Soil Science and Agricultural Chemistry

Chemical Properties of Soils: Soil Reaction, Cation Exchange Capacity, Base Saturation, and Redox Potentials

Explore the fundamental chemical properties of soils including soil pH, active and reserve acidity, Cation Exchange Capacity (CEC), Base Saturation, and oxidation-reduction systems, tailored for UP TGT and PGT Agriculture examinations.

Fundamentals of Soil Reaction and Soil pH

Soil reaction is one of the master variables governing chemical, biological, and physical properties of soils. It refers to the degree of acidity or alkalinity of the soil mass, quantitatively expressed as the negative logarithm of hydrogen ion activity (pH = -\log10[H^+]).

  • Active Acidity: Refers to the concentration of hydrogen (H^+) and aluminum (Al3+) ions present in the soil solution at any given moment. It is measured directly using a glass electrode pH meter.
  • Reserve (Potential) Acidity: Represents the quantity of exchangeable H^+ and Al3+ ions held electrostatically on the colloidal exchange complex (clays and humus). It is vastly larger than active acidity and acts as a buffer.
  • Buffering Capacity: The ability of a soil to resist sudden changes in pH upon the addition of acidic or basic amendments. Fine-textured soils rich in 2:1 layer silicates and organic matter possess high buffering capacities, whereas coarse-textured sandy soils have low buffering capacities.

Cation Exchange Capacity (CEC) and Anion Exchange Capacity (AEC)

Cation Exchange Capacity (CEC) is the capacity of a soil to adsorb and exchange positively charged ions (Ca2+, Mg2+, K^+, Na^+, NH_4^+, H^+, Al3+). It is expressed in centimoles of charge per kilogram of dry soil (cmol(p^+)/kg or traditionally meq/100g).

  • Origin of Charges: Isomorphic substitution within clay mineral crystal lattices generates permanent negative charges (e.g., substitution of Mg2+ for Al3+ in octahedral sheets, or Al3+ for Si4+ in tetrahedral sheets). pH-dependent charges arise from the dissociation of functional groups (carboxyl and phenolic hydroxyls) on soil organic matter and exposed edges of silicate clays.
  • CEC Values of Colloids: Humus (100-300\;cmol/kg), Vermiculite (100-150\;cmol/kg), Smectite (80-120\;cmol/kg), Illite (20-40\;cmol/kg), Kaolinite (3-15\;cmol/kg).
  • Anion Exchange Capacity (AEC): The capacity of a soil to hold and exchange negatively charged anions (NO_3^-, Cl^-, SO_42-, H_2PO_4^-). It is prominent in highly weathered tropical soils (Oxisols and Ultisols) rich in sesquioxides (iron and aluminum oxides/hydroxides) under acidic pH conditions where protonation creates positive charges.

Base Saturation Percentage and Exchangeable Sodium Percentage (ESP)

Base saturation is a vital chemical fertility index that denotes the proportion of the soil CEC occupied by basic cations (Ca2+, Mg2+, K^+, Na^+) rather than acidic cations (H^+, Al3+).

  • Formula: Base Saturation (%) = ( Sum of Basic CationsCEC ) × 100.
  • Agronomic Significance: Soils with high base saturation (>80%) are typically neutral to alkaline and fertile. Soils with low base saturation (<50%) are acidic, heavily leached, and prone to aluminum toxicity and calcium/magnesium deficiencies.
  • Exchangeable Sodium Percentage (ESP): Measures the sodicity hazard of soils, calculated as ESP = ( Exchangeable Na^+CEC ) × 100. Soils with an ESP > 15 are classified as sodic (alkaline) soils, characterized by structural dispersion and poor hydraulic conductivity.

Oxidation-Reduction (Redox) Potential (Eh) in Submerged Soils

Redox potential (Eh), measured in millivolts (mV), reflects the intensity of oxidation or reduction reactions in soils, governed by the availability of electron acceptors.

  • Aerobic Soils: High Eh (+400 mV to +700 mV). Oxygen serves as the primary electron acceptor. Organic matter decomposes rapidly; nitrogen exists as nitrate (NO_3^-); iron is present in oxidized ferric (Fe3+) forms.
  • Submerged (Paddy) Soils: Low Eh (dropping below +300 mV down to -300 mV). Oxygen is rapidly depleted by microorganisms. Sequential reduction of alternative electron acceptors occurs: NO_3^- is reduced to N_2 gas (denitrification), Mn4+ is reduced to soluble Mn2+, Fe3+ is reduced to mobile Fe2+ (causing gleying), and sulfates are reduced to hydrogen sulfide (H_2S).
  • Nutrient Availability Dynamics: Submergence increases the availability of phosphorus due to the dissolution of iron phosphate complexes upon reduction of Fe3+ to Fe2+, but can lead to zinc deficiency due to the precipitation of zinc as frankinite or zinc sulfide.

Soil Salinity and Alkalinity Chemistry

Salt-affected soils are categorized based on three chemical parameters: Electrical Conductivity of the saturation extract (EC_e), soil pH, and Exchangeable Sodium Percentage (ESP).

  • Saline Soils: EC_e > 4\;dS/m, pH < 8.5, ESP < 15. Dominated by neutral soluble salts of chlorides and sulfates of sodium, calcium, and magnesium. White alkali crusts are common.
  • Sodic (Sodified/Alkaline) Soils: EC_e < 4\;dS/m, pH > 8.5, ESP > 15. Dominated by sodium carbonate and bicarbonate, leading to high hydroxyl ion concentrations and dispersion of soil colloids (black alkali).
  • Saline-Sodic Soils: EC_e > 4\;dS/m, pH < 8.5, ESP > 15. Properties are intermediate; if leached without calcium amendments, they convert into sodic soils. Reclamation requires gypsum (CaSO_4 · 2H_2O) for sodic soils to replace exchangeable sodium with calcium.
Comparison of Salt-Affected Soil Classes
ParameterSaline SoilsSodic (Alkaline) SoilsSaline-Sodic Soils
Electrical Conductivity (ECe)> 4 dS/m< 4 dS/m> 4 dS/m
Soil pH (saturated paste)< 8.5> 8.5 (up to 10.0)< 8.5
Exchangeable Sodium Percentage (ESP)< 15> 15> 15
Dominant SaltsNaCl, Na2SO4, CaCl2, MgCl2Na2CO3, NaHCO3Combination of both
Soil Physical ConditionFlocculated (good structure)Dispersed (poor permeability)Flocculated while high salt
Cation Exchange Capacity (CEC) of Soil Colloids
Soil Colloid TypeCEC Range (cmol(p+)/kg)Origin of Charge
Humus (Organic Matter)100 - 300pH-dependent (carboxyl, phenolic)
Vermiculite100 - 150Permanent (isomorphic substitution)
Smectite (Montmorillonite)80 - 120Permanent (octahedral substitution)
Illite (Hydrous Mica)20 - 40Permanent (tetrahedral substitution)
Kaolinite3 - 15pH-dependent (broken edges)
Memory Trick / Mnemonic
CEC Magnitude Order of Soil Colloids
Happy Veterinarians See Interesting Kittens (Humus, Vermiculite, Smectite, Illite, Kaolinite)

Helps recall the descending order of Cation Exchange Capacity (CEC) from highest (100-300\;cmol/kg for humus) to lowest (3-15\;cmol/kg for kaolinite).

Memory Trick / Mnemonic
Sequential Reduction of Electron Acceptors in Submerged Soils
O N M F S C (Oxygen, Nitrate, Manganese, Iron, Sulfate, Carbon dioxide)

Recalls the exact redox sequence of electron acceptors as soil becomes anaerobic upon flooding (Eh declines from positive to negative values).

โšก High-Yield Exam Points (UP TGT / PGT Focus)
  • Soil pH is defined as the negative logarithm of hydrogen ion activity: pH = -\log10[H^+].
  • Humus possesses the highest CEC among all soil colloids ranging between 100 to 300 cmol(p+)/kg.
  • Kaolinite is a 1:1 type expanding/non-expanding clay mineral with a low CEC of 3 to 15 cmol(p+)/kg.
  • Sodic soils are reclaimed using gypsum (CaSO_4 · 2H_2O), which supplies divalent calcium ions to replace sodium on the exchange complex.
  • Electrical Conductivity (EC) of saturation extract for saline soils is greater than 4 dS/m at 25ยฐC.
  • Base saturation percentage is calculated as the sum of basic cations divided by CEC multiplied by 100.
  • Active acidity refers to hydrogen ions in the soil solution, whereas reserve acidity is held on exchange sites.
  • Submerged paddy soils exhibit reduced redox potentials (Eh), causing reduction of insoluble Fe3+ to soluble Fe2+.
โš ๏ธ Common Mistakes & Exam Pitfalls
  • Confusing saline soils with sodic soils: Saline soils have pH < 8.5 and EC > 4 dS/m, whereas sodic soils have pH > 8.5 and ESP > 15.
  • Assuming kaolinite has a high CEC: Kaolinite has a very low CEC (3-15 cmol/kg) due to minimal isomorphic substitution and fixed 1:1 lattice structure.
  • Believing that active acidity is larger than reserve acidity: Reserve acidity is thousands of times larger than active acidity in mineral soils.