Abstract
Fluoride (F) toxicosis in the forms of dental, skeletal and non-skeletal fluorosis were investigated in 996 tribal individuals (503 males and 493 females) above 10 years of age living in nine F endemic villages of Dungarpur district of Rajasthan, India. Drinking water sources of these villages contained F in the range of 1.5–4.4 ppm. Of these tribals, 735 (73.8 %) and 294 (29.5 %) were found to be afflicted with mild to severe dental and skeletal fluorosis, respectively. At 1.5 ppm F concentration the prevalence of dental and skeletal fluorosis was 33.9 and 10.7 %, respectively. A polymorphism of dental fluorosis in the form of brown to deep yellowish bilaterally stratified horizontal lines, pits or patches, and fine dots or granules was noted on anterior teeth of tribal individuals. Irregular wearing, excessive corrosions (abrasions), dark-yellowish pigmentation of exposed cementum and dentine material, diastemas between teeth, pronounced loss of tooth supporting bone with recession, and bulging of gingiva (gum) were also present. Among the adult and old tribal individuals, the following mild to severe manifestations of skeletal fluorosis such as crippling, kyphosis, invalidism and genu-varum syndrome were found. Sporadic cases of paraplegia and quadriplegia were also found. None of the fluorotic tribals showed evidence of genu-valgum syndrome. Radiological changes were also observed in these individuals. Other signs of chronic F intoxication in soft tissues (non-skeletal fluorosis) included colic, intermittent diarrhoea or constipation, bloating, urticaria, polyurea, polydipsia, repeated abortions, still birth and sterility. Data pertaining to prevalence of osteo-dental fluorosis in relation to age and F concentration exhibited statistically significant correlation.
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Introduction
Chronic exposure to fluoride (F) through drinking water in man and animals produces range of toxic effects on hard tissues like teeth (dental fluorosis) and bones (skeletal fluorosis) [1–6]. Excess F exposure also damages soft tissues and organs of body [1, 2, 7, 8]. The prevalence and severity of these toxic effects have also been studied in relation to certain biological and non-biological determinants [9–12]. In India, fluorosis is endemic in many states including Rajasthan, where almost all districts have high F content (up to 18.0 ppm) in their drinking/ground water sources [13, 14] and fluorosis in the form of osteo-dental fluorosis have been reported in certain areas of Rajasthan [15–17]. In southern Rajasthan, where tribal population is predominant, 0.3–10.8 ppm F concentration has been reported [18]. However, studies on fluorotoxicosis in socio-economically backward and mostly illiterate tribals are limited. The present paper reports relative prevalence and severity of toxic effects of F in tribals living in villages having high content of F in drinking water.
Material and Methods
During a recent cross-sectional survey in F endemic villages (Table 1) of Dungarpur district of Rajasthan, India, 996 tribal individuals of either sex (>10 years age) were clinically examined for evidence of osteo-dental fluorosis. The mean F concentration in drinking water of these villages ranged from 1.5 to 4.4 ppm [11]. Criteria for the identification of dental and skeletal fluorosis were followed as described in earlier report [1]. In addition, 1–2 clinically identified fluorotic individuals (>40 years) from each village were also examined radiologically for further evidence of skeletal fluorosis or any other bone deformities [19–21]. These subjects were also asked for medical history (non-skeletal fluorosis) as for colic, diarrhoea, constipation, abdominal pain, bloating, skin allergy, repeated urination and drinking of water, impaired reproductive functions etc.
Tribals of studied areas have very poor nutritional status. In general, they intake maize, barley, rice, onion with or without pulses and vegetables. Other food stuffs like milk, curd, ghee and fruits are very rare in their diets. They are mostly habitual for daily intake of local wine, tea and smoking.
In the present investigation, F concentration in urine and blood was not estimated in the fluorotic individuals. Identification of chronic F effects in these tribal people was based on clinical findings only. Data pertaining to prevalence of osteo-dental fluorosis were also analyzed statistically [22].
Results and Discussion
Dental Fluorosis
Bilateral dental mottling (Figs. 1, 2, 3, 4, 5) was found in 735 of 996 tribal people (73.8 %) in the present study (Table 1). The highest (100 %) and the lowest (33.9 %) prevalence of dental fluorosis were found in the areas with 3.7 and 1.5 ppm F concentration in drinking water, respectively. A variable prevalence of dental fluorosis was observed in the villages having the same or almost similar F concentration in the drinking water (Table 1). The maximum prevalence (97.4 %) of dental fluorosis was observed in above 60 year age group and the minimum (40.5 %) in the 10–20 year age group. However, a little variation in prevalence was found between the two sexes (Table 2). A high correlation coefficient was found between water fluoride concentration and prevalence of osteo/dental fluorosis.
Polymorphism of dental fluorosis was observed in tribal individuals which appeared bilaterally in the form of light brown to deep-yellowish pits or patches (Figs. 1, 2, 3, 4, 5), fine dots (Figs. 1, 2, 3, 4, 5) and horizontal stratified lines (Figs. 1, 2, 3, 4, 5 , 8, 9) at 1.5 ppm F concentration. Corrosion of tooth material with deep brown or black staining was found above 2.0 ppm F concentration in drinking water. In older people, irregular wearing, excessive corrosion or abrasions, recession and bulging of gingiva, and diastema (gaps) between teeth (Figs. 1, 2, 3, 4, 5) were found at F concentration above 2.0 ppm.
In India, dental fluorosis has previously been described in humans ingesting 0.5–1.0 ppm F in drinking water [23, 24], while at concentrations of 3.4–3.8 ppm, 100 % dental fluorosis has been reported [25]. In the present study, the highest (100 %) prevalence of dental fluorosis in tribals was observed in the villages having F concentration above 3.7 ppm. A variation in prevalence of fluorosis at almost similar F concentrations was observed in the present study. This can be attributed to a number of factors or determinants such as duration of F exposure and its intake frequency, habits, nutrition, climate, salts in drinking water besides the individual susceptibility, biological response and genetics of an individual [3, 26].
Skeletal Fluorosis
Out of 996 tribal people, 294 (29.5 %) revealed evidence of skeletal fluorosis of varying grades (Table 1). Of these 154 (30.6 %) were men and 140 (28.4 %) women. The prevalence of skeletal fluorosis was generally found to increase with increasing age and F concentration in drinking water (Table 2). Onset of skeletal deformities at 1.5 ppm F was observed mostly in the higher age group (>31 years). Crippling deformity was found at and above 2.0 ppm F. The more extreme forms of skeletal deformities or chronic F effects as kyphosis, invalidism, genu-varum (legs bowed outward at the knee), and crossed or scissor-shaped legs (Figs. 6, 7) were observed only in adults above the age of 41 who had been consuming water containing 3.0 ppm F. Secondary neurological complications, paraplegia and quadriplegia (Figs. 8, 9) were seen only in a few individuals (>50 years) where drinking water had 4.0 ppm concentration of F. None of the tribal individuals showed evidence of genu-valgum or knock-knees deformity (legs angle inward at the knee).
Radiographs (x-rays) of cervical spine (Figs. 10, 11, 12, 13, 14), ribs and lumbar-dorsal spine with pelvis (Figs. 10, 11, 12, 13, 14), lower limb (Figs. 10, 11, 12, 13, 14), forearm (Figs. 10, 11, 12, 13, 14) and pelvis (Figs. 10, 11, 12, 13, 14) of 1–2 fluorotic tribal subjects of each village showed increased bone mass and density as well as exostoses, calcification of ligaments and interosseous membranes and osteosclerosis. These changes were more progressive with increasing age and F concentration in the drinking water and provided further evidence of skeletal fluorosis in these villages. Other radiological changes have also been observed as described elsewhere [19–21].
The incidence and severeness of skeletal fluorosis was higher in the higher age group (Table 2) and increased with increasing F concentration, which is certainly due to longer exposure and increasing of F toxicity. Other workers have also observed a higher incidence of skeletal fluorosis in old age group [27]. Several workers have reported skeletal fluorosis and crippling at F levels above 1 and 3 ppm, respectively [1]. In the present study, no case of genu-valgum syndrome was noted, in contrast to some of the southern (Andhra Pradesh, Karnataka, and Tamil Nadu) and central (Madhya Pradesh) Indian states where fluorosis is also endemic and cases of genu-valgum syndromes along with osteoporosis of long bones have been reported [28, 29]. This deformity or F effect has not been reported from any other hyper endemic areas of Rajasthan [30]. The way in which F causes genu-valgum syndrome is still uncertain and inconclusive. However, level of some micronutrients may be responsible for this deformity. In F endemic areas of Andhra Pradesh genu-varum was observed in those people who had low calcium and high molybdenum content in their staple diet [28].
Non-skeletal Fluorosis
In the fluorotic people most common clinical signs or history such as intermittent diarrhoea or constipation, abdominal pain, flatulence, urticaria, polyurea and frequent intake of water (polydipsia) were found. Such observations have also been reported in humans [31–33] living in F endemic areas. However, in the areas under present survey, cases of repeated abortions, sterility, reluctance to reproductive functions and erectile dysfunction in male individuals were relatively higher as compared to non-endemic areas of F. Indeed gastro-intestinal discomforts, neurological and impaired reproductive dysfunctions are considered as the earlier signs of chronic F intoxication in both men [1, 31–33] and animals [7, 8, 34].
The prevalence and severity of chronic fluoride effects (fluorosis) are relatively higher in tribal individuals as compared to their non-tribal counter parts [26]. Infact tribals have poor nutritional status and habit of excessive drinking of local wines and tea [10]. Poor nutritional value of their food may cause deficiency of vitamins and other dietary components which can decrease or increase F absorption or intoxication [1]. It is well known that milk, curd and some vegetables are rich in calcium, whereas citrus fruits and leafy vegetables contain vitamin-C. Both these nutrients and fat (ghee and edible oils) reduce F absorption [1] and hence mitigate F toxicity. The tribals are predominantly farmers and laborers and generally drink more water, thereby maximizing their F intake besides drinking wine, beverages and tea that are additional sources of F toxicity. Besides these causes, intrinsic individual genetic differences of tribals may also contribute to the degree of F intoxication [26].
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Acknowledgments
Author thanks the University Grants Commission, New Delhi, India for financial assistance. Author is also thankful to Dr. H. Jain (Orthopaedician), Dr. Darshana Choubisa (Dentist) and Dr. Zulfiya Sheikh (Asst. Prof. of Zoology) for their cooperation.
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Choubisa, S.L. Fluoride in Drinking Water and its Toxicosis in Tribals of Rajasthan, India. Proc. Natl. Acad. Sci., India, Sect. B Biol. Sci. 82, 325–330 (2012). https://doi.org/10.1007/s40011-012-0047-8
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DOI: https://doi.org/10.1007/s40011-012-0047-8