Journal of Dental Research and Review

REVIEW ARTICLE
Year
: 2019  |  Volume : 6  |  Issue : 1  |  Page : 3--8

Novel materials for defluoridation in India: A systematic review


Sreekanth Bose, R Yashoda, Manjunath P Puranik 
 Department of Public Health Dentistry, Government Dental College and Research Institute, Bangalore, Karnataka, India

Correspondence Address:
Sreekanth Bose
Department of Public Health Dentistry, Government Dental College and Research Institute, Bangalore, Karnataka
India

Abstract

Background: Fluorosis is an endemic disease prevalent in 22 states in India affecting 70 million individuals. The process of removal of fluoride ions from water is known as defluoridation. Even though several defluondation techniques have been developed and implemented in India, most of these techniques have many disadvantages. Development of a newer defluoridation technique starts With laboratory experimentation of materials. Objectives: To identify recent advances in laboratory studies in India with regard to the materials used for defluoridation (published from 2010-2017). Methodology: The review was carned out according to the Joanna Briggs Institute (J81) critical appraisal guideline. A three-step search strategy was utilized which yielded twenty articles after the final step. These articles were evaluated to describe, compare and contrast the materials (Chemical, indigenous and herbal) in terms of effectiveness of fluonde removal, critical pH, cost and other factors. Results: Fluoride removal capacity varied around to 100% and optimum pH between 2 to 10 in different studies. Indigenous and herbal materials are cost effective compared to chemicals. But chemicals have better defluoridation capacity. The defluondating properties can be enhanced using certain combinations or pretreatment of these materials (eg-Heat activation). Conclusions: Indigenous and herbal products are suitable for Indian conditions because of the ease of availability and cost-effectiveness. The future research should focus on enhancing the defluoridating properties of locally available materials and field studies regarding the feasibility in real life scenarios.



How to cite this article:
Bose S, Yashoda R, Puranik MP. Novel materials for defluoridation in India: A systematic review.J Dent Res Rev 2019;6:3-8


How to cite this URL:
Bose S, Yashoda R, Puranik MP. Novel materials for defluoridation in India: A systematic review. J Dent Res Rev [serial online] 2019 [cited 2019 Jul 16 ];6:3-8
Available from: http://www.jdrr.org/text.asp?2019/6/1/3/256806


Full Text



 Introduction



Fluoride is one of the most potent ions present in groundwater which can cause endemic outcomes.[1] According to WHO 1984 and Indian standard drinking water specification 1991, the maximum permissible limit of fluoride is 1.5 ppm and highest desirable limit is 1.0 ppm.[2] As an extremely electronegative element, fluorine has high affinity to get attracted by positively charged ions such as calcium in mineralized tissues. Excess intake may cause fluorosis which can be dental, skeletal, and nonskeletal along with various neurological complications.[3]

Many countries first started to inspect the harmful effects of fluoride and its elimination from drinking water in the 1930s. The process of removal of fluoride ions from water is known as defluoridation. There were many materials and techniques explored to carry out fluoride removal. However, the experiments to construct a method of defluoridation that can be used under differing environmental, social, financial, and technical constraints have not been successful. Hence, the elimination of fluoride from water is important and a challenging task among scientists.[4]

The world's fluoride stores in ground are estimated to be 85 million tons, of which nearly 12 million tons are located in India.[5] A hot tropical climate with comparatively more drinking water consumption creates a high prevalence of affected population.[6] Fluorosis is an endemic disease thought to affect 70 million individuals and prevalent in 22 states of India, particularly in arid parts of the country.[7] Skeletal fluorosis is present among 43% of these individuals with clinical presentations such as severe pain in the back bone, joints and pelvic girdle which leads to stiffness of the vertebral column, immobile joints, and terminating in a crippling condition. Although there is no treatment or solution, this disease can be prevented.[8]

Throughout the years, several defluoridation procedures have been developed and actualized in India. Nalgonda technique developed by National Environmental Engineering Research Institute, based on combined use of alum and lime in a two-step process, is the most widely used. However, the technique has a lot of disadvantages such as the undesirable taste of treated water, high maintenance cost need of large space, the requirement of a regular attendant looking after-treatment process, temperature, and presence of silicate ions affect the efficacy. The purified water can produce adverse health outcomes such as dementia due to residual aluminum, the cathartic effect due to sulfate ion, and toxicity due to a soluble aluminum fluoride complex ion which does not form the sledge.[9]

Prasanti technology developed by Satya Sai University for Higher Learning, Puttaparthy use activated alumina. The limitations of this method include high expense, need for trained persons for reactivation of filter material, and formation of moderately high residual aluminum byproduct ranging from 0.1 to 0.3 ppm.[10]

While reverse osmosis which is considered as most effective in terms of fluoride removal also holds certain disadvantages such as economic burden, large waste volumes, extensive pretreatments, and chance of chemical attacks, plugging, and fouling by particulate matter in the units. Besides, this method removes all the ions present in water, essential for human growth and development.[11] Hence, there is a need for the development of a better method of defluoridation with fewer limitations.

Development of new defluoridation technique is a stepwise and complex process including laboratory testing of the material, bench scale test, pilot scale, and field scale demonstrations.

Laboratory experiments enable many parameters to be inspected in detail and a significant understanding about the performance of materials in various conditions. The information obtained from these studies is very useful in formulating and implementing newer methods of defluoridation. Much laboratory research has been done on materials in this decade in India.[12]

Hence, there is a need to evaluate the results of these studies by means of a systematic review.

Hence, the objective of this review was to identify recent advances in laboratory studies in India with regard to the materials used for defluoridation (published from 2010 to 2017) to critically evaluate the effectiveness of newer chemical, indigenous, and herbal materials studied for defluoridation in terms of effectiveness of fluoride removal, critical pH, cost, and other factors.

 Materials and Methods



The review was carried out according to the standards of Joanna Briggs Institute guidelines for systematic review.[13] A three-step search strategy was used in this review. An initial literature search of publications indexed in the English language was performed through core databases (MEDLINE and Google scholar), with the following keywords: effectiveness of materials, defluoridation, laboratory studies, and India. In the second step, articles describing laboratory investigations that evaluated material effectiveness for defluoridation done in India which were published over a period of 7 years (2010–2017) were retrieved for the study. Third, the reference list of all identified reports and articles was searched for additional studies. Gray literature was not included in the study. The date limitation in the search strategy might have excluded the potentially relevant studies. However, the objective was to find recent advances in defluoridation which could be achieved only through the time period restriction. Primary search and screening were conducted by the first reviewer. Inclusion and exclusion of the studies were decided by consensus among all reviewers.

The search yielded 127 articles. A total of sixteen articles were eliminated due to duplication while 22 articles were excluded because full-length articles were not available. Thus, 89 articles were retrieved at the second stage and critically assessed for inclusion by the team consisting of the three reviewers. A total of 62 articles were excluded at the second level, as they were not related to the main outcome of this study. Finally, based on the interpretations of the team, seven articles were excluded due to lack of clarity in the literature. Thus, a total of twenty articles were included in this systematic review, as shown in [Figure 1].{Figure 1}

 Results



A total of 20 studies conducted over 7 years (2007–2017) were included in this systematic review. The analysis of literature revealed that laboratory studies are being carried out on different types of materials which can be chemical, indigenous, or herbal. Most of the studies modified the material to achieve better fluoride removal properties. The studies included three major defluoridation techniques – adsorption, precipitation, and ion exchange [Table 1]. Maximum number of studies (seventeen) described materials using adsorption technique. Among them, ten studies were on herbal materials.{Table 1}

The most important properties evaluated in most of the studies were fluoride removal capacity and optimum pH of materials. Fluoride removal capacity varied around 40%–100% and optimum pH between 2 and 10 in different studies as shown in [Table 2], [Table 3], [Table 4].{Table 2}{Table 3}{Table 4}

Very few studies[21],[28] have focused on cost of the materials. Certain indigenous materials such as bentonite clay, rice husk ash, and shale were shown to have good economic viability. All the herbal materials under investigation are very much cost-effective and easily available in rural regions. Typha angustata cost only around US $25/ton.

Regeneration of material after the process is useful in reuse, limiting the total amount of material needed for fluoride removal. Some studies[14],[15],[16],[17],[19],[24],[28] have reported regeneration capacity of respective materials. Zirconium chitosan nanoparticles, chitosan composite modified with lanthanum complex, lanthanum-impregnated bauxite, aluminum hydroxide derived from hydrated aluminum sulfate, bentonite clay, tamarind, and T. angustata have regeneration capacity.

Hardness of water which is due to the presence of a wide variety of ions affects the adsorption capacity of the sorbent. Lanthanum-modified chitosan,[15] bentonite clay,[19] and tamarind seeds[24] showed lower defluoridation capacity in the presence of bicarbonate ions. The inhibitory effect of Shale[21] was in the order of carbonate, nitrate, chloride, and phosphate while it was carbonate, sulfate, chloride, nitrate for lanthanum-impregnated bauxite,[16] and Phyllanthus emblica.[27] Activated alumina proved to have no ionic interactions.[18]

 Discussion



Air, water, and food are the three fundamental requirements for the survival of individuals. Hence, the drinking water must be safe and potable.[34] Groundwater, which aquifers below the surface of the Earth, is one of the most important sources of drinking water. Groundwater frequently contains high amount of inorganic minerals such as fluoride which can cause risk to the well-being.[35]

Various techniques and materials were used for defluoridation of drinking water. Precipitation, adsorption, ion exchange, and membrane methods are the most important techniques used. This review showed that most of the recent laboratory investigations are using the method of adsorption.[36] The materials are either chemicals, indigenous, or herbal. Different materials such as alumina, alum, and activated charcoal are used traditionally depending on the techniques. The present day investigations focus on modifications of chemicals with known defluoridation properties to enhance the efficacy or finding newer indigenous/herbal materials with better fluoride removal capacity.[37]

Laboratory studies have the role of paving the path for new techniques. It will provide considerable insight and quantitative information about many of the physical properties of materials used for defluoridation. Recent advances in defluoridation of water in India are clustered around innovative laboratory experiments done for novel effective material. Chemicals such as alumina, limestone, and alum are used for defluoridation of water since early days. A systematic review done by Dubey et al. reported the use of chemicals, especially aluminum compounds in the ongoing field programs.[38]

Chitosan modified with lanthanum, lanthanum-impregnated bauxite, and aluminum hydroxide are new chemicals with their modifications under investigation which shows promising results in fluoride removal capacity. They exhibited fluoride removal capacity of 17.50 mg/g, 18.18 mg/g, and 25.8 mg/g, respectively.[14],[15],[16] Chitosan composite modified with nano zirconium was able to remove around 99% of fluoride from water.[14] These chemical compounds work around neutral pH. It was observed that acidic conditions produced by addition of phosphoric acid can give better defluoridation with limestone. Chemicals such as aluminum compounds are proved to be better candidates for the defluoridation process in the application, and this observation is in line with the review on emerging adsorbents by Jadhav et al.[39]

Most of the places endemic to fluorosis in India are remote areas where chemicals are not easily available. Indigenous materials are very useful in defluoridation because of the local availability and low cost. If defluoridation can be carried out efficiently by locally available indigenous materials, there will be lesser barriers in rural India for the implementation of such programs. Materials such as rice husk ash, bentonite clay, brick powder, and coal mine wastes have defluoridating capacity in the adsorption process. The defluoridating capacity was 9–10 mg/g for rice husk ash while coal mine waste and bentonite clay showed 88% and 97% fluoride removal.[19],[22] Under precipitation method, the brick powder had 50%–55% fluoride removal capacity which increased by 4%–5% when impregnated with alum.[20],[21] Generally, indigenous materials work around acidic pH. Eggshell waste has ion exchange properties which are useful for fluoride removal from water. Modifications of these materials can increase the efficiency.[23]

Herbal materials are observed to collect fluoride with the process of adsorption, and hence, application as defluoridating agents has been proposed. Acceptability of herbal materials among Indians make them good candidates for the process.[40] Seeds of tamarind and moringa, charcoal obtained from neem, banana peel and coffee husk and T. angustata plant, Indian gooseberry Tulsi have promising fluoride removal characteristics.[24],[25],[26],[27],[28],[29],[30],[31],[32],[33] The defluoridation capacities were 91% and 76% for tamarind and moringa seeds, respectively, 94% and 84% for neem and banana peel and coffee husk charcoals, respectively, and 82.1% and 42% for Indian gooseberry and Tulsi leaves, respectively.[24],[25],[26],[27],[29],[33] Herbal materials work efficiently around a wide spectrum of pH. Optimum pH for charcoal obtained from the banana peel and coffee husk is 2 while it is 8 for moringa seeds.[27],[31] Most of the plant extracts and compounds give desirable odor to the treated water, and medicinal properties of herbs will promote rural population to use it for defluoridation. Studies are aiming to increase the effectiveness of these compounds.

The Indian government is striving to provide people with safe drinking water provisions. India is a large country with huge population which makes it hard to address the issue of overabundance of fluoride in water through public-aided community-based treatment units. The absence of proprietorship by user communities and the consequent hesitance to take over the responsibility were also observed in many villages. Hence, domestic defluoridation techniques are best for Indian conditions.[41] It will reduce the burden of huge government investment to meet the needs of millions of endemic rural population. Domestic units are the “point of use” units with a higher level of individual possession. This might make sure better utilization and maintenance of these units. Past experience with domestic units with the assistance of United Nations Children's Fund has not been generally encouraging due to higher material cost. Indigenous and herbal materials are most suitable in this scenario. They are locally available and cost-effective.[42]

Studies are conducted on a variety of materials for their defluoridation capacity. Limitations of these studies include scarcity of literature regarding field applications. This can create a void in the practicability of use of materials about amount of workforce required, quality, and acceptability of purified water. Studies are not providing information about the cost of materials. The ability of methods to be converted into large scale or household water defluoridating units is also not discussed in the earlier studies. These factors were reflected on the results of this review and can be considered as limitation.

Indigenous and herbal products for fluoride removal are suitable methods in the Indian scenario. Cultural habits in India will promote using herbal materials for water treatments, and the purified water will have acceptable odor and taste. The low cost and availability are the factors which favor the use. Adsorption which has a tremendous potential for defluoridation because of its effectiveness, ease of operation, and ability to reuse the adsorbent (regeneration) is used for it. However, generally, these materials have very low fluoride removing capacity. The defluoridating properties can be enhanced using certain combinations, pretreatment (e.g., heat activation) of these materials before the defluoridation process. Hence, this systematic review recommends researchers to focus on enhancing the defluoridating properties of locally available materials and conduct field studies regarding the feasibility of models in real-life scenarios.

 Conclusions



Recent advances in developing effective materials for defluoridation in India show promising research in the development of novel materials. Effective, easily available, and low-cost materials (chemicals, indigenous products, and herbal materials) are the core of investigations. Modifications of known materials used for fluoride removal can also produce good results. Adsorption is proved to be the most studied method of defluoridation. It is the most appropriate mechanism while using indigenous and herbal products. These materials are suitable for Indian conditions because of the ease of availability and cost-effectiveness. Field studies are suggested to test the applicability of these materials.

Financial support and sponsorship

Nil.

Conflicts of interest

There are no conflicts of interest.

References

1Chouhan S, Flora SJ. Arsenic and fluoride: Two major ground water pollutants. Indian J Exp Biol 2010;48:666-78.
2Kumar M, Puri A. A review of permissible limits of drinking water. Indian J Occup Environ Med 2012;16:40-4.
3Shrivastava BK, Vani A. Comparative study of defluoridation technologies in India. Asian J Exp Sci 2009;23:269-74.
4Taricska JR, Lawrence K, Hung YT, Li KH. Fluoridation and defluoridation. Advanced Physicochemical Treatment Processes. Vol 4. Humana Press; 2006.
5Teotia SP, Teotia M, Singh KP. Highlights of forty years of research on endemic skeletal fluorosis in India. In: 4th International Workshop on Fluorosis Prevention and Defluoridation of Water; 02 March, 2004. p. 107-25.
6WHO Water Sanitation. Available from: http://www.who.int/water_sanitation_health/diseases-risks/diseases/fluorosis/en/. [Last accessed on 2018 May 15].
7Annadurai ST, Rengasamy JK, Sundaram R, Munusamy AP. Incidence and effects of fluoride in Indian natural ecosystem: A review. Adv Appl Sci Res 2014;5:173-85.
8Susheela AK. Epidemiology and control of fluorosis in India. J Nutr Found India 1984:1-3.
9Meenakshi, Maheshwari RC. Fluoride in drinking water and its removal. J Hazard Mater 2006;137:456-63.
10Agarwal KC, Gupta SK, Gupta AB. Development of new low cost defluoridation technology (KRASS). Water Sci Technol 1999;40:167-73.
11Dubey S, Agarwal M, Gupta AB. Recent developments in defluoridation of drinking water in India. In: Environmental Pollution. Singapore: Springer; 2018. p. 345-56.
12Ayoob S, Gupta AK, Bhat VT. A conceptual overview on sustainable technologies for the defluoridation of drinking water. Crit Rev in Environ Sci Technol 2008;38:401-70.
13Joanna Briggs Institute Reviewers' Manual Edition; 2011. Available from: http://www.joannabriggs.org/assets/docs/sumari/reviewersmanual2011.pdf. [Last accessed on 2018 May 15].
14Prasad KS, Amin Y, Selvaraj K. Defluoridation using biomimetically synthesized nano zirconium chitosan composite: Kinetic and equilibrium studies. J Hazard Mater 2014;276:232-40.
15Prabhu SM, Elanchezhiyan SS, Lee G, Meenakshi S. Defluoridation of water by tea-bag model using La(3+) modified synthetic resin@ chitosan biocomposite. Int J Biol Macromol 2016;91:1002-9.
16Vivek Vardhan CM, Srimurali M. Removal of fluoride from water using a novel sorbent lanthanum-impregnated bauxite. Springerplus 2016;5:1426.
17Mulugeta E, Zewge F, Chandravanshi BS. Development of a household water defluoridation process using aluminium hydroxide based adsorbent. Water Environ Res 2015;87:524-32.
18Samarghandi MR, Khiadani M, Foroughi M, Zolghadr Nasab H. Defluoridation of water using activated alumina in presence of natural organic matter via response surface methodology. Environ Sci Pollut Res Int 2016;23:887-97.
19Thakre D, Rayalu S, Kawade R, Meshram S, Subrt J, Labhsetwar N, et al. Magnesium incorporated bentonite clay for defluoridation of drinking water. J Hazard Mater 2010;180:122-30.
20Jain A, Singh SK. Defluoridation of water using alum impregnated brick powder and its comparison with brick powder. Int J Eng Sci Innov Technol 2014;3:591-6.
21Biswas G, Dutta M, Dutta S, Adhikari K. A comparative study of removal of fluoride from contaminated water using shale collected from different coal mines in India. Environ Sci Pollut Res Int 2016;23:9418-31.
22Ganvir V, Das K. Removal of fluoride from drinking water using aluminum hydroxide coated rice husk ash. J Hazard Mater 2011;185:1287-94.
23Lunge S, Thakre D, Kamble S, Labhsetwar N, Rayalu S. Alumina supported carbon composite material with exceptionally high defluoridation property from eggshell waste. J Hazard Mater 2012;237-238:161-9.
24Murugan M, Subramanian E. Studies on defluoridation of water by tamarind seed, an unconventional biosorbent. J Water Health 2006;4:453-61.
25Kumar NP, Kumar NS, Krishnaiah A. Defluoridation of water using tamarind (Tamarindus indica) fruit cover: Kinetics and equilibrium studies. J Chil Chem Soc 2012;57:1224-31.
26Sivasankar V, Rajkumar S, Murugesh S, Darchen A. Tamarind (Tamarindus indica) fruit shell carbon: A calcium-rich promising adsorbent for fluoride removal from groundwater. J Hazard Mater 2012;225-226:164-72.
27Veeraputhiran V, Alagumuthu G. Treatment of high fluoride drinking water using bioadsorbent. Res J Chem Sci 2011;1:49-54.
28Hanumantharao Y, Kishore M, Ravindhranath K. Characterization and defluoridation studies of active carbon derived from Typha angustata plants. J Anal Sci Technol 2012;3:167-81.
29Parlikar AS, Mokashi SS. Defluoridation of water by Moringa oleifera – A natural adsorbent. Int J Eng Sci Innov Technol 2013;2:245-52.
30Chakrabarty S, Sarma HP. Defluoridation of contaminated drinking water using neem charcoal adsorbent: Kinetics and equilibrium studies. Int J Chem Tech Res 2012;4:511-6.
31Getachew T, Hussen A, Rao VM. Defluoridation of water by activated carbon prepared from banana (Musa paradisiaca) peel and coffee (Coffea arabica) husk. Int J Environ Sci Technol 2015;12:1857-66.
32Mondal NK, Bhaumik R, Baur T, Das B, Roy P, Datta JK. Studies on defluoridation of water by tea ash: An unconventional biosorbent. Chem Sci Trans 2012;1:239-56.
33Ramesh MV, Naveenkumar PG, Prashant GM, Sakeenabi B, Allamaprabhu, Vijetha K, et al. Evaluation of effect of brushite-calcite and two indigenous herbs in removal of fluoride from water. J Clin Diagn Res 2016;10:ZC83-5.
34Ayoob S, Gupta AK. Fluoride in drinking water: A review on the status and stress effects. Crit Rev Environ Sci Technol 2006;36:433-87.
35Susheela AK, Mudgal A, Keast G. Fluoride in water: An overview. Water Front 1999:11-3.
36Piddennavar R, Krishnappa P. Review on defluoridation techniques of water. Int J Eng Sci 2013;2:86-94.
37Ingle NA, Dubey HV, Kaur N, Nagpal A. Defluoridating water. Br Dent J 2014;216:437.
38Dubey A, Tewari A. Defluoridation of drinking water: Efficacy and need. J Chem Pharm Res 2009;1:31.
39Jadhav SV, Bringas E, Yadav GD, Rathod VK, Ortiz I, Marathe KV, et al. Arsenic and fluoride contaminated groundwaters: A review of current technologies for contaminants removal. J Environ Manage 2015;162:306-25.
40Awasthi PK, Sankhla S, Mathur D. Natural biosorbents: A potential and economic alternative for water deflouridation. J Chem Biol Phys Sci 2016;6:402.
41Venkobachar C, Iyengar L, Mudgal AK. Household defluoridation of drinking water using activated alumina. In: Proceedings of the 2nd International Workshop on Fluorosis Prevention and Defluoridation of Water. Soborg, Denmark: India State of Forest Report, EnDeCo; 19 November, 1997. p. 138-45.
42Daw RK. Experiences with domestic defluoridation in India. In: Proceedings of the 30th WEDC International Conference on People-Centred Approaches to Water and Environmental Sanitation. Vientiane, Lao PDR; 25 October, 2004. p. 467-73.