Pedogenesis and Soil Forming Factors - Antonie Veldkamp
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Keynote: Soil Conservation for C Sequestration R
This paper was not peer-reviewed. Pages 459-465. In: D.E. Stott, R.H. Mohtar and G.C. Steinhardt (eds). 2001. Sustaining the Global Farm. Selected papers from the 10th International Soil Conservation Organization Meeting held May 24-29, 1999 at Purdue University and the USDA-ARS National Soil Erosion Research Laboratory. Keynote: Soil Conservation For C Sequestration R. Lal* ABSTRACT fragile ecosystems such as the Himalyan-Tibean ecoregion, The atmospheric concentration of greenhouse gases the Andeas, the West African Sahel, East African Highlands, (GHG) is increasing at the rate of 0.5% yr-1 (3.2 Pg C and the Caribbean region (Scherr and Yadav, 1995; Scherr, -1 -1 -1 yr ) for CO2, 0.6% yr for CH4 and 0.25 ppbv yr for 1999). In addition to effects on productivity, soil erosion N2O. The global radiative forcing due to three GHGs is also profoundly impacts the environment. contributed by 20% due to agricultural activities and Two principal impacts of erosion on environment include 14% to change in land use and attendant deforestation. reduction in quality of water and air through pollution and Principal agricultural activities that contribute to eutrophication of surface water, and emissions of emission of GHGs include plowing, application of radioactively-active gases (e.g., CO2, CH4 and N2O) to the fertilizers and manures, soil drainage, biomass burning, atmosphere. Increasing atmospheric concentration of -1 -1 residue removal. The loss of soil C is accentuated by soil radioactively-active gases (0.5% yr for CO2, 0.6% yr for -1 degradation (due to erosion, compaction, salinization CH4, 0.25% yr for N2O) (IPCC, 1995) necessitates etc.) and the attendant decline in soil quality. -
Measuring Soil Ph
Measuring soil pH Viti-note Summary: Soil pH refers to the acidity or alkalinity Equipment of the soil. It is a measure of the • Equipment Colorimetric test kit available from concentration of free hydrogen ions nurseries (includes mixing stick, plate, • Timing (H+) that are in the soil. Soil pH can dye, barium sulphate, pH colour chart, be measured in water (pH ) or a weak • Method w instructions), teaspoon, recording sheet calcium chloride solution (pH ). The pH CaCl and pen. • Timing range is from 0-14, with value of 7 being neutral. Soil pH values (as measured in a OR water and soil solution) indicate: Hand held pH meter, clear plastic jar with • Strong acidity if less than 5.0. screw-on lid, distilled water, recording sheet and pen. • Moderate acidity at 5.0 to 6.0. • Neutral between 6.5 and 7.5. Timing • Moderate alkalinity at 7.5 to 8.5. This measurement is best undertaken • Strong alkalinity for values of 8.5 when soil sampling is conducted and and above. would normally be done at the same time The limited data available suggests that as assessments for electrical conductivity. soil pHCaCl should be in the range 5.5-7.5 Soil pH should be measured in the fibrous for best vine performance. root zone (ie. 0-20cm depth) as well as Soil pH outside the neutral range can the deeper root zone (>20cm depth). influence the availability of specific Make sure the soil samples are taken nutrients to plants, as well as the inside the irrigation wetting pattern. -
NRCS Keys to Soil Taxonomy
United States Department of Agriculture Keys to Soil Taxonomy Ninth Edition, 2003 Keys to Soil Taxonomy By Soil Survey Staff United States Department of Agriculture Natural Resources Conservation Service Ninth Edition, 2003 The United States Department of Agriculture (USDA) prohibits discrimination in all its programs and activities on the basis of race, color, national origin, gender, religion, age, disability, political beliefs, sexual orientation, and marital or family status. (Not all prohibited bases apply to all programs.) Persons with disabilities who require alternative means for communication of program information (Braille, large print, audiotape, etc.) should contact USDA’s TARGET Center at 202-720-2600 (voice and TDD). To file a complaint of discrimination, write USDA, Director, Office of Civil Rights, Room 326W, Whitten Building, 14th and Independence Avenue, SW, Washington, DC 20250-9410, or call 202-720-5964 (voice and TDD). USDA is an equal opportunity provider and employer. Cover: A natric horizon with columnar structure in a Natrudoll from Argentina. 5 Table of Contents Foreword .................................................................................................................................... 7 Chapter 1: The Soils That We Classify.................................................................................. 9 Chapter 2: Differentiae for Mineral Soils and Organic Soils ............................................... 11 Chapter 3: Horizons and Characteristics Diagnostic for the Higher Categories ................. -
Basic Soil Science W
Basic Soil Science W. Lee Daniels See http://pubs.ext.vt.edu/430/430-350/430-350_pdf.pdf for more information on basic soils! [email protected]; 540-231-7175 http://www.cses.vt.edu/revegetation/ Well weathered A Horizon -- Topsoil (red, clayey) soil from the Piedmont of Virginia. This soil has formed from B Horizon - Subsoil long term weathering of granite into soil like materials. C Horizon (deeper) Native Forest Soil Leaf litter and roots (> 5 T/Ac/year are “bio- processed” to form humus, which is the dark black material seen in this topsoil layer. In the process, nutrients and energy are released to plant uptake and the higher food chain. These are the “natural soil cycles” that we attempt to manage today. Soil Profiles Soil profiles are two-dimensional slices or exposures of soils like we can view from a road cut or a soil pit. Soil profiles reveal soil horizons, which are fundamental genetic layers, weathered into underlying parent materials, in response to leaching and organic matter decomposition. Fig. 1.12 -- Soils develop horizons due to the combined process of (1) organic matter deposition and decomposition and (2) illuviation of clays, oxides and other mobile compounds downward with the wetting front. In moist environments (e.g. Virginia) free salts (Cl and SO4 ) are leached completely out of the profile, but they accumulate in desert soils. Master Horizons O A • O horizon E • A horizon • E horizon B • B horizon • C horizon C • R horizon R Master Horizons • O horizon o predominantly organic matter (litter and humus) • A horizon o organic carbon accumulation, some removal of clay • E horizon o zone of maximum removal (loss of OC, Fe, Mn, Al, clay…) • B horizon o forms below O, A, and E horizons o zone of maximum accumulation (clay, Fe, Al, CaC03, salts…) o most developed part of subsoil (structure, texture, color) o < 50% rock structure or thin bedding from water deposition Master Horizons • C horizon o little or no pedogenic alteration o unconsolidated parent material or soft bedrock o < 50% soil structure • R horizon o hard, continuous bedrock A vs. -
AGR-5: When to Apply Lime and Fertilizer
AGR-5 C O O P E R A T I V E E X T E N S I O N S E R V I C E U N I V E R S I T Y O F K E N T U C K Y • C O L L E G E O F A G R I C U L T U R E WHEN TO APPLY LIME AND FERTILIZER Kenneth Wells Department of Agronomy early half of all the fertilizer used in Kentucky each The mineral form of individual soil particles and the Nyear is bought by farmers during the rush of the spring extent to which these mineral soil particles have been planting season. As a result, it is often difficult for the coated with layers of oxides and organic materials also fertilizer industry to meet customer demands during this 6 affect the total soil reaction. to 8 week period. All clay particles in soil have a net negative (-) Much of the fertilizer now used during the spring rush electrical charge. Because of this negative charge, clay season could be applied during other seasons of the year. If particles will react with components of lime and fertilizer farmers scheduled fertilizer applications more evenly through- which dissolve as positively (+) charged particles (cations) out the year, dealers would be in a much better position to when added to soil. Lime materials dissolve to release provide them with the kinds and amounts of fertilizer they positively charged calcium (Ca++) and/or magnesium desire. Custom application services could be improved. -
Port Silt Loam Oklahoma State Soil
PORT SILT LOAM Oklahoma State Soil SOIL SCIENCE SOCIETY OF AMERICA Introduction Many states have a designated state bird, flower, fish, tree, rock, etc. And, many states also have a state soil – one that has significance or is important to the state. The Port Silt Loam is the official state soil of Oklahoma. Let’s explore how the Port Silt Loam is important to Oklahoma. History Soils are often named after an early pioneer, town, county, community or stream in the vicinity where they are first found. The name “Port” comes from the small com- munity of Port located in Washita County, Oklahoma. The name “silt loam” is the texture of the topsoil. This texture consists mostly of silt size particles (.05 to .002 mm), and when the moist soil is rubbed between the thumb and forefinger, it is loamy to the feel, thus the term silt loam. In 1987, recognizing the importance of soil as a resource, the Governor and Oklahoma Legislature selected Port Silt Loam as the of- ficial State Soil of Oklahoma. What is Port Silt Loam Soil? Every soil can be separated into three separate size fractions called sand, silt, and clay, which makes up the soil texture. They are present in all soils in different propor- tions and say a lot about the character of the soil. Port Silt Loam has a silt loam tex- ture and is usually reddish in color, varying from dark brown to dark reddish brown. The color is derived from upland soil materials weathered from reddish sandstones, siltstones, and shales of the Permian Geologic Era. -
(Hardpan) for Precision Agriculture on So
SITE - SPECIFIC CHARACTERIZATION, MODELING AND SPATIAL ANALYSIS OF SUB-SOIL COMPACTION (HARDPAN) FOR PRECISION AGRICULTURE ON SOUTHEASTERN US SOILS by MEHARI ZEWDE TEKESTE (Under the Direction of Randy L. Raper and Ernest W. Tollner) ABSTRACT Natural and machinery traffic-induced subsoil compacted layers (soil hardpans) that are found in many southeastern US soils limit root growth with detrimental effects on crop productivity and the environment. Due to the spatial variability of hardpans, tillage management systems that use site-specific depth tillage applications may reduce fuel consumption compared to the conventional uniform depth tillage. The success of site-specific tillage or variable depth tillage depends on an accurate sensing of the hardpan layers, field positioning, and controlling the application of real-time or prescribed tillage. The over arching objective of the work was to understand and advance the art and science of soil compaction analysis and prediction with an eye towards compaction management in precision farming. The specific objectives were (1) To investigate the influences of soil parameters (soil moisture and bulk density), and the soil-cone frictional property on the interpretations of cone penetrometer data in predicting the magnitude and depth of hardpans, (2) To determine spatial variability for creating hardpan maps and (3) To investigate a passive acoustic based real-time soil compaction sensing method. The soil cone penetration problems were also modeled using finite element modeling to investigate the soil deformation patterns and evaluate the capability of the finite element method to predict the magnitude and depth of the hardpan. Laboratory experiments in a soil column study indicated that the soil cone penetration resistances were affected by soil moisture, bulk density and cone material type. -
Contaminated Soil in Gardens
Contaminated Soil in Gardens How to avoid the harmful effects EUR/ICP/LVNG 03 01 02(A) E64737 EUROPEAN HEALTH21 TARGET 11 HEALTHIER LIVING By the year 2015, people across society should have adopted healthier patterns of living (Adopted by the WHO Regional Committee for Europe at its forty-eighth session, Copenhagen, September 1998) Abstract In many cities, gardens are located on old, abandoned landfills and dumping sites. Cities have expanded by filling up spaces around the city with garbage, rubble and earth. The places where old landfills were have often become gardens where citizens can get away and enjoy the open air away from the noise and racket of cities. Normal garbage and rubble in landfills do not present a problem, however industrial and chemical waste can present a health hazard, especially when concentrations of contaminants are above acceptable limits. Some special precautions are proposed in this booklet so that the potential ill effects of contaminated soil can be avoided. Keywords SOIL POLLUTANTS RISK MANAGEMENT GUIDELINES URBAN HEALTH Contents The soil is contaminated – what then? .......................................................1 What is in the ground under us?.................................................................2 How harmful substances may affect the body ............................................3 How to reduce the risk................................................................................4 The best way to garden..............................................................................5 -
HOW to IMPROVE SOIL DRAINAGE Charlotte Germane, Nevada County Master Gardener
GOT COMPACTION? HOW TO IMPROVE SOIL DRAINAGE Charlotte Germane, Nevada County Master Gardener From The Curious Gardener, Summer 2011 Do you suspect you might have a drainage problem in your garden? If your soil does not drain quickly enough, your plants will drown. Soils in the foothills Your soil drainage may not be as bad as you think it is. There’s so much talk in the foothills about clay soil that some gardeners assume they have poorly draining soil, and grumble about it, when they actually have pretty respectable loam. The USDA has mapped soil types and found that in the lower foothills the soil can be sandy loam over heavy sandy loam, or loam over clay loam. Above 2000 feet, it is typically loam over clay loam with cobblestones. An unusual feature of foothills soil is the serpentine outcropping. This combines poor drainage with toxic levels of magnesium. If you need to grow in a serpentine soil area, use raised beds. The serpentine soil under the beds will not provide adequate drainage. Another foothill soil issue that makes for poor drainage is “layered soil”. Soil naturally transitions from one kind to another, but layered soil means soil that changes abruptly, making it hard for water to move through easily. Layered soil occurs naturally (soil on top of rock or a clay pan) and can also be created by digging with rototillers and heavy equipment. Check for poor grading, over-irrigation, and thatched lawns Before you label your soil the culprit, walk your garden and evaluate the grading. It is possible that at the time of your home’s construction, or during a later landscaping project,the soil was graded so the water drained toward an area with no easy outlet. -
Diversity and Classification Problems of Sandy Soils in Subboreal Zone (Central Europe, Poland)
Diversity and classification problems of sandy soils in subboreal zone (Central Europe, Poland) Michał Jankowski Faculty of Biology and Earth Sciences, Nicolaus Copernicus University, Toruń, Poland, Email [email protected] Abstract The aim of this study was to present some examples of sandy soils and to discuss their position in soil systematics. 8 profiles represent: 4 soils widely distributed in postglacial landscapes of Poland (Central Europe), typical for different geomorphological conditions and vegetation habitats (according to regional soil classification: Arenosol, Podzolic soil, Rusty soil and Mucky soil) and 4 soils having unusual features (Gleyic Podzol and Rusty soil developed in a CaCO 3-rich substratum and two profiles of red-colored Ochre soils). According to WRB (IUSS Working Group WRB, 2007), almost all of these soils can be named Arenosols. Considering their individual morphological features (stage of development, sequence of horizons) and different ecological value, most of the studied soils should be classified into other Reference Soil Groups or even distinguished in individual units. Key Words Soil classification, Soil geography, Soil morphology, Arenosols, Podzols, Sand. Introduction Soils developed from loose quartz sands generally represent the least fertile mineral soils in the World. According to WRB soil classification (IUSS Working Group WRB 2007), one genetic variant - Podzols - is distinguished as individual unit from that textural group of soils. Most of the other sandy soils can only be classified as Arenosols, irrespective to their development rate, soil horizons sequence or ecological properties. Such arrangement does not reflect the real diversity of sandy soils, especially in comparison to the number of divisions covering soils of heavier texture. -
Alteration of Rocks by Endolithic Organisms Is One of the Pathways for the Beginning of Soils on Earth Received: 19 September 2017 Nikita Mergelov1, Carsten W
www.nature.com/scientificreports OPEN Alteration of rocks by endolithic organisms is one of the pathways for the beginning of soils on Earth Received: 19 September 2017 Nikita Mergelov1, Carsten W. Mueller 2, Isabel Prater 2, Ilya Shorkunov1, Andrey Dolgikh1, Accepted: 7 February 2018 Elya Zazovskaya1, Vasily Shishkov1, Victoria Krupskaya3, Konstantin Abrosimov4, Published: xx xx xxxx Alexander Cherkinsky5 & Sergey Goryachkin1 Subaerial endolithic systems of the current extreme environments on Earth provide exclusive insight into emergence and development of soils in the Precambrian when due to various stresses on the surfaces of hard rocks the cryptic niches inside them were much more plausible habitats for organisms than epilithic ones. Using an actualistic approach we demonstrate that transformation of silicate rocks by endolithic organisms is one of the possible pathways for the beginning of soils on Earth. This process led to the formation of soil-like bodies on rocks in situ and contributed to the raise of complexity in subaerial geosystems. Endolithic systems of East Antarctica lack the noise from vascular plants and are among the best available natural models to explore organo-mineral interactions of a very old “phylogenetic age” (cyanobacteria-to-mineral, fungi-to-mineral, lichen-to-mineral). On the basis of our case study from East Antarctica we demonstrate that relatively simple endolithic systems of microbial and/or cryptogamic origin that exist and replicate on Earth over geological time scales employ the principles of organic matter stabilization strikingly similar to those known for modern full-scale soils of various climates. Te pedosphere emergence is attributed to the most ancient forms of terrestrial life in the Early Precambrian which strongly aided the abiotic decay of rocks. -
Soil Taxonomy" in Particular ,
1. CONTROL NUMBER 2. SUBECT CLASSIFICATION (695) BIBLIOGRAPItlC DATA SHEET IN-AAJ-558 AF26-0000-0000 3. TITLE ANt) SUBTITLE (240) Experimental designs for predicting crop productivity with environmental and economic inputs for al rotcchnology transfer 4. PERSON.\I. AUTHORS (10P) Silva, J. A. 5. CORPORATE AUTHORS (101) Hawaii Univ. College of Tropical Agriculture 6. IDOCUMEN2< DATE (110)7. NUMBER OF PAGES (120) 8.ARC NUMBER [7 1981 13n631.5.S586b __ 9. R FRENCE ORGANIZATION (130) Hawaii 10. SUPI'PLEMENTARY NOTES (500) (In Departmental paper 49) 11. ABSTRACT (950) 12. DESCRIPTORS (920) 13. PROJECT NUMBER (150) Agricultural production Agricultural technology 931582C00 Technology transferi!Techoloy tansferYieldY e d14. CONTRACT NO.(I It)) 15. CONTRACT Soil fertility Experimentation TYPE (140) Tropics Productivity AID/ta-C-1108 Forecasting 16. TYPE OF DOCUMENT (160) AM 590-7 (10-79) Departmental Paper 49 Experimental Designs for Predicting Crop Productivity with Environmental and Economic Inputs for Agrotechnology Transfer Edited by James A. Silva ...... ,..,... *** .......... ....* ...... .... .. 00400O 00€€€€*00 .. ...* Y Y*b***S4....... ~~~.eeeeeoeeeeeU ........ o .. *.4.............*e............ :0 ooee............. ........... ....... nae of T c.e Haw i. ns..ut. CollegeofTrpclgr.cut a UnversityoHa B....EMAR.SO University of Hawaiio~ee BENCHMAR SO I Le~eSPoJECTU/ADCotac o.t-C1 14.. C4 '4 t 10 wte IA:A 77 d E/ Adt , I 26Esi ',. ,~ )~'I *3-! * Ire ~ -I ~ 0 1 N Koel4 'I M M Experimental Designs for Predicting Crop Productivity with Environmental and Economic Inputs for Agrotechnology Transfer Edited by James A. Silva Benchmark Soils Project UH/AiD Contract No. to-C-1108 The Author James A. Silva is Soil Scientist and Principal Investigator, Benchmark Soils Project/Hawaii, Department of Agronomy and Soil Science, College of Tropical Agriculture and Human Resources, University of Hawaii, Honolulu.