Soil Physical Properties

Total Page:16

File Type:pdf, Size:1020Kb

Soil Physical Properties Soil Horizons Master Horizons O A O horizon E A horizon E horizon B B horizon C horizon C R horizon W horizon R W Master Horizons O horizon – predominantly organic matter (litter and humus) A horizon – zone of organic matter accumulation E horizon – zone of eluviation (loss of clay, Fe, Al) B horizon – zone of accumulation (clay, Fe, Al, CaC03, salts…) – forms below O, A, or E horizon Master Horizons C horizon – little or no pedogenic alteration, unconsolidated parent material, soft bedrock R horizon – hard, continuous bedrock O horizon A horizon E horizon B horizon B horizon B horizon B horizon C horizon R horizon Transitional Horizons contains properties of horizon above and horizon below – AB – mostly A horizon, but some B horizon – BA – mostly B horizon, but some A horizon – BE – mostly B horizon, but some E horizon – BC – mostly B horizon, but some C horizon – CB – mostly C horizon, but some B horizon – C/B – intermingled bodies of C and B horizon material, majority is C horizon material Transitional Horizons EB BC Transitional Horizons BE BC Horizon Suffixes Horizon Criteria Suffix a highly decomposed organic matter (O) b buried genetic horizon (any) c concretions or nodules (any) e moderately decomposed organic matter (O) g strong gleying (any) h illuvial organic matter accumulation (B) i slightly decomposed organic material (O) k pedogenic carbonate accumulation (B or C) Horizon Suffixes Horizon Criteria Suffix o residual sesquioxide accumulation (B) p plow layer or other artificial disturbance (A) r weathered or soft bedrock (C) s illuvial sesquioxide accumulation (B) ss slickensides (B) t illuvial accumulation of silicate clay (B) v plinthite (B) w weak color or structure (B) x fragipan (B) Subhorizon Examples Ap Ap Bt Bt Btx Alfisol Ultisol Subhorizon Examples O A E Bh A Bs Bt Bw Bk C Spodosol Aridisol Subhorizon Examples Ap A1 Bo A2 Bk Mollisol Oxisol Subhorizon Examples Oe Oa C Histosol Entisol Subhorizon Examples Plinthic Kandiudult Numerical Suffixes A1 used to denote A2 subdivisions within a master horizon Bt1 Bt2 Bt3 C1 C2 Numerical Suffixes Ap A C1 Bt1 C2 Bt2 C3 BC Entisol Discontinuities changes in parent material or mode of deposition colluvium over residual limestone soil over sandstone bedrock – A, E, Bt1, 2Bt2, 2Bt3, 2BC, 2C, 3R by convention, 1 is understood, but not shown Discontinuities Bw Ap Bt1 2R Bt2 2Bt1 colluvium over residuum loess over limestone residuum Boundaries distinctness – distance through which one horizon grades into another abrupt (0-2.5cm), clear (2.5-5cm), gradual (5-15cm), diffuse (>15cm) topography – lateral undulation and continuity of the boundary between horizons smooth (planar), wavy (width>depth), irregular (depth>width), broken (discontinuous) Boundaries abrupt smooth abrupt wavy Boundaries clear smooth clear irregular Boundaries gradual smooth diffuse smooth Boundaries irregular broken SOIL COLOR SOIL COLOR Both use Munsell Notation Munsell notation (cont.) 7.5 YR 4 / 3 The number before the slash is the Value. The number after the slash is Value indicates the lightness of a the Chroma. color. The scale of value ranges Chroma describes how the “intensity” from 0 for pure black to 8 for pure of a color. The scale ranges from 1 to white. 8. For neutral colors, chroma is 0. Color Mechanics 1. Break the ped. If it is dry, moisten it slightly with water from your water bottle. 2. Stand with the sun over your shoulder so that sunlight shines on the color chart and the soil sample you are examining. 3. Compare the color of the inside surface with the soil color chart. Note: Sometimes, a soil sample may have more than one color. Record the colors and indicate (1) the matrix (dominant color) and (2) other colors (mottles or redox). Color Mechanics Viewing Conditions ? • very cloudy days • foggy days • early morning • late afternoon • wintertime conditions. • smoky conditions • indoor artificial light • nighttime ?????? Inferred Soil Characteristics Aquic Conditions soils with aquic conditions are those that undergo continuous or periodic saturation or reduction Saturation endosaturation – soil is saturated with water in all layers from the upper boundary of saturation to a depth of 200 cm or more from the mineral surface – groundwater saturation episaturation – water table is perched on top of an impermeable layer Formation of Redoximorphic Features Anaerobic conditions – soil is saturated so most all pores are filled with water, absence of oxygen Prolonged anaerobiosis – changes the chemical processes in the soil Reduction of Fe and Mn oxides – results in distinct soil morphological characteristics most are readily observable changes in soil color Soil Color and Oxidation / Reduction In subsoil horizons, Fe and Mn oxides give soils their characteristic brown, red, yellow colors Soil Color When reduced, Fe and Mn are mobile and can be Coating of Fe2O3 stripped from the soil particles Mineral grain (gray) Leaving the characteristic mineral grain color Gray Soil Red Soil Remove Fe – usually a “grayish” color Types of Redoximorphic Features Redox Concentrations – Masses – Pore Linings – Nodules and Concretions Redox Depletions – Depleted Matrix Reduced Matrix Redox Concentrations Bodies of apparent accumulation of Fe-Mn oxides – Masses – Pore Linings ped faces root channels – Nodules and Concretions Soft Masses Soft bodies – frequently in the soil matrix – variable shape – can usually be removed from the soil “intact” Soft Masses in Sand The masses have diffuse reddish boundaries Depleted Matrix Dominant color of the soil is “gray” Commonly used to identify hydric soils Describing Redoximorphic Features Concentrations and Depletions – Describe type, color, abundance and location (i.e. along macropores or within matrix) contrast can be obtained from color charts Reduced Matrix – Describe reduced matrix color, oxidized color, and time for color change to occur Mottles - Quantity few <2% common 2 to <20% many (>20%) Mottles - Size fine -- <2 mm medium -- 2 to 5 mm coarse -- 5 to 20 mm very coarse – 20 to 76 mm extremely coarse -- >76 mm Redox Concentrations Hard Fe/Mn nodule in matrix (likely relict) Pore linings on root Pore linings on ped surface channel Soft Fe mass in matrix Hard Fe/Mn concretion in matrix Hard Fe/Mn nodule in matrix (likely contemporary) Adapted from Fig 1, Vepraskas 1995 Schematic illustration showing different kinds of redox concentrations and their relationship to soil macropores and matrices Interpretation Problems Redoximorphic features do not occur in all soils Low amounts of soluble Organic Carbon High pH Cold temperatures Low amounts of Fe Aerated groundwater Rate of Feature Formation A 2 mm thick Fe depletion around a root channel ranged from less than 1 to greater than 100 years depending upon how long reducing conditions occurred and how much Fe was in solution each day – Recently constructed wetlands should have redox depletions evident within a couple of years if wetland hydrology is present during the “growing season” Age of Features Redox features do not always indicate current hydrologic condition – commonly found in drained (historic) wetlands – can be relict of past climates relict features may have sharp edges and abrupt boundaries with the soil – relict nodules and concretions are often rounded – contemporary features should have diffuse boundaries and / or be associated with ped faces or root channels REVIEW •1 We describe color using Munsell Notation to accurately convey what we see to someone else. •2 “Good” viewing conditions are critical to accurate reading of a color. •3 If the sun is low colors are redder. •4 Cloudy days make it difficult to read low chroma colors. •5 Color is a critical characteristic when working with redoximorphic features •6 The location of color within the “soil fabric” can separate relict features from current conditions; the age of color. •7 Observable soil colors, accurately described, leads to critical inferred characteristics. Soil Texture proportion by weight of sand, silt, and clay estimated in the field or measured in the laboratory placed into a texture class NOTE: – soil texture is only the fine-earth fraction (< 2mm) – particle size distribution is fine-earth plus rock fragments (>2mm) Particle Sizes Sand – 2 mm to 0.05 mm – very coarse sand – 1 to 2 mm – coarse sand – 0.5 to 1 mm – medium sand – 0.25 to 0.5 mm – fine sand – 0.10 to 0.25 mm – very fine sand – 0.05 to 0.10 mm Silt – 0.05 to 0.002 mm Clay -- < 0.002 mm (<2m) Relative Sizes of Particles beachball frisbee dime Silt Clay (feels floury) (feels sticky) (< 0.002 mm) (0.05 - 0.002 mm) Sand (feels gritty) (2.00 - 0.05 mm) Texture Classes Class Abbrev. Class Abbrev. very coarse sand VCOS fine sandy loam FSL coarse sand COS very fine sandy loam VFSL sand S loam L fine sand FS silt loam SIL very fine sand VFS silt SI loamy coarse sand LCOS sandy clay loam SCL loamy sand LS clay loam CL loamy fine sand LFS silty clay loam SICL loamy very fine sand LVFS sandy clay SC coarse sandy loam COSL silty clay SIC sandy loam SL clay C Texture 12 texture classes Triangle Texture Flowchart Rock Fragments -- Sizes SPHERICAL OR CUBELIKE – gravel (2 – 75 mm diameter) GRAVELLY – cobbles (75 – 250 mm diameter) COBBLY – stones (250 – 600 mm diameter) STONY – boulders (> 600 mm diameter) BOULDERY FLAT – channers (2 – 150 mm long) CHANNERY – flagstones (150 – 380 mm long) FLAGGY – stones (380 – 600 mm long) STONY – boulders (> 600 mm long) BOULDERY Rock Fragments -- Roundness Texture Modifiers Fragment
Recommended publications
  • Soils Section
    Soils Section 2003 Florida Envirothon Study Sections Soil Key Points SOIL KEY POINTS • Recognize soil as an important dynamic resource. • Describe basic soil properties and soil formation factors. • Understand soil drainage classes and know how wetlands are defined. • Determine basic soil properties and limitations, such as mottling and permeability by observing a soil pit or soil profile. • Identify types of soil erosion and discuss methods for reducing erosion. • Use soil information, including a soil survey, in land use planning discussions. • Discuss how soil is a factor in, or is impacted by, nonpoint and point source pollution. Florida’s State Soil Florida has the largest total acreage of sandy, siliceous, hyperthermic Aeric Haplaquods in the nation. This is commonly called Myakka fine sand. It does not occur anywhere else in the United States. There are more than 1.5 million acres of Myakka fine sand in Florida. On May 22, 1989, Governor Bob Martinez signed Senate Bill 525 into law making Myakka fine sand Florida’s official state soil. iii Florida Envirothon Study Packet — Soils Section iv Contents CONTENTS INTRODUCTION .........................................................................................................................1 WHAT IS SOIL AND HOW IS SOIL FORMED? .....................................................................3 SOIL CHARACTERISTICS..........................................................................................................7 Texture......................................................................................................................................7
    [Show full text]
  • 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.
    [Show full text]
  • 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
    [Show full text]
  • Sustaining the Pedosphere: Establishing a Framework for Management, Utilzation and Restoration of Soils in Cultured Systems
    Sustaining the Pedosphere: Establishing A Framework for Management, Utilzation and Restoration of Soils in Cultured Systems Eugene F. Kelly Colorado State University Outline •Introduction - Its our Problems – Life in the Fastlane - Ecological Nexus of Food-Water-Energy - Defining the Pedosphere •Framework for Management, Utilization & Restoration - Pedology and Critical Zone Science - Pedology Research Establishing the Range & Variability in Soils - Models for assessing human dimensions in ecosystems •Studies of Regional Importance Systems Approach - System Models for Agricultural Research - Soil Water - The Master Variable - Water Quality, Soil Management and Conservation Strategies •Concluding Remarks and Questions Living in a Sustainable Age or Life in the Fast Lane What do we know ? • There are key drivers across the planet that are forcing us to think and live differently. • The drivers are influencing our supplies of food, energy and water. • Science has helped us identify these drivers and our challenge is to come up with solutions Change has been most rapid over the last 50 years ! • In last 50 years we doubled population • World economy saw 7x increase • Food consumption increased 3x • Water consumption increased 3x • Fuel utilization increased 4x • More change over this period then all human history combined – we are at the inflection point in human history. • Planetary scale resources going away What are the major changes that we might be able to adjust ? • Land Use Change - the world is smaller • Food footprint is larger (40% of land used for Agriculture) • Water Use – 70% for food • Running out of atmosphere – used as as disposal for fossil fuels and other contaminants The Perfect Storm Increased Demand 50% by 2030 Energy Climate Change Demand up Demand up 50% by 2030 30% by 2030 Food Water 2D View of Pedosphere Hierarchal scales involving soil solid-phase components that combine to form horizons, profiles, local and regional landscapes, and the global pedosphere.
    [Show full text]
  • Soil Properties Database of Spanish Soils. Volumen
    65°^ e 0 6,2.1 Centro de Investigaciones Energeticas, Medioambientales y Tecnoldgicas Miner A, is /X Base de Dates de Propiedades Edafoldgicas de los Suelos Espanoles. VolumenXI. CASTHIA-LEON(b): Palentia, Valladolid y Avila C. Trueba RMillan T. Schmid received C. Lago JUL 121999 C. Roquero M. Magister OSTl MormesTecnicosCiemat 898 julio,1999 1. -a;:' ' > DISCLAIMER Portions of this document may be illegible in electronic image products. Images are produced from the best available original document. Informes T ecnicos Ciemat 898 julio, 1999 Base de Dates dePropiedades Edafologicas de los Suelos Espanoles. VohnnenXL CASHLLA-LEON(b): Palencia, Valladolid y Avila C. Trueba (*) R. Millan(*) T. Schmid (*) C. Lago (*) C. Roquero (**) M.Magister (**) (*) CIEMAT (**)UPM Departamento de Impacto Ambiental de la Energia Toda correspondenica en relation con este trabajo debe dirigirse al Servicio de Information y Documentation, Centro de Investigaciones Energeticas, Medioambientales y Tecnoldgicas, Ciudad Universitaria, 28040-MADRID, ESPANA. Las solicitudes de ejemplares deben dirigirse a este mismo Servicio. Los descriptores se ban seleccionado del Thesauro del DOE para describir las materias que contiene este informe con vistas a su recuperation. La catalogacidn se ha hecho utilizando el documento DOE/TIC-4602 (Rev. 1) Descriptive Cataloguing On-Line, y la clasificacion de acuerdo con el documento DOE/TIC.4584-R7 Subject Categories and Scope publicados por el Office of Scientific and Technical Information del Departamento de Energia de los Estdos Unidos. Se autoriza la reproduction de los resumenes analiticos que aparecen en esta publication. Deposito Legal: M -14226-1995 ISSN: 1135-9420 NIRO: 238-99-003-5 Editorial CIEMAT CLASIFICACION DOE Y DESCRIPTORES 540230 SOILS; SOIL CHEMISTRY; SOIL MECHANICS; RADIONUCLIDE MIGRATION; DATA BASE MANAGEMENT; DATA COMPILATION; SPAIN; “Base de Dates de Propiedades Edafologicas de los Suelos Espanoles.
    [Show full text]
  • Adsorption and Availability of Phosphorus in Response to Humic Acid Rates in Soils Limed with Caco3 OR Mgco3 9
    Ciência e Agrotecnologia, 42(1):7-20, Jan/Feb. 2018 http://dx.doi.org/10.1590/1413-70542018421014518 Adsorption and availability of phosphorus in response to humic acid rates in soils limed with CaCO3 or MgCO3 Adsorção e disponibilidade de fósforo em resposta a doses de ácido húmico em solos corrigidos por CaCO3 ou MgCO3 Henrique José Guimarães Moreira Maluf1*, Carlos Alberto Silva1, Nilton Curi1, Lloyd Darrell Norton2, Sara Dantas Rosa1 1Universidade Federal de Lavras/UFLA, Departamento de Ciência do Solo/DCS, Lavras, MG, Brasil 2Purdue University, Department of Agricultural and Biological Engineering, West Lafayette, Indiana, USA *Corresponding author: [email protected] Received in May 18, 2017 and approved in July 24, 2017 ABSTRACT Humic acid (HA) may reduce adsorption and increase soil P availability, however, the magnitude of this effect is different when 2+Ca prevails over Mg2+ in limed soils. The objective of this study was to evaluate the effects of HA rates and carbonate sources on the adsorption, phosphate maximum buffering capacity (PMBC), and P availability in two contrasting soils. Oxisol and Entisol samples were firstly incubated with the -1 following HA rates: 0, 20, 50, 100, 200 and 400 mg kg , combined with CaCO3 or MgCO3, to evaluate P adsorption. In sequence, soil samples were newly incubated with P (400 mg kg-1) to evaluate P availability. The least P adsorption was found when 296 mg kg-1 of HA was added to Oxisol. Applying HA rates decreased maximum adsorption capacity, increased P binding energy to soil colloids and did not alter PMBC of Entisol.
    [Show full text]
  • Meta-Analysis of the Effects of Soil Properties, Site Factors And
    Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Hydrol. Earth Syst. Sci. Discuss., 8, 10007–10052, 2011 Hydrology and www.hydrol-earth-syst-sci-discuss.net/8/10007/2011/ Earth System doi:10.5194/hessd-8-10007-2011 Sciences © Author(s) 2011. CC Attribution 3.0 License. Discussions This discussion paper is/has been under review for the journal Hydrology and Earth System Sciences (HESS). Please refer to the corresponding final paper in HESS if available. Meta-analysis of the effects of soil properties, site factors and experimental conditions on preferential solute transport J. K. Koestel, J. Moeys, and N. J. Jarvis Department of Soil and Environment, Swedish University of Agricultural Sciences (SLU), P.O. Box 7014, 750 07 Uppsala, Sweden Received: 27 October 2011 – Accepted: 28 October 2011 – Published: 15 November 2011 Correspondence to: J. K. Koestel ([email protected]) Published by Copernicus Publications on behalf of the European Geosciences Union. 10007 Discussion Paper | Discussion Paper | Discussion Paper | Discussion Paper | Abstract Preferential flow is a widespread phenomenon that is known to strongly affect solute transport in soil, but our understanding and knowledge is still poor of the site factors and soil properties that promote it. To investigate these relationships, we assembled a 5 database from the peer-reviewed literature containing information on 793 breakthrough curve experiments under steady-state flow conditions. Most of the collected experi- ments (642 of the 793 datasets) had been conducted on undisturbed soil columns, although some experiments on repacked soil, clean sands, and glass beads were also included. In addition to the apparent dispersivity, we focused attention on three poten- 10 tial indicators of preferential solute transport, namely the 5 %-arrival time, the holdback factor, and the ratio of piston-flow and average transport velocities.
    [Show full text]
  • Sugar Cane Response to Potassium Fertilization on Andisol, Entisol, and Mollisol Soils of Guatemala
    Guatemala Sugar Cane Response to Potassium Fertilization on Andisol, Entisol, and Mollisol Soils of Guatemala By Ovidio Pérez and Mario Melgar This research examines the potential for improved sugar cane yield and quality in Guatemala through increased potassium (K) use in combination with adequate nitrogen (N) and phosphorus (P) rates. A critical soil test K level for the major sugar cane-producing region of Guatemala is also suggested. Guatemala’s sugar cane region is located on its southern coastland in volcanic lowlands and coastal valleys. In the upper and middle parts of the region, high amounts of precipitation are common. Andisols and sandy soils with low K levels dominate. In contrast, the alluvial soils of the coastal valley generally have moderate levels of K. Most sugar cane growers do not consider application of K in their fer- tilization program, although K is extract- ed in large amounts by the crop. In fact, Andisols with low soil K sugar cane requires more K than N. levels are common in the Preliminary results from a regional study on N, P, and K use in sugar cane production area sugar cane showed a small but consistent crop response to K fertiliza- of Guatemala. tion on soils with low K levels (Pérez and Melgar, 1998). However, these experiments were characterized by addition of low rates of N and P. Unpublished data from local sugar cane companies have shown large Table 1. Effect of K on sugar cane yield, sugar content, application rates of N, P and K increase and juice purity. sugar production in some of these areas.
    [Show full text]
  • Engineering Values from Soil Taxonomy
    ENGINEERING VALUES FROM SOIL TAXONOMY W. R. Philipson, R. W. Arnold, and D. A. Sangrey, Cornell University Many properties of engineering interest can be deduced from the connota­ tive nomenclature of Soil Taxonomy, the pedological soil classification sys­ tem adopted for use by the National Cooperative Soil Survey in 1965. The system is based on soil properties that have been defined quantitatively and named. Each soil class name, in turn, is composed of word elements taken from the names of those properties that are diagnostic for the soil class. The major features of a soil placed within any class are signified directly by the specific formative elements appearing in the soil class name. The descriptions and formative elements of six surface horizons (epipedons ), 17 subsurface horizons, 56 special features, and the 10 soil classes at the highest level of the system (orders), are provided. Because the basis of this paper is use of Soil Taxonomy by engineers, emphasis is placed on the nomenclature rather than the structure of philosophy of the system. The 39 formative elements considered to be most informative for general engineering analysis are highlighted for handy reference. •SINCE 1965, all U.S. Department of Agriculture soil survey reports have correlated soils into the new Soil Taxonomy (11, 12), until recently referred to as the 7th Approxi­ mation (10). In contrast to the qualitative nature of the previous pedological classifi­ cation system (2, 8, 14), Soil Taxonomyprovides aquantitative framework in which to place soils of tne United States as well as many soils of the world. Authors, attempt­ ing to point out the engineering value of the previous system, have been forced to treat the general merits of pedological soil surveys (4, 5, 6) or to confine themselves to specific soil series encountered in their particular project (7, 13).
    [Show full text]
  • NRCS Introduction to Soils
    Soils Intro USDA Natural Resources Conservation Service Take an apple Have it represent the Earth Cut out and save … ¼ of the apple This much represents ldland area. Now cut that slice in half, and keep one piece. This much represents where people live. Cut that piece in quarters and keep one ¼. This represents the amount of soil where food can be grown. This is 3% (1/32) of the Earth’s surface. We Study Soil Because It’s A(n) Great integrator Snapshot of Medium of geologic, crop climatic, production biological, and human history Producer and Waste decomposer absorber of gases MdiMedium Source for plant material for growth construction, medicine, art, Home to etc. organisms (plants, animals Filter of and others) water and Essential natural resource wastes Five Soil Forming Factors Biota Parent Material Topography Climate (The first four factors over) Time Glacial Till Parent Material Sutton Series Glaciofluvial Parent Material Manchester Series Alluvium Parent Material Hadley Series Glaciolacustrine Parent Material Scitico Series Organic Parent Material Natchaug Series Disturbed Parent Material Soil Parent Material Soil Color Munsell Notation Hue VlValue Chroma Redox Concentrations Pore linings on root cha nn el and Fe mass ped surface in matrix Nodule in matrix Soft Fe/Mn Hard Fe/Mn accumulations accumulations Modules Concretions Redox Depletions B. Fe depletions along ped surfaces. A. No redox depletions. Fe(II) Clay in in Matrix Matrix C. Clay dep let ions along ped surfaces. A Soil Profile Soil Structure - With Structure Granular Blocky (Su bangu lar ) (Angu lar ) Platy Prismatic Columnar Wedge Soil Structure – Without Structure Single Grain Massive USDA Textural Triangle Landscape Factors • Depth to bedrock • Depth to water table • Flooding vs.
    [Show full text]
  • Chapter 3 Chapter 3 Learning Objectives
    Chapter 3 Learning Objectives Chapter 3 • Describe the current USDA soil classification system • List the six categories of classification in Soil Soil Taxonomy Taxonomy • Describe the major characteristics, the general degree of weathering and soil development, and the worldwide distribution and uses of the 12 soil orders • List key features of a particular soil and its environment given the soil name (e.g., Hapludalf) Diagnostic Subsurface Horizons Diagnostic Subsurface Horizons • 18 of them – Albic: light-colored elluvial horizon (leached) – Cambic: weakly developed horizon, some color • Six we will focus on (and the assoc. genetic change label): – Spodic: illuvial horizon with accumulations of O.M. – Argillic: subsurface accumulations of silicate clays – Albic (E) -Argg(illic (Bt) – CliCalcic: accumu ltilation o f car bona tes, o ften as – Cambic (Bw) - Fragic (Bx) white, chalk-like nodules – Spodic (Bhs) - Calcic (Bk) – Fragipan: cemented, dense, brittle pan Light colored horizon Albic Argillic Weakly developed horizon Cambic No significant accumulation silicate clays Unweathered Accumulation of Acid weathering, material organic matter Fe, Al oxides Spodic Calcic Fragipan Modified from full version of Figure 3.3 in textbook (page 62). 1 Levels of Description Levels of Description • Order Most general • Order – One name, all end in “-sol” There are 12. Differentiated by presence or absence of • Suborder diagnostic horizons or features that reflect • Great group soil-forming processes. EXAMPLE: ENTISOL • Subgroup • Suborder • Family • Great group • Subgroup •Series •Family Most specific •Series Levels of Description Levels of Description • Order – One name, all end in “-sol” There are 12 . • Order – One name, all end in “-sol” There are 12 .
    [Show full text]
  • Standard Characterization of Soils Employed in the Fao/Iaea Phosphate Project
    XA0201061 STANDARD CHARACTERIZATION OF SOILS EMPLOYED IN THE FAO/IAEA PHOSPHATE PROJECT D. MONTANGE CIRAD-CA GEC, Montpellier, France F. ZAPATA International Atomic Energy Agency, Vienna Abstract In the frame of the FAO/IAEA networked research project, the agronomic effectiveness of natural and modified phosphate rock (PR) products was evaluated using nuclear and related techniques under a variety of soil, climate and management conditions. In addition to the local soil analyses, it was decided to make a standard characterization of the soils employed in the project to gather direct and comparable information on the relevant soil properties affecting the suitability of PRs for direct application and to better interpret the results from the agronomic evaluation, including the creation of a database for phosphate modelling. This paper describes the standard characterization of soils, that was mainly made at CIRAD, Montpellier, France. A total of 51 soil samples were analyzed froml5 countries including Belarus (1), Brazil (2), Chile (3), China (20), Cuba (2) Ghana (6), Hungary (2), Indonesia (3), Kenya (1), Malaysia (1), Poland (1), Romania (2), Russia (1), Thailand (3) and Venezuela (3). Methods of analyses used for the soil characterization included textural class, pH, chemical analysis for total N and P, and exchangeable elements (CEC, saturation). Available P was measured using 4 methods including Olsen, Bray n, Pi paper and Resin. Available P measurements using resin method were made at CENA, Piracicaba, Brazil. The soil P dynamics was described using the 32P isotope exchange kinetic method at CEN Cadarache, France with the same soil samples. As a result of the worldwide distribution of the soils employed hi the project, the results showed a very large diversity in each of the measured soil characteristics.
    [Show full text]