North Dakota State University www.ag.ndsu.edu Crops Family-Youth-4-H Economics-Community-Leadership Home-Lawn-Garden-Trees Environment-Natural Resources Livestock Nutrition-Food Safety-Health
 


Managing Saline Soils in North Dakota (continued)

Click here for an Adobe Acrobat pdf version suitable for printing. (256 Kb)


Saline Soil Management (continued)

Lower the water table and lower salinity risks

The key to managing saline soils is to control the flow of saline water into the crop root zone. When the source of saline water is a shallow water table, the management tool is to lower the water table. Since drainage is not a common option in North Dakota, the solution is to continuously crop, using late-maturing, deep-rooted crops in the rotation.

A crucial element in successful salt reduction in a continuously cropped system is to eliminate bare or black summer fallow. Water use efficiency of fallow ranged from only 0 to 18 percent of rainfall during a five-year study. The researchers found that some water evaporated, but some contributed to ground-water below four feet in depth. If the soil profile is dry enough, however, the loss to groundwater is minimal and certain soils would retain more infiltrated water in the upper four feet in the spring.

The study found that fallowing in a loam-textured soil when soil moisture before planting was less than four inches in the top four feet did not contribute excess water to groundwater. Soil moisture levels of four inches of available water in the upper four feet in a loam soil is about 50 percent of field capacity. Extending this principle to a sandy loam would not be appropriate, since the maximum water holding capacity of coarser soils are often not much more than four inches, so significant rainfall is rapidly moved to deeper depths.

It would be rare to have soil moisture levels low enough in the spring that fallow would not result in seasonal losses of added precipitation to groundwater. When spring moisture levels are sufficient for crop production, the chances of salts reaching the rooting zone are very high and fallow should not be used.

A late-maturing, deep-rooted crop with salt tolerance would be a good choice to help lower the water table. Deep-rooted, salt-tolerant crops can utilize saline groundwater. Figure 7 shows that crops can root deep to utilize saline groundwater, depending on the soil texture.

black and white line graph of evapotranspiration.
Figure 7. Evapotranspiration supplied by a saline water table as affected by water table depth.
(Gismer and Gates, 1988).

Several studies have shown that alfalfa is an excellent choice to help lower the water table. Alfalfa should be used as a part of a rotation or as a permanent water barrier when it is necessary to control the flow of salt water from one soil to another. Along ditches, potholes and intermittent streams, a 30-foot strip of alfalfa will use enough water that salts are kept from approaching the surface (Figure 2b). In situations where the water table is too high, alfalfa will lower it better than any other crop. In recharge areas, alfalfa can use a large amount of water before it has a chance to discharge farther down slope.

Other possible rotational crops are sunflower and safflower. However, they are not as good as alfalfa in using water because of their annual growth habit. Sweet clover would be an excellent green manure crop which would help on fallow by lowering the water table and supplying nitrogen for the next crop. Water use by sweet clover is often great enough to reduce yields the following season. Proper management will reduce this risk. If green manures are used, shallow tillage instead of plowing is recommended, so that salts are not returned to the surface.

There may be years when, despite the best water table management, excessive rainfall could raise the water table close to the surface. However, the chances of this event would be greatly reduced if the water table was lower initially. Lowering the water table should be viewed as a long-term management tool, and not a quick nor permanent renovation technique.

Late-maturing crops with deep rooting properties are important for saline soil management for the following reasons:

  1. Late-maturing crops provide a mulching soil cover until frost, reducing the potential for late summer and early fall surface evaporation.
  2. Deep-rooted crops leave the soil drier at deeper depths going into the winter, increasing the potential for salts to leach away from the soil surface.
  3. Deep-rooted crops can use more water at the capillary water boundary, preventing further upward movement.

In a recharge area, which is the source of the water that carries salts to a discharge site, a perennial, deep-rooted crop is best at limiting discharge. The next choice is a deep-rooted, long season annual. The third choice is any annual crop.

The following crops are ranked by their potential contribution to limiting salt water discharge from a recharge area: alfalfa>sweet clover>sunflower, safflower, sugarbeet>barley, wheat, soybean, durum wheat and canola.

A crop rotation could be designed so that a combination of perennial and annual crops could be used to diversify the system to meet goals of improved soil quality and profitability. The most important point, no matter what cropping system is used, is to continuously crop the recharge area with something green for as long a period as possible.

In the discharge area, a salt-tolerant crop will be the only crop which can be grown. A list of crops and general crop tolerances are given in Tables 3-5. These lists are very general. There may be situations when the most salt-tolerant crops do not perform well in these areas. There may be other situations in which sensitive crops do quite well. There will also be differences between varieties of the same crop. Information concerning the salt tolerance of specific varieties should be obtained from a commercial seed source before making a selection. It will also be important to note Table 1, which shows that there are differences in the ability of crops to tolerate salt at germination and later on. Sugarbeet, once established, is one of the most salt-tolerant crops available, but it is very sensitive to salt levels at germination.



Managing Sodic Soils

Many saline soils in North Dakota also have elevated levels of sodium. High levels of sodium restrict water-holding capacity in two ways. First, sodium prevents soil clay particles from gathering together into small aggregates. This process of gathering together is called flocculation. Flocculation allows water to penetrate between the groups of soil particles and provide moisture at deeper depths. When sodium levels are high enough to prevent flocculation, the individual clay particles overlap each other randomly during wet conditions, preventing water penetration through the high sodium layer.

Secondly, when the soil dries out, areas within high sodium soils form hard massive structures which look like round-topped columns. These columns do not allow roots to penetrate, so the only water and nutrients which are available to plant roots come from the small surface area surrounding these structures. The plants are therefore allowed only a small percentage of the total possible volume of soil in which to grow.

Areas of high sodium in glacial till soils can be suspected when soil pH is greater than 8.4. However, many high sodium soils in southwest North Dakota have pH values less than 6 and may tend to be even more acidic in parts of some fields. Suspicions of sodium affected soils can be confirmed by requesting a sodium soil test, along with calcium and magnesium. The concentrations of all three elements can be used to calculate the SAR (sodium absorption ratio) or the ESP (exchangeable sodium percentage), which indicates the level of sodicity present. Most laboratories equipped to analyze for potassium are also equipped to analyze for sodium.

The spread of high sodium areas can be checked by following the same management plan as for any salt problem. Decreasing the level of sodium may be much more difficult, however. Because of the restriction of water movement within the soil, leaching is more difficult.

Use of gypsum as a sodium remediation amendment

If high levels of gypsum are present in the soils with high sodium, addition of gypsum will not help replace sodium in the soil. In these soils, deep tillage may help to mix the gypsum already present in the soil with the sodium bearing soil horizons. If the soils do not already contain gypsum, addition of gypsum will replace sodium with calcium in the profile. Amounts of gypsum required to amend the upper foot of soil may be four-eight tons/acre. The material needs to be mixed into the layer of soil which needs the amendment. In order for the application to work, sulfate should not be the dominant ion in the soil. If sulfate levels are low, or other anions such as chloride are proportionally high, then gypsum amendments will be able to dissolve and replace sodium ions. For the application to be successful, it is important that good drainage be present. Drainage can be either natural or tile. Water is also needed to flush the sodium out of the soil once the application is made. Without good drainage, any amendment will not work as needed.

In soils with high sulfate levels and relatively low levels of chloride, calcium chloride will perform an even faster remediation than gypsum at about 85 percent of the gypsum rate. Calcium chloride is more soluble than gypsum, therefore it needs less water to become active.



Summary of Saline Soil Management Tools

  1. Soil test for salinity levels and the extent of the problem in each field.
  2. Select the right crop and variety for the situation.
  3. Use shallow tillage.
  4. Schedule seeding in saline areas when salt levels are lowest, from snowmelt or spring rains.
  5. Do not fallow if available water in the top four feet of soil is sufficient to grow a minimal crop, or if the soil texture is sandy loam or coarser.
  6. Use long growing season, deep rooted crops to control the water table depth.

Summary of Sodic Soil Management Tools

  1. Soil test of sodium, have the laboratory determine the sodium index (SAR or ESP).
  2. Determine if gypsum is present at deeper soil layers, and if so, deep tillage may be helpful.
  3. Improve drainage within the site.
  4. If sulfates are low, gypsum applications from four-eight tons per acre combined with adequate soil mixing and drainage would improve the soil.
  5. If sulfates are high, calcium chloride, at rates about 85 percent of gypsum requirement, combined with adequate soil mixing and drainage would improve the soil.
  6. If amendments and drainage are cost-prohibitive, growing more drought tolerant crops, more timely tillage to avoid making clods and attention to inputs would improve profitability. If areas of sodium are extensive, the field may be better off in pasture, with drought tolerant, sodium/salt tolerant grasses.



References

Asana, R.D., and V.R. Kale. 1965. A study of salt tolerance of four varieties of wheat. Indian Journal of Plant Physiology. 8:5-22.

Bauer, A. and T. J. Conlon. 1978. Influence of tillage interval of fallow on soil water storage. N. Dak. Farm Res. Bull. 35(4):8-11.

Bernstein, L., and A.D. Ayers. 1949. Salt tolerance of cabbage and broccoli. Rep. to collaborators. US Salinity Lab., Riverside, CA.

Bernstein, L., and G. Ogata. 1966. Effects of salinity on nodulation, nitrogen fixation, and growth of soybeans and alfalfa. Agronomy Journal 58:201-203.

Bernstein, L., A.D. Ayers, and C.H. Wadleigh. 1951. The salt tolerance of white rose potatoes. American Society of Hort. Science. 57:231-236.

Bernstein, L., and R. Ford. 1958. Salt tolerance of forage crops. Rep. to collaborators. US Salinity Lab., Riverside, CA.

Bernstein, L., and L.E. Francois. 1973. Leaching requirements studies: Sensitivity of alfalfa to salinity of irrigation and drainage waters. Proc. Soil Science Society of America. 37:931-943.

Bierhuizen, J.F., and C. Ploegman. 1967. Zouttolerantie van tomaten. Mededelingen van de Directie Tuinbouvw. 30:302-310.

Black, A. L., P. L. Brown, A. D. Halverson and F. H. Siddoway. 1981. Dryland cropping strategies for efficient water use to control saline seeps in the Northern Great Plains. Agr. Water Mgt. 4:295-311.

Bower, C.A., C.D. Moodie, P. Orth, and F.B. Gschwend. 1954. Correlation of sugar beet yields with chemical properties of a saline-alkali soil. Soil Science 77:443:451.

Bower, C.A., G. Ogata, and J.M. Tucker. 1970. Growth of sudan and tall fescue grasses as influenced by irrigation water salinity and leaching fraction. Agronomy Journal 62:793-794.

Brown, J.W., and L. Bernstein. 1953. Salt tolerance of grasses. Effects of variations in concentrations of sodium, calcium, sulfate, and chloride. Rep. to Collaborators. US Salinity Lab., Riverside, CA.

Brown, P.L., A.D. Halvorson, F.H. Siddoway, H.F. Mayland, and M.R. Miller. 1982. Saline-Seep diagnosis, control, and reclamation. USDA Conservation and Research Report No. 30.

Brun, L.J., and B.K. Worcester. 1975. Soil water extraction by alfalfa. Agronomy Journal 67:586-588.

Cassel, D.K., and M.D. Sweeney. 1974. In Situ soil water holding capacities of selected North Dakota soils. North Dakota Agricultural Experiment Station Bulletin No. 495.

Cerdá, A., M. Caro, and F.G. Fernández. 1982. Salt tolerance of two pea cultivars. Agronomy Journal 74:796-798.

de Forges, J.M. 1970. Research on the utilization of saline water for irrigation in Tunisia. Nature Resources 6:2-6.

Dewey, D.R. 1960. Salt tolerance of twenty-five strains of Agropyron. Agronomy Journal 52:631-635.

Doering, E. J. and F. M. Sandoval. 1976. Saline seep development on upland sites in the Northern Great Plains. ARS-NC-32.

Francois, L.E. 1984. Salinity effects on germination, growth, and yield of turnips. Journal American Society of Horticultural Science 109:332-324.

Francois, L.E. 1994. Growth, seed yield, and oil content of canola grown under saline conditions. Agronomy Journal 86:233-237.

Francois, L.E. 1996. Salinity effects on four sunflower hybrids. Agronomy Journal 88:215-219.

Francois, L.E. and L. Bernstein. 1964. Salt tolerance of Sphaerophysa salsula. Rep. Collaborators. US Salinity Lab., Riverside, CA.

Francois, L.E., and R. Kleiman. 1990. Salinity effects on vegetative growth, seed yield, and fatty acid composition of crambe. Agronomy Journal 82:1110-1114.

Francois, L.E., T.J. Donovan, and E.V. Maas. 1984. Salinity effects on seed yield, growth, and germination of grain sorghum. Agronomy Journal 76:741-744.

Francois, L.E., E.V. Maas, T.J. Donovan, and V.L. Young. 1986. Effect of salinity on grain yield, quality, vegetative growth and germination of semi-dwarf and durum wheat.

Francois, L.E., T.J. Donovan, K. Lorenz, and E.V. Maas. 1989. Salinity effects on rye grain yield, quality, vegetative growth, and emergence. Agronomy Journal. 81:707-712.

Franzen, D.W. and J.L. Richardson. 2000. Soil factors affecting iron chlorosis of soybean in the Red River Valley of North Dakota and Minnesota. Journal of Plant Nutrition. 23:67-78.

Gismer, M. E. and T. K. Gates. 1988. Estimating saline water table contributions to crop water use. California Agriculture 42(2):23-24.

Graifenberg, A., L. Botrini, L. Guistiniani, and M. Lipucci di Paola. 1996. Yield, growth, and elemental content of zucchini squash grown under saline-sodic conditions. Journal of Horticultural Science 71:305-311.

Grieg, J.K., and F.W. Smith. 1962. Salinity effects on sweetpotato growth. Agronomy Journal 54:309-313.

Hassan, N.A.K., J.V. Drew, D. Knudsen, and R.A. Olson. 1970a. Influence of soil salinity on production of dry matter and uptake and distribution of nutrients in barley and corn: I. Barley (Hordeum vulgare). Agronomy Journal 62:43-45.

Hassan, N.A.K., J.V. Drew, D. Knudsen, and R.A. Olson. 1970b. Influence of soil salinity on production of dry matter and uptake and distribution of nutrients in barley and corn: II. Corn (Zea mays). Agronomy Journal 62:46-48.

Hayward, H.E., and W.B. Spurr. 1944. The tolerance of flax to saline conditions: Effect of sodium chloride, calcium chloride, and sodium sulfate. Journal of the American Society of Agronomy. 36:287-300.

Hoffman, G.J., and S.L. Rawlins. 1971. Growth and water potential of root crops as influenced by salinity and relative humidity. Agronomy Journal 63:877-880.

Hogg, T. J. and T. L. Henry. 1984. Comparison of 1:1 and 1:2 suspensions and extracts with the saturation extract in estimating salinity in Saskatchewan soils. Canadian Journal of Soil Science 64:669-704.

Holm, H. M. 1979. Saskatchewan soil salinity progress report #3 Saskatchewan Agriculture.

Johnsgard, G. A. 1974. Salt affected problem soils in North Dakota. 3rd printing. N. Dak. St. Univ. Ext. Serv. Bull. #2.

Knuteson, J.A., J.L. Richardson, D.D. Patterson, and L. Prunty. Pedogenic carbonates in a calciaquoll associated with a recharge wetland. Soil Science Society of America Journal 53:495-499.

Maas, E. V. 1986. Salt tolerance of plants. Applied Agr. Res. 1:12-26.

Maas, E.V. and S.R. Grattan. 1999. Crop yields as affected by salinity. p. 55-110. In Agricultural Drainage, R.W.Skaggs and J. Van Schilfgaarde, eds. Agronomy Monograph 38. ASA-CSSA-SSSA, Madison, WI.

Manchanda, H.R., and S.K. Sharma. 1989. Tolerance of chloride and sulphate salinity in chickpea (Cicer arietinum). Journal of Agricultural Science. 113:407-410.

McElgunn, J.D., and T. Lawrence. 1973. Salinity tolerance of Altai wild ryegrass and other forage grasses. Canadian Jounral of Plant Science 53:303-307.

Osawa, T. 1965. Studies on the salt tolerance of vegetable crops with special reference to mineral nutrition. Bull. Univ. Osaka Prefect., Ser. B (Osaka) 16:13-57.

Ploegman, C., J.F. Bierhuizen. 1970. Zouttolerantie van Komkommer. Bedrifsontwikkeling:Editie Tuinbouvw 1:32-39.

Seelig, B. D. and J. L. Richardson. 1991. Salinity and sodicity in North Dakota soils. North Dakota State Univ. Extension Service Bulletin 57.

Shannon, M.C., and L.E. Francois. 1978. Salt tolerance of three muskmelon cultivars. Journal of American Society of Horticultural Science 103:127-130.

Sommerfeldt, T. G. and E. Rapp. 1982. Management of saline soils. Communications Branch, Agric. Canada, Pub. 1624E.

Steppuhn, H., D. Curtin and F. Selles. 1991. The role of salt tolerant crops in sustainable irrigated agriculture. In: Proceedings of IRDC-90. Water Res. Inst. Univ. of Lethbridge, Alb. Canada.

US Salinity Lab, 1954. Diagnosis and improvement of saline and alkali soils. L.A. Richards, ed. Agriculture Handbook No. 60. USDA.

 

Contents | BACK



The NDSU Extension Service does not endorse commercial products or companies even though reference may be made to tradenames, trademarks or service names.

This publication may be copied for noncommercial, educational purposes in its entirety with no changes. Requests to use any portion of the document (including text, graphics or photos) should be sent to permission@ndsuext.nodak.edu. Include exactly what is requested for use and how it will be used.

For more information on this and other topics, see: www.ag.ndsu.edu


SF-1087 (revised), March 2007


 


County Commissions, North Dakota State University and U.S. Department of Agriculture cooperating. North Dakota State University does not discriminate on the basis of race, color, national origin, religion, sex, disability, age, Vietnam Era Veterans status, sexual orientation, marital status, or public assistance status. Direct inquiries to the Executive Director and Chief Diversity Officer, 202 Old Main, (701) 231-7708. This publication will be made available in alternative formats for people with disabilities upon request, 701 231-7881.