identification and classification of problematic soils pres ented by kulbir singh gill associate...

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IDENTIFICATION AND CLASSIFICATION OF PROBLEMATIC SOILS Presented by Kulbir Singh Gill Associate Professor, Deptt. of Civil Engineering, GNDEC,Ludhiana ([email protected])

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  • Slide 1
  • IDENTIFICATION AND CLASSIFICATION OF PROBLEMATIC SOILS Pres ented by Kulbir Singh Gill Associate Professor, Deptt. of Civil Engineering, GNDEC,Ludhiana ([email protected])
  • Slide 2
  • F ORMATION OF S OIL Soil is formed either by physical weathering or by chemical weathering. Because of different processes of weathering,soils exhibit different characteristics. Physical weathered rock to some extent represents the parent rock mass,for instance sand and gravel. Where as chemically weathered rocks results in the formation totally different material such as clay. Needless to say that sands and gravels are considered to be the best material from civil engineering point of view. Except the situation where permeability is to be controlled. Clays shows huge volume change when exposed to moisture.
  • Slide 3
  • C ONTD . Soils are heterogenious in nature. Soils are also anisotropic. If the wind is the weathering agent,it results in aeoline deposits which are cohesion less in nature such as sands. If water is the agent for movement of weathered rock products, it results in the formation of alluvial deposit and their suitability as construction material is varying from poor to fair. Other deposit are glacial, marine, beach, etc. Residual deposits are the one which is not transported to farther distances. Suitability of any soil can be assessed based on its properties.
  • Slide 4
  • P ROPERTIES OF SOILS The soil properties include index and engineering properties. The index properties are specific gravity, void ratio, liquid limit, plastic limit, shrinkage limit, relative density, dry density, porosity, initial water content, grains size distribution etc. The engineering properties are shear strength, compressibility and permeability. Unlike other material, soil behavior is influenced by many factors such as mineralogy, water content, void ratio, soil structure, pore fluid characteristics (Ion concentration, valancy of ion, dielectric constant), temperature, drainage, condition, strain rate, aging etc
  • Slide 5
  • I DENTIFICATION AND C LASSIFICATION OF SOILS Beside the complexity of understanding soil, geotechnical engineers made their best efforts to group the soil based on its specific response to different environmental conditions Soil can be classified as highly compressible and soil of low compressibility, expansive & non expansive, sensitive & insensitive, high plastic & low plastic, very soft to stiff clay, loose and dense sand etc. In this note, the identification and classification of different soils are presented in order to classify the good and poor soil, otherwise called as Problematic soil.
  • Slide 6
  • L IQUID L IMIT Liquid limit values of soils may be described as low, intermediate, high very high or extra high plasticity as given below in Table. Plasticity Classified asLiquid limit (%) Low20 to 35 Intermediate35 to 50 High50 to 70 Very high70 to 90 Extra highOver 90
  • Slide 7
  • P LASTICITY I NDEX No uniform standard is adopted in classifying degree of plasticity of soils. However, the classification given below is approximately the one which is often used and hence is recommended Soil classified asPlasticity Index (%) Non Plastic0-5 Moderately Plastic5-16 Plastic16-35 Highly plasticOver 35
  • Slide 8
  • S HRINKAGE LIMIT Shrinkage limit of soil is an indication of not only the shrinkage potential of clays but also an indicative of swelling nature. Swelling and Shrinkage Classification based on Shrinkage Limit Classified as Shrinkage table / Swelling detail Shrinkage limit (%) Very Low
  • I DENTIFICATION OF EXPANSIVE SOILS S.NoDegree of expansion Liquid limit (%) Shrinkage limit (%) Plasticity index (%) 12341234 Very high High Medium Low 60-70 40-60 30-40 20-30 >30 20-30 10-20 35 20-35 10-20
  • I DENTIFICATION OF EXPANSIVE SOIL ON THE BASIS OF GSD S.NoDegree of expansion Clay fraction (%) Colloidal content (%) 1 Very high >28 2 High 20-28 3 Medium 12-2015-20 4 Low 0-12
  • C LASSIFICATION OF SENSITIVE SOILS Classification Sensitivity, S 1 Low sensitivity 2-4 Medium sensitivity 4-8 High sensitivity 8-16 Quick >16
  • Slide 29
  • C LASSIFICATION OF SOILS ON THE BASIS OF IN SITU TESTS Correlation between N and Denseness of Sand NDenseness 0-4Very Loose25 - 32 4-10Loose27 - 35 10-30Medium30 - 40 30-50Dense35 = 45 > 50Very Dense> 45
  • Slide 30
  • C ONTD. Correlation between N and q u NConsistencyq u (kN / m 2 ) 0 - 2Very Soft< 25 2 - 4Soft25 50 4 - 8Medium50 100 8 - 15Stiff100 200 15 30Very Stiff200 400 > 30Hard> 400
  • Slide 31
  • I DENTIFICATION OF DISPERSIVE SOILS Dispersion occurs in soils when the repulsive forces between clay particles exceed the attractive forces thus bringing about deflocculating so that in the presence of relatively pure water the particles repel each other to form colloidal suspensions. Dispersive soils have a moderate to high clay material content but there are no significant differences in the clay fractions of dispersive and non-dispersive soils, except that soils with less than 10% clay particles may not have enough colloids to support dispersive piping. Dispersive soils contain a higher content of dissolved sodium (up to 12%) in their pore water than ordinary soils.
  • Slide 32
  • C ONTD. The sodium adsorption ratio (SAR) is used to quantify the role of sodium where free salts are present in the pore water and is defined as: SAR= Na/ 0.5(Ca+Mg ) with units expressed in meq/litre of the saturated extract.. Gerber and Harmse (1987) considered an SAR value greater than 10 indicative of dispersive soils, between 6 and 10 as intermediate, and less than 6 as non-dispersive.
  • Slide 33
  • C ONTD. The presence of exchangeable sodium is the main chemical factor contributing towards dispersive behavior in soil. This is expressed in terms of the exchangeable sodium percentage (ESP): ESP= Exchangeable sodium x 100/cation exchange capacity. Where the units are given in meq/100 g of-dry clay.
  • Slide 34
  • C ONTD. Soils with ESP values above 15% are highly dispersive (Bell and Maud, 1994). Those with low cation exchange values (15 meq/100 g of clay) have been found to be completely non- dispersive at ESP values of 6% or below. Unfortunately, dispersive soils cannot be differentiated from non- dispersive soils by routine soil mechanics testing. Although a number of special tests have been used to recognize dispersive soils, no single test can be relied on completely to identify them (Bell and Maud, 1994). These can be divided into physical and chemical tests. The former include the crumb test, the dispersion or double hydrometer test, the modified hydrometer or turbidity ratio test and the pinhole test.
  • Slide 35
  • C ONTD. Serious piping damage to embankments and failures of earth dams have occurred when dispersive soils have been used in their construction (Bell and Maud, 1 994). Severe erosion damage also can form deep gullies on earth embankments after rainfall. In many areas where dispersive soils are found there is no economical alternative other than to use these soils for the construction of earth dams. However, experience indicates that if an earth dam is built with careful construction control and incorporates filters, then it should be safe enough even if it is constructed with dispersive soils.
  • Slide 36
  • COLLAPSIBLE SOIL Collapsible soils, which are sometimes referred to as metastable soils, are unsaturated soils that undergo a large volume change upon saturation. This volume change may or may not be the result of the application of additional load. Foundations that are constructed on such soils may undergo large and sudden settlement if and when the soil under them becomes saturated with an unanticipated supply of moisture. This moisture may come from several sources, such as (a) broken water pipelines, (b) leaky sewers, (c) drainage from reservoirs and swimming pools, (d) slow increase of groundwater, and so on. This type of settlement generally causes considerable structural damage. Hence identification of collapsing soils during field exploration is crucial.
  • Slide 37
  • C ONTD. The majority of naturally occurring collapsing soils are aeolin that is, wind- deposited sand and/or silts, such as loess, aeolic beaches, and volcanic dust deposits. These deposits have high void ratios and low unit weights and are cohesionless or only slightly cohesive. Loess deposits have silt-sized particles. The cohesion in loess may be the result of the presence of clay coatings around the silt-size particles, which holds them in a rather stable condition in an unsaturated state. In the United States, large parts of the Midwest and arid West have such types of deposit. Loess deposits are also found over 1 5%-20% of Europe and over large parts of China
  • Slide 38
  • R ELATION OF C OLLAPSE P OTENTIAL TO THE S EVERITY OF F OUNDATION P ROBLEMS Cp(%)Severity of problem 0-1No Trouble 1-5Moderate Trouble 5-10Trouble 10-20Severe Trouble > 20Very Severe Trouble
  • Slide 39
  • S UMMARY Stability of any civil engineering structures lies primarily with the response of soil under the influence of external loading. It is a must for any civil engineer to understand the type of soil and their engineering characteristics prior to the use of same for any applications. If there is no proper importance given to the soil before start of construction activities in the beginning itself, then the rectification of damage to the structure, because of soil movement, if any would be much higher than the cost of the project itself.
  • Slide 40
  • T HANKS