Methods of Analysis Soil Sampling
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Simple Soil Tests for On-Site Evaluation of Soil Health in Orchards
sustainability Article Simple Soil Tests for On-Site Evaluation of Soil Health in Orchards Esther O. Thomsen 1, Jennifer R. Reeve 1,*, Catherine M. Culumber 2, Diane G. Alston 3, Robert Newhall 1 and Grant Cardon 1 1 Dept. Plant Soils and Climate, Utah State University, Logan, UT 84322, USA; [email protected] (E.O.T.); [email protected] (R.N.); [email protected] (G.C.) 2 UC Cooperative Extension, Fresno, CA 93710, USA; [email protected] 3 Dept. Biology, Utah State University, Logan, UT 84322, USA; [email protected] * Correspondence: [email protected] Received: 20 September 2019; Accepted: 26 October 2019; Published: 29 October 2019 Abstract: Standard commercial soil tests typically quantify nitrogen, phosphorus, potassium, pH, and salinity. These factors alone are not sufficient to predict the long-term effects of management on soil health. The goal of this study was to assess the effectiveness and use of simple physical, biological, and chemical soil health indicator tests that can be completed on-site. Analyses were conducted on soil samples collected from three experimental peach orchards located on the Utah State Horticultural Research Farm in Kaysville, Utah. All simple tests were correlated to comparable lab analyses using Pearson’s correlation. The highest positive correlations were found between Solvita®respiration, and microbial biomass (R = 0.88), followed by our modified slake test and microbial biomass (R = 0.83). Both Berlese funnel and pit count methods of estimating soil macro-organism diversity were fairly predictive of soil health. Overall, simple commercially available chemical tests were weak indicators of soil nutrient concentrations compared to laboratory tests. -
Tillage and Soil Ecology: Partners for Sustainable Agriculture
Soil & Tillage Research 111 (2010) 33–40 Contents lists available at ScienceDirect Soil & Tillage Research journal homepage: www.elsevier.com/locate/still Review Tillage and soil ecology: Partners for sustainable agriculture Jean Roger-Estrade a,b,*, Christel Anger b, Michel Bertrand b, Guy Richard c a AgroParisTech, UMR 211 INRA/AgroParisTech., Thiverval-Grignon, 78850, France b INRA, UMR 211 INRA/AgroParisTech. Thiverval-Grignon, 78850, France c INRA, UR 0272 Science du sol, Centre de recherche d’Orle´ans, Orle´ans, 45075, France ARTICLE INFO ABSTRACT Keywords: Much of the biodiversity of agroecosystems lies in the soil. The functions performed by soil biota have Tillage major direct and indirect effects on crop growth and quality, soil and residue-borne pests, diseases Soil ecology incidence, the quality of nutrient cycling and water transfer, and, thus, on the sustainability of crop Agroecosystems management systems. Farmers use tillage, consciously or inadvertently, to manage soil biodiversity. Soil biota Given the importance of soil biota, one of the key challenges in tillage research is understanding and No tillage Plowing predicting the effects of tillage on soil ecology, not only for assessments of the impact of tillage on soil organisms and functions, but also for the design of tillage systems to make the best use of soil biodiversity, particularly for crop protection. In this paper, we first address the complexity of soil ecosystems, the descriptions of which vary between studies, in terms of the size of organisms, the structure of food webs and functions. We then examine the impact of tillage on various groups of soil biota, outlining, through examples, the crucial effects of tillage on population dynamics and species diversity. -
Soil Testing Can Help Nutrient Deficiencies Or Imbalances
Do You Have Problems With: • Nutrient deficiencies in crops • Poor plant growth and response from applied fertilizers • Hard to manage weeds • Low crop yields • Poor quality forages • Irregular plant growth in your fields • Managing manure or compost applications Soil tests help to identify production problems related to Soil Testing Can Help nutrient deficiencies or imbalances. Above: Nitrogen defi- ciency in corn (photo: Ryan Stoffregen, Illinois). Below: Phosphorus deficiency in corn. Source: www.ipni.net Benefits of Soil Testing: • Determines nutrient levels in the soil • Determines pH levels (lime needs) • Provides a decision making tool to determine what nutrients to apply and how much • Potential for higher yielding crops • Potential for higher quality crops • More efficient fertilizer use Costs: Generally soil tests cost $7 to $10.00 per sample. The costs of soil tests vary depending on: 1. Your state (some states offer free soil testing) 2. The lab that is used. 3. The items being tested for (the cost increases as more nutrients are being analyzed). NOTE: Some state agencies and land grant universities provide free soil testing for the basic soil test items (pH, available phosphorus, potassium, calcium, and magnesium, and organic matter). Additional costs may be charged for testing for micronutrients. In other states, all soil testing is done by private labs and generally charge $7-$10 for the basic test. One soil test should be taken for each field, or for each 20 acres within a field. See example on page 3. Soil Testing How Often Should I Soil Test? Generally, you should soil test every 3-5 years or more often if manure is applied or you are trying to make large nutrient or pH changes in the soil. -
Soil Ecology
LSC 322 Laboratory 10 LAB #10: SOIL ECOLOGY Soil is one of the earth’s most important resources. For a community of plants and animals to become established on land, soil must first be present. Further, soil quality is often a limiting factor for growth many systems. Soil is a complex mixture of inorganic and organic materials, microorganisms, water and air. The weathering of bedrock produces small grains of rock that accumulate as a layer on the surface of the earth. There they are altered by biology, becoming mixed with organic matter, which results from the decomposition of the waste products and dead tissue of living organisms to form humus. The soil formation process is very slow (hundreds to thousands of years), so it can be very detrimental to a community if the soil is lost through erosion or its quality degraded by pollution or misuse. Soil Sampling As a class, we will identify interesting soil ecosystems on campus that we would like to examine further. Your small group will be assigned to collect one of those samples. Using a trowel, you will scoop the top 5 cm (this is where most of the biological “action” happens) into a ziplock bag. Also, take notes to record the environmental surroundings. What is the land usage? What plants are growing here? What is the soil moisture? These environmental characteristics will influence many aspects of the soil. Questions - Describe the environment from which you took your soil sample. Include all of the information from your notes. - How do these conditions relate to the soil characteristics measured during the lab exercise (texture, nutrients, pH, and biota)? After samples are collected, we will return to the lab and measure the following characteristics: Soil Texture Soil texture refers to the proportion of sand, silt, and clay present in a soil, which differ in their particle size. -
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. -
Dynamics of Soil Nitrogen and Carbon Accumulation for 61 Years After Agricultural Abandonment
Ecology, 81(1), 2000, pp. 88±98 q 2000 by the Ecological Society of America DYNAMICS OF SOIL NITROGEN AND CARBON ACCUMULATION FOR 61 YEARS AFTER AGRICULTURAL ABANDONMENT JOHANNES M. H. KNOPS1 AND DAVID TILMAN Department of Ecology, Evolution and Behavior, University of Minnesota, St. Paul, Minnesota 55108 USA Abstract. We used two independent methods to determine the dynamics of soil carbon and nitrogen following abandonment of agricultural ®elds on a Minnesota sand plain. First, we used a chronosequence of 19 ®elds abandoned from 1927 to 1982 to infer soil carbon and nitrogen dynamics. Second, we directly observed dynamics of carbon and nitrogen over a 12-yr period in 1900 permanent plots in these ®elds. These observed dynamics were used in a differential equation model to predict soil carbon and nitrogen dynamics. The two methods yielded similar results. Resampling the 1900 plots showed that the rates of accumulation of nitrogen and carbon over 12 yr depended on ambient carbon and nitrogen levels in the soil, with rates of accumulation declining at higher carbon and nitrogen levels. A dynamic model ®tted to the observed rates of change predicted logistic dynamics for nitrogen and carbon accumulation. On average, agricultural practices resulted in a 75% loss of soil nitrogen and an 89% loss of soil carbon at the time of abandonment. Recovery to 95% of the preagricultural levels is predicted to require 180 yr for nitrogen and 230 yr for carbon. This model accurately predicted the soil carbon, nitrogen, and carbon : nitrogen ratio patterns observed in the chronosequence of old ®elds, suggesting that the chronose- quence may be indicative of actual changes in soil carbon and nitrogen. -
Soil Test Handbook for Georgia
SOIL TEST HANDBOOK FOR GEORGIA Georgia Cooperative Extension College of Agricultural & Environmental Sciences The University of Georgia Athens, Georgia 30602-9105 EDITORS: David E. Kissel Director, Agricultural and Environmental Services Laboratories & Leticia Sonon Program Coordinator, Soil, Plant, & Water Laboratory The University of Georgia and Ft. Valley State University, the U.S. Department of Agriculture and counties of the state cooperating. The Cooperative Extension, the University of Georgia College of Agricultural and Environmental Sciences offers educational programs, assistance and materials to all people without regard to race, color, national origin, age, sex or disability. An Equal Opportunity Employer/Affirmative Action Organization Committed to a Diverse Work Force Issued in furtherance of Cooperative Extension work, Acts of May 8 and June 30, 1914, The University of Georgia College of Agricultural and Environmental Sciences and the U.S. Department of Agriculture cooperating. Dr. Scott Angle, Dean and Director Special Bulletin 62 September 2008 i TABLE OF CONTENTS INTRODUCTION .......................................................................................................................................................2 SOIL TESTING...........................................................................................................................................................4 SOIL SAMPLING .......................................................................................................................................................4 -
Addressing Pasture Compaction
Addressing Pasture Compaction Weighing the Pros and Cons of Two Options UVM Project team: Dr. Josef Gorres, Dr. Rachel Gilker, Jennifer Colby, Bridgett Jamison Hilshey Partners: Mark Krawczyk (Keyline Vermont) and farmers Brent & Regina Beidler, Guy & Beth Choiniere, John & Rocio Clark, Lyle & Kitty Edwards, and Julie Wolcott & Stephen McCausland Writing: Josef Gorres, Rachel Gilker and Jennifer Colby • Design and Layout: Jennifer Colby • Photos: Jennifer Colby and Rachel Gilker Additional editing by Cheryl Herrick and Bridgett Jamison Hilshey Th is is dedicated to our farmer partners; may our work help you farm more productively, profi tably, and ecologically. VT Natural Resources Conservation Service UVM Center for Sustainable Agriculture http://www.vt.nrcs.usda.gov http://www.uvm.edu/sustainableagriculture UVM Plant & Soil Science Department http://pss.uvm.edu Financial support for this project and publication was provided through a VT Natural Resources Conservation Service (NRCS) Conservation Innovation Grant (CIG). We thank VT-NRCS for their eff orts to build a 2 strong natural resource foundation for Vermont’s farming systems. Introduction A few years ago, some grass-based dairy farmers came to us with the question, “You know, what we really need is a way to fi x the compaction in pastures.” We started digging for answers. Th is simple request has led us on a lively journey. We began by adapting methods to alleviate compac- tion in other climates and cropping systems. We worked with fi ve Vermont dairy farmers to apply these practices to their pastures, where other farmers could come and observe them in action. We assessed the pros and cons of these approaches and we are sharing those results and observations here. -
Fundamentals in Soil Science Course a Course Offered by the Soil Science Society of America
Fundamentals in Soil Science Course A course offered by the Soil Science Society of America. This course is divided into six modules: Fundamentals of Soil Genesis, Classification, and Morphology, Fundamentals in Soil Chemistry and Mineralogy, Fundamentals in Soil Fertility and Nutrient Management, Soil Biology and Soil Ecology, Influences and Management of Soil Physical Properties and Soil and Land Use Management. Each module contains 2 lessons. Lectures are approximately two hours. To maximize learning, students will be expected to spend time reading and studying outside of the recorded lesson. Course Description The Soil Science Fundamentals Review Course is designed to provide an overview of the fundamental concepts in soil science: Genesis, Classification and Morphology, Physics, Chemistry, Fertility, Biology, and Land Use. Instructors will use the Fundamentals Performance Objectives (POs) as a guide for discussing topics within each section, but will not go through each objective individually. However, students are encouraged to ask questions regarding specific POs if needed. The objective of the course is to provide the student with a formalized way to build their fundamental knowledge and skills within the different areas of soil science to enhance their professional skills and/or to prepare to take the Fundamentals of Soil Science Exam. Lecture material is supplemented with additional readings and practical examples to illustrate the concepts and provide practical examples of how the concepts are used in practice. This course is not designed to teach a student how to take the Fundamentals Exam, but instead is designed to complement the students existing knowledge of soil science and help the student understand the principles behind the POs. -
Unit 2.3, Soil Biology and Ecology
2.3 Soil Biology and Ecology Introduction 85 Lecture 1: Soil Biology and Ecology 87 Demonstration 1: Organic Matter Decomposition in Litter Bags Instructor’s Demonstration Outline 101 Step-by-Step Instructions for Students 103 Demonstration 2: Soil Respiration Instructor’s Demonstration Outline 105 Step-by-Step Instructions for Students 107 Demonstration 3: Assessing Earthworm Populations as Indicators of Soil Quality Instructor’s Demonstration Outline 111 Step-by-Step Instructions for Students 113 Demonstration 4: Soil Arthropods Instructor’s Demonstration Outline 115 Assessment Questions and Key 117 Resources 119 Appendices 1. Major Organic Components of Typical Decomposer 121 Food Sources 2. Litter Bag Data Sheet 122 3. Litter Bag Data Sheet Example 123 4. Soil Respiration Data Sheet 124 5. Earthworm Data Sheet 125 6. Arthropod Data Sheet 126 Part 2 – 84 | Unit 2.3 Soil Biology & Ecology Introduction: Soil Biology & Ecology UNIT OVERVIEW MODES OF INSTRUCTION This unit introduces students to the > LECTURE (1 LECTURE, 1.5 HOURS) biological properties and ecosystem The lecture covers the basic biology and ecosystem pro- processes of agricultural soils. cesses of soils, focusing on ways to improve soil quality for organic farming and gardening systems. The lecture reviews the constituents of soils > DEMONSTRATION 1: ORGANIC MATTER DECOMPOSITION and the physical characteristics and soil (1.5 HOURS) ecosystem processes that can be managed to In Demonstration 1, students will learn how to assess the improve soil quality. Demonstrations and capacity of different soils to decompose organic matter. exercises introduce students to techniques Discussion questions ask students to reflect on what envi- used to assess the biological properties of ronmental and management factors might have influenced soils. -
Soil Salinity in Agricultural Systems: the Basics
Soil Salinity in Agricultural Systems: The Basics Jeffrey L. Ullman Agricultural & Biological Engineering University of Florida Strategies for Minimizing Salinity Problems and Optimizing Crop Production In-Service Training, Hastings, FL March 26, 2013 What is salt? What is Salt? . Salts are more than just sodium chloride (NaCl) . Salts consist of anions and cations . In terms of soil and irrigation water these generally include: Cations Anions Sodium Na+ Chlorides Cl- 2+ 2- Magnesium Mg Sulfates SO4 2+ 2- Calcium Ca Carbonates CO3 - Bicarbonates HCO3 What is Salt? . Other salts in agriculture + Potassium (K ) - Nitrate (NO3 ) Boron (B) • Often as boric acid (H3BO3, often written as B(OH)3) • Can form salts such as sodium borate (borax; Na2B4O7) Photo: Georgia Agriculture What is Salt? H O(l) NaCl(s) 2 Na+(aq) + Cl-(aq) (aq) indicates that Na+ and Cl- are hydrated ions Sodium sulfate Magnesium carbonate Source: Averill and Eldredge (2007) Types of Salts Some common salts NaCl Sodium chloride Table salt (halite) CO 2- 3 KCl Potassium chloride Muriate of potash Na+ 2- NaHCO3 Sodium bicarbonate Baking soda (nahcolite) SO4 - Cl CaSO4 Calcium sulfate Gypsum + K CaCO3 Calcium carbonate Calcite 2+ Ca MgSO Magnesium sulfate Epsom salt (epsomite) Mg2+ 4 K2SO4 Potassium sulfate Sulfate of potash (arcanite) HCO - 3 Glauber’s salt (thenardite Na SO Sodium sulfate 2 4 and mirabilite) Gypsum Calcite Thenardite Sources of Salt . Dissolution of parent rock material . Irrigation water . Saline groundwater . Fertilizers . Manure . Seawater intrusion Photo: J. Ullman Saline Soils . Accumulation of salts known as salination . Can occur in diverse types of soil with different physical, chemical and hydrologic properties Photo: USDA-NRCS Saline Soils . -
Articles, and the Creation of New Soil Habitats in Other Scientific fields Who Also Made Early Contributions Through the Weathering of Rocks (Puente Et Al., 2004)
Editorial SOIL, 1, 117–129, 2015 www.soil-journal.net/1/117/2015/ doi:10.5194/soil-1-117-2015 SOIL © Author(s) 2015. CC Attribution 3.0 License. The interdisciplinary nature of SOIL E. C. Brevik1, A. Cerdà2, J. Mataix-Solera3, L. Pereg4, J. N. Quinton5, J. Six6, and K. Van Oost7 1Department of Natural Sciences, Dickinson State University, Dickinson, ND, USA 2Departament de Geografia, Universitat de València, Valencia, Spain 3GEA-Grupo de Edafología Ambiental , Departamento de Agroquímica y Medio Ambiente, Universidad Miguel Hernández, Avda. de la Universidad s/n, Edificio Alcudia, Elche, Alicante, Spain 4School of Science and Technology, University of New England, Armidale, NSW 2351, Australia 5Lancaster Environment Centre, Lancaster University, Lancaster, UK 6Department of Environmental Systems Science, Swiss Federal Institute of Technology, ETH Zurich, Tannenstrasse 1, 8092 Zurich, Switzerland 7Georges Lemaître Centre for Earth and Climate Research, Earth and Life Institute, Université catholique de Louvain, Louvain-la-Neuve, Belgium Correspondence to: J. Six ([email protected]) Received: 26 August 2014 – Published in SOIL Discuss.: 23 September 2014 Revised: – – Accepted: 23 December 2014 – Published: 16 January 2015 Abstract. The holistic study of soils requires an interdisciplinary approach involving biologists, chemists, ge- ologists, and physicists, amongst others, something that has been true from the earliest days of the field. In more recent years this list has grown to include anthropologists, economists, engineers, medical professionals, military professionals, sociologists, and even artists. This approach has been strengthened and reinforced as cur- rent research continues to use experts trained in both soil science and related fields and by the wide array of issues impacting the world that require an in-depth understanding of soils.