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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 04 Issue: 12 | Dec-2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 691
Effect of Iron on Some Geotechnical Properties of Clays
Rintu Molly John1, Rani V2
1M.Tech Student, Marian Engineering College, Kazhakootam, Trivandrum, Kerala
2Associate Professor, Marian Engineering College, Kazhakootam, Trivandrum, Kerala
---------------------------------------------------------------------***---------------------------------------------------------------------
Abstract – Urbanization and industrial development hasled
to an increase in risk of environmental pollution. Heavy metal
contamination is a very serious threat faced by the
environment currently. Most of the heavy metals are toxic in
nature but are required in trace amounts by humans, animals
and plants. Iron is one such heavy metal which is essential but
at the same time in excess can cause contamination. This
paper studies the effect of iron on the liquid limit, plastic limit
and hydraulic conductivities of two soils. The resultsshowthat
iron tended to reduce the permeability of the soils. The liquid
limit and plastic limit was found to increase for CL clay
whereas for CH clay both the limits initially decreased and
then showed an increasing trend.
Key Words: Contamination, heavy metal, iron,
hydraulic conductivity, liquid limit, plastic limit
1. INTRODUCTION
The accelerated development of industries and
urbanization has led to an exponential increase in the
generation of waste and pollutants. The lack of proper
disposal facilities as well as the careless attitude of man has
led to the release and accumulation of pollutants into the
environment. These wastesmay compriseofbothhazardous
and non-hazardous wastes. Out of the hazardous wastes,
majority of it is constituted by heavy metals which mostly
are toxic and carcinogenic in nature.
Iron is one among the oldest heavy metals existing on
earth. It is a heavy metal which is essential for the
environment as a hole. It is required by plants, animals and
humans for their bodily metabolism and growth. A
deficiency of iron can cause anaemia whereas excess iron
can cause various health problemsincludinggastrointestinal
irritations and even cancer. Excess iron can also causesoilas
well as underground water contamination. The presence of
iron in soil can also result in the alteration of soil properties.
Therefore, it is important that the effect of this heavy metal
on soils be studied.
This paper deals with the study of how iron can alter the
liquid limit, plastic limit and hydraulic conductivities of two
soils; one of low plasticity (CL) and another of high plasticity
(CH).
2. METHODOLOGY
2.1 Materials used
Two soilswere used in this study. One wasa highplasticclay
(CH) acquired from a quarry in Coimbatore and the second
was of low plasticity (CL) obtained from Thonnakkal,
Trivandrum. The images of the soils used are shown in fig 1
and fig 2 and its index properties are given in table 1 and
table 2.
In order to artificially contaminate these soils, anhydrous
ferric chloride wasused. It was greenish blackinappearance
with a molecular mass of 162.21 g/mol. The contaminant is
shown in fig 3.
Table -1: Properties of CH soil
Properties Values
Specific gravity 2.24
pH 8.8
Permeability (cm/sec) 4.704 x10-7
Liquid limit (%) 127
Plastic limit (%) 41.66
Plasticity index (%) 85.34
IS classification CH
Optimum moisture content (%) 18.3
Dry density (g/cc) 1.31
% clay 60
% silt 40
UCC strength (kN/m2) 50.717
Table -2: Properties of CL soil
Properties Values
Specific gravity 2.64
pH 6.5
Permeability (cm/sec) 5.88 x 10-7
Liquid limit (%) 33.5
Plastic limit (%) 21.8
Plasticity index (%) 11.7
IS classification CL
Optimum moisture content (%) 23
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 04 Issue: 12 | Dec-2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 692
Dry density (g/cc) 1.591
% clay 59.2
% silt 29.1
% sand 11.7
UCC strength (kN/m2) 63.274
Fig -1: CH soil
Fig -2: CL soil
Fig -3: Anhydrous ferric chloride
2.2 Test procedure
The soils were contaminated with various molarities of
ferric chloride solutions; 0.05M, 0.1M, 0.2M, 0.3M, 0.4M and
0.5M. The liquid limit and plastic limit tests were carriedout
as per the procedure specified in IS 2720 PART 5. The
hydraulic conductivity test was performed according to IS
2720 PART 17.
2.3 Results and Discussions
Table 3 shows the results of the liquid limit test upon the
addition of ferric chloride and chart 1 represents the
variation.
Table -3: Liquid limit variation
MOLARITY CH CL
0 127 33.5
0.05 64.6 36
0.1 57.6 37.5
0.2 56.2 41.5
0.3 75.4 42.12
0.4 76.8 44.8
0.5 79.6 47.25
Liquid limit generally increases for CLclaywithincreasein
concentration of ferric chloride. This is in accordance with
the findingsof Arasan and Yetimoglu (2007). Theincreasein
liquid limit is due to dispersion of the clay particles when
permeated with ferric chloride solution. Also, the salt
solution must have caused the formation of new swelling
compounds which may have increased the liquid limit.
The liquid limit for CH clay decreased up to 0.2M, andthen
increased with increase in concentration of solution. The
solution tended to decrease the double layer thickness and
flocculate the clay particle, thus reducing the liquid limit.
Chart -1: Liquid limit variation of both soils
Table 4 shows the plastic limit variaton of the soils after
being contaminated with ferric chloride. The representation
of the above results is given by chart 2.
Table -4: Plastic limit variation
MOLARITY CH CL
0 41.66 21.8
0.05 37.84 23.5
0.1 36.6 24.35
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 04 Issue: 12 | Dec-2017 www.irjet.net p-ISSN: 2395-0072
© 2017, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 693
0.2 31.97 32.8
0.3 27.127 36.26
0.4 28.22 37.5
0.5 30.722 40.437
Chart -2: Plastic limit variation of both soils
The plastic limit increases with increase in concentration
of ferric chloride solution, which is in agreement with the
findings of Arasan and Yetimoglu (2007). The increase can
be as a result of dispersion of clay particle and formation of
new swelling compounds when the solution is added to it.
For CH clay, the plastic limit decreased initially and then
increased with increase in concentration of solution. The
reason for this trend can be explained by the flocculation of
clay particles due to reduction in double layer thickness.
Table 5 shows the variation in hydraulic conductivity
with the addition of the contaminant.
Table -5: Variation in hydraulic conductivity
MOLARITY
CH (x10-8
cm/sec)
CL (x10-8
cm/sec)
0 47.04 58.8
0.05 0.6439 0.276
0.1 0.865 0.801
0.2 1.799 1.56
0.3 1.196 2.21
0.4 1.2 2.385
0.5 1.241 2.46
The permeability of soil decreased by two orders,i.e.,from
10-7 to 10-9, when iron was added. But with increasing
concentration of ferric chloride, a slight increase in
permeability is observed. The increase in hydraulic
conductivity when the concentration of the salt solutionwas
increased can be attributed to the decrease in the thickness
of DDL, resulting in flocculation of the clay particles and
consequently high void ratio. This is in agreement with the
study conducted by Arasan (2010).
3. CONCLUSIONS
Iron is a heavy metal which is very essential for humans,
plants and animals. But in excess, it can cause soil as well as
water contamination. When it comes to the case of soils, it
can also lead to the alteration of soil properties. The
variation in liquid limit, plastic limit and hydraulic
conductivity was studied and the conclusions drawn are:
 An increase in liquid limit of 41%wasobservedforCL
clay and a decrease by 50% for CH clay.
 The plastic limit decreased by 35% for CH clay and
increased by almost 85% for CL clay.
 Permeability decreased by two orders, i.e., from 10-7
to 10-9 cm/sec on the addition of the contaminant,
then asthe concentration of contaminant increased, a
slight increase in permeability was observed, but still
lower than that of virgin soil.
REFERENCES
[1] Arasan, S., (2010). “Effect of Chemicals on Geotechnical
Propertiesof Clay Liners: A Review.”ResearchJournalof
Applied Sciences, Engineering and Technology, 2(8):
765-775.
[2] Arasan, S., Akbulut, R. K., Yetimoglu, T., and Yilmaz, G.,
(2010). “Swelling Pressure of Compacted Clay Liners
Contaminated with Inorganic Salt Solutions.”
Environmental & Engineering Geoscience, Vol. XVI, No.
4, pp 401-409.
[3] Deka, J., and Sarma, H. P., (2012). “Heavy metal
contamination in soil in an industrial zone and its
relation with some soil properties.” Archives of Applied
Science Research, 4 (2), pp 831-836.
[4] Raju, N. J., (2006). “Iron Contamination in Groundwater:
A case from Tirumala-Tirupati environs, India.” The
Researcher, Vol. 01, No. 01, pp 32-35.
[5] Singh, S., and Prasad, A., (2010). “Influence of ferric
chloride and humic acid on bentonite as clay liner.”
International Journal of Geotechnical Engineering, 4:1,
pp 45-53.
[6] Strezov, V., and Chaudhary, C., (2017). “Impacts of iron
and steelmaking facilities on soil quality.” Journal of
Environmental Management, pp 1-5.

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Effect of Iron on Some Geotechnical Properties of Clays

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 04 Issue: 12 | Dec-2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 691 Effect of Iron on Some Geotechnical Properties of Clays Rintu Molly John1, Rani V2 1M.Tech Student, Marian Engineering College, Kazhakootam, Trivandrum, Kerala 2Associate Professor, Marian Engineering College, Kazhakootam, Trivandrum, Kerala ---------------------------------------------------------------------***--------------------------------------------------------------------- Abstract – Urbanization and industrial development hasled to an increase in risk of environmental pollution. Heavy metal contamination is a very serious threat faced by the environment currently. Most of the heavy metals are toxic in nature but are required in trace amounts by humans, animals and plants. Iron is one such heavy metal which is essential but at the same time in excess can cause contamination. This paper studies the effect of iron on the liquid limit, plastic limit and hydraulic conductivities of two soils. The resultsshowthat iron tended to reduce the permeability of the soils. The liquid limit and plastic limit was found to increase for CL clay whereas for CH clay both the limits initially decreased and then showed an increasing trend. Key Words: Contamination, heavy metal, iron, hydraulic conductivity, liquid limit, plastic limit 1. INTRODUCTION The accelerated development of industries and urbanization has led to an exponential increase in the generation of waste and pollutants. The lack of proper disposal facilities as well as the careless attitude of man has led to the release and accumulation of pollutants into the environment. These wastesmay compriseofbothhazardous and non-hazardous wastes. Out of the hazardous wastes, majority of it is constituted by heavy metals which mostly are toxic and carcinogenic in nature. Iron is one among the oldest heavy metals existing on earth. It is a heavy metal which is essential for the environment as a hole. It is required by plants, animals and humans for their bodily metabolism and growth. A deficiency of iron can cause anaemia whereas excess iron can cause various health problemsincludinggastrointestinal irritations and even cancer. Excess iron can also causesoilas well as underground water contamination. The presence of iron in soil can also result in the alteration of soil properties. Therefore, it is important that the effect of this heavy metal on soils be studied. This paper deals with the study of how iron can alter the liquid limit, plastic limit and hydraulic conductivities of two soils; one of low plasticity (CL) and another of high plasticity (CH). 2. METHODOLOGY 2.1 Materials used Two soilswere used in this study. One wasa highplasticclay (CH) acquired from a quarry in Coimbatore and the second was of low plasticity (CL) obtained from Thonnakkal, Trivandrum. The images of the soils used are shown in fig 1 and fig 2 and its index properties are given in table 1 and table 2. In order to artificially contaminate these soils, anhydrous ferric chloride wasused. It was greenish blackinappearance with a molecular mass of 162.21 g/mol. The contaminant is shown in fig 3. Table -1: Properties of CH soil Properties Values Specific gravity 2.24 pH 8.8 Permeability (cm/sec) 4.704 x10-7 Liquid limit (%) 127 Plastic limit (%) 41.66 Plasticity index (%) 85.34 IS classification CH Optimum moisture content (%) 18.3 Dry density (g/cc) 1.31 % clay 60 % silt 40 UCC strength (kN/m2) 50.717 Table -2: Properties of CL soil Properties Values Specific gravity 2.64 pH 6.5 Permeability (cm/sec) 5.88 x 10-7 Liquid limit (%) 33.5 Plastic limit (%) 21.8 Plasticity index (%) 11.7 IS classification CL Optimum moisture content (%) 23
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 04 Issue: 12 | Dec-2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 692 Dry density (g/cc) 1.591 % clay 59.2 % silt 29.1 % sand 11.7 UCC strength (kN/m2) 63.274 Fig -1: CH soil Fig -2: CL soil Fig -3: Anhydrous ferric chloride 2.2 Test procedure The soils were contaminated with various molarities of ferric chloride solutions; 0.05M, 0.1M, 0.2M, 0.3M, 0.4M and 0.5M. The liquid limit and plastic limit tests were carriedout as per the procedure specified in IS 2720 PART 5. The hydraulic conductivity test was performed according to IS 2720 PART 17. 2.3 Results and Discussions Table 3 shows the results of the liquid limit test upon the addition of ferric chloride and chart 1 represents the variation. Table -3: Liquid limit variation MOLARITY CH CL 0 127 33.5 0.05 64.6 36 0.1 57.6 37.5 0.2 56.2 41.5 0.3 75.4 42.12 0.4 76.8 44.8 0.5 79.6 47.25 Liquid limit generally increases for CLclaywithincreasein concentration of ferric chloride. This is in accordance with the findingsof Arasan and Yetimoglu (2007). Theincreasein liquid limit is due to dispersion of the clay particles when permeated with ferric chloride solution. Also, the salt solution must have caused the formation of new swelling compounds which may have increased the liquid limit. The liquid limit for CH clay decreased up to 0.2M, andthen increased with increase in concentration of solution. The solution tended to decrease the double layer thickness and flocculate the clay particle, thus reducing the liquid limit. Chart -1: Liquid limit variation of both soils Table 4 shows the plastic limit variaton of the soils after being contaminated with ferric chloride. The representation of the above results is given by chart 2. Table -4: Plastic limit variation MOLARITY CH CL 0 41.66 21.8 0.05 37.84 23.5 0.1 36.6 24.35
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 04 Issue: 12 | Dec-2017 www.irjet.net p-ISSN: 2395-0072 © 2017, IRJET | Impact Factor value: 6.171 | ISO 9001:2008 Certified Journal | Page 693 0.2 31.97 32.8 0.3 27.127 36.26 0.4 28.22 37.5 0.5 30.722 40.437 Chart -2: Plastic limit variation of both soils The plastic limit increases with increase in concentration of ferric chloride solution, which is in agreement with the findings of Arasan and Yetimoglu (2007). The increase can be as a result of dispersion of clay particle and formation of new swelling compounds when the solution is added to it. For CH clay, the plastic limit decreased initially and then increased with increase in concentration of solution. The reason for this trend can be explained by the flocculation of clay particles due to reduction in double layer thickness. Table 5 shows the variation in hydraulic conductivity with the addition of the contaminant. Table -5: Variation in hydraulic conductivity MOLARITY CH (x10-8 cm/sec) CL (x10-8 cm/sec) 0 47.04 58.8 0.05 0.6439 0.276 0.1 0.865 0.801 0.2 1.799 1.56 0.3 1.196 2.21 0.4 1.2 2.385 0.5 1.241 2.46 The permeability of soil decreased by two orders,i.e.,from 10-7 to 10-9, when iron was added. But with increasing concentration of ferric chloride, a slight increase in permeability is observed. The increase in hydraulic conductivity when the concentration of the salt solutionwas increased can be attributed to the decrease in the thickness of DDL, resulting in flocculation of the clay particles and consequently high void ratio. This is in agreement with the study conducted by Arasan (2010). 3. CONCLUSIONS Iron is a heavy metal which is very essential for humans, plants and animals. But in excess, it can cause soil as well as water contamination. When it comes to the case of soils, it can also lead to the alteration of soil properties. The variation in liquid limit, plastic limit and hydraulic conductivity was studied and the conclusions drawn are:  An increase in liquid limit of 41%wasobservedforCL clay and a decrease by 50% for CH clay.  The plastic limit decreased by 35% for CH clay and increased by almost 85% for CL clay.  Permeability decreased by two orders, i.e., from 10-7 to 10-9 cm/sec on the addition of the contaminant, then asthe concentration of contaminant increased, a slight increase in permeability was observed, but still lower than that of virgin soil. REFERENCES [1] Arasan, S., (2010). “Effect of Chemicals on Geotechnical Propertiesof Clay Liners: A Review.”ResearchJournalof Applied Sciences, Engineering and Technology, 2(8): 765-775. [2] Arasan, S., Akbulut, R. K., Yetimoglu, T., and Yilmaz, G., (2010). “Swelling Pressure of Compacted Clay Liners Contaminated with Inorganic Salt Solutions.” Environmental & Engineering Geoscience, Vol. XVI, No. 4, pp 401-409. [3] Deka, J., and Sarma, H. P., (2012). “Heavy metal contamination in soil in an industrial zone and its relation with some soil properties.” Archives of Applied Science Research, 4 (2), pp 831-836. [4] Raju, N. J., (2006). “Iron Contamination in Groundwater: A case from Tirumala-Tirupati environs, India.” The Researcher, Vol. 01, No. 01, pp 32-35. [5] Singh, S., and Prasad, A., (2010). “Influence of ferric chloride and humic acid on bentonite as clay liner.” International Journal of Geotechnical Engineering, 4:1, pp 45-53. [6] Strezov, V., and Chaudhary, C., (2017). “Impacts of iron and steelmaking facilities on soil quality.” Journal of Environmental Management, pp 1-5.