{"id":294,"date":"2019-03-09T04:52:04","date_gmt":"2019-03-09T04:52:04","guid":{"rendered":"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/?post_type=chapter&#038;p=294"},"modified":"2019-04-22T09:14:16","modified_gmt":"2019-04-22T09:14:16","slug":"294","status":"publish","type":"chapter","link":"https:\/\/ebooks.inflibnet.ac.in\/esp10\/chapter\/294\/","title":{"rendered":"Chemical properties of soil"},"content":{"raw":"<div><span style=\"float: right\"><a href=\"https:\/\/youtu.be\/CijD5qmeD_Y\" target=\"_blank\" rel=\"noopener\"><img src=\"http:\/\/epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/2018\/11\/download.png\" alt=\"epgp books\" width=\"75px\" height=\"75px;\" \/><\/a>\r\n<\/span><\/div>\r\n&nbsp;\r\n\r\n&nbsp;\r\n\r\n<strong>27.1 Introduction<\/strong>\r\n\r\n&nbsp;\r\n<p style=\"text-align: justify\">Soil chemistry is the collaboration of various chemical components that exists among soil particles as well as in the soil solution the water sustained by soil. The chemical reactions that occur in soil are highly complicated, but their understanding will better help in managing turf and ornamentals. Soils act as storehouses for plant nutrients. Many nutrients, such as calcium and magnesium, may be supplied to plants entirely from reserves retained in the soil. Others like potassium are added regularly to soils as fertilizer with the purpose of being withdrawn when needed by crops. The relative capability of soils to store one particular group of nutrients, the cations, is referred to as <em>cation exchange capacity<\/em> or CEC. Soils are composed of a mixture of sand, silt, clay and organic matter. Both the clay and organic matter particles have a net negative charge. These negatively charged soil particles will attract and hold positively-charged particles, much like the opposite poles of a magnet attract each other. By the same demonstration, they will repel other negatively-charged particles, similarly as like poles of a magnet repel each other.<\/p>\r\n&nbsp;\r\n\r\n<strong>27.2 Cation Exchange Capacity<\/strong>\r\n\r\n&nbsp;\r\n<p style=\"text-align: justify\">Most chemical interactions occurring in soil on colloidal surfaces are because of their charged surfaces. Colloids have charged surfaces because of their chemical make-up and large surface area, which attract, \u2018ions\u2019 (charged particles) present in the soil solution. Depending on the ionic charge, size and concentration in the soil, ions can be sorbed by the colloid surface or exchanged with other ions and released to the soil solution. (Fig 27.1)<\/p>\r\n<a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-176.png\"><img class=\"aligncenter size-full wp-image-295\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-176.png\" alt=\"\" width=\"576\" height=\"371\" \/><\/a>\r\n\r\n<strong>complex 27.3 Factors affecting Cation Exchange Capacity<\/strong>\r\n\r\n&nbsp;\r\n<p style=\"text-align: justify\"><a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\"><strong>Soil <\/strong><\/a><strong>texture: <\/strong>The negatively charged clay colloids attract positively charged cations and retain them. Therefore, the cation exchange capacity of soils rises with rise in percentage of clay content.<\/p>\r\n<strong>\u00a0<\/strong>\r\n<p style=\"text-align: justify\">Clay soils with high CEC can hold large quantity of cations and reduces the loss of cations by leaching. Sandy soils, with low CEC, hold lesser amount of cations and thus cations are evacuated from <a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\">soil <\/a>by leaching (Fig 27.2).<\/p>\r\n&nbsp;\r\n<p style=\"text-align: justify\"><a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\"><strong>Soil <\/strong><\/a><strong>organic matter: <\/strong>High organic matter content increases the CEC. The CEC of clay<\/p>\r\n<p style=\"text-align: justify\"><strong>\u00a0<\/strong><\/p>\r\n<p style=\"text-align: justify\">minerals varies from 10 to 150 [cmol (p+) kg-1] whereas that of organic matter ranges from 200 to 400 [cmol (p+) kg-1].<\/p>\r\n<strong>\u00a0<\/strong>\r\n<p style=\"text-align: justify\"><strong>Nature of clay minerals: <\/strong>The CEC and specific area of the clay minerals are in the order: smectite &gt; fine mica &gt; kaolinite. Thus the CEC of a <a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\">soil <\/a>dominated by smectite type of clay minerals is much higher than kaolinite type dominated soils<\/p>\r\n&nbsp;\r\n<p style=\"text-align: justify\"><a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\"><strong>Soil <\/strong><\/a><strong>Reaction: <\/strong>As the pH is increased, the hydrogen held by the organic colloids and silicate clays (Kaolinite) becomes ionized and replaceable. The net result is enhancement of negative charge on the colloids and in turn an increase in CEC.<\/p>\r\n&nbsp;\r\n\r\n<strong>27.4 Importance of Cation Exchange<\/strong>\r\n\r\n&nbsp;\r\n\r\n&nbsp;\r\n<p style=\"text-align: justify\">Cation exchange is an important parameter in determination of <a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\">soil <\/a>fertility, <a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\">soil <\/a>acidity and basicity that results in altering <a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\">soil <\/a>physical properties as well as in mechanism for purifying or altering percolating waters.<\/p>\r\n&nbsp;\r\n<p style=\"text-align: justify\">Plant nutrients like calcium, magnesium, and potassium are supplied to plants in large amount from exchangeable forms.<\/p>\r\n&nbsp;\r\n<ul>\r\n \t<li style=\"text-align: justify\">The exchangeable K is a major source of plant K.<\/li>\r\n \t<li style=\"text-align: justify\">The exchangeable Mg is often a major source of plant Mg.<\/li>\r\n \t<li style=\"text-align: justify\">The amount of lime required to raise the pH of an acidic <a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\">soil <\/a>is greater as the CEC is greater.<\/li>\r\n \t<li style=\"text-align: justify\">Cation exchange sites hold Ca+, Mg+, K+, Na+, and NH4+ ions and slow down their losses by leaching.<\/li>\r\n \t<li style=\"text-align: justify\">Cation exchange sites hold fertilizer K+ and NH4+ and greatly reduce their mobility in soils.<\/li>\r\n \t<li style=\"text-align: justify\">Cation exchange sites adsorb various metals (Cd2+ , Zn2+, Ni2+, and Pb2+) which are present in wastewater adsorption, removes them from the percolating water, thus purifying the water which drains into groundwater.<\/li>\r\n<\/ul>\r\n<a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-177.png\"><img class=\"aligncenter size-full wp-image-296\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-177.png\" alt=\"\" width=\"1129\" height=\"733\" \/><\/a>\r\n\r\n<strong>Fig 27.2 Range of Cation Exchange Capacity\u00a0<\/strong>Source:Brady. The Nature and Properties of Soils. MacMillan\r\n\r\n&nbsp;\r\n<p style=\"text-align: justify\">The soil\u2019s ability to absorb and exchange ions is known as \u2018exchange capacity\u2019. Although both positive and negative charges are present on colloid surfaces, soils of this region are dominated by negative charges and have an overall (net) negative charge. Therefore, more cations (positive ions) are attracted to exchange sites than anions (negative ions), and soils tend to have greater cation exchange capacities (CEC) in comparison to anion exchange capacities (AEC). Fine-textured soils usually have a greater exchange capacity than coarse soils because of a higher proportion of colloids.<\/p>\r\n&nbsp;\r\n<p style=\"text-align: justify\"><strong>27.5 Soil pH<\/strong><\/p>\r\n&nbsp;\r\n<p style=\"text-align: justify\">Soil pH is associated with the soil\u2019s acidity or alkalinity and is the measure of hydrogen ions (H+) in the soil. A large amount of H+ relates to the low pH value and contrary. The pH scale varies from 0 to 14 with 7 being neutral, below 7 acidic, and above 7 alkaline or basic. Soil pH can influence CEC and AEC by changing the surface charge of colloids. A higher concentration of H+ (lower pH) will nullify the negative charge on colloids, thus decreasing CEC and increasing AEC. The opposite occurs when pH increases. (Fig 27.3)<\/p>\r\n&nbsp;\r\n\r\n<a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-178.png\"><img class=\"aligncenter size-full wp-image-297\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-178.png\" alt=\"\" width=\"672\" height=\"379\" \/><\/a>\r\n\r\n<strong>Importance of soil pH in crop production-<\/strong>\r\n\r\n&nbsp;\r\n<ul>\r\n \t<li style=\"text-align: justify\">1) It is useful in determining the availability of plant nutrients e.g. P is fixed by Al and Fe oxides at low pH, at high pH it is fixed by Ca. Therefore, P is available maximally at near neutral pH.<\/li>\r\n \t<li style=\"text-align: justify\">2) pH effects the availability of toxic amounts of minerals and elements that can diminish the crop growth<\/li>\r\n \t<li style=\"text-align: justify\">3) It manipulates the population and activities of beneficial microbe.<\/li>\r\n<\/ul>\r\n&nbsp;\r\n\r\n<strong>27.6 Salt-Affected Soils<\/strong>\r\n\r\n&nbsp;\r\n<p style=\"text-align: justify\">The presence and concentration of salts in soil can have conflicting impact on soil function as well as management. Salt affected soils mostly occur in arid and semiarid regions where evaporation surpasses precipitation and dissolved salts are left behind to accumulate, or in areas where vegetation or irrigation changes have resulted into leaching of salts and accumulation in low-lying places (saline seeps). The three main categories of salt-affected soils are saline, sodic and saline-sodic. Saline soils comprises of large amount of soluble salts, primarily calcium (Ca2+), magnesium (Mg2+), and potassium (K+), whereas sodic soils are dominated by sodium ions (Na+). Saline-sodic soils have both high salt and Na+ content. Concentration of salts in soil influences the structure, porosity and plant water relations which ultimately leads to reduced productivity (Table 1).<\/p>\r\n&nbsp;\r\n\r\n&nbsp;\r\n\r\n<a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-179.png\"><img class=\"aligncenter size-full wp-image-298\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-179.png\" alt=\"\" width=\"614\" height=\"340\" \/><\/a>\r\n<p style=\"text-align: justify\">The degree of acidity or alkalinity is an important parameter that affects various other chemical, physical and biological properties of soil. Soil acidity is determined as the total amount of acid present in the soil. The soil reaction is expressed as the soil pH; this is the measure of the relative acidity and alkalinity of the soil.<\/p>\r\n&nbsp;\r\n<p style=\"text-align: justify\"><strong>Active <\/strong>acidity is that measured by the soil pH.<\/p>\r\n<p style=\"text-align: justify\"><strong>Reserve <\/strong>acidity is that left within the soil microcell, it is usually measured by titrating the soil solution with a base (Fig 27.4).<\/p>\r\n<a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-180.png\"><img class=\"aligncenter size-full wp-image-299\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-180.png\" alt=\"\" width=\"611\" height=\"347\" \/><\/a>\r\n\r\n<strong>Causes of soil acidity:-<\/strong>\r\n\r\n&nbsp;\r\n<ul>\r\n \t<li style=\"text-align: justify\">1) Leaching loss of bases like Ca, Mg, etc.<\/li>\r\n \t<li style=\"text-align: justify\">2) Application of acid-forming fertilizers e.g. urea, NH4+ based fertilizers<\/li>\r\n \t<li style=\"text-align: justify\">3) Acid rains.<\/li>\r\n \t<li style=\"text-align: justify\">4) Decomposition of organic matter, CO2 is evolved; it mixed with soil water to form weak carbonic acid (H2CO3)<\/li>\r\n \t<li style=\"text-align: justify\">5) Hydrolysis of Al. Al3+ + 3H2O Al (OH) 3 + 3H+<\/li>\r\n<\/ul>\r\n<a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-181.png\"><img class=\"aligncenter size-full wp-image-300\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-181.png\" alt=\"\" width=\"450\" height=\"277\" \/><\/a>\r\n\r\n&nbsp;\r\n\r\n<strong>27.7 Soil Nutrients<\/strong>\r\n\r\n&nbsp;\r\n<p style=\"text-align: justify\">Sixteen\u00a0 elements\u00a0 or\u00a0 nutrients\u00a0 are\u00a0 essential\u00a0 for\u00a0 growth\u00a0 and\u00a0 reproduction\u00a0 in\u00a0 plants.\u00a0 Such\u00a0 as\u00a0<a href=\"https:\/\/en.wikipedia.org\/wiki\/Carbon\">carbon <\/a><strong>C<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Hydrogen\">hydrogen <\/a><strong>H<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Oxygen\">oxygen <\/a><strong>O<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Nitrogen\">nitrogen <\/a><strong>N<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Boron\">boron <\/a><strong>B<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Phosphorus\">phosphorus <\/a><strong>P<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Potassium\">potassium <\/a><strong>K<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Sulfur\">sulfur <\/a><strong>S<\/strong><a href=\"https:\/\/en.wikipedia.org\/wiki\/Calcium\">,cal\u00a0<\/a><a href=\"https:\/\/en.wikipedia.org\/wiki\/Calcium\">cium <\/a><strong>Ca<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Magnesium\">magnesium <\/a><strong>Mg<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Iron\">iron <\/a><strong>Fe<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Manganese\">manganese <\/a><strong>Mn<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Copper\">copper <\/a><strong>Cu<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Zinc\">zinc <\/a><strong>Zn<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Molybdenum\">molybdenum <\/a><strong>MO<\/strong>, and <a href=\"https:\/\/en.wikipedia.org\/wiki\/Chlorine\">chlorine <\/a><strong>Cl<\/strong>. Nutrients required for plants to complete their life cycle are called\u00a0 as <strong>essential\u00a0<\/strong><strong>nutrients<\/strong>. Nutrients that increase the plant growth but are not important to complete the plant's life cycle are called <strong>non-essential<\/strong>. With the exception of carbon, hydrogen and oxygen, which are supplied by carbon dioxide and water, the nutrients originate from the mineral component of the soil. Uptake of nutrients by plants can only occur when they are present in a plant-available form. In a variety of situations, nutrients are absorbed in an ionic form from soil water. The bulk of\u00a0 most\u00a0 nutrient\u00a0 elements\u00a0 in\u00a0 the\u00a0 soil\u00a0 are\u00a0 retained\u00a0 in\u00a0 crystalline\u00a0 form\u00a0 within\u00a0 primary\u00a0 and secondary minerals, to support rapid plant growth. For example, the application of finely ground minerals, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Feldspar\">feldspar <\/a>and <a href=\"https:\/\/en.wikipedia.org\/wiki\/Apatite\">apatite, <\/a>to soil seldom provides the necessary amounts of potassium and phosphorus at a rate sufficient for proper plant growth, as most of\u00a0 nutrients remain bound in the crystals of those minerals. Plant growth will be hampered if a particular nutrient availability is in limited supply for\u00a0 example if there\u00a0 is\u00a0 deficiency of\u00a0 phosphorous then the supply of other nutrients\u00a0 will\u00a0 be\u00a0 ineffective\u00a0 until\u00a0 the\u00a0 deficiency of\u00a0 phosphorous\u00a0 is\u00a0 removed.\u00a0 The\u00a0 nutrients adsorbed onto the surfaces of clay colloids and <a href=\"https:\/\/en.wikipedia.org\/wiki\/Soil_organic_matter\">soil organic matter <\/a>provide a more accessible reservoir of many plant nutrients such as K, Ca, Mg, P, and Zn. As plants absorb the nutrients from the soil water, the soluble pool is replaced from the surface bound pool. The decomposition of <a href=\"https:\/\/en.wikipedia.org\/wiki\/Soil_organic_matter\">soil organic matter <\/a>with the help of microbes is another mechanism whereby the soluble pool of nutrients is replenished this is important for the regular supply of plant-available nutrients from soil.<\/p>\r\n&nbsp;\r\n\r\n<strong>27.7.1 Pathways of mineral nutrient transport in roots.<\/strong>\r\n\r\n&nbsp;\r\n<p style=\"text-align: justify\">Minerals are absorbed at the surface of the root, by the root hairs. While passing through the cortex, they either follow the cell walls and the spaces between them or go directly through the plasma membranes and the protoplasts of the cells, passing from one cell to the next by the plasmodesmata. When they reach the endodermis, their further passage through the cell walls is blocked by the Casparian strips, and they must pass through the membrane and protoplast of an endodermal cell before they can reach the xylem. Minerals are absorbed at the surface of the root, mainly by the root hairs. (Fig 27.5).<\/p>\r\n&nbsp;\r\n\r\n&nbsp;\r\n\r\n<a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-182.png\"><img class=\"aligncenter size-full wp-image-301\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-182.png\" alt=\"\" width=\"609\" height=\"346\" \/><\/a>\r\n\r\n<strong>Movement of nutrient from soil to root<\/strong>\r\n\r\n&nbsp;\r\n\r\n&nbsp;\r\n<p style=\"text-align: justify\">There are three basic mechanisms by which nutrients make contact with the root surface for plant uptake. They are root interception, ma<strong>s<\/strong>s flow, and diffusion.<\/p>\r\n&nbsp;\r\n\r\n&nbsp;\r\n<p style=\"text-align: justify\">Root interception: Root interception occurs when a nutrient comes into physical contact with the root surface. As a general rule, the occurrence of root interception increases as the root surface area and mass increases, thus enabling the plant to explore a greater amount of soil. Root interception increases by mycorrhizal fungi, which colonize rootsand enhances root exploration into the soil. Root interception is responsible for an appropriate amount of calcium uptake, and some amounts of magnesium, zinc and manganese.<\/p>\r\n&nbsp;\r\n<p style=\"text-align: justify\">Mass flow: Mass flow occurs when nutrients are transported to the surface of roots by the water movement in the soil (i.e. percolation, transpiration, or evaporation). The rate of water flow determines the amount of nutrients that are transported to the root surface. Therefore, mass flow decreases. Most of the nitrogen, calcium, magnesium, sulfur, copper, boron, manganese and molybdenum move to the root by mass flow.<\/p>\r\n&nbsp;\r\n<p style=\"text-align: justify\">Diffusion: Diffusion is the\u00a0process of movement of a particular nutrient along a concentration gradient. When there is a difference in concentration of a particular nutrient within the soil solution, the nutrient will move from an area of higher to lower concentration. As the sugar dissolves, it moves through parts of the water with lower sugar concentration until it is evenly distributed, or uniformly concentrated. Diffusion delivers significant amounts of phosphorus, potassium, zinc, and iron to the root surface. Diffusion is a relatively slow process in comparison to the mass flow of nutrients with water movement toward the root. Mobility of a nutrient within the soil is closely related to the chemical properties of the soil, such as CEC and AEC, as well as the soil conditions, such as moisture. When there is enough moisture in the soil for leaching to occur, the percolating water can carry dissolved nutrients which will be subsequently lost from the soil profile. The nutrients which are easily leached are usually those nutrients that are less strongly held by soil particles. For instance, in a soil with a high CEC and low AEC, nitrate (an anion) will leach much more readily than calcium (a cation). Additionally, in such a soil, potassium will leach more readily than calcium (divalent cation) since calcium is more strongly held to the soil particles than potassium.<\/p>\r\n&nbsp;\r\n\r\n&nbsp;\r\n\r\n<strong>Summary:<\/strong>\r\n\r\n&nbsp;\r\n<p style=\"text-align: justify\">Soil chemical properties influence various processes in the soil which make it applicable for agricultural practices as well as various other purposes. Texture, structure, and porosity effect the movement and retaining of water, air and solutes in the soil, which subsequently have impact on plant growth and microbial activity.<\/p>\r\n<table>\r\n<tbody>\r\n<tr>\r\n<td><strong>you can view video on Chemical properties of soil<\/strong><\/td>\r\n<td><a href=\"https:\/\/youtu.be\/CijD5qmeD_Y\" target=\"_blank\" rel=\"noopener\"><img class=\"alignnone wp-image-120\" src=\"http:\/\/epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/2018\/11\/download.png\" alt=\"\" width=\"36\" height=\"36\" \/><\/a><\/td>\r\n<\/tr>\r\n<\/tbody>\r\n<\/table>\r\n\r\n<strong>Web links:<\/strong>\r\n\r\n&nbsp;\r\n<ul>\r\n \t<li style=\"text-align: justify\">http:\/\/gaia.flemingc.on.ca\/~jscarlet htm<\/li>\r\n \t<li style=\"text-align: justify\"><a href=\"http:\/\/grancominerals.com\/wp-content\/uploads\/2013\/08\/CEC_graphic.jpg\">http:\/\/grancominerals.com\/wp-content\/uploads\/2013\/08\/CEC_graphic.jpg<\/a> <a href=\"http:\/\/gaia.flemingc.on.ca\/~jscarlet\/ph.htm\">http:\/\/gaia.flemingc.on.ca\/~jscarlet\/ph.htm<\/a><\/li>\r\n<\/ul>\r\n&nbsp;\r\n\r\n&nbsp;","rendered":"<div><span style=\"float: right\"><a href=\"https:\/\/youtu.be\/CijD5qmeD_Y\" target=\"_blank\" rel=\"noopener\"><img decoding=\"async\" src=\"http:\/\/epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/2018\/11\/download.png\" alt=\"epgp books\" width=\"75px\" height=\"75px;\" \/><\/a><br \/>\n<\/span><\/div>\n<p>&nbsp;<\/p>\n<p>&nbsp;<\/p>\n<p><strong>27.1 Introduction<\/strong><\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">Soil chemistry is the collaboration of various chemical components that exists among soil particles as well as in the soil solution the water sustained by soil. The chemical reactions that occur in soil are highly complicated, but their understanding will better help in managing turf and ornamentals. Soils act as storehouses for plant nutrients. Many nutrients, such as calcium and magnesium, may be supplied to plants entirely from reserves retained in the soil. Others like potassium are added regularly to soils as fertilizer with the purpose of being withdrawn when needed by crops. The relative capability of soils to store one particular group of nutrients, the cations, is referred to as <em>cation exchange capacity<\/em> or CEC. Soils are composed of a mixture of sand, silt, clay and organic matter. Both the clay and organic matter particles have a net negative charge. These negatively charged soil particles will attract and hold positively-charged particles, much like the opposite poles of a magnet attract each other. By the same demonstration, they will repel other negatively-charged particles, similarly as like poles of a magnet repel each other.<\/p>\n<p>&nbsp;<\/p>\n<p><strong>27.2 Cation Exchange Capacity<\/strong><\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">Most chemical interactions occurring in soil on colloidal surfaces are because of their charged surfaces. Colloids have charged surfaces because of their chemical make-up and large surface area, which attract, \u2018ions\u2019 (charged particles) present in the soil solution. Depending on the ionic charge, size and concentration in the soil, ions can be sorbed by the colloid surface or exchanged with other ions and released to the soil solution. (Fig 27.1)<\/p>\n<p><a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-176.png\"><img loading=\"lazy\" decoding=\"async\" class=\"aligncenter size-full wp-image-295\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-176.png\" alt=\"\" width=\"576\" height=\"371\" srcset=\"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-176.png 576w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-176-300x193.png 300w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-176-65x42.png 65w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-176-225x145.png 225w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-176-350x225.png 350w\" sizes=\"auto, (max-width: 576px) 100vw, 576px\" \/><\/a><\/p>\n<p><strong>complex 27.3 Factors affecting Cation Exchange Capacity<\/strong><\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\"><a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\"><strong>Soil <\/strong><\/a><strong>texture: <\/strong>The negatively charged clay colloids attract positively charged cations and retain them. Therefore, the cation exchange capacity of soils rises with rise in percentage of clay content.<\/p>\n<p><strong>\u00a0<\/strong><\/p>\n<p style=\"text-align: justify\">Clay soils with high CEC can hold large quantity of cations and reduces the loss of cations by leaching. Sandy soils, with low CEC, hold lesser amount of cations and thus cations are evacuated from <a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\">soil <\/a>by leaching (Fig 27.2).<\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\"><a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\"><strong>Soil <\/strong><\/a><strong>organic matter: <\/strong>High organic matter content increases the CEC. The CEC of clay<\/p>\n<p style=\"text-align: justify\"><strong>\u00a0<\/strong><\/p>\n<p style=\"text-align: justify\">minerals varies from 10 to 150 [cmol (p+) kg-1] whereas that of organic matter ranges from 200 to 400 [cmol (p+) kg-1].<\/p>\n<p><strong>\u00a0<\/strong><\/p>\n<p style=\"text-align: justify\"><strong>Nature of clay minerals: <\/strong>The CEC and specific area of the clay minerals are in the order: smectite &gt; fine mica &gt; kaolinite. Thus the CEC of a <a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\">soil <\/a>dominated by smectite type of clay minerals is much higher than kaolinite type dominated soils<\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\"><a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\"><strong>Soil <\/strong><\/a><strong>Reaction: <\/strong>As the pH is increased, the hydrogen held by the organic colloids and silicate clays (Kaolinite) becomes ionized and replaceable. The net result is enhancement of negative charge on the colloids and in turn an increase in CEC.<\/p>\n<p>&nbsp;<\/p>\n<p><strong>27.4 Importance of Cation Exchange<\/strong><\/p>\n<p>&nbsp;<\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">Cation exchange is an important parameter in determination of <a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\">soil <\/a>fertility, <a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\">soil <\/a>acidity and basicity that results in altering <a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\">soil <\/a>physical properties as well as in mechanism for purifying or altering percolating waters.<\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">Plant nutrients like calcium, magnesium, and potassium are supplied to plants in large amount from exchangeable forms.<\/p>\n<p>&nbsp;<\/p>\n<ul>\n<li style=\"text-align: justify\">The exchangeable K is a major source of plant K.<\/li>\n<li style=\"text-align: justify\">The exchangeable Mg is often a major source of plant Mg.<\/li>\n<li style=\"text-align: justify\">The amount of lime required to raise the pH of an acidic <a href=\"http:\/\/ecoursesonline.iasri.res.in\/mod\/page\/view.php?id=6335\">soil <\/a>is greater as the CEC is greater.<\/li>\n<li style=\"text-align: justify\">Cation exchange sites hold Ca+, Mg+, K+, Na+, and NH4+ ions and slow down their losses by leaching.<\/li>\n<li style=\"text-align: justify\">Cation exchange sites hold fertilizer K+ and NH4+ and greatly reduce their mobility in soils.<\/li>\n<li style=\"text-align: justify\">Cation exchange sites adsorb various metals (Cd2+ , Zn2+, Ni2+, and Pb2+) which are present in wastewater adsorption, removes them from the percolating water, thus purifying the water which drains into groundwater.<\/li>\n<\/ul>\n<p><a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-177.png\"><img loading=\"lazy\" decoding=\"async\" class=\"aligncenter size-full wp-image-296\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-177.png\" alt=\"\" width=\"1129\" height=\"733\" srcset=\"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-177.png 1129w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-177-300x195.png 300w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-177-768x499.png 768w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-177-1024x665.png 1024w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-177-65x42.png 65w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-177-225x146.png 225w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-177-350x227.png 350w\" sizes=\"auto, (max-width: 1129px) 100vw, 1129px\" \/><\/a><\/p>\n<p><strong>Fig 27.2 Range of Cation Exchange Capacity\u00a0<\/strong>Source:Brady. The Nature and Properties of Soils. MacMillan<\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">The soil\u2019s ability to absorb and exchange ions is known as \u2018exchange capacity\u2019. Although both positive and negative charges are present on colloid surfaces, soils of this region are dominated by negative charges and have an overall (net) negative charge. Therefore, more cations (positive ions) are attracted to exchange sites than anions (negative ions), and soils tend to have greater cation exchange capacities (CEC) in comparison to anion exchange capacities (AEC). Fine-textured soils usually have a greater exchange capacity than coarse soils because of a higher proportion of colloids.<\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\"><strong>27.5 Soil pH<\/strong><\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">Soil pH is associated with the soil\u2019s acidity or alkalinity and is the measure of hydrogen ions (H+) in the soil. A large amount of H+ relates to the low pH value and contrary. The pH scale varies from 0 to 14 with 7 being neutral, below 7 acidic, and above 7 alkaline or basic. Soil pH can influence CEC and AEC by changing the surface charge of colloids. A higher concentration of H+ (lower pH) will nullify the negative charge on colloids, thus decreasing CEC and increasing AEC. The opposite occurs when pH increases. (Fig 27.3)<\/p>\n<p>&nbsp;<\/p>\n<p><a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-178.png\"><img loading=\"lazy\" decoding=\"async\" class=\"aligncenter size-full wp-image-297\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-178.png\" alt=\"\" width=\"672\" height=\"379\" srcset=\"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-178.png 672w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-178-300x169.png 300w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-178-65x37.png 65w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-178-225x127.png 225w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-178-350x197.png 350w\" sizes=\"auto, (max-width: 672px) 100vw, 672px\" \/><\/a><\/p>\n<p><strong>Importance of soil pH in crop production-<\/strong><\/p>\n<p>&nbsp;<\/p>\n<ul>\n<li style=\"text-align: justify\">1) It is useful in determining the availability of plant nutrients e.g. P is fixed by Al and Fe oxides at low pH, at high pH it is fixed by Ca. Therefore, P is available maximally at near neutral pH.<\/li>\n<li style=\"text-align: justify\">2) pH effects the availability of toxic amounts of minerals and elements that can diminish the crop growth<\/li>\n<li style=\"text-align: justify\">3) It manipulates the population and activities of beneficial microbe.<\/li>\n<\/ul>\n<p>&nbsp;<\/p>\n<p><strong>27.6 Salt-Affected Soils<\/strong><\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">The presence and concentration of salts in soil can have conflicting impact on soil function as well as management. Salt affected soils mostly occur in arid and semiarid regions where evaporation surpasses precipitation and dissolved salts are left behind to accumulate, or in areas where vegetation or irrigation changes have resulted into leaching of salts and accumulation in low-lying places (saline seeps). The three main categories of salt-affected soils are saline, sodic and saline-sodic. Saline soils comprises of large amount of soluble salts, primarily calcium (Ca2+), magnesium (Mg2+), and potassium (K+), whereas sodic soils are dominated by sodium ions (Na+). Saline-sodic soils have both high salt and Na+ content. Concentration of salts in soil influences the structure, porosity and plant water relations which ultimately leads to reduced productivity (Table 1).<\/p>\n<p>&nbsp;<\/p>\n<p>&nbsp;<\/p>\n<p><a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-179.png\"><img loading=\"lazy\" decoding=\"async\" class=\"aligncenter size-full wp-image-298\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-179.png\" alt=\"\" width=\"614\" height=\"340\" srcset=\"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-179.png 614w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-179-300x166.png 300w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-179-65x36.png 65w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-179-225x125.png 225w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-179-350x194.png 350w\" sizes=\"auto, (max-width: 614px) 100vw, 614px\" \/><\/a><\/p>\n<p style=\"text-align: justify\">The degree of acidity or alkalinity is an important parameter that affects various other chemical, physical and biological properties of soil. Soil acidity is determined as the total amount of acid present in the soil. The soil reaction is expressed as the soil pH; this is the measure of the relative acidity and alkalinity of the soil.<\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\"><strong>Active <\/strong>acidity is that measured by the soil pH.<\/p>\n<p style=\"text-align: justify\"><strong>Reserve <\/strong>acidity is that left within the soil microcell, it is usually measured by titrating the soil solution with a base (Fig 27.4).<\/p>\n<p><a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-180.png\"><img loading=\"lazy\" decoding=\"async\" class=\"aligncenter size-full wp-image-299\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-180.png\" alt=\"\" width=\"611\" height=\"347\" srcset=\"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-180.png 611w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-180-300x170.png 300w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-180-65x37.png 65w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-180-225x128.png 225w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-180-350x199.png 350w\" sizes=\"auto, (max-width: 611px) 100vw, 611px\" \/><\/a><\/p>\n<p><strong>Causes of soil acidity:-<\/strong><\/p>\n<p>&nbsp;<\/p>\n<ul>\n<li style=\"text-align: justify\">1) Leaching loss of bases like Ca, Mg, etc.<\/li>\n<li style=\"text-align: justify\">2) Application of acid-forming fertilizers e.g. urea, NH4+ based fertilizers<\/li>\n<li style=\"text-align: justify\">3) Acid rains.<\/li>\n<li style=\"text-align: justify\">4) Decomposition of organic matter, CO2 is evolved; it mixed with soil water to form weak carbonic acid (H2CO3)<\/li>\n<li style=\"text-align: justify\">5) Hydrolysis of Al. Al3+ + 3H2O Al (OH) 3 + 3H+<\/li>\n<\/ul>\n<p><a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-181.png\"><img loading=\"lazy\" decoding=\"async\" class=\"aligncenter size-full wp-image-300\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-181.png\" alt=\"\" width=\"450\" height=\"277\" srcset=\"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-181.png 450w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-181-300x185.png 300w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-181-65x40.png 65w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-181-225x139.png 225w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-181-350x215.png 350w\" sizes=\"auto, (max-width: 450px) 100vw, 450px\" \/><\/a><\/p>\n<p>&nbsp;<\/p>\n<p><strong>27.7 Soil Nutrients<\/strong><\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">Sixteen\u00a0 elements\u00a0 or\u00a0 nutrients\u00a0 are\u00a0 essential\u00a0 for\u00a0 growth\u00a0 and\u00a0 reproduction\u00a0 in\u00a0 plants.\u00a0 Such\u00a0 as\u00a0<a href=\"https:\/\/en.wikipedia.org\/wiki\/Carbon\">carbon <\/a><strong>C<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Hydrogen\">hydrogen <\/a><strong>H<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Oxygen\">oxygen <\/a><strong>O<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Nitrogen\">nitrogen <\/a><strong>N<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Boron\">boron <\/a><strong>B<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Phosphorus\">phosphorus <\/a><strong>P<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Potassium\">potassium <\/a><strong>K<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Sulfur\">sulfur <\/a><strong>S<\/strong><a href=\"https:\/\/en.wikipedia.org\/wiki\/Calcium\">,cal\u00a0<\/a><a href=\"https:\/\/en.wikipedia.org\/wiki\/Calcium\">cium <\/a><strong>Ca<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Magnesium\">magnesium <\/a><strong>Mg<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Iron\">iron <\/a><strong>Fe<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Manganese\">manganese <\/a><strong>Mn<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Copper\">copper <\/a><strong>Cu<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Zinc\">zinc <\/a><strong>Zn<\/strong>, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Molybdenum\">molybdenum <\/a><strong>MO<\/strong>, and <a href=\"https:\/\/en.wikipedia.org\/wiki\/Chlorine\">chlorine <\/a><strong>Cl<\/strong>. Nutrients required for plants to complete their life cycle are called\u00a0 as <strong>essential\u00a0<\/strong><strong>nutrients<\/strong>. Nutrients that increase the plant growth but are not important to complete the plant&#8217;s life cycle are called <strong>non-essential<\/strong>. With the exception of carbon, hydrogen and oxygen, which are supplied by carbon dioxide and water, the nutrients originate from the mineral component of the soil. Uptake of nutrients by plants can only occur when they are present in a plant-available form. In a variety of situations, nutrients are absorbed in an ionic form from soil water. The bulk of\u00a0 most\u00a0 nutrient\u00a0 elements\u00a0 in\u00a0 the\u00a0 soil\u00a0 are\u00a0 retained\u00a0 in\u00a0 crystalline\u00a0 form\u00a0 within\u00a0 primary\u00a0 and secondary minerals, to support rapid plant growth. For example, the application of finely ground minerals, <a href=\"https:\/\/en.wikipedia.org\/wiki\/Feldspar\">feldspar <\/a>and <a href=\"https:\/\/en.wikipedia.org\/wiki\/Apatite\">apatite, <\/a>to soil seldom provides the necessary amounts of potassium and phosphorus at a rate sufficient for proper plant growth, as most of\u00a0 nutrients remain bound in the crystals of those minerals. Plant growth will be hampered if a particular nutrient availability is in limited supply for\u00a0 example if there\u00a0 is\u00a0 deficiency of\u00a0 phosphorous then the supply of other nutrients\u00a0 will\u00a0 be\u00a0 ineffective\u00a0 until\u00a0 the\u00a0 deficiency of\u00a0 phosphorous\u00a0 is\u00a0 removed.\u00a0 The\u00a0 nutrients adsorbed onto the surfaces of clay colloids and <a href=\"https:\/\/en.wikipedia.org\/wiki\/Soil_organic_matter\">soil organic matter <\/a>provide a more accessible reservoir of many plant nutrients such as K, Ca, Mg, P, and Zn. As plants absorb the nutrients from the soil water, the soluble pool is replaced from the surface bound pool. The decomposition of <a href=\"https:\/\/en.wikipedia.org\/wiki\/Soil_organic_matter\">soil organic matter <\/a>with the help of microbes is another mechanism whereby the soluble pool of nutrients is replenished this is important for the regular supply of plant-available nutrients from soil.<\/p>\n<p>&nbsp;<\/p>\n<p><strong>27.7.1 Pathways of mineral nutrient transport in roots.<\/strong><\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">Minerals are absorbed at the surface of the root, by the root hairs. While passing through the cortex, they either follow the cell walls and the spaces between them or go directly through the plasma membranes and the protoplasts of the cells, passing from one cell to the next by the plasmodesmata. When they reach the endodermis, their further passage through the cell walls is blocked by the Casparian strips, and they must pass through the membrane and protoplast of an endodermal cell before they can reach the xylem. Minerals are absorbed at the surface of the root, mainly by the root hairs. (Fig 27.5).<\/p>\n<p>&nbsp;<\/p>\n<p>&nbsp;<\/p>\n<p><a href=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-182.png\"><img loading=\"lazy\" decoding=\"async\" class=\"aligncenter size-full wp-image-301\" src=\"http:\/\/esp10.epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-182.png\" alt=\"\" width=\"609\" height=\"346\" srcset=\"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-182.png 609w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-182-300x170.png 300w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-182-65x37.png 65w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-182-225x128.png 225w, https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-content\/uploads\/sites\/171\/2019\/03\/Untitled-182-350x199.png 350w\" sizes=\"auto, (max-width: 609px) 100vw, 609px\" \/><\/a><\/p>\n<p><strong>Movement of nutrient from soil to root<\/strong><\/p>\n<p>&nbsp;<\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">There are three basic mechanisms by which nutrients make contact with the root surface for plant uptake. They are root interception, ma<strong>s<\/strong>s flow, and diffusion.<\/p>\n<p>&nbsp;<\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">Root interception: Root interception occurs when a nutrient comes into physical contact with the root surface. As a general rule, the occurrence of root interception increases as the root surface area and mass increases, thus enabling the plant to explore a greater amount of soil. Root interception increases by mycorrhizal fungi, which colonize rootsand enhances root exploration into the soil. Root interception is responsible for an appropriate amount of calcium uptake, and some amounts of magnesium, zinc and manganese.<\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">Mass flow: Mass flow occurs when nutrients are transported to the surface of roots by the water movement in the soil (i.e. percolation, transpiration, or evaporation). The rate of water flow determines the amount of nutrients that are transported to the root surface. Therefore, mass flow decreases. Most of the nitrogen, calcium, magnesium, sulfur, copper, boron, manganese and molybdenum move to the root by mass flow.<\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">Diffusion: Diffusion is the\u00a0process of movement of a particular nutrient along a concentration gradient. When there is a difference in concentration of a particular nutrient within the soil solution, the nutrient will move from an area of higher to lower concentration. As the sugar dissolves, it moves through parts of the water with lower sugar concentration until it is evenly distributed, or uniformly concentrated. Diffusion delivers significant amounts of phosphorus, potassium, zinc, and iron to the root surface. Diffusion is a relatively slow process in comparison to the mass flow of nutrients with water movement toward the root. Mobility of a nutrient within the soil is closely related to the chemical properties of the soil, such as CEC and AEC, as well as the soil conditions, such as moisture. When there is enough moisture in the soil for leaching to occur, the percolating water can carry dissolved nutrients which will be subsequently lost from the soil profile. The nutrients which are easily leached are usually those nutrients that are less strongly held by soil particles. For instance, in a soil with a high CEC and low AEC, nitrate (an anion) will leach much more readily than calcium (a cation). Additionally, in such a soil, potassium will leach more readily than calcium (divalent cation) since calcium is more strongly held to the soil particles than potassium.<\/p>\n<p>&nbsp;<\/p>\n<p>&nbsp;<\/p>\n<p><strong>Summary:<\/strong><\/p>\n<p>&nbsp;<\/p>\n<p style=\"text-align: justify\">Soil chemical properties influence various processes in the soil which make it applicable for agricultural practices as well as various other purposes. Texture, structure, and porosity effect the movement and retaining of water, air and solutes in the soil, which subsequently have impact on plant growth and microbial activity.<\/p>\n<table>\n<tbody>\n<tr>\n<td><strong>you can view video on Chemical properties of soil<\/strong><\/td>\n<td><a href=\"https:\/\/youtu.be\/CijD5qmeD_Y\" target=\"_blank\" rel=\"noopener\"><img loading=\"lazy\" decoding=\"async\" class=\"alignnone wp-image-120\" src=\"http:\/\/epgpbooks.inflibnet.ac.in\/wp-content\/uploads\/2018\/11\/download.png\" alt=\"\" width=\"36\" height=\"36\" \/><\/a><\/td>\n<\/tr>\n<\/tbody>\n<\/table>\n<p><strong>Web links:<\/strong><\/p>\n<p>&nbsp;<\/p>\n<ul>\n<li style=\"text-align: justify\">http:\/\/gaia.flemingc.on.ca\/~jscarlet htm<\/li>\n<li style=\"text-align: justify\"><a href=\"http:\/\/grancominerals.com\/wp-content\/uploads\/2013\/08\/CEC_graphic.jpg\">http:\/\/grancominerals.com\/wp-content\/uploads\/2013\/08\/CEC_graphic.jpg<\/a> <a href=\"http:\/\/gaia.flemingc.on.ca\/~jscarlet\/ph.htm\">http:\/\/gaia.flemingc.on.ca\/~jscarlet\/ph.htm<\/a><\/li>\n<\/ul>\n<p>&nbsp;<\/p>\n<p>&nbsp;<\/p>\n","protected":false},"author":3,"menu_order":26,"template":"","meta":{"pb_show_title":"on","pb_short_title":"","pb_subtitle":"","pb_authors":["dr-meenakshi-nandal"],"pb_section_license":""},"chapter-type":[],"contributor":[60],"license":[],"class_list":["post-294","chapter","type-chapter","status-publish","hentry","contributor-dr-meenakshi-nandal"],"part":3,"_links":{"self":[{"href":"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-json\/pressbooks\/v2\/chapters\/294","targetHints":{"allow":["GET"]}}],"collection":[{"href":"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-json\/pressbooks\/v2\/chapters"}],"about":[{"href":"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-json\/wp\/v2\/types\/chapter"}],"author":[{"embeddable":true,"href":"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-json\/wp\/v2\/users\/3"}],"version-history":[{"count":5,"href":"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-json\/pressbooks\/v2\/chapters\/294\/revisions"}],"predecessor-version":[{"id":516,"href":"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-json\/pressbooks\/v2\/chapters\/294\/revisions\/516"}],"part":[{"href":"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-json\/pressbooks\/v2\/parts\/3"}],"metadata":[{"href":"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-json\/pressbooks\/v2\/chapters\/294\/metadata\/"}],"wp:attachment":[{"href":"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-json\/wp\/v2\/media?parent=294"}],"wp:term":[{"taxonomy":"chapter-type","embeddable":true,"href":"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-json\/pressbooks\/v2\/chapter-type?post=294"},{"taxonomy":"contributor","embeddable":true,"href":"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-json\/wp\/v2\/contributor?post=294"},{"taxonomy":"license","embeddable":true,"href":"https:\/\/ebooks.inflibnet.ac.in\/esp10\/wp-json\/wp\/v2\/license?post=294"}],"curies":[{"name":"wp","href":"https:\/\/api.w.org\/{rel}","templated":true}]}}