Community De-fluoridation - Experience in Kaiwara Village, Chikkaballapur District, Karnataka, India - Open Journal Systems
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Indian Journal of Public Health Research & Development, July 2020, Vol. 11, No. 7 85 Community De-fluoridation - Experience in Kaiwara Village, Chikkaballapur District, Karnataka, India Arjunan Isaac1, S Pruthvish2, Radhika3, N S Murthy4 1 Professor, 2Professor, Department of Community Medicine, 3Assistant Professor, Department of Biostatistics, 4 Professor, Department of Biostatistics, MS Ramaiah Medical College, Rajiv Gandhi University of Health Sciences, Bangalore, Karnataka Abstract Background and objective: Reverse osmosis technique is an adequate method for treating ground water for reducing the burden of abnormal levels of fluorides. The method protects the general population from diseases associated with high fluoride levels in the body. The objective of the present study was to assess the suitability and sustainability of reverse osmosis technology for community de-fluoridation of water used for cooking and drinking purposes in Kaiwara village, Karnataka. Methodology: This interventional study was conducted between July 2012 and June 2014 at Kaiwara village, Karnataka using reverse osmosis technique for de-fluoridation of water used for drinking and cooking. Complete chemical analysis of water was done before intervention, and processed water supplying the village was tested every six months after intervention for about two years. The variation in chemical concentrations of various components were analysed. Results: The mean baseline level of fluoride in untreated water was 2.075 mg/dl (above the safety limit), which dropped to 0.08 mg/dl at the end of first six months following the intervention, 0.042 mg/dl in 12 months, 0.1 mg/dl at 18 months and 0.01 mg/dl at 24 months after intervention, which were all below the safety limits for India in the treated water. The mean total dissolved solids in the water was 542.25 mg/dl in the untreated water, which dropped to zero after the first six months, remained at zero in the next six months, rose to 120 mg/dl at 18 months and then dropped to 70 mg/dl at 24 months in the treated water. The observed values were reduced significantly. Discussion: The study concluded that it is possible to set up a community de-fluoridation plant using reverse osmosis technique at Kaiwara village, Karnataka which is economically sustainable and acceptable by local population. Keywords: Water pollution, Fluorides, Reverse osmosis, Community participation. Introduction million people are currently affected, and 66 million people are at risk of developing fluorosis.3 Water as we know, is one among the most important components for all forms of life and safe drinking water Over the last few years, domestic purification is the primary requirement for every human being. There techniques came into use to minimise both inorganic is scarcity in the availability of portable water as natural and organic pollutants in water thereby maintaining the sources or industrial wastes may contaminate water. One quality of water supplied to the urban society.4 There are such contaminant is fluoride.1 various basic types of water purification systems that can be used alone or in combination, e.g., reverse osmosis, Fluorosis is one among the severe health problems cation exchange softening, oxidation, filtration, activated faced by the public in India. Two-third of the states in carbon, disinfection, distillation, anion exchange etc.4,5 India are fluoride endemic,2 while approximately 25
86 Indian Journal of Public Health Research & Development, July 2020, Vol. 11, No. 7 Fluoride concentration present at low levels (< identified next to the main water tank of Kaiwara village 0.5 ppm) in drinking water could cause lack of formation which had a storage capacity of 100,000 litres of water. of dental enamel, dental caries and reduced bone The Zilla Panchayath was approached for the electricity mineralisation whereas high fluoride levels in drinking connection required for running the Reverse Osmosis water could lead to adverse health effects ranging from plant (3Phase and 10KVA) from Kaiwara village. It was mild dental fluorosis to crippling skeletal fluorosis, proposed that a sum of Rs 5/- would be collected for 25 depending upon level of fluoride present and its duration litres of processed water from each household who were of exposure.6,7 willing to purchase the processed water from January 1, 2012 for cooking and drinking purposes. 99.4% of heads Karnataka is among the fluoride endemic states of the families were willing to contribute and 89.8% of in India.8 In Karnataka, districts endemic for fluorosis the heads of the family expressed acceptance for de- are Belgaum, Raichur, Bijapur, Gulbarga (districts fluoridation of water in the village. The money collected in northern Karnataka) as well as Tumkur, Mandya, by selling the processed water was used to run and Mysore, Chitradurga, Shimogga, Chikmagalur, maintain the R O plant. The cost of Rs 5/- per household Bangalore-rural and Kolar (districts of southern and was calculated considering Rs 3/- towards electricity and central Karnataka).9 Kaiwara village now comes under water charges for running of the R O Plant, maintenance Chikkaballapur district but used to be part of Kolar charges for the R O Plant (filter replacement, pump district previously, forming a part of the fluoride belt repair etc) and salaries for the watch man, plant operator bordering Andhra Pradesh. The weather conditions in and electrician. Rs 2/- was further collected towards Kaiwara village are like that of Chikkaballapur district.9 payment for the water distribution vehicle maintenance Results from some of the exploratory bore wells in and petrol for the running of the vehicle as well as salary Chikkaballapur region have recorded the concentration for the water distributer. of fluoride to 2 ppm and above.10 As Kaiwara has no A road map of Kaiwara was prepared and 20 spots alternate source of water, it is dependent solely on ground for water collection were identified in five areas of water through bore wells for its water supply which have the village, which were less than 100 meters from the unacceptable levels of fluoride. The present study aimed farthest house from the identified point (usual water to study the acceptability and sustainability of reverse collection points included). A vehicle with a 1000 litres osmosis technology for community defluoridation of tank fixed to it, which could be sealed from the top after water used for drinking and cooking purposes in Kaiwara filling with processed water and fitted with four taps, was village, Karnataka.10 used for the transport and distribution of the processed water to the collection point at a fixed time each day. Methodology Complete chemical analysis of untreated and processed The present interventional study was conducted water was made before intervention and processed water between July 2012 and June 2014 at Kaiwara village, was tested every six months after intervention for about Karnataka. The study was approved by the Ethical two years and the mean concentration levels before and Review Board. Having gone through a number of after the intervention were compared. studies on comparison of different methods for fluoride removal,11 the Council for Scientific and Industrial Results Research Government12 offered a 40,000 litres capacity The opinion given for all four samples of water reverse osmosis unit custom made for community after complete chemical analysis (Table 1) was that the defluoridation to pilot in the village, and report the water was found to be unfit for potable purpose, as all feasibility of operating and sustaining such a technology the four samples showed excess of fluoride. The mean within a village which can be replicated anywhere else baseline levels of fluoride in untreated water were found in rural India. to be 2.075 mg/dl and the mean total dissolved solids in Installation of the reverse osmosis plant was done in untreated water was found to be 542.25 mg/dl. a plot granted by the Kaiwara Gram Panchayath that was
Indian Journal of Public Health Research & Development, July 2020, Vol. 11, No. 7 87 Samples of the Feed, Product and Reject water in the processed water were found to be significantly obtained from the reverse osmosis plant and tested reduced. which will form a baseline data for our reverse osmosis Also, it was observed that the mean total dissolved process (refer Table 2). solids in the untreated water which was 542.25 mg/dl in The water sample after the intervention was the untreated water which dropped to zero after the first submitted to Public Health Institute Bangalore for six months, remained at zero in the next six months, rose complete chemical analysis (Table 3) and was found to to 120 mg/dl at 18 months and then dropped to 70 mg/ be useful for potable purposes. It was observed that the dl at 24 months in the treated water. The total dissolved mean fluoride levels in the water which was 2.705 mg/ solid in processed water was significantly reduced. dl in the untreated water, clearly above acceptable limits The changes in the various parameters seen in the for India (0.5 mg/dl to 0.9 mg/dl) dropped to 0.08 mg/ four reports are because at different times of the year, dl after the first six months, 0.042 mg/dl in the next six the conditions in bore wells supplying the main village months, 0.1 mg/dl in the next six months and 0.01 mg/ tank also change, depending on the availability of water dl in the last six months which were all below the safety in the various bore wells. limits for India in the treated water. The fluoride levels Table 1: Complete chemical analysis of baseline water available at Kaiwara village Concentration in Concentration in Component Concentration in Concentration in measured Chamundashwari Hill Chikkaballapur Vivekananda Tank Main Bore-well Tank Tank Turbidity as 0.0 0.0 0.0 0.0 (NTU) PH value 7.7 8 7.6 7.4 Dissolved solids 538 481 539.5 611 Total hardness 320 260 292 344 Calcium 54.4 65.6 76.8 94.4 Sodium 55.38 64.71 57.95 74.26 Potassium 4.87 3.6 7.82 5.26 Sulphate 68.6 43.93 184.1 70.2 Alkalinity 250 292 212 260 Chlorides 106 52 74 130 Iron 0.09 0.09 0.08 0.01 Fluoride 1.72 2.08 2.26 2.24 Nitrate 2.56 9.90 5.8 5.5 Physical Clear Clear Clear Clear appearance All components were measured in mg/dl
88 Indian Journal of Public Health Research & Development, July 2020, Vol. 11, No. 7 Table 2: Results of the test run-At 250 PSI pressure in the membrane filter Type of water in RO unit Total dissolved solids (ppm) Flow rate (litres/minute) Feed water 270 - Product water 10 96 Reject water 1100 24 Table 3: Complete chemical analysis of processed water done every six months from July 2012 to June 2013 Mean Mean Mean Mean Sl. concentration concentration concentration concentration Component measured (July 2012) (December 2012) (January 2013) (June 2013) No 1 Turbidity as (NTU) 0.0 0.0 0.0 0.0 2 PH value 6.8 7.8 6.30 7.40 3 Dissolved solids --- --- 120 70 4 Total hardness 76 36.0 58 10 5 Calcium 8.0 1.6 14.82 4.8 6 Sodium 7.2 --- 17 --- 7 Potassium 0.3 --- 0.30 --- 8 Sulphate 0.343 2.38 10 0.01 9 Alkalinity 22 8.0 60 48 10 Chlorides 22 22.0 17.72 10.70 11 Iron .022 Not detected 0.06 0.01 12 Fluoride .024 0.08 0.10 0.01 13 Nitrate 0.015 1.29 1.20 0.60 14 Physical appearance Clear Clear Clear Clear All components were measured in mg/dl
Indian Journal of Public Health Research & Development, July 2020, Vol. 11, No. 7 89 Discussion osmosis plants in Kaiwara village and five other reverse osmosis plants in the surrounding villages following our Fluoride is one of the normal constituents in model today. groundwater in this region. The concentration of fluoride is variable, and it depends on the source of Disclaimer: Not applicable. water. Provision of safe drinking water with optimal fluoride levels is the solution to protect against diseases Funding: MS Ramaiah Medical College, Bangalore, associated with abnormal fluoride content in water used Karnataka for drinking and cooking. In this study, reverse osmosis Conflicts of Interest: Nil technology was applied for community de-fluoridation of water in Kaiwara village, Karnataka. Ethical Clearance: Taken from Institutional Ethics Committee (MS Ramaiah Medical College, Bangalore, In this study, it was also observed that the mean Karnataka) fluoride levels in the water which was 2.705 mg/dl in the untreated water which is clearly above acceptable limits References for India (0.5 mg/dl to 0.9 mg/dl) dropped to 0.08 after 1. Glass RG. Water purification systems and the first 6 months, 0.042 mg/dl in the next six months, recommendations for fluoride supplementation. J 0.1 mg/dl in the next six months and 0.01 in the last six Dent Child. 1991;58(5):405-8. month which are all below the safety limits for India in the treated water. This reduction in fluoride levels in 2. Saravanan S, Kalyani C, Vijayarani MP, Jayakodi water was found to be significant. This is in accordance P, Felix A, Nagarajan S. Prevalence of dental with the study conducted by Prabhakar et. al.13 in which fluorosis among primary school children in there was statistical significance in the reduction of rural areas of Chidambaram taluk, Cuddalore fluoride levels by reverse osmosis technique. district, Tamil Nadu, India. Indian J Community Med. 2008;33:146–150. In the present study, it was observed that the mean 3. Majumdar KK. Health impact of supplying total dissolved solids in the water which was 542.25 mg/ safe drinking water containing fluoride below dl in the untreated water was dropped to zero after the permissible level on flourosis patients in a fluoride- six months, zero in the next six months, 120 mg/dl in the endemic rural area of West Bengal. Indian J Public next six months and then 70 mg/dl in the last six months Health. 2011;55:303–308. in the treated water. This reduction in total dissolved 4. Jobson MD, Grimm SE, Banks K. Henley G. The solid in water was found to be significant. This is in effects of water filtration systems on fluoride: accordance with the study conducted by Do-Hyung Kim Washington DC, Metropolitan area. J Dent child et.al.14 where there was reduction in the concentration of 2000;67:350-4. total dissolved salts by reverse osmosis technique which was significant. 5. Pranati Eswar and Devaraj C G. Water defluoridation: Field studies in India. Indian j. dent. From the current study, we concluded that it is adv. 2011;3:526-533. possible to set up, operate and sustain a community de- 6. World Health Organization. Guidelines for fluoridation plant using reverse osmosis technology. drinking water quality. Recommendations, 3rd The economic feasibility of using a technology like edition, vol 1, 2004. (accessed 17 January 2020). reverse osmosis for community defluoridation has https://www.who.int/water_sanitation_health/dwq/ been proved through the reverse osmosis technique- GDWQ2004web.pdf based intervention in Kaiwara village. This has been 7. Verma A, Shetty B K, Guddattu V, Chourasia M K, a self-sustaining and effective model for community Pundir P. High prevalence of dental fluorosis among de-fluoridation of water used for drinking and cooking adolescents is a growing concern: a school based purposes in Kaiwara village. The intervention has been cross-sectional study from Southern India. Environ self-sustaining for the past four years. This has been Health Prev Med. 2017;22:17. confirmed by the fact that there are already three reverse
90 Indian Journal of Public Health Research & Development, July 2020, Vol. 11, No. 7 8. Jha S K, Mishra V K, Sharma D K, Damodaran Technology. 2011;18:314-318. T. Fluoride in the environment and its metabolism 12. Council of Scientific & Industrial Research | CSIR in humans. Rev Environ Contam Toxicol. | GoI; Csir.res.in; (accessed 17 January 2020). 2011;211:121–42. https://www.csir.res.in/. 9. Susheela A K. Fluoride and Fluorosis. Fluorosis 13. Prabhakar A R, Raju O S, Kurthukoti A J, Vishwas Research & Rural Development Foundation. 2016. T D. The effect of water purification systems on 10. Md. Najeeb K. Ground Water Information Booklet fluoride content of drinking water. J Indian Soc Chickballapur District, Karnataka [Internet]. Vol. Pedod Prev Dent. 2008;26:6-11. 1. Ministry of Water Resources Central Ground 14. Kim D-H, Park S, Yoon Y, Park C M. Removal Water Board. 2012. of Total Dissolved Solids from Reverse Osmosis 11. Anand Babu, Sujish D, Murugappa M S, Concentrates from a Municipal Wastewater Mohanakrishnan G, Kalyanasundaram P, Raj B. A Reclamation Plant by Aerobic Granular Sludge. comprehensive treatment method for defluoridation Water. 2018;10:882. of drinking water. Indian Journal of Chemical
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