SALINITY
The salinity of soil refers to the amount of salts in the
soil. It can be estimated by measuring
the electrical conductivity (EC) of an extracted soil solution. Worldwide,
the major factor in the development of saline soils is a lack of precipitation.
Most naturally saline soils are found in (semi)arid regions and climates of the
globe.
SOIL
AFFECTED AREA :
Normally, the salinization of agricultural land
affects a considerable area of irrigation projects, on the order of 20 to
30%. A regional distribution of the
3,230,000 km² of saline land world wide is shown in the following table derived
from the FAO/UNESCO Soil Map of the World.
Region
|
Area (106ha)
|
84.7
|
|
69.5
|
|
59.4
|
|
Near and Middle
East
|
53.1
|
20.7
|
|
19.5
|
|
16.0
|
o
CAUSES OF SOIL
SALINITY :
Salt-affected soils are caused by excess accumulation
of salts, typically most pronounced at the soil surface. Salts can be
transported to the soil surface by capillary transport from a salt laden water
table and then accumulate due to evaporation. They can also be concentrated in
soils due to human activity, for example the use of potassium as fertilizer,
which can form sylvite, a naturally occurring salt. As soil salinity increases,
salt effects can result in degradation of soils and vegetation.
Salinization
is a process that results from:
Ø
High levels of
salt in the soils.
Ø
Landscape
features that allow salts to become mobile.
Ø
Climatic trends
that favoUr accumulation.
Ø
Human activities
such as land clearing, aquaculture activities and the salting of icy roads.
o
NATURAL OCCURENCE :
Salt is a natural element of soils and water. The ions
responsible for salinization are: Na+, K+, Ca2+, Mg2+ and Cl-.
As the Na+
(sodium) predominates, soils can become sodic. Sodic soils present particular
challenges because they tend to have very poor structure which limits or
prevents water infiltration and drainage.
o
DRY LAND SALINITY :
Salinity in drylands can occur when the
water table is between two to three metres from the surface of the soil. The
salts from the groundwater are raised by capillary action to the surface of the
soil. This occurs when groundwater is saline (which is true in many areas), and
is favored by land use practices allowing more rainwater to enter the aquifer
than it could accommodate.
For example, the clearing of trees for
agriculture is a major reason for dryland salinity in some areas.
o
SALINITY DUE TO
IRRIGATION :
Salinity from irrigation can occur over
time wherever irrigation occurs, since almost all water (even natural rainfall)
contains some dissolved salts. When the plants use the water, the salts are
left behind in the soil and eventually begin to accumulate.
Since soil salinity makes it more difficult
for plants to absorb soil moisture, these salts must be leached out of the
plant root zone by applying additional water. Salination from irrigation water
is also greatly increased by poor drainage and use of saline water for
irrigating agricultural crops.
o
EFFECT OF SALINITY
ON PLANT :
Salinity can affect plant growth in several
ways, directly and indirectly:
Ø
DIRECT SOIL SALINITY DAMAGE :
§
DECREASED WATER UPTAKE : High salts concentration results in high osmotic
potential of the soil solution, so the plant has to use more energy to absorb
water. Under extreme salinity conditions, plants may be unable to absorb water
and will wilt, even when the surrounding soil is saturated.
§
ION-SPECIFIC TOXICITY : When a plant absorbs water containing ions of harmful
salts (e.g. Sodium, Chloride, excess of Boron etc.), visual symptoms might
appear, such as stunted plant growth, small leaves, marginal necrosis of leaves or fruit distortions.
Ø
INDIRECT SOIL SALINITY :
§
INTERFERENCE WITH UPTAKE OF ESSENTIAL NUTRIENTS : An imbalance in the salts content may result in a harmful competition
between elements. This condition is called "antagonism", i.e. an
excess of one ion limits the uptake of another ion. For example, excess of
chloride reduces the uptake of nitrate, excess of phosphor reduces the uptake
of manganese, and excess of potassium limits the uptake of calcium.
§
SODIUM EFFECTS ON SOIL STRUCTURE : In saline
soils, sodium replaces calcium and magnesium, which are adsorbed to the surface
of clay particles in the soil. Thus, aggregation of soil particles is reduced,
and the soil will tend to disperse. When wet, a sodic soil tends to seal, its
permeability is dramatically reduced, and thus water infiltration capacity is
reduced as well. When dry, a sodic soil becomes hard has the tendency to crack.
This may result in damages to roots.
Salinity by itself actually improves soil
structure and eliminates to some degree the negative effect of sodium ions, but
of course, salinity cannot be increased without affecting plants growth.
o
EFFECT OF SALINITY
ON SOIL PHYSICAL PROPERTIES :
Soil water salinity can affect soil
physical properties by causing fine particles to bind together into aggregates.
This process is known as flocculation and is beneficial in terms of soil
aeration, root penetration, and root growth. Although increasing soil solution
salinity has a positive effect on soil aggregation and stabilization, at high
levels salinity can have negative and potentially lethal effects on plants. As
a result, salinity cannot be increased to maintain soil structure without
considering potential impacts on plant health.
o
MORPHOLOGICAL
SYMPTOMS :
Most of the parameters like low tillering, spikelet
sterility, less florets per panicle, low 1000 grain weight and leaf scorching,
are affected uniformly under both sodicity and salinity, however it is not a
thumb rule.
Major symptoms are :
§ White leaf tip followed by tip burning (salinity)
§ Stunted plant growth
§ Spikelet sterility
§ Low harvest index
§ Poor root growth
§ Patchy growth in field
o
TYPES OF
SALT-AFFECTED SOIL :
Salt buildup can result in three types of
soils:
I. SALINE SOIL :
Saline soils contain enough soluble salts to injure plants. They are
characterized by white or light brown crusts on the surface. Salts generally
found in saline soils include NaCl (table salt), CaCl2, gypsum (CaSO4), magnesium sulfate, potassium chloride and sodium
sulfate. The calcium and magnesium salts are at a high enough concentration to
offset the negative soil effects of the sodium salts. The pH of saline soils is
generally below 8.5.
II. SALINE-SODIC SOIL :
Saline-sodic soils are like saline soils,
except that they have significantly higher concentrations of sodium salts
relative to calcium and magnesium salts. The pH is generally below 8.5. Water
moves through these soils much as it does in saline soils, although the steps
for correcting saline-sodic soil are different. Simply leaching the salts from
this soil will convert it from saline-sodic to sodic soils.
III. SODIC SOIL :
Sodic soils are low in soluble salts but
relatively high in exchangeable sodium. Sodic soils are unsuitable for many
plants because of their high sodium concentration, which may cause plant
rooting problems, and because of their high pH, which generally ranges from 8.5
to 12.0.
These high sodium levels disrupt both the
chemical and physical composition of soil clays. As a result, the soil surface
has low permeability to air, rain and irrigation water. The soil is sticky when
wet but forms hard clods and crusts upon drying. This phenomenon may not occur
in very sandy soils because they lack clay content.
o
MEASURES TAKEN FOR
ANTI-SALINIZATION :
If steps are taken early, to correct the soil it will
be easier and less expensive, and it will have less negative impact on soils
and plants.
§
SELECTION OF CROPS
SUITING THE CONDITION :
Ø
SOIL TYPE-
water
infiltration capacity, how much air does the soil contain ,how much water will
be needed to wash the soil in order to avoid salinity build up should be known.
It is better avoid planting a salt sensitive crop in a soil which is not well
drained.
Ø
THE MICROCLIMATE CONDITIONS IN THE FIELD - parameters such as wind
direction and solar radiation should be measured because they may affect water
consumption of the crop.
Ø
TYPE OF IRRIGATION SYSTEM & ITS DISTRIBUTION - Each type of irrigation system
has its own water distribution pattern, depending also on the soil properties.
Make sure the emitters are set in the appropriate spacing, to allow uniform
irrigation depending on your soil type.
§
USE OF APPROPRAITE
FERTILIZER :
The fertilizers type and their quantities
should coincide with to the requirements of the crop and with nutrients which
are already in the soil. There are fertilizers which contain salts which are
not taken up by plants in large amounts, such as chlorides. These salts tend to
accumulate in the soil.
§
INTERVALS BETWEEN
IRRIGATION :
Irrigation regimen and intervals must be appropriate
to the soil conditions and to growth stage of the crop. Frequent and shallow
(superficial) applications result in salt accumulation in the root zone, while
larger applications, in longer intervals, will flush the salts below the root
zone.
§
PERIODIC TESTS OF
SOIL :
A
practical approach in order to prevent salinity buildup early enough is
sampling the soil 5 times over a growing period of 8 months (a test every 6
weeks or so). It is recommended to do at least one water analysis as well. The
tests will indicate any change in soil content, allowing you to adjust the
fertilization and irrigation regimen as needed.
o
MEASURES TAKEN FOR
DE-SALINIZATION :
Salt-affected soils can be corrected by:
§ Improving drainage
§ Reducing evaporation
§ Leaching
§ Application of chemical treatments
§ A combination of these methods
§ REDUCING EVAPORATION
:
Applying residue or mulch to the soil can
help lower evaporation rates
§
IMPROVING DRAINAGE :
In soils with poor drainage, deep tillage
can be used to break up the soil surface as well as claypans and hardpans,
which are layers of clay or other hard soils that restrict the downward flow of
water. Tilling helps the water move downward through the soil.
While deep tillage will help temporarily,
the parts of the soil not permanently broken up may reseal.
§
LEACHING :
Leaching can be used to reduce the salts in
soils. Enough low-salt water should be added to the soil surface to dissolve
the salts and move them below the root zone. The water must be relatively free
of salts (1,500 - 2,000 ppm total salts), particularly sodium salts. A water
test can determine the level of salts in your water.
Leaching works well on saline soils that
have good structure and internal drainage. Highly saline soils should be
leached using several applications, so that the water can drain well.
§
CHEMICAL TREATMENTS
:
Before leaching saline-sodic and sodic
soils, it must first treated with chemicals, to reduce the exchangeable sodium
content. To remove or exchange with the sodium, add calcium in a soluble form
such as gypsum. The laboratory analysis can determine how much calcium to add.
After the calcium treatment, the sodium can
then be leached through the soil along with the other soluble salts. Gypsum is
the most common amendment used to correct saline-sodic or sodic soils that have
no calcium source such as gypsum or free carbonates.