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Title: ACID, SALINE, AND SODIC SOILS


1
Chapter 3
  • ACID, SALINE, AND SODIC SOILS

2
Why study acid, saline, and sodic soils?
  • Acid, saline, and sodic soils have unique
    chemical and physical properties that influence
    how plants grow.
  • Since availability of nutrient ions is determined
    by their chemistry, it is important to understand
    how nutrient availability will be influenced by
    the special chemical properties of these soils.
  • What are acid soils?
  • Acid soils, technically defined, are soils that
    have a pH less than 7.0, since by convention pH
    of 7.0 is neutral, above 7.0 is basic (or
    alkaline) and below 7.0 is acidic. From the
    standpoint of plant growth, soil management is
    usually not affected until the pH is less than
    about 6.2 for legumes and 5.5 for non-legumes.
  • Understanding the concept of pH is fundamental to
    understanding and managing acid soils. Since pH
    is defined as the log H activity, a pH change
    of one unit (e.g. from pH of 6.0 to pH of 5.0)
    represents a 10-fold increase in acidity.
  • What causes soil acidity?
  • Acid soils are a natural phenomenon related to
    soil parent material and rainfall conditions
    under which the soil developed. Soils developed
    from limestone parent material, for example will
    often be neutral or alkaline in their pH (e.g. pH
    gt 7). Granitic parent material, on the other
    hand, will favor development of an acid soil.

3
Acid Soils
  • Under high rainfall conditions (gt 30 inches/year)
    parent material that is permeable, such as
    sandstone, will likely become acidic because
    there is sufficient leaching over geological time
    (tens and hundreds of thousands of years) to
    remove even basic materials like limestone.
  • Rainfall, by nature is slightly acidic because
    water and carbon dioxide form carbonic acid in
    the atmosphere (i.e. acid rain is normal).
    Thus, as basic materials are leached out of the
    parent material, H may remain to cause the soil
    to be acidic.
  • CO2 H2O ?? H HCO3-
  • atmosphere carbonic acid
  • Two other factors, that contribute to soil
    acidity, are the removal of basic cations and use
    of N fertilizers associated with intensive crop
    production.

4
Basic and Acidic Cations
  • The term basic cations is used to designate
    cations that, when combined with hydroxide (OH-)
    form a compound that would dissolve in water and
    create an alkaline solution
  • The cations Na, K, Ca 2 , and Mg 2 are good
    examples. In contrast, the hydroxides of Al 3
    and Fe 3 are so insoluble the ions would not be
    present in solution unless the solution were
    acidified to dissolve them.
  • Al 3 and Fe 3 , are usually referred to as
    acidic ions for this reason. Plants generally
    absorb nutrient cations in excess of nutrient
    anions. In this process, electrical neutrality
    or ion-charge balance may be maintained by
    simultaneous absorption of OH- or the exudation
    of H by the plant root.
  • In either case the result is a contribution of
    acidity to the soil.
  • Plant uptake of basic cations in excess of anions
    in a natural, non-agricultural environment
    contribute little to soil acidity because plants
    die and recycle the cations in-place.
  • Intensive agriculture accelerates the
    acidification because the bases are generally
    removed from the field with harvest and are not
    recycled.

5
Intensive agriculture relies heavily on the use
of ammoniacal sources of N. These fertilizer
materials undergo biological oxidation to NO3-
according to the overall general reaction NH4
2O2 ? NO3- 2H H2O which produces two
protons for every mole of N oxidized
6
mZE 11H 42He E- elementm massz - atomic
number ( of protons in the nucleus) All hydrogen
atoms have one proton____________________________
______________11H 21H 31H_______________________
___________________ stable stable radioactive deu
terium tritiummass 1 mass2 mass3no
neutron 1 neutron 2 neutrons1 proton 1 proton 1
proton1 electron 1 electron 1 electron__________
________________________________126C 136C 146C__
________________________________________stable st
able radioactivemass12 mass13 mass146
neutrons 7 neutrons 8 neutrons6 protons 6
protons 6 protons6 electrons 6 electrons 6
electrons________________________________________
__
7
Plant Uptake and Exchange
NO3-
OH-
NH4
H
8
What is the nature of soil acidity and soil
buffer capacity?
  • Soils behave as a system made up of the salt from
    a weak acid and strong base.
  • Clay and soil organic matter, provide surfaces
    for adsorption of cations
  • Clays have a net negative charge resulting from
    isomorphic substitution of divalent for trivalent
    ions (Mg 2 for Al 3 ) and trivalent for
    tetravalent ions (Al 3 for Si 4 ) within the
    mineral structure.
  • Soil organic matter contributes to the net
    negative charge of soils because of dissociated
    H from exposed carboxyl and phenol groups.
  • The cation exchange capacity (CEC) of organic
    matter is pH dependent, whereas most of the CEC
    from clays is not.
  • A small contribution to soil CEC is from
    unsatisfied charges at broken edges of clays.
  • The strength with which cations are adsorbed to
    cation exchange sites is directly proportional to
    the product of the charges involved and inversely
    proportional to the square of the distance
    between charges (Coulombs law). Consequently,
    the lyotropic series describing the adsorption of
    cations on clay particles in soils is generally
    considered being
  • Al 3 ? H gt Ca 2 ? Mg 2 gt K ? NH4 gt Na.

9
  • The similarity in strength of adsorption for
    Al and H is because H, although only 1/3 the
    charge strength of Al, is much smaller in
    diameter, allowing it to get closer to the
    internal negative charge of clays than is
    possible for the larger Al.
  • The electrostatic adsorption of cations on clay
    and organic matter surfaces creates a reservoir
    of these ions for the soil solution. The
    adsorbed ions are in equilibrium with like ions
    in the soil solution

10
Soil pH
  • Relative amounts of each ion adsorbed and in
    solution varies depending upon their relative
    concentrations in the soil solution and how
    strongly the ion is adsorbed (lyotropic series).
  • Amount of H in the soil solution is 1/100th the
    amount adsorbed on cation exchange sites
  • We might expect the amount of Ca 2 and K to be
    present in the soil solution at about 1/50th and
    1/10th their amount adsorbed on cation exchange
    sites
  • When soil pH is determined, only the H in the
    soil solution is measured.
  • Soil pH referred to as active acidity, whereas
    the H adsorbed on exchange sites is called
    potential or reserve acidity.
  • The buffer capacity of soils, that is, their
    ability to resist change in pH when a small
    amount of acid or base is added, is a function of
    their exchangeable acidic and basic cations.
  • Soils with low CEC (e.g. sandy, low organic
    matter) have weak buffer capacity, while soils
    with high CEC (e.g. clayey, high organic matter)
    have strong buffer capacity.

11
Effect of soil acidity on plants
  • Plant species vary in their response to acidic
    soil conditions. Those which have evolved and
    are cultivated in humid regions (e.g., fescue,
    blueberries, and azalea) tolerate acidic soils
    better than other species (e.g., bermudagrass and
    wheat) grown in arid and semiarid climates.
  • The chemical environment that plants must
    tolerate, or can benefit from, may be inferred
    from the relationship of percent base saturation
    and pH

Soil pH
12
pH and pOH
  • pH -log H
  • pOH - log OH-
  • pH pOH -log Kw 14
  • Kw ion-product constant for water
  • Kw HOH- 1 x 10-14
  • Ka acid-dissociation constant
  • Ka HA-/HA (A- conjugate base of the
    acid)
  • Kb base-dissociation constant
  • Kb OH-A/OHA (A conjugate acid of the
    base)
  • Ka Kb Kw
  • Ksp solubility-product constant
  • -degree to which a solid is soluble in water
  • -equilibrium constant for the equilibrium
    between an ionic solid and
    its saturated solution

13
Solubility
  • Solubility of a substancequantity that
    dissolves to form a saturated solution (g of
    solute/L)
  • Solubility product
  • Equilibrium constant for the equilibrium
    between an ionic solid and its saturated solution

Solid AgCl is added to pure water at 25C. Some
of the solid remains undissolved at the bottom of
the flask. Mixture stirred for 2 days to ensure
an equilibrium is reached. Ag conc. Determined
to be 1.34x10-5M. What is Ksp for AgCl?
AgCl ?? Ag Cl- Ksp AgCl-
At equilibrium, conc of Ag 1.34 x 10-5
conc of Cl- 1.34 x 10-5
Ksp (1.34 x 10-5)(1.34 x 10-5) 1.80 x
10-10
14
  • The percentage base saturation identifies the
    proportion of the CEC that is occupied by cations
    like Na, K, NH4, Ca 2 , and Mg 2 compared to
    the acidic cations of H and Al 3 .
  • This relationship is responsible for the fact
    that deficiencies of Ca, Mg and K are rare in
    soils with a pH near or above neutral.
  • Aluminum oxides (Al(OH)3, also expressed as
    (Al2O3 ? 3H2O) are of such low solubility that Al
    3 usually is not present in the soil solution or
    on cation exchange sites until the soil pH is
    less than about 5.5.
  • The apparent solubility product constant (Ksp)
    for Al(OH)3 in soils is about 10-30. From this,
    the concentration of Al in the soil solution
    and its change with change in pH can be
    calculated.

15
Aluminum
Solving the above at pH of 5, OH- would be equal
to 10-9
The concentration of Al (10-3) is moles/liter.
Since the atomic weight of Al is about 27, a
mole/liter would be 27 grams/liter (g/L) and the
concentration of 10-3 is equal to 0.027 g/L, or
27 ppm. 27 ppm at a pH of 5
16
Solubility
  • Critical to the management and growth of plants
    in acid soils is the knowledge that Al in the
    soil solution increases dramatically with
    decrease in pH below about 5.5. When solved for
    a soil pH of 4.0 (OH- is equal to 10-10), we have

A concentration of 1.0 mole/L is equal to 27 g/L
or 27,000 ppm. While there may not be a
1000-fold increase in soil solution Al 3
concentration when pH changes from 5.0 to 4.0,
these calculations should make it clear why Al 3
concentrations may be significant at pH 4.5, for
example, and immeasurable at 5.5.
17
Al toxicity
  • Soluble Al is toxic to winter wheat at
    concentrations of about 25 ppm.
  • Adverse effect of soil acidity on non-legume
    plants is usually a result of Al and Mn toxicity.
  • In winter wheat, Al toxicity inhibits or prunes
    the root system and often causes stunted growth
    and a purple discoloration of the lower leaves.
  • These symptoms are characteristic of P
    deficiency, and are likely a result of the plants
    reduced ability to extract soil P.
  • Al toxicity versus P deficiency? Solubility
    diagram

Laboratory exercise, applying P to decrease Al
toxicity?
18
pH preferences of common crops
  • pH is not an essential plant nutrient, and
    plants obtain their large H requirement from H2O
    and not H.
  • Thus, it is the chemical environment, for which
    pH is an index, that crops are responsive to
    rather than the pH itself.
  • Non-legumes require a soil pH above 5.5 because
    more acidic soils tend to have toxic levels of Mn
    and Al present.
  • Crops which grow well in soils more acidic than
    this can tolerate these metal ions and perhaps
    are ineffective in obtaining Fe from less acidic
    soils.
  • Legumes usually grow best at soil pH above 6.0
    because the rhizobium involved in fixing
    atmospheric N2 seem to thrive in an environment
    rich in basic cations.

Plants split H2O
Mangroves
Mangroves 2
19
How is soil acidity neutralized
  • Most effective way to neutralize soil acidity is
    by incorporation of aglime.

Neutralization of acid soil using aglime (CaCO3)
resulting in increasing exchangeable Ca and
formation of water and carbon dioxide.
20
Lime
  • Aglime is effective because it is the salt of a
    relatively strong base (calcium hydroxide) and a
    weak acid (carbonic acid), and is therefore basic
  • Ca(OH)2 H2CO3 ? CaCO3 H2O

carbonic acid
21
Lime needed to neutralize soil acidity
  • Exchangeable acidity must be neutralized in order
    to change soil pH because it represents most (99
    ) of the soil acidity. Since the amount of
    exchangeable acidity in the soil, at a given pH,
    depends on the soil CEC, the amount of lime
    required is a function of clay content, organic
    matter content, and soil pH.
  • Lime requirements can be determined directly in
    a laboratory by quantitatively adding small
    amounts of a solution of known strength base
    (e.g. 0.1 normal NaOH), to a known amount of the
    acid soil mixed with water.

22
pH and Lime
  • By measuring pH as the base is added, the amount
    of base required to obtain any pH can be
    estimated

Buffer index of 6.2
pH scale of 14? Why?
23
Lime
  • Direct determination of lime requirement is very
    time consuming and is not usually done in the
    routine determination of lime requirement by soil
    testing laboratories.
  • Direct determination identifies the amount of
    base, such as CaCO3, that must be applied if all
    the acidity is able to react with the base that
    is added
  • In practice, this is virtually impossible because
    of size differences between clay and organic
    matter colloids (very small) and the finely
    ground (relatively large) lime particles.
  • Field studies (calibration) can be conducted to
    develop the relationship between amounts of
    aglime identified by direct laboratory titration
    and crop response.

24
Lime Requirements
  • Most soil testing laboratories use an indirect
    method of determining aglime requirement.
  • Involves adding a known quantity of a lime-like
    chemical solution (i.e., buffer solution of pH
    7.2) to an acid soil and water mixture.
  • After equilibrium has been obtained (about two
    hours) the pH is measured.
  • This pH is often called the buffer pH or
    buffer index. The buffer index, by itself,
    does not identify how much lime must be added to
    neutralize an acid soil.
  • Field studies relating lime additions to soil pH
    are required to calibrate the buffer index, just
    as they would be in a direct titration approach.

25
Lime Requirements
Why do we now lime to 6.0? (and not anything
above 6.0)
26
Buffering Capacity
  • Buffer capacity is a function of CEC (e.g. clay
    and soil organic matter content).
  • Amount of lime required to neutralize acidity in
    a sandy soil (e.g. Meno fine sandy loam) and a
    fine textured soil (e.g. Pond Creek silt loam)
    will be quite different even when they have the
    same soil pH

27
Amount of potential acidity that needs to be
neutralized
28
How often should lime be applied
  • The answer to this question will depend on how
    intensively the soil is managed and how large is
    the soil buffer capacity. For example, the
    amount of basic cations removed in a 30-bushel
    wheat crop in grain and straw is shown to be
    about the same as that removed by a ton of good
    quality alfalfa hay

29
  • Soil will become acidic faster, and require
    liming more often, if both grain and straw are
    harvested.
  • If two fields are yielding at the same level, it
    might be expected that a sandy soil would need to
    be limed at lower rates, but more frequently,
    than a fine textured soil.

30
Common liming materials
  • Aglime. Any material that will react with, and
    neutralize, soil acidity may be considered for
    use to lime an acid soil. The most common
    liming material is aglime, a material that is
    primarily composed of calcium carbonate, mined
    from geological deposits at or near the earths
    surface.
  • Some deposits are high in magnesium carbonate and
    are called dolomitic limestone. Dolomitic
    limestone is also a good source of Mg for deep,
    sandy, acid soils where this nutrient may also be
    deficient. The mined limestone is usually
    crushed and sieved to obtain material of a small
    enough particle size to be effective for aglime.
  • Quick lime. Mined limestone may be processed to
    improve its purity and neutralizing strength.
    The term lime was initially used as a name for
    CaO, which may also be called unslaked lime,
    burned lime, or quick lime. It may be obtained
    by heating (burning) calcium carbonate to drive
    off carbon dioxide.

CaCO3 heat ? CaO CO2
Often used for stabilizing sewage sludge. When
added to the mixture of sewage solids and water,
it quickly reacts to raise the pH above 11
31
Liming Materials
  • Hydrated lime. Hydrated lime, which may also be
    called slaked lime or builders lime, is produced
    by reacting quick lime with water.

CaO H2O ? Ca(OH)2
32
Special Formulations
  • Liquid lime
  • Formulated by mixing finely ground limestone with
    water and a small amount of clay.
  • Clay is added to help keep the lime particles
    suspended in the water during application.
  • Since the solubility of CaCO3 is low, most of the
    lime is present in solid form and will react like
    an application of solid lime. The ECCE of the
    formulation will be much less (depends on how
    much water was added) than that of the lime used
    in the mixture, even when the dry lime had a high
    ECCE.
  • Typically the dry lime has an ECCE of nearly 100
    and the liquid lime is about 50 because about
    ½ of it is water.
  • Pelleted lime
  • Pelleted lime is created by compressing, or
    otherwise forming pellets out of finely ground,
    good quality CaCO3.
  • Neutralizing effectiveness of liming materials
    depends upon being able to maximize their surface
    contact with soil colloids.
  • The advantage of liquid lime and pelleted lime
    compared to conventional aglime is to minimize
    dust. The disadvantage is they are usually much
    more expensive, on a cost per ton of ECCE, than
    conventional aglime.

33
Industrial by-products.
  • Kiln dust from cement manufacturing plants,
  • Fly-ash from coal burning power plants,
  • Residual lime from metropolitan water treatment
    plants.
  • Effectiveness of these materials will depend on
    particle size and neutralizing strength of the
    material.

Lime from Water Treatment
  • History of Water Treatment

34
Plagiarism
Assignment Search Not until recently have
scientists documented that cereal in
Google Plagiarism
UC Davis Link
Mark 35 And when he had looked round about on
them with anger, being grieved for the hardness
of their hearts, he saith unto the man, Stretch
forth thine hand. And he stretched it out and
his hand was restored whole as the other
Nephi 218 But, behold, Laman and Lemuel would
not hearken unto my words and being grieved
because of the hardness of their hearts I cried
unto the Lord for them
35
How are the neutralizing values of liming
materials compared
  • Effective Calcium Carbonate Equivalent.
  • Effectiveness of the aglime identified as
    effective calcium carbonate equivalent, or ECCE.
  • Expression of the active ingredient of the
    material for neutralizing soil acidity.
  • ECCE of liming materials is expressed as a
    percentage of the material and takes into account
    the particle size and neutralizing strength of
    the material
  • Chemical Equivalence.
  • Equivalence of compounds relative to their acid
    neutralizing strength provides insight to their
    differences in neutralizing strength.
  • Accomplished by calculating the equivalent weight
    of a liming material and comparing it to the
    equivalent weight of CaCO3.
  • Only possible if the materials are pure
    chemically. This consideration is of interest,
    for example, when comparing the effectiveness of
    dolomitic lime (rich in MgCO3) to that of normal
    aglime (primarily CaCO3). The equivalent weight
    of each material is calculated, using the
    definition
  • An equivalent weight is the mass of a substance
    that will react with one gram of H, or one mole
    (6 x 1023) of charge.

36
Equivalent weights
  • Equivalent weights are the chemists way of
    converting apples and oranges (etc.), all to
    apples.
  • Atomic (or molecular) weight of an ionic species,
    divided by its charge is equal to its equivalent
    weight.
  • For both CaCO3 and MgCO3 the charge of ions
    involved is two, and one mole of the carbonate
    ion will neutralize two grams of H, or two moles
    of charge.
  • The molecular weight of CaCO3 is 100 and MgCO3 is
    84.
  • Equivalent weights are ½ their molecular weights,
    or
  • CaCO3 100/2 50
  • MgCO3 84/2 42
  • It only requires 42 g of MgCO3 to accomplish the
    same neutralizing as 50 g of CaCO3, the MgCO3 is
    50/42 or 1.19 times more effective than CaCO3.
  • Applying the same comparison to CaO (eq. wt. 28)
    and Ca(OH)2 (eq. wt. 37) it is clear that these
    materials would be required at much lower rates
    than CaCO3 (eq. wt. 50)

37
Important considerations to improve success of
liming
  • Soil Testing.
  • Reliable soil test (representative)
  • soil pH may be variable in the area (year to
    year?) (within year?)
  • Amount of Lime. The buffer index from a soil
    test serves as a good guide for determining how
    much lime should be added,
  • When non-legumes are grown successively in the
    same field, it is only necessary to apply enough
    lime to eliminate current and future Al and Mn
    toxicities.
  • Lime recommendations for continuous wheat
    production in Oklahoma are to apply only ¼ the
    amount required to raise the pH to 6.8.
  • This recommendation will raise the pH above 5.5
    and keep it below 6.5 to minimize the incidence
    of root-rot diseases.
  • Occasionally the buffer index for sandy, low
    organic matter soils will be so high that no lime
    is recommended.
  • In these cases a minimum of 0.5 ton ECCE/acre for
    non-legumes and 1.0 ton ECCE for legumes is
    recommended to assure the acidity will be
    corrected and the application is economical.
  • When lime recommendations are extremely large the
    amount should be split into an initial
    application of 5 ton/acre (230lb/1000 ft2)
    followed by the remainder applied a year later.

38
Considerations
  • Incorporation and Timing.
  • Lime must be physically mixed with the soil.
  • Pastures, perennial plantings, or no-till
    productions, may require three to five years
    before the lime causes a noticeable change in
    soil pH.
  • Important to lime fields before they are planted
    to a perennial crop or managed as no-till.
  • Systems where alfalfa is rotated with a
    non-legume annuals like corn or wheat, the field
    should be limed a year before the alfalfa is
    planted to take advantage of tillage operations
    related to corn or wheat production and allow
    more time for lime to react in the soil.
  • When lime is incorporated well, and there is good
    soil moisture, it may still take a year or more
    before noticeable change in soil pH occurs.
  • Tillage Depth. Lime recommendations are usually
    made assuming a six-inch tillage depth.
  • Sandy soils are usually cultivated to eight or
    ten inches and a proportional increase in the
    lime rate should be made.
  • For crops with a shallow root system, such as
    some vegetables, it may be important to reduce
    the lime rate to match a shallower depth of
    incorporation.

39
How can acid soils be managed without liming
  • Liming Alternative.
  • Acid tolerant varieties or different plant
    species.
  • Karl and Custer are not acid tolerant whereas the
    variety 2163 is acid tolerant.
  • Rye more acid tolerant than wheat.
  • The Al and Mn toxicity that prevent normal
    seedling root development in wheat can be
    alleviated by adding phosphate fertilizer in a
    band with the seed at planting.
  • Phosphate reacts strongly with Al to form
    insoluble aluminum phosphate, thus removing Al
    from solution and the exchange complex.
  • Rate of 60 lb P2O5/acre is required to obtain
    normal fall pasture but only 30 P2O5/acre is
    needed if wheat is managed for grain only.
  • If P is not deficient, the cost of applying the P
    for two or three years will usually equal the
    cost of an application of lime that would have
    lasted five to eight years.
  • These alternatives allow normal or near normal
    production but do not cause a change in soil pH.
  • Eventually the soil must be limed for long-term
    production.

40
What are saline soils
  • Classified as saline when they contain a high
    enough concentration of soluble salts to
    interfere with normal growth and development of
    salt-sensitive plants.
  • Soluble salts are compounds, like common table
    salt (NaCl), where ions that make up the salt are
    weakly bound and have a strong attraction for
    water.
  • These ions hold water quite tightly, salty water
  • (higher boiling point)
  • (lower freezing point)
  • Salt is added to water used in food preparation
    to raise the boiling point and hasten the
    process.
  • Salt spread on icy sidewalks and roads to melt
    ice that would otherwise remain solid at
    temperatures below freezing.
  • Soluble salts in soils soil water is held
    tightly enough by the ions that plants cannot use
    it (apparent moisture stress)
  • Saline soils characteristically remain moist
    longer than the rest of the field
  • Occupy poorly drained areas of the landscape
  • White surface layer of salt after they become
    dry.
  • Occur in semi-arid, temperate regions
  • Saline soils are uncommon in the moisture
    extremes of deserts and tropical rain forests.

41
Saline Soils
  • Saturating a soil sample with water (a paste
    condition) for about four hours,
  • Extracting the water (and dissolved salts)
  • Measuring its ability to conduct electricity.
  • Ions in water allow electricity to pass through
    it
  • More ions present the easier electricity is
    conducted
  • Conductivity is expressed in mhos/cm.
  • Conductivity of water is usually very low and
    expressed as mmhos/cm or micromhos/cm.
  • Soils are classified as saline when the extract
    of a saturated paste has an electrical
    conductivity (EC) equal to or in excess of 4,000
    micromhos/cm.
  • Concentration of soluble salts, expressed as ppm,
    is roughly equal to 0.65 times the conductivity
    expressed in micromhos/cm.
  • Soil with an EC of 4,000 micromhos/cm will
    contain about 2600 ppm soluble salts in the
    saturated soil solution.
  • Saline soils Reclamation
  • leaching soluble salts out of the soil.
  • create good surface and internal drainage.
  • incorporating large amounts of organic matter
    (create large pores in the surface soil)
  • Good quality irrigation water can be used to
    hasten the process.
  • Deep tillage should be avoided once the organic
    matter is incorporated
  • Salt tolerant species like bermudagrass or barley
    should be planted to provide a vegetative cover
  • Practices to reduce surface evaporation and
    encourage water movement downward ???

42
What is a Sodic Soil
  • Abnormally high levels of exchangeable sodium
    (Na).
  • When enough Na is adsorbed, clay particles repel
    each other.
  • Occurs when the exchangeable Na percentage (ESP)
    is equal to or exceeds 15
  • Soil pH of sodic soils will often be above 8.
  • Dispersed colloids become oriented as water moves
    into soil and eventually they plug soil pores.
  • Poor internal drainage resulting in dry subsoil
    and a moist or wet surface layer. Crops fail
    because of excess surface water (drown out) or
    for lack of water (dry subsoil) even though there
    may have been adequate rainfall or irrigation.
  • Reclaimed by improving surface and internal
    drainage and incorporating gypsum (CaSO4) in the
    surface.
  • Gypsum dissolves to supply a high concentration
    of Ca in soil solution that replaces
    exchangeable Na, freeing it to be washed out of
    the soil
  • Ca helps bind colloids into aggregates and
    restore soil permeability. Reclamation of sodic
    soils is similar to that of saline soils except
    that gypsum must be added to sodic soils.

43
What are Saline-Sodic Soils
  • Contain salts in excess of 4,000 micromhos/cm and
    exchangeable Na in excess of 15
  • Have all the features of the saline soil, and if
    reclamation procedures are used that do not
    include gypsum, they will become sodic soils when
    the salts are leached out.
  • Many salt affected soils are saline-sodic because
    a primary soluble ion is Na.
  • Reclamation takes several (2 or more) years,
    dependent upon the time required to get about two
    pore volumes of good quality water to pass
    through the soil.
  • Most soils are about 50 pore space and so a
    pore volume-depth for a four foot profile would
    be about two feet and two pore volumes about four
    feet.
  • Sandy soils in high rainfall regions may be
    reclaimed quite rapidly while clayey soils in
    semi-arid regions may take many years if rainfall
    is the only source of leaching water.

44
How Soluble is the Earths Crust
  • The extent to which the earths crust dissolves
    over time depends upon solubility of rocks and
    mineral, abundance of elements in the rocks and
    minerals, and rainfall.
  • Naturally occurring compounds containing either
    Na or Cl tend to be very soluble and, with time,
    end up in the oceans and seas of the world.

45
Turf
  • Does soil acidity increase in turf situations via
    the application of N
  • No continual removal of bases like in wheat and
    corn, thus soil acidity is diminished
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