permeability characteristics of coarse pond ash
TRANSCRIPT
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INTRODUCTION
LITERATURE REVIEW
SCOPE OF THE PRESENT WORK
EXPERIMENTAL WORK AND METHODOLOGY RESULTS AND DISCUSSIONS
CONCLUSIONS
REFERENCES
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Thermal power plants using coal is chief source of energy in
our country.
The total production of ash was found to be 131 million tonnes
during 2010-11
Wet disposal method is most widely used by the thermal
power plant.
At present around 265 km2 of area is covered by ash ponds
and by 2015 it would require 1,000 km2 for its disposal
Scarcity of land the power plants raise the height of dykes to
increase the ponding capacity.
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Filters and drains are two most important criteria for stability
and reliability of ash pond.
Purpose of filter
1. to protect the fly ash against being carried away with
seepage.
2. to take out the seepage water in order to keep the fly ash
in dry condition avoiding liquefaction .
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TITTLE OF
PAPER
AUTHOR
(YEAR)
DETAILS NAME OF THE
JOURNAL
Seismic failures
of Chilean
dams.
Dobry and Alvarez
(1967)
Studied seismic failures of
some tailings dams in Chilie
and found that the reason
being inadequate drainage.
Journal of
Geotechnical
Engineering,ASCE
Flow failures of
some mine
tailings dams
K. J. Jeyapalan,
(1981)
Reviewed failures of 16
tailings dams and ash dykes
which were caused due to
the instability of dams
constructed using theupstream method due to
excessive pore pressures
and absence of internal
drainage
Journal of
Geotechnical
Engineering,
ASCE
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TITTLE OF
PAPER
AUTHOR
(YEAR)
DETAILS NAME OF THE
JOURNAL
Granular Filterfor Ash Dykes S.R.Gandhi andV. Gima
Mathew(1996)
Conducted tests onamount of penetration,
amount of bypassing and
amount of clogging of fly
ash through different size
sand filter
IndianGeotechnical
Conference held at
Madras during
December 11-14,1996
Design And
Maintenance Of
Ash Pond For
Fly Ash
Disposal
S.R.Gandhi
(2005)
Described the design and
maintenance of ash pond
for fly ash disposal
Indian
Geotechnical
Conference,
Warangal. 2005
Use of Bottom
ash in lieu of
sand as filter in
ash dyke
embankment
J. Kumar and
D.N.Naresh
(2012)
Conducted a case study on
the use of bottom ash as
filter in lieu of sand as
internal drainage for
exiting the hydraulic
gradient
Geo Congress
2012,ASCE .
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MOTIVATION:
Non-availability of good sand as a filter material during monsoon
and just after monsoon creates a problem in construction of ash
dyke. Coarse pond ash and bottom ash which are the waste
products and non-plastic in nature and available abundantly may
replace the conventional sand as a filtering material.SCOPE
To study the crushability and permeability properties of samples
subjected to different loading intensities (dynamic compacting
energies of 0 to 4278 kJ/m3
) To find out the filter criteria and check whether these materials
are suitable as a filter media after being subjected to loading.
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Bottom ash and coarse pond ash samples were collected from
NTPC, Kaniha, Odisha
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Determination of index properties
Grain size distribution curve, specific gravity, plasticity index of
both the samples were determined as per the Indian Standard Code
of practice IS-2720 part (VI), IS-2720 part (III) and IS-2720 part
(VI) respectively.
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Physical parameter Pond Ash Bottom Ash
Colour Light grey Grey colour with
unburned coal
Shape Rounded/ sub rounded Rounded/ sub rounded
Mean diameter, D50 0.3 mm 0.28 mm
Uniformity coefficient,Cu
3.33 3.52
Coefficient of
curvature, Cc
1.2 1.028
Specific gravity, G 2.18 2.12
Plasticity index, Ip Non-plastic Non-plastic
Loss on ignition 0.347 4.0265
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Sample preparation
Subjected to dynamic compactions in a Proctor mould at drystate either in using Standard Proctor rammer or Modified
Proctor rammer
The number of blows and layers are so adjusted that the
resulting compactive effort (E) on the sample are either 149,595, 1070, 2674 or 4278 kJ/m3
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Grain size distributions for all twelve samples were conducted
as per IS: 2720 part (IV)
0
10
20
30
40
50
60
70
80
90
100
110
0.01 0.1 1 10 100
%f
iner
particle size in mm
E=0
E=149kJ/m3
E=595kJ/m3
E=1070kJ/m3
E=2674kJ/m3
E=4278KJ/m3
Fig 1 Grain size distribution curve of pond ash
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0
10
20
30
40
50
60
70
80
90
100
110
0.01 0.1 1 10 100
%f
iner
particle size in mm
E=0
E=149kJ/m3
E=595kJ/m3
E=1070kJ/m3
E=2674kJ/m3
E=4278kJ/m3
Fig 2 Grain size distribution curve of bottom ash
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Coefficient of uniformity, coefficient of curvature and mean
diameter of the samples
Compaction energy
in kJ/m3
Pond Ash Bottom ash
D50
Cu
Cc
D50
Cu
Cc
0 0.35 3.33 1.2 0.29 3.52 1.028
149 0.29 3.88 1.4 0.267 3.69 1.154
595 0.26 4.91 1.77 0.26 3.79 1.219
1070 0.258 5.08 1.8 0.25 4.20 1.279
2674 0.24 5.185 1.85 0.24 4.37 1.366
4278 0.23 5.192 1.9 0.23 5.79 1.392
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Determined as per IS-2720 part (14) for samples that have
been subjected to different compactive energies
Minimum dry density was determined by filling the standard
mould in sand raining method to their loosest state
Maximum dry density was determined with respect to their
densest state using vibrating table and putting a surcharged
weight over it
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Compaction
Energy in
kJ/m3
Pond ash Bottom ash
minimum
density in
gm/cc
maximum
dry density
in gm/cc
minimum
density in
gm/cc
maximum
dry density
in gm/cc
0 0.8025 1.009 0.862 1.038
149 0.858 1.081 0.901 1.087
595 0.8795 1.11 0.938 1.138
1070 0.9245 1.161 0.946 1.144
2674 1.0135 1.223 0.994 1.203
4278 1.0369 1.254 1.036 1.246
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Coefficient of permeability of both pond ash and bottom ashsamples were determined per IS: 2720 (part 36 )1987
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Compaction
Energy in
kJ/m3
Pond ash Bottom ash
Coefficient of
permeability
at minimum
density in 10-3cm/sec
Coefficient of
permeability
at maximum
dry density in10 -3 cm/sec
Coefficient of
permeability at
minimum
density in 10 -3cm/sec
Coefficient of
permeability
at maximum
dry density in10 -3 cm/sec
0 11.54 8.40 8.5478 5.388
149 10.06 7.193 7.264 4.493
595 9.070 5.147 5.611 2.656
1070 8.204 4.162 4.669 1.4158
2674 6.327 2.246 2.288 0.791
4278 4.256 1.354 1.123 0.551
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Cu increases from 3.33 to 5.192 for pond ash and for bottomash it increases from 3.52 to 5.79 with increase in compactive
energy from 0 to 4278 kJ/m3
Cc increases from1.2 to1.9 for pond ash sample and for
bottom ash sample 1.028 to1.392 with increase in compactiveenergy from 0 to 4278 kJ/m3
This indicates that with increase in compactive effort the size
of grains reduced and the samples tend to be well graded.
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0
1
2
3
4
5
6
7
0 500 1000 1500 2000 2500 3000 3500 4000 4500
C
cocuvueauomity
compaction energy in kJ/m3
Cu of pond ash
Cc of pond ash
Cu of bottom ash
Cc of bottom ash
Fig. 3 Coefficient of curvature and uniformity of samples subjected to different
compactive energies
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Fig. 4 Minimum and maximum density of samples subjected to different
compactive energies
0.7
0.8
0.9
1
1.1
1.2
1.3
0 500 1000 1500 2000 2500 3000 3500 4000 4500
dydtyngm/
compaction energy in kJ/m3
minimum dry density of pond ash
maximum dry density of pond ash
minimum dry density of bottom ash
maximum dry density of bottom ash
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0
2
4
6
8
10
12
0 500 1000 1500 2000 2500 3000 3500 4000 4500
pmety1cm/
compaction energy in kJ/m3
at minimum dry density condition of PA
at maximum dry density condition of PA
at minimum dry density condition of BA
at maximum dry density condition of BA
Fig 5 Graph between compaction energy and permeability
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D15 (F) > 5 D15 (B) or 0.1mm
D15 (F)=0.15mmTest result is found to be 5D15(B) = 0.88 mm but
After crushing D15 (F) = 0.07 and 5D15 (B) = 0.025mm
Partially Satisfying IS criteria
As it is a silty sand and for percentage finer than 15%- 39%
D15 (F) < (40-A)/(40-15) *(4D85(B)-0.7)+0.7 m m
where A = % passing 75 micron
Test result is found to be (40-A)/(40-15) *(4D85(B)-0.7)+0.7
= 9.716 mm
After crushing at maximum compaction energy is found to be
D15 (F) = 0.07< 2.708
Satisfying IS criteria
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Filter materials are non-cohesive
Maximum size of the filter materials are less than 75mm.
Filter material passing 75 micron is less than 5%
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Specific gravity for both pond ash and bottom ash are found to
be 2.18 and 2.12 respectively which are lower than theconventional earth material of similar gradation
As the compaction energy increases, particles crushed but their
gradation changes from uniformly graded to well grade
Particles after crushing (subjected to compaction energiesfrom 0 to 4278 kJ/m3 ) however it also satisfies the IS filter
criteria
After crushing permeability of both pond ash and bottom ash
decreases but lies within the range of sand Use of bottom ash as a filter material also reduces the cost of
construction of ash dyke.
It is also an effective means of utilisation of thermal power
plant waste.
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Dobry. R and Alvarez, L. (1967), Seismic Failures of Chilean
dams. Journal of Geotechnical Engineering, ASCE,Vol.93.No.SM6,pp.237-260
Jeyapalan, K.J. (1981). Flow Failures of some mine Tailings
Dams, Geotechnical Engineering. Vol. 12, pp. 153-166.
Gandhi, S.R., and Gima V. Mathew, (1996) Granular Filterfor Ash Dykes, Proceedings of Indian Geotechnical
Conference held at Madras during December 11-14, 1996.
pp.532-535.
Gandhi, S.R., Raju, V.S., and Vimal Kumar, (1997)Densification of Deposited Ash Slurry, Proceedings of 13th
International Conference on Solid Waste Management,
Philadelphia.
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Gandhi S. R.,(2005) Design And Maintenance Of Ash PondFor Fly Ash Disposal. Indian Geotechnical Conference,
Warangal.
Pedro J Amaya, Andrew J Amaya, (2007) The use of Bottom
Ash in the Design of Dams World of coal ash (WOCA),
Northen Kentucky , USA
Indian Standard (IS): 9429Drainage System for Earth and
Rockfill DamsCode of Practice.
Kumar, J. and Naresh, D.N (2012)Use of Bottom ash in lieu
of sand as filter in ash dyke embankment GeoCongress2012,ASCE
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