Abstracts
OBJECTIVE: To assess fluoride (F-) intake from water and toothpaste by children aged 18 to 36 months and to monitor the F- concentrations in the drinking water system in a tropical city of Brazil. METHODS: Children (n=58) aged 18-36 months, all lifetime residents of Penedo, state of Alagoas, Brazil, participated in this study. Water F- analyses were carried out in 7 different occasions at least a week apart. For 2 days all the water drunk by each child was accounted for. Fluoride intake from water for each child was estimated using the mean F- concentration of water in 7 different occasions. Fluoride intake from toothpaste was estimated by subtracting the recovered post-brushing F- from the original amount placed in the toothbrush. The F- intake from water and toothpaste was estimated by dividing the total amount of F- ingested by the weight of each child. RESULTS: The mean F- concentration in the drinking water was 0.94 ppm (mean range 0.78-1.1 ppm), which is above the 0.7 ppm recommended for this area of Brazil. Mean total F- intake from water and toothpaste was 0.128 mg F-/Kg Body Weight/day. The daily means of F- intake from water and toothpaste were 0.021 and 0.107 mg F-/Kg Body Weight, respectively. Ninety six percent of children showed F- intake above 0.07 mg F-/Kg Body Weight/day. CONCLUSIONS: Children in Penedo are at risk for developing dental fluorosis due to high F- intake from fluoridated toothpastes. Water fluoridation showed low contribution to the total F- intake. However, high water F- concentrations in the water indicate the need of surveillance of the artificial water fluoridation system.
Fluoride; Fluoridation; Toothpastes
OBJETIVOS: determinar a ingestão de flúor (F-) pela água e creme dental em crianças de 18 a 36 meses de idade que moram em uma cidade de clima tropical no Brasil e monitorar as concentrações de F- no sistema de água potável. MATERIAIS MÉTODOS: participaram deste estudo crianças (n=58), 18-36 meses, todas residentes vitalícias de Penedo (Alagoas), Brasil. As análises de F- em amostras de água foram realizadas em 7 ocasiões diferentes em semanas separadas. Durante 2 dias toda a água bebida por cada criança foi considerada. A ingestão de fluoreto para cada criança foi calculada pela média de flúor na água nas 7 ocasiões diferentes. A ingestão de F- pelo creme dental foi calculada subtraindo a saliva recuperada do expectorado pela quantidade de F- colocada na escova dental. A ingestão de F- de água e pasta de dentes foi calculada dividindo a quantia de F ingerida pelo peso de cada criança. RESULTADOS: A concentração média de F- em água potável foi de 0,94 ppm (variando de 0.78-1.12 ppm) estando acima do recomendado para esta área do Brasil que é de 0,7 ppm. A ingestão de F- total (água + creme dental) foi de 0,128 mg de F/Kg peso/dia. As médias diárias de ingestão de F- pela água e creme dental foram de 0,021 e 0,107 mg F-/Kg de peso corporal dia, respectivamente. Noventa que seis por cento das crianças demonstraram ingestão de F- superior a 0,07 mg de F-/Kg peso/dia. CONCLUSÕES: crianças em Penedo estão sob risco de desenvolver fluorose dental devido a elevada ingestão de F- pelo creme dental fluoretado. Adição de flúor à água de água mostrou baixa contribuição ao flúor total ingerido. Porém, altas concentrações de F- na água indicam a necessidade de vigilância do sistema de fluoretação artificial das águas.
Flúor; Fluoretação; Creme dental
ORIGINAL ARTICLES
Fluoride intake from drinking water and dentifrice by children living in a tropical area of Brazil
Ingestão de flúor pela água e creme dental por crianças residentes de uma área de clima tropical do Brasil
Leila Maria F. OmenaI; Milton F. de A. SilvaII; Cleone Calheiros PinheiroI; Jairo C. CavalcanteIV; Fábio Correia SampaioV
IDDS, M.Sc, Laboratory of Preventive Dentistry -Department of Dentistry - Federal University of Alagoas - Brazil
IIDDS, M.Sc. Ph.D, Laboratory of Preventive Dentistry -Department of Dentistry - Federal University of Alagoas - Brazil
IIIB.Sc, Laboratory of Preventive Dentistry -Department of Dentistry - Federal University of Alagoas - Brazil
IVMD, Department of Health - State of Alagoas - Brazil
VDDS, M.Sc., Ph.D, Laboratory of Oral Biology - Federal University of Paraiba - Brazil
Corresponding address Corresponding address: Milton F. de A. Silva P.O. Box, 533 - Cep.: 57020-970 Tel: 55 (82) 9972-3064 e-mail: mfas@csau.ufal.br
ABSTRACT
OBJECTIVE: To assess fluoride (F-) intake from water and toothpaste by children aged 18 to 36 months and to monitor the F- concentrations in the drinking water system in a tropical city of Brazil.
METHODS: Children (n=58) aged 18-36 months, all lifetime residents of Penedo, state of Alagoas, Brazil, participated in this study. Water F- analyses were carried out in 7 different occasions at least a week apart. For 2 days all the water drunk by each child was accounted for. Fluoride intake from water for each child was estimated using the mean F- concentration of water in 7 different occasions. Fluoride intake from toothpaste was estimated by subtracting the recovered post-brushing F- from the original amount placed in the toothbrush. The F- intake from water and toothpaste was estimated by dividing the total amount of F- ingested by the weight of each child.
RESULTS: The mean F- concentration in the drinking water was 0.94 ppm (mean range 0.78-1.1 ppm), which is above the 0.7 ppm recommended for this area of Brazil. Mean total F- intake from water and toothpaste was 0.128 mg F-/Kg Body Weight/day. The daily means of F- intake from water and toothpaste were 0.021 and 0.107 mg F-/Kg Body Weight, respectively. Ninety six percent of children showed F- intake above 0.07 mg F-/Kg Body Weight/day.
CONCLUSIONS: Children in Penedo are at risk for developing dental fluorosis due to high F- intake from fluoridated toothpastes. Water fluoridation showed low contribution to the total F- intake. However, high water F- concentrations in the water indicate the need of surveillance of the artificial water fluoridation system.
Uniterms: Fluoride; Fluoridation; Toothpastes.
RESUMO
OBJETIVOS: determinar a ingestão de flúor (F-) pela água e creme dental em crianças de 18 a 36 meses de idade que moram em uma cidade de clima tropical no Brasil e monitorar as concentrações de F- no sistema de água potável.
MATERIAIS MÉTODOS: participaram deste estudo crianças (n=58), 18-36 meses, todas residentes vitalícias de Penedo (Alagoas), Brasil. As análises de F- em amostras de água foram realizadas em 7 ocasiões diferentes em semanas separadas. Durante 2 dias toda a água bebida por cada criança foi considerada. A ingestão de fluoreto para cada criança foi calculada pela média de flúor na água nas 7 ocasiões diferentes. A ingestão de F- pelo creme dental foi calculada subtraindo a saliva recuperada do expectorado pela quantidade de F- colocada na escova dental. A ingestão de F- de água e pasta de dentes foi calculada dividindo a quantia de F ingerida pelo peso de cada criança.
RESULTADOS: A concentração média de F- em água potável foi de 0,94 ppm (variando de 0.78-1.12 ppm) estando acima do recomendado para esta área do Brasil que é de 0,7 ppm. A ingestão de F- total (água + creme dental) foi de 0,128 mg de F/Kg peso/dia. As médias diárias de ingestão de F- pela água e creme dental foram de 0,021 e 0,107 mg F-/Kg de peso corporal dia, respectivamente. Noventa que seis por cento das crianças demonstraram ingestão de F- superior a 0,07 mg de F-/Kg peso/dia.
CONCLUSÕES: crianças em Penedo estão sob risco de desenvolver fluorose dental devido a elevada ingestão de F- pelo creme dental fluoretado. Adição de flúor à água de água mostrou baixa contribuição ao flúor total ingerido. Porém, altas concentrações de F- na água indicam a necessidade de vigilância do sistema de fluoretação artificial das águas.
Unitermos: Flúor; Fluoretação; Creme dental.
INTRODUCTION
Fluoridated toothpastes have been regarded as one of the most important factors responsible for the decline of caries incidence in the western world during the last decades5,16. Fluoride (F-) has also been implicated with an increase in dental fluorosis23,6,17. There are compelling evidences that the use of fluoridated toothpaste before six years of age is a risk indicator for dental fluorosis17,7. In order to avoid the side effect of fluorosis, the amount of ingested fluoride should not exceed 0.07 mg F-/Kg body weight/day3,14. The critical period for dental fluorosis in permanent maxillary incisors appears to be from 15 to 24 months of age for boys and 21 to 30 months of age for girls7,13.
Two previous Brazilian studies performed in the South Region of Brazil demonstrated a total F intake in children of 0.09 mg F-/Kg body weight/day with 55% attributed to fluoridated toothpastes15 and 0.13 mg F-/Kg body weight/day with 80% attributed to fluoridated toothpastes1. So far, no data are available about the fluoride intake by children from the Northeast Region of Brazil, where industrial food is less consumed and utilization of fluoridated toothpastes may differ.
The purpose of this study was twofold: a) to assess the fluoride intake by children aged 18 to 36 months living in a tropical area of Brazil from fluoridated water and toothpaste and b) to assess the F- concentration in the drinking water of the city of Penedo.
MATERIAL AND METHODS
Area under study
The city of Penedo, with approximately 60,000 inhabitants, is one of the few cities of the Northeast region of Brazil with artificial water fluoridation. Fluoridation has been active since 1989. Penedo is localized at the northern margin of the São Francisco river, from where the water is collected and transferred to a water treatment plant where fluoride is added. The mean annual temperature is above 24ºC12. About 50% of the population survives with an annual income of US$ 330.00 and 4.2% have no income11. The DMFT of the region is around 3.5 for non-fluoridated communities and 1.7 for communities like Penedo2. A dental caries preventive program in nurseries and schools is available. The preventive program includes toothbrushing with fluoridated toothpaste twice a day in the nursery and mouthrinse with 0.2% NaF for school children older than 6 years of age.
Ethical consent and sample
The Institutional Review Board of the Federal University of Alagoas, Brazil, granted permission for the study. Only children (aged 18-36 months) whose parents signed the consent letter and provided full cooperation regarding sample collection and answered a questionnaire participated in this study. Fifty-eight children (28 male and 30 female) were eligible. These children were born and lifetime residents in Penedo and used the communal fluoridated water since birth; 32 were enrolled in the municipal nurseries, where they stayed all day, and 26 had to be followed at home.
Oral hygiene habits
Parents filled a questionnaire to provide data about the frequency that their child brushes his/her teeth, at what age they started toothbrushing, if they rinse their mouths after toothbrushing and if they have the habit of swallowing toothpaste. Additionally, one of the authors (LMFO) observed and registered the events during each child's toothbrushing procedure.
Water fluoride analysis
Drinking water samples were collected on seven different days. These 7 days of water collection were at least a week apart from each other. On the scheduled day, water samples were collected from 10 different locations across Penedo and analized for F- concentration.
After diluting each sample (1:1 v/v) with TISAB II, fluoride analysis was done in duplicate, using a specific ion electrode (combined F- electrode 9609, Orion Research Inc., USA) coupled to a pH/MV meter (Procyon Research Inc., Brazil). Fluoride standards ranged from 0.1 10 ppm F-.
The F- values in ppm were averaged to produce the fluoride concentration of the day.
Fluoride analysis in fluoridated toothpastes
A duplicate sample, 100 mg, of the dentifrices used by the children was analyzed for fluoride. Each sample was homogenized with 10 mL of distilled deionized water. Then, 0.5 mL of 2M HCL were added to 0.5 mL of the dentifrice solution. The former was incubated at 45ºC under constant agitation for 2 hours. After this time the mixture was neutralized with 1.0 mL of 1M NaOH and 2 mL of TISAB II were added. The fluoride concentration of each dentifrice sample was assessed using a specific ion electrode (combined F- electrode 96-09 Orion Res. Inc., USA) coupled to a pH/MV meter (Procyon Research Inc., Brazil). Standards ranged from 4 to 64 ppm F-.
Fluoride intake from drinking water
All the water ingested by each child during 2 days was accounted for. At the nurseries, water was weighed at each time a child asked for it. For those who were followed at home, a duplicate sample was collected and stored to be weighed later at the laboratory. The fluoride ingestion from water was calculated by multiplying the quantity of ingested water by the mean fluoride in the water calculated from the 7 days water collection samples. Results are expressed as mg F-/Kg body weight/day.
Fluoride intake from fluoridated toothpastes
The Rojas-Sanchez protocol was followed21. In brief, the person responsible for brushing the child's teeth was asked to brush the child's teeth as usual. Only 7 children used to brush by themselves and they did it as normally they would do. All toothbrushes were pre-weighed using a portable electronic balance (FX 300) with 0.01-g precision. After placing the dentifrice, the toothbrush was weighed again, so the amount of toothpaste could be determined. Then, the child had his/her teeth brushed either by the person responsible or by himself/herself as usual. When toothbrushing was completed, all residual dentifrice around his/her mouth and any spit out were collected and placed in 30 mL of distilled deionized water. The toothbrush was also placed in the same container and shaken until no residual toothpaste was present at the toothbrush (solution 1). Solution 1 was then frozen at -12ºC and later transported to the laboratory for fluoride analysis. A sample of the child's toothpaste was also collected for analysis.
Fluoride analysis
The collected solution (toothbrush residue + child's expectorate) was defrosted at room temperature and completely homogenized. An amount of 0.5 mL of 2M HCl was added to each 0.5 mL of the collected solution. This mixture was then incubated for 1 hour at 45ºC, under vigorous agitation (1300 rpm) in a Compact Thermomixer (Eppendorf Corp., Germany). After this time, the mixture was neutralized with 1.0 mL of 1M NaOH and 2 mL of TISAB II were added. The same procedure was applied to the standards. Then, the standards and samples were analyzed in duplicate, using the specific ion electrode (combined F- electrode 96-09 Orion Res. Inc., USA) coupled to a pH/MV metter (Procyon Research Inc., Brazil). Fluoride standards ranged from 4 to 64 ppm F-. The fluoride ingestion from the toothpaste was calculated by subtracting the fluoride in solution from the fluoride content in the toothpaste. Information about daily toothbrushing frequency and weight of each child were used to calculate the ingested mg F-/kg of body weight/day.
Statistical analysis
The mV readings produced by the samples and by the fluoride standards were entered into a computer and transformed in ppm using a polynomial equation and the Statview statistical package (SAS Institute, USA, 1995). Regression analysis was done to assess the relationship between age of the children and fluoride intake from toothpastes. All fluoride and children information data were entered into an ExcelTM spreadsheet and analyzed using the EpiInfo 2000 statistical package.
RESULTS
There were differences in fluoride concentration when comparing different collection sites. There were also day to day fluctuations at the same site. Figure 1 shows F- concentrations fluctuating during the collection days. Water sample fluoride concentration ranged from 0.58 - 1.52 ppm F-. The mean F- concentration was 0.94 ppm (range 0.78-1.14).
Fluoride concentration in the toothpastes used by the children ranged from 1,063 ± 16.31 to 1,514 ± 78.8 ppm F- (Table 1). The mean (±SD) amount of toothpaste placed on each toothbrush was 0.58 ± 0.20 g.
The mean (±SD) age of the children was 2.4 ± 04 years and their mean weight was 13.31 ± 2.89 Kg. About 70% of children in this study began toothbrushing from 6 to 18 months of age, 20% between 18 and 24 months of age and 12% in a later age; 69% (n=40) of the children brush their teeth 3 or more times a day, 22.4% (n=13) do it twice a day and only 8.6% (n=5) once a day. No one reported not to brush the teeth of their child.
A total of 89.7% (n=52) had the habit of swallowing toothpaste during toothbrushing but only 31% would eat toothpaste in occasions other than during toothbrushing time.
The mean±SD of fluoride placed on the toothbrush was 0.711±0.245 mg, from which 0.153±0.187 mg was expectorated. The estimated mean of F- ingested was 0.558±0.232 mg F-.
Table 2 shows mean (±SD) fluoride ingested from water and fluoridated toothpastes. The F-intake from water corresponds to less than 20% of the mean daily F- ingested. Toothpaste accounted for 84% of the daily F- ingested. Only 3.4% (n=2) of the children did not reach the limit of 0.07 mg F-/kg of body weight/day.
There was a positive and significant correlation (r=0.45, p<0.05) between age of the child and F- ingested (mg) from toothpaste per Kilogram of body weight (Figure 2). There was no significant correlation either for males or females when analyzed separately.
DISCUSSION
In Brazil, the most common sources of fluoride are fluoridated water, toothpaste and professional topical application. However, there are probably regional differences that should be considered. In the South and Southeast regions of Brazil, over 60% of the population is exposed to fluoridated water, compared to only 6.85% in the Northeast region and 13% in the North region8. There are reports that the water fluoridation system is not well controlled in other cities of Brazil. For example, the fluoride concentration in Bauru, state of Sao Paulo, ranged from 0.01 to 1.3 ppm9,4 .
In Penedo, fluoride was above the recommended level of 0.7 ppm F- in many of the water samples. On the other hand, the contribution of fluoridated drinking water to F- ingestion was only 0.02 mg F-/Kg body weight/day, which is well below the theoretical threshold of 0.07 mg F-/Kg body weight/day and this daily dosage poses little risk for dental fluorosis. This intake from water reflects a calculation using the mean fluoride concentration in water: 0.94 ppm. Since a fluctuation occurred, a range in F- ingestion from water can be expected. The high fluoride concentration in the drinking water of Penedo may occur in other parts of Brazil and is probably related to the lack of automatic dosage devices and fluoride specific electrodes to monitor the fluoride concentration in the water and trained personnel9. Water fluoridation control is expected to be improved after implementing new health governmental programs22.
In Chile, Villa, et al.25 (1998) suggested that there are no additional benefits from F- concentrations greater than 0.53 ppm in the drinking water. Moreover, in the United States, additional caries reduction obtained with a fluoride concentration in water higher than 0.7 ppm appears to be negligible or non-existent10. It is reasonable to maintain the water fluoride concentration at 0.7 ppm in Penedo, since dental caries is still a problem in that area and there is no guarantee about utilization of fluoridated toothpastes by the children22. In addition, there is evidence that dental fluorosis can be reduced by 50% without changes in the fluoride level in water20.
The Contente and Gessy Cristal toothpastes claim to have a fluoride concentration of 1,450 ppm F-, yet our analysis detected only 1,063 ppm F- and 1,163 ppm F-, respectively. Since these toothpastes have calcium carbonate as the abrasive component, despite the treatment with hydrochloric acid, fluoride may have combined with calcium and may not have been detected by our analysis. However, the toothpastes Colgate and Sorriso showed a fluoride concentration within 5% of the labeled fluoride concentration in spite of having similar abrasive and fluoride compound as the others. Similar results have been shown in toothpastes from countries with non-established market economies24.Thus, it appears that the formulation of these toothpastes needs improvement.
In Brazil, low socioeconomic status groups seldom use fluoridated toothpaste but this is not the case in Penedo26. The preventive dentistry program emphasizes the use of fluoridated toothpaste by young children. Brushing the teeth 3 times a day at this age is unusual. However, in Penedo's nursery schools, it is mandatory for each child to have their teeth brushed after their first and the last meal before going home. Parents are also encouraged to avoid their child going to bed with dirty teeth. Even though it is desirable to establish the habit of toothbrushing earlier in life, these children are using toothpastes with high fluoride concentration, not recommended for this age group. However, unlike other countries or even other Brazilian regions, where the so-called low dosage (400-550 ppm F-) children's toothpastes are available20; low fluoride toothpastes are not easily available in Penedo. Seventy percent of the children brushed their teeth 3 or more times per day and 89% enjoyed eating toothpaste, therefore it can be assumed that the risk for developing dental fluorosis is high. Two facts also add to the high intake of fluoride by these children: a) the cheapest toothpastes found in the Brazilian market have a fluoride concentration between 1,450 and 1,500 ppm, and b) the recommendation to fill the toothbrush bristles with toothpaste is stated in the health program in Penedo. Thus, the solution to reduce the fluoride intake from toothpaste could be to provide a low dosage children's toothpaste or by placing smaller amounts of toothpaste on the toothbrush when using a normal but lower concentration of 1,000-1,100 ppm F- toothpaste and by discouraging the habit of ingesting toothpaste. In Australia, Riordan20 (2002) showed that reducing the use of fluoride supplements and promoting the use of low fluoride toothpastes reduced dental fluorosis.
Even though some studies reported that fluoride ingestion during toothbrushing is reduced with age, we found the opposite18,19. This could be due to the age of the children in this study. Other studies compared toothpaste ingestion in 3- to 7-year-old children while in this study the children are younger and the difference in age are is only some months19. Another possibility might be that during this period and up to certain age, toothpaste ingestion increases and then later diminishes. Levy et al.14 (2001) observed that fluoride intake increases from 12 20 months and decreases with increasing mother's age in a three-way interaction. We could not evaluate this three-way interaction in this study.
Additional fluoride intake from food was not evaluated in this study. As food is prepared with drinking water and the food itself may contain some fluoride, the total fluoride ingestion may be even higher than observed. It is estimated that a fluoride intake of 1.0 mg from toothpaste plus 0.5 mg F- from diet may produce a total fluoride intake of 0.107 mg F-/kg bw13. Our findings are very similar to those found in Bauru: 0.130 mg F-/kg bw for total F- intake1. In the Bauru study, fluoridated toothpaste alone contributed with 0.106 mg F-/kg bw, whereas in our study this value was 0.107 mg F-/kg bw. Although brushing frequency might be overestimated in our study due to daily variations in brushing frequencies, the F- intake is high and needs to be considered by public health authorities. A survey of dental caries and fluorosis prevalence is being conducted to establish the real situation in this area.
CONCLUSIONS
Children in Penedo are at risk for developing dental fluorosis due to high F- intake from fluoridated toothpastes. Water fluoridation showed low contribution to the total F- intake. However, high water F- concentrations in the water indicate the need of surveillance of the artificial water fluoridation system.
Received: September 19, 2005
Modification: June 27, 2006
Accepted: September 6, 2006
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Corresponding address:
Publication Dates
-
Publication in this collection
09 Jan 2007 -
Date of issue
Oct 2006
History
-
Received
19 Sept 2005 -
Reviewed
27 June 2006 -
Accepted
06 Sept 2006