Constructing public oral health policies in Brazil: issues for reflection. (73/126)

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Change of urinary fluoride and bone metabolism indicators in the endemic fluorosis areas of southern China after supplying low fluoride public water. (74/126)

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Water fluoride concentration and fracture of the proximal femur. (75/126)

STUDY OBJECTIVE: The aim of the study was to examine the relationship between water fluoride concentration and the incidence of hip fracture, since evidence on this is at present inconsistent. DESIGN: Numbers of hospital admissions for fractures of proximal femur were obtained from hospital activity analysis data for the years 1978-1982. The fracture rates were compared with water fluoride concentrations in 39 county districts of England and Wales (fluoride concentrations had been measured in these districts between 1969 and 1973 as part of the British Regional Heart Study). PATIENTS: During the study period, 4121 men and 16,272 women aged 45 years and over were discharged from hospital after hip fracture. RESULTS: Poor correlations were found between discharge rates and both total (r = 0.16, p = 0.34) and natural (r = 0.01, p = 0.95) water fluoride concentrations. CONCLUSIONS: Water fluoridation to levels of around 1 mg/litre is unlikely to reduce hip fracture incidence markedly in this country.  (+info)

Water fluoridation in 40 Brazilian cities: 7 year analysis. (76/126)

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Seven years of external control of fluoride levels in the public water supply in Bauru, Sao Paulo, Brazil. (77/126)

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Physiologic conditions affect toxicity of ingested industrial fluoride. (78/126)

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Risk factors for dental caries in small rural and regional Australian communities. (79/126)

INTRODUCTION: Dental decay (caries) can cause pain, infection and tooth loss, negatively affecting eating, speaking and general health. People living in rural and regional Australian communities have more caries, more severe caries and more untreated caries than those in the city. The unique environmental conditions and population groups in these communities may contribute to the higher caries burden. In particular, some towns lack community water fluoridation, and some have a high proportion of Aboriginal people, who have significantly worse oral health than their non-Aboriginal counterparts. Because of these and other unique circumstances, mainstream research on caries risk factors may not apply in these settings. This study aimed to gather contemporary oral health data from small rural or regional Australian communities, and investigate caries risk factors in these communities. METHODS: A cross-sectional survey consisting of a standardized dental examination and questionnaire was used to measure the oral health of 434 children (32% Aboriginal) aged 3-12 years in three small rural or regional areas. Oral health was determined as the deciduous and permanent decayed, missing and filled teeth (dmft/DMFT), and the proportion of children without caries. Risk factors were investigated by logistic regression. RESULTS: The dmft/DMFT for children in this study was 1.5 for 5-6 year olds and 1.0 for 11-12 year olds (index groups reported). Independent predictors of having caries (Yes/No) were age group, holding a concession card (OR=2.45, 95%CI=1.58-3.80) and tooth-brushing less than twice per day (OR=2.11, 95% CI=1.34-3.34). Aboriginal status also became a significant variable under sensitivity analyses (OR 1.9, CI 1.12-3.24) when the tooth-brushing variable was removed. Gender, water fluoridation and parental education were not significant predictors of caries in these communities. CONCLUSIONS: The rural/remote children in this study had worse oral health than either state or national average in both the 5-6 year old and 11-12 year age group. Socioeconomic status, tooth-brushing and Aboriginal status were significantly associated with caries in these communities. To close the substantial gap in oral health outcomes between rural and metropolitan residents, approaches that target rural areas, Aboriginal people and those from low socioeconomic backgrounds are needed.  (+info)

Evaluating the impact of municipal water fluoridation on the aquatic environment. (80/126)

Although highly beneficial for dental health, low concentrations of fluoride in environmental waters may be toxic to several organisms. In an era of heightened public awareness about the environment, this may lead city officials to withhold implementing water fluoridation for environmental reasons. This paper presents a mass balance approach to evaluate this perceived risk. Generally speaking, fluoridated water loss during use, dilution of sewage by rain and ground water infiltrate, fluoride removal during secondary sewage treatment, and diffusion dynamics at effluent outfall combine to eliminate fluoridation-related environmental effects. In Montreal, water fluoridation would raise average aquatic fluoride levels in the waste water plume immediately below effluent outfall by only 0.05-0.09 mg/l. Downstream, these changes would be only 0.02-0.05 mg/l at 1 km, and 0.01-0.03 mg/l at 2 km below outfall. Overall river fluoride concentrations theoretically would be raised by 0.001-0.002 mg/l, a value not measurable by current analytical techniques. All resulting concentrations would be well below those recommended for environmental safety and would not exceed natural levels found elsewhere in Quebec. A literature review did not reveal any examples of municipal water fluoridation causing recommended environmental concentrations to be exceeded, although excesses occurred in several cases of severe industrial water pollution.  (+info)