Redalyc.SOILS DEVELOPED on DIFFERENT PARENT MATERIALS
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Depolymerization and Mineralization – Investigating N Availability by a Novel N Tracing Model
SOIL Discuss., doi:10.5194/soil-2016-11, 2016 Manuscript under review for journal SOIL Published: 3 March 2016 c Author(s) 2016. CC-BY 3.0 License. Depolymerization and mineralization – investigating N availability by a novel 15N tracing model Louise C. Andresen1, Anna-Karin Björsne1, Samuel Bodé2, Leif Klemedtsson1, Pascal Boeckx2 and Tobias Rütting1 5 1Department of Earth Sciences, University of Gothenburg, Gothenburg, 405 30, Sweden 2Isotope Bioscience Laboratory, ISOFYS, Ghent University, Ghent, 9000, Belgium Correspondence to: Louise C. Andresen ([email protected]) Abstract. Depolymerization of soil organic matter such as proteins and peptides into monomers (e.g. amino acids) is currently thought to be the rate limiting step for N availability in terrestrial N cycles. The mineralization of free amino acids 10 (FAA), liberated by depolymerization of peptides, is an important fraction of the total N mineralization. Accurate assessment of peptide depolymerization and FAA mineralization rates is important in order to gain a better understanding of the N cycle dynamics. Due to the short time span, soil disturbance and unnatural high FAA content during the first few hours after the labelling with the traditional 15N pool dilution experiments, analytical models might overestimate peptide depolymerization rate. In this paper, we present an extended numerical 15N tracing model Ntrace which incorporates the FAA pool and related 15 N processes in order to 1) provide a more robust and coherent estimation of production and mineralization rates of FAAs; 2) and 2) suggest an amino acid N use efficiency (NUEFAA) for soil microbes, which is a more realistic estimation of soil microbial NUE compared to the NUE estimated by analytical methods. -
Soil Properties, and Soil Organic Carbon Stocks of Tropical Andosol Under Different Land Uses
Open Journal of Soil Science, 2013, 3, 153-162 153 http://dx.doi.org/10.4236/ojss.2013.33018 Published Online July 2013 (http://www.scirp.org/journal/ojss) Soil Properties, and Soil Organic Carbon Stocks of Tropical Andosol under Different Land Uses Girma Abera*, Endalkachew Wolde-Meskel School of Plant and Horticultural Sciences, Hawassa University, Hawassa, Ethiopia. Email: *girmajibat2006 @yahoo.com Received December 21st, 2012; revised April 21st, 2013; accepted April 29th, 2013 Copyright © 2013 Girma Abera, Endalkachew Wolde-Meskel. This is an open access article distributed under the Creative Commons Attribution License, which permits unrestricted use, distribution, and reproduction in any medium, provided the original work is properly cited. ABSTRACT Land use effect of tropical Andosol, with two from crop lands (Site 1 and Site 2) and one from Agroforestry coffee plantation (Site 3) was explored under laboratory conditions to understand their physical, chemical and biological prop- erties and soil organic carbon (SOC) stocks from the rift valley of Ethiopia. Site 3 that acquired less cultivation than others exhibited better aggregate size fraction (AF, 55%), higher aggregate stability (AS, 91%), and greater active mi- crobial biomass (AMB), reflecting better soil structure development. Comparatively, higher total carbon (TC), organic carbon (OC) and total nitrogen (TN) concentrations were recorded in bulk soils and microaggregate fractions of Site 2 and Site 3 than in intensively cultivated Site 1. As expected, microaggregate fractions displayed greater OC and TN than bulk soils across all land uses. Site 1 revealed higher metabolic quotient (qCO2) and lower SOC stock (2.1 Mg·ha−1), suggesting microbial stress, while micro nutrients deficiencies were observed with the alkaline soil (Site 2). -
Sorption and Desorption of Vanadate, Arsenate and Chromate by Two Volcanic Soils of Equatorial Africa
Article Sorption and Desorption of Vanadate, Arsenate and Chromate by Two Volcanic Soils of Equatorial Africa Sara Gonzalez-Rodriguez 1 and Maria Luisa Fernandez-Marcos 1,2,* 1 Department of Soil Science and Agricultural Chemistry, Universidad de Santiago de Compostela, 27002 Lugo, Spain; [email protected] 2 Institute of Agricultural Biodiversity and Rural Development, University of Santiago de Compostela, 27002 Lugo, Spain * Correspondence: [email protected] Abstract: Sorption of oxyanions by soils and mineral surfaces is of interest due to their role as nutrients or pollutants. Volcanic soils are variable charge soils, rich in active forms of aluminum and iron, and capable of sorbing anions. Sorption and desorption of vanadate, arsenate, and chromate by two African andosols was studied in laboratory experiments. Sorption isotherms were determined by equilibrating at 293 K soil samples with oxyanion solutions of concentrations between 0 and 100 mg L−1 V, As, or Cr, equivalent to 0−2.0 mmol V L−1, 0−1.3 mmol As L−1, and −1 0−1.9 mmol Cr L , in NaNO3; V, As, or Cr were determined by ICP-mass spectrometry in the equilibrium solution. After sorption, the soil samples were equilibrated with 0.02 M NaNO3 to study desorption. The isotherms were adjusted to mathematical models. After desorption with NaNO3, desorption experiments were carried out with a 1 mM phosphate. The sorption of vanadate and arsenate was greater than 90% of the amount added, while the chromate sorption was much lower (19–97%). The sorption by the Silandic Andosol is attributed to non-crystalline Fe and Al, while in Citation: Gonzalez-Rodriguez, S.; the Vitric Andosol, crystalline iron species play a relevant role. -
World Reference Base for Soil Resources 2014 International Soil Classification System for Naming Soils and Creating Legends for Soil Maps
ISSN 0532-0488 WORLD SOIL RESOURCES REPORTS 106 World reference base for soil resources 2014 International soil classification system for naming soils and creating legends for soil maps Update 2015 Cover photographs (left to right): Ekranic Technosol – Austria (©Erika Michéli) Reductaquic Cryosol – Russia (©Maria Gerasimova) Ferralic Nitisol – Australia (©Ben Harms) Pellic Vertisol – Bulgaria (©Erika Michéli) Albic Podzol – Czech Republic (©Erika Michéli) Hypercalcic Kastanozem – Mexico (©Carlos Cruz Gaistardo) Stagnic Luvisol – South Africa (©Márta Fuchs) Copies of FAO publications can be requested from: SALES AND MARKETING GROUP Information Division Food and Agriculture Organization of the United Nations Viale delle Terme di Caracalla 00100 Rome, Italy E-mail: [email protected] Fax: (+39) 06 57053360 Web site: http://www.fao.org WORLD SOIL World reference base RESOURCES REPORTS for soil resources 2014 106 International soil classification system for naming soils and creating legends for soil maps Update 2015 FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS Rome, 2015 The designations employed and the presentation of material in this information product do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations (FAO) concerning the legal or development status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The mention of specific companies or products of manufacturers, whether or not these have been patented, does not imply that these have been endorsed or recommended by FAO in preference to others of a similar nature that are not mentioned. The views expressed in this information product are those of the author(s) and do not necessarily reflect the views or policies of FAO. -
The Muencheberg Soil Quality Rating (SQR)
The Muencheberg Soil Quality Rating (SQR) FIELD MANUAL FOR DETECTING AND ASSESSING PROPERTIES AND LIMITATIONS OF SOILS FOR CROPPING AND GRAZING Lothar Mueller, Uwe Schindler, Axel Behrendt, Frank Eulenstein & Ralf Dannowski Leibniz-Zentrum fuer Agrarlandschaftsforschung (ZALF), Muencheberg, Germany with contributions of Sandro L. Schlindwein, University of St. Catarina, Florianopolis, Brasil T. Graham Shepherd, Nutri-Link, Palmerston North, New Zealand Elena Smolentseva, Russian Academy of Sciences, Institute of Soil Science and Agrochemistry (ISSA), Novosibirsk, Russia Jutta Rogasik, Federal Agricultural Research Centre (FAL), Institute of Plant Nutrition and Soil Science, Braunschweig, Germany 1 Draft, Nov. 2007 The Muencheberg Soil Quality Rating (SQR) FIELD MANUAL FOR DETECTING AND ASSESSING PROPERTIES AND LIMITATIONS OF SOILS FOR CROPPING AND GRAZING Lothar Mueller, Uwe Schindler, Axel Behrendt, Frank Eulenstein & Ralf Dannowski Leibniz-Centre for Agricultural Landscape Research (ZALF) e. V., Muencheberg, Germany with contributions of Sandro L. Schlindwein, University of St. Catarina, Florianopolis, Brasil T. Graham Shepherd, Nutri-Link, Palmerston North, New Zealand Elena Smolentseva, Russian Academy of Sciences, Institute of Soil Science and Agrochemistry (ISSA), Novosibirsk, Russia Jutta Rogasik, Federal Agricultural Research Centre (FAL), Institute of Plant Nutrition and Soil Science, Braunschweig, Germany 2 TABLE OF CONTENTS PAGE 1. Objectives 4 2. Concept 5 3. Procedure and scoring tables 7 3.1. Field procedure 7 3.2. Scoring of basic indicators 10 3.2.0. What are basic indicators? 10 3.2.1. Soil substrate 12 3.2.2. Depth of A horizon or depth of humic soil 14 3.2.3. Topsoil structure 15 3.2.4. Subsoil compaction 17 3.2.5. Rooting depth and depth of biological activity 19 3.2.6. -
Progressive and Regressive Soil Evolution Phases in the Anthropocene
Progressive and regressive soil evolution phases in the Anthropocene Manon Bajard, Jérôme Poulenard, Pierre Sabatier, Anne-Lise Develle, Charline Giguet- Covex, Jeremy Jacob, Christian Crouzet, Fernand David, Cécile Pignol, Fabien Arnaud Highlights • Lake sediment archives are used to reconstruct past soil evolution. • Erosion is quantified and the sediment geochemistry is compared to current soils. • We observed phases of greater erosion rates than soil formation rates. • These negative soil balance phases are defined as regressive pedogenesis phases. • During the Middle Ages, the erosion of increasingly deep horizons rejuvenated pedogenesis. Abstract Soils have a substantial role in the environment because they provide several ecosystem services such as food supply or carbon storage. Agricultural practices can modify soil properties and soil evolution processes, hence threatening these services. These modifications are poorly studied, and the resilience/adaptation times of soils to disruptions are unknown. Here, we study the evolution of pedogenetic processes and soil evolution phases (progressive or regressive) in response to human-induced erosion from a 4000-year lake sediment sequence (Lake La Thuile, French Alps). Erosion in this small lake catchment in the montane area is quantified from the terrigenous sediments that were trapped in the lake and compared to the soil formation rate. To access this quantification, soil processes evolution are deciphered from soil and sediment geochemistry comparison. Over the last 4000 years, first impacts on soils are recorded at approximately 1600 yr cal. BP, with the erosion of surface horizons exceeding 10 t·km− 2·yr− 1. Increasingly deep horizons were eroded with erosion accentuation during the Higher Middle Ages (1400–850 yr cal. -
1 1 2 3 4 Estimating Organic Carbon in the Soils of Europe For
CORE Metadata, citation and similar papers at core.ac.uk Provided by Cranfield CERES 1 European Journal of Soil Science, 2005, Volume 56 Issue 5, Pages 655 – 671 2 3 4 5 Estimating Organic Carbon in the Soils of Europe for Policy Support 6 7 1,3 2 1 1 8 R.J.A. JONES , R. HIEDERER , E. RUSCO & L. MONTANARELLA 9 10 11 1Institute for Environment & Sustainability, Joint Research Centre, Ispra (VA) 21020, 12 Italy, 2Land Management Unit, Institute for Environment & Sustainability, Joint 13 Research Centre, Ispra (VA) 21020 Italy and 3National Soil Resources Institute, 14 Cranfield University, Silsoe, Bedfordshire MK45 4DT, UK 15 16 Correspondence: R.J.A. Jones. Email: [email protected] 17 18 Running title: Estimating soil organic carbon for Europe 19 1 20 Summary 21 The estimation of soil carbon content is of pressing concern for soil protection and in 22 mitigation strategies for global warming. This paper describes the methodology developed 23 and the results obtained in a study aimed at estimating organic carbon contents (%) in 24 topsoils across Europe. The information presented in map form provides policy makers 25 with estimates of current topsoil organic carbon contents for developing strategies for soil 26 protection at regional level. Such baseline data is also of importance in global change 27 modelling and may be used to estimate regional differences in soil organic carbon (SOC) 28 stocks and projected changes therein, as required for example under the Kyoto Protocol to 29 UNFCCC, after having taken into account regional differences in bulk density. 30 The study uses a novel approach combining a rule-based system with detailed 31 thematic spatial data layers to arrive at a much-improved result over either method, using 32 advanced methods for spatial data processing. -
Chernozems Kastanozems Phaeozems
Chernozems Kastanozems Phaeozems Peter Schad Soil Science Department of Ecology Technische Universität München Steppes dry, open grasslands in the mid-latitudes seasons: - humid spring and early summer - dry late summer - cold winter occurrence: - Eurasia - North America: prairies - South America: pampas Steppe soils Chernozems: mostly in steppes Kastanozems: steppes and other types of dry vegetation Phaeozems: steppes and other types of medium-dry vegetation (till 1998: Greyzems, now merged to the Phaeozems) all steppe soils: mollic horizon Definition of the mollic horizon (1) The requirements for a mollic horizon must be met after the first 20 cm are mixed, as in ploughing 1. a soil structure sufficiently strong that the horizon is not both massive and hard or very hard when dry. Very coarse prisms (prisms larger than 30 cm in diameter) are included in the meaning of massive if there is no secondary structure within the prisms; and Definition of the mollic horizon (2) 2. both broken and crushed samples have a Munsell chroma of less than 3.5 when moist, a value darker than 3.5 when moist and 5.5 when dry (shortened); and 3. an organic carbon content of 0.6% (1% organic matter) or more throughout the thickness of the mixed horizon (shortened); and Definition of the mollic horizon (3) 4. a base saturation (by 1 M NH4OAc) of 50% or more on a weighted average throughout the depth of the horizon; and Definition of the mollic horizon (4) 5. the following thickness: a. 10 cm or more if resting directly on hard rock, a petrocalcic, petroduric or petrogypsic horizon, or overlying a cryic horizon; b. -
Impact of Plant Roots and Soil Organisms on Soil Micromorphology and Hydraulic Properties
CMYK Biologia, Bratislava, 61/Suppl. 19: S339—S343, 2006 S339 Impact of plant roots and soil organisms on soil micromorphology and hydraulic properties Radka Kodešová1,VítKodeš2, Anna Žigová3 &JiříŠimůnek4 1Czech University of Agriculture in Prague, Department of Soil Science and Geology, Kamýcka 129,CZ–16521 Prague, Czech Republic; e-mail: [email protected] 2Czech Hydrometeorological Institute, Department of Water Quality, Na Šabatce 17,CZ–14306 Prague, Czech Republic 3Academy of Sciences of the Czech Republic, Institute of Geology, Rozvojová 269,CZ–16502 Prague, Czech Republic 4University of California Riverside, Department of Environmental Sciences, Riverside, CA 92521,USA Abstract: A soil micromorphological study was performed to demonstrate the impact of soil organisms on soil pore structure. Two examples are shown here. First, the influence of earthworms, enchytraeids and moles on the pore structure of a Greyic Phaeozem is demonstrated by comparing two soil samples taken from the same depth of the soil profile that either were affected or not affected by these organisms. The detected image porosity of the organism-affected soil sample was 5 times larger then the porosity of the not-affected sample. The second example shows macropores created by roots and soil microorganisms in a Haplic Luvisol and subsequently affected by clay coatings. Their presence was reflected in the soil water retention curve, which displayed multiple S-shaped features as obtained from the water balance carried out for the multi-step outflow experiment. The dual permeability models implemented in HYDRUS-1D was applied to obtain parameters characterizing multimodal soil hydraulic properties using the numerical inversion of the multi-step outflow experiment. -
Distribution and Classification of Volcanic Ash Soils
83 Distribution and Classification of Volcanic Ash Soils 1* 2 Tadashi TAKAHASHI and Sadao SHOJI 1 Graduate School of Agricultural Science, Tohoku University 1-1, Tsutsumidori, Amamiya-machi, Aoba-ku, Sendai, 981-8555 Japan e-mail: [email protected] 2 Professor Emeritus, Tohoku University 5-13-27, Nishitaga, Taihaku-ku, Sendai, 982-0034 Japan *corresponding author Abstract Volcanic ash soils are distributed exclusively in regions where active and recently extinct volcanoes are located. The soils cover approximately 124 million hectares, or 0.84% of the world’s land surface. While, thus, volcanic ash soils comprise a relatively small extent, they represent a crucial land resource due to the excessively high human populations living in these regions. However, they did not receive worldwide recognition among soil scientists until the middle of the 20th century. Development of international classification systems was put forth by the 1978 Andisol proposal of G. D. Smith. The central concept of volcanic ash soils was established after the finding of nonallophanic volcanic ash soils in Japan in 1978. Nowadays, volcanic ash soils are internationally recognized as Andisols in Soil Taxonomy (United States Department of Agriculture) and Andosols in the World Reference Base for Soil Resources (FAO, International Soil Reference and Information Centre and International Society of Soil Science). Several countries including Japan and New Zealand have developed their own national classification systems for volcanic ash soils. Finally correlation of the international and domestic classification systems is described using selected volcanic ash soils. Key words: Andisols, Andosols, Japanese Cultivated Soil Classification, New Zealand Soil Classification, Soil Taxonomy, World Reference Base for Soil Resources (WRB) 1. -
Critical Accumulation of Fertilizer-Derived Uranium in Icelandic Grassland
Critical accumulation of fertilizer-derived uranium in Icelandic grassland ANGOR UNIVERSITY Andosol Sun, Yajie; Amelung, Wulf; Gudmundsson, Thorstein; Wu, Bei; Bol, Roland Environmental Sciences Europe DOI: 10.1186/s12302-020-00367-w PRIFYSGOL BANGOR / B Published: 01/07/2020 Publisher's PDF, also known as Version of record Cyswllt i'r cyhoeddiad / Link to publication Dyfyniad o'r fersiwn a gyhoeddwyd / Citation for published version (APA): Sun, Y., Amelung, W., Gudmundsson, T., Wu, B., & Bol, R. (2020). Critical accumulation of fertilizer-derived uranium in Icelandic grassland Andosol. Environmental Sciences Europe, 32(1), [92]. https://doi.org/10.1186/s12302-020-00367-w Hawliau Cyffredinol / General rights Copyright and moral rights for the publications made accessible in the public portal are retained by the authors and/or other copyright owners and it is a condition of accessing publications that users recognise and abide by the legal requirements associated with these rights. • Users may download and print one copy of any publication from the public portal for the purpose of private study or research. • You may not further distribute the material or use it for any profit-making activity or commercial gain • You may freely distribute the URL identifying the publication in the public portal ? Take down policy If you believe that this document breaches copyright please contact us providing details, and we will remove access to the work immediately and investigate your claim. 26. Sep. 2021 Sun et al. Environ Sci Eur (2020) 32:92 https://doi.org/10.1186/s12302-020-00367-w COMMENTARY Open Access Critical accumulation of fertilizer-derived uranium in Icelandic grassland Andosol Yajie Sun1,2* , Wulf Amelung1,2, Thorstein Gudmundsson3, Bei Wu1 and Roland Bol1 Abstract Long-term phosphorus (P) fertilizer application can lead to an accumulation of uranium (U) in agricultural soil, poten- tially posing risks on the environment and human health. -
Alkalization Allitization Allogenic Alluvium Andosols
ANDOSOLS 39 Bibliography Pédro, G., 1983. Structuring of some basic pedological processes. Geo- derma, 31: 289–299. ALLOGENIC Describes components transported into the soil from some exter- nal place of origin. Equivalent to the geological term allochtho- nous. See Authigenic. ALLUVIUM Alluvial sediment deposited from flowing water; or per- taining to a deposit formed in that way. The parent material of alluvial soils. Bibliography Gerrard, J., 1987. Alluvial Soils. New York: Van Nostrand Reinhold, 305 pp. Figure A21 The alkaline soils field of Figure A19, magnified to show the approximate ranges of precipitation of carbonates, sulfates, halides and silicates in soils. The pH of an evaporating soil solution depends mainly on the concentrations of carbonate species in the system. The ANDOSOLS precipitation of neutral salts such as gypsum and halite is not pH dependent. The lower pH limits of sulfate and halide precipitation ranges shown in the diagram are based simply on empirical observation. A good deal of variability is possible depending principally Introduction on the initial composition of the soil solution. Andosols are soils of active volcanic areas. They exhibit unique soil properties that place them apart from other soils. The term ‘andosol’ is derived from Japanese, ‘an’ meaning dark, and ‘do’ Cross-references connotating soil (Figure A22). Andosols are also found outside active volcanic regions when environmental conditions favor their Calcisols Gypsisols formation. Andosols have a limited extent (1–2%) of Earth's land Solonchaks surface, but many such areas are densely populated. Solonetz The discussion of this entry follows the terminology of the World Reference Base for Soil Resources (WRB, FAO, 1998).