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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 5052
DIFFUSION CHARACTERISTICS OF KAOLINITE FLYASH LINER
Greeshma B S1, Rani V2
Greeshma B S ,PG Student, Department of Civil Engineering, Marian Engineering College, Tvm
Rani V , Associate Professor, Department of Civil Engineering, Marian Engineering College, Tvm
---------------------------------------------------------------------***---------------------------------------------------------------------
Abstract – Use of sanitary landfills for waste containment is
one of the oldest and most popular waste disposal
technique.The landfill liner is designed to isolate the waste
from the soil beneath to minimize the passage of leachate into
the Groundwater . Usuallycompactedlinermaterialsconsistof
soil rich in clay minerals for their low hydraulic conductivity.
Addition or partial replacement with industrial wastes such
as Flyash, Silicafume, Ground Granulated Blast Furnace Slag
(GGBS) make the CCL more economical. These industrial
wastes are abundantly available, very fineandtheir useinCCL
is an eco-friendly alternative to reduce their environmental
pollution. This paper reports the results of short term
laboratory tests of diffusion of chlorine ion through Kaolinite
partially replaced with flyash. Fly replacement levels are
varied up to 30% at regular intervals of 5%. The test results
indicated that chlorine ion diffusion is reduced for all
replacement levels of fly ash. It is concluded that partial
replacement of Kaolinite with fly ash up to 20% is acceptable
as diffusion of Chlorine ion increased beyond this replacement
level.
Key Words: kaolinite , Flyash , Liner,Diffusion
1.INTRODUCTION
1.1General
Landfillsarethemostpopularmunicipalsolidwaste
disposal system The design of liner is made so as to
isolate the waste from the environmentminimizingthe
passage of leachate into the groundwater. To ensure
thistheimportantcharacteristicsforcompactedlandfill
linersareselectionofmaterials,hydraulicconductivity,
strength, compressibility and contaminant retention
capacity. Usually soil rich in clay minerals are used as
compacted liner materials for their low hydraulic
conductivity. . Fly ash is generated in tons as a residue
from burning of coal in the power plants .Utilization of
this waste material has high environmental value. By
compacting the fly ash-clay mixture at the optimum
range of dry density and moisture content the bonding
between the particles is enhanced which in turn
increases the strength and longevity of the liner. The
bulkavailabilityofflyashhelpsreducingthecostofraw
materials required for liner as well as providing their
safe disposal in a large scale.
1.2 DIFFUSION
At any temperature different from absolute zero, all
atoms, irrespective of their state of aggregation
(gaseous,Liquid,orsolid)areconstantly inmotion.Since
the movementof particlesis associatedwithcollisions,
the path of a single particle is a zigzag one.However , an
aggregation of diffusing particles has an observable
drift from places of higher to places of lower
concentration .Due to this diffusion is known as
transport phenomenon.
Fig I: Symbolic representation of diffusion (Craig H.
Benson et al(1994))
In a diffusion reaction, the flux(matter,heat,
electricity…) follow the general relation:
Flux=(conductivity) x (driving force)
In the case of atomic and molecular diffusion, the
conductivity is referred to as the fiffusivity or the
diffusion constant and is represented by the symbol D.
The driving force for many types of diffusion is the
existence of a concentration gradient.The diffusion
coefficient is calculated using the equation
=erf [
-concentration ratio
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 5053
D –Diffusion coefficient (m2/s)
T – Thickness of GCL sample
C1-Source tank concentration(mg/l)
C2-Reciever tank concentration(mg/l)
Objective of the study.
 To investigate the basic characterization
Kaolinite and flyash
 To study compaction characteristics of
kaolinite-flyash liner.
 To evaluate diffusion characteristics of same.
2.MATERIALS AND METHODOLOGY
Materials
Kaolinite:Bentoniteforthepresentstudywascollected
from Associate Chemicals,Kochi
Flyash: Flyash taken from tamil nadu
Table 2:Initial properties of flyash
Properties Values
Specific gravity 2
Liquid Limit 29
Plastic limit Non plastic
Plasticity index Non plastic
Percentage clay(%) 16.25
Percentage silt(%) 29.75
Percentage sand(%) 46
OMC(%) 31.3
Dry density 1.16
UCC(kg/cc) .94
Table I:Initial properties of Kaolinite
Methodology
Compaction test: The test to determine the optimum
moisture content andmaximumdrydensityweredone
using standard proctor test according to IS 2720. 1980
(Part VIII). The variation in optimum moisturecontent
and maximum dry density was studied with the
addition of various percentages .
Diffusion test:
Procedure
 Two reservoirs(connected with a pipe) are
filled with distilled water
 soil specimen placed in the middle of the pipe
 Allow saturation of specimen for 48hours
 Add any solute of known concentration in one
of the reservoir
 Using titrationmethodchecktheconcentration
of solute in both reservoirs in different time
intervals
Properties Kaolinite
Specific gravity 2.67
Liquid limit (%) (IS 2720 PART
51985)
34
Plastic limit (%) ( IS 2720 PART
51985)
23
Plastic index (%) (IS 2720 PART
51985)
11
Shrinkage limit (%) (IS 2720 PART
51985)
21
IS Classification CL
Natural moisture content (%) -
Optimum moisture content (%) (IS
2720 PART 7)
24.5
Maximum dry density (g/cc) (IS 2720
PART 7)
1.424
Percentage of clay (IS 2720 PART 4) 66
Percentage of silt (IS 2720 PART 4) 23
Percentage of sand (IS 2720 PART 4) 11
UCC strength (kg/cm2) (IS 2720 PART
10)
.468
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 5054
Fig 2: Diffusion mould
RESULTS
compaction results
The value of OMC and MDD obtained from laboratory
compaction test provides a reference point while
estimating the actual water content of the field-
compacted soil liner. If the water content is not in the
proper range, the engineering propertiesofthesoilare
not likely to be in the range desired. For example, if the
soil is too wet, the shear strength of the soil may be too
low. Similarly, the dry unit weight of the field-
compacted soil may be compared to the maximum dry
unit weight determined from a specified laboratory
compaction test
Table 4: compaction characteristics of kaolinite flyash
mixture
% replacement of flyash MDD OMC
kaolinite +0% fly ash 1.424 24.5
kaolinite +10% flyash 1.5 24
kaolinite +15% flyash 1.59 23.6
kaolinite + 20% flyash 1.63 23
kaolinite + 25% flyash 1.6 23.2
kaolinite +30% flyash 1.53 23.6
Diffusion results
From these test results it can be understood that
partial replacement of clay by fly ash decreases the
diffusion coefficient. The reason for this can be
attributed to the factthatpartialreplacementofclayby
fly ash makes the clay-fly ash matrix more cohesive as
the fly ash particles are finer and act as ball bearing
while getting mixed with bentonite. The decrease in
Diffusion coefficient of the resulting modified CCL will
provide better performance as liner. The replacement
of bentonite by fly ash cannot be continued as this
replacementincreasesthepermeabilityoftheresulting
CCL.
CONCLUSIONS
Based on the laboratory tests conducted the following
conclusions are drawn.
1. Partial replacement of bentonite and kaolinite byfly
ash decreases the coefficient of diffusion .
2. Partial replacement of kaolinite as well as bentonite
by fly ash is an encouraging aspect from the
performance point of view of CCL; however, this
replacement level shall be restricted to 25%, as
permeability of modified CCL increases adversely
beyond this replacement level.
% Of Flyash Diffusion Coefficient Of Cl
Ions
0 4.2*10^-10
10 3.9*10^-10
25 2.8*10^-10
30 2.98*10^-10
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 5055
References
1) Alam .J et al(2012).Seepage characteristics and
Geotechnical properties of flyash mixed with
bentonite,International journal of scientific and
research ,volume 3,issue 8
2) Andal Mudimby et al.(2012),ConcreteConfinement
with Textile-Reinforced Mortar Jackets, ACI
Structural Journal, Vol.103, No.1, pp 28-37
3) K.Badv and R.Farsimadan (2009),Swelling and
diffusion characteristics of the experimental GCLs.
4) Erdal Cokca,Zeka Yilmaz (2004),Use of rubber and
bentonite added flyash as a liner material,waste
management ,pp153-164.
5) Kristin.M.Sample-Lord et al.(2016)solute diffusion
in bentonite pastes,Journal of Geotechnical and
Geoenvironmental engineering,ASCE.
6) Nayak et al.(2015),Assesment of coal ash-bentonite
mixture as landfill liner,Indian Geotechnical
Conference.
7) PuvvadiV.Sivapullaih and Vandana
Sreedharan(2012) ,Organically modified bentonite
as a part of Geosynthetic clay liner
system,Geosynthetics.
8) L.R. Van Loon, J.M. Soler (2004), Diffusion of HTO,
36Cl-, 125I-, and 22Na+ in Opalinus Clay: Effect of
confining pressure, sample orientation, sample
depth and temperature, PSI-BerichtNr.04-03,Paul-
Scherrer-Institute, Villigen, Switzerland.
9) P.M.H. Kau, P.J. Binning, P.W. Hitchcock and D.W.
Smith (1999), Experimental analysis of fluoride
diffusion and sorption in clays, J. Contam. Hydrol.
36, 131-151 Dresden, Germany

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IRJET- Diffusion Characteristics of Kaolinite Flyash Liner

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 5052 DIFFUSION CHARACTERISTICS OF KAOLINITE FLYASH LINER Greeshma B S1, Rani V2 Greeshma B S ,PG Student, Department of Civil Engineering, Marian Engineering College, Tvm Rani V , Associate Professor, Department of Civil Engineering, Marian Engineering College, Tvm ---------------------------------------------------------------------***--------------------------------------------------------------------- Abstract – Use of sanitary landfills for waste containment is one of the oldest and most popular waste disposal technique.The landfill liner is designed to isolate the waste from the soil beneath to minimize the passage of leachate into the Groundwater . Usuallycompactedlinermaterialsconsistof soil rich in clay minerals for their low hydraulic conductivity. Addition or partial replacement with industrial wastes such as Flyash, Silicafume, Ground Granulated Blast Furnace Slag (GGBS) make the CCL more economical. These industrial wastes are abundantly available, very fineandtheir useinCCL is an eco-friendly alternative to reduce their environmental pollution. This paper reports the results of short term laboratory tests of diffusion of chlorine ion through Kaolinite partially replaced with flyash. Fly replacement levels are varied up to 30% at regular intervals of 5%. The test results indicated that chlorine ion diffusion is reduced for all replacement levels of fly ash. It is concluded that partial replacement of Kaolinite with fly ash up to 20% is acceptable as diffusion of Chlorine ion increased beyond this replacement level. Key Words: kaolinite , Flyash , Liner,Diffusion 1.INTRODUCTION 1.1General Landfillsarethemostpopularmunicipalsolidwaste disposal system The design of liner is made so as to isolate the waste from the environmentminimizingthe passage of leachate into the groundwater. To ensure thistheimportantcharacteristicsforcompactedlandfill linersareselectionofmaterials,hydraulicconductivity, strength, compressibility and contaminant retention capacity. Usually soil rich in clay minerals are used as compacted liner materials for their low hydraulic conductivity. . Fly ash is generated in tons as a residue from burning of coal in the power plants .Utilization of this waste material has high environmental value. By compacting the fly ash-clay mixture at the optimum range of dry density and moisture content the bonding between the particles is enhanced which in turn increases the strength and longevity of the liner. The bulkavailabilityofflyashhelpsreducingthecostofraw materials required for liner as well as providing their safe disposal in a large scale. 1.2 DIFFUSION At any temperature different from absolute zero, all atoms, irrespective of their state of aggregation (gaseous,Liquid,orsolid)areconstantly inmotion.Since the movementof particlesis associatedwithcollisions, the path of a single particle is a zigzag one.However , an aggregation of diffusing particles has an observable drift from places of higher to places of lower concentration .Due to this diffusion is known as transport phenomenon. Fig I: Symbolic representation of diffusion (Craig H. Benson et al(1994)) In a diffusion reaction, the flux(matter,heat, electricity…) follow the general relation: Flux=(conductivity) x (driving force) In the case of atomic and molecular diffusion, the conductivity is referred to as the fiffusivity or the diffusion constant and is represented by the symbol D. The driving force for many types of diffusion is the existence of a concentration gradient.The diffusion coefficient is calculated using the equation =erf [ -concentration ratio
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 5053 D –Diffusion coefficient (m2/s) T – Thickness of GCL sample C1-Source tank concentration(mg/l) C2-Reciever tank concentration(mg/l) Objective of the study.  To investigate the basic characterization Kaolinite and flyash  To study compaction characteristics of kaolinite-flyash liner.  To evaluate diffusion characteristics of same. 2.MATERIALS AND METHODOLOGY Materials Kaolinite:Bentoniteforthepresentstudywascollected from Associate Chemicals,Kochi Flyash: Flyash taken from tamil nadu Table 2:Initial properties of flyash Properties Values Specific gravity 2 Liquid Limit 29 Plastic limit Non plastic Plasticity index Non plastic Percentage clay(%) 16.25 Percentage silt(%) 29.75 Percentage sand(%) 46 OMC(%) 31.3 Dry density 1.16 UCC(kg/cc) .94 Table I:Initial properties of Kaolinite Methodology Compaction test: The test to determine the optimum moisture content andmaximumdrydensityweredone using standard proctor test according to IS 2720. 1980 (Part VIII). The variation in optimum moisturecontent and maximum dry density was studied with the addition of various percentages . Diffusion test: Procedure  Two reservoirs(connected with a pipe) are filled with distilled water  soil specimen placed in the middle of the pipe  Allow saturation of specimen for 48hours  Add any solute of known concentration in one of the reservoir  Using titrationmethodchecktheconcentration of solute in both reservoirs in different time intervals Properties Kaolinite Specific gravity 2.67 Liquid limit (%) (IS 2720 PART 51985) 34 Plastic limit (%) ( IS 2720 PART 51985) 23 Plastic index (%) (IS 2720 PART 51985) 11 Shrinkage limit (%) (IS 2720 PART 51985) 21 IS Classification CL Natural moisture content (%) - Optimum moisture content (%) (IS 2720 PART 7) 24.5 Maximum dry density (g/cc) (IS 2720 PART 7) 1.424 Percentage of clay (IS 2720 PART 4) 66 Percentage of silt (IS 2720 PART 4) 23 Percentage of sand (IS 2720 PART 4) 11 UCC strength (kg/cm2) (IS 2720 PART 10) .468
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 5054 Fig 2: Diffusion mould RESULTS compaction results The value of OMC and MDD obtained from laboratory compaction test provides a reference point while estimating the actual water content of the field- compacted soil liner. If the water content is not in the proper range, the engineering propertiesofthesoilare not likely to be in the range desired. For example, if the soil is too wet, the shear strength of the soil may be too low. Similarly, the dry unit weight of the field- compacted soil may be compared to the maximum dry unit weight determined from a specified laboratory compaction test Table 4: compaction characteristics of kaolinite flyash mixture % replacement of flyash MDD OMC kaolinite +0% fly ash 1.424 24.5 kaolinite +10% flyash 1.5 24 kaolinite +15% flyash 1.59 23.6 kaolinite + 20% flyash 1.63 23 kaolinite + 25% flyash 1.6 23.2 kaolinite +30% flyash 1.53 23.6 Diffusion results From these test results it can be understood that partial replacement of clay by fly ash decreases the diffusion coefficient. The reason for this can be attributed to the factthatpartialreplacementofclayby fly ash makes the clay-fly ash matrix more cohesive as the fly ash particles are finer and act as ball bearing while getting mixed with bentonite. The decrease in Diffusion coefficient of the resulting modified CCL will provide better performance as liner. The replacement of bentonite by fly ash cannot be continued as this replacementincreasesthepermeabilityoftheresulting CCL. CONCLUSIONS Based on the laboratory tests conducted the following conclusions are drawn. 1. Partial replacement of bentonite and kaolinite byfly ash decreases the coefficient of diffusion . 2. Partial replacement of kaolinite as well as bentonite by fly ash is an encouraging aspect from the performance point of view of CCL; however, this replacement level shall be restricted to 25%, as permeability of modified CCL increases adversely beyond this replacement level. % Of Flyash Diffusion Coefficient Of Cl Ions 0 4.2*10^-10 10 3.9*10^-10 25 2.8*10^-10 30 2.98*10^-10
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 03 | Mar 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 5055 References 1) Alam .J et al(2012).Seepage characteristics and Geotechnical properties of flyash mixed with bentonite,International journal of scientific and research ,volume 3,issue 8 2) Andal Mudimby et al.(2012),ConcreteConfinement with Textile-Reinforced Mortar Jackets, ACI Structural Journal, Vol.103, No.1, pp 28-37 3) K.Badv and R.Farsimadan (2009),Swelling and diffusion characteristics of the experimental GCLs. 4) Erdal Cokca,Zeka Yilmaz (2004),Use of rubber and bentonite added flyash as a liner material,waste management ,pp153-164. 5) Kristin.M.Sample-Lord et al.(2016)solute diffusion in bentonite pastes,Journal of Geotechnical and Geoenvironmental engineering,ASCE. 6) Nayak et al.(2015),Assesment of coal ash-bentonite mixture as landfill liner,Indian Geotechnical Conference. 7) PuvvadiV.Sivapullaih and Vandana Sreedharan(2012) ,Organically modified bentonite as a part of Geosynthetic clay liner system,Geosynthetics. 8) L.R. Van Loon, J.M. Soler (2004), Diffusion of HTO, 36Cl-, 125I-, and 22Na+ in Opalinus Clay: Effect of confining pressure, sample orientation, sample depth and temperature, PSI-BerichtNr.04-03,Paul- Scherrer-Institute, Villigen, Switzerland. 9) P.M.H. Kau, P.J. Binning, P.W. Hitchcock and D.W. Smith (1999), Experimental analysis of fluoride diffusion and sorption in clays, J. Contam. Hydrol. 36, 131-151 Dresden, Germany