Rectify Soil Conditions with Tiger 90CR® Sulphur
Wesley Haun, Senior Agronomist, Tiger-Sul Products
The world population continues to increase and demand for continuous quality food supply increases. Several factors have contributed to significant increases in crop production, which includes improved hybrids/varieties, technology, and plant nutrient management. Maximizing crop yield potential on each acre/hectare requires attention to details. The scope of this discussion will focus on soil conditions and adding amendments to enhance plant nutrient availability. Soil amendments are materials added to soil to improve its characteristics that are more conducive to root growth and enhance nutrient uptake. Soil conditions that are predominant in western North America but occur to lesser extent in other areas include alkaline, saline, sodic, and saline/sodic soils (Table 1.0).
Table 1.0: Classification of salt affected soils
Classification | Electrical Conductivity (mmho/cm) | Soil pH | Sodium Adsorption Ratio (SAR)1 | Soil Physical Condition |
Slightly Saline | 2 – 4 | < 8.5 | < 13 | Normal |
Saline | > 4.0 | < 8.5 | < 13 | Normal |
Sodic | < 4.0 | > 8.5 | > 13 | Poor |
Saline – Sodic | > 4.0 | < 8.5 | > 13 | Varies |
Alkaline – High pH | < 4.0 | > 7.8 | < 13 | Varies |
1 If reported as exchangeable sodium percentage (ESP), use 15% as threshold value.
Source: R. M. Waskom & et. al. 2012. Diagnosing Saline and Sodic Soil Problems.
Fact Sheet 521 Colorado State University Extension.
Each of these soil conditions has Table 2.0 Diagnosing high pH, saline, or sodic soil problems specific causes and symptoms that result in adverse effects to plant growth (Table 2.0). Oftentimes, these soil conditions are confused, so a correct diagnosis is critical to a successful outcome. The best diagnostic tool to confirm a specific soil problem is a soil sample analysis.
Table 2.0: Diagnosing high pH, saline, or sodic soil problems
Problem | Potential Symptoms |
Alkaline — High pH | Nutrient deficiencies manifested as stunted, yellow plants, Dark green – purplish plants |
Saline soil | White crust on soil surface, water stressed plants, leaf tip burn |
Saline irrigation water | Leaf burn, poor growth, moisture stress |
Sodic soil | Poor drainage, black powdery residue on soil surface |
Saline-sodic soil | Generally, same symptoms as saline soil |
Source: R. M. Waskom & et. al. 2012. Diagnosing Saline and Sodic Soil Problems.
Fact Sheet 521 Colorado State University Extension.
ALKALINE SOILS
Frequently, nutrient deficiency symptoms are displayed by crops grown in soils with a pH greater than 7.8. Availability of most essential nutrients is limited as soil pH increases above 7.8. Plant nutrient deficiencies under these conditions can be managed temporarily by foliar nutrient application and for a longer term by reducing soil pH. Soil pH may be lowered with application of elemental sulphur (TIGER 90CR). Application rate is a function of soil texture (Table 3.0).
Table 3.0: Elemental sulphur required to decrease soil pH to a depth of 6 inches.
Application rate based on soil texture1 | |||
Desired change in pH | Sand | Silt Loam | Clay |
8.5 to 6.5 | 370 lbs. S/Ac | 730 lbs. S/Ac | 1460 lbs. S/Ac |
8.0 to 6.5 | 340 lbs. S/Ac | 670 lbs. S/Ac | 1340 lbs. S/Ac |
7.5 to 6.5 | 300 lbs. S/Ac | 600 lbs. S/Ac | 1200 lbs. S/Ac |
7.0 to 6.5 | 180 lbs. S/Ac | 360 lbs. S/Ac | 720 lbs. S/Ac |
8.5 to 5.5 | 830 lbs. S/Ac | 1669 lbs. S/Ac | 3310 lbs. S/Ac |
8.0 to 5.5 | 800 lbs. S/Ac | 1600 lbs. S/Ac | 3190 lbs. S/Ac |
7.5 to 5.5 | 760 lbs. S/Ac | 1530 lbs. S/Ac | 3050 lbs. S/Ac |
7.0 to 5.5 | 640 lbs. S/Ac | 1290 lbs. S/Ac | 2580 lbs. S/Ac |
1 Assumptions – cation exchange capacity of the sandy, silt loam, and clay soils are 5, 10, and 15 meq/100 g, repectively; soils are not calcareous.
Source: Robert Mullen & et.al. 2012. Soil Acidification: How to Lower Soil pH.
Fact Sheet AGF-507-07. Ohio State University Extension.
When TIGER 90CR sulphur is soil applied and goes through an oxidation process, sulphuric acid and H+ ions are released, soil is acidified, and pH is lowered. Since sulphur oxidation is a biological process, this activity will vary among soil types. Table 3.0 should be utilized as a starting point as individual situations are unique and may require more or less than the values provided. Collect soil samples one year after sulphur application to evaluate progress in adjusting soil pH.
SALINE SOILS
Saline soils contain excess soluble salts, which interfere with the plants ability to absorb water and nutrients. Most crops are more sensitive to salt injury during germination and seedling growth stages. The source of salts is a function of soil parent material, soil drainage, and weather conditions over time. These salts tend to accumulate in soil as water evaporates, especially in arid areas. Oftentimes, excess salts will crystallize on soil surface leaving a white residue.
Determination of soluble salts present is done by measuring the electrical conductivity (EC) of soil solution from a saturated soil sample. The units of measurement are “mmhos/cm”. The salt content is proportional to the EC of the soil solution. A general guideline for evaluating soil test results is provided in Table 4.0.
Table 4.0: Interpretation of Electrical Conductivity (EC)
EC (mmhos/cm) | Salt Rank | Interpretation |
0-2 | Low | Very little chance of plant injury |
2-4 | Moderate | Sensitive plants and seedlings of others may show injury |
4-8 | High | Most non-salt tolerant plants will show injury |
8-16 | Excessive | Salt tolerant plants will grow, most others severe injury |
16+ | Very Excessive | Very few plants will tolerate and grow |
Source: R.E. Lamond and D.A. Whitney. Kansas State University. Fact Sheet MF 1022
Reclamation of saline soils can only be accomplished by removing the accumulated salts from the root zone. Three methods have proved successful in managing saline soils. All three methods utilize water to move the salts and they include: 1) leaching, 2) artificial drainage, and 3) managed accumulation. Leaching involves applying more water than required by crop to move salts below root zone. Artificial drainage utilizes the leaching method to move salts to sub-surface drainage tiles to carry salt and water away from the field. Managed accumulation is the movement of salts from the immediate root zone to areas such as every other row middle, field edges, etc. that reduces potential harmful effects. Sequential applications of water should be added so that sufficient time for drainage is allowed between applications. Quantity of water needed for salt removal is dependent on beginning salt level in the soil, the desired salt level, quality of irrigation water, and method of water application. Generally, expect to use approximately 8-10 (20-25 cm) inches of water to remove approximately 70% of soluble salts per 12 inches (30 cm) of soil to be leached.
SODIC SOILS
Soils that contain high sodium (Na) and low total salts are referred to as sodic soils. These soils tend to crust and are cloddy when dry. Sodium causes the soil particles to disperse and results in poor soil structure and minimizes water infiltration. A soil sample analysis for Na and soluble salts will identify the specific problem or specific problems. The extent of Na severity is expressed as sodium adsorption ratio (SAR). This ratio provides the proportion of water-soluble Na to calcium and magnesium in soil. (Table 1.0) When the soil exceeds a Na SAR of 13, options for removing the Na need to be evaluated. Oftentimes, switching to a more tolerant crop is not an option, and the soil must be altered to create a more favorable environment for plant growth.
Sodic soils can be reclaimed by applying an amendment that will result in the displacement of Na from the soil cation exchange complex and replaced with calcium (Ca). When Na has been displaced, it can be leached out of the rooting zone with rainfall and/or irrigation. TIGER 90CR sulphur can be an effective amendment to displace Na if the soil has greater than 1% free lime (calcium carbonate, CaCO3). The sulphur is converted to sulphuric acid through microbial oxidation. The Sulphuric acid then reacts with lime (CaCO3) in the soil to form calcium sulphate (gypsum, CaSO4). Then the CaSO4 will dissolve in soil water and the Ca will react to displace the Na. TIGER 90CR has a high efficiency ratio due to its 90% sulphur concentration and clay content that enhances the soil reaction. As shown in Table 5.0, Tiger 90CR sulphur requires 75% less material to provide an equal amount of Ca to displace Na from the soil exchange complex. Should a sodic soil not contain free CaCO3, then CaSO4 would be the product of choice to supply Ca to displace the Na and move it out of the rooting zone by leaching. Reclaiming a sodic soil can be a slow process as soil structure damage is slow to improve.
Table 5.0: Soil amendments required to supply 1 lb. of soluble calcium:
Amendment | Purity % | Pounds |
Sulphur | 99.5% | 0.8 |
Tiger 90CR Sulphur | 90% | 1.1 |
Sulphuric acid | 95% | 2.6 |
Calcium Chloride | 100% | 3.7 |
Gypsum | 100% | 4.3 |
Source: Adapted from J.G. Davis & et.al. 2012. Managing Sodic Soils. Fact Sheet 504. Colorado State University Extension.
SALINE-SODIC SOILS
These soils contain high levels of soluble salts and high exchangeable sodium content (> 13 SAR). The physical properties of these soils reflect saline characteristics. To improve these soils, amendments and drainage are essential. Adding sufficient water to leach a saline-sodic soil without amendments will result in a sodic soil and may worsen the soil structure. Therefore, leaching of soluble salts must be followed by or preceded by the displacement of exchangeable Na with Ca.
Summary:
Benefits to employing TIGER 90CR sulphur as a soil amendment are as follows:
1) Removes sodium
2) Forms CaSO4
3) Faster water infiltration
4) Improved soil aeration
5) Release of phosphate and micronutrients
6) Most beneficial in alkaline or sodic situations
Soil characteristics vary from field to field and farm to farm; therefore, they require management adjustments. All soils should be evaluated individually with respect to the management needed to minimize yield limiting factors. Future yields are dependent upon current production practices to conserve and improve soil productivity.
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