above the groundwater level have a medium humification index. Horizons saturated with water are very low humidified. TOC stocks drop along the analysed soil sequence from the biogenic plain to the top of the kame hill. Celem badań było określenie zasobów i podstawowych właściwości materii organicznej sekwencji rolniczo użytkowanych gleb dawnej strefy brzegowej zanikających jezior. Obszar badań był zlokalizowany w zlewni jezior Sumowskich na Pojezierzu Brodnickim w Polsce północno-wschodniej. Analizowano transekt składający się z pięciu profili glebowych znajdujących się w pd.-zach. części dawnego Jeziora Sumowskiego. Obejmował on dno dawnego jeziora oraz przylegające wzgórze kemowe. Największe zróżnicowanie gleb dotyczyło ilości i jakości glebowej materii organicznej. Zarówno właściwości materii organicznej, jak i jej zasoby wyraźnie różnicują się w analizowanym transekcie. Materia organiczna poziomów murszowych gleb pojeziornych odznacza się najwyższym stopniem humifikacji, warstwy gytii, powyżej poziomu wód gruntowych, pośrednim, a poziomy nasycone wodą najniższym spośród analizowanych. Zasoby węgla organicznego zmniejszają się wzdłuż transektu od gleb pojeziornych do szczytu pagórka kemowego (pararędziny)

    Technogenic soils in Toruń

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    Chapter 5 in: Przemysław Charzyński, Maciej Markiewicz, Marcin Świtoniak (Eds.) 2013. Technogenic soils atlas. Polish Society of Soil Science. Toruń
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