permeability characteristics of coarse pond ash

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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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    THANK U !!!