Evolution of Loess-Derived Soil Along a Topo-Climatic Sequence in The
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Soil Contamination and Human Health: a Major Challenge For
Soil contamination and human health : A major challenge for global soil security Florence Carre, Julien Caudeville, Roseline Bonnard, Valérie Bert, Pierre Boucard, Martine Ramel To cite this version: Florence Carre, Julien Caudeville, Roseline Bonnard, Valérie Bert, Pierre Boucard, et al.. Soil con- tamination and human health : A major challenge for global soil security. Global Soil Security Sympo- sium, May 2015, College Station, United States. pp.275-295, 10.1007/978-3-319-43394-3_25. ineris- 01864711 HAL Id: ineris-01864711 https://hal-ineris.archives-ouvertes.fr/ineris-01864711 Submitted on 30 Aug 2018 HAL is a multi-disciplinary open access L’archive ouverte pluridisciplinaire HAL, est archive for the deposit and dissemination of sci- destinée au dépôt et à la diffusion de documents entific research documents, whether they are pub- scientifiques de niveau recherche, publiés ou non, lished or not. The documents may come from émanant des établissements d’enseignement et de teaching and research institutions in France or recherche français ou étrangers, des laboratoires abroad, or from public or private research centers. publics ou privés. Human Health as another major challenge of Global Soil Security Florence Carré, Julien Caudeville, Roseline Bonnard, Valérie Bert, Pierre Boucard, Martine Ramel Abstract This chapter aimed to demonstrate, by several illustrated examples, that Human Health should be considered as another major challenge of global soil security by emphasizing the fact that (a) soil contamination is a worldwide issue, estimations can be done based on local contamination but the extent and content of diffuse contamination is largely unknown; (b) although soil is able to store, filter and reduce contamination, it can also transform and make accessible soil contaminants and their metabolites, contributing then to human health impacts. -
Soil As a Huge Laboratory for Microorganisms
Research Article Agri Res & Tech: Open Access J Volume 22 Issue 4 - September 2019 Copyright © All rights are reserved by Mishra BB DOI: 10.19080/ARTOAJ.2019.22.556205 Soil as a Huge Laboratory for Microorganisms Sachidanand B1, Mitra NG1, Vinod Kumar1, Richa Roy2 and Mishra BB3* 1Department of Soil Science and Agricultural Chemistry, Jawaharlal Nehru Krishi Vishwa Vidyalaya, India 2Department of Biotechnology, TNB College, India 3Haramaya University, Ethiopia Submission: June 24, 2019; Published: September 17, 2019 *Corresponding author: Mishra BB, Haramaya University, Ethiopia Abstract Biodiversity consisting of living organisms both plants and animals, constitute an important component of soil. Soil organisms are important elements for preserved ecosystem biodiversity and services thus assess functional and structural biodiversity in arable soils is interest. One of the main threats to soil biodiversity occurred by soil environmental impacts and agricultural management. This review focuses on interactions relating how soil ecology (soil physical, chemical and biological properties) and soil management regime affect the microbial diversity in soil. We propose that the fact that in some situations the soil is the key factor determining soil microbial diversity is related to the complexity of the microbial interactions in soil, including interactions between microorganisms (MOs) and soil. A conceptual framework, based on the relative strengths of the shaping forces exerted by soil versus the ecological behavior of MOs, is proposed. Plant-bacterial interactions in the rhizosphere are the determinants of plant health and soil fertility. Symbiotic nitrogen (N2)-fixing bacteria include the cyanobacteria of the genera Rhizobium, Free-livingBradyrhizobium, soil bacteria Azorhizobium, play a vital Allorhizobium, role in plant Sinorhizobium growth, usually and referred Mesorhizobium. -
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. -
A Systemic Approach for Modeling Soil Functions
SOIL, 4, 83–92, 2018 https://doi.org/10.5194/soil-4-83-2018 © Author(s) 2018. This work is distributed under SOIL the Creative Commons Attribution 4.0 License. A systemic approach for modeling soil functions Hans-Jörg Vogel1,5, Stephan Bartke1, Katrin Daedlow2, Katharina Helming2, Ingrid Kögel-Knabner3, Birgit Lang4, Eva Rabot1, David Russell4, Bastian Stößel1, Ulrich Weller1, Martin Wiesmeier3, and Ute Wollschläger1 1Helmholtz Centre for Environmental Research – UFZ, Permoserstr. 15, 04318 Leipzig, Germany 2Leibniz Centre for Agricultural Landscape Research (ZALF), Eberswalder Straße 84, 15374 Müncheberg, Germany 3TUM School of Life Sciences Weihenstephan, Technical University of Munich, Emil-Ramann-Straße 2, 85354 Freising, Germany 4Senckenberg Museum of Natural History, Sonnenplan 7, 02826 Görlitz, Germany 5Martin-Luther-University Halle-Wittenberg, Institute of Soil Science and Plant Nutrition, Von-Seckendorff-Platz 3, 06120 Halle (Saale), Germany Correspondence: Hans-Jörg Vogel ([email protected]) Received: 13 September 2017 – Discussion started: 4 October 2017 Revised: 2 February 2018 – Accepted: 14 February 2018 – Published: 15 March 2018 Abstract. The central importance of soil for the functioning of terrestrial systems is increasingly recognized. Critically relevant for water quality, climate control, nutrient cycling and biodiversity, soil provides more func- tions than just the basis for agricultural production. Nowadays, soil is increasingly under pressure as a limited resource for the production of food, energy and raw materials. This has led to an increasing demand for concepts assessing soil functions so that they can be adequately considered in decision-making aimed at sustainable soil management. The various soil science disciplines have progressively developed highly sophisticated methods to explore the multitude of physical, chemical and biological processes in soil. -
Effects of Treated Wastewater Irrigation on Soil Salinity and Sodicity in Sfax (Tunisia): a Case Study"
CORE Metadata, citation and similar papers at core.ac.uk Provided by Érudit Article "Effects of treated wastewater irrigation on soil salinity and sodicity in Sfax (Tunisia): A case study" Nebil Belaid, Catherine Neel, Monem Kallel, Tarek Ayoub, Abdel Ayadi, et Michel Baudu Revue des sciences de l'eau / Journal of Water Science, vol. 23, n° 2, 2010, p. 133-146. Pour citer cet article, utiliser l'information suivante : URI: http://id.erudit.org/iderudit/039905ar DOI: 10.7202/039905ar Note : les règles d'écriture des références bibliographiques peuvent varier selon les différents domaines du savoir. Ce document est protégé par la loi sur le droit d'auteur. L'utilisation des services d'Érudit (y compris la reproduction) est assujettie à sa politique d'utilisation que vous pouvez consulter à l'URI https://apropos.erudit.org/fr/usagers/politique-dutilisation/ Érudit est un consortium interuniversitaire sans but lucratif composé de l'Université de Montréal, l'Université Laval et l'Université du Québec à Montréal. Il a pour mission la promotion et la valorisation de la recherche. Érudit offre des services d'édition numérique de documents scientifiques depuis 1998. Pour communiquer avec les responsables d'Érudit : [email protected] Document téléchargé le 13 février 2017 01:03 EFFECTS OF TREATED WASTEWATER IRRIGATION ON SOIL SALINITY AND SODICITY IN SFAX (TUNISIA): A CASE STUDY Effets de l’irrigation par les eaux usées traitées sur la salinité et la sodicité des sols de Sfax (Tunisie): Un cas d’étude Nebil belaid1,2 , CatheriNe Neel2*, MoNeM Kallel3, -
The Muencheberg Soil Quality Rating (SQR)
The Muencheberg Soil Quality Rating (SQR) FIELD MANUAL FOR DETECTING AND ASSESSING PROPERTIES AND LIMITATIONS OF SOILS FOR CROPPING AND GRAZING Lothar Mueller, Uwe Schindler, Axel Behrendt, Frank Eulenstein & Ralf Dannowski Leibniz-Zentrum fuer Agrarlandschaftsforschung (ZALF), Muencheberg, Germany with contributions of Sandro L. Schlindwein, University of St. Catarina, Florianopolis, Brasil T. Graham Shepherd, Nutri-Link, Palmerston North, New Zealand Elena Smolentseva, Russian Academy of Sciences, Institute of Soil Science and Agrochemistry (ISSA), Novosibirsk, Russia Jutta Rogasik, Federal Agricultural Research Centre (FAL), Institute of Plant Nutrition and Soil Science, Braunschweig, Germany 1 Draft, Nov. 2007 The Muencheberg Soil Quality Rating (SQR) FIELD MANUAL FOR DETECTING AND ASSESSING PROPERTIES AND LIMITATIONS OF SOILS FOR CROPPING AND GRAZING Lothar Mueller, Uwe Schindler, Axel Behrendt, Frank Eulenstein & Ralf Dannowski Leibniz-Centre for Agricultural Landscape Research (ZALF) e. V., Muencheberg, Germany with contributions of Sandro L. Schlindwein, University of St. Catarina, Florianopolis, Brasil T. Graham Shepherd, Nutri-Link, Palmerston North, New Zealand Elena Smolentseva, Russian Academy of Sciences, Institute of Soil Science and Agrochemistry (ISSA), Novosibirsk, Russia Jutta Rogasik, Federal Agricultural Research Centre (FAL), Institute of Plant Nutrition and Soil Science, Braunschweig, Germany 2 TABLE OF CONTENTS PAGE 1. Objectives 4 2. Concept 5 3. Procedure and scoring tables 7 3.1. Field procedure 7 3.2. Scoring of basic indicators 10 3.2.0. What are basic indicators? 10 3.2.1. Soil substrate 12 3.2.2. Depth of A horizon or depth of humic soil 14 3.2.3. Topsoil structure 15 3.2.4. Subsoil compaction 17 3.2.5. Rooting depth and depth of biological activity 19 3.2.6. -
Caracterización Fisicoquímica De Un Calcisol Bajo
Revista Mexicana de Ciencias Forestales Vol. 9 (49) DOI: https://doi.org/10.29298/rmcf.v9i49.153 Artículo Caracterización fisicoquímica de un Calcisol bajo diferentes sistemas de uso de suelo en el noreste de México Physicochemical characterization of a Calcisol under different land -use systems in Northeastern Mexico Israel Cantú Silva1*, Karla E. Díaz García1, María Inés Yáñez Díaz1, 1 1 Humberto González Rodríguez y Rodolfo A. Martínez Soto Abstract: Changes in land use cause variations in the physicochemical characteristics of soil. The present study aims to quantify the changes in the physicochemical characteristics of a Calcisol in three land uses in the Northeast of Mexico: Native Vegetation Area (AVN), Cropland Area (AA) and Pasture Area (ASP). Four composite soil samples were taken at 0-5 and 5-30 cm depth from each land- use plot. The variables bulk density, texture, mechanical resistance to penetration, organic matter, pH and electric conductivity were determined. The analysis of variance showed differences in the organic matter with values of 4.2 % for AVN, 2.08 % for ASP and 1.19 % and for AA in the depth 0-5 cm. The texture was clay loam for AA, silty loam for ASP and loam for AVN showing differences. The soil under the three types of land -use presented low salinity (70.2 to 396.0 µS cm-1) showing differences at both depths. The soil hardness showed differences (p≤0.05) between plots. The AA showed lower values (0.78 kg cm- 2), contrasting with the values obtained for ASP (2.98 kg cm-2) and AVN (3.10 kg cm-2). -
Improving Soil and Soil Functions
IMPROVING SOIL AND SOIL FUNCTIONS BAMPA FRANCESCA AND CREAMER RACHEL (WUR) AGRIRESEARCH CONFERENCE, INNOVATING FOR THE FUTURE OF FARMING AND RURAL COMMUNITIES BRUXELLES, 3RD MAY 2018 This project has received funding from the European Union’s Horizon 2020 research and innovation programme under grant agreement No 635201. SOILS ARE A FINITE RESOURCE compaction loss of biodiversity salinisation loss of organic matter flooding contamination landslides erosion sealing ...FROM THREATS TO FUNCTIONS 2 www.landmark2020.eu email [email protected] twitter @Landmark2020 02/05/2018 DEMANDS ON OUR LAND How do we increase our productivity? I want to grow my milk output by 50% DEMANDS ON OUR LAND 3 www.landmark2020.eu email [email protected] twitter @Landmark2020 02/05/2018 DEMANDS ON OUR LAND We need better water regulation by our land… 4 www.landmark2020.eu email [email protected] twitter @Landmark2020 02/05/2018 DDEMANDSEMANDS ONONOUROURLANDLAND We need to protect our We need to sequester carbon resources carbon 5 www.landmark2020.eu email [email protected] twitter @Landmark2020 02/05/2018 DEMANDS ON OUR LAND We need to find a home for our waste… 6 www.landmark2020.eu email [email protected] twitter @Landmark2020 02/05/2018 DEMANDS ON OUR LAND Soil biodiversity is the driver of many processes in soils Protect the home of biodiversity Lijbert Brussaard WHAT CAN OUR LAND SUPPLY? Water Provision Primary and purification Production Carbon sequestration Nutrient Cycling Habitat for biodiversity All soils / land perform all functions …but different parts of the land(scape) are better at delivering different functions Schulte et al., 2014 More info - interactive glossary http://landmark2020.eu/landmark-glossary/ 8 www.landmark2020.eu email [email protected] twitter @Landmark2020 02/05/2018 LAND MANAGEMENT: ASSESSMENT, RESEARCH, KNOWLEDGE BASE Objective: to quantify the supply of soil functions across the EU as determined by soil properties, land use and soil management practices. -
Soil Organic Carbon Storage As a Key Function of Soils
Geoderma 333 (2019) 149–162 Contents lists available at ScienceDirect Geoderma journal homepage: www.elsevier.com/locate/geoderma Soil organic carbon storage as a key function of soils - A review of drivers and indicators at various scales T ⁎ Martin Wiesmeiera,b, , Livia Urbanskia, Eleanor Hobleya, Birgit Langc, Margit von Lützowa, Erika Marin-Spiottad, Bas van Wesemaele, Eva Rabotf, Mareike Ließf, Noelia Garcia-Francoa, Ute Wollschlägerf, Hans-Jörg Vogelf, Ingrid Kögel-Knabnera,g a Chair of Soil Sciences, TUM School of Life Sciences Weihenstephan, Technical University of Munich, Freising, Germany b Bavarian State Research Center for Agriculture, Institute for Organic Farming, Soil and Resource Management, Freising, Germany c Senckenberg Museum of Natural History Görlitz, Görlitz, Germany d Department of Geography, University of Wisconsin-Madison, 550 North Park Street, Madison, WI 53706, USA e Georges Lemaître Centre for Earth and Climate Research, Earth and Life Institute, Université Catholique de Louvain, 1348 Louvain-la-Neuve, Belgium f Helmholtz Centre for Environmental Research - UFZ, Halle, Germany g Institute for Advanced Study, Technical University of Munich, Garching, Germany ARTICLE INFO ABSTRACT Handling Editor: Junhong Bai The capacity of soils to store organic carbon represents a key function of soils that is not only decisive for climate ff ff Keywords: regulation but also a ects other soil functions. Recent e orts to assess the impact of land management on soil Clay mineralogy functionality proposed that an indicator- or proxy-based approach is a promising alternative to quantify soil Specific surface area functions compared to time- and cost-intensive measurements, particularly when larger regions are targeted. The Metal oxides objective of this review is to identify measurable biotic or abiotic properties that control soil organic carbon Microorganisms (SOC) storage at different spatial scales and could serve as indicators for an efficient quantification of SOC. -
GYPSISOLS, DURISOLS, and CALCISOLS
GYPSISOLS, DURISOLS, and CALCISOLS Otto Spaargaren ISRIC – World Soil Information Wageningen The Netherlands Definition of Gypsisols Soils having z A gypsic or petrogypsic horizon within 100cm from the soil surface z No diagnostic horizons other than an ochric or cambic horizon, an argic horizon permeated with gypsum or calcium carbonate, a vertic horizon, or a calcic or petrocalcic horizon underlying the gypsic or petrogypsic horizon Gypsic horizon Results from accumulation of secondary gypsum (CaSO4.2H2O). It contains ≥ 15 percent gypsum (if ≥ 60 percent gypsum, horizon is called hypergypsic), and has a thickness of at least 15cm. Petrogypsic horizon The petrogypsic horizon z contains ≥ 60 percent gypsum z is cemented to the extent that dry fragments do not slake in water and the horizon cannot be penetrated by roots z has a thickness of 10cm or more Genesis of Gypsisols Main soil-forming factor is: Arid climate Main soil-forming process is: – Precipitation of gypsum from the soil solution when this evaporates. Most Gypsisols are associated with sulphate-rich groundwater that moves upward in the soil through capillary action and evaporates at the surface. Classification of Gypsisols (1) z Strong expression qualifiers: hypergypsic and petric z Intergrade qualifiers: calcic, duric, endosalic, leptic, luvic, and vertic z Secondary characteristics qualifiers, related to defined diagnostic horizons, properties or materials: aridic, hyperochric, takyric, and yermic Classification of Gypsisols (2) z Secondary characteristics qualifiers, not related to defined diagnostic horizons, properties or materials: arzic, skeletic, and sodic z Haplic qualifier, where non of the above applies: haplic Example of a Gypsisol (1) Yermi-Calcic Gypsisol (Endoskeletic and Sodic), Israel 0-2cm 2-6cm 6-21cm 21-38cm 38-50cm % gypsum 50-78cm % CaCO3 78-94cm 94-126cm 126-150cm 020406080 % Example of a Gypsisol (2) Yermi-Epipetric Gypsisol, Namibia Distribution of Gypsisols (1) Distribution of Gypsisols (2) Gypsisols cover some 100M ha or 0.7 % of the Earth’s land surface. -
Guides for Educators (May 2014) Soil Organic Matter (SOM)
Soil organic matter (SOM) is necessary for all soil functions, and it is the most important indicator of soil health. It is the organic component of soil. It consists of varying proportions of small plant residue (fresh), small living soil organisms, decomposing (active) organic matter, and stable organic matter (humus) in varying stages (fig. 1). SOM is a mineralizable source of nutrients for crops. It increases the availability of most nutrients, buffers the effects of high acidity, increases the available water capacity and moisture retention of the soil, helps to minimize compaction and surface crusting, increases water infiltration, provides food for micro-organisms that facilitate the availability of nutrients, holds soil aggregates together, decomposes pesticides, and acts as a carbon sink. The content of SOM can be estimated in the field and/or in a lab. The results can be used to estimate the amount of mineralized nitrogen, phosphorus, and sulfur available for crop production, which is needed to determine the appropriate application of fertilizers. As SOM increases, the buffering capacity of the soil also increases. Thus, the amount of surface-applied herbicides needed to effectively control weeds increases, the potential for herbicide carryover for future crops decreases, and the amount of lime needed to raise pH increases. Figure 1.—Major components of soil organic matter (Source: Soil Food Web; USDA, NRCS). Page 1 Guides for Educators (May 2014) Soil Health – Organic Matter USDA-NRCS Inherent Factors Affecting Soil Organic Matter Inherent factors affecting soil organic matter Both the top growth and roots of grass include climate and soil texture and clay vegetation dies continually each growing mineralogy. -
Soil Wind Erosion in Ecological Olive Trees in the Tabernas Desert (Southeastern Spain): a Wind Tunnel Experiment
Solid Earth, 7, 1233–1242, 2016 www.solid-earth.net/7/1233/2016/ doi:10.5194/se-7-1233-2016 © Author(s) 2016. CC Attribution 3.0 License. Soil wind erosion in ecological olive trees in the Tabernas desert (southeastern Spain): a wind tunnel experiment Carlos Asensio1, Francisco Javier Lozano1, Pedro Gallardo1, and Antonio Giménez2 1Departamento de Agronomía, CEIA3, Campus de Excelencia Internacional en Agroalimentación, Universidad de Almería, Almería, Spain 2Departamento de Ingeniería, Universidad de Almería, Almería, Spain Correspondence to: Carlos Asensio ([email protected]) Received: 12 April 2016 – Published in Solid Earth Discuss.: 29 April 2016 Revised: 27 July 2016 – Accepted: 28 July 2016 – Published: 22 August 2016 Abstract. Wind erosion is a key component of the soil degra- by other authors for Spanish soils. As the highest loss was dation processes. The purpose of this study is to find out the found in Cambisols, mainly due to the effect on soil crusting influence of material loss from wind on soil properties for and the wind-erodible fraction aggregation of CaCO3, a Ste- different soil types and changes in soil properties in olive via rebaudiana cover crop was planted between the rows in groves when they are tilled. The study area is located in the this soil type and this favored retention of particles in vege- north of the Tabernas Desert, in the province of Almería, tation. southeastern Spain. It is one of the driest areas in Europe, with a semiarid thermo-Mediterranean type of climate. We used a new wind tunnel model over three different soil types (olive-cropped Calcisol, Cambisol and Luvisol) and studied 1 Introduction micro-plot losses and deposits detected by an integrated laser scanner.