Salinity Basics
Soil salinity in Manitoba is estimated to affect 700,00 acres of
agricultural land. Usually this is in the form of localized areas
around sloughs and potholes, or along roadside ditches. While many
of these saline areas occur naturally, some non-saline cropland has
become salt –affected over the years or has become more intensively
affected as the result of traditional agricultural practices.
The main cause of salinity is excess water. Water tables
within 6 ft. of the soil surface can carry dissolved salts, found
naturally in prairie soils, into the plant root zone or even to the
soil surface by wick action. Salts reduce plant growth by preventing
the uptake of water and nutrients on these soils. There are three
types of salt-affected soils:
- true saline soils are those with sufficient amounts of soluble
salts to impair crop growth;
- sodic soils contain sufficient exchangeable sodium to
interfere with the growth of plants through undesirable soil
structure (very hard and crusted when dry and very slippery when
wet);
- saline-sodic soils contain a combination of soluble salts and
exchangeable sodium sufficient to interfere with plant growth.
Sodic or saline-sodic soils represent about 75,000 acres in
Manitoba. Soil test information can determine which type of
salt-affected soil the producer is dealing with. Electrical
conductivity (E.C.) measures total salt content; sodium adsorption
ratio (SAR) measures the ratio of sodium relative amounts of
calcium, magnesium and sodium; soic soils have considerably more
sodium present than calcium and magnesium).
The data can be summarized in the following table:
Type of Soil
Salinity |
E.C.
(dS/m) |
SAR |
pH |
Main
Problem |
non-saline |
< 4 |
< 13 |
< 8.5 |
none |
saline |
> 4 |
< 13 |
< 8.5 |
impaired water and nutrient uptake |
sodic |
< 4 |
> 13 |
> 8.5 |
poor trafficability, poor seedbed |
saline-sodic |
> 4 |
> 13 |
< 8.5 |
both conditions occur |
The greater the values for E.C. and SAR, the greater severity of
soil salinity and therefore the greater degree of difficulty in
remediating the salt-affected soils.
To reclaim a waterlogged, salt-affected soil, three basic steps
are required:
- The water table must be lowered. This is best
accomplished using perennial forages or through improvements in
subsurface drainage.
- The excess salts must be leached out. Rainfall or
irrigation should accomplish this over time.
- Where the sodium content of the soil is high, the sodium
must be replaced with at more desirable cation, such as calcium.
Prairie soils usually have enough calcium present to replace the
sodium.
Is Gypsum the Answer to These Problems
Gypsum has recently been suggested as soil amendment to remediate
such problems soils.
But application to saline soils will not be beneficial. In fact,
gypsum (calcium sulfate) is a salt itself, and may actually increase
the salt content.
Application of gypsum to sodic soils will provide calcium to
displace sodium. However, one still needs rainfall or irrigation to
leach the displaced sodium down and secondly, internal drainage to
allow downward movement out of the root zone. If either of these
conditions is lacking, then gypsum application alone is fruitless.
As mentioned previously, our soils tend to be naturally high in
calcium. In these instances application of sulfur alone (elemental
or ammonium sulfate) will solubilize and generate free calcium to
displace the sodium.
Where does gypsum fit? Gypsum is an effective supplier of calcium
and sulfur to crops. Since our soils are predominately calcium
carbonate based, this nutrient is generally not lacking and calcium
applications are not required. Sulfur deficiencies are more
widespread, and gypsum is effective in meeting crop needs. Sulfate-S
from gypsum is less available than from ammondium sulfate or
ammonium thiosulfate, but more readily available than from elemental
S.
Gypsum contains 14-20% S and should be compared to other S
fertilizers based on the cost per pound of S supplied. At present,
sulfur fertilizers cost about 20-22 cents per pound of S. Gypsum may
be available in a ground or pelted form. Specialized equipment, such
as lime spreaders, may be required to adequately apply the ground
form.
References:
Dryland Salinity Investigation Procedures Manual. Alberta
Agriculture. 1992.
Management of saline soils. Agriculture Canada. Publication
1624/E. 1983
Stalinization of soils in: The health of our soils – Towards
sustainable agriculture in Canada. AAFC. Publication 1906/E. 1995.
Soils ’84, Lesson 3: Salinity and Drainage. Manitoba
Agriculture. 1984.
Soil Salinity – Manitoba Map Sheet. Agriculture Canada.
Publication 5261/B. 1990.
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