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Size - < 2 m Clay fraction Surface area - area per unit mass High surface area ○ 1 g clay 1000 X greater than 1 g sand ○ Expressed as m2 g-1 Internal vs. external |
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Primarily composed of Al, Si, Fe, and Mg, and O 5 out of the 8 most common elements in the earth’s crust Cations coordinated to an anion (O) Coordination will depend on the size of the cation |
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Layer silicate clays 1:1, 2:1, 2:1:1 Fe and Al oxides Fe-oxides: red colors in many SW VA soils Allophane and associated materials Short-range order or amorphous Humus Dark brown to black colors |
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Phyllosilicates - Greek meaning leaf Dominant inorganic colloid in most soils Dominant cations Si, Al, Mg, Fe coordinated to oxygen Generate negative charge - Isomorphic substitution gives rise to the cation exchange capacity (CEC) of soils |
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Basic building blocks Silica and Al tetrahedron (Si4+/Al3+ coordinated to 4 O ) Al and Mg octahedron (Mg2+ or Al3+ coordinated to 6 O ) These tetrahedron can polymerize into tetrahedral and octahedral sheets Arrangement and composition of these tetrahedral and octahedral sheets give rise to different layer silicates |
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Tetrahedral and octahedral layers are held together by shared oxygen atoms 1:1 clay minerals 1 tetrahedral and 1 octahedral layer 2:1 clay minerals 2 tetrahedral and 1 octahedral layer 2:1:1 2 tetrahedral and “2” octahedral layers |
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Isomorphic substitution - substitution of one element for another of equal size Occurs during mineral formation Occurs in both tetrahedral/octahedral sheets Al3+ subst for Si4+ in tetrahedral layer Fe2+, Mg2+, Ni2+, Zn2+, Cu2+ for Al3+ in octahedral layer KEY -- element of lower positive charge substituting for one of higher charge |
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1:1 minerals Tetrahedral and octahedral sheets held together by shared oxygen atoms Layers or platelets bound to adjacent layers via hydrogen bonding ○ No internal surface area ○ No shrink swell Small amount of isomorphic substitution ○ Low CEC |
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2:1 clay minerals Octahedral sheet sandwiched between 2 tetrahedral sheets Sheets held together by shared oxygens Plates held together weakly ○ Expanding vs. semi-expanding Both internal and external surface area High amount of isomorphic substitution ○ High CEC |
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Expanding 2:1 minerals (e.g. smectites) Caused by swelling as water enters the interlayer space and forces plates apart ○ Problem from a construction standpoint High specific surface area due to internal surface Isomorphic substitution primarily in octahedral sheet (Mg2+ for Al3+) |
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Semi-expanding 2:1 minerals (e.g. vermiculite) Internal surface area containing cations and water Platelets held together more strongly than smectites hence only semi-expansible or limited expansion Lower specific surface area compared to smectites IS primarily Al3+ for Si4+ in tetrahedral layers |
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Clay fraction dominated by smectites Used in landfill liner construction Used to seal groundwater monitoring wells Detrimental from a construction standpoint ○ Homes ○ Highways |
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2:1 nonexpanding minerals (mica) Large amount of Al3+ for Si4+ isomorphic substitution in tetrahedral layer Excess negative charge satisfied by K+ cations in the interlayer K+ right size to fit in hexagonal hole created by Si-tetrahedra K+ acts as a binding agent preventing expansion of interlayers |
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2:1 with hydroxide sheet or 2:1:1 or 2:2 minerals (chlorite) Basic 2:1 structure and isomorphic substitution as mica (high net negative charge) Negative charge compensated by a positively charged hydroxide sheet in the interlayer Nonexpanding and no internal surface area |
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Fe oxides (goethite and hemitite) Al oxides (gibbsite) Weather from Fe and Al bearing primary minerals Very reactive surfaces Common in SE soils |
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What the heck is “red mud’ |
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When bauxite is mined (primarily Al(OH)3, it is essentially highly weathered Oxisol subhorizon (Bo and Cv) material that also contains significant Fe-oxides like Fe2O3 (hematite). The Fe-oxide is removed via washing the bauxite with NaOH which drives the pH above 10 and solubilizes the Fe-oxides and and any other entrained or sorbed metals. |
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What the heck is “red mud’ |
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So, basically this is really just high pH and Na rich Fe-oxides and is not particularly toxic (other than high pH/caustic) unless the bauxite was also high in Cd or some other heavy metal. In fact, a commercial product called Virosoil is made out of seawater neutralized (and rinsed) red mud and has been used widely to renovate soils and remediate heavy metal contaminated sites due to the strong abilities of Fe-oxides to specifically adsorb Pb, Cu, Ni and other nasties from soils! |
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Commonly associated with volcanic material Poorly crystalline Very reactive Small quantities present in SE soils. Abundant in soils weathered from volcanic ash |
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Breakdown and alteration of plant residues Dark in color Contain common organic functional groups Carboxyl (COOH) Phenolic Deprotonation of these functional groups gives rise to pH-dependent CEC Important for good soil structure |
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pH and Eh (redox potential) two master variables in soils. pH controls chemical, physical and biological properties of soil. Nutrient availability Contaminant fate and mobility Aggregate stability and water and air movement ○ Influence microorganisms |
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Pure water ionizes slightly (autoprotolysis) H2O = H+ + OH- Equilibrium constant Kw = [H+][OH-] = 10-14 Pure water has pH of 7 Above equation can solve for proton or hydroxyl concentration given the pH, [H+] X [OH-] must always equal 10-14 (see Box 9.1 in Brady) |
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pH = -log [H+] Logarithm base 10 pH 3 vs. 4 0.001 M vs. 0.0001 M 10 fold increase/decrease in concentration of proton and hydroxyl Base vs. acid cations (Al3+, H+ vs. Ca2+, Mg2+, K+, and Na+) |
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Range in soil pH values Sodic Soils (pH 8.5-11) Calcareous soils (pH 7-8.2) Humid region soils (pH 5.0 -5.5) Forest Soils (pH 3.5-5.5) Acid sulfate soils (pH 2-3.8) |
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Cations responsible for soils acidity are H+ and Al3+ (acid cations) Al3+ readily hydrolyzes as pH of soil solution is raised (Al is the major culprit) Al3+ + H2O = Al(OH)2+ + H+ Al(OH)2+ + H2O = Al(OH)2 + + H+ Al(OH)2 + + H2O = Al(OH)3 0 + H+ |
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Organic acids and functional groups that release acidity by dissociation R----H = R- + H+ Al3+ - organic complexes that release acidity by hydrolysis R----Al3+----R = R----AlOH2+----R + H+ |
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pH and the Nature of the Exchange Complex |
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Balance between prod/consumption of H+ Low pH (3 - 4.5) ○ Al3+ and H+ Moderately acid (4.5 - 6. 5) ○ Al(OH)x and base cations Neutral to alkaline pH (6.5 - 8.0) ○ Base cations |
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Organic vs. mineral Colloid |
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pH-dependent vs. permanent charge OM binds Al3+ tightly rendering it nonexchangeable Potential implications? |
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Classification of Acidity |
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Active Acidity - all titratable acidity in soil associate with the soil solution. Usually very small and best calculated by pH Exchangeable Acidity - bound Al3+ and H+ displaced into soln by conc. neutral salt (1 M KCl) organically complexed, exchange sites exchangeable H+ in OM, Al3+ in mineral |
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Classification of Acidity |
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Non-exchangeable acidity or residual - bound Al/H not displaced or very slowly displaced strongly complexed by OM Al-hydroxy cations (Al(OH)2+ or Al(OH)2 +) Reserve acidity - all titratable acidity associated with solid phase (NEA + EA). Represents buffer capacity of soil |
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Colloid Control of Soil Reaction |
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Active acidity only small part of soils total acidity Nature of exchange complex dominates soil pH % base saturation Nature of the solids Kinds of base forming cations |
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Soils tend to resist change in solution pH Equilibrium between various forms of acidity |
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Clay soils with exchangeable and residual acidity associated much more buffered than sandy soils Lime added to soil active acidity is neutralized Some exchangeable acidity will also be neutralized |
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Soils low base saturation resist changes in pH due to high quantity exchangeable Al Similar buffer reactions involve carbonates, bicarbonates, and carbonic acid (occur higher pH values) All things being equal higher CEC greater buffer capacity |
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Natural changes Weathering primary minerals consumes protons and releases base forming cations (Mg2+ and Ca2+) Microbial activity produces carbonic acid and organic acids as they degrade organic matter Redox ○ Soil becomes flooded and reduction reactions consume protons conversely oxidation reactions release protons |
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Chemical fertilizers (NH)4SO4 + 4O2 ---> 2HNO3 + H2SO4 + 2H2O Tillage practices (OM oxidation) Acid Deposition (dry and wet) SO2 + H2O --> H2SO4 NO2 + H2O --> HNO3 Irrigation practices (sodic soils) Pyrite oxidation (Coal and marshes) |
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