0 a Paleopedological and Ichnological Approach to Spatial

Total Page:16

File Type:pdf, Size:1020Kb

0 a Paleopedological and Ichnological Approach to Spatial 0 A Paleopedological and Ichnological Approach to Spatial and Temporal Variability in Pennsylvanian-Permian Strata of the Lower Dunkard Group A thesis presented to the faculty of the College of Arts and Sciences of Ohio University In partial fulfillment of the requirements for the degree Master of Science Michael G. Blair August 2015 © 2015 Michael G. Blair. All Rights Reserved. 2 This thesis titled A Paleopedological and Ichnological Approach to Spatial and Temporal Variability in Pennsylvanian-Permian Strata of the Lower Dunkard Group by MICHAEL G. BLAIR has been approved for the Department of Geological Sciences and the College of Arts and Sciences by Daniel I. Hembree Associate Professor of Geological Sciences Robert Frank Dean, College of Arts and Sciences 3 ABSTRACT BLAIR, MICHAEL G., M.S., August 2015, Geological Sciences A Paleopedological and Ichnological Approach to Spatial and Temporal Variability in Pennsylvanian-Permian Strata of the Lower Dunkard Group Director of Thesis: Daniel I. Hembree Paleosols record a wealth of paleoenvironmental, paleoecological, and paleoclimatic information. Plants and soil-dwelling animals both affect and are affected by soil properties, and, therefore, their traces serve to further refine the interpretations of paleosols. These characteristics make paleosols and ichnofossils particularly valuable in understanding lateral variability in the complex fluvial system represented by the upper fluvial plain facies province of the Upper Pennsylvanian to Lower Permian Dunkard Group. These deposits represent proximal to distal expressions of a migrating river and associated floodplain microenvironments. By understanding the degree to which soils and organism behaviors change over short distances at a given time, interpretations of regional change through vertical successions can be better calibrated. This study integrates physical properties of paleosols and ichnofossils at outcrop, hand sample, and thin section scales with chemical properties determined by X-ray fluorescence (XRF) and X-ray diffraction (XRD). These analyses provide bulk geochemical and clay mineralogical information to derive estimates of mean annual precipitation and various chemical weathering processes. Consideration of these factors allows interpretation of small-scale spatial and temporal variability to be recognized and understood in terms of local versus regional changes in environmental and climatic conditions. 4 ACKNOWLEDGEMENTS I would like to thank my advisor, Dr. Daniel Hembree for his support and patience, as well as my committee members, Dr. Craig Grimes and Dr. David Kidder. I would also like to thank Jeff Shaffer and Lauren Johnson for providing field assistance during the summer of 2014. I am extremely grateful for the support of my friends and family, especially my parents, Ron and Cathy Duchovic, and brother, Joel Blair. This research would not have been possible without funding from the Geological Society of America, the American Chemical Society Petroleum Research Fund (52708- UR8), and the Ohio University Department of Geological Sciences Al umni Graduate Research Grant. 5 TABLE OF CONTENTS Page Abstract………………………………………………………………………………… 3 Acknowledgments………………………………………………………………………4 List of Tables……..……………………………………………………………………. 9 List of Figures…...……………………………………………………………………..11 1 Introduction……………………………………………………………………....15 2 Geologic Setting………...………………………………………………………. 18 3 Methods…………………………………………………………………………. 24 3.1 Field……………………………………………………………………….. 24 3.2 Laboratory………………………………………………………………… 26 3.2.1 Thin Sections………………………………………………………... 26 3.2.2 Bulk Geochemistry………………………………………………….. 26 3.2.3 Clay Mineralogy…………………………………………………….. 27 4 Results…………………………………………………………………………... 32 4.1 Sedimentology and Stratigraphy………………………………………….. 32 4.2 Flora……………………………………………………………………….. 33 4.2.1 Plant Impressions…………………………………………………… 33 4.2.2 Rhizohaloes…………………………………………………………. 34 4.2.2.1 Reduced rhizohaloes…………………………………………. 34 4.2.2.2 Yellow rhizohaloes…………………………………………... 35 4.2.2.3 Diffuse purple rhizohaloes…………………………………… 35 6 4.2.3 Rhizoconcretions……………………………………………………. 35 4.2.4 Rhizotubules………………………………………………………… 36 4.2.5 Root Casts…………………………………………………………… 36 4.3 Fauna (Ichnofossils)………………………………………………………. 37 4.3.1 Scoyenia……………………………………………………………... 37 4.3.2 Arenicolites………………………………………………….............. 42 4.3.3 Skolithos…………………………………………………………….. 42 4.3.4 Cochlichnus…………………………………………………............. 43 4.3.5 Mermia……………………………………………………………… 43 4.3.6 Naktodemasis………………………………………………............... 44 4.3.7 Isopodichnus………………………………………………………… 44 4.3.8 Planolites……………………………………………………………. 45 4.3.9 Coprolites…………………………………………………………… 45 4.3.10 Pedotubules…………………………………………………………. 45 4.4 General Section Paleosols………………………………………………… 47 4.4.1 Paleosol 1 (P1)………………………………………………………. 47 4.4.2 Paleosol 2 (P2)………………………………………………………. 48 4.4.3 Paleosol 3 (P3)………………………………………………………. 54 4.4.4 Paleosol 4 (P4)………………………………………………………. 56 4.4.5 Paleosol 5 (P5)………………………………………………………. 57 4.4.6 Paleosol 6 (P6)………………………………………………………. 61 4.4.7 Paleosol 7 (P7)……………………………………………………….67 7 4.4.8 Paleosol 8 (P8)………………………………………………………. 69 4.4.9 Paleosol 9 (P9)………………………………………………………. 74 4.5 Coeval Profiles……………………………………………………………. 78 4.5.1 General Description…………………………………………………. 78 4.5.2 Northwest (NW-CP)………………………………………………… 85 4.5.3 Northwest Island (NWI-CP)………………………………………… 85 4.5.4 Northeast Island (NEI-CP)………………………………………….. 86 4.5.5 Northeast (NE-CP)………………………………………………….. 89 4.5.6 Southwest (SW-CP)………………………………………………… 90 4.5.7 Southwest Island (SWI-CP)………………………………………… 94 4.5.8 Southeast Island (SEI-CP)………………………………………….. 94 4.5.9 Southeast (SE-CP)………………………………………………….. 98 5 Discussion……………………………………………………………………… 104 5.1 Soil Forming Factors…………………………………………………….. 104 5.1.1 Parent Material……………………………………………………... 104 5.1.2 Climate……………………………………………………………... 106 5.1.3 Topography………………………………………………………… 114 5.1.4 Biota………………………………………………………………... 115 5.2 Vertical Variability………………...…………………………………….. 116 5.3 Lateral Variability………………………………...……………………… 122 5.4 Paleoclimate……………………………………………………………… 124 5.5 Soil Ecosystems………...………………………………………………... 127 8 5.5.1 Plants……………………………………………………………….. 127 5.5.2 Soil Animals………………………………………………………...133 6 Conclusion……………………………………………………………………....137 References……………………………………………………………………............. 141 Appendix 1: Bulk Geochemistry (General Section)…………………………………. 148 Appendix 2: Bulk Geochemistry (CP Profiles)……………………………………….149 Appendix 3: Weathering Indices through the General Section…………………..….. 150 9 LIST OF TABLES Page Table 3.1 Oxides and ranges reported by ALS Chemex following XRF analysis of bulk geochemistry…………………………………………………………………………… 28 Table 3.2 Molecular weathering ratios (From Retallack, 2001)……………..………... 29 Table 3.3 Paleoprecipitation proxies…………………………………………………... 29 Table 4.1 General section paleosol summary table, P1-P3. P1 and P2 are isolated from other units by buried upper and lower contacts. Stratigraphically higher paleosols (P3- P9) are separated by laterally continuous sandstone beds, which are used to dileneate paleosol-containing depositional cycles. Genetically distinct paleosols within a given cycle are highlighted, with colors corresponding to letters “a” (green, i.e. “3a”) through “c” (yellow, i.e. “3c”). Clay mineralogy is only reported in paleosols with a <4 m fraction greater than 10%. Only mineral species with >10% abundance are listed in parentheses following the total weight % of the clay size fraction for a given paleosol horizon.……………………………………………………………………………………… 50 Table 4.2 General section molecular weathering ratios, chemical index of alteration (CIA-K), CALMAG, estimated mean annual precipitation (MAP). Calculated using bulk geochemistry data derived from whole-rock X-ray fluorescence (XRF) of samples from general section paleosols. Negative values in the location column and a single asterisk next to the paleosol number indicate paleosols sample from the northwest trench, which was measured in 20 cm intervals descending from -20 to -700 from the stratigraphically lowest laterally continuous sandstone exposed in the northeast general section trench. The double asterisk next to P6 samples indicates that these were taken from the same depositional cycle as those taken from the northeast trench, but were sampled on the northwest corner of the study area where the paleosol is better exposed.…………….. 52 Table 4.3 General section clay mineralogy from X-ray diffraction (XRD) of the <4 micron fraction of general section paleosols. R1 M-L I/S 30%S: ordered mixed-layer illite/smectite with 30% smectite. R1 M-L I/S 20%S: ordered mixed-layer illite/smectite with 20% smectite. Negative values in the location column and a single asterisk next to the paleosol number indicate paleosols sample from the northwest trench, which was measured in 20 cm intervals descending from -20 to -700 from the stratigraphically lowest laterally continuous sandstone exposed in the northeast general section trench. The double asterisk next to P6 samples indicates that these were taken from the same depositional cycle as those taken from the northeast trench, but were sampled on the northwest corner of the study area where the paleosol is better exposed. Triple asterisks indicate an approximate location (±20 cm). The sample highlighted in pink was lost in transport and not analyzed.……………………………………………………………. 53 10 Table 4.4 General section paleosol summary table, P5-P4. Same conventions used as the previous summary table, but a a light purple-blue
Recommended publications
  • Topic: Soil Classification
    Programme: M.Sc.(Environmental Science) Course: Soil Science Semester: IV Code: MSESC4007E04 Topic: Soil Classification Prof. Umesh Kumar Singh Department of Environmental Science School of Earth, Environmental and Biological Sciences Central University of South Bihar, Gaya Note: These materials are only for classroom teaching purpose at Central University of South Bihar. All the data/figures/materials are taken from several research articles/e-books/text books including Wikipedia and other online resources. 1 • Pedology: The origin of the soil , its classification, and its description are examined in pedology (pedon-soil or earth in greek). Pedology is the study of the soil as a natural body and does not focus primarily on the soil’s immediate practical use. A pedologist studies, examines, and classifies soils as they occur in their natural environment. • Edaphology (concerned with the influence of soils on living things, particularly plants ) is the study of soil from the stand point of higher plants. Edaphologist considers the various properties of soil in relation to plant production. • Soil Profile: specific series of layers of soil called soil horizons from soil surface down to the unaltered parent material. 2 • By area Soil – can be small or few hectares. • Smallest representative unit – k.a. Pedon • Polypedon • Bordered by its side by the vertical section of soil …the soil profile. • Soil profile – characterize the pedon. So it defines the soil. • Horizon tell- soil properties- colour, texture, structure, permeability, drainage, bio-activity etc. • 6 groups of horizons k.a. master horizons. O,A,E,B,C &R. 3 Soil Sampling and Mapping Units 4 Typical soil profile 5 O • OM deposits (decomposed, partially decomposed) • Lie above mineral horizon • Histic epipedon (Histos Gr.
    [Show full text]
  • 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.
    [Show full text]
  • Study of Soil Moisture in Relation to Soil Erosion in the Proposed Tancítaro Geopark, Central Mexico: a Case of the Zacándaro Sub-Watershed
    Study of soil moisture in relation to soil erosion in the proposed Tancítaro Geopark, Central Mexico: A case of the Zacándaro sub-watershed Jamali Hussein Mbwana Baruti March, 2004 Study of soil moisture in relation to soil erosion in the proposed Tancítaro Geopark, Central Mexico: A case of the Zacándaro sub-watershed by Jamali Hussein Mbwana Baruti Thesis submitted to the International Institute for Geo-information Science and Earth Observation in partial fulfilment of the requirements for the degree of Master of Science in Geo-information Science and Earth Observation, Land Degradation and Conservation specialisation Degree Assessment Board Dr. D. Rossiter (Chairman) ESA Department, ITC Dr. D. Karssenberg (External examiner) University of Utrecht Dr. D. P. Shrestha (Supervisor) ESA Department, ITC Dr. A. Farshad (Co supervisor and students advisor) ESA Department, ITC Dr. P. Van Dijk (Programm Director, EREG), ITC INTERNATIONAL INSTITUTE FOR GEO-INFORMATION SCIENCE AND EARTH OBSERVATION ENSCHEDE, THE NETHERLANDS Disclaimer This document describes work undertaken as part of a programme of study at the International Institute for Geo-information Science and Earth Observation. All views and opinions expressed therein remain the sole responsibility of the author, and do not necessarily represent those of the institute. Abstract A study on soil moisture in relation to soil erosion was conducted in the proposed Tancítaro Geopark, Central Mexico with special attention to the Zacándaro sub-watershed. The study aims at applying a simple water balance and an erosion model as conservation planning tools. Two methods i.e. Thorn- thwaite and Mather (1955) and the Revised Morgan-Morgan-Finney (2001) were applied in a GIS environment to model available soil moisture and soil loss rates.
    [Show full text]
  • 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.
    [Show full text]
  • Soils Section
    Soils Section 2003 Florida Envirothon Study Sections Soil Key Points SOIL KEY POINTS • Recognize soil as an important dynamic resource. • Describe basic soil properties and soil formation factors. • Understand soil drainage classes and know how wetlands are defined. • Determine basic soil properties and limitations, such as mottling and permeability by observing a soil pit or soil profile. • Identify types of soil erosion and discuss methods for reducing erosion. • Use soil information, including a soil survey, in land use planning discussions. • Discuss how soil is a factor in, or is impacted by, nonpoint and point source pollution. Florida’s State Soil Florida has the largest total acreage of sandy, siliceous, hyperthermic Aeric Haplaquods in the nation. This is commonly called Myakka fine sand. It does not occur anywhere else in the United States. There are more than 1.5 million acres of Myakka fine sand in Florida. On May 22, 1989, Governor Bob Martinez signed Senate Bill 525 into law making Myakka fine sand Florida’s official state soil. iii Florida Envirothon Study Packet — Soils Section iv Contents CONTENTS INTRODUCTION .........................................................................................................................1 WHAT IS SOIL AND HOW IS SOIL FORMED? .....................................................................3 SOIL CHARACTERISTICS..........................................................................................................7 Texture......................................................................................................................................7
    [Show full text]
  • Soil Ph Ranges Neutral Acidity Alkalinity
    Sound Farm Idea #04 Lime For Pastures and Crops When it comes to managing soil health in the Northwest, it’s easy to focus on the big three nutrients (nitrogen, phosphorus, and potassium) in the soil, and overlook a fourth key aspect - soil pH. Soil pH refers to how acidic (sour) or alkaline (sweet) soil is on a scale between 0 and 14, with 7.0 being neutral. Most plants and crops prefer soil pH levels in the 6.0 – 7.0 range. Soil pH Ranges Neutral Acidity Alkalinity 10,000x 1,000x 100x 10x o 10x 100x 1,000x 10,000x 3 4 5 6 7 8 9 10 11 Here in Western Washington, our soils are typically mildly to strongly acidic (5.0 – 6.5). Soil pH is important for a number of reasons. First of all, it controls the rate of chemical reactions and the activity of soil microorganisms. As you move towards the ends of the scale, different nutrients will either become more or less available for plants. For example, phosphorus is readily available when soil pH is 6.5; decreasing the pH to 5.5 reduces its availability by half. Also, as soil pH decreases, the activity of beneficial nitrogen-fixing bacteria slows down and many detrimental disease-causing fungi become more active. It’s important to factor pH levels into your fertilizer applications to ensure that nutrients will be available to plants. Often, after a lime application, a lawn or pasture may quickly ‘green-up’. This is due to nutrients already in the soil becoming available during the pH adjustment.
    [Show full text]
  • Water Content Concepts and Measurement Methods Suat Irmak, Professor, Soil and Water Resources and Irrigation Engineering
    EC3046 December 2019 Soil- Water Potential and Soil- Water Content Concepts and Measurement Methods Suat Irmak, Professor, Soil and Water Resources and Irrigation Engineering Soil- water status is a critical and rapidly changing tion management. In addition, it is important for studying variable that determines and impacts numerous important soil- water movement, chemical transport, crop water stress, factors in production fields such as crop emergence and evapotranspiration, hydrologic and crop modeling, soil phys- growth, water management, water and crop yield productiv- ics, water resources management, climate change impacts ity relationships, and within- field hydrologic balances. Thus, on agricultural water management and crop productivity, its accurate determination dictates and impacts the success of meteorological studies, yield forecasting, water run- off and water management and related agricultural operations. This, run- on, infiltration studies, field traffic and within- field work in turn, affects the attainment of potential yield, as well as the ability and soil- compaction studies, aridity indices, and other reduction of water losses and chemical leaching. Maintaining agricultural and ecosystem functions and practices. Effective optimum soil moisture in the crop root zone also strongly in- irrigation management requires the knowledge of “when” fluences optimum nitrogen (N) uptake by plants, which helps and “how much” water to apply to optimize crop production. to reduce N leaching. Numerous soil moisture measurement Some of the most effective irrigation management decisions technologies are available. None of the methods, however, also include “how” to apply the irrigation water for most are perfectly suited to all operational conditions as each has effective productivity under different climate, soil, crop, and drawbacks and advantages, depending on the application management practices to reduce unbeneficial water losses conditions.
    [Show full text]
  • Review Article on Paleopedology And
    PRELIMINARY STUDY OF SOIL SAMPLES FROM IRON AGE NECROPOLES AT CAMPO Christophe MBIDA MINDZIE, Antoine MVONDO ZE, Conny MEISTER & Manfred K.H. EGGERT ABSTRACT This work was undertaken on soil samples of six prospective graves and four ”rubbish pits” from Campo and Akonetye sites. The studied soil samples could be divided into two distinguishing groups. The first was characterized by relatively high values of pH, very high content of calcium, phosphorus and potassium compared to values commonly found in surrounding forest soils. This group was found to correspond to the dump pits, while the second group of samples with low pH, lower content of calcium, phosphorus came from the hypothesised burial places. Key words: soil features, soil analyses, calcium and phosphorus content, dump pits, necropolis, burial. INTRODUCTION The most common features encountered in iron age sites of Southern Cameroon are the so called “rubbish pits”, which seem to be most obviously, a final use of those pits, when the original purposes for which they were dug were over. One of the studied sites located in the vicinity of the Catholic Church at Campo, a small town of south Cameroon revealed specific structures different in their nature from the dump pits. There were dump pits alongside with alignments of overturned clay potteries. The first surveys (ZANA, 2000; OSLISLY et al, 2006) confirmed the latter features were different and their specificity shown by the disposition and types of the artefacts recovered. It was hypothesized they were graves. The preliminary chemical study of soil samples from few pits and those new features was performed to determine the nature of the deposits and how they were deposited, as well as to analyse the context of conservation of artefact in the equatorial soils.
    [Show full text]
  • Soil Acidification
    viti-notes [grapevine nutrition] Soil acidifi cation Viti-note Summary: Characteristics of acidic soils • Soil pH Calcium and magnesium are displaced • Soil acidifi cation in by aluminium (Al3+) and hydrogen (H+) vineyards and are leached out of the soil. Acidic soils below pH 6 often have reduced • Characteristics of acidic populations of micro-organisms. As soils microbial activity decreases, nitrogen • Acidifying fertilisers availability to plants also decreases. • Effect of soil pH on Sulfur availability to plants also depends rate of breakdown of on microbial activity so in acidic soils, ammonium to nitrate where microbial activity is reduced, Figure 1. Effect of soil pH on availability of minerals sulfur can become unavailable. (Sulfur • Management of defi ciency is not usually a problem for acidifi cation Soil pH vineyards as adequate sulfur can usually • Correction of soil pH All plants and soil micro-organisms have be accessed from sulfur applied as foliar with lime preferences for soil within certain pH fungicides). ranges, usually neutral to moderately • Strategies for mature • Phosphorus availability is reduced at acid or alkaline. Soil pH most suitable vines low pH because it forms insoluble for grapevines is between 5.5 and 8.5. phosphate compounds with In this range, roots can acquire nutrients aluminium, iron and manganese. from the soil and grow to their potential. As soils become more acid or alkaline, • Molybdenum is seldom defi cient in grapevines become less productive. It is neutral to alkaline soils but can form important to understand the impacts of insoluble compounds in acid soils. soil pH in managing grapevine nutrition, • In strongly acidic soil (pH <5), because the mobility and availability of aluminium may become freely nutrients is infl uenced by pH (Figure 1).
    [Show full text]
  • Diagnostic Horizons
    Exam III Wednesday, November 7th Study Guide Posted Tomorrow Review Session in Class on Monday the 4th Soil Taxonomy and Classification Diagnostic Horizons Epipedons Subsurface Mollic Albic Umbric Kandic Ochric Histic Argillic Melanic Spodic Plaggen Anthropic Oxic 1 Surface Horizons: Mollic- thick, dark colored, high %B.S., structure Umbric – same, but lower B.S. Ochric – pale, low O.M., thin Histic – High O.M., thick, wet, dark Sub-Surface Horizons: Argillic – illuvial accum. of clay (high activity) Kandic – accum. of clay (low activity) Spodic – Illuvial O.M. accumulation (Al and/or Fe) Oxic – highly weathered, kaolinite, Fe and Al oxides Albic – light colored, elluvial, low reactivity Elluviation and Illuviation Elluviation (E horizon) Organic matter Clays A A E E Bh horizon Bt horizon Bh Bt Spodic horizon Argillic horizon 2 Soil Taxonomy Diagnostic Epipedons Diagnostic Subsurface horizons Moisture Regimes Temperature Regimes Age Texture Depth Soil Taxonomy Soil forming processes, presence or Order Absence of major diagnostic horizons 12 Similar genesis Suborder 63 Grasslands – thick, dark Great group 250 epipedons High %B.S. Sub group 1400 Family 8000 Series 19,000 Soil Orders Entisols Histosols Inceptisols Andisols Gelisols Alfisols Mollisols Ultisols Spodosols Aridisols Vertisols Oxisols 3 Soil Orders Entisol Ent- Recent Histosol Hist- Histic (organic) Inceptisol Incept- Inception Alfisol Alf- Nonsense Ultisol Ult- Ultimate Spodosol Spod- Spodos (wood ash) Mollisol Moll- Mollis (soft) Oxisol Ox- oxide Andisol And- Ando (black) Gelisol
    [Show full text]
  • 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.
    [Show full text]
  • Modeling Soil Nitrate Accumulation and Leaching in Conventional and Conservation Agriculture Cropping Systems
    water Article Modeling Soil Nitrate Accumulation and Leaching in Conventional and Conservation Agriculture Cropping Systems Nicolò Colombani 1 , Micòl Mastrocicco 2,*, Fabio Vincenzi 3 and Giuseppe Castaldelli 3 1 SIMAU-Department of Materials, Environmental Sciences and Urban Planning, Polytechnic University of Marche, Via Brecce Bianche 12, 60131 Ancona, Italy; [email protected] 2 DiSTABiF-Department of Environmental, Biological and Pharmaceutical Sciences and Technologies, Campania University “Luigi Vanvitelli”, Via Vivaldi 43, 81100 Caserta, Italy 3 SVeB-Department of Life Sciences and Biotechnology, University of Ferrara, Via L. Borsari 46, 44121 Ferrara, Italy; [email protected] (F.V.); [email protected] (G.C.) * Correspondence: [email protected]; Tel.: +39-0823-274-609 Received: 25 January 2020; Accepted: 29 May 2020; Published: 31 May 2020 Abstract: Nitrate is a major groundwater inorganic contaminant that is mainly due to fertilizer leaching. Compost amendment can increase soils’ organic substances and thus promote denitrification in intensively cultivated soils. In this study, two agricultural plots located in the Padana plain (Ferrara, Italy) were monitored and modeled for a period of 2.7 years. One plot was initially amended with 30 t/ha of compost, not tilled, and amended with standard fertilization practices, while the other one was run with standard fertilization and tillage practices. Monitoring was performed continuously via soil water probes (matric potential) and discontinuously via auger core profiles (major nitrogen species) before and after each cropping season. A HYDRUS-1D numerical model was calibrated and validated versus observed matric potential and nitrate, ammonium, and bromide (used as tracers). Model performance was judged satisfactory and the results provided insights on water and nitrogen balances for the two different agricultural practices tested here.
    [Show full text]