Reclamation of salt-affected soils

In the arid regions of the world, and along coastal areas subject to periodic inundation by sea water, soils may have such a high content of soluble salts that production of economic plants is not possible. The salts found in soils are generally the chlorides, carbonates, bicarbonates, and sulfates of sodium, with lesser amounts of potassium, magnesium, and calcium salts.

Normally, the salt is carried into the soil by water, either by upward moving saline groundwater or by saline irrigation or flood waters. As the water evaporates from the soil or is transpired by plants, the salt is left behind. Unless provision is made for removing it from the soil by flushing with nonsaline waters, the salt will accumulate until plant growth is inhibited. Thus, salts tend to accumulate in poorly drained soils where water does not move down through the soil profile and out in the drainage water and in soils of arid areas where the annual addition of nonsaline water to the surface soil in the form of rain is insufficient to wash the salts downward. Since all irrigation waters carry at least some salt, irrigation may hasten the process of salt accumulation in soils, and reclamation of arid lands by irrigation may be followed by a need for reclamation of salty lands by drainage and leaching.

The salt in soils dissolves in the soil water and damages plant growth by preventing the plants from getting needed water from the soil, since the energy required to remove a given quantity of water from a salt solution increases as the salt concentration of the solution increases. In some cases, the dissolved salts may be toxic to plants when taken up by the roots. In addition to their detrimental effects on plants, sodium ions from the dissolved salt may become adsorbed by the clay particles of the soil and render the soil very sticky when wet and hard and cloddy when dry. Soils containing significant amounts of adsorbed sodium are nearly impervious to water and roots. These detrimental accumulations of sodium are formed through a process called cation exchange.

Most productive soils have calcium cations adsorbed on the surfaces of the clay particles. But when such a soil is treated with a salt solution high in sodium and low in calcium, sodium cations from the salt solution replace the calcium cations held by the soil, and a so-called “sodic soil” results. These cations of sodium remain adsorbed by the soil after the salt solution is drained away. Whenever sodium cations are in excess of about 10 percent of the total amount of cations held in adsorbed form by the soil, a sodic soil of undesirable physical properties results. The Food and Agriculture Organization (FAO) uses the term solonetz (from the Russian sol etz “strongly salty”) to describe sodic soils.

The reclamation of salt-affected soils follows the exact reverse of the process by which they are formed. The first step is to improve the drainage so that upward movement of ground water to the soil surface ceases and water applied to the surface can move down through the soil profile. Then fresh nonsaline water is applied to the surface by irrigation. This fresh water washes out the excess salts, which are carried away in the drainage water. In the case of sodic soils, amendments that will supply a fresh source of soluble calcium to replace the sodium adsorbed by the soil are added. and leaching is carried out until the replaced sodium is removed. Gypsum (calcium sulfate) is the most common amendment used to supply calcium for the reclamation of sodic soils.

Procedures for the diagnosis and reclamation of salt-affected soils are generally used for planning this type of reclamation activity throughout the world. Saline and sodic soils are found in extensive areas in Russia, Pakistan, the Middle East, North Africa, Spain, and in the western United States. Deep tillage to break up the horizons high in adsorbed sodium is a common technique used for the reclamation of these soils.

Reclamation of swampy lands

Where excess water accumulates in and on the soil, the land is rendered unfit for production of many crops. Even where the wet condition is of fairly short duration, cultural operations required for crop production may be delayed past the optimum planting date or crops already planted may be drowned out. The reclamation of such wet areas is centred on means of removing the water from these areas more rapidly than it is removed in their natural condition. This process is termed drainage.

The first requirement of a drainage project is an outlet for the water. One of the most common means of providing this outlet is to dig a ditch from the swampy area to a river, sea, or other natural body of water. The size of the ditch is determined by the amount of water to be carried and the gradient of slope along the ditch. The topography of the land, the amount of water to be removed in a given time (called the drainage coefficient), and the distribution and nature of underlying strata are factors determining the design of the drainage systems for moving the water from the land to the outlet.

Of particular importance is the permeability, or ability to transmit water, of the soil and underlying strata. If the soil and underlying strata have a low permeability, a quality frequently found in clay soils, the excess water must be removed by surface flow. This may require regularly spaced small ditches throughout the area to be drained and a land forming or grading operation to provide slopes toward the field ditches and to eliminate low spots between ditches. If the soil is permeable, the excess water may be removed through tile lines installed beneath the surface of the soil. The tiles are traditionally made of fired clay or concrete, although corrugated plastic tubing is also commonly used. The spacing of the tile lines is governed by the permeability of the soil. The more permeable the soil, the farther apart the tile lines. The tile lines may be installed in a regular pattern in large wet areas or in a random pattern where critical wetness is confined to scattered spots in the area. Tile drains have the advantage over open ditch drains in that farm operations can be conducted across the tile lines, making it possible to use larger and more efficient fields, with no loss of land occupied by ditches.

Occasionally, underground drains are constructed without use of tile by drawing a bullet-shaped tool through the soil at a depth of 18–36 inches (46–91 cm). This tool leaves a channel through the subsoil that may serve the same drainage function as a tile line. The practice of forming unlined underground drains is called mole drainage. After a period of time, depending upon the stability of the soil, the unlined channels collapse and the mole drainage operation must be repeated. With the development of low-cost flexible plastic materials, devices for lining mole drains with perforated plastic liners to increase the life of the drains were developed.

If a permeable strata such as gravel underlies the area to be drained, widely spaced open ditches dug into the permeable strata usually provide effective drainage. Frequently, poorly drained swampy areas are occupied by soils very high in organic matter, called peats and mucks. When these organic soils are drained, the improved soil aeration brings about an increase in the rate of oxidation of the organic material, resulting in a loss of the soil material itself. This leads to a subsidence of the land surface, and, in some cases, the land surface may sink several feet. Subsidence of drained organic soils is more rapid in warm climates than in cooler areas. Appreciable subsidence has taken place in the reclaimed organic soils of the Everglades of Florida.

Some areas are too wet for crop production because of recurrent flooding from adjacent rivers and creeks. Reclamation of this type of wetland is usually effected by building levees along the stream to keep it confined in its channel. If necessary, excess water originating in the protected area is lifted over the levee by pumps. An extensive area of land is protected by levees in the lower Mississippi valley of the United States.

Projects for the reclamation of land by drainage are found in England, Europe, and the eastern United States. Large areas of organic soils have been reclaimed by drainage near Minsk, Belarus. Mole drainage is used in England, in New Zealand, and in Australia. Reclamation of wetland by drainage is an ancient practice, having been used by the Romans along the Tiber River.