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Eletrochemical Changes in Gleysol of the Amazon Estuary
http://dx.doi.org/10.4322/rca.1796 ORIGINAL ARTICLE George Rodrigues da Silva1* Paulo Augusto Lobato da Silva2 Sérgio Brazão e Silva1 Mário Lopes da Silva Junior1 Eletrochemical changes in Gleysol of the Marcos André Piedade Gama1 Antonio Rodrigues Fernandes1 Amazon estuary Alterações eletroquímicas em Gleissolo do estuário 1 Universidade Federal Rural da Amazônia – UFRA, Instituto de Ciências Agrárias, Av. Presidente Tancredo Neves, 2501, 66077-830, Belém, PA, amazônico Brasil 2 Empresa de Assistência Técnica e Extensão Rural do Estado do Pará – EMATER/PA, Rodovia BR- 316, km 12, s/n, 67105-970, Ananindeua, PA, ABSTRACT: Electrochemical reactions are intensified by soil flooding, which changes Brasil the dynamics of nutrients and negatively affects plant growth. In this work, we aimed to Corresponding Author: evaluate the changes in the redox potential (Eh), pH and nutrient availability in a Haplic E-mail: [email protected] Gleysol soil from a floodplain of the Guamá River, Belém, Pará State. During the period of floods (61 days), samples soils were collected on alternate days and analyzed in dry and wet conditions. Flooding resulted in higher pH values and decreased Eh, which stabilized after 32 days of flooding and did not affect the values of total nitrogen. An increase in the KEYWORDS Oxidation-reduction concentrations of phosphorus, sulfur, iron, manganese, copper and zinc were observed, and Availability of nutrients they were subsequently reduced with time of submergence. The reduction of sulfur occurred Waterlogged soils at low Eh and pH values near neutrality. The results show that nitrogen and sulfur do not limit agricultural production in the lowland soils of the Guamá River. -
General Characteristics of Soil| Sample Answer
General Characteristics of Soil| sample answer Q: ‘Examine the general composition and characteristics of any one soil type that you have studied’ (2007 Q17) Latosol- A tropical zonal soil. 3 aspects will be discussed. 1. Composition: Soil is composed of a number of ingredients/components. These components can vary in portion. All soils form as result of the action of several factors. THese factors combine to influence the many processes at work in soil formation eg. Leaching and weathering. These give soil its own characteristics. Soil is composed of number of ingredients and constituents. The components of soil are mixed in different quantities to create different soil types. They are made up of mineral matter, air, water, humus, living organisms. However, climate is the single most important factor in determining what a soil will be like as climate influences vegetation, the rate of weathering and soil, forming processing in an area. The majority of soil is composed of mineral matter. Mineral matter are rock particles from the bedrock and weathered rock. The soil type varies depending on mineral matter. Unconsolidated material eg boulder clay will help form soil more rapidly than solid bedrock as it is partly weathered. Soil is also composed of organic matter. Organic matter includes decaying plants and animals which bacteria and fungi breakdown. Humus is a dark brown jelly-like substance formed from organic matter. Living organisms are also included in ‘organic matter’, earthworms, beetles, fungi, bacteria; they digest organic matter to humus and also mix and create soil. Water is another important component of soil. -
Development Direction of the Soil-Formation Processes for Reclaimed Soda Solonetz-Solonchak Soils of the Ararat Valley During Their Cultivation
Annals of Agrarian Science 16 (2018) 69e74 Contents lists available at ScienceDirect Annals of Agrarian Science journal homepage: http://www.journals.elsevier.com/annals-of-agrarian- science Development direction of the soil-formation processes for reclaimed soda solonetz-solonchak soils of the Ararat valley during their cultivation R.R. Manukyan National Agrarian University of Armenia, 74, Teryan Str., Yerevan, 0009, Armenia article info abstract Article history: The data of the article show that the long-term cultivation of reclaimed sodium solonetz-solonchak soils Received 29 May 2017 entails to further improvement of their properties and in many parameters of chemical compositions of Accepted 19 August 2017 soil solution and soil-absorbing complex they come closer to irrigated meadow-brown soils in the period Available online 6 February 2018 of 15e20 years of agricultural development. The analysis of the experimental research by the method of non-linear regression shows, that for the enhancement of some yield determining parameters to the Keywords: level of irrigated meadow-brown soils, a time period of 30e40 years of soil-formation processes is Soil-formation processes needed and longer time is necessary for humidification. The forecast of soil-formation processes for the Reclaimed soda solonetz-solonchaks fi Irrigated meadow-brown soils long-term period, allows to reveal the intensity and orientation of development of the speci ed pro- fi fi Multi-year cultivation cesses and to develop the scienti cally-justi ed actions for their further improvement. Improvement © 2018 Agricultural University of Georgia. Production and hosting by Elsevier B.V. This is an open access Forecasting article under the CC BY-NC-ND license (http://creativecommons.org/licenses/by-nc-nd/4.0/). -
Prairie Wetland Soils: Gleysolic and Organic Angela Bedard-Haughn Department of Soil Science, University of Saskatchewan
PS&C Prairie Soils & Crops Journal Agricultural Soils of the Prairies Prairie Wetland Soils: Gleysolic and Organic Angela Bedard-Haughn Department of Soil Science, University of Saskatchewan Summary Gleysolic and Organic soils are collectively referred to as “wetland soils”. They are found in wet low-lying or level landscape positions. Gleysolic soils are found throughout the agricultural Prairies, in association with Chernozemic and Luvisolic soils. In semi-arid regions, they are frequently tilled in dry years and can be very productive due to their relatively high levels of soil moisture and nutrients. In the Prairie Provinces, Organic soils tend to be mostly associated with the Boreal transition zones at the northern and eastern perimeter of the Prairies. With proper management, these can also provide productive agricultural land, particularly for forages. Introduction Soils of the Gleysolic and Organic orders are collectively referred to as “wetland soils”. Soil maps of the agricultural region of the Canadian Prairies seldom have areas mapped as dominantly Gleysolic8 or Organic9; however, these soils are found throughout the region wherever climate and/or topography have led to persistent water-saturated conditions. Gleysols are mineral soils with colors that reflect intermittent or prolonged anaerobic (i.e., saturated, low oxygen) conditions (Fig. 1A). Organic soils reflect permanent anaerobic conditions, which lead to soils that are made up of variably decomposed plant residues, mostly from water-tolerant (i.e., hydrophytic) vegetation (Fig. 1B). Figure 1: A) Humic Luvic Gleysol, Saskatchewan and B) Typic Fibrisol (Organic), Manitoba7. Of the some 100,000,000 ha covered by the Canada Land Inventory (CLI) in the Prairie Provinces12, Gleysolic soils occupy less than 15% of the Prairie ecoregions and up to 40% in the Mid-Boreal (boreal = “northern”) Upland (Alberta) and Interlake Plain (Manitoba) ecoregions12. -
World Reference Base for Soil Resources 2014 International Soil Classification System for Naming Soils and Creating Legends for Soil Maps
ISSN 0532-0488 WORLD SOIL RESOURCES REPORTS 106 World reference base for soil resources 2014 International soil classification system for naming soils and creating legends for soil maps Update 2015 Cover photographs (left to right): Ekranic Technosol – Austria (©Erika Michéli) Reductaquic Cryosol – Russia (©Maria Gerasimova) Ferralic Nitisol – Australia (©Ben Harms) Pellic Vertisol – Bulgaria (©Erika Michéli) Albic Podzol – Czech Republic (©Erika Michéli) Hypercalcic Kastanozem – Mexico (©Carlos Cruz Gaistardo) Stagnic Luvisol – South Africa (©Márta Fuchs) Copies of FAO publications can be requested from: SALES AND MARKETING GROUP Information Division Food and Agriculture Organization of the United Nations Viale delle Terme di Caracalla 00100 Rome, Italy E-mail: [email protected] Fax: (+39) 06 57053360 Web site: http://www.fao.org WORLD SOIL World reference base RESOURCES REPORTS for soil resources 2014 106 International soil classification system for naming soils and creating legends for soil maps Update 2015 FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS Rome, 2015 The designations employed and the presentation of material in this information product do not imply the expression of any opinion whatsoever on the part of the Food and Agriculture Organization of the United Nations (FAO) concerning the legal or development status of any country, territory, city or area or of its authorities, or concerning the delimitation of its frontiers or boundaries. The mention of specific companies or products of manufacturers, whether or not these have been patented, does not imply that these have been endorsed or recommended by FAO in preference to others of a similar nature that are not mentioned. The views expressed in this information product are those of the author(s) and do not necessarily reflect the views or policies of FAO. -
The Digital Soil Map of the World
THE DIGITAL SOIL MAP OF THE WORLD FOOD AND AGRICULTURE ORGANIZATION OF THE UNITED NATIONS Version 3.6, completed January 2003 (C) FAO/UNESCO, 1995 All rights reserved worldwide. Background The present version (3.6) of the digitized Soil Map of the World has been cleaned of errors both in the database and in the lines constituting the digitized map itself. The original map sheets covering the Americas are in bipolar oblique conformal projection. The other sheets, covering Europe, Africa, Asia and Australasia, are based on the Miller oblated stereographic projection; a system consisting of three conformal projections centred on each continent, joined together in a continuous fashion by so-called "fill-in" projections. This allows a complete angular continuity between all sheets. The soil map was prepared using the topographic map series of the American Geographical Society of New York as a base at a nominal scale of 1:5 000 000. The base map comprises sixteen sheets; for the purpose of the Soil Map of the World the information has been redistributed over eighteen sheets in order to obtain sheets of equal size. A nineteenth sheet contains the legend. The digital database is in the Geographic projection. All maps were intersected with a template containing water related features (coastlines, lakes, islands, glaciers and double-lined rivers). This layer was superimposed on the soil map (the information is represented in the FAOSOIL item as: inland WATer, and GLaciers). The Soil Map of the World except for Africa was intersected with the Country Boundaries map from the World Data Bank II (with country boundaries updated to January 1994 at 1:3 000 000 scale), obtained from the US Government. -
Effects of Afforestation on Soil Structure Formation in Two Climatic Regions Of
JOURNAL OF FOREST SCIENCE, 61, 2015 (5): 225–234 doi: 10.17221/6/2015-JFS Eff ects of aff orestation on soil structure formation in two climatic regions of the Czech Republic V. Podrázský1, O. Holubík2, J. Vopravil2, T. Khel2, W.K. Moser3, H. Prknová1 1Faculty of Forestry and Wood Sciences, Czech University of Life Sciences Prague, Prague, Czech Republic 2Research Institute for Soil and Water Conservation, Department of Soil Science and Soil Conservation, Prague-Zbraslav, Czech Republic 3U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station, Flagstaff, Arizona, USA ABSTRACT: The aim of this study was to determine the effect of agricultural land afforestation on soil characteristics. Two sites in two regions of the Czech Republic were evaluated, at lower as well as higher submountain elevations: in the regions of the Orlické hory Mts. and Kostelec nad Černými lesy, afforested, arable and pasture lands were com- pared for basic chemical and physical characteristics. It was determined: pH, CEC, exchangeable nutrients, SOC, bulk density, volume density, porosity (differentiated by pore size), water conductivity and soil aggregate stability. This study demonstrated the important influence of previous land use upon soil characteristics. The characteristics of the arable horizon can persist for many years; in forests, the mineral horizons (15–30 cm) can persist within 15–30 years after afforestation. Afforestation, which caused an increase in soil porosity by decreasing reduced bulk density and increasing capillary and gravitational pores (increasing the water-holding capacity and soil air capacity), is important for maintaining the soil stability. The positive effect on infiltration and retention capacity resulted not only from the presence of a forest overstorey, but also from the presence of permanent grass cover of pasture land. -
Ph, SOIL ACIDITY, and PLANT GROWTH 67 Numbers, the Danish Biochemist S
pH, SOIL ACIDITY, AND PLANT GROWTH 67 numbers, the Danish biochemist S. P. L. Sorenson devised a system called pH for expressing the acidity or alka- pH, Soil Acidity, linity of solutions. The pH scale goes from o to 14. At pH 7, the midpoint of the scale, there and Plant Growth are equal numbers of hydrogen and hydroxyl ions, and the solution is neu- W. H. Allaway tral. pH values below 7 indicate an acid solution, where there are more hydro- When crop plants do not grow gen ions than hydroxyl ions, with the well, one of the first questions acidity (or hydrogen ion concentra- tion) increasing as the pH values get the soil scientist usually asks smaller. is, ''What is the pH of the soil?'' pH values above 7 denote alkaline solutions, with the concentration of or, 'Is the soil acid, neutral, hydroxyl ions increasing as the pH or alkaline?'' values get larger. The pH scale is based on logarithms The reason for these questions lies in of the concentration of the hydrogen the fact that the pH, or degree of and hydroxyl ions. This means that a acidity of the soil, often is a symptom solution of pH 5 has 10 times the hy- of some disorder in the chemical con- drogen ion concentration of a solution dition of the soil as it relates to plant of pH 6. A solution of pH 4 has 10 nutrition. times more hydrogen ions than one of A measurement of soil acidity or pH 5 and 10 times 10, or 100 times, alkalinity is like a doctor's measure- the hydrogen ion concentration of a ment of a patient's temperature. -
Some Features of Soil Contamination Based on Soil Monitoring System in Slovakia
SOME FEATURES OF SOIL CONTAMINATION BASED ON SOIL MONITORING SYSTEM IN SLOVAKIA Jozef Kobza National Agricultural and Food Centre – Soil Science and Conservation Research Institute Bratislava, Regional working place Banská Bystrica, Mládežnícka 36, 974 04 Banská Bystrica, Slovakia, e-mail: [email protected] Identification of factors in relation to soil contamination 1. Natural (physical-geographical) factors include: V climatic conditions (temperature, precipitation, evapotranspiration, speed and directions of wind) V soil - lithological conditions (geology, soil type, texture, occurrence of geochemical anomalies, etc.) V vegetation (type of vegetation, rooting, etc.) V topography (slope, relief, elevation/altitude) 2. Anthropogenic factors include: V land use and farming system (crop land, grassland, forest) V use of fertilisers and organic manures V irrigation, melioration practices V other sources (sealing, mining, waste disposal, pollutant emissions) Measured risk elements in soil monitoring network in Slovakia • Cd, Pb, Cu, Zn, Ni, Cr, Se, Co, As (aqua regia) • Hg (total content, AMA 254) • Fw (watersoluble fluorine measured by ionselective electrode) Mean content of risk elements on agricultural soils in Slovakia Soils As Cd Co Cr Cu Ni Pb Zn Se Hg FM 10.8 0.7 8.8 39.1 34.0 37.0 54.3 122.8 - 0.2 ČA 10.0 0.4 7.8 42.9 22.7 29.6 21.1 75.6 0.2 0.06 ČM 10.0 0.4 7.8 42.9 22.7 29.6 21.1 75.6 0.3 0.1 HM 9.2 0.2 10.0 41.5 22.9 32.6 19.7 68.8 0.1 0.05 LM+PG 9.9 0.3 9.7 42.8 17.0 23.3 24.2 66.7 0.2 0.07 KM 14.8 0.3 12.6 52.2 28.9 29.2 27.0 -
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. -
Redalyc.STRUCTURAL QUALITY of POLYACRYLAMIDE-TREATED
Revista Brasileira de Ciência do Solo ISSN: 0100-0683 [email protected] Sociedade Brasileira de Ciência do Solo Brasil Vandeval Maranhão de Melo, Diego; Gomes de Almeida, Brivaldo; Rodrigues de Souza, Edivan; Santos Silva, Laércio; Jacomine, Paulo Klinger Tito STRUCTURAL QUALITY OF POLYACRYLAMIDE-TREATED COHESIVE SOILS IN THE COASTAL TABLELANDS OF PERNAMBUCO Revista Brasileira de Ciência do Solo, vol. 38, núm. 2, 2014, pp. 476-485 Sociedade Brasileira de Ciência do Solo Viçosa, Brasil Available in: http://www.redalyc.org/articulo.oa?id=180231134011 How to cite Complete issue Scientific Information System More information about this article Network of Scientific Journals from Latin America, the Caribbean, Spain and Portugal Journal's homepage in redalyc.org Non-profit academic project, developed under the open access initiative 476 Diego Vandeval Maranhão de Melo et al. STRUCTURAL QUALITY OF POLYACRYLAMIDE-TREATED COHESIVE SOILS IN THE COASTAL TABLELANDS OF PERNAMBUCO(1) Diego Vandeval Maranhão de Melo(2), Brivaldo Gomes de Almeida(3), Edivan Rodrigues de Souza(3), Laércio Santos Silva(4) & Paulo Klinger Tito Jacomine(5) SUMMARY Water-soluble polymers are characterized as effective flocculating agents due to their molecular features. Their application to soils with horizons with structural problems, e.g, a cohesive character, contributes to improvements in the physical quality and thus to the agricultural suitability of such soils. The purpose of this study was to evaluate the structural quality of soils with cohesive horizons of coastal tablelands in the State of Pernambuco treated with polyacrylamide (PAM) as chemical soil conditioner. To this end, three horizons (one cohesive and two non- cohesive) of a Yellow Argisol (Ultisol) were evaluated and to compare cohesive horizons, the horizon of a Yellow Latosol (Oxisol) was selected. -
The Comparative Effects of Calcium Carbonate and of Calcium Silicate on the Yield of Sudan Grass Grown in a Ferruginous Latosol and a Hydrol Humic Latosol
TECHNICAL BULLETIN No. 53 JUNE 1963 The Comparative Effects of Calcium Carbonate and of Calcium Silicate on the Yield of Sudan Grass Grown in a Ferruginous Latosol and a Hydrol Humic Latosol N. H. MONTEITH and G. DONALD SHERMAN HAWAII AGRICULTURAL EXPERIMENT STATION, UNIVERSITY OF HAWAII The Comparative Effects of Calcium Carbonate and of Calcium Silicate on the Yield of Sudan Grass Grown in a Ferruginous Latosol and a Hydrol Humic Latosol N. H. MONTEITH and G. DONALD SHERMAN UNIVERSITY OF HAWAII COLLEGE OF TROPICAL AGRICULTURE HAWAII AGRICULTURAL EXPERIMENT STATION HONOLULU, H AWAII J UNE 1963 T ECIINICAL B ULLETIN No. 53 ACKNOWLEDGMENT The authors gra tcfully acknow ledge the assistance of the staff of th e Experiment Station of the H awaii an Sugar Planters' Association in pro viding greenhouse, photographic, and laboratory facilities, and for advice on sta tistical and analytical methods. Research funds on this proj ect were pro vid ed by the Hawaiian Sugar Planters' Association Experiment Station under a coope rative research agreemcnt with the Department of Agronomy and Soil Science. Funds and materials we re also provided by the Tenn essee Valley Authority, Contract No. TV21132A. THE AUTHORS N. H. MONTEITH was In structor in Agricultur e, University of Hawaii, 1961-1962. DR. G. DONALD SHERMAN, Associate Director of the Hawaii Agricultural Experiment Station, is Senior Soil Scientist at the Hawaii Agricultural Ex periment Station and Senior Professor of Soil Science, University of Hawaii. CONTENTS PAGE INTRODUcrION 5 LITERAT UHE REVIEW 5 Effect of Calcium Carbonate on Phosphorus Availability 5 Effect of Calcium Carbonate on Other Factors 7 Effect of Calcium Silicate on Phosphorus Availability 8 Effect of Calcium Silicate on Other Factors 8 EXPEmMENTAL PROCEDUHES 9 Soils .