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INTERNATIONAL RESEARCH JOURNAL OF ENGINEERING AND TECHNOLOGY (IRJET) E-ISSN: 2395-0056
VOLUME: 06 ISSUE: 09 | SEP 2019 WWW.IRJET.NET P-ISSN: 2395-0072
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A REVIEW ON REMOVAL OF FLUORIDE IN WATER
K. GAYATRI JYOTSNA1, M. VINUTHNA2, M.V.V. CHANDANALAKSHMI3
1M.Tech, Department of Chemical Engineering, AUCE (A), Andhra University, A.P., India
2PhD, Department of Chemical Engineering, AUCE (A), Andhra University, A.P., India
3Professor, Department of Chemical Engineering, AUCE (A), Andhra University, A.P., India
--------------------------------------------------------------------***-----------------------------------------------------------------------
Abstract- Water is the main component for the survival of human being. The major sources of water are rivers, lakes, ponds,
tanks, and surface runoffs. Three fourth surface of the Earth is covered with water. For maintaining the fragile ecosystem, the
physiochemical parameters of the water bodies plays a very important role. These parameters are disturbed due to the
contaminants entering into the water bodies. Among the contaminants of water, Fluoride also causes a major contamination
in drinking water which is due to natural and anthropogenic activities that causes a serious threat to human as well as
animal health. So there is a need for the removal of fluoride from the drinking water. Current paper deals with a study of
removal methods of Fluoride from the water like coagulation and precipitation, reverse osmosis, nanofiltration,
electrodialysis, ion exchange, electrocoagulation and adsorption.
Keywords: Fluoride, Precipitation, Ion-exchange, Adsorption, electrocoagulation
1. INTRODUCTION:
Water is the most important component as it forms the basic medium for origin of life [1]. The water chemical composition
mainly depends on the utilization for domestic, industrial, and agricultural purposes. 0.6% of the total water resources is
covered with the ground water which is the suitable for drinking in rural and urban areas in India. But in the current days
ground water is getting polluted by the urbanization and industrialisation. The major pollutants are hydrocarbons, heavy
metals like nickel, fluorides, nitrates etc. which are effecting the human health.
Fluoride as a pollutant present in groundwater creates a major problem in drinking water supply. It exists either as
inorganic fluorides or organic fluoride compounds [2]. Depending on the concentration of the fluoride in drinking water, it
is either beneficial or detrimental to the human health [2, 3]. Fluoride is advantageous for bone and teeth mineralization,
maintenance of fertility, hematopoiesis, and enzymes activation, such as adenylate cyclase [4]. It is a known fact that a less
amount of fluoride intake decreases the vulnerability to dental caries in human beings [5]. A few decades ago, usage of
fluorinated toothpaste for prevention of dental caries was obsession, but soon it became outdated due to increasing
reports of ill effects on oral health such as the occurrence of perioral dermatitis [6]. According to WHO, the maximum
acceptable concentration of fluoride is 1.5 mg/l [7]. While India’s permissible limit of fluoride in drinking water is 1mg/l
[8].
2. SOURCES:
Fluorite, apatite, rock phosphate and topaz igneous and sedimentary rocks are the most common natural fluorine bearing
minerals that constitutes source of fluoride in drinking water [9]. Milk is usually responsible for the exposure of fluoride in
small quantity. Fluoride is consumed due to ingestion of tea which is reported in a range of 0.04 mg to 2.7 mg per person
per day [10]. Occurrence of alkaline soil around the fluoride contaminated water sources is the outstanding feature of the
fluoride affected areas [11]. The main sources of fluoride can be broadly divided into two categories:
1) Natural sources :
 Forage grasses and grains
 Water
 Volcanic activities
2) Anthropogenic sources
 Mineral Mixture and Other Feed Supplements
 Airborne Fluoride
 Industrial Effluents
 Agrochemicals and Household Products
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3. HEALTH EFFECTS:
Several investigators had reviewed that, during the last 5-6 years the life-long impact and accumulation of fluorides causes
human skeletal and teeth damage and also the changes in DNA-structure, paralysis of volition, cancer, etc. [12]. Susheela
reported the effect of fluoride contamination on human health like aches and pain in the joints, viz. neck, back, hip,
shoulder and knee without visible signs of accumulation; non-ulcer dyspepsia, viz. nausea, vomiting, pain in the stomach,
bloated feeling/ gas formation in the stomach, constipation followed by diarrhea, etc.[13]. Czarnowski et.al. explained that
increase in fluoride intake, have an impact on the bone density, urine and hair of the human being. [14].
Table: 1 Permissible limit of fluoride of drinking water [15]
Name of the Organization Desirable Limits
Bureau of Indian Standards 0.6-1.2
Indian Council of Medical Research 1.0
The Committee on Public Health Engineering Manual and
Code Practice, Government of India.
1.0
World Health Organization (International Standards for
Drinking Water)
1.5
The fluoride intake will effect both human health as well as animals:
3.1 HUMAN HEALTH:
3.1.1 Dental Fluorosis:
In dental fluorosis, enamel of the teeth loses its luster due to large amount of fluoride intake during permanent dentition,
and it mostly affects children. The mild form of dental fluorosis is recognised by chalky white teeth, whereas yellowish
brown pigmentation in the middle of the teeth and severe pitting of the teeth. The effect of dental fluorosis may not be
apparent if the teeth are already fully grown prior to the fluoride over exposure. Therefore, the fact that an adult shows no
signs of dental fluorosis does not necessarily mean that his or her fluoride intake is within the safety limit.
3.1.2 Skeletal Fluorosis:
Skeletal fluorosis affects both children and adults. It does not manifest until the disease attains an advanced stage. In the
early stages of skeletal fluorosis, patients complain of arthritic symptoms. Fluoride gets deposited in joints of shoulder
bones, neck and pelvic, and knees and makes it difficult to move, walk, and bend. In later stages, skeletal fluorosis is
marked by restriction of spine movements and, hence, can be easily diagnosed. The advanced stage is osteoporosis.
3.1.3 Nonskeletal Fluorosis/Other Problems:
Besides skeletal and dental fluorosis, excessive consumption of fluoride may lead to muscle fiber degeneration, low
hemoglobin levels, deformities in RBCs (red blood corpuscles), excessive thirst, headache, skin rashes, nervousness,
neurological manifestations (it affects brain tissue similar to the pathological changes found in humans with Alzheimer’s
disease), depression, gastrointestinal problems, urinary tract disorders, nausea, abdominal pain, tingling sensation in
fingers and toes, reduced immunity, repeated miscarriages or still births, male sterility, etc. It is also responsible for
alterations in the functional mechanisms of liver, kidney, digestive system, respiratory system, excretory system.
3.2 ANIMAL HEALTH:
Almost all terrestrial and aquatic animals are susceptible to high doses of fluoride, although the tolerance level varies from
one species to another. For terrestrial animals, important sources of excess fluoride intake include drinking water, soil, or
vegetation naturally containing excess soluble fluoride compounds or contaminated with fluoride compounds emitted by
volcanic eruptions or industrial activities.
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3.2.1 Invertebrates:
Many invertebrates are highly susceptible to fluoride toxicity. Honeybees and silkworm larvae are highly susceptible to
fluoride toxicity; the silk industry in several countries has been badly affected by industrial fluoride pollution [16,17].
Aquatic invertebrates and vertebrates including fish are also susceptible to fluoride toxicity. In general, freshwater or
softwater-dwelling aquatic animals have -lower fluoride tolerance than marine or hardwater-dwelling animals [18].
3.2.2 Vertebrates:
Among terrestrial vertebrates, herbivores are more susceptible than carnivores and other animals occupying an upper
position in the food pyramid. Domestic and wild herbivores are more exposed to environmental contaminants as they are
nonselective eaters and can consume contaminated feed, forage, and water.
It is thus required to bring the concentration of fluoride to required level. So here are some article reviews of the various
techniques available for the removal of fluoride from water.
4. METHODS FOR DEFLUORIDATION OF WATER
Surendra roy et.al. [19] said that the fluoride contaminated groundwater used for drinking purposes should be determined
examined and accordingly a suitable method can be chosen for its treatment.
Sl.no Removal
Method
Process Advantages Disadvantages Name of the
Author
Medium used Reference
numbers
1 Coagulation
and
Precipitation
Involves the
addition of
chemicals
and the
formation of
fluoride
precipitates
1. Commonly
used
2. It is more
practical.
3. Easy to
understand
1. Low
treatment
efficiency upto
70%
2.Requirement
of large dosage
of chemicals for
treatment.
3.Requirement
of skilled
manpower
Meenakshi
et.al.,
Lawler,D.F.
et.al.,
Larsen,M.J.
et.al.,
Qafas,Z.et.al.,
Dahi,E et.al.,
Aldaco et.al.
Aluminium sulfate
and lime (NEERI
METHOD),salts of
Calcium,
aluminium and
iron, bone char
combined with
sodium
dihydrogen
phosphate and
calcium chloride,
granular calcite.
20-25
2 Reverse
Osmosis
It is a
physical
process in
which the
anions are
removed by
applying
pressure on
the feed
water to
direct it
through the
semi
permeable
membrane.
1.Membrane
can be
completely
recovered
after every
arrangement
of
examination.
2.This can
remove 90%
of fluoride
regardless of
initial
concentration
1.Non
attainable for
rural regions.
2. Very
expensive.
3.Skilled labor
required.
4.Need pH
improvement.
Ndiaye et.al.
Behanu et.al
Gedam et.al.
Diawara et.al.
1. RO membrane
of Ethiopian Rift
Region,
2.Polyamide RO
Membrane,
3.Low Pressure
RO
26-29
3 Nano
Filtration
It removes
the larger
dissolved
solids when
compared
with RO.
1. High
productivity.
2. No
Chemicals
needed.
3.used for
wide range of
pH.
1. Highly
expensive
technique.
2. Prone to
fouling, scaling
or membrane
degradation.
Tahaikt et.al.
Pontie et.al.
Bejaoui et.al.
1.NF90 2.NF400. 30-32
4 Electro-
dialysis
Removal of
ionic
components
1. Flexible
2.low
chemical
1. Only
separation of
Ionic
Adhikary et.al.
Amor et.al.
Annour et.al.
used this method
in the combination
of chitosan with
33-39
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from
aqueous
solutions
through ion
exchange
membranes
under the
driving force
of an electric
current
request.
3.High water
recovery.
Components.
2. Specific
power
consumption
for Pumping.
3.Necessity of
concentrate
treatment.
Sahli et.al.
Kabay et.al.
Ergun et.al.
Lahnid et.al.
the help of CMX-
ACS membranes,
others used the
combination of
electrodialysis and
anion exchanger.
5 Ion
Exchange
Fluoride can
be removed
from water
supplies with
a strongly
fundamental
anion-
exchange
resin
containing
quartenary
ammonium
functional
groups.
1.Removes
fluoride upto
90-95 %.
2.Retains the
taste and
color of water
intact
1. Presence of
sulfate,
phosphate,
bicarbonate,
etc. results in
ionic
competition.
2. Relatively
higher cost.
3. Treated
water
sometimes has
a low pH and
high levels of
chlorides.
Mohan Rao
et.al.
Haron et.al.
Castel et.al.
Zhou et.al.
yttrium loaded
poly(hydroxamic
acid)
resin,lanthanum-
impregnate cross
linked gelatin
40-43
6 Electro-
coagulation
Technique
for applying
direct
current to
sacrificial
electrodes
that are
submerged in
an aqueous
solution.
1.obliges
basic
equipment
2.simple to
handle
3.less support
cost
4.treated
water is
consumable,
colorless and
odourless
1.electrodes
should be
consistently
supplanted
2.utilizes high
electricity
3. Loss of
productivity
due to the
formation of
oxide film on
the cathode.
Yang et.al.
Feng Shen et.al.
Drouiche et.al.
Un et al.
Bennajah et al.
Aluminium
electrodes,
Iron cylindrical
reactor as anode,
44-47
6 Adsorption Adsorption is
the bond of
molecules
species from
bulk solution
for a surface
of a solid by
physical or
chemical
forces.
1. Ease of
operation.
2.Adsorption
procedure in
worthwhile
3. High
productivity
for fluoride
removal and
can remove
up to 90%
fluoride.
4. Cost
effective.
5. Produce
high quality
water.
6.
Regeneration
is conceivable.
1. Process is
dependent on
pH.
2. Regeneration
is required.
3. Disposal of
fluoride-laden
material.
Kariyanna et.al.
J.P. Barbier
et.al.,
Muthukumaran
et..al.,
Rongshu et.al.,
Y.Min et.al.,
Y. Wang et.al.,
Nava et.al.,
Padmavathy
et.al.
Theragaonkar
et.al.
Gandhi et.al.
Mohapatra et.al.
Amit Bhatnagar
et.al.
Prins Satish
et.al.
Activated alumina,
activated carbon
coated with silica
gel, calcite,
activated saw
dust, activated
coconut shell
powder, activated
fly ash, groundnut
shell, coffee husk,
rice husk,
magnesia,
serpentine, bone
charcoal, orange
peel, chalk powder
48-60
5. CONCLUSION:
A large number of factors and geological conditions influence the correlations between different pairs of physio-chemical
parameters of water samples directly or indirectly. Some parameters are directly measured by their respective measuring
equipments, some are determined by titrimetric methods and some elements like fluorides are to be treated by various
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methods. As there is a need for the treatment of fluoride present in water, which causes lot of problems. The method for
treatment of fluoride can be chosen as per the advantages and limitations, among which adsorption is the best process for
the removal of fluoride from water according to the study.
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IRJET- A Review on Removal of Fluoride in Water

  • 1. INTERNATIONAL RESEARCH JOURNAL OF ENGINEERING AND TECHNOLOGY (IRJET) E-ISSN: 2395-0056 VOLUME: 06 ISSUE: 09 | SEP 2019 WWW.IRJET.NET P-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 1506 A REVIEW ON REMOVAL OF FLUORIDE IN WATER K. GAYATRI JYOTSNA1, M. VINUTHNA2, M.V.V. CHANDANALAKSHMI3 1M.Tech, Department of Chemical Engineering, AUCE (A), Andhra University, A.P., India 2PhD, Department of Chemical Engineering, AUCE (A), Andhra University, A.P., India 3Professor, Department of Chemical Engineering, AUCE (A), Andhra University, A.P., India --------------------------------------------------------------------***----------------------------------------------------------------------- Abstract- Water is the main component for the survival of human being. The major sources of water are rivers, lakes, ponds, tanks, and surface runoffs. Three fourth surface of the Earth is covered with water. For maintaining the fragile ecosystem, the physiochemical parameters of the water bodies plays a very important role. These parameters are disturbed due to the contaminants entering into the water bodies. Among the contaminants of water, Fluoride also causes a major contamination in drinking water which is due to natural and anthropogenic activities that causes a serious threat to human as well as animal health. So there is a need for the removal of fluoride from the drinking water. Current paper deals with a study of removal methods of Fluoride from the water like coagulation and precipitation, reverse osmosis, nanofiltration, electrodialysis, ion exchange, electrocoagulation and adsorption. Keywords: Fluoride, Precipitation, Ion-exchange, Adsorption, electrocoagulation 1. INTRODUCTION: Water is the most important component as it forms the basic medium for origin of life [1]. The water chemical composition mainly depends on the utilization for domestic, industrial, and agricultural purposes. 0.6% of the total water resources is covered with the ground water which is the suitable for drinking in rural and urban areas in India. But in the current days ground water is getting polluted by the urbanization and industrialisation. The major pollutants are hydrocarbons, heavy metals like nickel, fluorides, nitrates etc. which are effecting the human health. Fluoride as a pollutant present in groundwater creates a major problem in drinking water supply. It exists either as inorganic fluorides or organic fluoride compounds [2]. Depending on the concentration of the fluoride in drinking water, it is either beneficial or detrimental to the human health [2, 3]. Fluoride is advantageous for bone and teeth mineralization, maintenance of fertility, hematopoiesis, and enzymes activation, such as adenylate cyclase [4]. It is a known fact that a less amount of fluoride intake decreases the vulnerability to dental caries in human beings [5]. A few decades ago, usage of fluorinated toothpaste for prevention of dental caries was obsession, but soon it became outdated due to increasing reports of ill effects on oral health such as the occurrence of perioral dermatitis [6]. According to WHO, the maximum acceptable concentration of fluoride is 1.5 mg/l [7]. While India’s permissible limit of fluoride in drinking water is 1mg/l [8]. 2. SOURCES: Fluorite, apatite, rock phosphate and topaz igneous and sedimentary rocks are the most common natural fluorine bearing minerals that constitutes source of fluoride in drinking water [9]. Milk is usually responsible for the exposure of fluoride in small quantity. Fluoride is consumed due to ingestion of tea which is reported in a range of 0.04 mg to 2.7 mg per person per day [10]. Occurrence of alkaline soil around the fluoride contaminated water sources is the outstanding feature of the fluoride affected areas [11]. The main sources of fluoride can be broadly divided into two categories: 1) Natural sources :  Forage grasses and grains  Water  Volcanic activities 2) Anthropogenic sources  Mineral Mixture and Other Feed Supplements  Airborne Fluoride  Industrial Effluents  Agrochemicals and Household Products
  • 2. INTERNATIONAL RESEARCH JOURNAL OF ENGINEERING AND TECHNOLOGY (IRJET) E-ISSN: 2395-0056 VOLUME: 06 ISSUE: 09 | SEP 2019 WWW.IRJET.NET P-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 1507 3. HEALTH EFFECTS: Several investigators had reviewed that, during the last 5-6 years the life-long impact and accumulation of fluorides causes human skeletal and teeth damage and also the changes in DNA-structure, paralysis of volition, cancer, etc. [12]. Susheela reported the effect of fluoride contamination on human health like aches and pain in the joints, viz. neck, back, hip, shoulder and knee without visible signs of accumulation; non-ulcer dyspepsia, viz. nausea, vomiting, pain in the stomach, bloated feeling/ gas formation in the stomach, constipation followed by diarrhea, etc.[13]. Czarnowski et.al. explained that increase in fluoride intake, have an impact on the bone density, urine and hair of the human being. [14]. Table: 1 Permissible limit of fluoride of drinking water [15] Name of the Organization Desirable Limits Bureau of Indian Standards 0.6-1.2 Indian Council of Medical Research 1.0 The Committee on Public Health Engineering Manual and Code Practice, Government of India. 1.0 World Health Organization (International Standards for Drinking Water) 1.5 The fluoride intake will effect both human health as well as animals: 3.1 HUMAN HEALTH: 3.1.1 Dental Fluorosis: In dental fluorosis, enamel of the teeth loses its luster due to large amount of fluoride intake during permanent dentition, and it mostly affects children. The mild form of dental fluorosis is recognised by chalky white teeth, whereas yellowish brown pigmentation in the middle of the teeth and severe pitting of the teeth. The effect of dental fluorosis may not be apparent if the teeth are already fully grown prior to the fluoride over exposure. Therefore, the fact that an adult shows no signs of dental fluorosis does not necessarily mean that his or her fluoride intake is within the safety limit. 3.1.2 Skeletal Fluorosis: Skeletal fluorosis affects both children and adults. It does not manifest until the disease attains an advanced stage. In the early stages of skeletal fluorosis, patients complain of arthritic symptoms. Fluoride gets deposited in joints of shoulder bones, neck and pelvic, and knees and makes it difficult to move, walk, and bend. In later stages, skeletal fluorosis is marked by restriction of spine movements and, hence, can be easily diagnosed. The advanced stage is osteoporosis. 3.1.3 Nonskeletal Fluorosis/Other Problems: Besides skeletal and dental fluorosis, excessive consumption of fluoride may lead to muscle fiber degeneration, low hemoglobin levels, deformities in RBCs (red blood corpuscles), excessive thirst, headache, skin rashes, nervousness, neurological manifestations (it affects brain tissue similar to the pathological changes found in humans with Alzheimer’s disease), depression, gastrointestinal problems, urinary tract disorders, nausea, abdominal pain, tingling sensation in fingers and toes, reduced immunity, repeated miscarriages or still births, male sterility, etc. It is also responsible for alterations in the functional mechanisms of liver, kidney, digestive system, respiratory system, excretory system. 3.2 ANIMAL HEALTH: Almost all terrestrial and aquatic animals are susceptible to high doses of fluoride, although the tolerance level varies from one species to another. For terrestrial animals, important sources of excess fluoride intake include drinking water, soil, or vegetation naturally containing excess soluble fluoride compounds or contaminated with fluoride compounds emitted by volcanic eruptions or industrial activities.
  • 3. INTERNATIONAL RESEARCH JOURNAL OF ENGINEERING AND TECHNOLOGY (IRJET) E-ISSN: 2395-0056 VOLUME: 06 ISSUE: 09 | SEP 2019 WWW.IRJET.NET P-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 1508 3.2.1 Invertebrates: Many invertebrates are highly susceptible to fluoride toxicity. Honeybees and silkworm larvae are highly susceptible to fluoride toxicity; the silk industry in several countries has been badly affected by industrial fluoride pollution [16,17]. Aquatic invertebrates and vertebrates including fish are also susceptible to fluoride toxicity. In general, freshwater or softwater-dwelling aquatic animals have -lower fluoride tolerance than marine or hardwater-dwelling animals [18]. 3.2.2 Vertebrates: Among terrestrial vertebrates, herbivores are more susceptible than carnivores and other animals occupying an upper position in the food pyramid. Domestic and wild herbivores are more exposed to environmental contaminants as they are nonselective eaters and can consume contaminated feed, forage, and water. It is thus required to bring the concentration of fluoride to required level. So here are some article reviews of the various techniques available for the removal of fluoride from water. 4. METHODS FOR DEFLUORIDATION OF WATER Surendra roy et.al. [19] said that the fluoride contaminated groundwater used for drinking purposes should be determined examined and accordingly a suitable method can be chosen for its treatment. Sl.no Removal Method Process Advantages Disadvantages Name of the Author Medium used Reference numbers 1 Coagulation and Precipitation Involves the addition of chemicals and the formation of fluoride precipitates 1. Commonly used 2. It is more practical. 3. Easy to understand 1. Low treatment efficiency upto 70% 2.Requirement of large dosage of chemicals for treatment. 3.Requirement of skilled manpower Meenakshi et.al., Lawler,D.F. et.al., Larsen,M.J. et.al., Qafas,Z.et.al., Dahi,E et.al., Aldaco et.al. Aluminium sulfate and lime (NEERI METHOD),salts of Calcium, aluminium and iron, bone char combined with sodium dihydrogen phosphate and calcium chloride, granular calcite. 20-25 2 Reverse Osmosis It is a physical process in which the anions are removed by applying pressure on the feed water to direct it through the semi permeable membrane. 1.Membrane can be completely recovered after every arrangement of examination. 2.This can remove 90% of fluoride regardless of initial concentration 1.Non attainable for rural regions. 2. Very expensive. 3.Skilled labor required. 4.Need pH improvement. Ndiaye et.al. Behanu et.al Gedam et.al. Diawara et.al. 1. RO membrane of Ethiopian Rift Region, 2.Polyamide RO Membrane, 3.Low Pressure RO 26-29 3 Nano Filtration It removes the larger dissolved solids when compared with RO. 1. High productivity. 2. No Chemicals needed. 3.used for wide range of pH. 1. Highly expensive technique. 2. Prone to fouling, scaling or membrane degradation. Tahaikt et.al. Pontie et.al. Bejaoui et.al. 1.NF90 2.NF400. 30-32 4 Electro- dialysis Removal of ionic components 1. Flexible 2.low chemical 1. Only separation of Ionic Adhikary et.al. Amor et.al. Annour et.al. used this method in the combination of chitosan with 33-39
  • 4. INTERNATIONAL RESEARCH JOURNAL OF ENGINEERING AND TECHNOLOGY (IRJET) E-ISSN: 2395-0056 VOLUME: 06 ISSUE: 09 | SEP 2019 WWW.IRJET.NET P-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 1509 from aqueous solutions through ion exchange membranes under the driving force of an electric current request. 3.High water recovery. Components. 2. Specific power consumption for Pumping. 3.Necessity of concentrate treatment. Sahli et.al. Kabay et.al. Ergun et.al. Lahnid et.al. the help of CMX- ACS membranes, others used the combination of electrodialysis and anion exchanger. 5 Ion Exchange Fluoride can be removed from water supplies with a strongly fundamental anion- exchange resin containing quartenary ammonium functional groups. 1.Removes fluoride upto 90-95 %. 2.Retains the taste and color of water intact 1. Presence of sulfate, phosphate, bicarbonate, etc. results in ionic competition. 2. Relatively higher cost. 3. Treated water sometimes has a low pH and high levels of chlorides. Mohan Rao et.al. Haron et.al. Castel et.al. Zhou et.al. yttrium loaded poly(hydroxamic acid) resin,lanthanum- impregnate cross linked gelatin 40-43 6 Electro- coagulation Technique for applying direct current to sacrificial electrodes that are submerged in an aqueous solution. 1.obliges basic equipment 2.simple to handle 3.less support cost 4.treated water is consumable, colorless and odourless 1.electrodes should be consistently supplanted 2.utilizes high electricity 3. Loss of productivity due to the formation of oxide film on the cathode. Yang et.al. Feng Shen et.al. Drouiche et.al. Un et al. Bennajah et al. Aluminium electrodes, Iron cylindrical reactor as anode, 44-47 6 Adsorption Adsorption is the bond of molecules species from bulk solution for a surface of a solid by physical or chemical forces. 1. Ease of operation. 2.Adsorption procedure in worthwhile 3. High productivity for fluoride removal and can remove up to 90% fluoride. 4. Cost effective. 5. Produce high quality water. 6. Regeneration is conceivable. 1. Process is dependent on pH. 2. Regeneration is required. 3. Disposal of fluoride-laden material. Kariyanna et.al. J.P. Barbier et.al., Muthukumaran et..al., Rongshu et.al., Y.Min et.al., Y. Wang et.al., Nava et.al., Padmavathy et.al. Theragaonkar et.al. Gandhi et.al. Mohapatra et.al. Amit Bhatnagar et.al. Prins Satish et.al. Activated alumina, activated carbon coated with silica gel, calcite, activated saw dust, activated coconut shell powder, activated fly ash, groundnut shell, coffee husk, rice husk, magnesia, serpentine, bone charcoal, orange peel, chalk powder 48-60 5. CONCLUSION: A large number of factors and geological conditions influence the correlations between different pairs of physio-chemical parameters of water samples directly or indirectly. Some parameters are directly measured by their respective measuring equipments, some are determined by titrimetric methods and some elements like fluorides are to be treated by various
  • 5. INTERNATIONAL RESEARCH JOURNAL OF ENGINEERING AND TECHNOLOGY (IRJET) E-ISSN: 2395-0056 VOLUME: 06 ISSUE: 09 | SEP 2019 WWW.IRJET.NET P-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.34 | ISO 9001:2008 Certified Journal | Page 1510 methods. As there is a need for the treatment of fluoride present in water, which causes lot of problems. The method for treatment of fluoride can be chosen as per the advantages and limitations, among which adsorption is the best process for the removal of fluoride from water according to the study. REFERENCES: 1. Manoj Kumar, Avinash puri-‘A Review of permissible limits of drinking water’- Indian Journal of Occupational and Environmental Medicine - April 2012 - Volume 16 - Issue 1. 2. Sneha Jagpat et.al. – ‘Fluoride in Drinking Water and Defluoridation of water’- Chemical Reviews, 2012, 112, 2454- 2466. 3. Muturu C., Onyango,M.S. et.al. – ‘Fluoride removal performance of Phosphoric acid treated lime: breakthrough analysis and point-of-use system performance. Water SA,38 (2),279-286. 4. Kirck KL (1991) Biochemistry of the elemental halogens and inorganic halides. Plenum, New York; pp 19-68. 5. Treasure ET, Dever JG (1992) The prevalence of caries in 5 year old children living in fluorinated and non fluorinated communities in New Zealand NZ Dent J 88:9-13 6. Mellete JR, Aeling JL, Nuss DD (1983) Perioral dermatitis J Assoc Military Dermatol 9:3-8. 7. WHO (World Health Organisation), 2006, Guidelines for Drinking Water Quality: Incorporating First Addendum to Third Edition. World Health Organisation, Geneva., 375 p. 8. Misra, A.K. and Mishra, A., 2007, Study of quaternary aquifiers in Ganga Plain India: Focus on groundwater salinity, fluoride and fluorosis. J. Hazardous Mater., 144, 438-448. 9. Teotia, S.P.S., Teotia, M. and Singh R.K., 1981, Hydro-geochemical aspects of endemic skeletal fluorosis in India- An epidemiologic study., Fluoride, 14 (2), 69-74. 10. Murray J.J., (Ed.) 1986, Appropriate Use of Fluorides for Human Health., World Health Organisation,Geneva. 11. Paya, P. and Datta, S.A., 2010, Fluoride contamination in groundwater of Patan District, Gujarat, India., International Journal of Engineering Studies, 2(2), 171-177. 12. Johnston,R. and Heijnen, H., 2002, Safe Water technology for arsenic removal., Report World Health Organisation. 13. Susheela, A.K., 1999, Fluorosis management programme in India., Curr. Sci., 77(10), 1250-1255. 14. Czarnowski, W., Krechniak, J., Urbanska, B., Stolarska, K., Taraszewska-Czarnowska, M. and Muraskzo-Klaude, A., 1999, The Impact of Waterborne Fluoride on Bone density, Fluoride, 32 (2), 91-95. 15. Payel Roy, Ritesh Kumar and Goutham Kumar Roy, Fluoride Pollution Abatement, Research gate. 16. Bourbon P (1967) Analytical problems posed by pollution by fluorine compounds J Air Pollut Control Assoc 17:661-663. 17. Weinstein LH, Davison A (2004) Fluorides in the environment: effects of plants and animals. CABI Publishing, Cambridge. 18. Camargo JA (2003) Fluoride toxicity to aquatic organism: a review Chemosphere 50: 251-264. 19. Surendra Roy, Gurucharan Dass, 2013, Fluoride Contamination in Drinking water, Resources and Environment, 3(3), 53-58. 20. Meenakshi, R.C.; Maheshwari J. Hazard.Mater.2006, B137, 456. 21. Lawler, D.F.; Williams, D.H. Water Res. 1984, 11, 25. 22. Larsen,M.J.; Pearce, E.I.F. Caries Res.2002,36, 341. 23. Qafas, Z.; Kacemi,K.E.;Ennaassia, E.; Edelahi,, M.C. Sci.Lett. 2002, 3, 1. 24. E. Dahi, Contact Precipitation for defluoridation of water, 22nd WEDC Conference New Delhi, India,1996, pp. 266- 268. 25. R. Aldaco, A. Garea, and A. Irabein, Modelling of particle growth: Application to water treatment in a fluidized bed reactor, Chemical Engineering Journal, 134, 2007, pp. 66-71. 26. P.I. Ndiaye, P. Moulln, L. Dominguez, J.C. Millet,and F.Charbit, Removal of Fluoride from electronic industrial effluent by RO membrane separation, Desalination 173, 2005, pp. 25-32. 27. B. Aseefa, Defluoridation of Ethiopian rift valley region water using reverse osmosis membranes, Journals of EEA, 23, 2006, pp. 1-6. 28. V.V. Gedam, J.L. Patil, S. Kagne, R.S. Sirsam and P. Labhasetwar, Performance evaluation of Polyamide reverse osmosis membrane for removal of contaminants in ground water collected from Chandrapur district, Journal of Membrane Science and Technology, 2(3), 2012, pp. 1-5. 29. C.K. Diawara, S.N. Diop, M.A. Diallo, and M.A. Farcy, Determination Performance of nanofiltration and low pressure reverse osmosis (LPRM) membranes in the removal of fluorine and salinity from brakish drinking water, Journal of Water Resource and Protection, 3, 2011, pp. 912-917. 30. M.Tahaikt, R.E. Habbani, A.A. Haddou, I.Achary, Z. Amor, M.Taky, A.Alami, A. Boughriba, M.Hafsi and A. Elmidaoui, Fluoride removal from groundwater by nanofiltration, Desalination, 212, 2007, pp. 46-53.
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