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Announcements ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Visual comparison of common silicate clays Smectite Kaolinite1:1  Vermiculite Fine-grained mica Chlorite 2:1 clays 1:1 clays
Fine-grained Mica (2:1) ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
Structure of soil mica (Illite) ~ 20% of the silica sites are occupied by aluminium (tetrahedral substitution) yielding a VERY strong net negative charge
Structure of soil mica (Illite) Explore Soil Mica (muscovite) HERE 1.  Isomorphous substitution is in the tetrahedral sheets 2.  K+  in the interlayer  space to satisfy the charge and “locks up” the structure K+ K+
Visual comparison of common silicate clays Smectite Kaolinite1:1  Vermiculite Fine-grained mica Chlorite 2:1 clays 1:1 clays
Chlorites (2:1:1) ,[object Object],[object Object],[object Object],[object Object],[object Object]
Structure of Chlorite Mg-Al-Fe  hydroxy sheet Mg-Al-Fe  hydroxy sheet ,[object Object],[object Object],[object Object],= Al  = Fe = Mg Explore Chlorite HERE
Explore Nacrite HERE Nacrite Nacrite, Lodève Basin, France                                        Field of view approx. 200 microns wide
Visual comparison of common silicate clays Smectite Kaolinite1:1  Fine-grained mica Chlorite 2:1 clays 1:1 clays H bonding Vermiculite
Comparison of common silicate clays Edges only  –  NO isomorphic substitution Property Kaolinite Smectite Fine-grained mica General class 1:1 (TO) 2:1 (TOT) 2:1 (TOT) Swelling Low High Low or none Nutrient supply capacity Low High Moderate Charge location Octahedral  sheets Tetrahedral  sheets Bonding Hydrogen ( strong ) Van der Waal’s ( weak )  Click here Potassium ions ( strong )
Smectite Kaolinite1:1  Fine-grained mica Chlorite 1:1 clays Location of  isomorphic substitution  and resulting  internal  charge imbalance No charge except at edges octahedral tetrahedral octahedral tetrahedral tetrahedral octahedral tetrahedral tetrahedral octahedral tetrahedral tetrahedral tetrahedral tetrahedral tetrahedral tetrahedral octahedral tetrahedral octahedral Vermiculite 2:1 clays H bonding Consider:  hydration, cation adsorption, swelling, shrinking, plasticity
Genesis of silicate clays ,[object Object],[object Object],Why different clays form… ,[object Object],[object Object]
Crystal Growth ,[object Object]
Factors affecting mineral stability   ,[object Object],[object Object],[object Object],[object Object]
Weathering pattern of clay formation Oxisols Ultisols Entisols, Inceptisols Vertisols
Where to find different clays
Types of charge  ,[object Object],[object Object],(due to isomorphous substitution) (variable, due to edge phenomena)
Permanent charge Octahedral sheet neutral Net negative charge -
+ pH-dependent charge: on edges!!!  Espec. Important in kaolinite, humus, where no internal charge imbalance  (exchange on edge only) H +  bound tightly at low pH, so  the lower the pH , the less exchange there is (i.e.,  lower nutrient availability ) As pH increases, hydrogen is held loosely and can be exchanged for other cations Under moderately acidic conditions – little or no charge results pH dependent charges are associated with the edges of inorganic (clay crystals) and organic colloids (OM) Low pH  (moderately acidic) Al +2 OH OH OH - - - NH 4 + K + Na + High pH  (less acidic)
Kaolinite Well crystallized kaolinite from the Keokuk geode, USA                                        Field of view approx. 18 microns wide
Ideas about Origin of Life on Earth ,[object Object],[object Object],[object Object],[object Object],[object Object],Requires self-replication, metabolism
[object Object],[object Object],[object Object],[object Object],How does replication originate? RNA
Clays and the origins of life on Earth ,[object Object],[object Object],[object Object],[object Object],[object Object]
Clay is a replication platform/template
“ Sweet crystal” hypothesis: clay minerals have grooves that catalyze synthesis of polysaccharide chains Polysaccharides – polymer chains, contain carbon, hydrogen and oxygen in a 1:2:1 ratio A.G. Cairns-Smith – 1987, Clay minerals and the origin of life (book) R.M. Hazen – 2001, Life’s rocky start - Scientific American
END OF Clay structure & properties
Chapter 8 How plants get  nutrients  from soils (ion exchange)
Ch. 8 Learning Objectives ,[object Object],[object Object],[object Object]
Ion exchange ,[object Object],[object Object],[object Object]
What’s so great about ion exchange? ,[object Object],[object Object],[object Object]
“ Next to photosynthesis and respiration, probably no process in nature  is as vital to plant and animal life  as the exchange of ions between  soil particles and growing plant roots.” Nyle C. Brady
2  Controls  on ion exchange ,[object Object],[object Object],[object Object],[object Object],r 2  charge F = Coulomb’s Law
Controls on ion exchange ,[object Object],[object Object],[object Object],[object Object],r 2  charge F = Coulomb’s Law
Controls on ion exchange ,[object Object],[object Object],[object Object],[object Object],r 2  charge F = Coulomb’s Law
Strength of adsorption is related to the combined effects of  Charge and Size
Exchange affinity Held more strongly Held more weakly This is referred to as the  “ Lyotropic series” Al 3+  > Ca 2+  > Mg 2+  > NH 4 +  = K +  > Na + Strength of adsorption related to valence (charge)  ÷  hydrated  radius
Definitions ,[object Object],[object Object],[object Object],[object Object],[object Object]
Announcements ,[object Object],[object Object],[object Object],[object Object]
What is clay? ,[object Object],[object Object],[object Object]
 
Smectite Kaolinite1:1  Fine-grained mica Chlorite 1:1 clays Location of  isomorphic substitution  and resulting  internal  charge imbalance No charge except at edges octahedral tetrahedral octahedral tetrahedral tetrahedral octahedral tetrahedral tetrahedral octahedral tetrahedral tetrahedral tetrahedral tetrahedral tetrahedral tetrahedral octahedral tetrahedral octahedral Vermiculite 2:1 clays H bonding Consider:  hydration, cation adsorption, swelling, shrinking, plasticity
 
Ion exchange vs.  CEC Sandy loam VERY  acidic  soil How many charges are there to fill??? H + H + NO 3 - NO 3 - NO 3 - H + HSO 4 - exchange surface CEC = 7;   AEC = 2 NH 4 + Ca 2+ H + Mg 2+ K + NO 3 - Cl -
Cation Exchange Capacity (CEC) ,[object Object],[object Object],[object Object],[object Object],[object Object],Number of charges,  not the number of ions ,  is what matters 1 mol = 6.022 X 10 23  atoms (1 cmol = 1/100 mol)
CEC depends upon ,[object Object],[object Object],Which of the 12 soil orders would have the highest CEC?
Anion Exchange Capacity (AEC) ,[object Object],[object Object],[object Object],Number of charges,  not the number of ions ,  is what matters
Positive Charge in soils:  (creates Anion Exchange Capacity) ,[object Object],Al or Fe
Charges on soil colloids* * Itty bitty soil components –  silicate clays, oxides, humic substances So  what  will those negative charges adsorb? Colloid type Negative charge Positive charge Humus (O.M.) Silicate clays Oxides of Al and Fe  200  cmol c /kg 0 cmol c /kg 100  cmol c /kg 0 cmol c /kg 4 cmol c /kg 5  cmol c /kg
Source of charge on 1:1 clays Broken edge of a kaolinite crystal showing  oxygen  atoms as the  source of  NEGATIVE  charge Charge is pH dependent
Source of charge for the smectites Isomorphous substitution here, in the octahedral sheet means a net  NEGATIVE  charge Permanent charge
Source of charge for the micas 3. Charge imbalance mostly on edges Permanent charge K+ K+ 2. K+ satisfies charge and “locks up” the structure  no internal exchange surfaces   1. Isomorphous substitution in  tetrahedral sheets
Negative charges on humus Central unit of a  humus colloid (mostly C and H) ENORMOUS external surface area! (but no internal surface – all edges) Charge is pH dependent  Explore Soil Organic Matter (SOM) HERE
Surface charge comparison 13 out of 18 “sites” are negative (72%)  3 out of 9 “sites” are negative  ( 33%)  But the numbers will vary as the pH of the soil varies!
Examples of cation exchange +  Ca 2+      The interchange between a cation in solution and one on a colloid must be  CHARGE  balanced.  K + K + K + K + K + K + K + Strength of adsorption of ions in solution Relative concentration of ions in solution +  2K + Ca 2+ K + K + Al 3+ +  3K +    K + K + K + +  Al 3+
Sources of acidity: Hydrolysis  (weathering reaction)     H +  (requires water) Biological decomposition    H +   (requires water) Dissolution of minerals  (weathering reaction)     Al 3+   (requires water)
“ Acid” cations ,[object Object],[object Object],[object Object],[object Object]
Adsorbed cations: climate effect Humid region soil Arid region soil Low pH (acidic) High pH (basic) H + H + H + Al 3+ K + K + Ca 2+ Mg 2+ H + Mg 2+ NH 4 +
Typical Adsorbed cations (%) Soil order “ Acid cations ” (H + , Al 3+ ) “ Base cations ” (everything else, e.g., Ca 2+ , NH 4 + , K + , etc.) Ultisol Alfisol Mollisol 45 55 65 35 30 70
A real-life application: ,[object Object],[object Object]
CEC (cmol c /kg): soil order 1:1 clays 2:1 clays O.M. Low pH 128.0 3.5 Lower moisture Ultisols Alfisols 9.0 Mollisols 18.7 Vertisols 35.6 Histosols low high
OM has highest CEC 2:1 clays 1:1 clays Non-clayey soils Highly weathered oxides
Measuring CEC saturate  w/ ammonium remove xs salt leach measure
Calculating CEC ,[object Object],[object Object],K + Al 3+ H + Ca 2+ Ca 2+ K + K + K +
Ion Exchange Animation ,[object Object]
Announcements ,[object Object],[object Object],[object Object],[object Object],[object Object]
Controls on Ion exchange? ,[object Object],[object Object]
Remember ,  CEC depends upon ,[object Object],[object Object]
Rough Rule of thumb CEC = ( % O.M.  x  200 CEC ) + ( % clay  x  50 CEC ) But …CEC of clay minerals ranges from  3 to 150 !
Organic matter challenge ,[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object]
(cmol c /kg) low really high high
Sample calculation Calculate the net negative charge of a soil sample containing  5%  organic matter (OM) and  20%  montmorillonite (smectite) type of clay. Net negative charge  = (% OM  *  its’ CEC)  +  (% clay  *  its’ CEC) Net negative charge   =   [( 5 /100) kg *  200  cmol c /kg] + [( 20 /100) kg *  100  cmol c /kg] CEC OM ~  200  cmol c /kg CEC montmorillonite ~ 100  cmolc/kg 10  cmolc/kg  + 20  cmolc/kg  =  30  cmolc/kg
More . . . ,[object Object],[object Object],[object Object],See your text, Box 8.2, p. 209, for more (0.05 * 200) + (0.20 * 3) = 10.6 cmol c /kg (0.01 * 200) + (0.20 * 100) + (0.01 * 150)  = 23.5 cmolc/kg
CEC and pH  – for 1:1 clays and humus CEC low high 3 8 Soil pH Why?
pH-dependent charge
Influence of pH on the CEC of smectite and humus or Kaolinite Edge charge = Internal charge
Charge characteristics Colloid type Total charge Constant (%) Variable (%) Positive charge Organic 200 Smectite 200 Kaolinite 8 10 90 0 5 95 2 95 5 0 Permanent  charge pH dependent  charge
CEC and weathering intensity Alfisols, Vertisols, Argiudolls Ultisols Oxisols
Base saturation ,[object Object],[object Object],[object Object],(replace with non-acid cation)
Cations –  acid forming vs base forming Sources of acidity:  Hydrolysis (weathering reaction)    H +  (requires water) Biological decomposition    H +   (requires water) Dissolution (weathering reaction)    Al 3 +   (requires water) Al 3 +  + 3H 2 O    Al(OH 3 ) + 3H + non-acid “ Acid cations ” (H + , Al 3+ ) “ Base cations ” (everything else, e.g.,  Ca 2+ , NH 4 + , K + , etc.)
Equation for base saturation non-acid cation “ Acid cations ” (H + , Al 3+ ) “ Base cations ” (everything else, e.g., Ca 2+ , NH 4 + , K + , etc.)
Back to why we might care… … plants (i.e. FOOD!)
How a plant works Nutrients
How a plant works
Nutrient Availability: Mechanism ,[object Object],[object Object]
Availability of nutrients ,[object Object],[object Object],[object Object]
Cation Saturation ,[object Object],[object Object],[object Object],[object Object],Ca2+   displacement easier and more rapid ,[object Object]
Cation Complementarity ,[object Object],[object Object],The availability of the nutrient depends on the other cations in solution/adsorbed assume system is at equilibrium  H +   >   Al 3+  > Ca 2+  > Mg 2+  > NH 4 +  = K +  > Na + loosely held cations, relative to the other cations present are more readily available pH = 5 -   Al 3+ -   H + -   H + -   H + -  NH 4 + +  NO 3 - pH = 8.5 -   Na + -   Na + -   Na + -   Ca 2+ -   NH 4 + -   Ca 2+ Held strongly Held weakly Al 3+  > Ca 2+  > Mg 2+  > NH 4 +  = K +  > Na +
Cation exchange in action The fate of the K is limited by the other ions present  on the exchange surface
Root uptake of nutrients ,[object Object],[object Object],[object Object]
Test review ,[object Object],[object Object],[object Object],[object Object],[object Object],BRING A CALCULATOR
[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],[object Object],Example test question… = 100(1-[1.3 g/cm 3 /2.65 g/cm3 ])  =  51% = 390g/300cm 3  =  1.3g/cm 3 D b =mass dry soil/bulk volume % PS = 100 * (1-[D b /D p ]) You will recall…
Gravimetric  Moisture Content:   The amount (by wt.) of water contained in a soil sample at a given time. ,[object Object],[object Object],[object Object],[object Object],Mass of water relative to the mass of the dry soil particles
Particle Size Clay Silt Sand Pore   size , infiltration rate, drainage rate, aeration
Surface area,  pore   volume , nutrient supply capacity, plasticity and cohesion, swelling Particle Size Clay Silt Sand
A soil is said to be at field capacity just after all the gravitational water has drained from the soil.  Water potential (suction) is -10 cbar at field capacity.  Many crop plants are most productive when soil moisture levels are kept at levels of at least 60 - 90% of field capacity.  For  soil a , what is the minimum range of soil volumetric water content you would aim for to keep your crops most productive?  For soil a, field capacity (-10 cbar) is at at ~38%.  60% of 38% is 0.6*38% or ~ 23% 90% of 38% is 0.9*38% or ~34% You would want to keep your volumetric moisture content up at at least 23 to 34%.
Which soil  (a or b)  has a higher bulk density? What is the bulk density of  soil a ? Max volumetric water content for soil a is ~45%, which means the %PS for soil a is ~45%.  %PS  = [1 – (D b /D p )] * 100 45%  = [1 – (X/2.65)] * 100 X= 1.46 g/cm 3 Soil a has higher bulk density.  You can tell because it’s maximum water content is lower.
If your field started completely dry, and your irrigation system delivers 1 cm water per hour, how long would you have to irrigate  soil a  for to bring the top 30 cm of your field to a moisture content that is 60% of field capacity?
 
If your field started completely dry, and your irrigation system delivers 1 cm water per hour, how long would you have to irrigate  soil a  for to bring the top 30 cm of your field to a moisture content that is 60% of field capacity? ,[object Object],[object Object],[object Object],[object Object],[object Object]
Which soil ( a or b ) holds more water at wilting point?  (Wilting point is at a suction of -1500 cbar).  Is this water available to plants? ,[object Object]
Adhesion & cohesion ,[object Object],[object Object], ,[object Object]
 (cbar)  (%) Moisture Characteristic Curve Suction units: 1 bar   100cbar 1.01971 x 10 5  Pa  0.9869 atm 10 6  dynes/cm 2 14.5 psi 1019.753 cm H 2 O ~33 feet H 2 O volumetric water content Suction 0 -10 -100 -10 3 -10 4 -10 5 0 10 20 30 40 50 60
Difference is a function of texture, structure, & OM content.  (cbar)  (%) Estimating moisture content using Moisture Characteristic Curve and Tension data -15 bar -490 bar  (bar) soil A soil B soil C soil D -1 -10 -100 -10 3 -10 4 -10 5 0 10 20 30 40 50 60 -0.01 -0.1 -1 -10 -100 -1000 -10 -100 -1000 -10 4 -10 5 -10 6  (cm)
Darcy’s law  (K sat )   ,[object Object],h 2 h 1 L inlet outlet A K = intrinsic permeability of media and the hydraulic properties of the liquid Air bubble  Q =  K  A  H L K sat  = sat. hydraulic conductivity  H = h 1  – h 2  (head change) A = cross sectional area L = media column length Q = V/t (infiltration rate) Q = discharge  (cm 3 /t)
Shape of  silicon  tetrahedron and  aluminum   octahedron O OH O O O OH OH OH OH Si Al
Octahedral sheet Octahedral sheet Tetrahedral sheet Tetrahedral sheet Tetrahedral sheet Tetrahedral sheet
Isomorphous substitution ,[object Object],[object Object],~ equal & shape/size (ionic radii)
Permanent charge Octahedral sheet neutral Net negative charge
pH-dependent charge: on edges!!!  Espec. Important in kaolinite, humus, where no internal charge imbalance H +  bound tightly, so  the lower the pH , the less exchange there is (i.e.,  lower nutrient availability )
CEC and pH  – for 1:1 clays and humus CEC low high 3 8 Soil pH
Smectite Kaolinite1:1  Fine-grained mica Chlorite 1:1 clays Location of  internal  charge imbalance No charge except at edges octahedral tetrahedral octahedral tetrahedral tetrahedral octahedral tetrahedral tetrahedral octahedral tetrahedral tetrahedral tetrahedral tetrahedral tetrahedral tetrahedral octahedral tetrahedral octahedral Vermiculite 2:1 clays H bonding Consider:  hydration, cation adsorption, swelling, shrinking, plasticity “ Young” Clays “ Old” Clays
100%  silt 100%  sand 100% clay % clay % silt % sand
Color ,[object Object],[object Object],[object Object],“ quantified” using the Munsell system 8/ 6/ 5/ 4/ 3/ 2/ Hue Value /8 /4 /3 /2 /1 /6 7/ Chroma 5Y 5R 5YR 5G 5RP
Aggregate stability
Why Are Aggregates Important? ,[object Object],[object Object],[object Object]
When aggregates break down…
Conditions that Promote Aggregate Stability ,[object Object],[object Object],[object Object],[object Object],[object Object]
 
Controls on ion exchange ,[object Object],[object Object],[object Object]
Exchange affinity This is referred to as the  “ Lyotropic series” Strength of adsorption proportional to valence (charge)  ÷  hydrated  radius

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Week 7 Clay And Ion Exchange (1)

  • 1.
  • 2. Visual comparison of common silicate clays Smectite Kaolinite1:1 Vermiculite Fine-grained mica Chlorite 2:1 clays 1:1 clays
  • 3.
  • 4. Structure of soil mica (Illite) ~ 20% of the silica sites are occupied by aluminium (tetrahedral substitution) yielding a VERY strong net negative charge
  • 5. Structure of soil mica (Illite) Explore Soil Mica (muscovite) HERE 1. Isomorphous substitution is in the tetrahedral sheets 2. K+ in the interlayer space to satisfy the charge and “locks up” the structure K+ K+
  • 6. Visual comparison of common silicate clays Smectite Kaolinite1:1 Vermiculite Fine-grained mica Chlorite 2:1 clays 1:1 clays
  • 7.
  • 8.
  • 9. Explore Nacrite HERE Nacrite Nacrite, Lodève Basin, France                                        Field of view approx. 200 microns wide
  • 10. Visual comparison of common silicate clays Smectite Kaolinite1:1 Fine-grained mica Chlorite 2:1 clays 1:1 clays H bonding Vermiculite
  • 11. Comparison of common silicate clays Edges only – NO isomorphic substitution Property Kaolinite Smectite Fine-grained mica General class 1:1 (TO) 2:1 (TOT) 2:1 (TOT) Swelling Low High Low or none Nutrient supply capacity Low High Moderate Charge location Octahedral sheets Tetrahedral sheets Bonding Hydrogen ( strong ) Van der Waal’s ( weak ) Click here Potassium ions ( strong )
  • 12. Smectite Kaolinite1:1 Fine-grained mica Chlorite 1:1 clays Location of isomorphic substitution and resulting internal charge imbalance No charge except at edges octahedral tetrahedral octahedral tetrahedral tetrahedral octahedral tetrahedral tetrahedral octahedral tetrahedral tetrahedral tetrahedral tetrahedral tetrahedral tetrahedral octahedral tetrahedral octahedral Vermiculite 2:1 clays H bonding Consider: hydration, cation adsorption, swelling, shrinking, plasticity
  • 13.
  • 14.
  • 15.
  • 16. Weathering pattern of clay formation Oxisols Ultisols Entisols, Inceptisols Vertisols
  • 17. Where to find different clays
  • 18.
  • 19. Permanent charge Octahedral sheet neutral Net negative charge -
  • 20. + pH-dependent charge: on edges!!! Espec. Important in kaolinite, humus, where no internal charge imbalance (exchange on edge only) H + bound tightly at low pH, so the lower the pH , the less exchange there is (i.e., lower nutrient availability ) As pH increases, hydrogen is held loosely and can be exchanged for other cations Under moderately acidic conditions – little or no charge results pH dependent charges are associated with the edges of inorganic (clay crystals) and organic colloids (OM) Low pH (moderately acidic) Al +2 OH OH OH - - - NH 4 + K + Na + High pH (less acidic)
  • 21. Kaolinite Well crystallized kaolinite from the Keokuk geode, USA                                        Field of view approx. 18 microns wide
  • 22.
  • 23.
  • 24.
  • 25. Clay is a replication platform/template
  • 26. “ Sweet crystal” hypothesis: clay minerals have grooves that catalyze synthesis of polysaccharide chains Polysaccharides – polymer chains, contain carbon, hydrogen and oxygen in a 1:2:1 ratio A.G. Cairns-Smith – 1987, Clay minerals and the origin of life (book) R.M. Hazen – 2001, Life’s rocky start - Scientific American
  • 27. END OF Clay structure & properties
  • 28. Chapter 8 How plants get nutrients from soils (ion exchange)
  • 29.
  • 30.
  • 31.
  • 32. “ Next to photosynthesis and respiration, probably no process in nature is as vital to plant and animal life as the exchange of ions between soil particles and growing plant roots.” Nyle C. Brady
  • 33.
  • 34.
  • 35.
  • 36. Strength of adsorption is related to the combined effects of Charge and Size
  • 37. Exchange affinity Held more strongly Held more weakly This is referred to as the “ Lyotropic series” Al 3+ > Ca 2+ > Mg 2+ > NH 4 + = K + > Na + Strength of adsorption related to valence (charge) ÷ hydrated radius
  • 38.
  • 39.
  • 40.
  • 41.  
  • 42. Smectite Kaolinite1:1 Fine-grained mica Chlorite 1:1 clays Location of isomorphic substitution and resulting internal charge imbalance No charge except at edges octahedral tetrahedral octahedral tetrahedral tetrahedral octahedral tetrahedral tetrahedral octahedral tetrahedral tetrahedral tetrahedral tetrahedral tetrahedral tetrahedral octahedral tetrahedral octahedral Vermiculite 2:1 clays H bonding Consider: hydration, cation adsorption, swelling, shrinking, plasticity
  • 43.  
  • 44. Ion exchange vs. CEC Sandy loam VERY acidic soil How many charges are there to fill??? H + H + NO 3 - NO 3 - NO 3 - H + HSO 4 - exchange surface CEC = 7; AEC = 2 NH 4 + Ca 2+ H + Mg 2+ K + NO 3 - Cl -
  • 45.
  • 46.
  • 47.
  • 48.
  • 49. Charges on soil colloids* * Itty bitty soil components – silicate clays, oxides, humic substances So what will those negative charges adsorb? Colloid type Negative charge Positive charge Humus (O.M.) Silicate clays Oxides of Al and Fe 200 cmol c /kg 0 cmol c /kg 100 cmol c /kg 0 cmol c /kg 4 cmol c /kg 5 cmol c /kg
  • 50. Source of charge on 1:1 clays Broken edge of a kaolinite crystal showing oxygen atoms as the source of NEGATIVE charge Charge is pH dependent
  • 51. Source of charge for the smectites Isomorphous substitution here, in the octahedral sheet means a net NEGATIVE charge Permanent charge
  • 52. Source of charge for the micas 3. Charge imbalance mostly on edges Permanent charge K+ K+ 2. K+ satisfies charge and “locks up” the structure no internal exchange surfaces 1. Isomorphous substitution in tetrahedral sheets
  • 53. Negative charges on humus Central unit of a humus colloid (mostly C and H) ENORMOUS external surface area! (but no internal surface – all edges) Charge is pH dependent Explore Soil Organic Matter (SOM) HERE
  • 54. Surface charge comparison 13 out of 18 “sites” are negative (72%) 3 out of 9 “sites” are negative ( 33%) But the numbers will vary as the pH of the soil varies!
  • 55. Examples of cation exchange + Ca 2+  The interchange between a cation in solution and one on a colloid must be CHARGE balanced. K + K + K + K + K + K + K + Strength of adsorption of ions in solution Relative concentration of ions in solution + 2K + Ca 2+ K + K + Al 3+ + 3K +  K + K + K + + Al 3+
  • 56. Sources of acidity: Hydrolysis (weathering reaction)  H + (requires water) Biological decomposition  H + (requires water) Dissolution of minerals (weathering reaction)  Al 3+ (requires water)
  • 57.
  • 58. Adsorbed cations: climate effect Humid region soil Arid region soil Low pH (acidic) High pH (basic) H + H + H + Al 3+ K + K + Ca 2+ Mg 2+ H + Mg 2+ NH 4 +
  • 59. Typical Adsorbed cations (%) Soil order “ Acid cations ” (H + , Al 3+ ) “ Base cations ” (everything else, e.g., Ca 2+ , NH 4 + , K + , etc.) Ultisol Alfisol Mollisol 45 55 65 35 30 70
  • 60.
  • 61. CEC (cmol c /kg): soil order 1:1 clays 2:1 clays O.M. Low pH 128.0 3.5 Lower moisture Ultisols Alfisols 9.0 Mollisols 18.7 Vertisols 35.6 Histosols low high
  • 62. OM has highest CEC 2:1 clays 1:1 clays Non-clayey soils Highly weathered oxides
  • 63. Measuring CEC saturate w/ ammonium remove xs salt leach measure
  • 64.
  • 65.
  • 66.
  • 67.
  • 68.
  • 69. Rough Rule of thumb CEC = ( % O.M. x 200 CEC ) + ( % clay x 50 CEC ) But …CEC of clay minerals ranges from 3 to 150 !
  • 70.
  • 71. (cmol c /kg) low really high high
  • 72. Sample calculation Calculate the net negative charge of a soil sample containing 5% organic matter (OM) and 20% montmorillonite (smectite) type of clay. Net negative charge = (% OM * its’ CEC) + (% clay * its’ CEC) Net negative charge = [( 5 /100) kg * 200 cmol c /kg] + [( 20 /100) kg * 100 cmol c /kg] CEC OM ~ 200 cmol c /kg CEC montmorillonite ~ 100 cmolc/kg 10 cmolc/kg + 20 cmolc/kg = 30 cmolc/kg
  • 73.
  • 74. CEC and pH – for 1:1 clays and humus CEC low high 3 8 Soil pH Why?
  • 76. Influence of pH on the CEC of smectite and humus or Kaolinite Edge charge = Internal charge
  • 77. Charge characteristics Colloid type Total charge Constant (%) Variable (%) Positive charge Organic 200 Smectite 200 Kaolinite 8 10 90 0 5 95 2 95 5 0 Permanent charge pH dependent charge
  • 78. CEC and weathering intensity Alfisols, Vertisols, Argiudolls Ultisols Oxisols
  • 79.
  • 80. Cations – acid forming vs base forming Sources of acidity: Hydrolysis (weathering reaction)  H + (requires water) Biological decomposition  H + (requires water) Dissolution (weathering reaction)  Al 3 + (requires water) Al 3 + + 3H 2 O  Al(OH 3 ) + 3H + non-acid “ Acid cations ” (H + , Al 3+ ) “ Base cations ” (everything else, e.g., Ca 2+ , NH 4 + , K + , etc.)
  • 81. Equation for base saturation non-acid cation “ Acid cations ” (H + , Al 3+ ) “ Base cations ” (everything else, e.g., Ca 2+ , NH 4 + , K + , etc.)
  • 82. Back to why we might care… … plants (i.e. FOOD!)
  • 83. How a plant works Nutrients
  • 84. How a plant works
  • 85.
  • 86.
  • 87.
  • 88.
  • 89. Cation exchange in action The fate of the K is limited by the other ions present on the exchange surface
  • 90.
  • 91.
  • 92.
  • 93.
  • 94. Particle Size Clay Silt Sand Pore size , infiltration rate, drainage rate, aeration
  • 95. Surface area, pore volume , nutrient supply capacity, plasticity and cohesion, swelling Particle Size Clay Silt Sand
  • 96. A soil is said to be at field capacity just after all the gravitational water has drained from the soil. Water potential (suction) is -10 cbar at field capacity. Many crop plants are most productive when soil moisture levels are kept at levels of at least 60 - 90% of field capacity. For soil a , what is the minimum range of soil volumetric water content you would aim for to keep your crops most productive? For soil a, field capacity (-10 cbar) is at at ~38%. 60% of 38% is 0.6*38% or ~ 23% 90% of 38% is 0.9*38% or ~34% You would want to keep your volumetric moisture content up at at least 23 to 34%.
  • 97. Which soil (a or b) has a higher bulk density? What is the bulk density of soil a ? Max volumetric water content for soil a is ~45%, which means the %PS for soil a is ~45%. %PS = [1 – (D b /D p )] * 100 45% = [1 – (X/2.65)] * 100 X= 1.46 g/cm 3 Soil a has higher bulk density. You can tell because it’s maximum water content is lower.
  • 98. If your field started completely dry, and your irrigation system delivers 1 cm water per hour, how long would you have to irrigate soil a for to bring the top 30 cm of your field to a moisture content that is 60% of field capacity?
  • 99.  
  • 100.
  • 101.
  • 102.
  • 103.  (cbar)  (%) Moisture Characteristic Curve Suction units: 1 bar 100cbar 1.01971 x 10 5 Pa 0.9869 atm 10 6 dynes/cm 2 14.5 psi 1019.753 cm H 2 O ~33 feet H 2 O volumetric water content Suction 0 -10 -100 -10 3 -10 4 -10 5 0 10 20 30 40 50 60
  • 104. Difference is a function of texture, structure, & OM content.  (cbar)  (%) Estimating moisture content using Moisture Characteristic Curve and Tension data -15 bar -490 bar  (bar) soil A soil B soil C soil D -1 -10 -100 -10 3 -10 4 -10 5 0 10 20 30 40 50 60 -0.01 -0.1 -1 -10 -100 -1000 -10 -100 -1000 -10 4 -10 5 -10 6  (cm)
  • 105.
  • 106. Shape of silicon tetrahedron and aluminum octahedron O OH O O O OH OH OH OH Si Al
  • 107. Octahedral sheet Octahedral sheet Tetrahedral sheet Tetrahedral sheet Tetrahedral sheet Tetrahedral sheet
  • 108.
  • 109. Permanent charge Octahedral sheet neutral Net negative charge
  • 110. pH-dependent charge: on edges!!! Espec. Important in kaolinite, humus, where no internal charge imbalance H + bound tightly, so the lower the pH , the less exchange there is (i.e., lower nutrient availability )
  • 111. CEC and pH – for 1:1 clays and humus CEC low high 3 8 Soil pH
  • 112. Smectite Kaolinite1:1 Fine-grained mica Chlorite 1:1 clays Location of internal charge imbalance No charge except at edges octahedral tetrahedral octahedral tetrahedral tetrahedral octahedral tetrahedral tetrahedral octahedral tetrahedral tetrahedral tetrahedral tetrahedral tetrahedral tetrahedral octahedral tetrahedral octahedral Vermiculite 2:1 clays H bonding Consider: hydration, cation adsorption, swelling, shrinking, plasticity “ Young” Clays “ Old” Clays
  • 113. 100% silt 100% sand 100% clay % clay % silt % sand
  • 114.
  • 116.
  • 118.
  • 119.  
  • 120.
  • 121. Exchange affinity This is referred to as the “ Lyotropic series” Strength of adsorption proportional to valence (charge) ÷ hydrated radius

Editor's Notes

  1. no protein enzymes in existence to form the first nucleotides or catalyze the first formation of RNA strands because these proteins are only formed by RNA … all that was required was an assemblage of RNAs capable of both catalysis and replication with change. The prebiotic synthesis of RNA may have been carried out on the surfaces of clay minerals (and other layered minerals) using montmorillonite clay-catalyzed reactions of activated monomers (the building blocks of RNA)
  2. ALL clay minerals have edge charges.
  3. (a) 13 negative charges and 5 positive charges; (b) 3 negative charges and 6 positive charges
  4. Upper case takes place readily as Ca2+ binds more strongly than does K+ (lyotropic series) Second case: need more than 3 K+ for the reaction to take place even though the reaction is a charge-balanced one (I.e., only 3 of the K+ are involved). This is because the Al3+ is higher on the lyotropic series. Note also that these are REVERSIBLE (unless something precipitates, volatilizes, or is strongly adsorbed).
  5. E- remember to put this on test
  6. Teton Dam failure story: used silt instead of clay as dam’s core, and it failed, killing 11 people and wiping out thousands of homes.
  7. Teton Dam failure story: used silt instead of clay as dam’s core, and it failed, killing 11 people and wiping out thousands of homes.