Soil Compaction and Pasture Performance
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Topic: Soil Classification
Programme: M.Sc.(Environmental Science) Course: Soil Science Semester: IV Code: MSESC4007E04 Topic: Soil Classification Prof. Umesh Kumar Singh Department of Environmental Science School of Earth, Environmental and Biological Sciences Central University of South Bihar, Gaya Note: These materials are only for classroom teaching purpose at Central University of South Bihar. All the data/figures/materials are taken from several research articles/e-books/text books including Wikipedia and other online resources. 1 • Pedology: The origin of the soil , its classification, and its description are examined in pedology (pedon-soil or earth in greek). Pedology is the study of the soil as a natural body and does not focus primarily on the soil’s immediate practical use. A pedologist studies, examines, and classifies soils as they occur in their natural environment. • Edaphology (concerned with the influence of soils on living things, particularly plants ) is the study of soil from the stand point of higher plants. Edaphologist considers the various properties of soil in relation to plant production. • Soil Profile: specific series of layers of soil called soil horizons from soil surface down to the unaltered parent material. 2 • By area Soil – can be small or few hectares. • Smallest representative unit – k.a. Pedon • Polypedon • Bordered by its side by the vertical section of soil …the soil profile. • Soil profile – characterize the pedon. So it defines the soil. • Horizon tell- soil properties- colour, texture, structure, permeability, drainage, bio-activity etc. • 6 groups of horizons k.a. master horizons. O,A,E,B,C &R. 3 Soil Sampling and Mapping Units 4 Typical soil profile 5 O • OM deposits (decomposed, partially decomposed) • Lie above mineral horizon • Histic epipedon (Histos Gr. -
Basic Soil Science W
Basic Soil Science W. Lee Daniels See http://pubs.ext.vt.edu/430/430-350/430-350_pdf.pdf for more information on basic soils! [email protected]; 540-231-7175 http://www.cses.vt.edu/revegetation/ Well weathered A Horizon -- Topsoil (red, clayey) soil from the Piedmont of Virginia. This soil has formed from B Horizon - Subsoil long term weathering of granite into soil like materials. C Horizon (deeper) Native Forest Soil Leaf litter and roots (> 5 T/Ac/year are “bio- processed” to form humus, which is the dark black material seen in this topsoil layer. In the process, nutrients and energy are released to plant uptake and the higher food chain. These are the “natural soil cycles” that we attempt to manage today. Soil Profiles Soil profiles are two-dimensional slices or exposures of soils like we can view from a road cut or a soil pit. Soil profiles reveal soil horizons, which are fundamental genetic layers, weathered into underlying parent materials, in response to leaching and organic matter decomposition. Fig. 1.12 -- Soils develop horizons due to the combined process of (1) organic matter deposition and decomposition and (2) illuviation of clays, oxides and other mobile compounds downward with the wetting front. In moist environments (e.g. Virginia) free salts (Cl and SO4 ) are leached completely out of the profile, but they accumulate in desert soils. Master Horizons O A • O horizon E • A horizon • E horizon B • B horizon • C horizon C • R horizon R Master Horizons • O horizon o predominantly organic matter (litter and humus) • A horizon o organic carbon accumulation, some removal of clay • E horizon o zone of maximum removal (loss of OC, Fe, Mn, Al, clay…) • B horizon o forms below O, A, and E horizons o zone of maximum accumulation (clay, Fe, Al, CaC03, salts…) o most developed part of subsoil (structure, texture, color) o < 50% rock structure or thin bedding from water deposition Master Horizons • C horizon o little or no pedogenic alteration o unconsolidated parent material or soft bedrock o < 50% soil structure • R horizon o hard, continuous bedrock A vs. -
National University of Engineering Ge111
NATIONAL UNIVERSITY OF ENGINEERING COLLEGE OF ENVIRONMENTAL ENGINEERING ENVIRONMENTAL ENGINEERING PROGRAM GE111 – EDAPHOLOGY I. GENERAL INFORMATION CODE : GE111 – Edaphology SEMESTER : 5 CREDITS : 03 HOURS PER WEEK : 04 (Theory – Practices – Laboratory) PREREQUISITES : GE102 – Geography CONDITION : Mandatory II. COURSE DESCRIPTION Concept and importance of edaphological soil and its interest for Engineering. Detailed knowledge of the components, physical and chemical properties, genesis, classification and principles of cartography, of natural soils and anthropogenic urban soils. Principle of soil evaluation, as a starting point in studies of environmental planning, territorial planning and environmental impact assessment. Finally, it is intended that students understand the importance of soil as a non-renewable resource and the degradations to which its inappropriate use leads; It is also intended to train in the corrective and rehabilitating measures of degraded soils. III. COURSE OUTCOMES At the end of the course the student will: Organizes data for proper analysis and interpretation and calculations (soil densities, physical chemical and biological properties). Explains and determines the genesis of the soil, the physical properties of the soil, geo reference, physiographic units. Understand and apply densities, to determine the consistency of the soil, the probability of resistance in an earthquake. Interpret and perform types of soil sampling to take to the laboratory to determine their physical, chemical, and biological characteristics. Build models to determine the degree of contamination, is determined by the parameters, using the LMOs, ECAs, In soils. IV. LEARNING UNITS 1. SOIL GENESIS / 4 HOURS Objective of soil science: Interest in Engineering. Genesis. Pedological and edaphological approach. Factors of soil formation. Climate action. Properties of the soil affected by the climate. -
Soil Acidification
viti-notes [grapevine nutrition] Soil acidifi cation Viti-note Summary: Characteristics of acidic soils • Soil pH Calcium and magnesium are displaced • Soil acidifi cation in by aluminium (Al3+) and hydrogen (H+) vineyards and are leached out of the soil. Acidic soils below pH 6 often have reduced • Characteristics of acidic populations of micro-organisms. As soils microbial activity decreases, nitrogen • Acidifying fertilisers availability to plants also decreases. • Effect of soil pH on Sulfur availability to plants also depends rate of breakdown of on microbial activity so in acidic soils, ammonium to nitrate where microbial activity is reduced, Figure 1. Effect of soil pH on availability of minerals sulfur can become unavailable. (Sulfur • Management of defi ciency is not usually a problem for acidifi cation Soil pH vineyards as adequate sulfur can usually • Correction of soil pH All plants and soil micro-organisms have be accessed from sulfur applied as foliar with lime preferences for soil within certain pH fungicides). ranges, usually neutral to moderately • Strategies for mature • Phosphorus availability is reduced at acid or alkaline. Soil pH most suitable vines low pH because it forms insoluble for grapevines is between 5.5 and 8.5. phosphate compounds with In this range, roots can acquire nutrients aluminium, iron and manganese. from the soil and grow to their potential. As soils become more acid or alkaline, • Molybdenum is seldom defi cient in grapevines become less productive. It is neutral to alkaline soils but can form important to understand the impacts of insoluble compounds in acid soils. soil pH in managing grapevine nutrition, • In strongly acidic soil (pH <5), because the mobility and availability of aluminium may become freely nutrients is infl uenced by pH (Figure 1). -
Dynamics of Carbon 14 in Soils: a Review C
Radioprotection, Suppl. 1, vol. 40 (2005) S465-S470 © EDP Sciences, 2005 DOI: 10.1051/radiopro:2005s1-068 Dynamics of Carbon 14 in soils: A review C. Tamponnet Institute of Radioprotection and Nuclear Safety, DEI/SECRE, CADARACHE, BP. 1, 13108 Saint-Paul-lez-Durance Cedex, France, e-mail: [email protected] Abstract. In terrestrial ecosystems, soil is the main interface between atmosphere, hydrosphere, lithosphere and biosphere. Its interactions with carbon cycle are primordial. Information about carbon 14 dynamics in soils is quite dispersed and an up-to-date status is therefore presented in this paper. Carbon 14 dynamics in soils are governed by physical processes (soil structure, soil aggregation, soil erosion) chemical processes (sequestration by soil components either mineral or organic), and soil biological processes (soil microbes, soil fauna, soil biochemistry). The relative importance of such processes varied remarkably among the various biomes (tropical forest, temperate forest, boreal forest, tropical savannah, temperate pastures, deserts, tundra, marshlands, agro ecosystems) encountered in the terrestrial ecosphere. Moreover, application for a simplified modelling of carbon 14 dynamics in soils is proposed. 1. INTRODUCTION The importance of carbon 14 of anthropic origin in the environment has been quite early a matter of concern for the authorities [1]. When the behaviour of carbon 14 in the environment is to be modelled, it is an absolute necessity to understand the biogeochemical cycles of carbon. One can distinguish indeed, a global cycle of carbon from different local cycles. As far as the biosphere is concerned, pedosphere is considered as a primordial exchange zone. Pedosphere, which will be named from now on as soils, is mainly located at the interface between atmosphere and lithosphere. -
Soil Acidification
Soil Acidification and Pesticide Management pH 5.1 November 14, 2018 MSU Pesticide Education Program pH 3.8 Image courtesy Rick Engel Clain Jones [email protected] 406-994-6076 MSU Soil Fertility Extension What happened here? Image by Sherrilyn Phelps, Sask Pulse Growers Objectives Specifically, I will: 1. Show prevalence of acidification in Montana (similar issue in WA, OR, ID, ND, SD, CO, SK and AB) 2. Review acidification’s cause and contributing factors 3. Show low soil pH impact on crops 4. Explain how this relates to efficacy and persistence of pesticides (specifically herbicides) 5. Discuss steps to prevent or minimize acidification Prevalence: MT counties with at least one field with pH < 5.5 Symbol is not on location of field(s) 40% of 20 random locations in Chouteau County have pH < 5.5. Natural reasons for low soil pH . Soils with low buffering capacity (low soil organic matter, coarse texture, granitic rather than calcareous) . Historical forest vegetation soils < pH than historical grassland . Regions with high precipitation • leaching of nitrate and base cations • higher yields, receive more N fertilizer • often can support continuous cropping and N each yr Agronomic reasons for low soil pH • Nitrification of ammonium-based N fertilizer above plant needs - + ammonium or urea fertilizer + air + H2O→ nitrate (NO3 ) + acid (H ) • Nitrate leaching – less nitrate uptake, less root release of basic - - anions (OH and HCO3 ) to maintain charge balance • Crop residue removal of Ca, Mg, K (‘base’ cations) • No-till concentrates acidity where N fertilizer applied • Legumes acidify their rooting zone through N-fixation. Perennial legumes (e.g., alfalfa) more than annuals (e.g., pea), but much less than fertilization of wheat. -
Demonstration of Physical Separation/Leaching Methods for the Remediation of Heavy Metals Contaminated Soils at Small Arms Ranges
84 4 0 ,;*v , DEMONSTRATION OF PHYSICAL ftsJS1:3«*s SEPARATION/LEACHING METHODS FOR THE REMEDIATION OF HEAVY waBHi METALS CONTAMINATED SOILS AT SMALL ARMS RANGES m &r<&S?GtXl WBTMBUTION BTATEMEHTT Approved for pntfelie r*l«u«*f Dürtrlbattoa UnHmtaKl M£3 SEPTEMBER 1997 19980M 177 flTIC QUALITY DTS^EOTED S This Document Contains Missing Page/s That Are Unavailable In The Original Document AEC Form <t5, 1 Feb 93 replaces THAMA Form <t5 which is obsolete. Form Approved REPORT DOCUMENTATION PAGE OMB No. 0704-0188 Public reporting burden for this collection of information is estimated to average 1 hour per response, including the time for reviewing instructions, searching existing data sources, gathering and maintaining the data needed, and completing and reviewing the collection of information. Send comments regarding this burden estimate or any other aspect of this collection of information, including suggestions for reducing this burden, to Weshington Headquarters Services, Directorate for Information Operations and Reports, 1215 Jefferson Davis Highway, Suite 1204, Arlington, VA 22202-4302, and to the Office of Management and Budget, Paperwork Reduction Project (0704-0188), Washington, DC 20503. 1. AGENCY USE ONLY (Leave blank) REPORT DATE 3. REPORT TYPE AND DATES COVERED September 1997 Technology Demonstration, Nov 1995-Sep 1997 4. TITLE AND SUBTITLE 5. FUNDING NUMBERS Demonstration of Physical Separation/Leaching Methods for the Remediation of Heavy Metals Contaminated Soils at Small Arms Ranges 6. AUTHOR(S) BDM Engineering Services Company 7. PERFORMING ORGANIZATION NAME(S) AND ADDRESS(ES) 8. PERFORMING ORGANIZATION BDM Engineering Services Company REPORT NUMBER 1801 Randolph Road, S.E. -
Behavior of Pesticides in Soils and Water 1
Archival copy: for current recommendations see http://edis.ifas.ufl.edu or your local extension office. SL 40 Behavior of Pesticides in Soils and Water 1 P.S.C. Rao and A.G. Hornsby2 During the past twenty years, concern has arisen applied, and to show how this information can be as to the presence of pesticides in the environment used, along with other factors, to select the proper and the threat they pose to wildlife and mankind. pesticide. Certainly, pesticides have improved longevity and the quality of life, chiefly in the area of public health. PATHWAYS OF PESTICIDE LOSS The use of pesticides also constitutes an important There are basically two ways properly-applied aspect of modern agriculture. Florida's temperate to pesticides may reach surface and ground waters- subtropical climate favors growth of many harmful through runoff and leaching. Runoff is the physical insects, weeds and diseases, thus making this state transport of pollutants over the ground surface by particularly dependent on pesticides for economical rainwater which does not penetrate the soil. Leaching crop management. is a process whereby pollutants are flushed through Unfortunately, pesticides are poisons and can be the soil by rain or irrigation water as it moves particularly dangerous when misused. Fish-kills, downward. In many areas of Florida, soils are sandy reproductive failure in birds, and acute illnesses in and permeable and leaching is likely to be a more people have all been attributed to exposure to or serious problem than runoff. We now have ingestion of pesticides - usually as a result of technology to help estimate the potential misapplication or careless disposal of unused contamination of water from a given pesticide. -
Nitrogen Deposition Contributes to Soil Acidification in Tropical Ecosystems
Global Change Biology Global Change Biology (2014), doi: 10.1111/gcb.12665 Nitrogen deposition contributes to soil acidification in tropical ecosystems XIANKAI LU1 , QINGGONG MAO1,2,FRANKS.GILLIAM3 ,YIQILUO4 and JIANGMING MO 1 1Key Laboratory of Vegetation Restoration and Management of Degraded Ecosystems, South China Botanical Garden, Chinese Academy of Sciences, Guangzhou 510650, China, 2University of Chinese Academy of Sciences, Beijing 100049, China, 3Department of Biological Sciences, Marshall University, Huntington, WV 25755-2510, USA, 4Department of Microbiology and Plant Biology, University of Oklahoma, Norman, OK 73019, USA Abstract Elevated anthropogenic nitrogen (N) deposition has greatly altered terrestrial ecosystem functioning, threatening eco- system health via acidification and eutrophication in temperate and boreal forests across the northern hemisphere. However, response of forest soil acidification to N deposition has been less studied in humid tropics compared to other forest types. This study was designed to explore impacts of long-term N deposition on soil acidification pro- cesses in tropical forests. We have established a long-term N-deposition experiment in an N-rich lowland tropical for- À1 À1 est of Southern China since 2002 with N addition as NH4NO3 of 0, 50, 100 and 150 kg N ha yr . We measured soil acidification status and element leaching in soil drainage solution after 6-year N addition. Results showed that our study site has been experiencing serious soil acidification and was quite acid-sensitive showing high acidification < < (pH(H2O) 4.0), negative water-extracted acid neutralizing capacity (ANC) and low base saturation (BS, 8%) through- out soil profiles. Long-term N addition significantly accelerated soil acidification, leading to depleted base cations and decreased BS, and further lowered ANC. -
Nitrate Leaching from Intensive Organic Farms to Groundwater
Open Access Hydrol. Earth Syst. Sci., 18, 333–341, 2014 Hydrology and www.hydrol-earth-syst-sci.net/18/333/2014/ doi:10.5194/hess-18-333-2014 Earth System © Author(s) 2014. CC Attribution 3.0 License. Sciences Nitrate leaching from intensive organic farms to groundwater O. Dahan1, A. Babad1, N. Lazarovitch2, E. E. Russak3, and D. Kurtzman4 1Department of Environmental Hydrology & Microbiology, Zuckerberg Institute for Water Research, Blaustein Institutes for Desert Research, Ben-Gurion University of the Negev, Midreshet Ben-Gurion, Israel 2Wyler Department of Dryland Agriculture, French Associates Institute for Agriculture and Biotechnology of Drylands, Jacob Blaustein Institutes for Desert Research, Ben-Gurion University of the Negev, Midreshet Ben-Gurion, Israel 3Geological and Environmental Sciences, Ben-Gurion University of the Negev, Beer Sheva, Israel 4Institute of Soil, Water and Environmental Sciences, Agricultural Research Organization, The Volcani Center, Bet Dagan, Israel Correspondence to: O. Dahan ([email protected]) Received: 18 June 2013 – Published in Hydrol. Earth Syst. Sci. Discuss.: 29 July 2013 Revised: 8 December 2013 – Accepted: 11 December 2013 – Published: 27 January 2014 Abstract. It is commonly presumed that organic agriculture productive agriculture must inherently include the leaching causes only minimal environmental pollution. In this study, of excess lower quality water below the root zone to the un- we measured the quality of percolating water in the vadose saturated zone and ultimately to the groundwater (Shani et zone, underlying both organic and conventional intensive al., 2007; Dudley et al., 2008). As such, maintaining the del- greenhouses. Our study was conducted in newly established icate balance between productive agriculture and groundwa- farms where the subsurface underlying the greenhouses has ter quality requires a broad perspective over different time been monitored continuously from their establishment. -
Lowering Soil Ph for Horticulture Crops
PURDUE EXTENSION HO-241-W Commercial Greenhouse and Nursery Production Lowering Soil pH for Horticulture Crops Purdue Horticulture and Michael V. Mickelbart and Kelly M. Stanton, Landscape Architecture Purdue Horticulture and Landscape Architecture www.ag.purdue.edu/HLA Steve Hawkins and James Camberato, Purdue Agronomy Purdue Agronomy www.ag.purdue.edu/AGRY The pH scale measures the acidity or alkalinity of a solution. The scale extends from 0 (a very strong acid) to 14 (a very strong base or highly alkaline). The middle of the scale, 7, is neutral, neither acidic nor basic. Soil pH is important because it affects the availability of nutrients in the rooting zone. This publication explains when lowering soil pH is important for commercial producers and recommends practices to safely and effectively lower soil pH. For more about soil pH, see Purdue Extension publication HO-240-W, Commercial Greenhouse and Nursery Production: Soil pH (available from the Purdue Extension Education Store, www. the-education-store.com). When it comes to soil pH, an accurate diagnosis is essential. Before making any changes, test your soil pH. Purdue Extension provides a list of commercial soil testing labs at: www.ag.purdue.edu/agry/extension/Pages/soil-testing-labs.aspx Why Lower Soil pH? Some plants (such as blueberries or azaleas) are adapted to grow in acid soils — even as low as pH 4.5. If you are trying to grow them you may want a soil pH less than 6, but remember that even acid-loving plants have their limits. Table 1. Effects of soil amendments on pH. -
Chemical and Biochemical Properties of Soils Developed from Different Lithologies in Northwestern Spain (Galicia)
Article Chemical and Biochemical Properties of Soils Developed from Different Lithologies in Northwestern Spain (Galicia) Valeria Cardelli 1,*, Stefania Cocco 1, Alberto Agnelli 2, Serenella Nardi 3, Diego Pizzeghello 3, Maria J. Fernández‐Sanjurjo 4 and Giuseppe Corti 1 1 Department of Agricultural, Food and Environmental Sciences, Università Politecnica delle Marche, Ancona, 60131, Italy; [email protected] (S.C.); [email protected] (G.C.) 2 Department of Agricultural, Food and Environmental Sciences, Università degli Studi di Perugia, Perugia, 06121, Italy; [email protected] 3 Department of Agronomy, Food, Natural Resources, Animals and the Environment, Università degli Studi di Padova, Legnaro, 35020, Italy; [email protected] (S.N.); [email protected] (D.P.) 4 Department of Soil and Agronomic Chemistry, Universidade de Santiago de Compostela, Lugo, 27001, Spain; [email protected] * Correspondence: [email protected]; Tel.: +39‐338‐599‐6867 Academic Editors: Adele Muscolo and Miroslava Mitrovic Received: 15 March 2017; Accepted: 19 April 2017; Published: 22 April 2017 Abstract: Physical and chemical soil properties are generally correlated with the parent material, as its composition may influence the pedogenetic processes, the content of nutrients, and the element biocycling. This research studied the chemical and biochemical properties of the A horizon from soils developed on different rocks like amphibolite, serpentinite, phyllite, and granite under a relatively similar climatic regime from Galicia (northwest Spain). In particular, the effect of the parent material on soil evolution, organic carbon sequestration, and the hormone‐like activity of humic and fulvic acids were tested. Results indicated that all the soils were scarcely fertile because of low concentrations of available P, exchangeable Ca (except for the soils on serpentinite and phyllite), and exchangeable K, but sequestered relevant quantities of organic carbon.