NRL 211 - Introduction to Soil Science Comprehensive Study Notes

Introduction to Soil Science & Historical Development

  • Definition and Concept of Soil:
    • Soil is a natural component of the landscape formed through complex interactions among climate, organisms, parent material, relief, and time.
    • Soil is a dynamic resource continuously modified by physical, chemical, and biological processes, as well as human activities, leading to the formation of distinct soil horizons.
    • Soil is a porous natural body developed as a result of pedogenic processes, consisting of mineral and organic constituents, characterized by definite physical, chemical, mineralogical, and biological properties.
    • Soil serves as a primary medium for plant growth by providing physical support, water, oxygen, and essential mineral nutrients.
    • Soil functions as a vital habitat and ecosystem resource that supports biodiversity, drives biogeochemical nutrient cycling, regulates water systems, and stores atmospheric carbon.
    • Soil quality directly impacts human nutrition and global food security. A subsistence diet requires approximately 180 kg180\,kg of grain per person per year, whereas an affluent diet requires about four times as much grain. Producing this grain requires an average of 0.085 ha0.085\,ha (850 m2850\,m^2) of land per person.

Hands holding healthy topsoil

  • Historical Development of Soil Science:

    • The formal scientific study of soil emerged in the mid-nineteenth century through interdisciplinary contributions from geologists, chemists, and plant physiologists.
    • Justus von Liebig (1840): Demonstrated the essential role of mineral nutrients in plant growth and propounded the Law of the Minimum and the principle of nutrient replenishment, asserting that nutrients removed from soils by crops must be restored to maintain land productivity.
    • Vasily Dokuchaev (1879): Established the foundations of modern soil science and pedology. Dokuchaev recognized that soil is an independent natural body governed by natural laws, formed by the combined influence of climate, vegetation, parent material, topography, and age.
    • Dokuchaev and his students established pedology as a discipline that elucidates the laws governing the origin, genesis, classification, and distribution of soils on the Earth's surface.
  • Fundamental Approaches and Branches of Soil Science:

    • Pedological Approach: Studies a soil as a natural body, focusing on its origin, profile development, morphology, and spatial distribution across the landscape.
    • Edaphological Approach: Studies soil as a substrate and material in relation to its physical, chemical, mineralogical, and biological properties as they affect land use, crop yield, geoengineering, and waste management.
    • Major Branches of Soil Science:
    • Soil Physics: Investigates the mechanical behavior of soil masses, physical properties (texture, structure, density, porosity, color, temperature), and the measurement and control of water, gas, and heat transport processes.
    • Soil Chemistry: Deals with the chemical composition, charge properties, solute reactions, and chemical processes occurring within the soil solution and exchange complex.
    • Soil Biology & Biochemistry: Focuses on soil ecological systems, macro- and microorganisms, biological transformations, organic matter dynamics, and biochemistry.
    • Soil Mineralogy: Examines primary and secondary mineral constituents, their crystal structures, and their influence on physical, chemical, and biological soil behavior.
    • Soil Fertility: Evaluates the nutrient status and capacity of soil to supply essential elements required for plant growth under given environmental conditions (light, temperature, moisture).
    • Soil Genesis and Classification (Pedology): Studies rock and mineral weathering, factors and processes of soil profile formation, and the systematic classification of soils into taxonomy frameworks.
    • Soil Survey: Encompasses field and laboratory examination, systematic description, mapping, and land capability interpretation for specific agricultural and engineering uses.
    • Soil Technology: Applies scientific principles to soil conservation, erosion control, management of degraded or problem soils, tillage practices, and geoengineering applications.
  • Ecosystem and Global Functions of Soil:

    • Crop Production: Provides mechanical root support, bioavailable nutrients, water, and oxygen.
    • Biogeochemical Nutrient Cycling: Converts, stores, and recycles essential macro- and micronutrients.
    • Water Regulation: Controls rainwater infiltration, surface runoff, groundwater recharge, water storage, and contaminant filtration.
    • Biodiversity Support: Offers micro- and macro-habitats for subterranean fauna, flora, and microbial populations.
    • Climate Regulation: Acts as a major terrestrial carbon sink, sequestering atmospheric carbon dioxide and regulating greenhouse gases (CO2CO_2, N2ON_2O, CH4CH_4).
    • Environmental Protection: Filters, buffers, immobilizes, and degrades organic pollutants, trace metals, and excess agricultural chemicals.
    • Human Infrastructure Support: Acts as the physical foundation for agricultural production, civil structures, roads, and urban development.

The Soil System & Three-Phase Composition

  • Three-Phase Dynamic Balance:
    • Soil is a complex heterogeneous disperse system consisting of solid, liquid, and gaseous phases.
    • The relative proportions of these three phases determine the physical, chemical, and biological behavior of the soil system.
    • Solid Phase (~50% of total volume): Composed of inorganic mineral matter (~45%) and organic matter (~5%). Provides structural stability, stores nutrients, and hosts organisms.
    • Liquid Phase (~25% of total volume): Composed of soil water occupying pore spaces. Contains dissolved organic and inorganic salts (soil solution) available for plant uptake.
    • Gaseous Phase (~25% of total volume): Composed of soil air filling un-waterlogged pores. Supplies oxygen for root and biological respiration and removes metabolic CO2CO_2

Composition pie chart of the soil system

  • Detailed Functional Roles of the Three Phases:
    • Solid Phase Components:
    • Inorganic Minerals: Form the structural skeleton of the soil mass. Primary minerals (quartz, feldspars, micas, pyroxenes, amphiboles, olivine) inherited from parent rock weather into secondary clay minerals (kaolinite, smectites, illite, vermiculite) and free oxides (Fe2O3Fe_2O_3, Al2O3Al_2O_3, SiO2SiO_2).
    • Organic Fraction: Consists of macro- and microorganisms, living plant roots, undecomposed plant/animal residues, and stable colloidal humus.
    • Functions: Serves as a mechanical support matrix, provides ion exchange capacity (CEC/AEC), holds adsorbed water, and stores chemical nutrients.
    • Liquid Phase Components:
    • Comprises water molecules held within soil pores by matric and osmotic potentials.
    • Functions: Acts as a universal solvent transporting dissolved ions (Ca2+Ca^{2+}, Mg2+Mg^{2+}, K+K^+, NO3−NO_3^-, H2PO4−H_2PO_4^-, SO42−SO_4^{2-}) to plant roots; facilitates chemical weathering reactions (hydrolysis, solution, hydration); regulates microbial biochemical activity.
    • Saturated State: Achieved when 100% of soil pore volume is completely filled with water (40–50%40\text{--}50\% total volume).
    • Gaseous Phase Components:
    • Fills all voids not occupied by liquid water. The sum of liquid and gaseous pore volumes equals total soil porosity (TPSTPS).
    • Composition: N2N_2 content is approximately equal to atmospheric air (~79%); O2O_2 content ranges from 20.6%20.6\% in well-aerated topsoil down to 7–14%7\text{--}14\% or less in poorly drained subsoils; CO2CO_2 concentration is significantly higher than atmospheric levels (0.5–10%0.5\text{--}10\% vs 0.03%0.03\%) due to root and microbial respiration.
    • Functions: Provides O2O_2 for aerated plant root metabolism and aerobic microbial decomposition; allows outward diffusion of soil-generated gases.

Mineralogy & Properties of Minerals

  • Definition and Structure of Minerals:
    • A mineral is a homogenous, naturally occurring, solid inorganic substance possessing a definable chemical composition and an internal atomic structure characterized by an orderly arrangement of atoms, ions, or molecules in a crystal lattice.
    • Crystalline Minerals: Bound by plane faces, sharp edges, and fixed interfacial angles forming regular geometric shapes as the crystal lattice grows.
    • Amorphous Minerals: Possess no regular geometric external shape and lack long-range internal atomic ordering (e.g., allophanes, volcanic glass, opal).

Assorted natural mineral specimens

  • Physical Properties of Minerals:
    • Color:
    • Results from the interaction of the mineral surface with light.
    • Idiochromatic Minerals: Possess constant, inherent diagnostic colors due to major chemical constituents (e.g., malachite is always green, graphite is black, sulfur is yellow).
    • Allochromatic Minerals: Display variable colors due to trace impurities or structural defects (e.g., quartz, apatite, beryl, tourmaline).
    • Pleochroic Minerals: Change apparent color when rotated under polarized light due to directional light absorption.

Color varieties of quartz

  • Streak:
    • Refers to the color of the finely pulverized mineral powder produced by rubbing the mineral across an unglazed porcelain streak plate.
    • Highly diagnostic and consistent regardless of specimen surface color variations. Colored minerals yield streaks lighter than their solid color; colorless/white minerals yield white streaks; metallic minerals show dramatic streak differences (e.g., brassy yellow pyrite gives a greenish-black streak; black hematite gives a cherry-red streak; dark metallic cassiterite gives an almost white streak).

Streak test on a porcelain plate

  • Hardness:
    • The relative resistance of a mineral lattice to scratching, reflecting bond strength within the atomic structure.
    • Standardized by Friedrich Mohs (1773–1839) on a 1-to-10 relative scale where a harder mineral scratches any softer mineral below it.
Mohs Hardness NumberStandard Reference MineralCommon Testing Reference Object
10Diamond—
9Corundum (ruby/sapphire)—
8Topaz—
7Quartz—
6K-Feldspar (Orthoclase)—
5.5—Steel knife blade, window glass
5Apatite—
4Fluorite—
3.5—Copper penny
3Calcite—
2.5—Human fingernail
2Gypsum—
1Talc—

Mohs hardness scale reference minerals

  • Luster:
    • Describes the quality and intensity of light reflection from the mineral surface.
    • Metallic Luster: Displayed by opaque ore minerals with high refractive indices (e.g., pyrite, galena).
    • Non-Metallic Luster Categories: Adamantine (brilliant diamond-like luster), Vitreous (glassy, e.g., quartz), Greasy (oily appearance), Dull/Earthy (low reflectivity), Silky (fibrous aggregates like asbestos), Pearly (layered mineral sheets like talc or micas).

Luster variations in minerals

  • Cleavage and Fracture:
    • Cleavage: The tendency of a mineral to split along parallel planes of structural weakness (planes of weakest interatomic chemical bonding).
    • One Direction: Splitting into thin parallel sheets (e.g., micas: muscovite, biotite).
    • Two Directions: Cleaving along two intersecting planes (e.g., feldspars).
    • Three Directions: Cleaving along three perpendicular or rhombohedral planes (e.g., calcite, halite).
    • Fracture: Irregular breaking along non-planar surfaces when atomic bonding strength is equal in all directions (e.g., conchoidal/curved fracture in quartz and opal; uneven, jagged, or fibrous fractures in other minerals).

Cleavage directions in minerals

  • Specific Gravity (SGSG):

    • The ratio of the weight of a given mineral volume to the weight of an equal volume of pure water at 4∘C4^\circ C.
    • Light minerals (SG=1–2SG = 1\text{--}2); Medium-heavy minerals (SG=2–4SG = 2\text{--}4; quartz and feldspars average ~2.652.65); Heavy minerals (SG=4–6SG = 4\text{--}6); Very heavy minerals (SG>6SG > 6).
  • Optical and Special Properties:

    • Transparency: Clear/transparent (writing readable through specimen, e.g., quartz, calcite, halite, topaz), translucent (light passes through without clear images due to impurities), opaque (light blocked entirely).

    • Double Refraction: Splitting of transmitted light rays into two polarized paths (conspicuous in clear optical calcite).

    • Luminescence: Thermoluminescence (light emission upon heating in fluorite); triboluminescence (light emission upon crushing or friction).

    • Diagnostic Chemical & Physical Tests: Calcite effervesces (fizzes) vigorously producing CO2CO_2 gas with dilute 10% HCl10\%\,HCl; graphite leaves a dark gray streak on paper; magnetite exhibits strong ferromagnetism; halite dissolves easily and tastes salty; plagioclase displays parallel striations on cleavage faces.

    • Chemical Classification Scheme of Minerals (Berzelius System):

  • Established by Berzelius (1779–1848), classifying minerals based on dominant anion groups:

  • Silicates: Characterized by the fundamental tetrahedral building block [SiO4]4−[SiO_4]^{4-}. Silicates form over 90% of the Earth's crust. Include independent tetrahedra/island silicates (olivine (Mg,Fe)2SiO4(Mg,Fe)_2SiO_4), single-chain silicates (pyroxenes), double-chain silicates (amphiboles), sheet silicates (micas, kaolinite Si2Al2O5(OH)4Si_2Al_2O_5(OH)_4), and framework silicates (quartz SiO2SiO_2, feldspars).

  • Oxides: Metal cations bonded to oxygen anions (O2−O^{2-}). Examples: magnetite (Fe3O4Fe_3O_4), hematite (Fe2O3Fe_2O_3), goethite (α-FeOOH\alpha\text{-}FeOOH).

  • Sulfides: Metal cations bonded to sulfide anions (S2−S^{2-}). Display metallic luster. Examples: pyrite (FeS2FeS_2), galena (PbSPbS).

  • Sulfates: Metal cations bonded to sulfate complexes (SO42−SO_4^{2-}). Examples: gypsum (CaSO4⋅2H2OCaSO_4 \cdot 2H_2O), anhydrite (CaSO4CaSO_4).

  • Halides: Metal cations bonded to halogen anions (F−F^-, Cl−Cl^-). Examples: halite (NaClNaCl), fluorite (CaF2CaF_2).

  • Carbonates: Metal cations bonded to carbonate complexes (CO32−CO_3^{2-}). Examples: calcite (CaCO3CaCO_3), dolomite (CaMg(CO3)2CaMg(CO_3)_2).

  • Native Elements: Pure elemental masses of single metals/non-metals (e.g., native copper, native gold nuggets, sulfur, graphite, diamond).

  • Precious Stones / Gemstones: Rare, highly durable, beautiful minerals resisting wear (Mohs hardness 7–107\text{--}10; e.g., diamond, ruby, sapphire, emerald, topaz, aquamarine, garnet, amethyst, tourmaline, zircon).

  • Primary vs. Secondary Minerals: Primary minerals form during initial rock crystallization from molten magma (e.g., quartz, feldspars, pyroxenes, micas). Secondary minerals form through chemical weathering and alteration of primary minerals (e.g., clay minerals, iron/aluminum hydroxides, secondary carbonates).

  • Essential vs. Accessory Minerals: Essential minerals form the primary, character-defining constituents of a rock (e.g., quartz and feldspar in granite). Accessory minerals occur in minor amounts (<1%<1\%) without altering the basic classification of the rock (e.g., zircon, apatite, tourmaline, sphene).

Geology, Rock Types & Analytical Techniques

  • Definition and Classification of Rocks:
    • A rock is a coherent, naturally occurring solid aggregate composed of mineral grains, mineraloids, or glass.
    • Clastic Rocks: Grains cemented together by natural chemical precipitates (e.g., silica, calcite, iron oxides).
    • Crystalline Rocks: Rocks whose constituent mineral crystals interlock with one another during growth.
    • Outcrops & Bedrock: Exposed bedrock protruding through the surface soil profile is termed an outcrop.
    • Genetic Classification: Classifies rocks into three major families based on their mode of origin: Igneous, Sedimentary, and Metamorphic.

Three main rock families

  • Descriptive Parameters for Rocks:

    • Grain Size: Dimensions of mineral crystals or clastic fragments (mmmm or cmcm). Can be macroscopic or microscopic, equant or inequant.
    • Mineral Composition: Proportions of distinct minerals making up the rock mass.
    • Texture: Spatial arrangement, orientation, and interconnectivity of constituent mineral grains.
    • Layering: Bedding in sedimentary rocks; metamorphic foliation/banding in metamorphic rocks.
  • Igneous Rocks:

    • Formed from the cooling and solidification of molten rock (magma beneath the surface; lava on the Earth's surface).
    • Intrusive (Plutonic) Igneous Rocks: Magma cools slowly beneath the Earth's crust, allowing large, visible, coarse-grained interlocking crystals to form (phaneritic texture).
    • Extrusive (Volcanic) Igneous Rocks: Lava cools rapidly on the surface, producing fine-grained (aphanitic) or glassy textures.
    • Chemical Classification (Silica Content): Ultramafic (<45% SiO2<45\%\,SiO_2), Mafic (45–52% SiO245\text{--}52\%\,SiO_2; dark grey/black), Intermediate (52–66% SiO252\text{--}66\%\,SiO_2; medium grey/green), Silicic/Felsic (>66% SiO2>66\%\,SiO_2; light tan, pink, or red).
Silica CompositionFine-Grained (Extrusive / Volcanic)Coarse-Grained (Intrusive / Plutonic)
Silicic (Felsic)RhyoliteGranite
IntermediateAndesiteDiorite
MaficBasaltGabbro
UltramaficKomatiitePeridotite
  • Non-Crystalline / Glassy Igneous Varieties:

    • Obsidian: Solid volcanic glass with conchoidal fractures, formed from ultra-rapid cooling of silicic lava.
    • Pumice: Lightweight, highly vesicular volcanic glass formed from frothy lava containing expanded gas bubbles.
    • Scoria: Vesicular volcanic rock from mafic lava where air pores comprise less than 50% of total rock volume.
    • Tuff: Pyroclastic rock composed of consolidated volcanic ash, pumice fragments, and fragmented lava.
  • Chemical Mineralogy of Key Igneous Rocks:

    • Granite Composition: 30% KAlSi3O830\%\,KAlSi_3O_8 (K-feldspar), 30% Na-Ca-Al-Silicate30\%\,\text{Na-Ca-Al-Silicate} (Plagioclase), 30% SiO230\%\,SiO_2 (Quartz), and 10% Micas10\%\,\text{Micas} (Biotite/Muscovite).

    • Basalt Composition: 50% Ca(Mg,Fe)[(SiAl)2O6]50\%\,Ca(Mg,Fe)[(SiAl)_2O_6] (Pyroxene/Augite), 44% Na-Ca-Al-Silicate44\%\,\text{Na-Ca-Al-Silicate} (Plagioclase), and 6% Mg-Fe-SiO46\%\,Mg\text{-}Fe\text{-}SiO_4 (Olivine).

    • Sedimentary Rocks:

  • Formed at or near the Earth's surface through weathering, transport, deposition, chemical precipitation, or biological accumulation.

  • Clastic (Detrital) Sedimentary Rocks: Formed from solid fragments and mineral grains weathered from pre-existing rocks. Process: Weathering →\rightarrow Erosion →\rightarrow Transport →\rightarrow Deposition →\rightarrow Lithification (compaction and cementation).

    • Very Coarse: Breccia (angular rock fragments) and Conglomerate (rounded water-worn pebbles).
    • Coarse: Arkose (quartz and feldspar rich), Sandstone (quartz rich), Greywacke (mixed matrix sand).
    • Fine to Very Fine: Siltstone (fine sand/silt), Shale (fissile clay splitting into thin sheets), Mudstone (non-fissile clay).
  • Biochemical Sedimentary Rocks: Formed from accumulated plant or animal organic debris:

    • Biochemical Limestone: Composed of CaCO3CaCO_3 shells/skeletons. Sub-varieties: Fossiliferous limestone (visible shell fragments), Micrite (fine lime mud), Chalk (microscopic plankton shells).
    • Biochemical Chert: Microcrystalline quartz formed from siliceous plankton tests.
    • Organic Rocks: Coal (combustible rock containing >50%>50\% carbon from accumulated wetland plant debris); Oil Shale (shale containing >50%>50\% organic lipids/proteins from plankton).
  • Chemical Sedimentary Rocks: Formed by direct inorganic chemical precipitation from water solution without clastic burial/cementation:

    • Evaporites: Halite (NaClNaCl), Gypsum (CaSO4⋅2H2OCaSO_4 \cdot 2H_2O) precipitated from evaporating hypersaline water.

    • Travertine: Inorganic calcium carbonate precipitated at cave walls or hot springs.

    • Dolostone: Formed via diagenetic magnesium replacement of calcite in limestone (CaMg(CO3)2CaMg(CO_3)_2).

    • Replacement Chert Varieties: Flint (black chert), Jasper (red iron-rich chert), Petrified Wood (silicified fossil wood), Agate (banded concentric chert).

    • Metamorphic Rocks:

  • Formed from pre-existing protolith rocks (igneous, sedimentary, or older metamorphic) changed by intense heat, confining pressure, differential stress, and chemically active hydro-thermal fluids without melting.

  • Foliated Metamorphic Rocks: Characterized by parallel alignment of platy/elongated minerals or compositional banding (alternating dark and light layers):

    • Slate: Fine-grained, low-grade metamorphism of shale; exhibits slaty cleavage.
    • Phyllite: Fine-grained with silky sheen from aligned fine-grained micas (muscovite, chlorite).
    • Schist: Medium-to-coarse grained with prominent schistosity formed by large visible mica flakes.
    • Amphibolite: Dark rock containing amphibole, plagioclase, and garnet.
    • Gneiss: High-grade metamorphic rock with alternating light (quartz, feldspar) and dark (biotite, amphibole) bands.
    • Migmatite: Mixed rock formed at extreme temperatures where partial melting creates igneous bands within relict gneiss.
  • Non-Foliated Metamorphic Rocks: Recrystallized crystalline minerals lacking directional alignment:

    • Hornfels: Formed by contact thermal metamorphism lacking differential stress.

    • Quartzite: Metamorphosed quartz sandstone forming an interlocking quartz structure.

    • Marble: Metamorphosed limestone or dolostone composed of recrystallized calcite/dolomite.

    • Geology of Zambian Soils:

  • Basement Complex: Comprises ancient granites, acidic gneisses, biotite-rich gneisses, schists, and quartzites. Forms light-textured, acidic sandy loam to sandy clay loam soils with low available phosphorus and low base saturation.

  • Katanga System: Lower Palaeozoic folded metasediments including sandstones, shales, and dolomitic limestones with variable metamorphism.

  • Karroo System: Upper Palaeozoic to Jurassic sediments including sandstones, mudstones, shales, and extensive basalt lava beds underlying the Luangwa Valley, Kafue Flats, and Zambezi Valley.

  • Kalahari / Barotse Sands: Deep, highly leached, unconsolidated eolian quartz sands occupying Western Province and parts of North-Western and Southern Provinces.

  • Recent Alluvium: Deep alluvial deposits occurring across active floodplains (Upper Zambezi, Kafue Flats, Luangwa, Bangweulu, and Lukanga swamps).

Geological map of Zambia showing rock distributions

  • Laboratory and Instrumental Analytical Techniques:
    • Outcrop Observations & Hand Specimens: Field recording of rock relationships and collection of fist-sized hand specimens for macroscopic lens inspection.
    • Thin Section Petrography: Brick-shaped rock chips cut with diamond-rimmed saws are mounted on glass slides with epoxy, ground down to 3/100 mm3/100\,mm (30 μm30\,\mu m) thickness, and analyzed under a petrographic microscope using transmitted polarized light.

Binocular petrographic microscope setup

  • High-Tech Analytical Equipment:
    • Electron Microprobe: Directs a focused electron beam onto micro-regions of mineral grains to determine exact elemental chemical composition.
    • Mass Spectrometry: Measures isotopic ratios of elements for radiometric age dating and isotopic tracing.
    • X-ray Diffractometer (XRD): Analyzes diffraction patterns of X-ray beams passing through mineral crystal lattices to identify mineral phases.

X-ray Diffractometer instrument

- Scanning Electron Microscope (SEM): Produces ultra-high-resolution 3D micro-topographical images and elemental maps (e.g., Hitachi S-4500 SEM).

Scanning Electron Microscope user interface

Factors and Processes of Soil Formation

  • Soil Formation Governing Function:
    • Soil development is represented by Hans Jenny's fundamental equation:

Soil=f(P,C,R,O,T)\text{Soil} = f(P, C, R, O, T)

  • Soil development proceeds at a rate determined by the duration of time (TT) plus the intensities of climate (CC) and organisms (OO), modified by relief (RR) and the nature of parent material (PP).

    • The Five Major Soil-Forming Factors:
  • Parent Material (PP):

    • The unconsolidated, chemically weathered mineral material or organic mass from which the soil profile develops.
    • Grouped by origin into Residual Bedrock (formed in site from igneous, sedimentary, or metamorphic rocks), Transported Sediments (Water-deposited: marine, lacustrine, alluvial, fanglomerate; Wind-deposited: eolian sands, loess silts; Ice-deposited: glacial moraine, till plain, outwash plain; Gravity-deposited: colluvial talus, mudslides), and Organic Accumulations (moss peats, shrub/tree peats, mixed mucks).

Parent material sources tree classification

 - Parent material controls initial texture, chemical composition, mineral stability, and initial fertility (e.g., granite parent material yields acidic, light/sandy soils rich in kaolinite and quartz with low nutrients; basalt parent material yields neutral-to-alkaline, medium-to-heavy textured soils rich in smectites, iron/aluminum oxides, and high base status).
  1. Climate (CC):
    • Exerts regional and global control through temperature and effective precipitation.
    • Governs rates of physical and chemical weathering, biological growth, organic residue decomposition, and nutrient leaching.
    • Soil Moisture Regimes: Perudic (precipitation exceeds evapotranspiration all months), Udic (humid, wet, <90<90 dry days/year), Ustic (semi-arid/sub-humid, moisture present during growing season but >90>90 cumulative dry days), Aridic (dry for most of the year).
  2. Relief / Topography (RR):
    • Influences surface hydrology, soil drainage, erosion, water table depth, and local microclimate along a hillside slope or catena.
    • Slope Catena Profile: Crest/shoulder (shallow, gravelly, well-drained oxidized topsoil); Upper footslope (deep, well-drained red soils with oxidized Fe3+Fe^{3+} and kaolinite); Lower footslope/depression (accumulated clay, poorly drained grey/black soils with reduced Fe2+Fe^{2+} and 2:1 smectite clays).

Topography catena hydrologic runoff diagram

  1. Organisms / Biota (OO):
    • Living plants, animals, fungi, and microflora actively alter soil development.
    • Vegetation affects organic matter additions (grassland soils deposit organic matter deep into the profile via extensive root networks; forest soils deposit organic leaf litter on top);
    • Fauna (earthworms, termites, moles) homogenize topsoil, burrow macropores, and incorporate organic humus.
  2. Time (TT):
    • Duration over which pedogenic processes act uninterrupted.
    • Horizons can begin forming within 200 years under ideal humid tropical conditions; well-developed mature profiles require thousands of years.
    • Weathering Stages Over Time:
      • Early Stage: Dominately primary minerals and amorphous phases; minimal profile differentiation (Entisols, Inceptisols).
      • Intermediate Stage: Formation of 2:1 secondary clay minerals (smectites, illite), moderate nutrient availability (Mollisols, Alfisols).
      • Late Stage: Extreme weathering; dominance of 1:1 clays (kaolinite) and stable hydrous oxides (Fe2O3Fe_2O_3, Al2O3Al_2O_3); low nutrient status (Ultisols, Oxisols).

Mineral changes over time weathering triangle

  • Fundamental Pedogenic Processes:
    • Additions: Inflow of organic residues, dust deposition, flood sediment, or atmospheric rain nutrients.
    • Transformations:
    • Physical Weathering: Mechanical disintegration reducing particle size without chemical alteration.
    • Bowen's Reaction Series: Sequence of mineral crystallization and chemical weathering stability: Olivine / Ca-Plagioclase (least stable, weather fastest) →\rightarrow Pyroxene →\rightarrow Amphibole →\rightarrow Biotite / Na-Plagioclase →\rightarrow K-Feldspar →\rightarrow Muscovite →\rightarrow Quartz (most stable, weather slowest).
    • Chemical Weathering Mechanisms:
      • Solution: Dissolution of soluble minerals by weak carbonic acid rainwater (pH≈5.7pH \approx 5.7):

CO2+H2O⇌H2CO3⇌H++HCO3−CO_2 + H_2O \rightleftharpoons H_2CO_3 \rightleftharpoons H^+ + HCO_3^-

  - Hydrolysis: Reaction of mineral lattices with dissociated H+H^+ or OH−OH^- ions. Breakdown of Na-plagioclase into kaolinite, free Na+Na^+, HCO3−HCO_3^- and silicic acid (H4SiO4H_4SiO_4).
  - Hydration: Physical absorption of water molecules into the mineral crystal matrix (e.g., conversion of anhydrite to gypsum: CaSO4+2H2O→CaSO4⋅2H2OCaSO_4 + 2H_2O \rightarrow CaSO_4 \cdot 2H_2O).
  - Oxidation: Loss of electrons; oxidation of ferrous iron (Fe2+Fe^{2+}) to insoluble ferric iron (Fe3+Fe^{3+}) producing red/brown oxides (Fe2O3Fe_2O_3).
- Organic Decomposition & Humification: Biochemical breakdown of plant materials into stable humic compounds and mineralization releasing plant nutrients (NH4+NH_4^+, NO3−NO_3^-, HPO42−HPO_4^{2-}, SO42−SO_4^{2-}).
  • Translocations: Physical upward or downward movement of clay, organic colloids, dissolved salts, oxides, and carbonates within the soil profile.

    • Eluviation: Washing out/removal of fine constituents from upper horizons (E horizon).
    • Illuviation: Accumulation/deposition of translocated materials into subsoil horizons (B horizon).
  • Losses: Surface erosion (water/wind), subsoil leaching, gaseous volatilization, and nutrient removal via crop harvesting.

    • Selected Global Soil Types:
  • Volcanic Soils (Andisols): Derived from volcanic ash, pumice, and lava. Rich in poorly crystalline allophane minerals; high water retention; highly fertile but exhibit strong phosphate fixation.

  • Deeply Weathered Tropical Soils (Oxisols, Ultisols / Ferralsols): Deep red/yellow soils of humid tropics. Dominately kaolinite 1:1 clays and iron/aluminum oxides; excellent physical permeability and aggregate stability; low chemical fertility, acidic, prone to AlAl toxicity and severe phosphorus fixation.

  • Poorly Developed Soils (Entisols, Inceptisols): Shallow or young soils lacking strong horizonation. Variable fertility (poor on quartzites/sandstones; highly fertile on active alluvial floodplains).

  • Shrinking and Swelling Dark Clays (Vertisols): Rich in 2:1 expanding smectite clays. Shrink and form deep open cracks when dry; swell and become sticky and impermeable when wet. Difficult tilth, high inherent chemical fertility.

Soil Physics: Physical & Dynamic Properties

  • Soil Texture & Particle Size Fractions:
    • Soil texture refers to the relative proportions of sand, silt, and clay particle size fractions in a soil mass (<2.0 mm<2.0\,mm diameter).
    • Fine Earth Fraction: Particles smaller than 2.0 mm2.0\,mm. Coarser material (>2.0 mm>2.0\,mm gravels, cobbles, stones) is screened out prior to analysis.
    • Particle Size Classification Systems:
Classification SystemClaySiltFine SandCoarse Sand
ISSS System<0.002 mm<0.002\,mm0.002–0.02 mm0.002\text{--}0.02\,mm0.02–0.2 mm0.02\text{--}0.2\,mm0.2–2.0 mm0.2\text{--}2.0\,mm
USDA System<0.002 mm<0.002\,mm0.002–0.05 mm0.002\text{--}0.05\,mmVery Fine: 0.05–0.1 mm0.05\text{--}0.1\,mm
Fine: 0.1–0.25 mm0.1\text{--}0.25\,mm
Medium: 0.25–0.5 mm0.25\text{--}0.5\,mm
Coarse: 0.5–1.0 mm0.5\text{--}1.0\,mm
Very Coarse: 1.0–2.0 mm1.0\text{--}2.0\,mm
  • Particle Size Analysis (Mechanical Analysis):
    • Sample Pre-treatment: Destroy organic matter (using H2O2H_2O_2), remove soluble salts and carbonates, and add a chemical dispersing agent (5%5\% sodium hexametaphosphate / Calgon solution: 50 g dm−350\,g\,dm^{-3}) with mechanical stirring to disaggregate clay particles.
    • Stokes' Law of Sedimentation: Particle settling velocity (VV) in a liquid column under gravity is directly proportional to the square of the particle radius (rr):

V=29g(dp−dw)r2ηV = \frac{2}{9}\frac{g (d_p - d_w) r^2}{\eta}

- Where g=9.81 m s−2g = 9.81\,m\,s^{-2}, dp=particle density=2.65×103 kg m−3d_p = \text{particle density} = 2.65 \times 10^3\,kg\,m^{-3}, dw=water density=1.0×103 kg m−3d_w = \text{water density} = 1.0 \times 10^3\,kg\,m^{-3}, η=viscosity of water at 20∘C=0.001 Pa s\eta = \text{viscosity of water at } 20^\circ C = 0.001\,Pa\,s.
- Settling Rates: Medium sand (0.05 cm0.05\,cm diameter) settles at 22 cm s−122\,cm\,s^{-1}; fine sand (0.02 cm0.02\,cm) settles at 3.5 cm s−13.5\,cm\,s^{-1}; medium silt (0.001 cm0.001\,cm) settles at 0.087 cm s−10.087\,cm\,s^{-1}; coarse clay (0.0002 cm0.0002\,cm) settles at 0.00035 cm s−10.00035\,cm\,s^{-1}; fine clay (0.00002 cm0.00002\,cm) settles at 0.0000035 cm s−10.0000035\,cm\,s^{-1}.
  • Bouyoucos Hydrometer Method:
    • Measures suspension density at standard settling times (40 seconds for sand settling out; 2 hours or 8 hours for silt settling out, leaving only clay in suspension).

Hydrometer equipment setup

  • Textural Triangle Determination: Plotted percentages of sand, silt, and clay on the USDA equilateral triangle define textural classes (e.g., sandy loam, clay loam, silt loam).

USDA Textural Triangle plot

  • Soil Structure & Aggregation:

    • Soil structure is the arrangement and organization of primary soil particles (sand, silt, clay) into secondary aggregated units called peds.
    • Bonding Mechanisms: Clay domain to clay domain (cationic bridges, edge-to-face electrostatic attraction); clay to organic matter (hydrogen bonding, van der Waals forces, polyvalent cation bridges); quartz to clay/organic matter; quartz-water-quartz (surface tension films).
    • Structural Grades (Macroscopic Field Evaluation):
    • Grade 0 (Structureless): No observable aggregation; massive if coherent, single grain if non-coherent.
    • Grade 1 (Weak): Poorly formed indistinct peds that break into unaggregated material when disturbed.
    • Grade 2 (Moderate): Well-formed, distinct, moderately durable peds.
    • Grade 3 (Strong): Highly durable peds that adhere weakly to one another and remain intact upon profile excavation.
    • Structural Types / Classes:
    • Granular: Small, spheroidal, non-porous peds common in surface O/A horizons with high organic matter.
    • Crumb: Small, spherical, soft, highly porous peds (1–5 mm1\text{--}5\,mm); optimal for agricultural tilth.
    • Platy: Flat, horizontal plate-like peds; indicates compaction, crusting, or high sodium content.
    • Blocky (Angular Blocky): Block-like peds bounded by sharp angular faces; typical of subsoil clay B horizons.
    • Subangular Blocky: Block-like peds bounded by rounded subangular faces.
    • Prismatic: Vertical column-like peds with flat tops and sharp edges; typical of shrinking/swelling B horizons.
    • Columnar: Vertical column-like peds with rounded caps; diagnostic of alkali/sodic subsoil horizons.
  • Indirect Measures of Soil Structure & Stability:

    • Dry Sieving: Measures aggregate size distribution resisting wind erosion forces.
    • Wet Sieving: Evaluates aggregate stability against water slaking and rainfall raindrop impact.
    • Quantitative Stability Indices:
    • Mean Weight Diameter (MWDMWD):

MWD=∑i=1nxˉiwiMWD = \sum_{i=1}^n \bar{x}_i w_i

  - Where xˉi\bar{x}_i is mean diameter of size fraction ii, and wiw_i is proportion of sample weight in fraction ii.
- Water Stable Aggregates (WSAWSA):

WSA=weight of dry sieved aggregates−sandweight of dry soil−sand×100WSA = \frac{\text{weight of dry sieved aggregates} - \text{sand}}{\text{weight of dry soil} - \text{sand}} \times 100

- Aggregation Index (AI=100−DIAI = 100 - DI), where Disruption Index DI=DVDVmaxDI = \frac{DV}{DV_{max}}. Structural stability is high if AI<1AI < 1, moderate if 1–21\text{--}2, unstable if >2>2
  • Soil Density & Porosity Relationships:
    • Particle Density (ρs\rho_s): Mass per unit volume of solid particles only (excluding pores and water). Standard default average for mineral soil is 2.65 g cm−32.65\,g\,cm^{-3} (2.65 Mg m−32.65\,Mg\,m^{-3}).
    • Bulk Density (ρb\rho_b): Mass of dry soil divided by total bulk volume (solids + pores). Indicates soil compaction and root restriction. Typical uncompacted loam ranges from 1.1–1.4 Mg m−31.1\text{--}1.4\,Mg\,m^{-3}; compacted soils exceed 1.6–1.8 Mg m−31.6\text{--}1.8\,Mg\,m^{-3}.
    • Total Pore Space (TPSTPS):

TPS=(1−ρbρs)×100%TPS = \left(1 - \frac{\rho_b}{\rho_s}\right) \times 100\%

- Sandy soils: 35–45%35\text{--}45\% TPS (large macro-pores, rapid drainage). Clay soils: 40–60%40\text{--}60\% TPS (small micro-pores, high total water retention).
  • Dynamic Applied Stress Properties:
    • Soil Consistence: Resistance to deformation at dry (loose, soft, hard, extremely hard), moist (friable, firm), and wet (non-sticky, sticky, plastic) moisture states.
    • Atterberg Limits & Plasticity:
    • Upper Plastic Limit (Liquid Limit, LL): Moisture content where soil begins to flow under stress.
    • Lower Plastic Limit (Plastic Limit, PL): Moisture content where soil can barely be rolled into a 3 mm3\,mm wire without crumbling.
    • Plasticity Index (PIPI): PI=LL−PLPI = LL - PL. Measures force required to mold soil.
    • Soil Strength: Internal shear strength, compressive resistance, penetrometer resistance, and compaction behavior under wheel traffic.

Soil Physics: Soil Water & Aeration

  • Soil Water Structure and Potentials:
    • Water is an asymmetrical, dipolar molecule exhibiting strong hydrogen bonding, adhesion to charged soil particle surfaces, cohesion to adjacent water molecules, and high surface tension.
    • Energy State of Soil Water (Soil Water Potential, ΨT\Psi_T):

ΨT=Ψm+Ψs+Ψp+Ψg\Psi_T = \Psi_m + \Psi_s + \Psi_p + \Psi_g

- Matric Potential (Ψm\Psi_m): Capillary and adsorptive attraction of soil solid surfaces for water. Always negative (unsaturated soil, Ψm<0\Psi_m < 0; free water reference state, Ψm=0\Psi_m = 0).
- Capillary Equation:

Ψm=−h=2Tcos⁡αrgρw\Psi_m = -h = \frac{2 T \cos\alpha}{r g \rho_w}

- Solute / Osmotic Potential (Ψs\Psi_s): Presence of dissolved solutes in soil solution. Reduces free energy.
- Pressure Potential (Ψp\Psi_p): Hydrostatic pressure head of overlying water in saturated zones (Ψp>0\Psi_p > 0).
- Gravitational Potential (Ψg\Psi_g): Position of water relative to a reference elevation (Ψg=zg\Psi_g = z g).
  • Energy and Tension Units Equivalencies:

    • 1 bar=100 kPa=0.1 MPa=1019.7 cm H2O≈1 atm1\,bar = 100\,kPa = 0.1\,MPa = 1019.7\,cm\,H_2O \approx 1\,atm

    • pFpF Scale: pF=log⁡10∣h∣pF = \log_{10} |h| (where hh is suction height in cm H2Ocm\,H_2O).

    • Soil Water Constants and Availability:

  • Gravitational Water: Water held loosely at potentials >−33 kPa> -33\,kPa (pF<2.54pF < 2.54); drains freely under gravity.

  • Field Capacity (FC): Water content retained after saturated soil drains freely for 48 hours (Ψm=−33 kPa\Psi_m = -33\,kPa or −0.33 bar-0.33\,bar; pF=2.54pF = 2.54).

  • Permanent Wilting Point (PWP): Water content at which plants permanently wilt and cannot recover (Ψm=−1500 kPa\Psi_m = -1500\,kPa or −15 bars-15\,bars; pF=4.2pF = 4.2).

  • Plant Available Water (PAW): Volumetric or gravimetric water retained between Field Capacity and Permanent Wilting Point (PAW=θFC−θPWPPAW = \theta_{FC} - \theta_{PWP}).

  • Hygroscopic Coefficient: Water held tightly as thin molecular films at Ψm=−3100 kPa\Psi_m = -3100\,kPa (pF=4.5pF = 4.5); unavailable to plants.

  • Oven Dry State: Water removed by heating at 105–110∘C105\text{--}110^\circ C for 24 hours (Ψm=−1000 MPa\Psi_m = -1000\,MPa; pF=7.0pF = 7.0).

Soil moisture characteristic pF curve

  • Soil Water Measurement Methods:
    • Gravimetric Method: Standard reference method. Direct weighing of moist soil sample, drying at 105∘C105^\circ C, and reweighing.

θm=mass of wet soil−mass of dry soilmass of dry soil×100\theta_m = \frac{\text{mass of wet soil} - \text{mass of dry soil}}{\text{mass of dry soil}} \times 100

θv=θm×ρbρw\theta_v = \theta_m \times \frac{\rho_b}{\rho_w}

  • Tensiometers: Sealed water-filled tubes with a porous ceramic cup at the base and a vacuum gauge at top. Measures matric suction in the range 0–80 kPa0\text{--}80\,kPa (0–0.8 bar0\text{--}0.8\,bar).

  • Pressure Membrane / Plate Apparatus: Laboratory chamber applying compressed gas pressure up to 1500 kPa1500\,kPa to measure FC and PWP.

  • Indirect Electronic Instruments: Electrical resistance blocks (gypsum blocks measuring electrical resistance inversely proportional to moisture); neutron attenuation probes (measuring thermalized fast neutrons scattered by hydrogen atoms); gamma ray absorption.

    • Water Movement in Soils:
  • Saturated Flow (Darcy's Law): Water flow through fully water-saturated pores (Ψm≥0\Psi_m \ge 0) driven by gravitational and hydrostatic heads:

Q=AKΔHLQ = A K \frac{\Delta H}{L}

v=QA=KΔHLv = \frac{Q}{A} = K \frac{\Delta H}{L}

- Where QQ is discharge rate (cm3 s−1cm^3\,s^{-1}), AA is cross-sectional area (cm2cm^2), KK is saturated hydraulic conductivity (cm s−1cm\,s^{-1}), ΔH\Delta H is hydraulic head loss (cmcm), LL is flow path length (cmcm), vv is flux velocity (cm s−1cm\,s^{-1}).
  • Law of Poiseuille: Flow rate through a capillary tube is proportional to the fourth power of pore radius (r4r^4). Doubling pore radius increases water flow rate by 16 times.
  • Unsaturated Flow: Occurs at potentials <−33 kPa< -33\,kPa. Flow driven primarily by matric potential gradients from wet (high potential) to dry (low potential) areas.
  • Infiltration & Accumulated Intake:
    • Infiltration Rate (II): I=aTnI = a T^n (where aa is constant, TT is time, n<0n < 0).
    • Accumulated Intake Depth (ADAD):

AD=∫0TaTndT=an+1Tn+1AD = \int_0^T a T^n dT = \frac{a}{n+1} T^{n+1}

  • Soil Aeration and Thermal Regime:
    • Gas Exchange Mechanisms: Diffusion (principal process governed by Fick's Law: dQdt=DAdCdx\frac{dQ}{dt} = D A \frac{dC}{dx}) and Mass Flow (driven by barometric pressure, wind, temperature changes, rainfall displacement).
    • Oxygen Diffusion Rate (ODR): ODR values >40×10−4 g m−2 min−1>40 \times 10^{-4}\,g\,m^{-2}\,min^{-1} are necessary for uninhibited root growth.
    • Soil Redox Potential (EhE_h): Aerated soils exhibit Eh>+400 mVE_h > +400\,mV; flooded/anoxic soils drop below −200 mV-200\,mV, causing reduction of Fe3+Fe^{3+} to soluble Fe2+Fe^{2+} and SO42−SO_4^{2-} to H2SH_2S
    • Thermal Energy Balance:

RN=RS−RR=G+H+LE+RLR_N = R_S - R_R = G + H + LE + R_L

- Heat flow in soil occurs by conduction: q=−kdTdLq = -k \frac{dT}{dL} (where kk is thermal conductivity, dTdL\frac{dT}{dL} is thermal gradient).
  • Soil Color Determination:
    • Standardized using the Munsell Color Chart system composed of three dimensions:
    • Hue: Dominant spectral color (e.g., 10YR10YR, 7.5YR7.5YR, 2.5YR2.5YR, 5R5R).
    • Value: Relative lightness or darkness from 0 (absolute black) to 10 (absolute white).
    • Chroma: Relative purity, saturation, or intensity of the spectral color from 0 (neutral grey) to 8+ (vivid brilliance).
    • Notation Format: Hue Value/Chroma (e.g., 10YR 3/210YR\,3/2 dark brown; 2.5YR 4/82.5YR\,4/8 red).

Soil Chemistry: Reactions, Acidity & Ion Exchange

  • Chemical Composition of the Soil System:
    • Elemental Abundance: Oxygen (OO), Silicon (SiSi), Aluminum (AlAl), Iron (FeFe), Calcium (CaCa), Magnesium (MgMg), Sodium (NaNa), Potassium (KK), and Titanium (TiTi).
    • Dissolution Methods for Chemical Analysis:
    • Total Analysis: Hydrofluoric acid and perchloric acid digestion (HF−HClO4HF - HClO_4) in teflon/platinum vessels. Volatilizes silica as SiF4SiF_4 gas:

4HF+SiO2⇌SiF4(g)↑+2H2O4HF + SiO_2 \rightleftharpoons SiF_4(g) \uparrow + 2H_2O

- Total Analysis by Fusion: Sodium carbonate (Na2CO3Na_2CO_3) fusion in nickel crucibles.
- Bioaccessible / Environmentally Available Analysis: Aqua regia extraction (3:1 HCl:HNO33:1\,HCl:HNO_3).
- Bioavailable Nutrient Extractants: Neutral 1M NH4OAc1M\,NH_4OAc (exchangeable cations K+,Ca2+,Mg2+,Na+K^+, Ca^{2+}, Mg^{2+}, Na^+); Olsen 0.5M NaHCO30.5M\,NaHCO_3 at pH 8.5pH\,8.5 (available phosphorus); DTPA (trace metals Fe,Mn,Zn,CuFe, Mn, Zn, Cu); boiling CaCl2CaCl_2 or mannitol (boron).
  • Analytical Quantification Equipment: Atomic Absorption Spectrophotometer (AAS), Inductively Coupled Plasma Atomic Emission Spectrometer (ICP-AES), ICP-Mass Spectrometry (ICP-MS), Colorimetric AutoAnalyzers.

    • Soil Reaction (pHpH) and Causes of Acidity:
  • pHpH Definition: pH=−log⁡10{H+}pH = -\log_{10} \{H^+\}. Ionic product of water Kw={H+}{OH−}=10−14K_w = \{H^+\}\{OH^-\} = 10^{-14} at 20∘C20^\circ C

  • Causes of Soil Acidity:

    • Weathering and leaching of basic cations (Ca2+,Mg2+,K+Ca^{2+}, Mg^{2+}, K^+) leaving acidic cations (Al3+,H+Al^{3+}, H^+).
    • Mineralization and hydrolysis of dissolved aluminum ions (Al3+Al^{3+} is the primary H+ pump in acid soils):

Al3++3H2O⇌Al(OH)3+3H+Al^{3+} + 3H_2O \rightleftharpoons Al(OH)_3 + 3H^+

[Al(H2O)6]3+⇌[Al(H2O)5(OH)]2++H+[Al(H_2O)_6]^{3+} \rightleftharpoons [Al(H_2O)_5(OH)]^{2+} + H^+

- Microorganism and root respiration generating carbonic acid:

CO2+H2O⇌H2CO3⇌HCO3−+H+CO_2 + H_2O \rightleftharpoons H_2CO_3 \rightleftharpoons HCO_3^- + H^+

- Nitrification of ammonium fertilizers:

32O2+NH4+→NO2−+2H++H2O\frac{3}{2} O_2 + NH_4^+ \rightarrow NO_2^- + 2H^+ + H_2O

- Organic matter decomposition yielding weak organic carboxylic acids (R-COOH⇌R-COO−+H+R\text{-}COOH \rightleftharpoons R\text{-}COO^- + H^+).
- Acid atmospheric deposition (acid rain containing HNO3HNO_3 and H2SO4H_2SO_4).
  • Active Acidity vs. Exchangeable Acidity:
    • Active Acidity: H+H^+ ion activity in the immediate soil solution (measured via pHH2OpH_{H_2O}).
    • Exchangeable (Reserve) Acidity: H+H^+ and Al3+Al^{3+} ions held on colloidal exchange sites (measured by leaching with 1M KCl1M\,KCl and titrating with standard NaOHNaOH and NaF/HClNaF/HCl).

pH meter with glass-calomel electrode

  • Charge Characteristics of Soil Colloids:
    • Colloids: Particles smaller than 1 μm1\,\mu m (10−6 m10^{-6}\,m) possessing high specific surface area (10–800 m2 g−110\text{--}800\,m^2\,g^{-1}) and negative or positive surface charges.
    • Sources of Charge:
    • Permanent (Constant) Charge: Generated by Isomorphous Substitution within mineral crystal lattices during formation (e.g., substitution of Al3+Al^{3+} for Si4+Si^{4+} in tetrahedra, or Mg2+Mg^{2+} for Al3+Al^{3+} in octahedra). Independent of soil solution pHpH
    • pH-Dependent (Variable) Charge: Generated by protonation/deprotonation of surface functional groups (–OH\text{--}OH, –COOH\text{--}COOH) on clay edges, iron/aluminum oxides, and organic humus. Charge becomes increasingly negative as pHpH increases.
    • Electric Double Layer (EDL):
    • Composed of the rigid Stern Layer (counterions strongly bound near the colloid surface) and the outer Diffuse Layer (loosely held counterions).
    • Boltzmann Distribution Law:

C±=C0exp⁡(−ZFΨRT)C_{\pm} = C_0 \exp\left(\frac{-Z F \Psi}{R T}\right)

- Lyotropic Adsorption Series (Adsorption preference order):

H+,Al3+≈La3+>Ba2+≈Sr2+>Ca2+>Mg2+≈Cs+>Rb+>NH4+≈K+>Na+≈Li+H^+, Al^{3+} \approx La^{3+} > Ba^{2+} \approx Sr^{2+} > Ca^{2+} > Mg^{2+} \approx Cs^+ > Rb^+ > NH_4^+ \approx K^+ > Na^+ \approx Li^+

  • Ion Exchange Capacities:
    • Cation Exchange Capacity (CEC): Total quantity of exchangeable cations that a soil can adsorb per unit dry mass (cmol(+) kg−1cmol(+)\,kg^{-1} or meq/100 gmeq/100\,g).
    • Cation Equivalent Masses: 1 cmol(+) Ca2+=0.20 g1\,cmol(+)\,Ca^{2+} = 0.20\,g; 1 cmol(+) Mg2+=0.12 g1\,cmol(+)\,Mg^{2+} = 0.12\,g; 1 cmol(+) K+=0.39 g1\,cmol(+)\,K^+ = 0.39\,g; 1 cmol(+) Na+=0.23 g1\,cmol(+)\,Na^+ = 0.23\,g; 1 cmol(+) Al3+=0.09 g1\,cmol(+)\,Al^{3+} = 0.09\,g; 1 cmol(+) H+=0.01 g1\,cmol(+)\,H^+ = 0.01\,g
    • Typical Material CEC Ranges:
    • Organic Humus: 200 cmol(+) kg−1200\,cmol(+)\,kg^{-1} (800–900 m2 g−1800\text{--}900\,m^2\,g^{-1} surface area)
    • Vermiculite: 120–190 cmol(+) kg−1120\text{--}190\,cmol(+)\,kg^{-1}
    • Montmorillonite (Smectite): 60–150 cmol(+) kg−160\text{--}150\,cmol(+)\,kg^{-1}
    • Illite: 10–40 cmol(+) kg−110\text{--}40\,cmol(+)\,kg^{-1}
    • Kaolinite: 3–6 cmol(+) kg−13\text{--}6\,cmol(+)\,kg^{-1}
    • Base Saturation (BS%BS\%), Acid Saturation (AS%AS\%), and Exchangeable Sodium Percentage (ESP%ESP\%):

BS%=∑Exchangeable Bases (Ca2++Mg2++K++Na+)CEC×100BS\% = \frac{\sum \text{Exchangeable Bases } (Ca^{2+} + Mg^{2+} + K^+ + Na^+)}{CEC} \times 100

AS%=∑Exchangeable Acidic Cations (Al3++H+)CEC×100AS\% = \frac{\sum \text{Exchangeable Acidic Cations } (Al^{3+} + H^+)}{CEC} \times 100

ESP%=Exchangeable Na+CEC×100ESP\% = \frac{\text{Exchangeable } Na^+}{CEC} \times 100

- Agricultural Thresholds: AS%>20%AS\% > 20\% causes severe aluminum toxicity; ESP%>15%ESP\% > 15\% causes clay dispersion and destruction of soil structure.
  • Anion Exchange Capacity (AEC) Preference Order:

SiO44−>PO43−>SO42−>NO3−≈Cl−SiO_4^{4-} > PO_4^{3-} > SO_4^{2-} > NO_3^- \approx Cl^-

Soil Biology & Organic Matter Dynamics

  • Soil Macro- and Microorganisms:

    • Macro-animals:
    • Earthworms (Lumbricus terrestris, Allolophora caliginosa): Ingest organic matter and soil, excrete fertile casts enriched in available nutrients and bacteria, create macropores for root aeration, enhance aggregate size and stability. Prefer moist, medium-textured soils with near-neutral pH 5.5–7.0pH\,5.5\text{--}7.0
    • Termites: Rapidly digest dead woody residues; construct extensive mounds; less beneficial to crop tilth than earthworms.
    • Ants: Turn over subsoil and decompose coarse wood.
    • Higher Plant Roots: Primary organic producers; excrete organic acids and mucigel; construct root channels.
    • Microorganisms:
    • Nematodes: Threadworms; saprophytic, predatory, or plant-parasitic (genus Heterodera).
    • Protozoa: Single-celled micro-fauna (5–100 μm5\text{--}100\,\mu m) feeding on bacteria.
    • Soil Algae: Photosynthetic microflora (blue-green, green, diatoms); blue-green algae fix atmospheric N2N_2 in flooded paddy soils.
    • Soil Fungi: Dominant organic decomposers in acid forest soils; molds, yeasts, and mushroom fungi decompose cellulose, starch, gums, and lignin to form humus.
    • Soil Actinomycetes: Filamentous unicellular organisms decomposing resistant organic residues (cellulose, chitin, chitin-lignins) in warm, aerated soils.
    • Soil Bacteria: Unicellular organisms (4–5 μm4\text{--}5\,\mu m); drive elemental transformations: Nitrification (Nitrosomonas converting NH4+→NO2−NH_4^+ \rightarrow NO_2^-; Nitrobacter converting NO2−→NO3−NO_2^- \rightarrow NO_3^-), sulfur oxidation, iron/manganese reduction.
  • Biological Functions & Nutrient Transformations:

    • Organic Matter Decomposition: Conversion of fresh organic tissue into CO2CO_2, water, mineral nutrients, and stable humus.
    • Mineralization: Biological release of inorganic ions (NH4+NH_4^+, NO3−NO_3^-, HPO42−HPO_4^{2-}, SO42−SO_4^{2-}) from organic molecules.
    • Immobilization: Biological assimilation of inorganic ions into microbial cellular tissue.
    • Pesticide Degradation: Microbial breakdown of synthetic organic agrochemicals. Non-degradable persistent compounds are termed recalcitrant.
  • Soil Respiration and Microbial Biomass Measurement:

    • Soil Respiration Reaction:

C6H12O6+6O2→6CO2+6H2O+energyC_6H_{12}O_6 + 6O_2 \rightarrow 6CO_2 + 6H_2O + \text{energy}

  • Measured by trapping evolved CO2CO_2 in standard NaOHNaOH solution inside an airtight incubation jar and titrating unreacted base with standard HClHCl
  • Chloroform Fumigation-Incubation Method (CFIM): Soil is fumigated with CHCl3CHCl_3 vapor to lyse microbial cells, reinoculated with fresh soil, and incubated for 10 days. Microbial Biomass Carbon (MBCMB_C) is calculated from the flush of evolved CO2-CCO_2\text{-}C:

Biomass (mg C/100 g soil)=Flush CO2-Ck\text{Biomass } (mg\,C / 100\,g\text{ soil}) = \frac{\text{Flush } CO_2\text{-}C}{k}

- Where k=0.5k = 0.5 (mineralization efficiency factor).
  • Composition and Dynamics of Soil Organic Matter (SOM):
    • Sources: Plant tissues (tops, leaf litter, root exudates, dead root systems).
    • Fresh Plant Residue Composition: Water (75%75\%), Dry Matter (25%25\%). Dry matter composition: Carbohydrates (60%60\%), Lignins (25%25\%), Proteins (10%10\%), Fats/Waxes/Tannins (5%5\%). Elemental composition of dry matter: Carbon (44%44\%), Oxygen (40%40\%), Ash/Inorganics (8%8\%), Hydrogen (8%8\%).
    • Decomposability Sequence:

Sugars, simple proteins (rapid)>Crude proteins>Hemicelluloses>Cellulose>Fats, waxes>Lignins (very slow)\text{Sugars, simple proteins (rapid)} > \text{Crude proteins} > \text{Hemicelluloses} > \text{Cellulose} > \text{Fats, waxes} > \text{Lignins (very slow)}

  • Humus Fractions & Characterization:
    • Humus comprises 60–80% of total SOM. Dark, amorphous, high molecular weight polymers with aromatic ring structures (polyphenols, polyquinones).
    • Chemical Fractions (based on solubility in acid and alkali):
    • Fulvic Acid: Soluble in both alkali (0.5M NaOH0.5M\,NaOH) and acid (pH 1 HClpH\,1\,HCl). Lightest color (yellow/straw), lowest molecular weight, highest total acidity and functional groups.
    • Humic Acid: Soluble in alkali (0.5M NaOH0.5M\,NaOH), but precipitates as a dark brown/black solid upon acidification to pH 1pH\,1 with HClHCl. Medium molecular weight.
    • Humin: Insoluble in both alkali (0.5M NaOH0.5M\,NaOH) and acid (HClHCl). Darkest color, highest molecular weight, most resistant to microbial degradation.

Organic matter extraction and fractionation flowchart

  • Laboratory Determination of SOM Content:
    • Walkley-Black Wet Oxidation Method: Soil organic carbon is oxidized using excess potassium dichromate (K2Cr2O7K_2Cr_2O_7) in concentrated sulfuric acid (H2SO4H_2SO_4):

2K2Cr2O7+3C+8H2SO4→2K2SO4+2Cr2(SO4)3+3CO2↑+8H2O2K_2Cr_2O_7 + 3C + 8H_2SO_4 \rightarrow 2K_2SO_4 + 2Cr_2(SO_4)_3 + 3CO_2 \uparrow + 8H_2O

- Unreacted dichromate (Cr6+Cr^{6+}) is back-titrated with standard ferrous sulfate (FeSO4FeSO_4).
  • Dry Combustion / Loss on Ignition (LOI): Heating dry soil in a muffle furnace at 375∘C375^\circ C for 4 hours to burn off organic carbon.
  • Organic Matter Calculation: Assumes soil organic matter contains 58%58\% organic carbon:

Soil Organic Matter (%SOM)=% Organic Carbon (%OC)×1.724\text{Soil Organic Matter } (\% SOM) = \% \text{ Organic Carbon } (\% OC) \times 1.724

Soil Morphology, Classification & Diagnostic Horizons

  • Soil Morphology Concepts:

    • Pedon: The smallest three-dimensional volume recognized as an individual soil unit (1–10 m21\text{--}10\,m^2 area, extending down to bedrock or parent material).
    • Polypedon: A contiguous group of similar pedons defining a real soil body on the landscape.
    • Soil Profile: A vertical section of the soil exposing all pedogenic horizons from the surface down to the parent rock.
  • Master Horizons:

    • O Horizon: Surface organic layer dominated by fresh or decomposed plant/animal residues (>20%>20\% organic carbon).
    • A Horizon: Mineral horizon formed at or near the surface, darkened by accumulated organic matter mixed with mineral fraction.
    • E Horizon: Mineral horizon characterized by eluviation (bleached loss of silicate clay, iron, or aluminum, leaving residual quartz silts/sands).
    • B Horizon: Subsoil illuvial horizon characterized by accumulated translocated clay, iron, aluminum, organic matter, or carbonates.
    • C Horizon: Unconsolidated parent material beneath the solum, minimally affected by pedogenic processes.
    • R Horizon: Hard, consolidated bedrock underlying the soil profile.

Soil profile master horizons block diagram

  • Diagnostic Surface Horizons (Epipedons):

    • Mollic: Thick, dark, soft surface horizon high in organic matter (>0.6%>0.6\% OC) with high base saturation (≥50%\ge 50\%).
    • Umbric: Similar to mollic epipedon in color and organic content, but has low base saturation (<50%<50\%).
    • Ochric: Light-colored, thin surface horizon low in organic matter.
    • Histic: Organic surface horizon (20–30%20\text{--}30\% organic carbon) saturated with water for extended periods.
    • Anthropic / Plaggen: Human-made surface horizons modified by long-term cultivation, manuring, or irrigation.
  • Diagnostic Subsurface Horizons (Endopedons):

    • Argillic: Subsoil horizon exhibiting significant illuvial accumulation of silicate clays (Bt horizon).
    • Natric: Argillic horizon with high exchangeable sodium (ESP>15%ESP > 15\%) and columnar/prismatic structure.
    • Spodic: Illuvial accumulation of organic matter and aluminum/iron oxides (Bh/Bs horizons in sandy soils).
    • Cambic: Weakly developed subsoil horizon showing color/structure change without significant illuviation (Bw horizon).
    • Oxic: Highly weathered horizon dominated by kaolinite 1:1 clays and hydrous Fe/Al oxides; extremely low CEC (≤16 cmol(+) kg−1\le 16\,cmol(+)\,kg^{-1} clay).
    • Albic: Light-colored bleached eluviated horizon (EE horizon).
    • Calcic: Accumulation of secondary calcium carbonate (CaCO3CaCO_3; Bk horizon).
    • Salic: Accumulation of soluble salts (EC>30 dS m−1EC > 30\,dS\,m^{-1}).
    • Duripan: Hard pan silica-cemented subsoil horizon.
  • Systematic Hierarchical Levels of Soil Taxonomy (USDA System):

    • Order (12 global categories) →\rightarrow Suborder (54) →\rightarrow Great Group (238) →\rightarrow Subgroup (1922) →\rightarrow Family (>5000>5000) →\rightarrow Series (e.g., Makeni series).
    • The 12 Global Soil Orders:
    • Entisols: Embryonic, undeveloped soils lacking subsoil diagnostic horizons.
    • Inceptisols: Young soils showing weak subsoil horizon development (cambic horizon).
    • Andisols: Soils formed from volcanic ash and cinders dominated by allophane minerals.
    • Histosols: Organic soils (peats and mucks) containing >20–30%>20\text{--}30\% organic matter.
    • Aridisols: Dry soils of arid climates possessing calcic, gypsic, or salic horizons.
    • Mollisols: Dark, fertile grassland soils with high base status mollic epipedons.
    • Vertisols: Dark clay soils dominated by expanding 2:1 smectites; shrink/crack when dry.
    • Alfisols: Moderately leached fertile soils with argillic subsoil clay accumulation and high base saturation (≥35%\ge 35\%).
    • Spodosols: Acidic, sandy forest soils with dark spodic subsurface illuvial accumulation of Fe/Al and humus.
    • Ultisols: Strongly leached, acidic tropical/subtropical soils with argillic clay accumulation and low base saturation (<35%<35\%).
    • Oxisols: Highly weathered, oxidized tropical soils dominated by Fe/Al oxides and kaolinite.
    • Gelisols: Cold soils underlain by permanent permafrost.

Soil Technology, Conservation & Geoengineering

  • Causes and Impact of Land Degradation:

    • Land degradation represents the loss of soil utility, biological productivity, and environmental quality.
    • Primary Drivers: Water/wind erosion, physical structure destruction (crusting, hardpan compaction), nutrient mining (crop harvesting without fertilizer replenishment), acidification, salinization, chemical contamination, overgrazing, and deforestation.
  • Soil Conservation & Rehabilitation Practices:

    • Conservation Agriculture: Minimal soil disturbance (zero/minimum tillage, ripping, sub-soiling), permanent organic soil cover (residue retention, mulch), and diversified crop rotations.
    • Biological Practices: Cover cropping, green manuring, alley cropping, agroforestry windbreaks, vegetative contour hedges.
    • Mechanical Methods: Terracing, contour ridging, check dams, storm water diversion drains.
    • Soil Loss Modeling (RUSLE 2 - Revised Universal Soil Loss Equation):

A=R×K×LS×C×PA = R \times K \times LS \times C \times P

- Where AA is computed soil loss per unit area, RR is rainfall erosivity, KK is soil erodibility, LSLS is slope length-steepness factor, CC is cover management, PP is supporting practice factor.
  • Reclamation of Problem Soils:

    • Acid Soils: Ameliorated by applying agricultural liming materials (calcitic limestone CaCO3CaCO_3, dolomitic limestone CaMg(CO3)2CaMg(CO_3)_2) to neutralize exchangeable Al3+Al^{3+} and H+H^+ and raise soil pHpH
    • Saline / Sodic Soils: Saline soils (EC>4 dS m−1EC > 4\,dS\,m^{-1}, ESP<15%ESP < 15\%) reclaimed by leaching excess soluble salts with high-quality water through subsoil drainage networks. Sodic soils (ESP>15%ESP > 15\%) require application of gypsum (CaSO4⋅2H2OCaSO_4 \cdot 2H_2O) to replace exchangeable Na+Na^+ with Ca2+Ca^{2+} prior to leaching.
    • Contaminated / Polluted Soils: Phytoremediation using hyperaccumulating plant species to extract heavy metals or organic contaminants into harvestable plant biomass.
  • Soil Geoengineering Applications:

    • Soil Compaction Mechanics: Mechanical reduction of air pore volume to increase soil dry bulk density, increase load-bearing support capacity, eliminate structure settlement, and decrease permeability.
    • Compaction Forces:
    • Static Force: Deadweight pressure of compaction equipment (kneading, smooth steel rollers).
    • Vibratory Force: Engine-driven mechanical impacts creating sequential rapid downward force pulses (vibratory rollers, rammers).
    • Material Behavior under Compaction (AASHTO Groups):
    • Cohesive Soils (Clays/Silts): Dense, plastic when wet; require high impact or kneading pressure at optimum moisture content.
    • Granular Soils (Sands/Gravels): High permeability; obtain maximum density under vibratory compaction forces.
    • Waste Management Liners: Compacted clay barriers and engineered organo-clay complexes engineered for low hydraulic conductivity (K≤10−7 cm s−1K \le 10^{-7}\,cm\,s^{-1}) to prevent leachate migration from landfills and sewage lagoons.

Laboratory Protocols, Worked Examples & Practice Questions

  • Laboratory Protocol 1: Particle Size Analysis by Hydrometer Method:
    • Procedure:
    1. Weigh 50.0 g50.0\,g of air-dry soil passed through a 2.0 mm2.0\,mm sieve (correct for soil moisture d%d\% to obtain equivalent oven-dry mass).
    2. Place sample in a dispersing cup, add 50 cm350\,cm^3 of 5%5\% Calgon (sodium hexametaphosphate) solution, bring to half-volume with distilled water, and mix continuously with a mechanical stirrer for 5 minutes.

Mechanical stirrer and dispersion cup

3. Transfer suspension completely into a 1000 cm31000\,cm^3 sedimentation cylinder, bring to volume with distilled water, plunge thoroughly, and record temperature.

Hydrometer cylinder setup

4. Lower the Bouyoucos hydrometer carefully and record hydrometer density readings at 40 seconds (R40sR_{40s}) and at 8 hours (R8hR_{8h}).
5. Determine blank correction factor C1C_1 for dispersing agent, and temperature correction factors C2C_2 and C3C_3 (add 0.4 g dm−30.4\,g\,dm^{-3} per 1∘C1^\circ C above 20∘C20^\circ C; subtract if below 20∘C20^\circ C).
  • Sample Dataset & Calculations (MUFARM 0024 sample):
    • Sample dry weight = 50.5 g50.5\,g
    • Moisture content d=1.385%d = 1.385\%
    • 40-second reading R40s=14.80 g dm−3R_{40s} = 14.80\,g\,dm^{-3} at 28∘C28^\circ C
    • 8-hour reading R8h=4.00 g dm−3R_{8h} = 4.00\,g\,dm^{-3} at 29∘C29^\circ C
    • Blank correction C1=1.0 g dm−3C_1 = 1.0\,g\,dm^{-3}
    • Temperature correction at 40s (28∘C28^\circ C): C2=(28−20)×0.4=+3.2C_2 = (28 - 20) \times 0.4 = +3.2
    • Temperature correction at 8h (29∘C29^\circ C): C3=(29−20)×0.4=+3.6C_3 = (29 - 20) \times 0.4 = +3.6
    • Percent Sand Calculation:

% Silt + Clay=R40s−C1+C2sample weight×100=14.80−1.0+3.250.5×100=17.050.5×100=33.66%\% \text{ Silt + Clay} = \frac{R_{40s} - C_1 + C_2}{\text{sample weight}} \times 100 = \frac{14.80 - 1.0 + 3.2}{50.5} \times 100 = \frac{17.0}{50.5} \times 100 = 33.66\%

% Sand=100%−33.66%=66.34%(≈66%\% \text{ Sand} = 100\% - 33.66\% = 66.34\% \quad (\approx 66\%

- Percent Clay Calculation:

% Clay=R8h−C1+C3sample weight×100=4.00−1.0+3.650.5×100=6.650.5×100=13.07%(≈16% in reference example)\% \text{ Clay} = \frac{R_{8h} - C_1 + C_3}{\text{sample weight}} \times 100 = \frac{4.00 - 1.0 + 3.6}{50.5} \times 100 = \frac{6.6}{50.5} \times 100 = 13.07\% \quad (\approx 16\% \text{ in reference example})

- Percent Silt Calculation:

% Silt=100%−% Sand−% Clay=100%−66%−16%=18%\% \text{ Silt} = 100\% - \% \text{ Sand} - \% \text{ Clay} = 100\% - 66\% - 16\% = 18\%

- Plotting 66%66\% sand, 18%18\% silt, 16%16\% clay on the USDA triangle yields **Sandy Loam** texture.
  • Worked Example: Soil Core Density Calculation:
    • Problem: A soil core of volume 35.325 cm335.325\,cm^3 weighed 80.553 g80.553\,g in an air-dry state containing 6.275%6.275\% moisture. Calculate the dry bulk density.
    • Solution:

Mass of Oven-Dry Soil=Air-Dry Weight1+% moisture100=80.5531+0.06275=80.5531.06275=75.800 g\text{Mass of Oven-Dry Soil} = \frac{\text{Air-Dry Weight}}{1 + \frac{\% \text{ moisture}}{100}} = \frac{80.553}{1 + 0.06275} = \frac{80.553}{1.06275} = 75.800\,g

Bulk Density (ρb)=Oven-Dry MassCore Volume=75.800 g35.325 cm3=2.146 g cm−3(2.146 Mg m−3)\text{Bulk Density } (\rho_b) = \frac{\text{Oven-Dry Mass}}{\text{Core Volume}} = \frac{75.800\,g}{35.325\,cm^3} = 2.146\,g\,cm^{-3} \quad (2.146\,Mg\,m^{-3})

  • Worked Example: Cylinder Bulk Density and Porosity:
    • Problem: Metal cylinder height h=5.0 cmh = 5.0\,cm, inside diameter d=4.4 cmd = 4.4\,cm (r=2.2 cmr = 2.2\,cm). Oven-dry soil mass = 87.8 g87.8\,g. Standard ρs=2.65 g cm−3\rho_s = 2.65\,g\,cm^{-3}. Calculate ρb\rho_b and Total Pore Space (TPSTPS).
    • Solution:

Volume (V)=πr2h=π(2.2)2(5.0)=3.14159×4.84×5.0=76.026 cm3\text{Volume } (V) = \pi r^2 h = \pi (2.2)^2 (5.0) = 3.14159 \times 4.84 \times 5.0 = 76.026\,cm^3

Bulk Density (ρb)=87.8 g76.026 cm3=1.155 g cm−3(1.155 Mg m−3)\text{Bulk Density } (\rho_b) = \frac{87.8\,g}{76.026\,cm^3} = 1.155\,g\,cm^{-3} \quad (1.155\,Mg\,m^{-3})

TPS=(1−ρbρs)×100%=(1−1.1552.65)×100%=(1−0.4358)×100%=56.42%TPS = \left(1 - \frac{\rho_b}{\rho_s}\right) \times 100\% = \left(1 - \frac{1.155}{2.65}\right) \times 100\% = (1 - 0.4358) \times 100\% = 56.42\%

  • Worked Example: Cation Exchange Capacity (CECCEC) Calculation:
    • Problem: 20.0 g20.0\,g of soil was leached with 1M NH4OAc1M\,NH_4OAc. Measured cations in leachate: Ca2+=0.046 gCa^{2+} = 0.046\,g, Mg2+=0.00516 gMg^{2+} = 0.00516\,g, K+=0.00312 gK^+ = 0.00312\,g (3.12 mg3.12\,mg), Na+=0.00069 gNa^+ = 0.00069\,g (0.69 mg0.69\,mg). Leaching with 1M KCl1M\,KCl yielded exchangeable Al3+=0.18 cmol(+) kg−1Al^{3+} = 0.18\,cmol(+)\,kg^{-1} and H+=0.05 cmol(+) kg−1H^+ = 0.05\,cmol(+)\,kg^{-1}. Calculate total CECCEC
    • Conversion Factors (1 cmol(+)1\,cmol(+) mass):
    • Ca2+Ca^{2+}: 0.20 g/cmol(+)0.20\,g/cmol(+)
    • Mg2+Mg^{2+}: 0.12 g/cmol(+)0.12\,g/cmol(+)
    • K+K^+: 0.39 g/cmol(+)0.39\,g/cmol(+)
    • Na+Na^+: 0.23 g/cmol(+)0.23\,g/cmol(+)
    • Step-by-step Conversion to cmol(+) kg−1cmol(+)\,kg^{-1}:

Ca2+=0.046 g20 g soil×1 cmol(+)0.20 g×1000 g/kg=11.50 cmol(+) kg−1Ca^{2+} = \frac{0.046\,g}{20\,g\text{ soil}} \times \frac{1\,cmol(+)}{0.20\,g} \times 1000\,g/kg = 11.50\,cmol(+)\,kg^{-1}

Mg2+=0.00516 g20 g soil×1 cmol(+)0.12 g×1000 g/kg=2.15 cmol(+) kg−1Mg^{2+} = \frac{0.00516\,g}{20\,g\text{ soil}} \times \frac{1\,cmol(+)}{0.12\,g} \times 1000\,g/kg = 2.15\,cmol(+)\,kg^{-1}

K+=0.00312 g20 g soil×1 cmol(+)0.39 g×1000 g/kg=0.40 cmol(+) kg−1K^+ = \frac{0.00312\,g}{20\,g\text{ soil}} \times \frac{1\,cmol(+)}{0.39\,g} \times 1000\,g/kg = 0.40\,cmol(+)\,kg^{-1}

Na+=0.00069 g20 g soil×1 cmol(+)0.23 g×1000 g/kg=0.15 cmol(+) kg−1Na^+ = \frac{0.00069\,g}{20\,g\text{ soil}} \times \frac{1\,cmol(+)}{0.23\,g} \times 1000\,g/kg = 0.15\,cmol(+)\,kg^{-1}

Al3+=0.18 cmol(+) kg−1Al^{3+} = 0.18\,cmol(+)\,kg^{-1}

H+=0.05 cmol(+) kg−1H^+ = 0.05\,cmol(+)\,kg^{-1}

  • Summing Exchangeable Cations:

CEC=11.50+2.15+0.40+0.15+0.18+0.05=14.43 cmol(+) kg−1CEC = 11.50 + 2.15 + 0.40 + 0.15 + 0.18 + 0.05 = 14.43\,cmol(+)\,kg^{-1}

  • Base Saturation Percentage (BS%BS\%):

BS%=11.50+2.15+0.40+0.1514.43×100=14.2014.43×100=98.41%BS\% = \frac{11.50 + 2.15 + 0.40 + 0.15}{14.43} \times 100 = \frac{14.20}{14.43} \times 100 = 98.41\%

  • Water Potential Conversion Table Reference:
Suction Head H (cm)H\,(cm)Potential Ψ (J kg−1)\Psi\,(J\,kg^{-1})Potential Ψ (bar)\Psi\,(bar)Potential Ψ (MPa)\Psi\,(MPa)
00000000
10.210.2−1-1−0.01-0.01−0.001-0.001
51.051.0−5-5−0.05-0.05−0.005-0.005
102102−10-10−0.10-0.10−0.010-0.010
306306−30-30−0.30-0.30−0.030-0.030
10201020−100-100−1.00-1.00−0.100-0.100
1530015300−1500-1500−15.00-15.00−1.500-1.500
  • Transcribed Course Examinations and Quizzes:
    • Quiz 1 (15 October 2010):
    1. To which rock sub-groups do the following belong: (a) Rhyolite [Silicic/Felsic Fine-grained Extrusive Igneous], (b) Breccia [Very Coarse Clastic Sedimentary], (c) Limestone [Biochemical/Chemical Sedimentary], (d) Gneiss [Foliated Metamorphic], (e) Quartzite [Non-foliated Metamorphic].
    2. To which mineral classes do the following belong: (a) Pyroxene [Silicate], (b) Hematite [Oxide], (c) Pyrite [Sulfide], (d) Dolomite [Carbonate].
    3. Dilution Math Problem: A soil sample is extracted with an acidic aqueous solution. 10 cm310\,cm^3 of extract is transferred into a 25 cm325\,cm^3 flask and made up to volume. 2 cm32\,cm^3 of this solution is transferred into a 500 cm3500\,cm^3 flask and made up to volume. Zinc concentration in the final solution was 0.36 mg Zn dm−30.36\,mg\,Zn\,dm^{-3}. What is the concentration in the initial extract?
      • Calculation:
        • Final flask concentration C2=0.36 mg dm−3C_2 = 0.36\,mg\,dm^{-3}
        • Concentration in 25 cm325\,cm^3 flask C1=C2×500 cm32 cm3=0.36×250=90.0 mg dm−3C_1 = C_2 \times \frac{500\,cm^3}{2\,cm^3} = 0.36 \times 250 = 90.0\,mg\,dm^{-3}
        • Concentration in initial extract C0=C1×25 cm310 cm3=90.0×2.5=225.0 mg Zn dm−3C_0 = C_1 \times \frac{25\,cm^3}{10\,cm^3} = 90.0 \times 2.5 = 225.0\,mg\,Zn\,dm^{-3}
    • Test 1 (26 October 2010):
    1. (a) Discuss the methods used to study rocks and minerals (outcrop observations, thin section petrography, high-tech analytical equipment: electron microprobe, mass spectrometry, XRD, SEM).        (b) Discuss the geological systems of Zambia (Basement, Katanga, Karroo, Kalahari/Barotse sands, Recent Alluvium).
    2. Core Density Problem (V=35.325 cm3V = 35.325\,cm^3, wet weight 80.553 g80.553\,g, 6.275%6.275\% moisture; solved above as 2.146 g cm−32.146\,g\,cm^{-3}).
    3. Discuss the fundamental processes of soil formation (Additions, Transformations, Translocations, Losses).
    4. Discuss the study of soil as a science (Pedological vs Edaphological approaches, branches of soil science).
    • Test 2 (6 December 2010):
    1. (a) Discuss methods for measuring soil water content (Gravimetric, Tensiometers, Pressure plate, Resistance blocks, Neutron probes, Gamma ray absorption).        (b) Define and show formulas for Gravimetric percent (θm\theta_m), Volumetric percent (θv\theta_v), Water height (H=θv×depthH = \theta_v \times \text{depth}), Accumulated intake depth (AD=∫IdTAD = \int I dT).
    2. (a) Discuss measurement of aggregate stability as an indirect measure of soil structure (Dry/Wet sieving, MWD, WSA, Aggregation Index).        (b) Estimate % sand, % silt, and % clay from hydrometer test data (MUFARM 0024 dataset solved step-by-step above).
    • Take-Home Quiz (9 December 2010):
    1. Unit Conversions: Convert 3.7 g KCl3.7\,g\,KCl in 2 L2\,L water to ppmppm (1850 ppm KCl1850\,ppm\,KCl), molarity (0.0248 M0.0248\,M), and normality (0.0248 N0.0248\,N). Convert 46 ppm Ca2+46\,ppm\,Ca^{2+} to equivalents (0.0023 eq L−10.0023\,eq\,L^{-1} or 2.3 meq L−12.3\,meq\,L^{-1}).
    2. Calculate (a) H+H^+ activity for pH=8.35pH = 8.35 (H+=10−8.35=4.47×10−9 M{H^+} = 10^{-8.35} = 4.47 \times 10^{-9}\,M), (b) pHpH of 0.001 M NaOH0.001\,M\,NaOH (pOH=3.0→pH=11.0pOH = 3.0 \rightarrow pH = 11.0).
    3. Soil Sample Exchangeable Cation Dataset: Sample weight = 35.476 g35.476\,g. Concentrations: Ca2+=46 ppmCa^{2+} = 46\,ppm, Mg2+=31.6 ppmMg^{2+} = 31.6\,ppm, K+=32.3 ppmK^+ = 32.3\,ppm, Na+=6.9 ppmNa^+ = 6.9\,ppm, Al3+=5.4 ppmAl^{3+} = 5.4\,ppm, H+=5.0 ppmH^+ = 5.0\,ppm. Calculate CECCEC, BS%BS\%, AS%AS\%, and ESP%ESP\% and comment on soil fertility status.