Redalyc.Paleopedology of Soils in Thick Holocene Loess, Nebraska
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Morphological Characteristics and Classification of Soils Derived from Diverse Parent Materials in Central Cross River State, Nigeria
GLOBAL JOURNAL OF PURE AND APPLIED SCIENCES VOL. 14, NO. 3, 2008: 271 - 277 271 COPYRIGHT (C) BACHUDO SCIENCES CO. LTD. PRINTED IN NIGERIA. 1SSN 1118-0579 MORPHOLOGICAL CHARACTERISTICS AND CLASSIFICATION OF SOILS DERIVED FROM DIVERSE PARENT MATERIALS IN CENTRAL CROSS RIVER STATE, NIGERIA M. E. NSOR and I. J. IBANGA (Received 5 October 2007; Revision Accepted 5 December 2007) ABSTRACT Variation in soil characteristics is usually a reflection of the difference in materials from which the soil was formed. This study sought to investigate the characteristics of soils formed on different parent materials with a view to classifying them. This study was carried out in selected soils derived from three major types of parent materials in central Cross River State, South Eastern Nigeria. A total of six (6) pedons were excavated, two (2) pedons in each of the identified parent materials. The parent materials were Sandstone-shale-siltstone intercalations. Basement complex and Basalt. The study indicated that soils derived from sandstone-shale-siltstone materials are characterized by ochric sandy loam and loamy sand epipedons with moderate medium sub-angular blocky structures. These soils are also light coloured with dominant hues of 7.5YR with hard to slightly hard and hard to very hard dry consistence at the surface and sub-soil respectively. Soils of basement complex are characterized by the possession of loamy sand epipedons with weak medium crumb and sub-angular blocky structures having predominantly dull yellowish brown and bright yellowish brown colours at the surface and sub-soils. The dry consistences of the surface soils are slightly hard while the sub-soils are hard to very hard. -
Keynote: Soil Conservation for C Sequestration R
This paper was not peer-reviewed. Pages 459-465. In: D.E. Stott, R.H. Mohtar and G.C. Steinhardt (eds). 2001. Sustaining the Global Farm. Selected papers from the 10th International Soil Conservation Organization Meeting held May 24-29, 1999 at Purdue University and the USDA-ARS National Soil Erosion Research Laboratory. Keynote: Soil Conservation For C Sequestration R. Lal* ABSTRACT fragile ecosystems such as the Himalyan-Tibean ecoregion, The atmospheric concentration of greenhouse gases the Andeas, the West African Sahel, East African Highlands, (GHG) is increasing at the rate of 0.5% yr-1 (3.2 Pg C and the Caribbean region (Scherr and Yadav, 1995; Scherr, -1 -1 -1 yr ) for CO2, 0.6% yr for CH4 and 0.25 ppbv yr for 1999). In addition to effects on productivity, soil erosion N2O. The global radiative forcing due to three GHGs is also profoundly impacts the environment. contributed by 20% due to agricultural activities and Two principal impacts of erosion on environment include 14% to change in land use and attendant deforestation. reduction in quality of water and air through pollution and Principal agricultural activities that contribute to eutrophication of surface water, and emissions of emission of GHGs include plowing, application of radioactively-active gases (e.g., CO2, CH4 and N2O) to the fertilizers and manures, soil drainage, biomass burning, atmosphere. Increasing atmospheric concentration of -1 -1 residue removal. The loss of soil C is accentuated by soil radioactively-active gases (0.5% yr for CO2, 0.6% yr for -1 degradation (due to erosion, compaction, salinization CH4, 0.25% yr for N2O) (IPCC, 1995) necessitates etc.) and the attendant decline in soil quality. -
Sborník Příspěvků Z Konference Pedologické Dny, Velké Bílovice, 2003
PEDOGENEZE A KVALITATIVNÍ ZMĚNY PŮD V PODMÍNKÁCH PŘÍRODNÍCH A ANTROPICKY OVLIVNĚNÝCH ÚZEMÍ Bořivoj ŠARAPATKA a Marek BEDNÁŘ (Eds.) Sborník referátů z 11. pedologických dnů KOUTY NAD DESNOU, 20.–21. 9. 2006 Editoři © Bořivoj Šarapatka, Marek Bednář, 2006 1. vydání Olomouc 2006 ISBN 80-244-1448-1 2 ÚVOD Vážené kolegyně a kolegové, letošní již 11. pedologické dny jsme zasadili do horské oblasti mikro - regionu Jeseníky. Území, ve kterém strávíme dva jistě pěkné a přínosné dny, je velmi cenné přírodovědně. Na rozloze 740 km2 se zde nachází chráněná krajinná oblast Jeseníky. Na různorodém geologickém podloží se vyvinula unikátní společenstva rostlin a živočichů, která byla začleně- na do reprezentativní sítě zvláště chráněných území. Snad nejvýznamněj- ším maloplošným chráněným územím je známá NPR Praděd s takovým přírodním fenoménem, jakým je ledovcový kar Velké kotliny, který náleží botanicky k druhově nejbohatším lokalitám ve střední Evropě. Zájmové území mikroregionu není významné pouze z přírodo- vědného hlediska. Je i intenzivně zemědělsky a lesnicky obhospodařová- no. Od středověkého osídlení postupně docházelo k trvalému odlesňo- vání a zemědělskému využití území, vyšší polohy regionu zůstávaly bez trvalých sídel. Dnes na zemědělské půdě v oblasti dominují trvalé travní porosty. Nebylo tomu ale tak vždy, o čemž svědčí nejen hospodaření po druhé světové válce, ale i starší údaje např. z 19. století. Tehdy v jesenické oblasti tvořila orná půda více než 70 % z celkové půdy zemědělské (na- příklad v Loučné to bylo v roce 1900 74,8 %). O využití krajiny jak z pohledu zemědělského, tak lesnického bude pojednávat řada konferenčních příspěvků. Většinou budou prezentovat široký záběr týkající se nových poznatků o pedogenezi a kvalitativních změnách půd, a to jak v podmínkách přírodních, tak antropicky ovliv- něných území. -
Contaminated Soil in Gardens
Contaminated Soil in Gardens How to avoid the harmful effects EUR/ICP/LVNG 03 01 02(A) E64737 EUROPEAN HEALTH21 TARGET 11 HEALTHIER LIVING By the year 2015, people across society should have adopted healthier patterns of living (Adopted by the WHO Regional Committee for Europe at its forty-eighth session, Copenhagen, September 1998) Abstract In many cities, gardens are located on old, abandoned landfills and dumping sites. Cities have expanded by filling up spaces around the city with garbage, rubble and earth. The places where old landfills were have often become gardens where citizens can get away and enjoy the open air away from the noise and racket of cities. Normal garbage and rubble in landfills do not present a problem, however industrial and chemical waste can present a health hazard, especially when concentrations of contaminants are above acceptable limits. Some special precautions are proposed in this booklet so that the potential ill effects of contaminated soil can be avoided. Keywords SOIL POLLUTANTS RISK MANAGEMENT GUIDELINES URBAN HEALTH Contents The soil is contaminated – what then? .......................................................1 What is in the ground under us?.................................................................2 How harmful substances may affect the body ............................................3 How to reduce the risk................................................................................4 The best way to garden..............................................................................5 -
The Retention of Organic Matter in Soils
Biogeochemistry 5: 35-70 (1988) © Martinus Nijhoff/Dr W. Junk Publishers, Dordrecht Printed in the Netherlands The retention of organic matter in soils J.M. OADES Department of Soil Science, Waite Agricultural Research Institute, The University of Adelaide, Glen Osmond, South Australia 5064 Key words: organic matter, turnover, organomineral interactions, clay, base status, cation bridges, oxide surfaces Abstract. The turnover of C in soils is controlled mainly by water regimes and temperature, but is modified by factors such as size and physicochemical properties of C additions in litter or root systems, distribution of C throughout the soil as root systems, or addition as litter, distribution of C within the soil matrix and its interaction with clay surfaces. Soil factors which retard mineralization of C in soils are identified from correlations of C contents of soils with other properties such as clay content and base status. The rate and extent of C mineralization depends on the chemistry of the added organic matter and interaction with clays of the microbial biomass and metabolites. The organomineral interactions are shown to depend on cation bridges involving mainly Ca in neutral to alkaline soils, Al in acid soils and adsorption of organic materials on iron oxide surfaces. The various organomineral interactions lead to aggregations of clay particles and organic materials, which stabilizes both soil structure and the carbon compounds within the aggregates. Introduction Soils represent a major pool (172 x 10'°t) in the cycling of C from the atmosphere to the biosphere and are the habitat for terrestrial photosynthet- ic organisms which fix some 11 x 1 0"°tCy-1, about one half of which eventually finds it way into soils. -
Agricultural Soil Compaction: Causes and Management
October 2010 Agdex 510-1 Agricultural Soil Compaction: Causes and Management oil compaction can be a serious and unnecessary soil aggregates, which has a negative affect on soil S form of soil degradation that can result in increased aggregate structure. soil erosion and decreased crop production. Soil compaction can have a number of negative effects on Compaction of soil is the compression of soil particles into soil quality and crop production including the following: a smaller volume, which reduces the size of pore space available for air and water. Most soils are composed of • causes soil pore spaces to become smaller about 50 per cent solids (sand, silt, clay and organic • reduces water infiltration rate into soil matter) and about 50 per cent pore spaces. • decreases the rate that water will penetrate into the soil root zone and subsoil • increases the potential for surface Compaction concerns water ponding, water runoff, surface soil waterlogging and soil erosion Soil compaction can impair water Soil compaction infiltration into soil, crop emergence, • reduces the ability of a soil to hold root penetration and crop nutrient and can be a serious water and air, which are necessary for water uptake, all of which result in form of soil plant root growth and function depressed crop yield. • reduces crop emergence as a result of soil crusting Human-induced compaction of degradation. • impedes root growth and limits the agricultural soil can be the result of using volume of soil explored by roots tillage equipment during soil cultivation or result from the heavy weight of field equipment. • limits soil exploration by roots and Compacted soils can also be the result of natural soil- decreases the ability of crops to take up nutrients and forming processes. -
Biomechanical and Biochemical Effects Recorded in the Tree Root Zone – Soil Memory, Historical Contingency and Soil Evolution Under Trees
Plant Soil (2018) 426:109–134 https://doi.org/10.1007/s11104-018-3622-9 REGULAR ARTICLE Biomechanical and biochemical effects recorded in the tree root zone – soil memory, historical contingency and soil evolution under trees Łukasz Pawlik & Pavel Šamonil Received: 17 September 2017 /Accepted: 1 March 2018 /Published online: 15 March 2018 # The Author(s) 2018 Abstract increase in soil spatial complexity. We hypothesized that Background and aims The changing soils is a never- trees can be a strong local factor intensifying, blocking ending process moderated by numerous biotic and abi- or modifying pedogenetic processes, leading to local otic factors. Among these factors, trees may play a changes in soil complexity (convergence, divergence, critical role in forested landscapes by having a large or polygenesis). These changes are hypothetically con- imprint on soil texture and chemical properties. During trolled by regionally predominating soil formation their evolution, soils can follow convergent or divergent processes. development pathways, leading to a decrease or an Methods To test the main hypothesis, we described the pedomorphological features of soils under tree stumps of fir, beech and hemlock in three soil regions: Haplic Highlights Cambisols (Turbacz Reserve, Poland), Entic Podzols 1) The architecture of tree root systems controls soil physical and (Žofínský Prales Reserve, Czech Republic) and Albic chemical properties. Podzols (Upper Peninsula, Michigan, USA). Soil pro- 2) The predominating pedogenetic process significantly modifies files under the stumps, as well as control profiles on sites the effect of trees on soil. 3) Trees are a factor in polygenesis in Haplic Cambisols at the currently not occupied by trees, were analyzed in the pedon scale. -
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. -
Topsoil Characterization for Sustainable Land Management 1
DRAFT FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS TOPSOIL CHARACTERIZATION FOR SUSTAINABLE LAND MANAGEMENT Land and Water Development Division Soil Resources, Management and Conservation Service Rome 1998 2 ACKNOWLEDGEMENTS This study is based upon earlier work by O.C. Spaargaren "Framework for Characterization and Classification of Topsoils in the World" (1992 unpublished) and A. Hebel "Soil Characterization and Evaluation System (SCE) with Emphasis on Topsoils and their Fertility-related Characteristics" (1994 unpublished). We would also like to acknowledge the cooperation of the University of Hohenheim, especially Dr. Gaiser and Prof. Stahr for testing the system, and various contributions, suggestions and constructive criticism received from Ms L.M. Jansen, Ms A Bot, Mr F. Nachtergaele, and last but not least, Mr M.F. Purnell. CONTENTS 1. Introduction 1 2. Topsoil Characterization Within Existing Soil Classification Systems 3 2.1 Introduction 3 2.2 Fertility Capability Classification (FCC) 3 2.3 Soil Classification Systems 3 3. Factors Influencing Topsoil Properties 7 3.1 Climate 7 3.2 Vegetation and Organic Matter 7 3.3 Topography and Physiography 8 3.4 Mineralogical Soil Constituents 9 3.5 Surface Processes 9 3.6 Biological Activity 10 3.7 Human Activity 10 4. Definition of Topsoil Properties and Modifiers 13 4.1 Texture 13 4.2 Organic Material 13 4.3 Organic Matter Status 14 4.4 Physical Features 16 4.5 Chemical Features 18 4.6 Biological Features 20 4.7 Drainage Features 21 4.8 Land Use 21 4.9 Erosion or Degradation 23 4.10 External Physical Conditions 25 4.11 Slope 26 4.12 Examples of Topsoil Characterization 26 5. -
2021 Soils/Land Use Study Resources
2021 NCF Envirothon Soil Test Study Guide Lincoln, Nebraska 2021 NCF-Envirothon Nebraska Soils and Land Use Study Resources Key Topic #1: Physical Properties of Soil and Soil Formation 1. Describe the five soil forming factors, and how they influence soil properties. 2. Explain the defining characteristics of a soil describing how the basic soil forming processes influence affect these characteristics in different types of soil. 3. Identify different types of parent material, their origins, and how they impact the soil that develops from them. 4. Identify and describe soil characteristics (horizon, texture, structure, color). 5. Identify and understand physical features of soil profiles and be able to use this information interpret soil properties and limitations. Study Resources Sample Soil Description Scorecard – University of Nebraska – Lincoln Land Judging Documents, edited by Judy Turk, 2021 (Pages 3-4) Soil Description Field Manual Reference – University of Nebraska – Lincoln Land Judging Documents, edited by Judy Turk, 2021 (Pages 5-17) Correlation of Field Texturing Soils by Feel, Understanding Soil Laboratory Data, and Use of the Soil Textural Triangle – Patrick Cowsert, 2021 (Pages 18-21) Tips for Measuring Percent Slope on Contour Maps – Excerpt from Forest Measurements by Joan DeYoung, 2018 (Pages 22-23) Glossary – Excerpts from Geomorphic Description System version 5.0, 2017, and Field Book for Describing Soils version 3.0, 2012 (Pages 24-27) Study Resources begin on the next page! Contestant Number Sample Soil Description Card Site/Pit Number Host: University of Nebraska – Lincoln Number of Horizons Lower Profile Depth 2021 –Scorecard Nail Depth A. Soil Morphology Part A Score __________ Moist Horizons Boundary Texture Color Redox. -
Effects of Climatic Change on Soil Hydraulic Properties During
water Article Effects of Climatic Change on Soil Hydraulic Properties during the Last Interglacial Period: Two Case Studies of the Southern Chinese Loess Plateau Tieniu Wu 1,2 , Henry Lin 2, Hailin Zhang 1,*, Fei Ye 1, Yongwu Wang 1, Muxing Liu 1, Jun Yi 1 and Pei Tian 1 1 Key Laboratory for Geographical Process Analysis & Simulation, Hubei Province, Central China Normal University, Wuhan 430079, China; [email protected] (T.W.); [email protected] (F.Y.); [email protected] (Y.W.); [email protected] (M.L.); [email protected] (J.Y.); [email protected] (P.T.) 2 Department of Ecosystem Science and Management, The Pennsylvania State University, University Park, PA 16802, USA; [email protected] * Correspondence: [email protected]; Tel.: +86-27-6786-7503 Received: 16 January 2020; Accepted: 10 February 2020; Published: 12 February 2020 Abstract: The hydraulic properties of paleosols on the Chinese Loess Plateau (CLP) are closely related to agricultural production and are indicative of the environmental evolution during geological and pedogenic periods. In this study, two typical intact sequences of the first paleosol layer (S1) on the southern CLP were selected, and soil hydraulic parameters together with basic physical and chemical properties were investigated to reveal the response of soil hydraulic properties to the warm and wet climate conditions. The results show that: (1) the paleoclimate in the southern CLP during the last interglacial period showed a pattern of three warm and -
This Work Is Protected by Copyright And
This work is protected by copyright and other intellectual property rights and duplication or sale of all or part is not permitted, except that material may be duplicated by you for research, private study, criticism/review or educational purposes. Electronic or print copies are for your own personal, non- commercial use and shall not be passed to any other individual. No quotation may be published without proper acknowledgement. For any other use, or to quote extensively from the work, permission must be obtained from the copyright holder/s. THE SEDIMENTOLOGY AND STRATIGRAPHY OF RED BEDS IN THE WESTPHALIAN A TO C OF CENTRAL ENGLAND Thesis submitted to the University of Keele for the degree of Ph.D. by Bernard Maurice Besly B.A. 1983 M7S308 Abstract Red beds in the Westphalian A to C of Central England belong to the Etruria Formation. Examination of exposures and cores has allowed subdivision of this Formation into three Facies Associations. Facies Association I forms the gradational base of the red bed sequence. The sediments resemble the underlying Productive Coal Measures, consisting dominantly of grey organic-rich mudstones. Much of this Association is formed by seat-earth palaeosols, which occasionally contain red pigment. Facies Association II forms most of the Etruria Formation, and consists largely of dark red mudstone. Throughout there are mottled horizons which are interpreted as lateritic palaeosols. Occasional upward-fining sand bodies containing lateral accretion surfaces are present. Facies Associations I and II are interpreted as fluvial deposits. The rivers were dominated by suspended load and deposited thick overbank sequences. In Association I the overbank areas were swampy, while in Association II good drainage prevailed.