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International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 05 | May 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 7889
FLUORIDE REMOVAL USING LOW COST ADSORBENT - LIME
Anupama Rodge1, Sachin Mane2, Dr. Ashok More3
1P.G. Student, D.Y. Patil College of Engineering Akurdi.
2Professer, Department of Civil Engineering, D.Y. Patil College of Engineering Akurdi.
3Head of Department of Civil Engineering, D.Y. Patil College of Engineering Akurdi.
---------------------------------------------------------------------***----------------------------------------------------------------------
Abstract - Fluoride is naturally found in water. If fluoride level exceed, it causes dental problems and even several other effects
on human body. Thus, removal of Fluoride from aqueous solution by using lime is an adsorbent has been investigated. Lime is
locally available and is a low cost alternative to other adsorbents. The studies were carriedoutbyvaryingthecontacttime, doseof
adsorbent and pH. The optimum condition for removal of Fluoride from aqueous solution is described. The possibility of lime as a
adsorbent is studied.
Key Words: Fluoride, adsorbent, low cost, contact time, dose of adsorbent, pH.
1. INTRODUCTION
Fluoride is a naturally found in the water. Fluorine is present in the form of fluorides in a number of minerals and in many
rocks. Fluorine and its compounds are used in industry such as production of high purity graphite, fertilizers, electrolysis of
alumina, semiconductors, etc. Fluoride is beneficial in human body for the formation of dental enamel and maintenance of
healthy bones when present within the permissible limit. The ingestion of excess fluoride can causefluorosiswhich affectsthe
teeth and bones. Moderate amounts lead to dental effects, but long-term ingestion of large amounts can lead to potentially
severe bone problems. Low levels of fluoride intake help to prevent dental caries. Researchers during the last 5–6 years have
proved that life-long impact and accumulation of fluorides cause changes in the DNA-structure, cancer, etc.
The various methods used for defluoridation include adsorption, ion exchange, precipitation and electro dialysis. Out of all
these methods adopted for defluoridation, adsorption is most commonly and extensively used method fordefluoridation.The
adsorption method is low costing. The method is used widely due to wide range of adsorbents available. One of such waste
products i.e. lime is used to explore the possibility of its utility for adsorption.
2. MATERIALS AND METHODS
2.1. Materials:
The raw material required is locally available. The lime was collected from the shop directly. The reagentusedisacid-zirconyl
SPADNS for spectrophotometric determination of fluoride.
2.2. Samples:
The water sample was prepared synthetically by using the stock solution. The stock solution for fluoride was prepared by
dissolving 221mg anhydrous sodium fluoride in 1000ml distilled water.
2.3. Method:
The material was treated with chemicals as a pretreatment. To obtain the powder form, the material was crushed to required
size. The experimentation was carried out by batch study. The 25 ml of sample was taken in 100ml volume flask. The water
sample has initial concentration of 3mg/l. After adding of the adsorbents, the mixture was mixed thoroughly. After roughly 2
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 05 | May 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 7890
min of settlement of adsorbents further testing of sample was carried out. Out of the treated samples, 10ml was taken
separately and 2ml of SPADNS reagent was added and absorbance level for fluoride was checked using spectrophotometer.
Similar experimentation was done by varying the parameters like contact time, dose of adsorbents and pH. Contact time was
varied at 15min intervals each starting from 30minutes to 120 minutes. Similarily,dose werevariedfrom4,8,12,16 and20g/l
and pH was checked over a range 4 to 9.
3. RESULTS AND DISCUSSION:
3.1. Effect of variation of Contact Time:
The contact time for the materials was varied from 30, 45, 60, 75, 90, 105 and 120 minutes. The interval was kept 15minutes
between two consecutive readings to get uniform curves. It was noticed that as the contact time increases, the adsorption or
the removal efficiency of the adsorbents was increased significantly.
Table 1: Variation of Contact time
Sr no. Contact Time (min) % Removal of Lime
1 30 17
2 45 23
3 60 47
4 75 52
5 90 77
6 105 80
7 120 85
Fig1. Contact time Vs % Removal
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 05 | May 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 7891
3.2. Effect of variation of Dose of Adsorbents:
The adsorbance capacity increases with the increase in dosage. The initial concentration of fluoride in the sample was kept 3
mg/l. The dose of adsorbents was varied from 4, 8, 12, 16 and 20 g/l.
Table 2: Variation of Dose of Adsorbents
Fig2: Dose of adsorbents Vs % Removal
3.3 Effect of variation of pH:
The pH influences the adsorbance capacities of the materials. Different capacities are shown by materials at different pH.
Table 3: Variation of pH
Sr no. pH % Removal
Lime
1 4 60
2 6 64
3 8 68
4 9 48
Sr no. Dose of Adsorbent
(g/l)
% Removal
Lime
1 4 40
2 8 50
3 12 53
4 16 65
5 20 68
International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056
Volume: 06 Issue: 05 | May 2019 www.irjet.net p-ISSN: 2395-0072
© 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 7892
Fig 3: pH Vs % Removal
4. CONCLUSION
Lime is found to be effective in removal of fluoride. The removal percentage for fluoride was found to be different fordifferent
condition. The pH 4 is found optimum for fluoride removal.
REFERENCES
[1] Sailaja Kumari. B, Bhagawan. D, Himabindu. V, Jyostna Cherukuri, Removal of fluoride from drinking water by adsorption
onto Activated Alumina and activated carbon, Int. Journal of Engineering Research and Applications. ISSN: 2248-9622, Vol. 5,
Issue 8, (Part - 3) August 2015, pp.19-24.
[2] Chidambaram, S. Ramanathan, Vasudevan S, Fluoride removal studies in water using natural material. Water, air and soil
pollution, 29, p. 0378-473, 2001.
[3] Veressinina Y., Trapido M., Ahelik V., and Munter R., Fluoride in drinking water:Theproblemanditspossiblesolution. Proc.
Estonian Acad. Sci. Chem., 50(2), P. 81-88, 2001
[4] M. Srimurali, A. Pragathi, J. Karthikeyan, A study on removal of fluorides from drinking
water by adsorption onto low-cost materials, Environ. Pollut. 99 (1998) 285–289.
[5] S. Ghorai, K.K. Pant, Investigations on the column performance of fluoride adsorption by activated alumina in a fixed-bed,
Chem. Eng. J. 98 (2004) 165–173.
[6] Y.H. Li, S. Wang, A. Cao, D. Zhao, X. Zhang, C. Xu, Z. Luan, D. Ruan, J. Liang, D. Wu, B. Wei,Adsorptionoffluoridefromwaterby
amorphous alumina supported on carbon nanotubes, Chem. Phys. Lett. 350 (2001) 412–416.

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IRJET- Fluoride Removal using Low Cost Adsorbent – Lime

  • 1. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 05 | May 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 7889 FLUORIDE REMOVAL USING LOW COST ADSORBENT - LIME Anupama Rodge1, Sachin Mane2, Dr. Ashok More3 1P.G. Student, D.Y. Patil College of Engineering Akurdi. 2Professer, Department of Civil Engineering, D.Y. Patil College of Engineering Akurdi. 3Head of Department of Civil Engineering, D.Y. Patil College of Engineering Akurdi. ---------------------------------------------------------------------***---------------------------------------------------------------------- Abstract - Fluoride is naturally found in water. If fluoride level exceed, it causes dental problems and even several other effects on human body. Thus, removal of Fluoride from aqueous solution by using lime is an adsorbent has been investigated. Lime is locally available and is a low cost alternative to other adsorbents. The studies were carriedoutbyvaryingthecontacttime, doseof adsorbent and pH. The optimum condition for removal of Fluoride from aqueous solution is described. The possibility of lime as a adsorbent is studied. Key Words: Fluoride, adsorbent, low cost, contact time, dose of adsorbent, pH. 1. INTRODUCTION Fluoride is a naturally found in the water. Fluorine is present in the form of fluorides in a number of minerals and in many rocks. Fluorine and its compounds are used in industry such as production of high purity graphite, fertilizers, electrolysis of alumina, semiconductors, etc. Fluoride is beneficial in human body for the formation of dental enamel and maintenance of healthy bones when present within the permissible limit. The ingestion of excess fluoride can causefluorosiswhich affectsthe teeth and bones. Moderate amounts lead to dental effects, but long-term ingestion of large amounts can lead to potentially severe bone problems. Low levels of fluoride intake help to prevent dental caries. Researchers during the last 5–6 years have proved that life-long impact and accumulation of fluorides cause changes in the DNA-structure, cancer, etc. The various methods used for defluoridation include adsorption, ion exchange, precipitation and electro dialysis. Out of all these methods adopted for defluoridation, adsorption is most commonly and extensively used method fordefluoridation.The adsorption method is low costing. The method is used widely due to wide range of adsorbents available. One of such waste products i.e. lime is used to explore the possibility of its utility for adsorption. 2. MATERIALS AND METHODS 2.1. Materials: The raw material required is locally available. The lime was collected from the shop directly. The reagentusedisacid-zirconyl SPADNS for spectrophotometric determination of fluoride. 2.2. Samples: The water sample was prepared synthetically by using the stock solution. The stock solution for fluoride was prepared by dissolving 221mg anhydrous sodium fluoride in 1000ml distilled water. 2.3. Method: The material was treated with chemicals as a pretreatment. To obtain the powder form, the material was crushed to required size. The experimentation was carried out by batch study. The 25 ml of sample was taken in 100ml volume flask. The water sample has initial concentration of 3mg/l. After adding of the adsorbents, the mixture was mixed thoroughly. After roughly 2
  • 2. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 05 | May 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 7890 min of settlement of adsorbents further testing of sample was carried out. Out of the treated samples, 10ml was taken separately and 2ml of SPADNS reagent was added and absorbance level for fluoride was checked using spectrophotometer. Similar experimentation was done by varying the parameters like contact time, dose of adsorbents and pH. Contact time was varied at 15min intervals each starting from 30minutes to 120 minutes. Similarily,dose werevariedfrom4,8,12,16 and20g/l and pH was checked over a range 4 to 9. 3. RESULTS AND DISCUSSION: 3.1. Effect of variation of Contact Time: The contact time for the materials was varied from 30, 45, 60, 75, 90, 105 and 120 minutes. The interval was kept 15minutes between two consecutive readings to get uniform curves. It was noticed that as the contact time increases, the adsorption or the removal efficiency of the adsorbents was increased significantly. Table 1: Variation of Contact time Sr no. Contact Time (min) % Removal of Lime 1 30 17 2 45 23 3 60 47 4 75 52 5 90 77 6 105 80 7 120 85 Fig1. Contact time Vs % Removal
  • 3. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 05 | May 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 7891 3.2. Effect of variation of Dose of Adsorbents: The adsorbance capacity increases with the increase in dosage. The initial concentration of fluoride in the sample was kept 3 mg/l. The dose of adsorbents was varied from 4, 8, 12, 16 and 20 g/l. Table 2: Variation of Dose of Adsorbents Fig2: Dose of adsorbents Vs % Removal 3.3 Effect of variation of pH: The pH influences the adsorbance capacities of the materials. Different capacities are shown by materials at different pH. Table 3: Variation of pH Sr no. pH % Removal Lime 1 4 60 2 6 64 3 8 68 4 9 48 Sr no. Dose of Adsorbent (g/l) % Removal Lime 1 4 40 2 8 50 3 12 53 4 16 65 5 20 68
  • 4. International Research Journal of Engineering and Technology (IRJET) e-ISSN: 2395-0056 Volume: 06 Issue: 05 | May 2019 www.irjet.net p-ISSN: 2395-0072 © 2019, IRJET | Impact Factor value: 7.211 | ISO 9001:2008 Certified Journal | Page 7892 Fig 3: pH Vs % Removal 4. CONCLUSION Lime is found to be effective in removal of fluoride. The removal percentage for fluoride was found to be different fordifferent condition. The pH 4 is found optimum for fluoride removal. REFERENCES [1] Sailaja Kumari. B, Bhagawan. D, Himabindu. V, Jyostna Cherukuri, Removal of fluoride from drinking water by adsorption onto Activated Alumina and activated carbon, Int. Journal of Engineering Research and Applications. ISSN: 2248-9622, Vol. 5, Issue 8, (Part - 3) August 2015, pp.19-24. [2] Chidambaram, S. Ramanathan, Vasudevan S, Fluoride removal studies in water using natural material. Water, air and soil pollution, 29, p. 0378-473, 2001. [3] Veressinina Y., Trapido M., Ahelik V., and Munter R., Fluoride in drinking water:Theproblemanditspossiblesolution. Proc. Estonian Acad. Sci. Chem., 50(2), P. 81-88, 2001 [4] M. Srimurali, A. Pragathi, J. Karthikeyan, A study on removal of fluorides from drinking water by adsorption onto low-cost materials, Environ. Pollut. 99 (1998) 285–289. [5] S. Ghorai, K.K. Pant, Investigations on the column performance of fluoride adsorption by activated alumina in a fixed-bed, Chem. Eng. J. 98 (2004) 165–173. [6] Y.H. Li, S. Wang, A. Cao, D. Zhao, X. Zhang, C. Xu, Z. Luan, D. Ruan, J. Liang, D. Wu, B. Wei,Adsorptionoffluoridefromwaterby amorphous alumina supported on carbon nanotubes, Chem. Phys. Lett. 350 (2001) 412–416.