SOIL MECHANICS
Transcript of SOIL MECHANICS
Terzaghi Institute
GATE | IES | TNPSC | PSU | 9994102301, 9994165522
SOIL MECHANICS
Terzaghi Institute
GATE | IES | TNPSC | PSU | 9994102301, 9994165522
S No Chapter Name Page No
01 Soil Properties
02 Consistency of soil
03 Soil classification & Structure
04 Effective stress
05 Permeability
06 Seepage Analysis
07 Stress distribution
08 Compaction
09 Consolidation
10 Shear strength
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Unit I
PROPERTIES OF SOIL
Introduction
1) Disintegration of rock is called weathering
of rock. Weathering constitutes Soil.
Types of Weathering
a) Physical weathering
Due to change in temperature, running
water, roots of trees.
Constitutes cohesionless soil (like
sand, gravel, cobble, boulder)
b) Chemical weathering :
Due to Oxidation, Hydration,
Carbonation, Leaching.
Constitutes cohesive soil (like clay)
Types of Soil
a) Residual soil :
Rate of weathering is more than rate of
transportation. (Shallow depth)
b) Transported soil :
Rate of weathering is less than rate of
transportation.
It has great importance in geotechnical
engineering.
Table 1.1 Sources of Transportation
Source Term
Water :
Running Water
Lake (Still water)
Sea
Alluvial
Lacustrine
Marine/Marl
Gravity Colluvial, Talus
Air Aeoline, Dune, Loess
Ice (glacier) Drift, glacial drift
Cumulose – Organic Soil (Peat & Muck)
– Soil produced by decomposition of
vegetation under excess water
Bentonite – Soil formed from volcanic
origin (highly porous – Void ratio = 5)
Black cotton soil – It is the soil having
very high swelling & shrinkage property. The
most suitable foundation is under reamed pile.
Application of Soil Mechanics
a) Designing of foundation (shallow or
deep)
b) Designing of earthen dams
c) Designing of retaining walls
d) Designing of underground
structures
e) Designing of rigid pavements
f) Designing of canals
Table 1.2 Types of soil based on the size
Type of Soil Size
Fine grained Soil
Clay
Silt
Fine sand
< 2μ
2 μ to 75 μ
75 μ to 425 μ
Medium sand 425μ to 2mm
Coarse sand 2mm to 4.75mm
Gravel
Fine Gravel
Coarse Gravel
4.75mm to 20mm
20mm to 80mm
Cobble 80mm to 300mm
Boulder >300mm
Black cotton soils
These are residual deposits formed
from basalt or trap Rocks.
Suitable for growing cotton.
Black cotton soils are clays at high
plasticity.
Shear strength is very low.
They have high shrinkage and swelling
characteristics due to the clay mineral
(Montmorillonite)
They are highly compressible and have
very low bearing capacity.
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Occurs in large part of central India
and a portion of south India.
Under Reamed piles are suitable
foundations for this type of soil.
Alluvial Soils:
Occurs in large parts of Northern India
(Indogangetic plains) and Brahmaputra
plains and some places in peninsular
India.
Alluvial deposits are generally of low
density and are liable to liquefaction in
Earthquake prone areas.
They are well graded and can be
compacted to a high dry density. These
have generally high shear strength.
Lateritic Soils
Formed by the decomposition of rock,
removal of bases and silica and
accumulation of Iron Oxide and
Aluminum Oxide.
These are residual soils formed from
basalt.
Lateritic soils are soft and can be cut with
a knife when wet, hardens with passage of
time.
Muck- It denotes a mixture of fine soil
particles and highly decomposed organic
matter. It is black in colour and of
extremely soft consistency. It cannot be
used for engineering works. The organic
matter is in an advanced stage of
decomposition.
Cumulose- peat + Muck
Hardpans are types of soil that after great
resistance to the drilling tools during Soil
Exploration.
They are dense, well graded, cohesive
aggregates of mineral.
Hardpans do not disintegrate when
submerged in water.
Humus→ Dark, Brown, Organic
amorphous (shapeless) earth of the top
soil. It consists of partly decomposed
vegetal matter.
Loam→ Mixture of sand, silt and clay.
Marl→ Stiff, marine calcareous clay of
Greenish colour.
Moorum→ The word moorum is derived
from a Tamil word meaning powdered
rock.
Consists of small pieces of disintegrated
rock (or) shale with (or) without Boulders.
Varved clays→ Sedimentary deposits.
Alternate thin layers of silt and clay
(layers less than 1cm each)
Peat→ It is an organic soil having fibrous
aggregates of macroscopic and
microscopic particles. It is formed from
vegetal matter under conditions of excess
moisture, such as in swamps. It is highly
compressible and not suitable for
foundations.
Three Phase Diagram
1.2 Technical Terms
1. Void ratio (e)
• e = 𝑽𝒐𝒍.𝒐𝒇 𝒗𝒐𝒊𝒅𝒔
𝑽𝒐𝒍.𝒐𝒇𝒔𝒐𝒍𝒊𝒅𝒔 =
e = 𝑽𝒗
𝑽𝒔
• Range : Can have any value greater than
0
Table 1.3 Range of void ratio
Void ratio Range
e > 1
e < 1
e = 1
Fig : 1.1 Three phase diagram
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2. Porosity (n):
• n = 𝑽𝒐𝒍. 𝒐𝒇 𝒗𝒐𝒊𝒅𝒔
𝑽𝒐𝒍.𝒐𝒇 𝒔𝒐𝒊𝒍 𝒎𝒂𝒔𝒔 x 100
n = 𝑽𝒗
𝑽 x 100
Range: 0 < n < 100%.
• Relation between 'n' and 'e' is
en =
1+ e
3. Degree of saturation (Sr):
• Sr = 𝐕𝐨𝐥𝐮𝐦𝐞 𝐨𝐟 𝐰𝐚𝐭𝐞𝐫
𝐕𝐨𝐥𝐮𝐦𝐞 𝐨𝐟 𝐯𝐨𝐢𝐝𝐬 𝑿 100
Sr = 𝐕𝐰
𝐕𝐯 𝐗 𝟏𝟎𝟎
• Range : 0 ≤ Sr ≤ 1
Table 1.4 Sr Range
Soil type Degree of
saturation
Fully saturated soil
mass 1
Dry soil mass 0
4. Air content (ac)
• ac= 𝑉𝑎
𝑉𝑣
• Range : 0 ≤ ac ≤ 1
• ac + sr = 1
Table 1.5
Soil type Air content
Fully saturated soil mass 0
Dry soil mass 1
5. Percentage of air voids (ηa)
ηa= 𝑉𝑎
𝑉x 100 Range: 0 ≤ ηa< 1
Table 1.6
Soil type Percentage of air
voids
Fully saturated soil
mass 0
Dry soil mass < 1 (ηa = ac x n)
6. Water content or moisture content:
• Wt.of water
w= ×100Wt.of solids
W
S
Ww = ×100
W | Range: w ≥ 0
7. Bulk unit weight of soil (𝜸𝒃) (Partially
saturated state)
γb = Total weight
Volume of soil mass =
WS+ Ww
V
8. Dry unit weight of soil (𝜸𝒅)
γd = Weight of solids
Volume of soil mass =
Wd(or)Ws
V
9. Unit weight of solids (𝜸𝒔)
γs = Weight of solids
Volume of Solids =
Ws
Vs
10. Saturated unit weight: (sat) (Fully
saturated state)
• It is bulk unit weight when soil is fully
saturated
• It is also equal to total weight of soil
when fully saturated per unit of total
volume.
sat = 𝑾𝒔𝒂𝒕
𝑽
11. Submerged unit weight (sub or )
• It is the submerged weight of soil
solids per unit of total volume of soil.
sub = sat - w
• It is based on Archimedes’ principle.
γs > γsat > γbulk > γd > γsub
12. Specific Gravity of soil solids or soil (G or
Gs)
S
W
γG =
γ
• For a given soil, G remains constant
• G = 2.65 (sand) and G = 2.7 (Clay)
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• G (true / absolute / specific gravity) if
voids are not considered at all.
Table 1.7 Apparent / Mass / Bulk specific
gravity of soil
Type of Soil (Gm) Bulk Specific gravity
Partially Saturated
soil
γb
γw
Dry soil γd
γw
Saturated Soil γsat
γw
• Gm is not constant and Gm< G
15. Relative density or Density index:
R.D = I.D = 𝒆𝐦𝐚𝐱 − 𝒆𝒏𝒂𝒕
𝒆𝐦𝐚𝐱 − 𝒆𝒎𝒊𝒏 x 100%
emax = soil in loosest state
emin = soil in densest state
enat = voids in natural state
min
min mad x
d d
d
1 1
1 1
γ γ
γ γ
R.D = ×100
Or
dmax d dmin
d dmax dmin
γ γ - γRD= ×
γ γ - γ
Table 1.7
Soil type Relative Density
Very loose 0 to 15%
Loose 15 to 35%
Medium 35 to 65%
Dense 65 to 85%
Very dense 85 to 100%
1.3. Some Important Relations
1) Gs.w = e.Sr
2) e = 𝑛
1−𝑛
3) n = 𝑒
1+𝑒
4) γb = γd(1 + w)
5) ηa = ac x n
6) ac + Sr= 1
7) ηa = ( 1 - Sr)n
8) γd = 𝐺𝑠 .γ𝑤
1+𝑒
9) γd = (1− 𝜂𝑎)𝛾𝑤𝐺
1+𝑤.𝐺
10) γb= γd+ Sr (γsat- γd)
11) γb = (𝐺𝑠+𝑆𝑟𝑒
1+𝑒)γw
12) γsat = (𝐺𝑠+𝑒
1+𝑒)γw
13) γsub = γsat - γw
14) γsub = (𝐺𝑠−1
1+𝑒)γw
15) Critical hydraulic gradient
ic = 𝑮𝒔−𝟏
𝟏+𝒆 (i.e) ic =
𝜸𝒔𝒖𝒃
𝜸𝒘
16) Actual hydraulic gradient,
ia = ∆𝑯
𝑳𝒔 =
𝑯𝟏− 𝑯𝟐
𝑳𝒔
• ia should not be less than ic
• If ia≥ ic (Sand boiling occurs)
• Safe Hydraulic gradient = 𝑖𝑐
𝐹.𝑂.𝑆
Sand Boiling (Quick Condition)
It is not a type of sand but a hydraulic
condition in which human beings and other
objects are not sucked in.
It occurs only in cohesion less soil,
especially in fine sand and not in clay soil.
Sand boiling does not takes place in soils
having high permeability (eg. Coarse sand
and gravel)
Sand boiling occurs only when the effective
pressure in the soil becomes zero. σ' = 0
Downward soil pressure due to self-weight –
upward seepage pressure = 0
Fig : 1.2
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Actual hydraulic gradient is dependent on
head of water in upstream, downstream and
length of seepage.
Critical hydraulic gradient is dependent
only on soil properties.
To prevent Sand Boiling
Increase the seepage length by providing
sheet piles.
Provide extra head of water on
downstream side.
WATER CONTENT DETERMINATION
Water content of soil is an important
soil parameter which significantly
influences the behavior of soil,
particularly of cohesive soils.
It is important to quantify the state of
soil immediately after it is received in
the testing laboratory and just prior to
commencing any other tests (example,
shear strength test compression test
etc.)
Water content and unit weight changes
during transportation and storage.
Hence it is important to determine it
before carrying out any other tests.
The water content of a soil sample can
be determined by any one of the
following methods:
(1) Oven Drying method
(2) Torsion Balance method
(3) Pycnometer ·method
(4) Sand Bath method
(5) Alcohol method
(6) Calcium Carbide method
(7) Radiation method
(1) Oven drying method
The oven drying method is a standard
laboratory method. This is a very
accurate method.
The soil sample is taken in a small,
non-corrodible, airtight container.
The soil sample in container is then
dried at a temperature of 105 - 110°C
for 24 hrs in laboratory. Above 110°C,
water of crystallization may be lost
Water of crystallization is the water in
molecular structure.
For soils containing significant amount
of organic matter a temperature of 60°
to 80°C is recommended. At higher
temperature, gypsum loses its water of
crystallization and the organic soils
tend to decompose and get oxidized.
w 2 3
w 3 1
W W WWater content
W W W
W1 = wt of container
W2 = wt of container + wt of moist soil
W3 = wt of container + wt of dry soil
(2) Torsion Balance Method
The infra-red lamp and torsion balance
moisture meter is used for rapid and
accurate determination of the water
content. The equipment has two main
parts:
(i) The infra-red lamp, and
(ii) The torsion balance.
Since drying and weighing occur
simultaneously, the method is useful
for soils which quickly re-absorb
moisture after drying.
(3) Pycnometer method
A pycnometer is a glass jar of about 1
litre capacity and fitted with a brass
conical cap by means of a screw-type
cover. The cap has a small hole of 6
mm-diameter at its apex.
The pycnometer method for the
determination of water content can be
used only if the specific gravity of
solid (G) particles is known.
First, the weight of the empty
pycnometer is determined (W1) in the
dry condition. Then the sample of
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moist soil is placed in the pycnometer
and its weight with the soil is
determined (W2).
The remaining volume of the
pycnometer is then gradually filled
with distilled water or kerosene. The
entrapped air should be removed either
by gentle heating and vigorous shaking
or by applying vacuum.
The weight of the pycnometer,
soil and water is obtained (W3)
carefully. Lastly, the bottle is emptied,
thoroughly cleaned and filled with
distilled water or kerosene, and its
weight taken (W1).
Ww = W2 – Ws
w 2 1
s s
W W WW 1
W W
s w
4 1 3 1 s
s w
W γW W W W W
G γ
3 4
s
s
W WW
G 1
2 1
3 4 s
s
W Ww 1
W W G
G 1
s2 1
3 4 s
G 1W Ww = 1
W W G
Removal of entrapped air is difficult
from cohesive soil. Hence this method
is more suited for cohesionless soil
(4) Sand Bath Method
Sand bath method is a field method for
the determination of water content.
This method is rapid, but not very
accurate.
A sand bath is a large, open vessel
containing sand filled to a depth of 3
cm or more.
The soil sample is taken in a tray. The
sample is crumbled and placed loosely
in the tray. A few pieces of white
paper are also placed on the sample.
The tray is weighed and the mass of
wet sample is obtained.
The tray is ·then placed on the sand-
bath. The sand bath is heated over a
stove. Drying takes about 20 to 60
minutes, depending upon the type of
soil.
During heating, the specimen is turned
with a palette knife. Overheating of
soil should be avoided. The white
paper turns brown when overheating
occurs.
The drying should be continued till the
sample attains a constant mass.
When drying is complete, the tray is
removed from the sand bath, cooled
and weighed. The water content is
determined as
w Final initial
w Final trav
W W W
W W W
(5) Calcium Carbide Method
This method of the determination of
water content makes use of the fact
that when water reacts with calcium
carbide (Ca C2) acetylene gas (C2 H2)
is produced.
CaC2 + H2O = C2 H2 + Ca (OH)2
The water content of the soil is
determined indirectly from the
pressure of the acetylene gas formed.
The instrument used is known as
moisture tester.
Fig : 1.3
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The pressure of the acetylene gas
produced acts on the diaphragm of the
moisture tester. The quantity of gas is
indicated on a pressure gauge. From
the calibrated scale-of the pressure
gauge, the water content (wt) based on
the total mass is determined. The water
content (w) based on the dry mass is
determined using the following
formula.
w wt
s t
W Ww
W W W
Ww = Wt × Ws + wt ×Ww
W w (1 – wt) = Ws × wt
w t
s t
W w
W 1 w
t
t
ww
1 w
= water content based on weight
of solid.
(6) Radiation Method
Radio-active isotopes are used for the
determination of water content of
soils. A device containing a radio-
active isotopes material, such as cobalt
60, is placed in a capsule It is then
lowered in a steel casing A, placed in a
bore hole as shown in Fig.
The steel casing has a small
opening on its one side through which
rays can come out. A detector is
placed inside another steel casing B,
which also has an opening facing that
in casing A.
Neutrons are emitted by the radio-
active material. The hydrogen atoms in
water of the soil cause scattering of
neutrons. As these neutrons strike with
the hydrogen atoms, they lose energy.
The loss of energy is
proportional to the quantity of water
present in the soil. The detector is
calibrated to give directly the water
content.
The method is extremely useful for the
determination of a soil in the in-situ
conditions. The method very carefully
used, as it may lead to radioactive
problem if proper shielding
precautions are not taken.
SPECIFIC GRAVITY OF SOLID
DETERMINATION (Gg)
Pycnometer Method
This method is same as pycnometer
method of water content determination
with the difference that here dry soil
sample is taken instead of moist soil
sample as was taken in water content
determination.
Fig 1.5
Wt of solid = (W2 – W1)
Wt of equivalent volume of water =
(W4 – W1) – (W3 – W2)
Fig : 1.4
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s
wt of solidG
wt of equivalent volume of water
2 1
s
4 1 3 2
W WG
W W W W
Sp. gravity values are generally
reported at 27°C.
If Gs T°C = Sp gravity at T°C [if test
temperature = T°]
Then o
sT C
os27
G unit weight of water at T CG
unit weight of water at 27 CC
MEASUREMENT OF UNIT WEIGHT
The Bulk Unit weight of the sample is
total weight per Unit Volume of soil
mass.
The weight of soil sample can be
determined to a high degree of
precision in comparison to the volume
of sample
The methods basically differ in
procedure for the measurement of the
Volume.
Dry unit weight can be determined
from the bulk unit weight by using the
formula.
1d
γγ
1 w
The following methods are generally used for
determination of Bulk unit weight.
(1) Core Cutter Method.
(2) Water Displacement Method.
(3) Sand Replacement Method
(4) Water Balloon Method.
(5) Radiation Method.
1. Core Cutter Method
It is a field method.
A core cutter of known volume 1000
cm3 is punched into ground and then
core containing soil is taken out of the
ground.
Weight of core with soil sample and
empty core is measured
A representative soil sample is taken
for water content measurement.
Bulk unit weight is calculated as
below.
2 1t
W Wγ
V
W2: Weight of core filled with soil.
W1: Weight of Empty core.
V: Volume of Core.
Further d is calculated from the t &
w (water content) value as:
td
γγ
1+w
This method is quite suitable for soft,
fine grained soils.
It cannot be used for stoney, gravelly
soils & dry soil.
This method is practicable only at the
places where the surface of the soil is
exposed and the cutter can be easily
driven.
2. Water Displacement Method
The volume of the specimen is
determined in this method by water
displacement. As the soil mass
disintegrates when it comes in contact
with water, the sample is coated with
paraffin wax to make it impervious.
A test specimen is trimmed to more or
less a regular shape and weighed. It is
then coated with a thin of paraffin wax
by dipping it in molten wax.
The specimen is allowed to cool and
weighed. The difference between the
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two observations is equal to the mass
of the paraffin.
The waxed specimen is then immersed
in a water displacement container. The
volume of the specimen is equal to the
volume of water which comes out of
the outflow tube.
The actual volume of the soil
specimen is less than the volume of the
waxed specimen.
The volume of the wax is determined
from the mass of the wax peeled off
from the specimen after the test and
the mass density of wax.
Now, 1
1
p
M MV V
Where,
V = volume of specimen
V1 = Volume of waxed specimen
M1 = mass of waxed specimen
M = mass of specimen
ρp = mass density of paraffin
(approximately 0.998 gm/m2)
A representative sample of the soil is
taken from the middle of specimen
for· the water content determination.
Once the mass, volume and the water
content of the specimen have been
determined, the bulk density and the
dry density are found.
3. Sand Replacement Method
This is a field method.
A small area is excavated, and the
excavated soil sample, is precisely
weighed.
A calibrated cylinder containing sand
is placed over the excavated area and
the pit is filled with the sand.
Volume of the pit is obtained from the
calibrated cylinder
The bulk unit weight is calculated.
A representative sample is tested for
water content.
γd is obtained from t & w.
It is suitable for gravelly sandy and dry
soil.
4. Water Balloon method
In this method, volume of the
excavated pit is obtained by covering
the hole with a plastic sheet and filling
it with water. Weight of excavated
sample is measured and γt, is
calculated.
5. Radiation Method
The bulk density of insitu soil can also
be determined using the radiation
method.
Radiation methods for determination
of bulk density of soil are quick and
convenient and are gaining popularity.
Note :
Oven drying method : Most accurate
method
Calcium carbide method: Quickest
method
Fig : 1.6
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SEDIMENTATION ANALYSIS
The soil particles less than 75 – μ size
can be further analyzed for the
distribution of the various grain-sizes
of the order of silt and clay by
'sedimentation analysis' or 'wet
analysis'.
The soil fraction is kept in suspension
in a liquid medium, usually water.
The particles descend at velocities
related to their sizes, among other
things.
The analysis is based on 'Stokes Law'.
As per this law, if a single sphere is
allowed to fall in an infinite liquid
medium without interference, its
velocity first increases under the
influence of gravity, but soon attains a
constant value.
This constant velocity, which is
maintained indefinitely unless the
boundary conditions change, is known
as the 'terminal velocity'.
The principle is obvious, coarser
particles tend to settle faster than finer
ones.
By Stokes' law the terminal velocity of
the spherical particle is given by
t 1γ γu
18μ
Stokes' Law is considered valid for
particle diameters ranging from 0.2 to
0 .002 mm.
For particle sizes greater than 0.2 mm
turbulent motion is set up and for
particle sizes smaller than 0.002 mm.
Brownian motion is set up. In both
these cases, Stokes’ law is not valid.
The limitations of sedimentation analysis,
based on Stokes’ law are as follows:
(i) The finer soil particles are never
perfectly spherical. Their shape is
plate-like or needle-like. However, the
particles are assumed to be spheres,
with equivalent diameters (the basis of
equivalence being the attainment of
the same terminal velocity as that in
the case of a perfect sphere.)
(ii) Stokes' law is applicable to a sphere
falling freely without any interference
in an infinite liquid medium.
The sedimentation analysis is
conducted in a one-litre jar, the depth
being finite the walls of the jar could
provide a source of interference to the
free fall of particles near it.
The fall of any particle may be
affected by the presence of adjacent
particles, thus the fall may not be
really free.
However, it is assumed that
the effect of these sources of
interference is insignificant if
suspension is prepared with about 50 g
of soil per litre of water.
(iii) All the soil grains may not have the
same specific gravity. However, an
average value is considered all right,
since the variation may be
insignificant in .the particles
constituting the fine fraction.
(iv) Particles constituting to fine soil
fraction may carry surface electric
charges, which have a tendency to
create ‘flocs’. Unless these flocs are
broken, the sizes calculated may be
those of the flocs. Flocs can be a
source of erroneous results.
A deflocculating agent, such
as sodium silicate, sodium oxalate, or
sodium hexametaphosphate, is used to
get over this difficulty.
The general procedure for sedimentation
analysis, which may be performed either with
the aid of a pipette or a hydrometer is as
follows:
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An appropriate quantity of' an oven-
dried soil sample, finer than 75–μ size,
is mixed with a known volume (V) of
distilled water in jar.
The sample is pretreated with an
oxidizing agent and an acid to remove
organic matter and calcium
compounds.
Addition of hydrogen peroxide on
heating would remove organic matter.
Treatment with 0.2 N hydrochloric
acid would remove· calcium
compounds.
Later, a deflocculating or a dispersing
agent such as sodium
hexametaphosphate is added to the
solution. The mixture is shaken
thoroughly by means of a mechanical
stirrer and the test is started keeping
the jar vertical.
The soil particles assumed to be
uniformly distributed throughout the
suspension. at the instant of
commencement of the test
PIPETTE METHOD
It is a laboratory method. A pipette
sedimentation jar and a number of
sampling bottles are necessary for the
test.
The method consists in drawing off 10
ml samples of soil suspension by
means of the sampling pipette from a
standard depth of 10 cm at various
time intervals after the start of
sedimentation.
The usual total time intervals at which
the samples are drawn are 30 s, 1 min,
2 min, 4 min, 8 min, 15 min, 30 min, 1
h, 2h, and 4 h from the start of
sedimentation.
The pipette should be inserted about
20 seconds prior to the chosen instant
and the process of sucking should not
take more than 20 seconds.
Each of the samples taken is
transferred ton sampling bottle and
dried in an oven.
The concentration of all sized particles are
present in a particular volume at time t = 0.
This concentration is equal to weight
of solid per cc in original soil
suspension = x.
If after time t sample is taken out in
pipette from height He, then all
particles having settling velocity
greater than He will have settled below
height He.
At this height at time t sample
collected will have the same
concentration of particles of settling
velocity less than eH
t as was there in
the original soil suspension.
If settling velocity of particles size (D)
= He/t then
% finer than D =
wt of solid per cc at
depth Heafter time t
wt of solid per cc in the
original suspension
As,
2
s w eγ γ D H
18μ t
Find ‘D’ from this formula corresponding to
various time ‘t’ and plot grain size distribution
curve.
Fig : 1.7
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In pipette method, sample is collected
from height He at various time intervals i.e. He
is fixed.
Note: Let there be 4-types of particles in the
sample. Let in the original soil suspension
before the start of sedimentation the
concentration of various particles be as shown
below.
Fig : 1.9
If particle has settling velocity greater
than He/t, then concentration of soil
suspension collected at height He will
be 600 g/l.
e
Thus,
%finer than size
concentration of sample
collected at time t from height H 100
concentration of soil from
original soil suspension
600100
650
If particle has size D. then % finer than size D
is 600
100650
.
Where D is given by 2
s weγ γ DH
t 18μ
HYDROMETER ANALYSIS
The hydrometer method differs from the
pipette analysis in that the weight is of solids
per ml in the suspension at the chosen depth at
chosen instants of time are obtained indirectly
by reading the specific gravity of the soil
suspension with the aid of a hydrometer.
Hydrometer is a device which is used
to measure the specific gravity of
liquids. However, for a soil suspension
the particles start settling down right
from the start and hence the unit
weight of the suspension varies from
top to bottom.
As time passes the hydrometer goes
down because weight of hydrometer is
balanced by the weight of liquid
displaced by hydrometer. As solid
concentration goes on reducing in
water, more amount of liquid has to be
displaced to .balance the weight of
hydrometer.
We have already discussed that % of finer than
D
ewt.of solid per cc at depth H
after time t
wt.of solid per cc in original
soil suspension
Where D is given by
Fig : 1.10 Hydrometer
Fig : 1.8
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Fig : 1.12
2
s w eγ γ D H
18μ t
Thus using hydrometer we have to measure
density of soil suspension at a depth He after
time t. Fig. (a) Shows the height He But due to
its own volume, insertion of hydrometer will
lead to displacement of liquid.
Fig 1.11
Thus, Point at A1 occupies the position A2. A2
is the centre of volume of hydrometer.
Vh = Volume of hydrometer
AJ = Area of Jar
h = length of bulb in hydrometer
Volume of bulb can be thought of as
the total volume of hydrometer.
Hydrometer measures density of soil
suspension at depth He which is given
by
h h1
1 j
V VhH H
2 2A A
h1
j
V1H H h
2 A
H will correspond to hydrometer reading Rh.
Thus He will be related to Rh . Hydrometer is
calibrated such that hR1 Sp
1000 gravity of
soil suspension at depth He
h
density of soil
R suspension at depth He1+ =
1000 density of water
h
density of immersed wt of solid per+
R water unit volume1+ =
1000 density of water
Note:
s s w w
s w
s w w s w s
s w
V γ V γDensity of soil suspension
V V
V V γ γ γ V
V V
s w s
w
s w
s s ww
s v s
w d
s
γ γ Vγ
V V
V γ γ= γ 1
V V γ
1γ W 1
G
Wd = wt of ·solid per unit volume of solution
s s w s s
s
1V γ γ immersed wt V γ 1
G
Immersed wt per unit volume
s s
s w s
V γ 11
V V G
hR immersed wt of solid/cc of solution1 1
1000 wt density of water
d
sh
w
1W 1
GR1 1
1000 γ
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h w s
d
s
R γ GW
1000 G 1
% finer than dWD 100
W
Where,
W = weight of solid per unit volume in original
soil suspension
% finer than
h w s
s
R γ G 100D
G 1 1000 W
h s w
s
R G γ%finer than D
G 1 10W
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Unit II
CONSISTENCY OF SOIL
2.1 Introduction
The term consistency denotes the degree of
firmness.
1) It represents the different physical states
such as
a) Liquid state
b) Very soft
c) Soft
d) Stiff
e) Very stiff
f) Semi solid or solid
2) The term consistency is mainly meant for
fine grained soils (less than 425 micron)
3) It has been developed by Mr.Atterberg in
1911.
4) Consistency of soil is expressed in
a) Atterberg Limit
b) Unconfined compressive strength of
clay (qu)
5) Atterberg limits
a) Liquid limit (LL)
b) Plastic Limit (PL)
c) Shrinkage Limit (SL)
2.2 Liquid Limit
a) It is the min. water content of fully
saturated soil mass on which the soil is in
liquid state having very low shear strength
(2.7 kPa) which is measurable.
Table 2.1 Dimensions of Groove
Apparatus Bottom
width
Top
width Depth
Casagrande
groove 2mm 11mm 8mm
ASTM
groove 2mm 13.6mm 10mm
b) There are three methods to determine
Liquid Limit in the lab
Casagrande L.L method
One point Method
Static cone penetrometer method (IS
2720 – 1970)
2.2.1 Casagrande Method Procedure
• Fine grained soil (dry state) passing
through IS 425 micron sieve is taken into
account
• The dry mass is about 120 gm
• A certain amount of water (say about 25%)
is added to dry soil.
• Soil paste is made and placed on the brass
cup of Casagrande apparatus.
• The Casagrande cup is lifted (1cm) and
dropped on the rubber pad with the help of
handle (Blow).
• The number of blows is counted till the
groove is closed (N1).
• The water content of the soil mass is
determined accurately (Say w1).
Fig : 2.2
Fig : 2.1
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Fig : 2.5
• The volume of the water content is
changed and the test is repeated.
• A number of test results are obtained.
• A graph is plotted in between number of
blow (log scale) on x axis and
corresponding water content on y axis
(ordinate).
• The graph such plotted is known as Flow
curve (st. line).
• The water content corresponding to 25
blows on the flow curve is known as liquid
limit.
• The slope of the flow curve is known as
flow index (If)
𝑰𝒇= tanθ = 𝒘𝟏− 𝒘𝟐
𝒍𝒐𝒈𝟏𝟎(𝑵𝟐𝑵𝟏
)
• Flow index is a measure of shear strength
of soil.
• If flow index is higher, shear strength will
be lesser.
• Both are indirectly proportional to each
other.
Note: Ifb > IfA (θ2 > θ1) then shear strength of B
is less than shear strength of A.
2.2.2 One Point Method
In one point method, only one trial is
conducted using casagrande apparatus and then
by mathematical relations.
Liquid limit (LL) = w [𝑵
𝟐𝟓]
𝟎.𝟏
2.2.3 Static Cone Penetrometer Method
In static cone penetrometer method, the water
content corresponding to 25mm penetration of
cone is called liquid limit.
2.3 Plastic Limit
• It is the water content of fully saturated
soil mass on which a thread of 3mm
diameter of soil starts crumbling while
rolling into a thread.
• The size of the soil grain should be less
than 425 micron
2.4 Shrinkage Limit
• It is an arbitrary limit (water content)
between semi solid and solid state of the
saturated soil mass.
• It is the lowest level of full saturation.
• It is the max. water content of the saturated
soil mass below which the volume of soil
mass does not change even though water
content of saturation is lowered.
• If saturated soil sample is taken and
allowed to dry up gradually, its volume
will go on reducing till a stage will come
after which the reduction in the soil water
will not result in further reduction in the
total volume of the soil sample.
• The water content corresponding to that
stage is known as shrinkage limit.
Fig : 2.6
Fig : 2.3
Fig : 2.4
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• The oven dried sample having volume Vd
and mass Md. Evidently, according to the
definition, volumes V2 and Vd are equal.
Now, mass of water in (a) = M1 –Md
Loss of water from (a) to (b) = (V1 − V2)ρw
Mass of water in (b) = (𝑀1 –𝑀𝑑)-(𝑉1 − 𝑉2)𝜌𝑤
ws = (M1 –Md)−(V1−V2)ρw
Mdx 100
ws = [w1 −(V1−V2)ρw
Md]x 100
𝒘𝒔 = [𝒘𝟏 −( 𝑽𝟏−𝑽𝟐)𝝆𝒘
𝑾𝒅] x 100
w1 = Water content of the original saturated
sample of volume V1
𝑉𝑑 = dry volume of the soil sample
𝑤𝑑 = dry weight of the soil sample
𝑀𝑑 = dry mass of the soil sample
2.5 Formulas
1. Degree Of Shrinkage
D.S = 𝑽𝟎−𝑽𝒅
𝑽𝟎 x 100%
Vo = Initial volume of soil mass
Vd = Dried volume of soil mass
Table 2.2 Quality of soil
D.S Quality of Soil
< 5 Good
5 – 10 Moderate
10 – 15 Poor
> 15 V. poor
2. Volumetric Shrinkage
V.S = 𝑽𝟎−𝑽𝒅
𝑽𝒅 x 100%
3. Shrinkage Ratio
S.R =
𝑽𝟎−𝑽𝒅𝑽𝒅
𝑳.𝑳 −𝑺.𝑳 (or) S.R =
𝜸𝒅
𝜸𝒘 = Gm
4. Plasticity Index
It indicates the plasticity of the soil
IP = L.L – P.L (or) WL - WP
For organic soil L.L and P.L both are
high, hence 𝐼𝑃 will be lower.
For clay if IP is high, then it is called
fat clay and if IP is low it is called lean
clay.
Table 2.3 Degree of Plasticity
IP Degree of Plasticity
-ve Non plastic
< 7 Low plastic
7 to 17 Medium plastic
> 17 Highly plastic
5. Liquidity Index
IL = 𝑤𝑛−𝑊𝑃
𝑤𝐿−𝑊𝑃 x100 % (or) IL =
𝒘𝒏−𝑾𝑷
𝑰𝑷 x100%
Wn - water content at natural state
Wp - water content at plastic limit
WL - water content at liquid limit
6. Consistency Index
IC = 𝒘𝑳−𝑾𝒏
𝑰𝑷
IL + IC = 1
Wn - Water content at natural state
Table 2.4 Range of IL and IC
IL IC Consistency
> 1 0 Liquid state
1 – 0.75 0 – 0.25 Very soft
0.75 - 0.5 0.25 – 0.5 Soft
0.5 – 0.25 0.5 – 0.75 Medium
0.25 – 0 0.75 - 1 Stiff
< 0 > 1 Semi solid (or) Solid
7. Toughness Index
IT = 𝑰𝑷
𝑰𝒇
Table 2.5
IT Soil type
0 – 3 For general soil
< 1 Crushable / friable soil at plastic limit
8. Activity Number
AC = 𝑰𝑷
% 𝑭𝒊𝒏𝒆𝒓 𝒕𝒉𝒂𝒏 𝟐 𝒎𝒊𝒄𝒓𝒐𝒏
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Table 2.6 Nature of soil
AC Nature of soil
< 0.75 Inactive
0.75 – 1.25 Normal
> 1.25 Active
9. Sensitivity of Clay
It indicates the loss of shear strength
without change in the water content.
St = 𝒒𝒖 (𝒖𝒏𝒅𝒊𝒔𝒕𝒖𝒓𝒃𝒆𝒅)
𝒒𝒖 (𝒓𝒆𝒎𝒐𝒖𝒍𝒅𝒆𝒅)
Table 2.7 Sensitivities of clay
St Nature
1 – 4 Normal
4 – 8 Sensitive
8 – 16 Extra sensitive
> 16 Quick condition
10. Shrinkage limit
s
m s
1 1W = -
G G
11. Specific Gravity
s1
= 1
Shrinkage limitShrinkage ratio
G
12. Thixotrophy
It is a property of soil due to which it
regains a part of original strength while
reorienting its grains in presence of
adsorbed water without the change in
water content in a disturbed condition.
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PRACTICE QUESTIONS
Q.1) A soil sample has a diameter of 38 mm
and a height of 76 mm. Its wet weight is 1.15
N. Upon drying, its weight reduced to 0.5 N,
Gs = 2.7. In the wet state the degree of
saturation and the water content of the soil
sample are.
a) 130% and 96%
b) 96% and 130%
c) 30% and 96%
d) 30% and 100%
Q.2) A soil has a bulk density of 22 kN/m3
and water content 10%. The dry density of
soil is
a) 18.6 kN/m3
b) 20.0 kN/m3
c) 22.0 kN/m3
d) 23.2 kN/m3
Q.3) Valid range for n, the percentage voids,
is
a) 0 < n < 100
b) 0 ≤ n ≤ 100
c) n > 0
d) n ≤ 0
Q.4) Select the correct statement
a) Unit weight of dry soil is greater than
unit weight of wet soil.
b) For dry soils, dry unit weight is less
than total unit weight.
c) Unit weight of soil increase due to
submergence in water.
d) Unit weight of soil decrease due to
submergence in water
Q.5) Varved clay is
a) A mixture of sand, silt, clay
b) A chemically bonded soil mixture
c) Alternate thin layers of silt and clay
d) Decomposed volcanic ash deposit
Q.6) A phenomenon involved in soil by
losing it strength due to remoulding and
increase in strength with passage of time is
called
a) Sensitivity
b) Thixotropy
c) Activity
d) Consistency index
Q.7) Inverse of Relative density of soil is
a)
max nat
max min
100%e e
e e
b)
max min
max nat
100%e e
e e
c)
nat max
max min
100%e e
e e
d)
max min
nat max
100%e e
e e
Q.8) Pick up the incorrect definition from
the following:
a) Ratio of the compressive strength of un-
confined undisturbed soil to that of
remoulded soil, is known as the sensitivity of
the soil sample
b) The rotation of soil particles into stable
state while remoulding, is known as the
thixotropy of soil
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c) The water content at which a soil changes
from the liquid state to solid state, is known
liquid limit of the soil
d) The water content at which a soil flows, is
known plastic limit of the soil
Q.9) According to Atterberg, the soil is said
to be of medium plasticity index PI is
a) 0 < PI < 7
b) 7 ≤ PI ≤ 17
c) 17 ≤ PI ≤ 27
d) PI ≥ 27
Q.10) For a soil having liquid limit of 45%,
plastic limit of 25% and shrinkage limit of
15%, the plasticity index is
a) 20%
b) 40%
c) 50%
d) 60%
/
ORIGIN OF SOILS
FORMATION
weathering of rocks
Decomposition oforganic matter
Geological CycleWeathering -
Transportation -Deposition - Upheaval
Weathering Physical Eg. Gravel,Sands
Chemical Eg. Clays
Transportation
Sedimentary soils
Sedentary (Residual)soils Eg. Black
cotton soils, Lateritesoils River - Alluvial Soil,
Lake - Lacustrine soil,Sea - Marine soils, Wind - Aeolian soils,Gravitation - ColluvialGlacier - Glacierdeposited soil
Aeolian soil Eg. Sanddunes, Loess
Colluvial soil Eg.Talus
Glacier Eg. Drift, till
Gravitational forces arepredominant
Surface forces arepredominant
Special Soils
Varved Clay(Lacustrine deposit)alternate layers of
clay+silt
Moorum - Gravel +Red Clay
Loam - Sand+Silt +Clay
Bentonite -Decomposed volcanicash (contains high %
of montmorillonite)
Exhibits high degree ofshrinkage & swelling
Organic soils Eg.Peat,Humus
Peat, highly organicfibrous in nature
Humus, partlydecomposed
amorphous in nature
Muck is a mixture oforganic & inorganic
soils
/
PROPERTIES OF SOIL
PHASE SYSTEM
3 Phase system -Unsat (Partiallly sat) soil, 2 Phase system- Saturated or dry soil Vol indiacted on right
& wt indicated on leftside of phase diagram
Imp Properties of soil
Void ratio, e = Vv/Vs(value of e>0sometimes >1 also)e=n/(1-n)
Porosity, n = Vv/V(value 0<n<100)
n=e/(1+e)
Degree of sat, S =Vw/Vv (value0<=S<=100)
Air Content, ac =Va/Vv (value
0<=ac<=1) ac + S =1
% air voids, na =[Va/V]*100 (value
0<=na<=n) na = n.ac
Water Content, w =[Ww/Ws]*100 (valuew>0 sometimes >100
Unit Weights of Soilγs>γsat>γ>γd>γ'
Bulk unit weight,,γ=W/V
Dry unit weight, γd=[Ws (or) Wd]/V
Sat unit weight, γsat=(W @ ful sat)/V
Unit weight of solids,γs=(Ws orWd)/Vs (γs
is constant for a soil
Submerged unitweight, γ'=γsat-γw
(based on archimedi'sprinciple)
Specific GravitiesTrue Sp.Gravity orSp. Gravity, G = γs/
γw (G is constant for asoil) Apparent/mass/bulk
sp.gravity Gm = γ/γw(Gm<G & not constant)
Imp Relationships
S.e = w.Gγd=γ/(1+w), γd=Gγw/(1+e), γd=((1-na)Gγw)/(1+wG),
γ=γw (G+Se)/(1+e),γ=γd+S(γsat-γd) V1/V2 =γd1/γd2 =
(1+e1)/(1+e2 )
Water Content ExpMethod
Oven Drying -Accurate Mathod
Calcium Carbide -Quick Method
Temp 105-110 degCelsius for 24 hours
For high organic soil60 deg celsius is
prefered
If gypsum is present,not more than 80 deg
celsius but for longtime
Specific Gravity ExpMethod
Pycnometer method,Oven dried sample is
used
G =(W2-W1)/[ (W2-W1) - (W3-W4)]
W1 = pycnometer, W2=Pyc+ dry sample, W3= Pyc+drysample+water, W4 =pyc+water
/
INDEX PROPERTIES
Grain sizedistribution
Sieve analysis(coarse grained soil)
Sedimentationanalysis (fine grained
soil <75μ)
Based on stoke's law(valid only if size of
particle is b/w 0.2mmand 0.2 μ)
Pipette Method(accurate method)
Hydrometer MethodMeniscus Correction(always +ve)
Dispersing agentcorrection (always -ve)
Dispersion solution -33g of sodium
hexametaphosphate+7g of soadium
carbonate
Temp correction (+vewhen T>27 and -ve
when T<27)
v=(gD^2 (S-1))/18γ(approx v=902D^2)
RelativeDensity/Density Index(coarse grained soil)
ID= (emax-e) / (emax-emin)
<15% - very loose, 15to 35% - loose, 35 to65% - medium dense,
65 to 85%- dense,>85% - very dense
Grain sizedistribution curve
Well graded, uniformlygraded and gap
graded soil
Cu = D60/D10 (always>=1)
>6 for well graded soil
b/w 1 & 2, foruniformly graded soill
>4, for well gradedgravel
Cc =(D30^2)/(D10×D60 )
= 1, unifromly gradedsoil
b/w 1 & 3, for wellgraded soils
Atterberg'sConsistency limits(FIne grained soil)Liquid limit
Plastic limit
Shrinkage limit
Drop of cup is 1 cm
Shear strength @ LL =2.7 kPa
Flow Index (Slope offlow curve w vs n (log
plot))
Shrinkage ratio, SR =Gm @ its dry state
Important Indices
Plastic Index Ip = wL -wp
Shrinkage Index, Is =wp - ws
Flow index, If = (w1-w2)/log10 (n2/n1)
Toughness index, It =Ip/If (↑ value,better
strength@ wp)
Liquidity Index, IL =(w-wp)/Ip
Consistency index, Ic= (wL-wp)/Ip
Activity, A = Ip/C
A < 0.75, inactive
A = 0.75 to 1.25,normal
A > 1.25, Active
Volumetric Shrinkage =(w1-ws)*SR
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Unit III
SOIL CLASSIFICATION & STRUCTURE
Particle Size Distribution
For measuring the distribution of particle
sizes in a soil sample, it is necessary to
conduct different particle size tests or
mechanical analysis.
By mechanical analysis is meant the
separation of a soil into its different size
fractions.
The mechanical analysis is performed in two
stages:
Sieve analysis
Sedimentation analysis
Sieve Analysis
In the BS (British Standards) and ASTM
(American Standard Test Method), the
sieve sizes are given in terms of the
numbers of openings per inch.
The number of openings per square inch is
equal to the square of the sieve.
The complete sieve analysis can be divided
into two parts as given below.
1. Wet sieving:
It is carried out for separating fine grains
from coarse grains by washing the soil
specimen on a 75µ sieve mess.
2. Dry sieve Analysis:
It is carried out when particles coarser than
75 µ. Samples (with fine removed) are
dried and shaken through a set of sieves of
descending sizes.
The weight retained on each sieve is
measured.
The cumulative percentage quantities finer
than sieve sizes (passing each given sieve
size) are then determined.
Calculation for percentage finer
The data obtained is presented as a distribution
curve with
Grain size along x-axis (Log scale)
Percentage passing along y-axis
(Arithmetic scale)
% finer passing through each sieve.
Table 3.1 Sieve Analysis
S.No. Sieve
size
% Retained = 𝑾𝟏
∑ 𝑾
Cumulative % Retained % finer = 100 – Cumulative % Retained
1. 2mm
2 1 mm
3 600µ
4 425 µ
5 300 µ
6 212 µ
7 150 µ
8 75 µ
9 Pan
Fig : 3.1
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Fig : 3.2 A schematic curve showing grading characteristics of soil
GRAIN SIZE DISTRIBUTION CURVE
A grain size distribution plot is a special
purpose graph generally used to depict the
results of a sieve analysis, commonly known
as gradation test.
It is also known as grading curve.
Gradation curve is plotted between the
percentage finer y-axis (on natural scale).
vs the particle size (on log scale) x-axis.
To obtain the grading characteristics, three
points are located first on the grading curve.
D60 = Size at 60% finer by weight (retained =
40%)
D30 = Size at 30% finer by weight
D10 = Size at 10% finer by weight
The grading characteristics are obtained as
follows
Effective size = D10
Uniformity coefficient, Cu = 𝑫𝟔𝟎
𝑫𝟏𝟎
Curvature coefficient, Cc = (𝐃𝟑𝟎)𝟐
𝐃𝟔𝟎 × 𝐃𝟏𝟎
Observations from the Curve
For well graded soil (i.e. soil which has a
distribution of particles over a wide size
range) And,
Cu > 4 (for gravel)
Cu >6 (for sand)
1 < Cc< 3
For uniform soil (i.e soil which has a
narrow particle size range)
Cu=1
CLASSIFICATION OF SOILS
The Unified Soil Classification System
(USCS):
Originally developed by Casagrande.
According to USCS, the coarse grained
soils are classified on the basis of their
grain size distribution and the fine grained
soils (whose behavior is controlled by
plasticity) on the basis of their plasticity
characteristics.
All soils are classified into four major
groups:
(a) Coarse grained
(b) Fine grained
(c) Organic soils
(d) Peat
Coarse grained soils are those having 50%
or more retained on the 0.075 mm sieve.
Further, the coarse grained soils are
designated as gravel (G) if 50% or more of
the coarse fraction is retained on the 4.75
mm sieve otherwise, they are designated as
sands (S).
Both Gravel and sand are subdivided into
four sub groups
(a) Well graded (W)
(b) Poorly graded (P)
(c) Silty (M)
(d) Clayey(C)
Well graded soil (W) has wide distribution
of grain sizes present, whereas, a poorly
graded (P) soil is either uniform or gap
graded.
Whether a soil is well graded or poorly
graded can be determined by plotting the
grain size distribution curve and
computing the coefficient of uniformity
(Cu) and the coefficient of curvature (Cc).
Table 3.2 Prefix and suffix of USCS:
Soil type Prefix Subgroup Suffix
Gravel G Well graded W
Sand S Poorly graded P
Silt M Silty M
Clay C Clayey C
Organic O WL < 50% L
Peat Pt WL ˃ 50% H
Fine grained soils having more than 50%
material passing the 0.075 mm sieve are
further subdivided into silt (M) and clay
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Fig : 3.3 Plasticity chart for laboratory classification
Fig : 3.4
(C), based on their liquid limit and
plasticity index.
Note:
If percentage of fines
< 5% passing 75𝜇 – GW,GP,SW,SP
>12% passing 75𝜇- GM,GC,SM,SC
5 - 12% passing 75𝜇 – GW-GM,SP-SC
(dual symbol)
The A-line on Casagrande’s plasticity
chart generally separates the more clay like
materials from those that are silty and also
the organic from the inorganic.
Silt, clay and organic fractions are further
subdivided into soils possessing low (L) and
high (H) plasticity when the LL is less than
50% and more than 50% respectively.
Some soils possessing the characteristics
of more than one group are termed as
Boundary.
Soils & hence, are assigned dual group
symbols e.g., GW-GC, which means well
graded gravel with some clay fines.
“AASHTO” SOIL CLASSIFICATION
SYSTEM
According to AASHTO system, the soils
are classified into eight groups: A-1
through A-7 with an additional group A-8
for peat or muck.
The system includes several subgroups.
Soils within each group are evaluated
according to the group index calculated
from empirical formula:
GI = 0.2 a + 0.005 ac + 0.01 bd
Where,
a = that part of the percent passing the 75 µ
sieve greater than 35 and not exceeding 75.
b = that part of the percent passing the 75µ
sieve greater than 15 and not exceeding 55.
c = that part of liquid limit greater than 40 and
not greater than 60.
d = that part of plasticity index greater than 10
and not exceeding 30.
Greater the G.I. value, the less desirable a
soil is for highway construction with in
that subgroup.
Table 3.3
GI SOIL TYPE
0 – 2 Good
2 – 5 Fair
5 – 10 Poor
10 - 20 Very Poor
Indian Standard Soil Classification
System (ISSCS):
It is based on USCS with the modification
that the fine grained soils have been
subdivided into three subgroup of low,
medium and high compressibility as
against only two in the USCS.
Equation of A-line = 0.73(WL – 20)
The plasticity chart of ISSCS is:
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Fig : 3.5 Grading curves
Table 3.3 Prefixes and suffixes of ISSCS:
Soil type Prefix Subgroup Suffix
Gravel G Well graded W
Sand S Poorly graded P
Silt M Silty M
Clay C clayey C
Organic O WL< 35% L
Peat Pt 35 <WL< 50 I
WL> 50 H
Typical grading curves are given below
Curve A a poorly graded medium sand
Curve B a well graded gravel sand
Curve C a gap graded cobbles sand
Curve D a sandy silt
Curve E a silty clay.
Fig : 3.5
Table 3.4 Soil classification using group symbols
Group Symbol Classification
GW Coarse Soils
Well graded gravel
GP Poorly-graded gravel
GM Silty gravel
GC Clayey gravel
SW Well graded sand
SP Poorly graded sand
SM Silty sand
SC Clayey sand
ML Fine soils
Silt of low plasticity
MI Silt of medium plasticity
MH Silt of high plasticity
CL Clay of low plasticity
CI Clay of medium plasticity
CH Clay of high plasticity
OL Organic soil of low plasticity
OI Organic of medium
plasticity
OH Organic of high plasticity
Pt Peat
IMPORTANT POINTS
Only particles of coarse grained soil
can be seen by naked eye.
Best soil for homogeneous rolled
embankment dam–—GC
Best soil for core of rolled earthen
dam—GC
Best soil for shell of rolled earth
dam—G W
Best soil for foundation when seepage
not important—GM
Best soil for foundation when seepage
important.—GW
Best soil for road surfacing—GC
Soil Structures
Soil structure is determined by how
individual soil granules clump or bind
together and aggregate, and therefore, the
arrangement of soil pores between them.
Soil structure has a major influence on
water and air movement, biological
activity, root growth and seeding
emergence.
For coarse-grained soils the soils structures
can be classified as
Single Grained Structure
Single grained structure is characteristic of
coarse grained soils, with a particle size
greater than 0.02 mm.
Cohesion less soils such as gravel and sand
in which gravitational forces are more
predominant than surface forces, take an
equilibrium position.
The deposition may occur in a loose state,
with large voids or in a sense state with
less of voids.
Fig : 3.6 Single grained structure
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Honeycomb Structure
This structure occurs in soils having small
granular particles which have cohesion
because of their fineness.
Soils in honeycomb structure are loose.
They can support loads only under static
condition.
The structure has a large voids spaces and
may carry high loads without a significant
volume change.
The structure can be broken down by
external disturbances.
Clay consisting of very fine particles or
colloids may have two types of structure
such as flocculated and dispersed.
Both of the structures are described below
Flocculated Structures
The clay particles haves large surface area
and therefore electrical forces are
predominant in such soils.
The clay particles haves negative charge
on the surface and a positive charge on the
edges.
Inter particle contact develops between the
positively charged edges and negatively
charged faces.
Such a structure is formed when the net
electrical forces between adjacent soils
particles at the time of depositions are
attraction forces.
Dispersed Structures
These structures develop in clays that have
been reworked or remolded.
The particles develop almost parallel
orientation.
Dispersed or oriented structure is formed
when the platelets have face-to-face
contact in more or less parallel array.
Such a structure is formed if the net
electrical forces between adjacent soil
particles at the time of deposition are
repulsion.
TWO LAYER SHEET MINERALS
The basic kaolinite unit is a two layer unit
that is formed by stacking a gibbsite sheet on a
silica sheet.
Kaolinite Minerals
Kaolinite is the most common mineral of
the kaolin group.
The basic units of kaolinite minerals (i.e.,
gibbsite and silica sheet) are stacked one
on top of the other to form a lattice of the
mineral.
The units are held together by hydrogen
bonds. The strong bond does not permit
water to enter the lattice, thus kaolinite
minerals are stable and do not expand
under saturation.
Fig : 3.7 Honeycomb Structure
Fig : 3.8 Flocculated Structure
Fig : 3.9 Dispersed Structure
Fig : 3.10
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Fig : 3.13 Polar representation of water molecule (dipole action)
THREE LAYER SHEET MINERALS
Typically, the three layer sheet minerals
are categorized as follows
Montmorillonite Minerals
The basic structural unit consists of an
alumina sheet sandwiched between two
silica sheets.
The two successive structural units are
joined together by a link between oxygen
ions of the two silica sheets.
The negatively charged surfaces of the
silica sheet attract water in the space
between two structural units.
This result in an expansion of the mineral,
thus montmorillonite minerals exhibit high
shrinkage and high swelling
characteristics.
IlIite Minerals
The basic structural unit is similar to that
of Montmorillonite; there is always a
substantial amount of isomorphous
substitution of silica by aluminum in silica.
The link between different structural units
is non-exchangeable potassium ion (K+).
Properties of mineral illite are somewhat
intermediate between that of kaolinite and
montmorillonite.
CLAY WATER RELATIONSHIP
Normally clayey soils are associated
with water and its properties are
significantly influenced with the
presence of water whereas granular
soils are not sensitive to the amount of
water present
Water is a dipolar molecule. The
centre of gravity of +ve & –ve charges
do not coincide. Hence it is treated as a
bar magnet.
Clay particles always carry a net
negative charge except at edges.
Reason for charge accumulation
1. Isomorphous substitution by lower
valency cation.
2. Breakage of particles
3. Dissociation of hydroxyl (OH-) radical
into hydrogen ions.
Fig : 3.11
Fig : 3.12
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General Mechanism of Clay water
Interaction
Due to the attraction of +ve and –ve
charges close to the clay surface,
results in formation of adsorbed layer
of water and double diffused layer.
Following are the ways by which water is held
to the clay surface
(a) Attraction between negatively charged
faces of clay and +ve ends of dipoles
(electrostatic attraction).
(b) Attraction between cations in the water
and negatively charged ends of
dipoles.
(c) Hydrogen atom of the water molecule
is attracted to the oxygen or hydroxyl
ion on the surface of clay crystals.
Adsorbed Water
Water held on the surface of particle
by powerful forces of electrical
attraction and virtually in a solid state,
this layer is very thin (10A°)
Adsorbed water cannot be removed by
oven drying at 105 - 110°C and may
therefore be considered to be part of
the solid grain. Heating at 105 – 110°C
will change clay soil structure.
Fig : 3.18
Cations distribute themselves around
the negatively charged surface of clay
particles with the greatest density near
the surface.
Beyond this there is an outer layer
which is attracted to lesser degree and
is more mobile. This layer which
extends up to the limit is called as
diffused double layer and its density
decreases with the increasing distance
from the surface.
Ultimately the concentration
becomes equal to that in water in the
void space.
Rigid layer and diffused layer
combinedly is called Electrical double
layer.
The oriented water is considered to
affect the behaviour of clay particles
Fig : 3.16
Fig : 3.17
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when subjected to stress because it
comes between the particle surface.
For a given particle, the thickness of
the cation layer depends mainly on the
valency and concentration of cations.
An increase in valency (due to cation
on exchange) or an increase in
concentration will lead to decrease in
the layer thickness.
CATION EXCHANGE CAPACITY
The ability of clay particles to absorb
ions on its surface or edges is called
base or cation exchange capacity
which is a function of the mineral
structure of the clay and the size of the
particles.
CEC = f [Mineral structure, size of
particles]
Cation is termed as exchangeable
because one cation can easily be
exchanged with the other.
Behaviour of clay soil is dependent on
the exchangeable cation in the clay.
Different clay has different change
deficiencies and has varying ability to
adsorb exchangeable cations.
The Base Exchange capacity is
expressed in terms of the weight of a
cation, which may be held on the
surface of 100 g of dry soil material. It
is measured in milli equivalent (meq)
per 100 gm of dry soil where 1 meq is
1mg of hydrogen or the portion of any
ion which will combine with or
displace 1 mg of hydrogen.
Montmorillonite has 10 times Base
Exchange capacity as compared to
Kaolinite. CEC of Illite is in between
Kaolinite and Montmorillonite.
Depositional environment, weathering
action, leaching etc. will govern the
kind of ions present in clay.
Marine clay has predominantly Na &
Mg cations.
Valence of the cations is the basic
factor in the process of replacement of
exchange.
Replacement ability of various cations
are as follows:
Al3+
> Ca2+
> Mg2+
> K+ > H
+ > Na
+ > Li
+
This principle of cation exchange can
be used with advantage in many
practical situations, as for example, in
the stabilization of sodium clay soil by
using lime. Here, calcium ions replace
the sodium ions by virtue of their
Superior replacing power and reduces
the swellings of sodium
Montmorillonite, because the adsorbed
layer of water would be thinner when
the valence of the cation is larger.
Clay Particles Interaction
Soil structure of clay depends on the
force of attraction and repulsion
between the soil particles. But there is
an adsorbed layer of water between
two particles. Hence particles interact
through adsorbed layer.
Thus factors such as nature of ions
present, their concentration, size etc.
affects the soil structure.
Fig : 3.19
Fig : 3.20
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The repulsive force between clay
particles are due to similar charges in
clay particles. This force comes into
play when particles come closer to
such an extent that adsorbed water
layer starts interacting.
Attractive forces between clay
particles are due to Vander wall forces
various types of linkage such as
hydrogen bond etc.
Force of repulsion and attraction both
act between clay mineral particles.
Repulsion occurs between like charges
of the double layer of cation and the
force of repulsion depending on the
characteristics of layers.
An increase in cation valency or
concentration will result in decrease in
repulsive force and vice versa.
Attraction between clay particles is
due to Vander wall forces which are
independent of double layer.
If two particles come closer and
interact such that Total energy
decreases then net force is attractive.
This leads to Flocculated structure.
If however, net force is repulsive,
Dispersed structure will be formed
Flocculated structure (are mostly edge
to face but it can be Edge to edge
also).
Dispersed structure have face to face
configuration.
Tendency to flocculate depends on
1. Concentration of electrolytes
2. Valency of ions
3. Temperature
Dispersed structure with face to face
configuration has lower void ratio as
compared to flocculated structure
which has large void ratio.
Marine clay has flocculated structure,
lacustrine clay has dispersed structure.
Sodium clay can absorb more water
than Ca clay because absorbed layer
thickness in calcium clay is smaller
(diffused layer being thinner, there by
tendency to absorb water being less).
Thus liquid limit of sodium clay is
larger as compared to calcium – clay.
As sodium clay can adsorb more water
its swelling property is more. If Na is
replaced by calcium, tendency to
swelling is less. This is used in soil
stabilization.
Note: Decrease in layer thickness, decrease
repulsion.
Table 3.5 Comparison between Clay Minerals
Fig : 3.21 Flocculated Structure
Fig : 3.22
Fig : 3.23 Dispersed Structure
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Clay Mineral Grain size Base exchange
capacity
Ip Dry strength Active tip
Montmorillonite Min largest Max Max largest
Illite Intermediate Intermediate Intermediate Intermediate Intermediate
Kaolinite Max Least Min Min Least
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PRACTICE QUESTIONS
Q.1) The following data refer to a sample of
soil
Percent passing 4.75 mm IS siever – 71
Percent passing 75 μ IS siever – 4
Uniformity coefficient – 7.5
Coefficient of curvature – 2.7
The soil is classified as
a) SW
b) GW
c) SM
d) GM
Q.2) Dispersed type of soil structure is an
arrangement comprising particles having
a) face to face or parallel orientation
b) edge to edge orientation
c) edge to face orientation
d) all of the above
Q.3) Of the following soils, characterized by
their USCS group symbol, which one is
most suitable as fill for a road embankment?
a) SM
b) GC
c) GW
d) CL
Q.4) For general engineering purposes, soils
are classified by
a) particle size classification system
b) textural classification system
c) High Way Research Board (HRB),
d) unified soil classification system.
Q.5) An arrangement composed of ‘flocs’ of
soil particle is known as
a) Dispersed structure
b) Cohesive matrix structure
c) Honey comb structure
d) Flocculent structure
Q.6) For a soil sample, degree of shrinkage
is less than 5%. The quality of the soil
sample is
a) poor
b) very poor
c) medium good
d) good
Q.7) Unified soil classification system
(USCS) was developed by
a) Kozney
b) Atterberg
c) Casagrande
d) Rankine
Q.8) The group index of a soil depends on
a) Liquid limit
b) Plastic limit
c) All of the mentioned
d) None of the mentioned
Q.9) According to IS classification, the
range of silt size particle is
a) 4.75 mm to 2.00 mm
b) 2.00 mm to 0.425 mm
c) 0.425 mm to 0.075 mm
d) 0.075 mm to 0.002 mm
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Q.10) The number of basic soil components
in IS classification system (IS: 1498) is
a) 4
b) 5
c) 7
d) 18
/
SOIL CLASSIFICATION
Based on indexproperties
Particle sizeclassification
< 2μ - Clay, 2 to 75μ -Silt, 75μ to 4.75mm -Sand, 4.75 to 80mm -Gravel, 80 to 300 mm
Cobble, > 300mm -Boulder
AASHTO/HRB SoilClassification
Based on particle sizedistribution &
plasticitycharacteristics
Soil is classified into 7groups (A1, A2..A7)
Black cotton fallsunder A7 (smaller
group number, bettersoil for pavement)
Group Index =0.2a+0.005ac+0.01 bd
(0 to 20)
Depends on % soilpassing 75μ sieve,
Liquid limit & Plasticlimit
GI = 0 best soil & 20poor soil for pavement
Suitable forpavement design
USCS Classification
Suitable for"Air fieldclassification" by
casagrande
Based on particle sizedistribution, plasticity
& compressibilitycharacteristics
IS Soil Classification
Derived from USCS
Primary SoilClassification (18)
Coarse Grained soil(% retained on 75μ is
> 50%)
Gravel (more than50% of coarse fractionretained on 4.75mm)
Sand (more than 50%of coarse fractionpasses 4.75mm)
Fine Grained soil (%passing on 75μ is >
50%)Inorganic Silts (M)
Inorganic Clay (C)
Organic silts & clays(O)
Highly Organic soil(Peat, Pt)
Plasticity Chart (Ip vswL)
Equation of A line =0.73 (wL - 20)
Inorganic Clay aboveA line & Inorganic Silts
below A line
wL<35 - low comp,35<wL<50 - int comp,
>50 - High comp
Organic silts & claysbelow A line
Well graded gravel(GW) - fines<5%,
Cu>4 & Cc b/w 1&3
Poorly graded gravel(GP) - fines < 5% &
not meeting allgradation req of GW
Silty Gravel (GM) -fines>12%, below A
line or Ip<4
Clayey Gravel (GC) -fines>12%, above A
line with Ip>7
Dual Symbols
Fines b/w 5% and 12%, GP-GM, SW-SC,
GW-GC, SP-SM etc
Ip lies b/w 4 & 7, GM-GC, SM-SC etc
/
SOIL STRUCTURE &CLAY MINERALOGY
Behaviour of soildepends on soil
structure
Types of soilstructure
Single grainedstructure (eg. gravel
& sand)
Honey combedstructure (eg. Fine
sand or silts)
Flocculated structure(eg. clays)Dispersed structure
(eg. remoulded clays)
Edge to faceorientation
has high shearstrength, high
permeability & lowcompressibility
Formed where there isnet attractive forceexist b/w particles
Formed where there isnet repulsive b/w
particles
Face to Faceorientation
has low shearstrength, low
permeability & highcompressibility
Remoulding
Loss of strength incohesive soil
Thixotropy
Regain of lost strengthwith passage of time,
with no change inwater content
Clay MineralogyKaolinite
Illite
Montmorillonite
HalloysiteGibbsite & silicasheets one over
another with H-bond
Causes no swelling &no shrinkage
Stable Mineral eg.china clay
Contains nonexchangeablepotassium ions
Medium swelling &shrinkageExhibits large
swelling & shrinkage
highest % ofmontmorillonite is seen in bentonite followedby black cotton soil
Behaviour similar tokaolinite
Specific Surface Area(m^2/g or cm^2/g)
Finer the soil, higherSSA
Montmorillonitehigher SSA = 800
m^2/g
Diffuse Double layer
Present only in clays
adsorbed waterimparts plasticity to the
clay