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3.4: Cation Exchange Capacity

  • Page ID
    34622
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    CEC

    This stands for Cation Exchange Capacity. Cation is pronounced CAT-EYE-0N. A cation is a positively charged element. We are specifically interested in cation elements that are plant nutrients: Calcium (Ca++), Potassium (K+), and Magnesium (Mg ++).

    Exchange Capacity tells us how many spaces or sites there are in soil where exchanges can take place. Soil with a high CEC has a lot of exchange sites while soil with a low CEC does not have much capacity or ability to exchange cations.

    CEC is a measurement that tells us whether or not a particular soil has few or many sites or spaces that can exchange, catch, hold, and release nutrients. The CEC tells us if the cations can readily exchange places with hydrogen ions and become available for absorption by the plant. A soil with high CEC is potentially quite good soil for growing crops compared to a soil with low CEC This value cannot be readily changed; it is a function of the soil’s parent material and texture.

    A soil’s CEC can be compared to a bank. A large bank has a lot of money available for exchange. Some is in the vault, locked away, and some is in circulation. Similarly, soils with C.E.C’s measuring 20 (milliequivalents/100grams) have a larger reserve of cation sites (or vault space) than soils with a CEC of 10 meq/100g. The units of measure are a bit too complex to go into here, but it can be said that high CEC soils can hold perhaps thousands of pounds of cation nutrients per acre at any given time.

    The CEC depends on the soil’s physical properties (its texture) and on the amount of organic matter present. As discussed previously, soils with fine textures like clay have a lot of surface area compared to sandy soils. They have a large “vault”. Clays hold nutrients better than sandy soils. Sandy soils need to be fertilized more often because any free cations not taken up by the plant are readily leached, or washed, out of the soil by rainfall. Nitrates are positively charged nitrogen molecules that cause problems on sandy soils, leaching through them and into rural well water, for example.

    sand silt clay

    Sometimes clay soils hold the nutrient ions too tightly, they do not let enough cations out of the vault and out into circulation. When this happens there may be plenty of calcium for example in the soil bank, but not enough in circulation to feed the plant. This is where pH comes into the picture and, as we’ll read in the next section, % Base Saturation.  When pH is slightly acidic, plenty of H+ ions are available to bump cations off clay sites and they are put into soil-water solution and thus become available to the plant.

    All things being equal, sandy soils typically have C.E.C s of less than 5 meq/100g, and heavy clays have CEC s over 20. Silt loams have more desirable CECs in between.

    Sand

    Silt Loam (meq/100g)

    Heavy Clay

    <5

    In between

    >20

    Caption Exchange Capacity Management

    The CEC in soils is due to well-humified (“very dead”) organic matter and clay minerals. The total CEC in the soil is the sum of the CEC due to organic matter and due to clays. In fine-textured soils with medium- to high-CEC clays, much of the CEC may be due to clays. Conversely, in sandy loams with little clay, or in some of the soils of the southeastern United States and of the tropics that contain clays with low CEC, organic matter may account for an overwhelming fraction of the total CEC. There are two practical ways to increase the ability of soils to hold nutrient cations such as potassium, calcium, magnesium, and ammonium:

    • Add organic matter by using the methods discussed in other chapters.
    • If the soil is too acidic, use lime (see “pH Management”) to raise its pH to the high end of the range needed for the crops you grow.

    One of the benefits of liming acid soils is increasing soil CEC. As the pH increases, so does the CEC of organic matter as well as some clay minerals. As hydrogen (H+) on humus is neutralized by liming, the site where it was attached now has a negative charge and can hold Ca++, Mg++, K+, etc.

    Many soil testing labs will run CEC if asked. However, there are a number of possible ways to do the test. Some labs determine what the CEC would be if the soil’s pH was 7 or higher. They do this by adding the acidity that would be neutralized if the soil was limed to the current soil CEC. This is the CEC the soil would have at the higher pH but is not the soil’s current CEC. For this reason, some labs total the major cations actually held on the CEC (Ca++ + K+ + Mg++) and call it effective CEC. It is more useful to know the effective CEC—the actual current CEC of the soil—than the CEC determined at a higher pH.

    Estimating Organic Matter's Contribution To A Soil's CEC

    The CEC of soil is usually expressed in terms of the number of milliequivalents (me) of negative charge per 100 grams of soil. (The actual number of charges represented by one me is about 6 followed by 20 zeros.) A useful rule of thumb for estimating the CEC due to organic matter is as follows: for every pH unit above pH 4.5, there is 1 me of CEC in 100 grams of soil for every percent of organic matter. (Don’t forget that there will also be CEC due to clays.) SOM = soil organic matter.

    Example 1: pH = 5 and 3% SOM → (5 – 4.5) x 3 = 1.5 me/100g

    Example 2: pH = 6 and 3% SOM → (6 – 4.5) x 3 = 4.5 me/100g

    Example 3: pH = 7 and 3% SOM → (7 – 4.5) x 3 = 7.5 me/100g Example 4: pH = 7 and 4% SOM → (7 – 4.5) x 4 = 10 me/100g

    Soil Acidity

    Background

    • pH 7 is neutral.
    • Soils with pH levels above 7 are alkaline; those of less than 7 are acidic.
    • The lower the pH, the more acidic is the soil.
    • Soils in humid regions tend to be acidic; those in semiarid and arid regions tend to be around neutral or alkaline.
    • Acidification is a natural process.
    • Most commercial nitrogen fertilizers are acid-forming, but many manures are not.
    • Crops have different pH needs, probably related to nutrient availability or susceptibility to aluminum toxicity at low pH.
    • Organic acids on humus and aluminum on the CEC account for most of the acid in soils.

    Management

    • Test soils regularly, every other year if possible, to track soil acidity changes and to make timely adjustments if needed.
    • Use limestone to raise the soil pH. (If magnesium is also low, use dolomitic lime, which contains magnesium in addition to calcium.)
    • Mix lime thoroughly into the plow layer.
    • Spread lime well in advance of planting sensitive crops, if at all possible.
    • If the lime requirement is high—some labs say greater than 2 tons, others say greater than 4 tons—consider splitting the application over two years.
    • Reducing soil pH (making soil more acid) for acid-loving crops is best done using elemental sulfur (S).

    This page titled 3.4: Cation Exchange Capacity is shared under a CC BY-NC 4.0 license and was authored, remixed, and/or curated by Valerie Dantoin (Northeast Wisconsin Technical College) via source content that was edited to the style and standards of the LibreTexts platform.