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Soil profile, physical properties-soil structure and texture , Soils of Kerala-problem soils of Kerala soil profile A vertical section of soil through all its horizons and extending in to the parent material. A vertical exposure of the horizon sequence is termed as “soil profile”. A soil horizon is a layer of soil, approximately parallel to the soil surface, differing in properties and characteristics from adjacent layers below or above it. Practically, soil profile is an important tool for soil classification which is applicable for thorough understanding of the soils. Five master horizons are recognized in soil profile and are designated using capital letters O, A, E, B and C. O Horizons:(Organic) It comprises of organic horizons that form above the mineral soil. They result from litter derived from dead plants and animals. ‘O’ horizons usually occur in forested areas and are generally absent in grassland regions. A - Horizon: It is the top most mineral horizon. It contains a strong mixture of decomposed (humified) organic matter, which tends to impart a darker color than that of the lower horizons. E - Horizon: It is an eluviated horizon. Clay and sesquioxides are invariably leached out, leaving a concentration of resistant minerals such as quartz. An ‘E’ horizon is generally lighter in color than the ‘A’ horizon and is found under ‘A’ horizon. “B” – Horizon : (Illuvial) The sub -surface ‘B’ horizons include layers in which illuviation of materials has taken place from above and even from below. In humid regions, the B horizons are the layers of maximum accumulation of materials such as sesquioxides and silicate clays. In arid and semi-arid regions Ca CO 3, Ca SO 4 and other salts may accumulate in the B horizon. ‘C’ – Horizon: It is the unconsolidated material underlying the ‘Solum’ (A & B). It may or may not be the same as the parent material from which the solum formed. The ‘C’ horizon is out side the zones of major biological activities and is generally little affected by the processes that formed the horizons above it. ‘R’- Layer : Underlying consolidated rock, with little evidence of weathering.
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Soil profile, physical properties-soil structure and texture , Soils of Kerala-problem soils of Keralasoil profile A vertical section of soil through all its horizons and extending in to the parent material.A vertical exposure of the horizon sequence is termed as “soil profile”.A soil horizon is a layer of soil, approximately parallel to the soil surface,differing in properties and characteristics from adjacent layers below or above it.Practically, soil profile is an important tool for soilclassification which is applicable for thorough understanding of the soils.Five master horizons are recognized in soil profile and are designated usingcapital letters O, A, E, B and C.O Horizons:(Organic) It comprises of organic horizons that form above the mineral soil. Theyresult from litter derived from dead plants and animals. ‘O’ horizons usually occur in forestedareas and are generally absent in grassland regions.A - Horizon: It is the top most mineral horizon. It contains a strong mixture of decomposed(humified) organic matter, which tends to impart a darker color than that of the lower horizons.E - Horizon: It is an eluviated horizon. Clay and sesquioxides are invariably leached out, leavinga concentration of resistant minerals such as quartz. An ‘E’ horizon is generally lighter in colorthan the ‘A’ horizon and is found under ‘A’ horizon.“B” – Horizon : (Illuvial) The sub -surface ‘B’ horizons include layers in which illuviation ofmaterials has taken place from above and even from below. In humid regions, the B horizons arethe layers of maximum accumulation of materials such as sesquioxides and silicate clays. In aridand semi-arid regions Ca CO 3, Ca SO 4 and other salts may accumulate in the B horizon.‘C’ – Horizon: It is the unconsolidated material underlying the ‘Solum’ (A & B). It may or may notbe the same as the parent material from which the solum formed. The ‘C’ horizon is out side thezones of major biological activities and is generally little affected by the processes that formedthe horizons above it.‘R’- Layer : Underlying consolidated rock, with little evidence of weathering.SOIL PHYSICAL PROPERTIES: The physical properties include texture, structure, density, porosity,consistency, temperature, colour and water content.SOIL COMPONENTSMineral soil consists of four major components i.e., inorganic or mineral materials, organicmatter, water and air. In a representative loam surface soil, the solid mineral particles compriseabout 45% of the soil volume and organic matter 5%. At optimum moisture for plant growth, thepore space is divided roughly in half, 25 %, of volume being water space and 25 % air. Theproportions of air and water are subjected to rapid and great fluctuations.Mineral Matter: The Inorganic portion of soils is quite variable in size andcomposition. It is composed of small rock fragments and minerals of various kinds.Rock Fragments2.0 - 75.0 mm - gravel or pebblesSoil Particles0.2 - 2.0mm - sand (gritty)0.02 - 0.2mm - fine sand (gritty)0.002 - 0.02mm - silt (powdery)< 0.002mm - clay (sticky)The proportion of different sized particles (texture) determines the nutrient supplyingpower of the soil, considerably.SOIL TEXTURE : Soil texture may be defined as the relative proportion of particles of varioussizes ( Soil separates / Mechanical fractions ) such as sand, silt and clay. It is almost a permanentproperty of the soil and may change slowly with time.SOIL TEXTURAL CLASSES: Textural names are given to the soils based on each of the threesoil separates – sand, silt and clay. Soils that are preponderantly clay are called CLAY; thosewith high silt content are SILT and those with high sand percentage are SAND. Three broadand fundamental groups of soil textural classes are recognized: SANDS, LOAMS and CLAYS.

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Soil Structure may be defined as ‘the arrangement of primary particles (sand, silt andclay), secondary particles (aggregates) and voids (pores) in to a certain definite pattern underfield conditions’.Granular and crumb structures are characteristic of many surface soils (A horizon) particularlythose high in organic matter. They are best suited for growing crops. This structure is invariably subjected to management practices.

Governs the water and air permeability in to soils.Influences water holding capacity, soil-water relationship and growth ofmicroorganisms.Influences availability of plant nutrients.SOIL COLOURSoil color is one of the obvious characteristics of soil and is frequently used to describesoil, than any other. Soil color, as such, does not have any influence on plant growth.Humus – brown or dark brown.Iron oxides – red, rust – brown, or yellow depending upon degree of hydration.Quartz Lime stones – whiteSOIL REACTIONThe soil reaction describes the degree of acidity or alkalinity of a soil.The pH value represents the amount of free or active acidity and not thetotal acidity. the pH value ranges from 0 to 14 where pH value of 0represents the highest limit of active acidity; pH ‘7’ represents neutrality and pH‘14’ represents the highest degree of alkalinity or basicity.Classification of soils based on pH:Based on the pH value of soil solution, the soils have been classifiedinto the following categories.pH Range Category (Rating)< 4.5 Extremely acidic4.5 – 5.0 Very strongly acidic5.1 – 5.5 Strongly acidic5.6 – 6.0 Medium acidic6.1 – 6.5 Slightly acidic6.6 – 7.5 Neutral7.5 – 7.8 Mildly alkaline

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7.9 – 8.4 Moderately alkaline8.5 – 9.0 Strongly alkaline> 9.1 Very strongly alkalineImportance of soil pH on nutrient availability of plant nutrientsSoilreaction is the important factor which governs the availability of variousnutrients by influencing the soil properties like physical, chemical and biologicaletc. Bacteria and actinomycetes prefer near neutral to slightly alkalinereaction (pH 6.5 – 8.0).Fungi work satisfactorily at all pH ranges.nitRogen and Phosphorus availability is high in the neutral pH range. The availability of micronutrients like zinc, iron, copper andmanganese are more in the acidic range.SOIL MOISTURE CONSTANTSSoil moisture constants are expressed in terms of the energy with which the water is held atthat moisture cont ent and the relationship is a continuous function with out break.Soil moisture constant Soil moisture potentialOven dry soil -10,000 barsAir dry soil -1,000 barsHygroscopic coefficient -31 barsWilting coefficient -15 barsField capacity -1/3 barsSaturation Almost “O”SATURATION :Saturation water content is the amount of moisture present, when all the poresare filled with water.FIELD CAPACITY:After heavy rain or irrigation to the soil the water drains off rapidly for the firstfew hours and then starts to drain slowly. After two or three days, this rapid movementbecomes slow and negligible later. The soil is said to be at field capacity. At thiscondition water moves out of macro pores and air occupies their places. The micro poresare still filled with water, which is available to plants. But generally 1/3 bartension is frequently used to describe field capacity.WILTING POINT: (wilting coefficient or Permanent wilting percentage):It is the soil moisture content at which plants show wilting symptoms and can’trecoup or recover even though it is kept in humid chamber. Sometimes, plants exhibit wilting symptoms but recover withthe addition of water or when placed in humid chamber. The water content at thiscondition is called the temporary wilting point.Available water : Water held by soil at potential ranging between -15 bars to -1/3 bars, isconsidered as plant available water.SOIL BIOLOGYThe soil is teeming with millions of living organisms which make it a living and a dynamicsystem. The organisms in the soil, not only help in development of soils but carryout a number oftransformations facilitating the availability of nutrients to the plants.

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Benefits of soil organismsOrganic matter decomposition Nitrogen fixationSolubilisation of plant nutrientsProduction of soil enzymes, growth promoting substances and antibioticsProtect plant roots from invasion by soil parasites and pathogens.IMPORTANCE OF SOIL ORGANIC MATTER / HUMUSInfluence of Humus / Organic matter on soil physical, biological and chemicalproperties.1 Imparts dark color to soils2 Supplies polysaccharides for binding soil particles for formation of aggregates (genesis ofgood soil structure)3 Increases infiltration rate of water and provides better drainage4 Increases water holding capacity5 Reduces plasticity, cohesion, stickiness etc in clay soils6 Reduces bulk density, there by influence porosity favorably7 Through granulation, reduces wind erosion losses8 Provides mulching (raw organic matter) and lowers soil temperature during summer.Acts as an insulator and retards heat movement between atmosphere and soil9 Reduces alkalinity in soils by releasing organic acids and CO2

10 With high adsorption capacity, it accounts for 30 -90% of the adsorbing power of mineralsoils ( Carboxylic group – 54% ; phenolic & enolic groups – 36%; imide group – 10%)11 Acts as a buffering agent and reduces the likelihood damage from acids and alkalis.12 With its solubilising effect, increses the availability of nutrients13 Acts as a store house for nutrients. Organic matter is the source of 90-95% of nitrogen inunfertilized soils. Also supplies available ‘P’, ‘S’ and micro nutrients like Fe, Mn, Cu andZn etc.,14 Adsorbs temporarily the heavy metal pollutants and cleans the contaminated waters.15 Serves as a source of energy for macro and micro organisms in soils and helps inperforming various beneficial functions in soils (N - fixation, mineralisation etc.)16 Acts as a chelate and increases the availability of micro nutrients17 Various organic substances like vitamins, antibiotics and growth promoting substancesnamely auxins are produced by different micro organisms during decomposition oforganic matter. Also some fungi-toxins are produced to control diseases.Soil Fertility and Productivity

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A productive soil has to be fertile, while a fertile soil may or may not be productive. A soil is said to be fertile if it contains and can supply all the thirteen essential plant nutrients (N, P, K, Ca, Mg, S, Fe, Mn, Zn, Cu, B, Mo, Cl) in adequate amounts needed by the growing crop plants. However, for good plant growth and productivity also needed are adequate amounts of water and air in soil. Furthermore for release of several plant nutrients a good activity of many soil microorganisms is also required. Thus for a soil to be productive good soil physical and microbiological properties are also needed in addition to it being fertile. Also a soil to be productive must also needed in addition to it being fertile. Also a soil to be productive must also be safe from natural hazards such as floods and associated erosion.Problem soilsProblem soils are the soils whose productivity is lowered due to inherentunfavourable soil conditions viz., salt content and soil reaction.saline soils : Saline soils contain neutral soluble salts ofchlorides and sulfates of sodium, calcium and magnesium.Reclamation of salt affected soils: Leaching : The main objective in reclamation of these soils is to leach thesalts below the root zone (hence, drainage system should be installed ifnecessary). Leaching requirement (LR) has been defined as that fraction of waterthat must be leached through the root zone to control soil salinity at a specifiedlevel.This is achieved by flooding and draining.alkali or sodic soils: soils with pHmore than 8.5 Acid soils :soils with pH < 6.5 can also be categorized as acidic soils.

Plant nutrition: Plant nutrition is defined as the supply and absorption of chemicalcompounds required for plant growth and metabolism. It is the process ofabsorption and utilization of essential elements for plant growth and reproduction.Nutrient: Nutrient may be defined as the chemical compound or ion required by anorganism. The mechanism by which the nutrients are converted to cellular materialor used for energetic purposes are known as metabolic processes.Essential Plant Nutrients Arnon and Stout (1939) suggested the following criteria for the essentiality of a plant nutrient: (i) A deficiency of the essential element makes it impossible for a plant to complete its life cycle, (ii) The deficiency is specific to particular essential element, (iii) An essential element is directly involved in the nutrition of the plant. Based on the these criteria 16 elements have been so far considered as essential plant nutrients. These are : C, H, O, N, P, K, Ca, Mg, S, Fe, Mn, Zn, Cu, B, Mo and Cl. Of these 3 elements (CHO) are taken from air and soil water, while the rest 13 are taken from the soil through soil solution.Classification of nutrients

On the basis of the amounts of these nutrients taken by plants they are classified as: (i) macronutrients and (ii) micronutrients.

3.1.1 Macronutrients (taken up in large amounts, generally in kg per hectare). These can be further sub-divided as

(i) Primary nutrients (taken up in large amounts): N, P, K.

(ii) Secondary nutrients (taken up in lesser amounts than N,P and K) : Ca, Mg, S

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3.1.2. Micronutrients : These are taken up in very small amounts, generally expressed in g or mg per hectare, these include Fe, Mn, Zn, Cu, B, Mo, Cl.

Ionic forms in which taken up by plants, functions and deficiency symptoms of essential plant nutrients.

Nutrients(ionic forms)

Functions Deficiency symptoms

N (NH4+, NO3-) Synthesis of protein, component of chlorophyll, enzymes, nuclei acids

Light green colour of leaves, older leaves show the symptoms first.

P (H2PO4-, HPO4-) Component of ATP and ADP and hence involved in energy transfer in photosynthesis, helps in root development

Leaves show purplish to red coloration

K (K+) Control stomata opening for photosynthesis, neutralizes organic acids

Scorching and burning of leaf margins

Ca (Ca++) Component of cell wall, involved in cell division and cell growth, co-factor for enzymes

Failure in the development of terminal buds, dead spots in the mid-rib of leaves. In maize the tip of the new leaves may have a sticky material that causes them to adhere to one another

Mg (Mg++) Component of chlorophyll Light green veination in leaves, cupping of leaves

S (SO4-) Component of proteins – S containing amino acids cystine and methonine

Similarly to N deficiency but seen on top leaves as a contrast to N deficiency symptoms which first appear

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in lower leaves. In rapeseed mustard young leaves of S deficient plants become pale, chlorotic and cupped

Zn (Zn++) Formation of auxins & chloroplasts; carbohydrate metabolism

Stunted growth, pale to white coloration of young leaves (white bud disease of maize); browning and scorching of leaves (khaira disease of rice)

Nitrogenous fertilizers

A large number of fertilizers containing nitrogen are available. These can be broadly grouped into four classes, namely ammonium, nitrate, ammonium and nitrate and amide containing fertilizers. These are given in Table 4.

Table 4. Nitrogen content and other characteristics of nitrogenous fertilizers

Fertilizers Total N (%) Other nutrients (%)

Equivalent acidity/basicity(kg Ca/CO3)

Other characteristics

Ammonium fertilizers

Anhydrous ammonia

82.2 - 147 Marketed as compressed liquid gauge pressure –75 pounds/sqm at 50oF and 197 pounds/sqm at 100oF

Ammonium sulphate

20 24% S 107-110 Marketed in fine to medium fine crystals, non-hygroscopic

Ammonium chloride

26 - 128 Not widely used, manufactures in white, crystalline form, non-hygroscopie

Nitrate fertilizers

Sodium nitrate16 20% Na 29 Naturally

occurring chemical. In early 20th

century it was prime source of nitrogen. Very hygroscopic, marketed in grey

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granules

Calcium nitrate15 19% Ca 21 Available in

white crystalline highly hygroscopic and not marketed in India

Ammonium and nitrate fertilizer

Ammonium sulphate nitrate

26

(19.25% NH4& 67.5% NO3)

5-6% S 93 Slightly hygroscopic

Calcium ammonium nitrate

25

(12.5% NH4 & 12.5% NO3)

81% Ca Neutral Slightly hygroscopic but excellent handling qualities

Amide fertilizers

Urea46 - 80 Most popular,

cheap. Free flowing fertilizer. It comes in white prilled form

Calcium cynamid

20 54% Ca - It is no longer produced

Bulky organic manures: These include FYM, rural compost, town compost, biogas compost, night soil, sludge, green manures and other bulky sources of organic matter.

6.5.2. Concentrated organic manures: These include oil cakes, blood meal, fish manure, meat meal and wool waste.

The application of organic manure improves the physical, chemical and biological conditions of soils besides providing plant nutrients. The humus of organic manures is a colloidal material with negative electric charge and is coagulated with cations. With organic manures soil particles form granules. Soil with more granules is less sticky, have a better permeability, and greater water holding capacity. Organic manures also increase buffering capacity of soils. Soils with higher buffering capacity are capable of regulating the soil pH. Thus addition of organic manures create a good environment for crop growth.

Composition of

Phosphorus (P2O5)

(%)

Nitrogen

(%)

Calcium (CaO)

Magne-sium

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phosphatic fertilizers Fertilizers

(%) (MgO) (%)

Total Available

Water soluble

Total

Ammoniacal

Nitrate

Amide

Single super phosphate

18-20 16.5-17

16 - - - - 25-30 0.5

Triple super phosphate

46 43 42.5 - - - - 17-20 0.5

Diammonium phosphate

46 41 41 18 18 - - - -

Ammonium phosphate sulphate

(16:20:0)

20 19.5 19.5 16 16 - - - -

Ammonium phosphate sulphate (20+2

20 20 17 20 18 2 - - -

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0+0)

Ammonium phosphate sulphate nitrate

20 20 17 20 17 3 - - -

Urea ammonium phosphate (28:28:0)

28 28 25,2 28 9 - 19 - -

Urea ammonium

24 24 20.4 24 7.5 - 16.5 - -

phosphate (24:24:0)

Nitro-phosphate (20:20:0)

20 20 5.4 - - - - - -

Udaipur rock phosphate

20-35

- - - - - - - -

Mussoorie rock phosphate

23-34

- - - - - - - -

Jhabua rock phosphate

31-38

- - - - - - - -

Soil Fertility Evaluation and Fertilizer Recommendations

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The selection of the proper rate of plant nutrients is influenced by a knowledge of the nutrient requirement of the crop and the nutrient-supplying power of the soil on which the crop is to be grown. The techniques commonly employed to assess the fertility status of a soil are : (i) nutrient-deficiency symptoms of plants, (ii) analyses of tissue from plants growing on the soil, (iii) biological tests in which the growth of either higher plants or certain micro-organisms is used as a measure of soil fertility and (iv) chemical soil tests.Nutrient-deficiency symptoms of plantsTissue tests: Rapid tests for the determination of nutrient elements in the plant sap of fresh tissue have found an important place in the diagnosis of the needs of growing plants.Total analysis: Total analysis is performed on the whole plant or on plant parts. Precise analytical techniques are used for measurement of the various elements after the plant material is dried, ground, and ashed.Biological tests

Biofertilizers

The bio-inoculants or preparations containing microorganisms that supply nutrients especially nitrogen and phosphorus are known as biofertilizers. On the basis of nutrients supply, these are broadly classified in four groups: (i) nitrogen fixers, (ii) phosphorus solubilizers, (iii) plant growth promoters (iv) organic matter decomposers.

14.1. Nitrogen fixers Certain micro-organisms like bacteria and blue-green algae have the ability to use atmospheric nitrogen and made available this nutrient to the crop plants. Some of these ‘nitrogen fixers’ like rhizobia are obligate symbionts in leguminous plants (Tilak and Saxena, 1996), while others colonize root zones and fix nitrogen with loose association with plants. A very important bacterium of the latter category is Azospirillum, which was discovered by a Brazilian scientist in the mid 1970s. The third group includes free-living nitrogen fixers such as blue-green algae and Azotobacter.

14.1.1. Legume Inoculants : The most widely used biofertilizer for pulse crops is Rhizobium which colonizes the roots of specific legumes to form turmour like growth called root nodules. The Rhizobium-legume association can fix up to 100-200 kg N/ha in one crop season and in certain situations can leave behind substantial nitrogen for the following crop.

The range of nitrogen fixed per hectare per year by different legumes is 100-150 kg for clover, 53-85 kg for cowpea, 68-200 kg for pigeonpea, 46 kg for peas, 35-106 kg for lentil, 112-152 kg for groundnut, 49-130 kg for soybean, 50-55 kg for mungbean and 37-196 kg for guar (Tilak, 1998). Stem nodulating legumes such as Sesbania rostrata, Aeschynomene sp. and Neptunia oleracea have become popular in improving soil fertility. The N-fixing bacteria associated with such stem nodulating legumes belong to Azorhizobium, a fast growing species of Rhizobium. The N-acumulating potential of stem nodulating legumes under flooded conditions ranges from 40-200 kg N/ha (Rao et al., 1994).

14.1.2. Azotobacter and Azospirillum : The beneficial effects of Azotobacter on cereals, millets, vegetables, cotton and sugarcane under both irrigated and dryland conditions have been well substantiated and documented. Application of this biofertilizer has been found to increase the yield of wheat, rice, pearlmillet and sorghum by 0-30% over control. Apart from nitrogen, this organism is also capable of producing antibacterial and antifungal compounds, hormones and siderophores (Tilak, 1993).

Azospirillum, an associative microareophilioc organism living in association with diverse group of plants consists of 5 species namely, A. brasilense, A. lipoferum, A. amazonense, A.

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halopreference and A. irkense. Associative nitrogen fixation, capability to produce plant growth promoting antifungal, antibacterial substances and their effect on root morphology are the principal mechanisms responsible for the increase in crop yields (Tilak and Annapurna, 1993). Inoculation with Azospirillum results in enhanced assimilation of mineral nutrients (N, P, K, Rb+, Fe2+), and offers resistance to pathogens (Wani, 1990).

A new bacterium Herbaspirillum taxonomically closely related to Azospirillum has also been isolated from forage grasses (Indira and Bagyaraj, 1996). Acetobacter diazotrophicus is a saccharophilic bacterium and is associated with sugarcane, sweet sorghum and sweet potato. Reports from Brazil indicate that this bacterium fixes around 150-250 kg N/ha/year in case of sugarcane.

14.1.3. Blue-green algae : A judicious use of blue green algae could provide to the country’s entire rice acrease as much nitrogen as obtained from 15-17 lakh tonnes of urea. Methods have been developed for mass production of algal biofertilizers and it is becoming popular among the rice growers in many parts of the country (Ventakaraman and Tilak, 1990). Recent research has shown that algae also help to reduce soil alkalinity, and this opens up possibilities for bioreclamation of such inhospitable environments. This area is of particular relevance, because 7 million hectares of arable land in our country are salt affected.

14.1.4. Azolla : Azolla is known as a floating nitrogen factory in low land rice fields and in shallow fresh water bodies. The Azolla anabaena association use the energy from photosynthesis to fix atmospheric nitrogen amount to 100-150 kg/ha/year from about 40-60 tonnes of biomass (Singh, 1998). An integrated system of rice-Azolla-fish has been developed in China. We need to give greater thrust on this system.

Phosphate solubilizers

14.2.1. Phosphorus solubizing bacteria : Bacteria such as Pesudomonas and Bacillus excrete acids into the growth medium and hence solubilize bound phosphorus (Gaur, 1985). These organisms are quite useful in the utilization of rock phosphate with low content of P. Field experiments conducted with P-solubilizers like Aspergillus awamori, P. striata and B. polymyxa significantly increased the yields of various crops like wheat, rice, cowpea, etc. Use of rock phosphate with phosphate solubilizing bacteria resulted in a saving of 30 kg P2O5/ha (Gaur, 1985).

14.2.2. Mycorrhizae : Recent research has shown the possibility of domesticating mycorrhizae in agricultural systems. They also ubiquitous in geographic distribution occurring with plants growing in all environmental conditions. VA-mycorrhizal fungi occur over a broad ecological range from aquatic to desert environments. These fungi belonging to the genera Glomus, Gigaspora, Acaulospora, Entrophosphora, Modicella, Sclerocystis and are obligate symbionts. These fungi have been cultured on nutrient media using standard microbiological techniques. They are multiplied in the roots of host plants and the inoculum is prepared using infected roots and soil.

Crop responses to VAM inoculation are governed by soil type, host variety, VAM strains, temperature, moisture, cropping practices and soil management practices. The major constraint for using VAM has been the inability to produce ‘clean pure’ inoculum on large scale. Field trials indicated that VAM inoculation increased yields at certain locations and the response varied from soil type, soil fertility particularly with available P status of soil and VAM culture (Tilak, 1993). Mycorrhizal fungi assists in the uptake of phosphorus and trace metals and positively influences water and nutrient status via hormonal influences. However, lack of suitable inoculum production technology is the major limitation for the commercial exploitation of this system.

14.3. Plant growth promoting Rhizobacteria

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A group of rhizosphere bacteria (rhizobacteria) that exerts a beneficial effect on plant growth is referred to as Plant Growth Promoting Rhizobacteria or PGPR (Schroth and Hancock, 1981). PGPR belongs to several genera, namely, Actinoplanes, Agrobacterium, Alcaligenes, Amorphosporangium, Arthrobacter, Azotobacter, Bacillus, Bradyrhizobium, Cellulomonas, Enterobacter, Erwinia, Flavobacterium, Pseudomonas, Rhizobium, Streptomyces and Zanthomonas (Weller, 1988). Bacillus sp. are appealing candidates as PGPR because of their endospore producing ability which make them ideal inoculants for dry areas. Currently Pseudomonas spp. are receiving much attention as PGPR, because of their multiple effects on plant growth promotion.

PGPR are believed to improve plant growth by colonizing the root system and pre-emptying the establishment of suppressing Deleterious Rhizosphere Micro Organisms (DRMO) on the root (Schroth and Hancock, 1981). Inoculating planting material with PGPR presumably prevents or reduces the establishment of pathogens (Suslow, 1982). Production of siderophores is yet another molecular weight high affinity Fe+3 chelators that transport iron into bacterial cells and are responsible for increased plant growth by PGPR (Kloepper et al., 1980). Under Fe-deficient conditions, fluorescent Pseudomonas produce yellow-green fluorescent siderophore-iron complex (Hohnadel and Meyer, 1986) which creates an iron deficient environment deleterious to fungal growth.

Integrated Nutrient Management (INM)

The concept of INM is the rationalization of plant nutrient management in order to upgrade the efficiency of plant nutrient supply to the crops through the adequate association of local and external plant nutrient sources accessible and affordable to the farmers resulting ultimately in higher productivity and income to the farmers. In INM, better management results in plant nutrient gains, which are reinvested in the plant nutrient cycle in order to gradually upgrade the plant nutrient capital on the farm (soil reserves, crop residues, manures etc.) in an economically justified, socially acceptable and ecofriendly manner. This should also increase the cash flow for the purchase of chemical fertilizer.

INM firstly operates at the field level, optimizing the stocks and flows of plant nutrients from the diverse sources in order to increase the uptake of plant nutrients by the crops, the agronomic and physiological efficiency and at the same time to reduce losses of plant nutrients from the soil.

At the farm level INM is the combination of plant nutrition practices and allocation of plant nutrient sources optimizing the flows of nutrients passing through the soil/crop/livestock system and increasing both the stock of plant nutrients in the system and income of the farmers. INM aims at the accumulation of the production capacity of the farmers through accurate and profitable investments in external plant nutrient sources and amendments, efficient processing and recycling of crop residues and onfarm organic wastes. An inventory has to be made for the entire farming system involving seed, irrigation, manure, residues, animals on the farm etc. Only a careful periodic study of the inventory permits the proper implementation of INM.

The concept of INM can then be extended to the entire village or a district or a state. This will then involve making of inventories beyond the cropped areas and should list the source and amount of irrigation water, its quality including plant nutrient content, sediments provided by floods, plant nutrients removed by cutting of trees, contribution of pasture land if any and loss

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of gains of nutrients by rains, floods and storms. When planned and proceed well, INM leads to the betterment of soils, pasture and forest lands animal stock, people and area as a whole.

15.1. Components of INM

The major components of INM are as follows:

15.1.1. Fertilizers: Fertilizers are concentrated source of one or more plant nutrients. The nutrient supply through fertilizers during 2004-2005 was 18.4 million tonnes consisting of 11.7, 4.6 and 2.1 million tonnes of N, P2O5 and K2O, respectively (FAI, 2005). In contrast, nutrient removal by crops was 8-10 million tonnes higher than nutrient addition through fertilizers. This gap needs to be bridged through organics and biofertilizers.

15.1.2. Organic manures: Among the organic manures, the most common is the compost/farmyard manure (FYM). Organic manures not only supply plant nutrients inbalanced proportion but also improve, physical and biological properties of soil and thus make the system sustainable.

15.1.3. Green manures: Green manuring with legumes has long been known to be beneficial for sustainable crop productivity. In several studies conducted in India green manure was able to replace 60 kg N/ha. A fertilized green manure crop would substitute more mineral fertilizer N than an unfertilized green manure crop (Sharma and Mittra, 1988). A wide variability in N substitution through green manuring to the order of 45-120 has been reported. However, most commonly observed N additions through an array of green manures are in the range of 40-60 kg N/ha.

15.1.4. Crop rotation: To overcome the ecological diseases of monoculture, the first solution that man found was the changing of crops from one to another or from one season to another. Even before the modern agriculture was established the farmer had discovered the restorative power of legumes. For example, Vigil as early as 70-19 BC advocated the application of legumes and indicated in the following passage.

“Or, changing the season, you will sow these yellow wheat, wherever before you have taken up joyful pulse, with resulting pods”.

Thus the key to successful crop rotation was a soil restorer legume such as beans (Vicia faba L.), clover, lupins (Lupinus album L.) and Vatch (Vicia savita L.). The famous English Norfold rotation popular in 18th Century in England was turnip, barley, clover and wheat in a 4 year sequence. Thomas Jefferson followed a 5 year rotation of wheat-corn/potato-pea (Pisum sativum L.) – rye (Secale cereals L.)/wheat-clover/buck wheat (Fagopynum esculentum Moench). Even today only 20% of the corn in the United States is grown in continuous monoculture, while the remaining 80% is grown in a 2 year rotation with soybean or in short (2-or-3 year rotation) with alfalfa, cotton, dry bean or other crop. The legumes restore soil fertility in many ways. Some of them are: (i) they fix atmospheric N2 and leave part of it in soil, (ii) their deeper tap root system absorbs moisture and nutrients from deeper soil layers and some of the nutrients absorbed are left in the root mass in the surface soil, (iii) improve soil permeability, (iv) lesser disease and pest problem and (v) better weed control.

15.1.5. Crop residues : Substantial amounts of crop residues are produced in India every year. Five major crops namely rice, wheat, sorghum, pearlmillet and maize alone yield approximately 225 MT straw/stover with an average composition of about 0.5% N, 0.5% P2O5 and 1.5% K2OSoil drainage : When rainfall intensity exceeds the infiltrability of soil or the amount of rainfallexceeds the storage capacity of soil, the excess water accumulates at the soil surface and may

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keep the soil under saturated condition for longer time.82Drainage means removal of excess water from surface or sub-surface of soil body bymeans of some water conveying devices.Excess water may be due to 1) over irrigation 2) accumulation of monsoon runoff in lowlying areas for want of an outlet and 3) seepage from reservoirs, canals and ditches.The drainage problem are two types : surface drainage problem and sub-surfacedrainage problems. Surface drainage problems arise in the flat areas of land that are subjectedto ponded water. Uneven land, low capacity of disposal channels, above ground level waterbodies are the chief causes for ponding of water in an area.The sub-surface drainage problems may arise due to low soil permeability, humid climate andrise of ground water causing development of a shallow water table.In case of surface drainage, water is removed directly from the land by land smoothing,land grading, bunding and ditching. Land surfaces are also reshaped to eliminate ponding and tocreate slopes so as to induce gravitational flow over land and channels to an outlet. The excesswater can also be diverted from the land by diversion ditches, dykes etc.Subsurface drainage refers to the outflow or artificial removal of excess water from with in thesoil, generally by lowering the water table or by preventing its rise, using mostly the artificialwater conveying devices. An underground net work can be created for facilitating sub surfacedrainage.A mole drainage system: It is created by pulling through the soil at the desired depth a pointedcylindrical plug about 7-10 cm in diameter. The compressed wall channel thus formed providesa mechanism for the removal of excess water. This is an easy system to install, but is easilyclogged after few years.A perforated plastic pipe can be laid underground using special equipment. Water moves in tothe plastic pipe through the perforations and can be channeled to an outlet ditch. About 90% ofthe underground drain systems being installed are of this type.A clay tile system made up individual clay pipe units 30-40 cm long can be installed in anopen ditch. The files are then covered with a thin layer of straw, manure or gravel and the ditch83is then refilled with soil. Tile drains were popular two decades ago, but high installation costsmake them less competitive than the perforated plastic systems.IMPORTANCE OF DRAINAGE1 Drainage is essential, as the crop growth will be drastically affected by continuous soilsaturation with water.2 Soil saturation may encourage certain diseases and parasites.3 Poor drainage leads to the development of salt affected soils.4 High water table may limit root penetration.5 Soil saturation stops the gaseous exchange causing oxygen deficiency and accumulationof CO2 to toxic levels in root zone.6 Wet soil requires more heat to warm up than dry soil, due to high specific heat of water,the growing season for winter crops is shortened in poorly drained soils.7 Under poor drainage conditions / anaerobic conditions many organic and inorganiccompounds will be reduced to toxic levels and inhibit crop growth.8 Denitrification occurs in anaerobic conditions.9 Some micronutrients will become unavailable.


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