Distribution and Classification of Volcanic Ash Soils
Total Page:16
File Type:pdf, Size:1020Kb
Load more
Recommended publications
-
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). -
Stabilization and Destabilization of Soil Organic Matter: Mechanisms and Controls
13F7H GEODERLIA ELSEVIER Geoderma 74 (1996) 65-105 • Stabilization and destabilization of soil organic matter: mechanisms and controls Phillip Sollins, Peter Homann, Bruce A. Caldwell Department of Forest Science Oregon State University Corvallis, OR 97331, USA Receed 1 December 1993; revised 26 July 1995; accepted 3 April 1996 Abstract We present a conceptual model of the processes by which plant leaf and root litter is transformed to soil organic C and CO 2. Stabilization of a portion of the litter C yields material that resists further transformation; destabilization yields material that is more susceptible to microbial respiration. Stability of the organic C is viewed as resulting from three general sets of characteristics. Recalcitrance comprises, molecular-level characteristics of organic substances, including elemental composition, presence of functional groups, and molecular conformation, that influence their degradation by microbes and enzymes. Interactions refers to the inter-molecular interactions between organics and either inorganic substances or other organic substances that alter the rate of degradation of those organics or synthesis of new organics. Accessibility refers to the location of organic substances with respect to microbes and enzymes. Mechanisms by which these three characteristics change through time are reviewed along with controls on those mechanisms. This review suggests that the following changes in the study of soil organic matter dynamics would speed progress: (1) increased effort to incorporate results -
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. -
The Hidden Ecological Resource of Andic Soils in Mountain Ecosystems: Evidence from Italy
Solid Earth, 9, 63–74, 2018 https://doi.org/10.5194/se-9-63-2018 © Author(s) 2018. This work is distributed under the Creative Commons Attribution 4.0 License. The hidden ecological resource of andic soils in mountain ecosystems: evidence from Italy Fabio Terribile1,2, Michela Iamarino1, Giuliano Langella1, Piero Manna2,3, Florindo Antonio Mileti1, Simona Vingiani1,2, and Angelo Basile2,3 1Department of Agricultural Sciences, University of Naples Federico II, Via Università 100, 80055 Portici (Naples), Italy 2CRISP, Interdepartmental Research Centre on the Earth Critical Zone, University of Naples Federico II, Via Università 100, 80055 Portici (Naples), Italy 3Institute for Mediterranean Agricultural and Forestry Systems, National Research Council of Italy, Via Patacca 85, 80056 Ercolano (Naples), Italy Correspondence: Fabio Terribile ([email protected]) Received: 9 June 2017 – Discussion started: 9 August 2017 Revised: 1 November 2017 – Accepted: 20 November 2017 – Published: 31 January 2018 Abstract. Andic soils have unique morphological, physical, 1 Introduction and chemical properties that induce both considerable soil fertility and great vulnerability to land degradation. More- Andic soils (i.e. soils with evident andosolization process) over, they are the most striking mineral soils in terms of are known to have a unique set of morphological, physi- large organic C storage and long C residence time. This is cal, and chemical soil properties. Andosolization (Ugolini especially related to the presence of poorly crystalline clay et al., 1988; Shoji et al., 1993) is a major soil-forming pro- minerals and metal–humus complexes. Recognition of andic cess regardless of whether these soils meet or do not meet soils is then very important. -
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. -
Diagnostic Horizons
Exam III Wednesday, November 7th Study Guide Posted Tomorrow Review Session in Class on Monday the 4th Soil Taxonomy and Classification Diagnostic Horizons Epipedons Subsurface Mollic Albic Umbric Kandic Ochric Histic Argillic Melanic Spodic Plaggen Anthropic Oxic 1 Surface Horizons: Mollic- thick, dark colored, high %B.S., structure Umbric – same, but lower B.S. Ochric – pale, low O.M., thin Histic – High O.M., thick, wet, dark Sub-Surface Horizons: Argillic – illuvial accum. of clay (high activity) Kandic – accum. of clay (low activity) Spodic – Illuvial O.M. accumulation (Al and/or Fe) Oxic – highly weathered, kaolinite, Fe and Al oxides Albic – light colored, elluvial, low reactivity Elluviation and Illuviation Elluviation (E horizon) Organic matter Clays A A E E Bh horizon Bt horizon Bh Bt Spodic horizon Argillic horizon 2 Soil Taxonomy Diagnostic Epipedons Diagnostic Subsurface horizons Moisture Regimes Temperature Regimes Age Texture Depth Soil Taxonomy Soil forming processes, presence or Order Absence of major diagnostic horizons 12 Similar genesis Suborder 63 Grasslands – thick, dark Great group 250 epipedons High %B.S. Sub group 1400 Family 8000 Series 19,000 Soil Orders Entisols Histosols Inceptisols Andisols Gelisols Alfisols Mollisols Ultisols Spodosols Aridisols Vertisols Oxisols 3 Soil Orders Entisol Ent- Recent Histosol Hist- Histic (organic) Inceptisol Incept- Inception Alfisol Alf- Nonsense Ultisol Ult- Ultimate Spodosol Spod- Spodos (wood ash) Mollisol Moll- Mollis (soft) Oxisol Ox- oxide Andisol And- Ando (black) Gelisol -
Alumohydrocalcite Caal2(CO3)2(OH)4 • 3H2O C 2001-2005 Mineral Data Publishing, Version 1 Crystal Data: Triclinic
Alumohydrocalcite CaAl2(CO3)2(OH)4 • 3H2O c 2001-2005 Mineral Data Publishing, version 1 Crystal Data: Triclinic. Point Group: 1or1. As fibers and needles, to 2.5 mm; commonly in radial aggregates and spherulites, feltlike crystal linings, and powdery to chalky masses. Physical Properties: Cleavage: {100} perfect; {010} imperfect. Tenacity: Brittle. Hardness = 2.5 D(meas.) = 2.21–2.24 D(calc.) = 2.213 Decomposes in boiling H2O to calcite and hydrous aluminum oxide. Optical Properties: Transparent to opaque. Color: Chalky white to pale blue, pale yellow, cream, gray; pale rose or brownish pink to dark violet in chromian varieties; colorless in transmitted light. Luster: Vitreous to pearly, earthy. Optical Class: Biaxial (–). Orientation: X = b; extinction inclined 6◦–10◦. α = 1.485–1.502 β = 1.553–1.563 γ = 1.570–1.585 2V(meas.) = 64◦ 2V(calc.) = 50◦–55◦ Cell Data: Space Group: P 1or P 1 (chromian). a = 6.498(3) b = 14.457(4) c = 5.678(3) α =95.83(5)◦ β =93.23(3)◦ γ =82.24(3)◦ Z=2 X-ray Powder Pattern: Bergisch-Gladbach, Germany. 6.25 (100), 6.50 (70), 3.23 (60), 2.039 (50), 2.519 (40), 7.21 (30), 2.860 (30) Chemistry: (1) (2) (3) (1) (2) (3) CO2 24.2 26.4 26.19 CaO 17.8 16.5 16.68 Al2O3 31.3 22.0 30.33 H2O 26.7 26.6 26.80 Cr2O3 8.3 Total 100.0 99.8 100.00 2− 1− (1) Bergisch-Gladbach, Germany; (CO3) , (OH) , and H2O confirmed by IR. -
Behaviour and Geotechnical Properties of Residual Soils and Allophane Clays
Wesley, L. (2009). Behaviour and geotechnical properties of residual soils and allophane clays. Obras y Proyectos 6, 5-10. Behaviour and geotechnical properties of residual soils and allophane clays Fecha de entrega: 20 de Septiembre 2009 Fecha de aceptación: 23 de Noviembre 2009 Laurie Wesley Department of Civil and Environmental Engineering, the University of Auckland, Private Bag 92019, Auckland, New Zealand, [email protected] An overview of the properties of residual soils is given in the first part En la primera parte del artículo se entrega una descripción general de of the paper. The different processes by which residual and sedimentary los suelos residuales. Se detallan los diferentes procesos en los cuales son soils are formed are described, and the need to be aware that procedures formados los suelos residuales y sedimentarios, poniendo hincapié en la applicable to sedimentary soils do not necessarily apply to residual soils necesidad de estar atento a que los procedimientos aplicados a los suelos is emphasised. In particular, it is shown that the log scale normally sedimentarios no son necesariamente aplicables a los suelos residuales. used for presenting oedometer test results is not appropriate or relevant En particular, se muestra que la escala logarítmica generalmente usada to residual soils. The second part of the paper gives an account of para presentar resultados de ensayos edométricos no es apropiada o the special properties of allophane clays. Their abnormally high water pertinente para suelos residuales. La segunda parte del artículo da content and Atterberg limits are described, and it is shown that despite cuenta de las propiedades especiales de arcillas alofánicas. -
Influence of Soil Type on the Reliability of the Prediction Model
agronomy Article Influence of Soil Type on the Reliability of the Prediction Model for Bioavailability of Mn, Zn, Pb, Ni and Cu in the Soils of the Republic of Serbia Jelena Maksimovi´c*, Radmila Pivi´c,Aleksandra Stanojkovi´c-Sebi´c , Marina Jovkovi´c,Darko Jaramaz and Zoran Dini´c Institute of Soil Science, Teodora Drajzera 7, 11000 Belgrade, Serbia; [email protected] (R.P.); [email protected] (A.S.-S.); [email protected] (M.J.); [email protected] (D.J.); [email protected] (Z.D.) * Correspondence: [email protected] Abstract: The principles of sustainable agriculture in the 21st century are based on the preservation of basic natural resources and environmental protection, which is achieved through a multidisciplinary approach in obtaining solutions and applying information technologies. Prediction models of bioavailability of trace elements (TEs) represent the basis for the development of machine learning and artificial intelligence in digital agriculture. Since the bioavailability of TEs is influenced by the physicochemical properties of the soil, which are characteristic of the soil type, in order to obtain more reliable prediction models in this study, the testing set from the previous study was grouped based on the soil type. The aim of this study was to examine the possibility of improvement in the prediction of bioavailability of TEs by using a different strategy of model development. After the training set was grouped based on the criteria for the new model development, the developed basic models were compared to the basic models from the previous study. The second step was to develop Citation: Maksimovi´c,J.; Pivi´c,R.; models based on the soil type (for the eight most common soil types in the Republic of Serbia—RS) Stanojkovi´c-Sebi´c,A.; Jovkovi´c,M.; and to compare their reliability to the basic models. -
Iron and Aluminum Association with Microbially Processed Organic Matter Via Meso-Density Aggregate Formation Across Soils: Organo- Metallic Glue Hypothesis
https://doi.org/10.5194/soil-2020-32 Preprint. Discussion started: 11 June 2020 c Author(s) 2020. CC BY 4.0 License. Iron and aluminum association with microbially processed organic matter via meso-density aggregate formation across soils: organo- metallic glue hypothesis 5 Rota Wagai1, Masako Kajiura1, Maki Asano2 1National Agriculture and Food Research Organization, Institute for Agro-Environmental Sciences. 3-1-3 Kan-nondai, Tsukuba, Ibaraki, 305-8604, Japan 2Faculty of Life and Environmental Sciences, University of Tsukuba, 1-1-1 Tennodai, Tsukuba, Ibaraki 305-8572, Japan Correspondence to: Rota Wagai ([email protected]) 10 Abstract. Global significance of iron (Fe) and aluminum (Al) for the storage of organic matter (OM) in soils and surface sediments is increasingly recognized. Yet specific metal phases involved or the mechanism behind metal-OM correlations frequently shown across soils remain unclear. We identified density fraction locations of major metal phases and OM using 23 soil samples from 5 climate zones and 5 soil orders (Andisols, Spodosols, Inceptisols, Mollisols, Ultisols), including several subsurface horizons and both natural and managed soils. Each soil was separated to 4 to 7 density fractions using sodium 15 polytungstate with mechanical shaking, followed by the sequential extraction of each fraction with pyrophosphate (PP), acid oxalate (OX), and finally with dithionite-citrate (DC) to estimate pedogenic metal phases of different solubility and crystallinity. The extractable Fe and Al concentrations (per fraction) generally showed unique unimodal distribution along particle density gradient for each soil and each extractable metal phase. Across the studied soils, the maximum metal concentrations were always at meso-density range (1.8-2.4 g cm-3) within which PP-extractable metals peaked at 0.3-0.4 g cm- 20 3 lower density range relative to OX- and DC-extractable metals. -
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).