Effects of Soil Erosion on Soil Productivity and Soil Quality
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Effects of Erosion Control Practices on Nutrient Loss
Effects of Erosion Control Practices on Nutrient Loss George F. Czapar, University of Illinois John M. Laflen, Iowa State University Gregory F. McIsaac, University of Illinois Dennis P. McKenna, Illinois Department of Agriculture Elements of Soil Erosion Soil erosion by water is the detachment of soil particles by the direct action of raindrops and runoff water, and the transport of these particles by splash and very shallow flowing water to small channels or rills. Detachment of soil particles also occurs in these rills due to the force exerted by the flowing water. When rills join together and form larger channels, they may become gullies. These gullies can be either temporary (ephemeral) or permanent (classical). Non-erodible channels might be grassed waterways, or designed channels that limit flow conditions so that channel erosion does not occur. Gross erosion includes sheet, rill, gully and channel erosion, and is the first step in the process of sediment delivery. Because much eroded sediment is deposited in or near the field of origin, only a fraction of the total eroded soil from an area contributes to sediment yield from a watershed. Sediment delivery is affected by a number of factors including soil properties, proximity to the stream, man made structures-including sediment basins, fences, and culverts, channel density, basin characteristics, land use/land cover, and rainfall-runoff factors. Coarse- textured sediment and sediment from sheet and rill erosion are less likely to reach a stream than fine-grained sediment or sediment from channel erosion. In general, the larger the area, the lower the ratio of sediment yield at the watershed outlet or point of interest to gross erosion in the entire watershed, defined as the sediment delivery ratio (SDR). -
Agricultural Soil Compaction: Causes and Management
October 2010 Agdex 510-1 Agricultural Soil Compaction: Causes and Management oil compaction can be a serious and unnecessary soil aggregates, which has a negative affect on soil S form of soil degradation that can result in increased aggregate structure. soil erosion and decreased crop production. Soil compaction can have a number of negative effects on Compaction of soil is the compression of soil particles into soil quality and crop production including the following: a smaller volume, which reduces the size of pore space available for air and water. Most soils are composed of • causes soil pore spaces to become smaller about 50 per cent solids (sand, silt, clay and organic • reduces water infiltration rate into soil matter) and about 50 per cent pore spaces. • decreases the rate that water will penetrate into the soil root zone and subsoil • increases the potential for surface Compaction concerns water ponding, water runoff, surface soil waterlogging and soil erosion Soil compaction can impair water Soil compaction infiltration into soil, crop emergence, • reduces the ability of a soil to hold root penetration and crop nutrient and can be a serious water and air, which are necessary for water uptake, all of which result in form of soil plant root growth and function depressed crop yield. • reduces crop emergence as a result of soil crusting Human-induced compaction of degradation. • impedes root growth and limits the agricultural soil can be the result of using volume of soil explored by roots tillage equipment during soil cultivation or result from the heavy weight of field equipment. • limits soil exploration by roots and Compacted soils can also be the result of natural soil- decreases the ability of crops to take up nutrients and forming processes. -
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. -
Progressive and Regressive Soil Evolution Phases in the Anthropocene
Progressive and regressive soil evolution phases in the Anthropocene Manon Bajard, Jérôme Poulenard, Pierre Sabatier, Anne-Lise Develle, Charline Giguet- Covex, Jeremy Jacob, Christian Crouzet, Fernand David, Cécile Pignol, Fabien Arnaud Highlights • Lake sediment archives are used to reconstruct past soil evolution. • Erosion is quantified and the sediment geochemistry is compared to current soils. • We observed phases of greater erosion rates than soil formation rates. • These negative soil balance phases are defined as regressive pedogenesis phases. • During the Middle Ages, the erosion of increasingly deep horizons rejuvenated pedogenesis. Abstract Soils have a substantial role in the environment because they provide several ecosystem services such as food supply or carbon storage. Agricultural practices can modify soil properties and soil evolution processes, hence threatening these services. These modifications are poorly studied, and the resilience/adaptation times of soils to disruptions are unknown. Here, we study the evolution of pedogenetic processes and soil evolution phases (progressive or regressive) in response to human-induced erosion from a 4000-year lake sediment sequence (Lake La Thuile, French Alps). Erosion in this small lake catchment in the montane area is quantified from the terrigenous sediments that were trapped in the lake and compared to the soil formation rate. To access this quantification, soil processes evolution are deciphered from soil and sediment geochemistry comparison. Over the last 4000 years, first impacts on soils are recorded at approximately 1600 yr cal. BP, with the erosion of surface horizons exceeding 10 t·km− 2·yr− 1. Increasingly deep horizons were eroded with erosion accentuation during the Higher Middle Ages (1400–850 yr cal. -
What Is Soil Erosion? Soil Erosion by Wind Or Water Is the Physical Wearing Away of the Soil Surface
Do you have a problem with: • Low yields • Time & expense to repair and gullies • Small rills and channels in your fields • Soil deposited at the base of slopes or along fence lines • Sediment in streams, lakes, and reservoirs Soil Erosion May be the Problem! Erosion from cropland What is soil erosion? Soil erosion by wind or water is the physical wearing away of the soil surface. Soil material and nutrients are removed in the process. Why be concerned? • Erosion reduces crop yields • Erosion removes topsoil, reduces soil organic matter, and destroys soil structure Signs of Erosion – Sediment entering river • Erosion decreases rooting depth • Erosion decreases the amount of water, air, and nutrients available to plants • Nutrients and sediment removed by water erosion cause water quality problems and fish kills • Blowing dust from wind erosion can affect human health and create public safety hazards • Increased production costs Erosion removes our richest soil. How much does it cost? • Technical assistance to assess and plan erosion control systems from NRCS is free • No till and mulch till may require special tillage equipment or planters if this equipment is not al- ready available • Vegetative barriers may cost $50-$100 per mile of barrier • Cover crops may cost between $10 and $40 per acre depending on the type of seed used Controlling Soil Erosion Signs of Erosion – Small rills and channels on the soil Dust clouds & “dirt devils” such as the one pictured surface are a sign of water erosion here are signs of wind erosion. How to Reduce Erosion: The key to reducing is erosion is to keep the soil covered as much as possible for both wind and water ero- sion concerns. -
How Do Newly-Amended Biochar Particles Affect Erodibility and Soil Water Movement?—A Small-Scale Experimental Approach
Article How Do Newly-Amended Biochar Particles Affect Erodibility and Soil Water Movement?—A Small-Scale Experimental Approach Steffen Seitz * , Sandra Teuber , Christian Geißler, Philipp Goebes and Thomas Scholten Department of Geosciences, Soil Science and Geomorphology, University of Tübingen, Rümelinstrasse 19–23, 72070 Tübingen, Germany; [email protected] (S.T.); [email protected] (C.G.); [email protected] (P.G.); [email protected] (T.S.) * Correspondence: steff[email protected]; Tel.: +49-7071-29-77523 Received: 16 July 2020; Accepted: 23 September 2020; Published: 6 October 2020 Abstract: Biochar amendment changes chemical and physical properties of soils and influences soil biota. It is, thus, assumed that it can also affect soil erosion and erosion-related processes. In this study, we investigated how biochar particles instantly change erodibility by rain splash and the initial movement of soil water in a small-scale experiment. Hydrothermal carbonization (HTC)-char and Pyrochar were admixed to two soil substrates. Soil erodibility was determined with Tübingen splash cups under simulated rainfall, soil hydraulic conductivity was calculated from texture and bulk soil density, and soil water retention was measured using the negative and the excess pressure methods. Results showed that the addition of biochar significantly reduced initial soil erosion in coarse sand and silt loam immediately after biochar application. Furthermore, biochar particles were not preferentially removed from the substrate surface, but increasing biochar particle sizes partly showed decreasing erodibility of substrates. Moreover, biochar amendment led to improved hydraulic conductivity and soil water retention, regarding soil erosion control. In conclusion, this study provided evidence that biochar amendments reduce soil degradation by water erosion. -
A New Soil Quality Index (SQI) for Assessing Forest Soil Health
Soil Vital Signs: A New Soil Quality Index (SQI) for Assessing Forest Soil Health Michael C. Amacher, Katherine P. O’Neill, and Charles H. Perry May 2007 United States Forest Service Rocky Mountain Research Paper Department Research Station RMRS-RP-65WWW of Agriculture Amacher, Michael C.; O’Neil, Katherine P.; Perry, Charles H. 2007. Soil vital signs: A new Soil Quality Index (SQI) for assessing forest soil health. Res. Pap. RMRS-RP-65WWW. Fort Collins, CO: U.S. Department of Agriculture, Forest Service, Rocky Mountain Research Station. 12 p. Abstract __________________________________________ The Forest Inventory and Analysis (FIA) program measures a number of chemical and physical properties of soils to address specific questions about forest soil quality or health. We developed a new index of forest soil health, the soil quality index (SQI), that integrates 19 measured physical and chemical properties of forest soils into a single number that serves as the soil’s “vital sign” of overall soil quality. Regional and soil depth differences in SQI values due to differences in soil properties were observed. The SQI is a new tool for establishing baselines and detecting forest health trends. Keywords: forest soil health, Forest Inventory and Analysis, soil indicator database, soil quality index The Authors Michael C. Amacher is a research soil scientist with the Forest and Woodland Program Area at the Forestry Sciences Laboratory in Logan, UT. He holds a B.S. and a M.S. in chemistry and a Ph.D. in soil chemistry, all from The Pennsylvania State University. He joined the Rocky Mountain Research Station in 1989. -
Sustaining the Pedosphere: Establishing a Framework for Management, Utilzation and Restoration of Soils in Cultured Systems
Sustaining the Pedosphere: Establishing A Framework for Management, Utilzation and Restoration of Soils in Cultured Systems Eugene F. Kelly Colorado State University Outline •Introduction - Its our Problems – Life in the Fastlane - Ecological Nexus of Food-Water-Energy - Defining the Pedosphere •Framework for Management, Utilization & Restoration - Pedology and Critical Zone Science - Pedology Research Establishing the Range & Variability in Soils - Models for assessing human dimensions in ecosystems •Studies of Regional Importance Systems Approach - System Models for Agricultural Research - Soil Water - The Master Variable - Water Quality, Soil Management and Conservation Strategies •Concluding Remarks and Questions Living in a Sustainable Age or Life in the Fast Lane What do we know ? • There are key drivers across the planet that are forcing us to think and live differently. • The drivers are influencing our supplies of food, energy and water. • Science has helped us identify these drivers and our challenge is to come up with solutions Change has been most rapid over the last 50 years ! • In last 50 years we doubled population • World economy saw 7x increase • Food consumption increased 3x • Water consumption increased 3x • Fuel utilization increased 4x • More change over this period then all human history combined – we are at the inflection point in human history. • Planetary scale resources going away What are the major changes that we might be able to adjust ? • Land Use Change - the world is smaller • Food footprint is larger (40% of land used for Agriculture) • Water Use – 70% for food • Running out of atmosphere – used as as disposal for fossil fuels and other contaminants The Perfect Storm Increased Demand 50% by 2030 Energy Climate Change Demand up Demand up 50% by 2030 30% by 2030 Food Water 2D View of Pedosphere Hierarchal scales involving soil solid-phase components that combine to form horizons, profiles, local and regional landscapes, and the global pedosphere. -
Global Status, Processes and Trends in Soil Erosion
Status of the World’s Main Report Soil Resources Chapter 6 Global soil status, processes and trends © FAO | Giuseppe Bizzarri © FAO INTERGOVERNMENTAL TECHNICAL PANEL ON SOILS Disclaimer and copyright Recommended citation: FAO and ITPS. 2015. Status of the World’s Soil Resources (SWSR) – Main Report. Food and Agriculture Organization of the United Nations and Intergovernmental Technical Panel on Soils, Rome, Italy 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. ISBN 978-92-5-109004-6 © FAO, 2015 FAO encourages the use, reproduction and dissemination of material in this information product. Except where otherwise indicated, material may be copied, downloaded and printed for private study, research and teaching purposes, or for use in non-commercial products or services, provided that appropriate acknowledgement of FAO as the source and copyright holder is given and that FAO’s endorsement of users’ views, products or services is not implied in any way. -
Soil Erosion
Soil erosion Soil erosion in sloping agricultural land in Tunisia. Photolibrary on soil erosion processes. The most serious form of soil degradation is from accelerated erosion. Erosion is the washing or blowing away of surface soil, sometimes down to the bedrock. While some erosion takes place without the influence of man, the soil is lost so slowly that it is usually replaced through natural processes of decay and regeneration so soil loss and creation of new soil are balanced. What keeps soil in a natural state from eroding is vegetation. Undisturbed by man, soil is usually covered by a canopy of shrubs and trees, by dead and decaying leaves or by a thick mat of grass. Whatever the vegetation, it protects the soil when the rain falls or the wind blows. The leaves and branches of trees and the cushion of grass absorb the force of raindrops, and root systems of plants hold the soil together. Even in drought, the roots of native grasses, which extend several metres into the ground, help tie down the soil and keep it from blowing away. With its covering of vegetation stripped away, however, soil is as vulnerable to damage as a tortoise without its shell. Whether the plant cover is disturbed by cultivation, grazing, burning, or bulldozing, once the soil is laid bare to the erosive action of wind and water, the slow rate of natural erosion is greatly accelerated. Losses of soil take place much faster than new soil can be created, and a kind of deficit spending begins with the topsoil. -
Soil Quality 1
START FARMINGSOIL QUALITY 1 introduction to soils Soil Quality Culman Steve ealthy soils yield healthy crops, But what is healthy soil and how do we Healthy, high-quality soil has: Hachieve it? • Good soil tilth • Sufficient depth Soil health is the foundation of productive farming practices. Fertile soil provides essential nutrients to • Sufficient, but not excessive, nutrient supply plants. Important physical characteristics of soil-like • Small population of plant pathogens and insect structures and aggregation allow water and air to pests infiltrate, roots to explore, and biota to thrive. Diverse • Good soil drainage and active biological communities help soil resist • Large population of beneficial organisms physical degradation and cycle nutrients at rates to • Low weed pressure meet plant needs. Soil health and soil quality are terms • No chemicals or toxins that may harm the crop used interchangeably to describe soils that are not • Resilience to degradation and unfavorable only fertile but also possess adequate physical and conditions biological properties to “sustain productivity, maintain —from Soil Health Training Manual environmental quality and promote plant and animal health” (Doron 1994). According to the (USDA) Natural Resource Remember, soil fertility is only one component Conservation Service, “Soil quality is how well soil does of soil quality. Fertile soils are able to provide the what we want it to do.” In order to grow our crops, we nutrients required for plant growth. These are the want the soil to hold water and nutrients like a sponge chemical components of soil. Some plants need certain where they are readily available for plant roots to take nutrients in large amounts, like nitrogen, phosphorus, them up, suppress pests and weeds that may attack and potassium, which are called macronutrients. -
Manual on Integrated Soil Management and Conservation Practices Iii
Manual on integrated soil management and conservation practices iii Foreword The processes of land erosion in various regions of Latin America and Africa have their origin in social, economic and cultural factors that translate into the over-exploitation of the natural resources and the application of inadequate practices for the management of soils and water. The consequences of this are damage to much of the agricultural land, with detrimental effects on food production for the growing population in these continents. Over the last few decades, many efforts have been made to stop the degradation of agricultural land but the process of adoption of new conservationist technologies by the farmers is still slow. Furthermore, the availability of technical personnel trained for this change is limited. The technological strategies that have been developed for the management and conservation of soil and water sometimes are not adapted for the beneficiaries, because they could not participate in the processes of the diagnosis, planning and execution of the actions. In addition, the promotion of conservation tillage systems and practices that were not adapted to specific regional requirements has created credibility problems with the farmers probably since they had been developed in other places and introduced without a correct diagnosis of the local situation. The development of technologies that guarantee the maintenance of agricultural land productivity in Latin America and Africa is a challenge that both technicians and farmers must face through collaborative research and field work in the farmers’ own environments and conditions. This includes identification of the problems of management and conservation of soils and water and a greater emphasis on the evaluation of the potential for systems of conservation tillage adapted to the specific conditions of each region.