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28/04/2021 - 00:00
Soil science is FULL of acronyms! We discuss 11 of them in detail in this blog article. From pH to pF, from CEC to HC. Nicely ordered, clearly explained and richely illustrated.
"An acronym is a pronounceable word formed from the first letter (or first few letters) of each word in a phrase or title. The newly combined letters create a new word that becomes a part of everyday language."
Soil science is FULL of acronyms! We'll discuss 11 of them, arranged in alphabetical order:
pH is a measure of the acidity or basicity (alkalinity) of a soil.
The pH scale is logarithmic and inversely symbolizes the concentration of hydrogen ions (H+) in a solution. The pH scale ranges from 1 to 14.
The table below shows you the pH of some common substances and may help you to understand the pH scale.
The soil pH is very important for plant growth:
The majority of food crops prefer a neutral or slightly acidic soil, because the solubility of most nutrients necessary for healthy plant growth is highest at pH 6.3-6.8. Some plants however prefer more acidic (e.g., potatoes, strawberries) or alkaline (brassicas) conditions.
When the pH falls drops below 5.5, most major plant-nutrient minerals (including nitrogen (N), phosphorus (P), potassium (K), sulphur (S), magnesium (Mg), and calcium (Ca)) and some micronutrients become insoluble and hence unavailable for uptake by plant roots:
Many positively charged nutrients (cations, such as zinc (Zn2+), aluminium (Al3+), iron (Fe2+), copper (Cu2+), cobalt (Co2+), and manganese (Mn2+)) are soluble and available for uptake by plants below pH 5.0, although their availability can be excessive and thus toxic in more acidic conditions. In more alkaline conditions they are less available, and symptoms of nutrient deficiency may occur.
The table below visually illustrates how soil pH affects availability of plant nutrients
The CEC or Cation Exchange Capacity is the capacity of the soil to store exchangeable cations.
In a soil, clay mineral and organic matter components have negatively charged sites on their surfaces. Also plant roots have an overall negative charge.
Just like a magnet, these negatively charged sites will attract positively charged ions (cations) by electrostatic force. Some of these cations are critical for plant growth:
In general terms, soils with a high CEC are more fertile, because they can retain more of these cations. Cations in the soil compete with one another for a spot on the cation exchange capacity. However, some cations are attracted and held more strongly than other cations.
CEC is expressed in meq/100g. Soil CEC typically increases as clay content and organic matter increases.
|The relationship between soil texture and CEC|
|Soil Texture||Typcial CEC (meq/100g soil)|
|Clay loam and clay||20-50|
The CEC of a soil can be increased by mixing soil amendments with a high CEC. For example, the CEC value of TerraCottem exceeds 150 meq/100g. This is due to the high CEC of its carrier materials and especially its superabsorbant polymers. These are crosslinked polymer chains with lots of negative charged areas inside its chemical structure:
There is a direct relation between the pH and the CEC of a soil. The CEC is lowest at soil pHs of 3.5 to 4.0 and increases as the pH is increased. Because CEC may vary considerably with soil pH, it is a common practice to measure a soil's CEC at a pH of 7.0. Remark (see figure below): at low pH, some positive charges may also occur on specific soil mineral surfaces. These may retain anions (negatively charged ions) such as chloride (Cl-) and sulphate (SO42-).
The soil cations can be divided into two groups:
The words "base" and "acid" refer to the cation’s influence on soil pH. A soil with a lot of acid cations held by soil particles will have a low pH. On the other hand, a highly alkaline soil predominately consists of base cations.
(*) Unlike ammonium, calcium, magnesium and potassium, sodium is not an essential element for all plants. Soils that contain high levels of sodium can develop salinity and sodicity problems.
NPK is short for nitrogen (N), phosphorus (P) and potassium (K). These are followed by 3 numbers, for example 20-8-5 and represent the percentage of these components in the package.
In the above example of 20-5-8, a 20kg bag of that fertiliser will contain 20% of nitrogen, 8% of phosphorus pentoxide and 5% of potassium oxide. Thus:
Two more examples:
"Up, Down, and All Around"
This is a good reminder of describing the purpose of each element:
Soil organic matter is made up of plant and animal residues in different stages of decomposition, cells of soil microorganisms, and many types of decomposed substances.
We can distinguish either "living" and "dead" organic matter:
There are four main processes in the soil organic matter cycle, and all of them rely on soil microbes:
Humus is thus the "end product" of decomposition of organic matter. It gives the soil its dark brown colour. Usually, humus represents the majority of total soil organic matter.
Humus consists of:
Compost is not humus! Compost is plant material that is slightly decomposed. Even aged, well-rotted compost is still only slightly decomposed. Once added to your garden compost will continue to decompose for several years.
This is the carbon-to-nitrogen ratio of organic matter. There is always more carbon than nitrogen in organic matter. For example, a ratio of 20:1 means that there is 20g of carbon for each 1g of nitrogen in that organic matter.
The lower the C:N ratio, the more rapidly nitrogen will be released into the soil for immediate crop use.
Most soil organic matter comes from plant tissue:
This brings us directly to the benefits of organic matter:
(*) Remark: in sports turf midst there are lots of discussions about the role of organic matter. On sand-based fields OM can rapidly accumulate around the base of the grass plants. A "thatch" layer is formed that compromises the drainage capacity. Thatch build-up can be caused by several factors, amongst which the relatively low microbiological activity in such soil profiles and over-application of nitrogen fertilisers. Adequate maintenance is needed to maintain the organic matter within the preferred ranges.
Water retention capacity (WRC) or water holding capacity (WHC) is the ability of a soil to physically hold water.
It is commonly expressed as v/v (percent of volume) either w/w (percent of weight).
WRC is primarily controlled by:
Soils with smaller particles (silt and clay) have a larger surface area than those with larger particles (sand). A larger surface area allows a soil to hold more water. Based upon the percentage of sand, silt and clay in a soil, we can distinguish 12 soil texture categories. This is visually represented in a soil texture triangle.
Example: imagine a soil sample with 65% of sand, 27% of clay and 8% of silt.
These 12 soil types have a different water holding capacity:
The relation between the volumetric water content in your soil and the water potential (i.e. the suction force applied to that water) is expressed in a water retention curve or pF - curve.
The name pF is short for "Potenz" (or "exponentiation") and "Freier energie" (or "available energy").
|A drainpipe at a depth of 100 centimetres for example, will excert a suction force of 100cm or pF2.|
Watch the following video: the sponge in the video represents the soil matrix:
As the water retention capacity primarily is controlled by soil texture (and organic matter), the shape of the pF-curve changes with soil texture. A common shape for a clay, silt and loam soil is:
The amount of Plant Available Water (PAW) in a clay soil is much higher than in a sandy soil:
|At FC, the volumetric water content in this sandy soil is +/- 8%; at WP merely 2%. This gives 8-2 = 6% PAW in a sandy soil.
In this clay soil, the volumetric water content is +/- 47%; at WP +/- 28%. This gives 47-28 = 19% PAW.
This also is the reason why a clay soil with 20% of water will feel dry and a sandy soil with 10% of sand will feel humid. The WRC of soils can be increased by adding soil amendments suited for that purpose.
The following figure gives a good overview of the PAW in relation to the 12 soil types:
Soil Electrical Conductivity (EC) is a measure of the amount of salts in soil (salinity of soil).
Soil electrical conductivity gives us an indication about the total amount of salts, not the presence of specific salts.
It is an important indicator of soil health. It has an impact on:
A too high EC will disrupt the soil water balance and hinder plant growth.
Soils with high salt contents occur naturally in arid and semiarid climates. However, salt levels can increase as a result of cropping, irrigation, land use and application of fertiliser and compost.
Soil electrical conductivity is expressed in μS/cm (or mS/cm), dS/m or ppm:
Based upon the EC value, a classification can be made for the degree of salinity:
|ECe method (dS/m) (*)|
|0 - 2||2 - 4||4 - 8||8 - 16||> 16|
|(*) There are different methods to determine the EC: ECe (on a saturated soil paste extract), EC1:1 (on a mixture of soil over water mass ratio of 1:1), EC1:5 (on a mixture of soil over water mass ratio of 1:5), ...|
The salt tolerance of a plant is the maximum salt level that plant can tolerates without losing its productivity or inhibiting growth:
Soil hydraulic conductivity is the ability of a soil to transmit water, under saturated or nearly saturated conditions.
The hydraulic conductivity is a flow rate and hence expressed in a volume of water per unit of time.
Sometimes the hydraulic conductivity is equated to the infiltration rate, but from a scientific point of view this is not quite true:
The infiltration capacity changes over the course of a rain storm (or irrigation event), so you can’t just measure infiltration capacity at any random point of time. Initial infiltration rate is high, but afterward it decreases. Finally it become constant. That steady-state rate is approximately equal to the saturated hydraulic conductivity. And it’s that steady state rate that we most often want to measure.
The saturated hydraulic conductivity Ks is expressed in mm/hr or cm/hr and is strongly related to soil texture and structure:
Management practices that improve soil organic matter content, soil aggregation, and porosity can also improve infiltration.
|Measuring saturated hydraulic conductivity Ks|
The most common way to measure saturated hydraulic conductivity Ks in the field is using a "double ring infiltrometer".
Two concentric rings are pounded slightly into the soil and filled with water. The water from the outer ring helps wet the soil and infiltrates both vertically and laterally into the dry soil. The infiltration rate is measured in the inner ring, where infiltration and percolation are happening only vertically, thanks to the water from the outer ring.Tests can be conducted in two ways: falling head and constant head. In a falling head test, water is added to the rings and the water level declines over time as infiltration occurs. In constant head tests, a device called a Mariotte bottle is added to the infiltrometer, which releases water so that a constant level (or head) is maintained inside the rings.
The video below shows a falling head double ring infiltrometer test:
Depending on the speed of infiltration, the following classification can be made:
|Rates (mm/hr)||Classification||Soil type|
|10 - 20||Medium||Sandy and silty soils|
|5 - 10||Moderate||Loams|
|1 - 5||Low||Clay soils|
|< 1||Very low||Sodic clay soils|
Importance of infiltration capacity
Best management practices are needed to improve soil infiltration: