- Kathy R Phipps (), associate professora,
- Eric S Orwoll, professor of medicineb,
- Jill D Mason, associate professora,
- Jane A Cauley, associate professor of epidemiologyc
- a School of Dentistry, Oregon Health Sciences University, 611 SW Campus Drive, Portland, OR 97201, USA,
- b School of Medicine, Oregon Health Sciences University, 3181 SW Sam Jackson Park Road, Portland,
- c Department of Epidemiology, School of Public Health, University of Pittsburgh, 130 DeSoto Street, Crabtree A524, Pittsburgh, PA 15261, USA
- Correspondence to: K R Phipps
- Accepted 5 July 2000
Objective: To determine whether fluoridation influences bone mineral density and fractures in older women.
Design: Multicentre prospective study on risk factors for osteoporosis and fractures.
Setting: Four community based centres in the United States.
Participants: 9704 ambulatory women without bilateral hip replacements enrolled during 1986-8; 7129 provided information on exposure to fluoride.
Main outcome measures: Bone mineral density of the lumbar spine, proximal femur, radius, and calcaneus plus incident fractures (fractures that occurred during the study) of vertebrae, hip, wrist, and humerus.
Results: Women were classified as exposed or not exposed or having unknown exposure to fluoride for each year from 1950 to 1994. Outcomes were compared in women with continuous exposure to fluoridated water for the past 20 years (n=3218) and women with no exposure during the past 20 years (n=2563). In women with continuous exposure mean bone mineral density was 2.6% higher at the femoral neck (0.017 g/cm2, P<0.001), 2.5% higher at the lumbar spine (0.022 g/cm2, P<0.001), and 1.9% lower at the distal radius (0.007 g/cm2, P=0.002). In women with continuous exposure the multivariable adjusted risk of hip fracture was slightly reduced (risk ratio 0.69, 95% confidence interval 0.50 to 0.96, P=0.028) as was the risk of vertebral fracture (0.73, 0.55 to 0.97, P=0.033). There was a non-significant trend toward an increased risk of wrist fracture (1.32, 1.00 to 1.71, P=0.051) and no difference in risk of humerus fracture (0.85, 0.58 to 1.23, P=0.378).
Conclusions: Long term exposure to fluoridated drinking water does not increase the risk of fracture.
Editorial by Hausen
In 1945 Grand Rapids, Michigan, increased the fluoride concentration of its water supply to 1.0 ppm and became the first city to implement water fluoridation. After 15 years children in Grand Rapids had a 56% reduction in rates of dental decay.1 Since 1950 the number of individuals drinking fluoridated water has steadily increased. Today an estimated 300 million people are exposed to fluoridated water, including 5.5 million in the United Kingdom and 144 million in the United States.2
While the benefit of fluoridation in the prevention of dental caries has been overwhelmingly substantiated, the effect of fluoridation on bone mineral density and rates of fracture is inconsistent. Ecological studies that compare rates of fracture specific for age and sex between fluoridated and non-fluoridated communities have variously found that exposure to fluoridated water increases the risk of hip fracture,3-5 increases the risk of proximal humerus and distal forearm fracture,6 has no effect on fracture risk,7-10 and decreases the risk of hip fracture. 11 12 Ecological studies, however, have a major design flaw—they are based on community level data and cannot control for confounding variables at the individual level.
We determined, on an individual level, whether older women with long term exposure to fluoridated water had different bone mass and rates of fracture compared with women with no exposure. Given our widespread exposure to fluoridation, the impact of fluoride on rates of fracture is an important public health issue. In a previous study in which we found no effect of fluoridation on bone mass or risk of fracture in women we had limited power to look at individual fractures and had a relatively small proportion of women exposed to fluoride for long duration.13 In the current study we increased power to look at individual fractures by increasing the number of participants, including more women with long term exposure to fluoride, and following the population for a longer period of time.
Participants—This study was ancillary to the study of osteoporotic fractures, a multicentre study of risk factors for osteoporosis and fractures. During 1986-8 we recruited 9704 white women aged at least 65 years in Portland, Oregon; Minneapolis, Minnesota; Baltimore, Maryland; and the Monongahela Valley (an area with several small communities) in Pennsylvania. Recruitment sources included lists for jury selection and registration of voters, motor vehicle records, and membership records of health plans. Men and black women were excluded as were white women who were unable to walk without assistance and women who had a bilateral hip replacement.
Exposure to fluoridated water—Exposure to fluoridated water was assessed with a questionnaire on residence history. Women were asked to list each address (street, city, state, and postal code), years they lived at that address, and the type of water supply (public, well, spring, etc) for each of their residences from 1950 to 1994. Water system maps and the 1992 fluoridation census2 were used to link street addresses with water system and fluoridation status. If a question arose, the appropriate water district was contacted to ascertain water source and fluoride content. For each year women were coded as being exposed or not exposed or having unknown exposure. The coding of unknown was used for residences outside the United States, incomplete addresses, and private wells in areas with naturally occurring fluoride. The questionnaire was sent to the 7612 women still active in the study and 94% (7129) completed it. To assess the reliability of the residence history, duplicate histories were completed by a randomly selected group of 103 women. The κ statistic for agreement between fluoride exposure was 0.94.
Measurement of bone mass—Bone mineral density (g/cm2) of the distal radius, proximal radius, and calcaneus were measured with single photon absorptiometry (Osteo-Analyzer, Siemens-Osteon, Wahiawa, Hawaii). Bone mineral density of the lumbar spine and proximal femur were measured with dual energy x ray absorptiometry (QDR 1000, Hologic Inc, Waltham, Massachusetts).
Assessment of risk factors—Information on medical history, drugs and supplements, reproductive history, menopause, alcohol consumption, exercise, smoking, caffeine intake, and history of fractures was obtained through a questionnaire. Dietary calcium was assessed by a food frequency questionnaire administered by an interviewer.14 Women were also asked about walking, time spent sitting or lying down, and the amount of difficulty experienced with activities of daily living. Height and weight were also measured.15
Ascertainment of incident non-spinal fractures—During the study participants were contacted every four months to inquire if a fracture had occurred (incident fracture). About 99% of these contacts were completed.16 If a fracture was reported the woman was interviewed and a copy of the radiographic report obtained. To be coded as a fracture the report had to mention the occurrence of an acute fracture. Fractures due to major trauma were excluded. All fractures that occurred up until 1 December 1995 were included (average follow up of 7.0 years).
Ascertainment of prevalent and incident vertebral fractures—Lateral radiographs of the thoracic and lumbar spine were taken during the first clinical visit. A vertebral body was considered to have a prevalent fracture (fracture that had occurred before the study) if any of the following ratios were more than 3SD below the mean: the ratio of anterior to posterior height, mid-height to posterior height, and anterior height to the anterior height of the adjacent vertebrae.17 Repeat radiographs were obtained from 7238 women (average follow up of 4.0 years). The following definition of an incident vertebral fracture was used: a 20% reduction in the vertebral height of the anterior, middle, or posterior dimension of a vertebral body and at least a 4 mm decrease in the vertebral height of a dimension.
Statistical analysis—To evaluate the effect of long term fluoride exposure we statified data by fluoride exposure. Women with no exposure during 1971-90 (n=2563) were compared with women with continuous exposure (n=3218) and women with mixed exposure (n=1348). A 20 year period was selected because information on residence history for dates before 1971 was less reliable. We used χ2 tests of homogeneity and analysis of variance and covariance to compare mean bone mineral density and other covariates across the exposure groups. We used proportional hazard and logistic regression models to assess the relation between fluoride and incident fractures. Multivariable models included those factors that differed between the fluoride exposure groups plus factors previously shown to be significantly related to skeletal health in the study of osteoporotic fractures. 18 19
Characteristics of the study population—Compared with women with continuous exposure, women with no exposure were older and heavier, were more likely to have had a surgical menopause, reported a higher use of both thiazide diuretics and thyroid hormones, drank less alcohol, had lower calcium intakes, had higher muscle strength at the knee but lower grip strength, and were less likely to have more than a high school education (table 1). There was no difference in physical activity, history of falls, functional status, or smoking. Women with no or mixed exposure were more likely to have non-insulin dependent diabetes and women with mixed exposure reported a lower use of oestrogen.
Bone mineral density—Tables 2 and 3 give data on bone mineral density adjusted for age and other variables for the lumbar spine, proximal femur, radius, and calcaneus stratified by fluoride exposure. Compared with women with no exposure, women with continuous exposure had significantly higher bone mineral density of the lumbar spine, femoral neck, and trochanter, but significantly lower density of the radius. Women with mixed exposure tended to have bone density values between the other exposure groups.
Incident fractures—Twenty three per cent of the women experienced at least one non-vertebral fracture during observation. Women with continuous exposure had fewer fractures of the spine, hip, and humerus but more wrist fractures than women with no exposure (table 4). After adjustment for potential confounders, women with continuous exposure had a 31% reduction in risk of hip fracture (P=0.028) and a 27% reduction in risk of vertebral fracture (P=0.033). There was a trend towards fewer fractures of the humerus (P=0.387) and more fractures of the wrist (P=0.051), but the differences were not significant. The risk of fracture in women with mixed exposure did not differ from that in women with no exposure (table 5).
Osteoporosis is a major public health problem. In the European Community osteoporosis is responsible for more than one million fractures each year, and the number is expected to increase. Because of this it is imperative that steps be taken to understand the determinants of fracture and to decrease the population's risk of osteoporosis and subsequent fractures.
Strength of study
In the 1950s and 1960s several cross sectional studies suggested an increase in bone density in individuals living in fluoridated areas.20-22 These early studies, however, failed to control for important confounding variables. To overcome this problem, we considered known confounders. In addition, we included only those fractures confirmed by radiographic report and carefully assessed long term exposure to fluoridated water. Using a prospective design, mixed with a retrospective assessment of fluoride exposure, we found that exposure to fluoridation was associated with an increase in bone mass at the lumbar spine and proximal femur and a slight decrease in the risk of hip and vertebral fractures. We also found that women with long term exposure to fluoridated water had decreased bone mineral density of the radius. Women with mixed exposure tended to have fracture risks between those seen in women with no exposure and those with continuous exposure, especially at the hip and wrist.
Comparisons with recent research
In addition to the definitive concordance we found between bone mineral density and fractures, our findings are consistent with results of recent studies that evaluated the impact of fluoridation on bone mineral density and fractures. In a study of 3222 women Kroger et al found higher bone mineral density of the lumbar spine (2.7%) and femoral neck (1.1%) among postmenopausal women exposed to fluoridation for at least 10 years.23 Hillier et al, however, found no association between fluoridation and risk of hip fracture risk in a case-control study of men and women aged 50 years and older (odds ratio 1.0, 95% confidence interval 0.7 to 1.5).24
Adults living in non-fluoridated areas have an estimated fluoride intake of 0.88-2.20 mg/day compared with 1.58-6.60 mg for adults in a fluoridated area.25 The plasma fluoride concentrations of people in fluoridated areas are usually between 0.7-2.4 µmol/l.26 Although low, these concentrations have been shown to affect the mitogenic activity of bone cells in vitro. Farley et al report that fluoride, in concentrations as low as 1 µmol/l, increases bone cell proliferation.27 It is reasonable to expect that concentrations of fluoride at 1 ppm may have discernible skeletal effects after 20 years of exposure.
What is already known on this topic
Several ecological studies have found that rates of hip fracture are higher in communities with fluoridated drinking water compared with communities without fluoridation
These studies, however, have not controlled for several factors known to be associated with rates of fracture including use of oestrogen, smoking, and body weight
What this study adds
Long term exposure to fluoridation does not increase the risk of osteoporotic fracture among older women
In terms of any effect on bone mineral density community water fluoridation as a public health measure for the prevention of dental caries is safe
Fluoride is ubiquitous and is found in food, water, air, and dental products. It is estimated, however, that about 80% of dietary fluoride is from water and beverages. 28 29 Detailed histories of residence are the best tool currently available to estimate long term fluoride exposure. Because concentrations of environmental fluoride are low, the distinction between the exposed and the unexposed population is often blurred, making the traditional tool of epidemiology (questionnaires) less sensitive.30 A biomarker of exposure could increase sensitivity in studies on the impact of fluoride on osteoporosis. The only validated biomarker for long term fluoride exposure is fluoride concentrations in bone. While bone biopsies provide an accurate concentration of total body burden of fluoride they are unacceptable to patients. Fluoride concentrations in fasting plasma, saliva, and nails may be potential measures of exposure. The development and validation of a fluoride biomarker is an essential next step in the continued study of the relation between fluoride and skeletal health.
This is the first prospective study with adequate power to examine the risk of specific fractures associated with fluoride on an individual rather than a community basis. Our results show that long term exposure to fluoridation may reduce the risk of fractures of the hip and vertebrae in older white women. Because the burden of osteoporosis is largely due to fractures of the hip, this finding may have enormous importance for public health. If fluoridation does reduce the risk of hip fracture it may be one of the most cost effective methods for reducing the incidence of fractures related to osteoporosis. In addition, our results support the safety of fluoridation as a public health measure for the control of dental caries.
Contributors: KRP (guarantor) developed the study protocols, coordinated the study, and participated in data analysis, interpretation, and writing of the paper. ESO participated in the protocol design, interpretation of the data, and writing of the paper. JDM participated in the design and execution of the study including data collection, data documentation, quality control, and writing of the paper. JAC had the original idea for the present study and participated in data collection, interpretation of the data, and writing of the paper.
Funding United States National Institutes of Health (DE10814, AG05407, AR35582, AG05394, AR35584, AR35583). United States Environmental Protection Agency, Center for Environmental Epidemiology, University of Pittsburgh. The views expressed are those of the authors and do not necessarily reflect the views or policies of the US Environmental Protection Agency.
Competing interests None declared.