Soil Classification Based on Spectral and Environmental Variables
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Soil Properties and Pre-Columbian Settlement Patterns in The
SOIL, 1, 65–81, 2015 www.soil-journal.net/1/65/2015/ doi:10.5194/soil-1-65-2015 SOIL © Author(s) 2015. CC Attribution 3.0 License. Soil properties and pre-Columbian settlement patterns in the Monumental Mounds Region of the Llanos de Moxos, Bolivian Amazon U. Lombardo1,2, S. Denier1, and H. Veit1 1Universität Bern, Geographisches Institut, Hallerstrasse 12, 3012 Bern, Switzerland 2CaSeS research group, IMF-CSIC, C/Egipciaques, 15-08001 Barcelona, Spain Correspondence to: U. Lombardo ([email protected]) Received: 5 May 2014 – Published in SOIL Discuss.: 15 May 2014 Revised: – – Accepted: 26 September 2014 – Published: 6 January 2015 Abstract. In the present paper we explore to what degree soil properties might have influenced pre-Columbian settlement patterns in the Monumental Mounds Region (MMR) of the Llanos de Moxos (LM), Bolivian Amazon. Monumental mounds are pre-Hispanic earth buildings and were preferentially built on mid- to late Holocene palaeolevees of the Grande River (here denominated PR1), while levees of older palaeorivers (PR0) were only sparsely occupied. We dug two transects across PR0 and PR1 levee–backswamp catenas and analysed them for grain size, pH, cation exchange capacity (CEC) and Corg. Our data show that PR1 soils, where the density of mounds is higher, have far greater agricultural potential than PR0 soils, which are affected by aluminium toxicity in the backswamps and by high levels of exchangeable sodium in the levees. This study provides new data on the soil properties of the south-eastern Bolivian Amazon and reinforces the hypothesis that environmental constraints and opportunities exerted an important role on pre-Columbian occupation patterns and the population density reached in the Bolivian Amazon. -
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. -
Effect of Soil Chiseling on Soil Structure and Root Growth for a Clayey Soil Under No-Tillage
Geoderma 259–260 (2015) 149–155 Contents lists available at ScienceDirect Geoderma journal homepage: www.elsevier.com/locate/geoderma Effect of soil chiseling on soil structure and root growth for a clayey soil under no-tillage Márcio Renato Nunes a,⁎, José Eloir Denardin b, Eloy Antônio Pauletto c, Antônio Faganello b, Luiz Fernando Spinelli Pinto c a University of São Paulo, “Luiz de Queiroz” College of Agriculture, Avenida Pádua Dias, 11, CEP 13418-900 Piracicaba, São Paulo, Brazil b Embrapa Trigo, Rodovia BR 285, km. 294, P.O. Box 451, CEP 99001-970 Passo Fundo, Rio Grande do Sul, Brazil c Federal University of Pelotas, Department of Soil Science, Campus Universitário s/n, P.O. Box 354, 96010-900 Pelotas, Rio Grande do Sul, Brazil article info abstract Article history: Soil chiseling under no-tillage (NT) promotes root growth in depth. This practice, however, might affect soil ag- Received 11 November 2014 gregation. This study evaluated the chiseling effects on the aggregation of a Ferralic Nitisol (Rhodic), under NT, in Received in revised form 2 June 2015 humid subtropical climate region. The treatments carried out consisted of the time that soil was kept under NT Accepted 3 June 2015 after chiseling: continuous NT for 24 months after chiseling in September 2009; continuous NT for 18 months Available online xxxx after chiseling in March 2010; continuous NT for 12 months after chiseling in September 2010; continuous NT for 6 months after chiseling in March 2011; NT in newly chiseling soil in September 2011; continuous NT without Keywords: Soil physical attributes chiseling (control). -
Plant Uptake of Radionuclides in Lysimeter Experiments
AT9900006 Plant uptake of radionuclides in lysimeter experiments M.H. Gerzabek F. Strebl B. Temmel June 1998 OEFZS—4820 SEIBERSDORF 30-20 / OEFZS-4820 June 1998 Plant uptake of radionuclides in lysimeter experiments In: Environmental Pollution 99 (1998) 93-103 M.H. Gerzabek, F. Strebl, B. Temmel Department of Environmental Research Division of Life Sciences ENVIRONMENTAL POLLUTION ELSEVIER Environmental Pollution 99 (1998) 93-103 Plant uptake of radionuclides in lysimeter experiments M.H. Gerzabek*, F. Strebl, B. Temmel Austrian Research Centre Seibersdorf, Division of Life Sciences, A-2444 Seibersdorf Austria Received 20 June 1997; accepted 15 October 1997 Abstract The results of seven years lysimeter experiments to determine the uptake of 60 Co, 137Cs and 226 Ra into agricultural crops (endive, maize, wheat, mustard, sugarbeet, potato, Faba bean, rye grass) are described. The lysimeter consists of twelve monolithic soil profiles (four soil types and three replicates) and is located in Seibersdorf/Austria, a region with a pannonian climate (pronounced differences between hot and semi-arid summers and humid winter conditions, annual mean of precipitation: 517 mm, mean annual temperature: 9.8°C). Besides soil-to-plant transfer factors (TF), fluxes were calculated taking into account biomass production and growth time. Total median values of TF’s (dry matter basis) for the three radionuclides decreased from 226 Ra (0.068 kg kg" 1) to ,37Cs (0.043 kg kg" 1) and 60 Co (0.018 kg kg" 1); flux values exhibited the same ranking. The varying physical and chemical proper ties of the four experimental soils resulted in statistically significant differences in transfer factors or fluxes between the investigated soils for l37Cs and 226 Ra, but not for 60 Co. -
The Soil Map of the Flemish Region Converted to the 3 Edition of the World Reference Base for Soil Resources
Ontwikkelen en toepassen van een methodiek voor de vertaling van de Belgische bodemclassificatie van de kustpolders naar het internationale WRB systeem en generaliseren van de WRB-bodemkaart voor gans Vlaanderen naar het 1 : 250 000 schaalniveau The soil map of the Flemish region converted to the 3 rd edition of the World Reference Base for soil resources Stefaan Dondeyne, Laura Vanierschot, Roger Langohr Eric Van Ranst and Jozef Deckers Oct. 2014 Opdracht van de Vlaamse Overheid Bestek nr. BOD/STUD/2013/01 Contents Contents............................................................................................................................................................3 Acknowledgement ...........................................................................................................................................5 Abstract............................................................................................................................................................7 Samenvatting ...................................................................................................................................................9 1. Background and objectives.......................................................................................................................11 2. The soil map of Belgium............................................................................................................................12 2.1 The soil survey project..........................................................................................................................12 -
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. -
Physical and Chemical Properties in Relation to Soil Permeability in the Area of the Velika Gorica Well Fi
73 The Mining-Geology-Petroleum Engineering Bulletin Physical and chemical properties UDC: ͢͡͡Ǥ͟ǣ͢͡͡Ǥ͡ in relation to soil permeability DOI: 10.17794/rgn.2018.2.7 in the area of the Velika Gorica well Ƥ eld Original scientiƤ c paper Stanko Ruži«i©1; Zoran Kova«1; Dražen Tumara2 1Faculty of Mining, Geology and Petroleum Engineering (Pierottijeva 6, 10000 Zagreb, Croatia, Assistant Professor) 1Faculty of Mining, Geology and Petroleum Engineering (Pierottijeva 6, 10000 Zagreb, Croatia, Post-doctorand) 2Energy Institute Hrvoje Požar (Savska cesta 163, 10001 Zagreb, Croatia, Junior Researcher) Abstract Hydraulic parameters aơ ect the behaviour of various ions in soils. The goal of this paper is to get a better understanding of the relationship between physical and chemical properties and soil permeability at the location of the case study soil proƤ le Velika Gorica, based on physical and chemical data. The soil proƤ le is situated in the Eutric Cambisol of the Za- greb aquifer, Croatia. The Zagreb aquifer represents the only source of potable water for inhabitants of the City of Zagreb and the Zagreb County. Based on the data obtained from particle size analysis, soil hydraulic parameters and measured water content, unsaturated hydraulic conductivity values were calculated for the estimation of soil proƤ le permeability. Soil water retention curves and unsaturated hydraulic conductivities are very similar for all depths because soil texture does not change signiƤ cantly through the depth. Determination of major anions and cations on soil samples was per- formed using the method of ion chromatography. The results showed a decrease of ions concentrations after a depth of Ͱ.6 m. -
Drained Organic Soils Under Agriculture
Geoderma 355 (2019) 113911 Contents lists available at ScienceDirect Geoderma journal homepage: www.elsevier.com/locate/geoderma Drained organic soils under agriculture — The more degraded the soil the higher the specific basal respiration T ⁎ Annelie Säuricha,1, Bärbel Tiemeyera, , Axel Dona, Sabine Fiedlerb, Michel Bechtolda,2, Wulf Amelungc, Annette Freibauera,3 a Thünen Institute of Climate-Smart Agriculture, Bundesallee 65, 38116 Braunschweig, Germany b Institute for Geography, Johannes Gutenberg-University Mainz, 55099 Mainz, Germany c University of Bonn, Institute of Crop Science and Resource Conservation, Soil Science and Soil Ecology, Nussallee 13, 53115 Bonn, Germany ARTICLE INFO ABSTRACT Handling Editor: Ingrid Kögel-Knabner Drained peatlands are hotspots of carbon dioxide (CO2) emissions from agricultural soils. As a consequence of Keywords: both drainage-induced mineralisation and anthropogenic mixing with mineral soils, large areas of former Carbon dioxide peatlands under agricultural use underwent a secondary transformation of the peat (e.g. formation of ag- Peatland agriculture gregates). These soils show contents of soil organic carbon (SOC) at the boundary between mineral and organic Heinemeyer incubation soils. However, the carbon (C) dynamics of such soils have rarely been studied so far. The aim of the present Anthropogenic disturbance study was to evaluate the vulnerability of soil organic matter (SOM) to decomposition over the whole range of − Peat-sand-mixing peat-derived soils under agriculture including very carbon rich mineral soils (76–526 g kg 1 SOC). A total of 62 soil samples covering a broad range of soil and site characteristics were selected from the sample set of the German Agricultural Soil Inventory. -
Are CH4, CO2, and N2O Emissions from Soil Affected by the Sources and Doses of N in Warm-Season Pasture?
atmosphere Article Are CH4, CO2, and N2O Emissions from Soil Affected by the Sources and Doses of N in Warm-Season Pasture? Darlena Caroline da Cruz Corrêa, Abmael da Silva Cardoso * , Mariane Rodrigues Ferreira, Débora Siniscalchi, Ariana Desie Toniello, Gilmar Cotrin de Lima, Ricardo Andrade Reis and Ana Claudia Ruggieri Departamento de Zootecnia, Faculdade de Ciências Agrárias e Veterinárias, UNESP—Universty Estadual Paulista, Jaboticabal 14884-900, SP, Brazil; [email protected] (D.C.d.C.C.); [email protected] (M.R.F.); [email protected] (D.S.); [email protected] (A.D.T.); [email protected] (G.C.d.L.); [email protected] (R.A.R.); [email protected] (A.C.R.) * Correspondence: [email protected] Abstract: The intensification of pasture production has increased the use of N fertilizers—a practice that can alter soil greenhouse gas (GHG) fluxes. The objective of the present study was to evaluate the fluxes of CH4, CO2, and N2O in the soil of Urochloa brizantha ‘Marandu’ pastures fertilized with different sources and doses of N. Two field experiments were conducted to evaluate GHG fluxes following N fertilization with urea, ammonium nitrate, and ammonium sulfate at doses of 0, 90, 180, and 270 kg N ha−1. GHG fluxes were quantified using the static chamber technique and gas chromatography. In both experiments, the sources and doses of N did not significantly affect cumulative GHG emissions, while N fertilization significantly affected cumulative N O and CO 2 2 emissions compared to the control treatment. The N2O emission factor following fertilization with urea, ammonium nitrate, and ammonium sulfate was lower than the United Nations’ Intergovern- Citation: Corrêa, D.C.d.C.; Cardoso, A.d.S.; Ferreira, M.R.; Siniscalchi, D.; mental Panel on Climate Change standard (0.35%, 0.24%, and 0.21%, respectively, with fractionation Toniello, A.D.; Lima, G.C.d.; Reis, fertilization and 1.00%, 0.83%, and 1.03%, respectively, with single fertilization). -
Soil Organic Matter As Sole Indicator of Soil Degradation
Environ Monit Assess (2017) 189:176 DOI 10.1007/s10661-017-5881-y Soil organic matter as sole indicator of soil degradation S.E. Obalum & G.U. Chibuike & S. Peth & Y. Ouyang Received: 27 July 2016 /Accepted: 7 March 2017 # Springer International Publishing Switzerland 2017 Abstract Soil organic matter (SOM) is known to play properties as well. Thus, functions of SOM almost al- vital roles in the maintenance and improvement of many ways affect various soil properties and processes and soil properties and processes. These roles, which largely engage in multiple reactions. In view of its role in soil influence soil functions, are a pool of specific contribu- aggregation and erosion control, in availability of plant tions of different components of SOM. The soil func- nutrients and in ameliorating other forms of soil degra- tions, in turn, normally define the level of soil degrada- dation than erosion, SOM has proven to be an important tion, viewed as quantifiable temporal changes in a soil indicator of soil degradation. It has been suggested, that impairs its quality. This paper aims at providing a however, that rather than the absolute amount, temporal generalized assessment of the current state of knowl- change and potential amount of SOM be considered in edge on the usefulness of SOM in monitoring soil its use as indicator of soil degradation, and that SOM degradation, based on its influence on the physical, may not be an all-purpose indicator. Whilst SOM re- chemical and biological properties and processes of mains a candidate without substitute as long as a one- soils. -
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