Soil solid phase (3-5)

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53 Terms

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Organic matter in soil: C cycle

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Soil one of the most important C reserve on earth

Nitrogen important for soil, organism in the soil can catch it in the atmosphere and break it for the soil → fertilizer are Nitrogen already broken for the soil

OM → Source of C and energy

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Organic matter composition

Composition of the OM: C (50%), H, O, N, S, P and metal cations

Changes from soil to soil, from season to season…

Content of OM in the topsoil:

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Concentration vs Stock of organic C

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Content*(density or area) → stock

Concentration is important but stock also

Global stock C distribution

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More in the soil than in plants, more in colder places cause there are less organism

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Soil OM: global fluxes and stocks

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OM in soil definitions

Organic matter = humus in the broad sense: all dead plant and dead animal substances in and on the mineral soil and their organic transformation products

Edaphon (soil biota): living organisms and roots → not part of the soil organic matter

Mineralization: complete microbial degradation to inorganic substances

Humification: formation of humus = protection of OM from further decomposition

Decomposition: breakdown of organic matter → transformation of organic residues by heterotrophic organisms leads to differentiation of the organic matter:

  • Plant remains

  • Microbial remains

  • Mineral-bound organic substance

  • Charcoal

  • Dissolved organic carbon (DOC)

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C/N Ratio

Indicator for the ease of decomposition of OM but also for biological activity

Mineralisation = release of CO2 while N is incorporated into microbial biomass → C/N becomes smaller → C/N ratio goes lower when you lose carbon, because Nitrogen doesn't get lost

Degradability of organic matter: the smaller the more degradable → spruce woods really degradable

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Composition of OM: Plant remains

Parenchyma (basic tissue)

  • Found in living green tissues (leaves, needles, fine roots)

  • Cell walls mainly contain cellulose and hemicellulose

  • Rich in proteins

  • Low C/N ratio (< 50)

  • Easily degradable

Lignified tissue

  • Includes wood (xylem) and supporting tissue (sclerenchyma)

  • Cell walls contain cellulose, hemicellulose, and lignin

  • High C/N ratio (> 100)

  • Structurally strong and resistant to decomposition

Cellulose

  • Main structural component of plant cell walls

  • Long chains of glucose forming strong microfibrils

  • Mostly crystalline, partly amorphous

  • Provides mechanical strength

  • Usually associated with hemicellulose and lignin

Hemicellulose

  • Cell wall polysaccharides made of different sugars

  • Shorter and more branched than cellulose

  • Amorphous and easily degradable

  • Links cellulose microfibrils together

Lignin

  • Very complex and highly cross-linked polymer

  • Common in vascular and woody plant tissues

  • Provides rigidity, protection, and resistance to microbes

  • Very resistant to degradation (not easily broken down)

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Composition of OM: Plant wax and fats

Lipids

  • Mostly unbranched hydrocarbon chains

  • Chemically diverse group (fatty acids, phospholipids, glycolipids)

  • Key components of biological membranes

  • Important for energy storage and waterproofing

  • Generally more resistant to degradation than carbohydrates

Cutin

  • Structural polymer forming the plant cuticle (wax layer)

  • Found on the surface of leaves and stems

  • Built from hydroxy fatty acids

  • Provides protection against water loss and pathogens

  • Contributes to plant resistance and durability

Suberin

  • Cell wall component in outer tissues of woody plants

  • Especially abundant in bark and roots

  • Similar to cutin but made of longer-chain components

  • Acts as a strong barrier to water, gases, and microbes

  • Very resistant to biological degradation

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Composition of OM: cellular constituent

Proteins

  • Long chains of amino acids (polypeptides)

  • Present in plant and microbial tissues

  • Readily degradable by many microorganisms

  • Important nutrient source (especially nitrogen)

  • Less stable than structural compounds like lignin

Tannins

  • Polyphenolic compounds

  • Bind to proteins and reduce their availability

  • Can slow down microbial decomposition

  • Common in leaves, bark, and woody tissues

Other Cellular Compounds

  • Pigments: e.g. chlorophyll

  • Starch: energy storage compound in plants

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Nitrogen, sulphur and phosphorus in OM

Nitrogen → Almost exclusively binding to OM in soil (95%) → First in microbial biomass, then stabilized in OM → Mostly in peptides

Sulfur: → up to 90% S in organic form, 30 - 75% as organo sulphates, rest as amino acids

Phosphorus → > 50% bound in the form of orthophosphate

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Mineralization and humification

Mineralization

  • Microbial breakdown of organic matter into inorganic nutrients

  • Produces carbon dioxide, water, and plant-available nutrients

  • Fast for easily degradable compounds (carbohydrates, proteins)

  • Leads to nutrient release into soil solution

Humification

  • Transformation of organic residues into stable humic substances

  • Favored by resistant compounds (lignin, fats, waxes, tannins)

  • Slower process than mineralization

  • Contributes to long-term carbon storage in soils

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Decomposition of litter

  • Plant litter is decomposed by microorganisms and soil fauna

  • Early phase: biochemical breakdown of simple compounds

  • Initial phase: leaching and rapid microbial growth

  • Crushing phase: mechanical fragmentation by soil fauna

  • Final phase: enzymatic degradation, nutrient release, accumulation of resistant compounds

Key idea: Litter decomposition drives nutrient cycling and soil organic matter formation.

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Biochemistry of degradation processes

Biochemistry of Degradation Processes

  • Easily degradable polymers are enzymatically hydrolyzed early

    • Proteins, starch, nucleic acids, simple lipids

  • Complex and resistant compounds require prior physical breakdown

    • Cellulose: degraded by specialized enzyme systems

    • Lignin: broken down via oxidative reactions

  • End result: small molecules that serve as microbial food

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Speed of litter degradation

Litter factors (degradability):

  • N content of the substance (C/N ratio)

  • Lignin content (lignin/N ratio)

  • Tannin content (polyphenol/N ratio)

External factors, environmental factors:

  • Heat/temperature

  • Availability of H2O and O2

  • pH

  • Inhibitors (bactericides, fungicides)

<p>Litter factors (degradability):</p><ul><li><p>N content of the substance (C/N ratio) </p></li><li><p>Lignin content (lignin/N ratio) </p></li><li><p>Tannin content (polyphenol/N ratio)</p></li></ul><p>External factors, environmental factors:</p><ul><li><p>Heat/temperature </p></li><li><p>Availability of H2O and O2 </p></li><li><p>pH </p></li><li><p>Inhibitors (bactericides, fungicides)</p></li></ul><p></p>
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Stabilisation of OM

Stabilisation (Humification)

  • Processes that slow down organic matter decomposition

  • Leads to accumulation of humus in soil

  • Stabilized organic matter is older and more persistent

Stabilisation by Recalcitrance

  • Delayed degradation due to molecular structure

  • Primary recalcitrance: plant-derived compounds with resistant structures (litter, roots)

  • Secondary recalcitrance: microbial and animal products forming resistant macromolecules

  • Includes pyrogenic (black) carbon, highly resistant

Key Idea → Chemical complexity increases resistance to microbial breakdown

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Old and new concept of stabilisation

Old Concept

  • Soil organic matter forms large, stable humic macromolecules

  • Stabilisation driven mainly by chemical condensation reactions

  • Humic substances (humic acids, fulvic acids, humin) seen as real soil entities

  • Molecular complexity = long-term stability

New Concept

  • Soil organic matter is mostly made of small, simple biomolecules

  • Stability depends on environmental protection, not molecular size

  • Key mechanisms: mineral association, physical protection, limited microbial access

  • Carbon persistence is dynamic and can change with conditions

Key Idea → Soil carbon is stabilized by its environment, not by intrinsic “humic” polymers

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Stabilization through sorption and aggregation

Stabilisation through Sorption

  • Organic matter binds to mineral surfaces (clays, metal oxides)

  • Sorption reduces accessibility for microbes and enzymes

  • Strong organo-mineral associations increase persistence

  • Particularly important for small organic molecules

Stabilisation through Aggregation (Physical Disconnection)

  • Organic matter is physically protected inside soil aggregates

  • Limited access of microorganisms, oxygen, and enzymes

  • Larger aggregates store carbon short- to medium-term

  • Mineral-associated organic matter enables long-term storage

Key Idea → Soil carbon stability is controlled by physical protection and mineral interactions, not by molecular complexity alone

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Importance of organic matter for soil

  • Major nutrient source for plants (especially nitrogen, phosphorus, sulfur)

  • Improves nutrient retention and gradual release

  • Enhances soil aggregation and structural stability

  • Reduces erosion through clay–organic matter complexes

  • Increases water-holding capacity

  • Influences soil temperature via light absorption

  • Supports decomposition of organic pollutants

  • Key reservoir for carbon storage (e.g. peatlands, permafrost, biochar)

Key Idea: Soil organic matter is essential for soil fertility, structure, and climate regulation.

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Humus forms

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Mull

  • Most favorable humus form

  • Nutrient-rich soils

  • Neutral to slightly acidic

  • High microbial and soil fauna activity

  • Fast litter decomposition

  • No distinct organic (Oa) layer

  • Typical of deciduous forests and species-rich grasslands

Moder

  • Intermediate between Mull and Mor

  • Neutral to slightly acidic

  • Moist conditions

  • Moderate biological activity

  • Oi, Oe, and Oa horizons present with gradual boundaries

  • Common in coniferous, mixed, and deciduous forests

Mor

  • Least favorable humus form

  • Nutrient-poor soils

  • Acidic, often very wet or very dry

  • Low microbial and animal activity

  • Fungi-dominated decomposition

  • Thick litter layer, slow decomposition

  • Sharp boundaries between Oi, Oe, and Oa

  • Typical of coniferous forests and harsh environments

Key Idea:
Humus forms reflect decomposition intensity, biological activity, and nutrient availability.

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Parent material → Rocks

Soils are made of organic matter and rocks from the bedrock, also called parent material.

The parent rock of a soil largely determines the soil development and the mineral content.

Rocks are classified according to their history of origin: Magmatic, metamorphic and sedimentary

Magmatic rock soil properties:

  • Basalt / Gabbro → base-rich, nutrient-rich

  • Andesite / Diorite → intermediate

  • Rhyolite / Granite → silica-rich, nutrient-poor

  • Extrusive: fine-grained, chemical weathering dominant

  • Intrusive: coarse-grained, physical weathering dominant

  • Key idea: More silica → fewer bases → lower soil fertility.

Sedimentary rocks:

  • Clastic: formed from mechanical weathering (e.g. sandstone, shale)

  • Chemical: formed by precipitation from solution (e.g. rock salt, some limestones)

  • Organic: formed from accumulated biological material (e.g. coal, some limestones)

  • Key idea:
    Sedimentary rocks form from weathering, precipitation, or biological accumulation.

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Lithosphere cycle

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Most common minerals in earth crust and soil

Most commons elements in earths crust → O and Si → SiO2 most common mineral

This is also true for Soils

Primary → comes from the rock → broken down rock goes into the soil

Secondary → chemical composition changes

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Minerals: silicates

Origin

  • Main source of secondary (pedogenic) minerals

  • Formation depends on temperature, pressure, cooling rate, and chemistry

  • Crystallize in sequence from high to low temperature

    • Early: olivine, pyroxene

    • Late: feldspars, quartz

Silicate Structures

  • Isolated tetrahedra → olivine

  • Single chains → pyroxenes

  • Double chains → amphiboles

  • Sheets (layers) → micas, clay minerals

  • Framework → feldspars, quartz

Properties

  • Structures linked by oxygen bridges

  • Negative charge attracts metal cations

  • Isomorphic substitution creates chemical diversity

  • Structure controls stability and weatherability

Key Idea → More complex silicate structures are more stable and weather more slowly

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Micas (sheet)

Types

  • Muscovite: light-colored mica

  • Biotite: dark-colored mica

Structure

  • Sheet (layer) silicates with a 2:1 structure

  • Layers held together by potassium ions

Importance for Soils

  • Important source of potassium

  • Easily weathered minerals

  • Biotite weathers faster than muscovite

Occurrence

  • Magmatic rocks: mainly biotite

  • Sedimentary and metamorphic rocks: mainly muscovite

Key Idea → Micas are nutrient-bearing, easily weatherable minerals important for soil fertility

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Tectosilicate (3D) → Quartz and Feldspar

Quartz

  • Pure framework silicate

  • Very resistant to weathering

  • Common as sand and silt in soils and sediments

  • Does not supply nutrients

  • Hard, irregular fracture surfaces

Feldspars

  • Framework silicates with aluminum substitution

  • Charge balanced by potassium, sodium, or calcium

  • Most abundant minerals in magmatic rocks

  • Easily weathered compared to quartz

  • Smooth cleavage surfaces

Relevance for soil

  • Feldspars release nutrients during weathering

  • Weathering forms secondary (clay) minerals

  • Quartz accumulates due to high resistance

Key Idea → Quartz persists; feldspars transform and feed soils

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Weathering

  • Weathering alters rocks and primary minerals

  • Occurs at the interface with atmosphere, biosphere, and hydrosphere

  • Transforms primary minerals into secondary minerals

  • Produces clay minerals, oxides, and hydroxides

  • Key process linking lithosphere to soil formation

Key idea:
Weathering is the bridge between rocks and soils.

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Physicall weathering

  • Mechanical breakdown of rocks without chemical change

  • Reduces grain size and increases surface area

Main Processes

  • Pressure release: cracking after erosion of overlying rock

  • Gravity: impact and crushing

  • Temperature changes: differential expansion of minerals

  • Frost weathering: ice expansion widens cracks

  • Salt weathering: crystal growth in pores and fractures

  • Biological pressure: root growth

Transport & Abrasion

  • Water: rolling, abrasion, scouring

  • Wind: saltation and suspension of fine particles

  • Ice: transport and abrasion at glacier base

Key Idea:
Physical weathering fragments rocks and prepares material for chemical weathering and soil formation.

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Chemical weathering

  • Chemical transformation or dissolution of minerals

  • Driven by water, acids, and biological activity

  • Continuous process because products are removed by water

Main Processes

  • Hydration

    • Water molecules enter mineral structures

    • Weakens crystal bonds and promotes dissolution

    • Especially important for highly soluble minerals (e.g. salts)

  • Hydrolysis / Protolysis

    • Reaction of minerals with acidic water

    • Carbonic acid from CO₂-rich water plays a key role

    • Very important for carbonate dissolution and silicate alteration

  • Complexation

    • Organic acids released during decomposition bind metal ions

    • Increases mobility of metals such as iron and aluminum

    • Enhances mineral dissolution and element transport

  • Oxidation

    • Reaction with O₂

    • Fe²⁺ → Fe³⁺, S²⁻ → SO₄²⁻

    • Produces H⁺, lowers pH

    • Forms Fe oxides/hydroxides (goethite, hematite)

  • Protolyis (Hydrolysis) of Silicates

    • Reaction of silicates with H⁺ (water / carbonic acid)

    • Breaks Si–O–Al bonds

    • Releases K⁺, Na⁺, Ca²⁺

    • Forms clay minerals (e.g. kaolinite) + silica

  • Weathering of Silicates – Overview

    • Early stage: loss of interlayer cations (e.g. K⁺), structure partly preserved

    • Advanced stage: complete lattice breakdown → new secondary minerals

    • Products: clays, oxides, hydroxides

Weathering Products

  • Weathering residues (solid remains)

  • Weathering solutions (dissolved ions transported away)

Key Idea → Chemical weathering transforms primary minerals and releases elements, driving soil formation and nutrient cycling.

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Weathering stability of minerals

Water solubility → Easily soluble salts < gypsum < calcite < dolomite

Structure of the silicates → Island < chains < leaf < framework (feldspars < quartz)

Fe(II) content (oxidizability) → Biotite < Muscovite

In general → Olivine < Pyroxene < Amphibole < Biotite < Plagioclase < Muscovite ≈ Orthoclase < Quartz

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Pedogenesis image

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Secondary minerals

  • Formed after partial or complete dissolution of primary minerals in the parent material

  • Main products:

    • Clay minerals (from layer silicates, e.g. micas)

    • Fe, Mn and Al oxides and hydroxides

    • Secondary carbonates and salts

These secondary minerals form in soils during pedogenesis.

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Clay Mineral

Origin

  • Formed from silicate weathering

  • Structure similar to mica (tetrahedral + octahedral layers)

  • Doesn’t change structure → Still tetrahedra/octahedra but with different minerals and charge

  • Particle size < 2 µm (clay fraction)

Identification

  • Formula unit: smallest repeating crystal unit

  • Basal spacing: distance between two consecutive layer units

Structural Types (classification)

  • Based on Si tetrahedra / Al octahedra stacking:

    • 1:1 (e.g. kaolinite)

    • 2:1 (e.g. smectite, illite)

    • 2:1:1 (e.g. chlorite)

    • Special forms: tubes, spheres

  • Different interlayer compositions (K⁺, water, cations, OH layers)

Isomorphic Substitution

  • Tetrahedral: Si⁴⁺ → Al³⁺

  • Octahedral: Al³⁺ → Mg²⁺ or Fe²⁺

  • Creates permanent negative layer charge

Charge Compensation

  • Exchangeable cations in interlayers

  • Positively charged Al-hydroxide layers

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Two layer clay mineral → Kaolinite

  • Structure: 1 tetrahedral + 1 octahedral layer (1:1)
    → layers linked by H-bonds, no interlayer

  • Basal spacing: ~0.72 nm

  • Formula: Al₂(OH)₄Si₂O₅

Origin

  • Forms in Si-poor, strongly weathered (tropical) environments

  • End product of silicate weathering

Properties

  • White, non-expanding, no swelling/shrinking

  • Used for ceramics (porcelain)

Soil relevance

  • No nutrients in structure

  • Very low CEC (little isomorphic substitution)

  • Typical of low-fertility soils

 

Everything that could leach or so has happened, really ancient, not fertile, really deep

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Three layer clay minerals (Illite, Smectite, Vermiculite)

Illite (2:1)

  • Derived from mica

  • Basal spacing ~1 nm

  • K⁺ fixed in interlayer → almost no swelling → K keeps layers together, not exchangeable

  • Important K source for soils

Smectite (2:1)

  • Often from basic igneous rocks

  • Expandable (1–2 nm)

  • Strong swelling/shrinking

  • Interlayer: hydrated, exchangeable cations

  • High CEC, high water retention

  • Hydrated cations in the middle

  • Available for plants, really fertile

Vermiculite (2:1)

  • Forms from biotite/muscovite

  • Expandable up to ~2 nm

  • Strong water retention

  • Interlayer cations partly fixed, partly exchangeable

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Four layer clay mineral (Chlorite)

Chlorite (2:1:1 clay mineral)

  • Primary and secondary clay mineral

  • Structure: 2:1 layers + hydroxide interlayer (Mg-, Al-, or Fe-hydroxides)

  • Not expandable

  • Very low to no cation exchange capacity (CEC)

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Layered clay minerals

  • Kaolinite (1:1)
    No true interlayer; layers held by H-bonds (O–H···O) → non-expandable, very low CEC → no shrink or swell

  • Illite (2:1)
    K⁺ fixed in the interlayer → strong layer bonding, no swelling, moderate CEC → hold by K

  • Smectite / Vermiculite (2:1)
    Hydrated, exchangeable cations + H₂O in the interlayer → expandable, high CEC → lot’s of exchange, swelling and shrinking

  • Chlorite (2:1:1)
    Mg/Al hydroxide interlayer → rigid structure, non-expandable, very low CEC.

<ul><li><p><strong>Kaolinite (1:1)</strong><br>No true interlayer; layers held by H-bonds (O–H···O) → non-expandable, very low CEC → no shrink or swell</p></li><li><p><strong>Illite (2:1)</strong><br>K⁺ fixed in the interlayer → strong layer bonding, no swelling, moderate CEC → hold by K</p></li><li><p><strong>Smectite / Vermiculite (2:1)</strong><br>Hydrated, exchangeable cations + H₂O in the interlayer → expandable, high CEC → lot’s of exchange, swelling and shrinking</p></li><li><p><strong>Chlorite (2:1:1)</strong><br>Mg/Al hydroxide interlayer → rigid structure, non-expandable, very low CEC.</p></li></ul><p></p>
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Further clay minerals

Mixed layers → transitions between layered forms, more reactive than pure minerals

Examples → Imogolite and Allophane

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Clay mineral transformation

  • Phyllosilicates (layer silicates)—especially micas—are the main precursors of clay minerals.

  • Physical weathering opens layer edges and removes interlayer K⁺, which is replaced by larger Ca²⁺ and Mg²⁺.

  • This drives the transformation sequence mica → illite → vermiculite / smectite, and with further alteration can lead to kaolinite or chlorite.

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Short summary clay minerals

  • Important secondary new formations in the soil (see «Weathering» for details)

  • They are subject to constant change, but their stability is usually significantly higher than that of primary silicates

Importance for soil

  • Clay minerals are components of the finest fraction of the soil, < 2 µm, = clay fraction

  • Storage for nutrients whose leaching is prevented

  • Microstructure makers in soil: particles adhere to each other, bind to themselves and to other coarse particles, expand and shrink etc..

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Oxide and hydroxide of Fe, Al, Mn

  • They are final products of weathering of silicate minerals.

  • Weathering releases Fe, Al and Mn ions into the soil solution.

  • These ions are oxidised and then precipitate.

  • This forms iron, aluminium and manganese oxides and hydroxides.

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Aluminium hydroxides: gibbsite

  • An aluminium hydroxide mineral formed during strong weathering.

  • Colourless to white.

  • Built from Al-octahedra (layered structure).

  • Forms only when silicon is very low in soil water.

  • Typical of intense weathering, especially in tropical regions.

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Iron oxides and hydroxides

Iron oxides & hydroxides (overview)

  • Form during weathering of silicates when Fe²⁺ is released and oxidized to Fe³⁺

  • Give soils yellow–brown–red colours

  • Stable in oxic (aerobic) conditions, dissolve under reducing (anaerobic) conditions

  • Very important for nutrient and trace-element binding

Main types

  • Hematite (α-Fe₂O₃)

    • Red colour

    • Forms in warm, dry, well-aerated conditions

    • Typical of tropical and subtropical soils

  • Goethite (α-FeOOH)

    • Yellow–brown colour

    • Forms at moderate temperatures

    • Very stable, common in temperate soils

  • Lepidocrocite (γ-FeOOH)

    • Orange colour

    • Forms under reducing / waterlogged conditions

    • Metastable, often local and temporary

  • Ferrihydrite (poorly crystalline Fe oxide)

    • Brown

    • Very young, poorly ordered (“rust”)

    • Forms during rapid oxidation, very reactive

  • Schwertmannite

    • Yellow–brown

    • Forms in acidic, sulphate-rich waters

    • Typical product of pyrite (FeS₂) weathering

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Mn oxides

Manganese (Mn) oxides

  • Form during weathering of silicates

  • Mn²⁺ is oxidized to Mn⁴⁺, precipitating as Mn oxides

Main form

  • MnO₂

    • Black colour

    • Forms black mottles/concretions in hydromorphic soils

    • Immobile under aerobic conditions

Redox behaviour

  • Under reducing and acidic conditions:

    • Mn oxides dissolve

    • Mn²⁺ becomes mobile and colourless

  • Acid soils and permanently waterlogged soils → low Mn content

Soil importance

  • Bind trace elements under aerobic conditions

  • Release trace elements under anaerobic conditions

  • Behaviour very similar to Fe oxides

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Oxides: indicators of soil formation

  • Goethite (FeOOH)

    • Forms in humid, wet climates

    • Indicates moderate weathering

    • No hematite → conditions too wet

  • Hematite (Fe₂O₃)

    • Forms in hot, tropical climates

    • Indicates intense weathering

    • Often together with goethite

  • Fe and Mn translocation (shifting)

    • Occurs in acidic, wet soils (e.g. Podzols)

    • Fe and Mn are mobilized under reducing conditions

    • Bleaching = loss of Fe/Mn

    • Accumulation horizons = re-precipitation under oxic or pH change

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Salts

Carbonates

  • Main types:

    • Calcite (CaCO₃): white, reacts with HCl → CO₂

    • Dolomite (CaMg(CO₃)₂): less soluble, Mg source

  • Origin:

    • Primary minerals (e.g. limestone)

    • Secondary carbonates from weathering

  • Soil importance:

    • Neutralize acids (CO₂, organic acids)

    • Buffer soil acidification

    • Increase soil pH

Sulphates & Phosphates

  • Sulphates (from sulphuric acid):

    • Anhydrite: CaSO₄

    • Gypsum: CaSO₄·2H₂O

  • Phosphates (from phosphoric acid):

    • Apatite: main primary P mineral

    • Vivianite, Strengite: secondary Fe–phosphates

  • Soil importance:

    • Phosphates = key P source for soils and biosphere

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Grain size

  • Grain size = particle size of soil (also called texture).

  • It describes how soil particles are distributed by size.

Why grain size matters

  • Controls porosity (pore size and distribution)

  • Regulates water and air movement

  • Affects transport and retention of substances (filter function)

  • Influences biological activity

  • Controls erosion risk

  • Important for soil structure (microstructure)

Basic soil fractions

  • Fine earth: particles < 2 mm

  • Soil skeleton (coarse fraction): particles > 2 mm

Typical characteristics

  • Coarse fraction: mostly rounded grains, mainly SiO₂ (quartz)

  • Fine fraction: mostly flat/leafy particles, rich in mica and clay minerals

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Soil skeleton

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Fine earth fraction

It's used the logaritmic scale, and if you take 2 (the border between gravel and sand) then it's 63 the middle on the logaritmic scale

<p>It's used the logaritmic scale, and if you take 2 (the border between gravel and sand) then it's 63 the middle on the logaritmic scale</p>
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Mineral content in the grain fractions

  • Quartz: mainly sand (also silt)

  • Primary silicates (feldspars, pyroxenes, etc.): sand → silt

  • Micas: mainly silt (can weather to clay)

  • Clay minerals: clay (< 2 µm)

  • Fe/Al/Mn oxides & hydroxides: clay (very fine particles/coatings)

Rule of thumb:
Sand = quartz

silt = a bit of everything

clay = clay minerals and others

<ul><li><p><strong>Quartz:</strong> mainly sand (also silt)</p></li><li><p><strong>Primary silicates (feldspars, pyroxenes, etc.):</strong> sand → silt</p></li><li><p><strong>Micas:</strong> mainly silt (can weather to clay)</p></li><li><p><strong>Clay minerals:</strong> clay (&lt; 2 µm)</p></li><li><p><strong>Fe/Al/Mn oxides &amp; hydroxides:</strong> clay (very fine particles/coatings)</p></li></ul><p><strong>Rule of thumb:</strong><br>Sand = quartz</p><p>silt = a bit of everything</p><p>clay = clay minerals and others</p>
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Grain size determination in the field

Finger test

  • Sand: gritty, loose, not sticky, no ribbon

  • Silt: smooth–floury, weak cohesion, no ribbon

  • Clay: sticky, plastic, shiny, forms long ribbon

  • Loam: intermediate; slightly plastic, short ribbon

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Lab grain size determination

  • Sieve < 2 mm (fine soil only)

  • Remove binding material (salts & organic matter)

  • Measure with laser diffraction

  • Smaller particles → stronger laser scattering

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Grain size triangle

knowt flashcard image
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Grain size and soil functions

Physical effects

  • Sand: drains fast, low water storage

  • Silt: best water available to plants

  • Clay: slow drainage, high water storage (often stagnant)

Chemical effects

  • Sand: few nutrients, low buffering

  • Clay: many nutrients, high buffering

Pollutants

  • Finer grains (silt–clay) retain pollutants more than sand