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Soil Chemistry

Explore the significance of colloids in soil, including their negative charge, ion exchange mechanisms, and how they impact nutrient availability for plants. Learn about Cation Exchange Capacity (CEC), ion adsorption, leaching, and the role of pH in soil health.

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Soil Chemistry

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  1. Soil Chemistry

  2. Colloids(Clay minerals and humus and clay-humus complexes) • most chemically active part of soil • surface area • net negative charge • Nutrient cations (+) and anions (- ) are held on colloid surfaces, in reserve for plants

  3. Why are colloids negative? 1.Clay: • Oxygen ions along edges of micelles

  4. 2. humus: H+ ions tend to migrate away from organic compounds, to soil solution, leaving net negative charge (OH-)

  5. Ion Exchange What is the exchange? exchange of ions on soil surface(clay and humus) with ions in soil solution. (Cations and anions are involved)

  6. animate

  7. Leaching • ions (on soil surfaces) cannot be removed by leaching. • ions (in solution) can be removed by leaching.

  8. When soil is dried… …the ions on soil surfacesSTAY ON adsorption sites …the soluble ions (in soil solution) precipitate or crystallize (come out of solution) as salts.

  9. Examples of soluble cations precipitating

  10. Ion exchange Exchangeable ions on soil surface trading places with ions in solution.

  11. On soil surfaces, there areexchangeable and nonexchangeableions Exchangeable: weakly held, in contact with soil solution, ready for quick replacement, available for plants “outer sphere complex”

  12. Nonexchangeable: adsorbed by strong bonds or held in inaccessible places • (e.g., the K+ between layers of illite) • “inner sphere complex” • not part of ion exchange !

  13. Cation exchange capacity (CEC) Sum total of exchangeable cations that a soil can adsorb. If a soil has a high CEC, it prevents nutrients from being leached away from roots

  14. CEC Expressed in: milliequivalents per 100 g (meq/100g)

  15. Dynamic equilibrium Strive for equivalent proportions of solution and exchangeable ions. Upset equilibrium by: removal by plants leaching fertilization weathering Initiate ion exchange

  16. Ion exchange exampleAdd K fertilizer K+ Ca+2 Ca+2 K+ Ca+2 + K+ + K+ K+ Ca+2 K+ K+ K+ exchangeable exchangeable solution solution

  17. Rules of ion exchange • Process is Reversible • Charge by charge basis • Ratio Law: • ratio of exchangeable cations will be same as ratio of solution cations

  18. K+ Ca+2 Ca+2 K+ Ca+2 + K+ + K+ K+ Ca+2 K+ K+ K+ 1 Ca : 2 K 1 Ca : 2 K Same ratio

  19. Energy of adsorption The more strongly a cation is attracted to the exchange surface, the greater the chance of adsorption. Depends on: 1. charge 2. hydrated radius

  20. Strong --------------------------------------Weak Al+3 > Ca+2 > Mg+2 > [K+ = NH4+ ] > Na+ > H+

  21. The less tightly held (lower energy of adsorption) ions are the ones furthest from the soil surfaces and can be leached more easily and are further down the soil profile. • The strongly held ones are closer to the soil particle surfaces and tend to move more slowly down profile

  22. How do plants get nutrients? • Nutrients on the colloids are kept within root zone of plants. • H+ from roots exchange with cations on a charge-by-charge basis

  23. Two videos: • CEC • CEC

  24. Treating a sodic soil • Sodic: too much sodium (Na) • Add gypsum (CaSO4) : increases calcium concentration; Ca is adsorbed at expense of sodium Al+3 > Ca+2 > Mg+2 > [K+ = NH4+ ] > Na+ > H+

  25. Base saturation % of exchange sites occupied by basic cations(cationsother than H+ and Al+3) Base saturation + H+/Al ion saturation should equal 100%

  26. Base saturation and pH relationship(for midwest US soils) Notice neutral pH (7.0) requires a base sat of 80%.

  27. Soil pH

  28. Soil pH importance • Determines solubility of nutrients • Before plants can get nutrients, they must be dissolved in soil solution • Microbial activity also depends on pH

  29. pH negative log of the hydrogen ion concentration (also a measure of OH- concentration) If H+concentration > OH- : acidic If OH- > H+ : basic Soil pH is pH of solution, NOT exchange complex

  30. “Slightly acid” 6.0 – 6.6 “Moderately acid” 5.0 – 6.0 “Strongly acid” < 5.0 “Slightly basic” 7.4 – 8.0 “Moderately basic” 8.0 – 9.0 “Strongly basic” > 9.0 General soil pH conditions:

  31. In soil, both H+ and Al+3 ions produce acidity Al+3 produces H+ ions when it reacts with water. (when pH below 6: Al+3 is the cause of acidity)

  32. Causes of soil basicity • Hydrolysis of basic cations • Hydrolysis of carbonates

  33. 1. Hydrolysis of basic cations:(especially Ca+2, Mg+2, K+, NH4+, Na+) (also called exchangeable bases) Extent to which exchangeable bases will hydrolyze depends on ability to compete with H+ ions for exchange sites. Na Na Na Na + + OH- H2O Na H Na + Na Na Na Na

  34. K+ and Na+ are weakly held compared to Ca+2 and Mg+2. • Recall energy of adsorption So, K+ and Na+ are hydrolyzed easily and yield higher pHs .

  35. 2. Hydrolysis of carbonates(especially CaCO3, MgCO3, Na2CO3) • As long as there are carbonates in the soil, carbonate hydrolysis controls pH. • Calcareous soils remain alkaline because H+ ions combine with OH- to form H2O. • For those soils to become acid, all carbonates must be leached. • Basic cations replaced by Al+3 and H+ Ca+2 + HCO3- + OH- CaCO3 + H2O Na2CO3 + H2O Na + HCO3- + OH- (higher pH because Na more soluble)

  36. Causes of soil acidity • Accumulation of soluble acids • Exchangeable acids (Al+3, H+)

  37. Accumulation of soluble acidsat faster rate than they can be neutralized or removed • Carbonic acid (respiration and atmospheric CO2) b. Mineralization of organic matter (produces organic, nitric, sulfuric acids) Precipitation increases both a and b

  38. 2. Exchangeable acids Dissociation of exchangeable H+ or Al+3 Al+3 ties up OH- from water, releases an equivalent amount of H+ ions. Al+3 + H2O AlOH+2 + H+

  39. CEC and pH Only 2:1 silicate clays do not have pH-dependent CECs. Others are pH-dependent: 1:1 kaolinite: low pH: low CEC high pH: high CEC Oxidic clays pH dependence of humus

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