Cation Exchange Capacity (CEC), Anion Exchange Capacity (AEC), Base Saturation, and Buffering Capacity
- Introduction
- Soils act as reservoirs of plant nutrients due to the presence of charged colloids — mainly clay minerals and organic matter (humus).
These colloids carry negative and positive charges, which allow them to adsorb, retain, and exchange ions (cations and anions) with the soil solution. - The ability of a soil to hold and exchange these ions determines its fertility, nutrient retention, and buffering power.
- Cation Exchange Capacity (CEC)
Definition
- Cation Exchange Capacity (CEC) is the total quantity of exchangeable cations that a soil can adsorb and exchange per unit weight of soil.
- In simpler terms:
CEC measures the soil’s ability to hold positively charged ions (cations) such as Ca²⁺, Mg²⁺, K⁺, Na⁺, and NH₄⁺ on negatively charged colloid surfaces.
- Unit of Measurement
- Milliequivalents per 100 grams of soil (meq/100g) or
- Centimoles of charge per kilogram (cmol(+)/kg)
- 1 meq/100g = 1 cmol(+)/kg
- Mechanism of Cation Exchange
- Clay and humus particles have negative surface charges.
- They attract and hold cations by electrostatic forces, not by chemical bonds.
- These cations are reversibly exchangeable with cations in the soil solution.
- Example: Clay – Ca + 2K+ ↔ Clay – (K)2 + Ca2+
- Thus, the cations on colloid surfaces are in dynamic equilibrium with those in the soil solution.
- Sources of CEC
- Isomorphous substitution in clay minerals (permanent charge).
- Ionization of hydroxyl groups (–OH) at clay edges (variable charge).
- Dissociation of carboxyl (–COOH) and phenolic (–OH) groups in humus.
- Factors Affecting CEC
|
Factor |
Effect |
Explanation |
|
Type of clay |
High in 2:1 clays, low in 1:1 clays |
Montmorillonite > Illite > Kaolinite |
|
Amount of clay |
Directly proportional |
More clay → more exchange sites |
|
Organic matter |
Strongly increases CEC |
Humus has high CEC (200–400 meq/100g) |
|
Soil pH |
Increases with pH |
Deprotonation of –OH, –COOH groups |
|
Degree of weathering |
Highly weathered → low CEC |
Laterites, oxides have very low CEC |
- Typical CEC Values of Soil Components
|
Material |
CEC (meq/100g) |
|
Sand |
< 2 |
|
Kaolinite |
3 – 15 |
|
Illite |
20 – 40 |
|
Montmorillonite (Smectite) |
80 – 150 |
|
Vermiculite |
100 – 150 |
|
Humus |
200 – 400 |
- Importance of CEC
- Nutrient Retention: Prevents leaching of essential cations.
- Nutrient Supply: Cations held on colloids can be exchanged and made available to plants.
- Soil Fertility Indicator: High CEC = fertile soil.
- Soil Management: Influences fertilizer efficiency and lime requirements.
- Buffering Effect: Soils with high CEC resist sudden changes in nutrient concentration and pH.
- Anion Exchange Capacity (AEC)
Definition
- Anion Exchange Capacity (AEC) is the total quantity of exchangeable anions (negatively charged ions) that a soil can adsorb and exchange per unit weight of soil.
- In contrast to CEC, AEC involves positively charged soil surfaces that attract anions such as Cl⁻, NO₃⁻, SO₄²⁻, H₂PO₄⁻, and HCO₃⁻.
- Origin of AEC
- AEC arises mainly due to protonation of surface hydroxyl (–OH) groups in Fe, Al oxides, and the edges of kaolinite.
- It is therefore pH-dependent and dominant in acidic soils.
- –OH + H⁺ → –OH₂⁺
The protonated surface (–OH₂⁺) attracts anions.
- Factors Affecting AEC
|
Factor |
Effect |
Explanation |
|
Soil pH |
AEC ↓ as pH ↑ |
At high pH, H⁺ dissociates → fewer positive charges |
|
Type of mineral |
High in Fe/Al oxides |
Goethite, gibbsite have strong positive charges |
|
Organic matter |
Usually reduces AEC |
OM mainly produces negative charges |
|
Weathering |
Highly weathered tropical soils → higher AEC |
Due to dominance of sesquioxides |
- Relative Magnitude of AEC and CEC
|
Soil Type |
CEC (meq/100g) |
AEC (meq/100g) |
Dominant Exchange |
|
Alluvial (young) soil |
15–40 |
< 1 |
Cation exchange |
|
Black cotton (Vertisol) |
80–120 |
< 1 |
Cation exchange |
|
Lateritic / red soil |
5–15 |
2–5 |
Both possible |
|
Oxisols (highly weathered) |
3–10 |
3–10 |
Often both, pH-dependent |
- Importance of AEC
- Retention of Anions: Prevents leaching losses of NO₃⁻, PO₄³⁻, SO₄²⁻ in acidic soils.
- Influence on Fertilizer Efficiency: In strongly acid soils, AEC helps retain applied phosphate and sulfate.
- pH Buffering: AEC contributes to the soil’s ability to buffer against acidification.
- Relationship Between pH, CEC, and AEC
|
Soil Reaction (pH) |
Dominant Charge |
Exchange Capacity |
|
Strongly Acidic (<5.5) |
Positive |
AEC dominates |
|
Near Neutral (6–7) |
Negative |
CEC dominates |
|
Alkaline (>7.5) |
Strongly Negative |
High CEC, negligible AEC |
- Base Saturation (BS)
Definition
- Base Saturation is the percentage of the Cation Exchange Capacity (CEC) that is occupied by basic cations — primarily Ca²⁺, Mg²⁺, K⁺, and Na⁺.
- Base Saturation (%) = Sum of exchangeable bases / CEC×100
- Example Calculation
If a soil has:
- Exchangeable Ca²⁺ = 8 meq/100g
- Mg²⁺ = 2 meq/100g
- K⁺ = 1 meq/100g
- Na⁺ = 1 meq/100g
- CEC = 20 meq/100g
Then, Base Saturation = (8+2+1+1) / 20 ×100 = 60%
So, 60% of the exchange sites are occupied by basic cations; the remaining 40% are held by acidic cations (H⁺ and Al³⁺).
- Significance of Base Saturation
|
Base Saturation (%) |
Soil Reaction |
Fertility Status |
|
> 80 |
Neutral to slightly alkaline |
Very fertile |
|
50–80 |
Slightly acidic |
Moderately fertile |
|
20–50 |
Acidic |
Low fertility |
|
< 20 |
Strongly acidic |
Infertile, requires liming |
Interpretation:
- High base saturation → good nutrient reserve, well-limed soils.
- Low base saturation → acidic, leached soils (need lime or amendments).
- Buffering Capacity of Soil
Definition
- Buffering capacity is the ability of soil to resist changes in pH when acids or bases are added.
- Soils with high CEC (e.g., clays and humus-rich soils) have greater buffering capacity, while sandy soils have poor buffering.
- Factors Influencing Buffering Capacity
|
Factor |
Effect on Buffering |
|
Clay content |
↑ CEC → ↑ buffering |
|
Type of clay |
Montmorillonite > Kaolinite |
|
Organic matter |
Increases buffering (due to carboxyl groups) |
|
Base saturation |
High BS → strong buffering |
|
pH |
Minimum buffering near pH 6.0 (point of zero charge for many soils) |
- Importance of Buffering Capacity
- Stabilizes Soil pH — protects plants from rapid pH changes.
- Improves Fertilizer Efficiency — prevents nutrient toxicity/deficiency.
- Regulates Microbial Activity — maintains favorable environment for microbes.
- Guides Lime Requirement — high buffering soils need more lime to raise pH.
- Interrelationships: CEC, AEC, Base Saturation, and Buffering
|
Parameter |
Related To |
Effect on Soil Behavior |
|
CEC |
Negative charges |
Nutrient-holding capacity for cations |
|
AEC |
Positive charges |
Retention of anions, important in acidic soils |
|
Base Saturation |
Occupancy of exchange sites |
Indicates soil fertility and acidity |
|
Buffering Capacity |
Total exchange and reserve ions |
Resistance to pH and nutrient changes |
In general:
High CEC + High Base Saturation → High Fertility and Strong Buffering
Low CEC + Low Base Saturation → Infertile, Poorly Buffered Soil
- Typical Values in Common Indian Soils
|
Soil Type |
CEC (meq/100g) |
Base Saturation (%) |
pH Range |
|
Alluvial Soil |
15–25 |
70–90 |
6.5–8.0 |
|
Black Cotton (Vertisol) |
80–100 |
90–100 |
7.5–8.5 |
|
Red Soil |
5–15 |
40–60 |
5.5–6.5 |
|
Laterite Soil |
3–10 |
20–40 |
4.5–5.5 |
|
Sandy Soil |
< 5 |
< 30 |
6.0–7.0 |
- Summary Table
|
Parameter |
Definition |
Nature |
Typical Range |
Importance |
|
CEC |
Total cations adsorbed/exchanged |
Negative charge |
2–150 meq/100g |
Retains nutrients, improves fertility |
|
AEC |
Total anions adsorbed/exchanged |
Positive charge |
1–10 meq/100g |
Retains anions in acid soils |
|
Base Saturation |
% of CEC occupied by base cations |
Reflects soil reaction |
0–100% |
Indicates fertility and acidity |
|
Buffering Capacity |
Resistance to pH change |
Depends on CEC & OM |
Variable |
Maintains stable pH and fertility |
