School of Medicine, University of Central Lancashire, Preston, UK.
Cochrane Oral Health, Division of Dentistry, School of Medical Sciences, Faculty of Biology, Medicine and Health, The University of Manchester, Manchester, UK.
Cochrane Database Syst Rev. 2024 Oct 4;10(10):CD010856. doi: 10.1002/14651858.CD010856.pub3.
Dental caries is a major public health problem in most industrialised countries, affecting 60% to 90% of school children. Community water fluoridation (CWF) is currently practised in about 25 countries; health authorities consider it to be a key strategy for preventing dental caries. CWF is of interest to health professionals, policymakers and the public. This is an update of a Cochrane review first published in 2015, focusing on contemporary evidence about the effects of CWF on dental caries.
To evaluate the effects of initiation or cessation of CWF programmes for the prevention of dental caries. To evaluate the association of water fluoridation (artificial or natural) with dental fluorosis.
We searched CENTRAL, MEDLINE, Embase and four other databases up to 16 August 2023. We also searched two clinical trials registers and conducted backward citation searches.
We included populations of all ages. For our first objective (effects of initiation or cessation of CWF programmes on dental caries), we included prospective controlled studies comparing populations receiving fluoridated water with those receiving non-fluoridated or naturally low-fluoridated water. To evaluate change in caries status, studies measured caries both within three years of a change in fluoridation status and at the end of study follow-up. For our second objective (association of water fluoridation with dental fluorosis), we included any study design, with concurrent control, comparing populations exposed to different water fluoride concentrations. In this update, we did not search for or include new evidence for this objective.
We used standard methodological procedures expected by Cochrane. For our first objective, we included the following outcomes as change from baseline: decayed, missing or filled teeth ('dmft' for primary and 'DMFT' for permanent teeth); decayed, missing or filled tooth surfaces ('dmfs' for primary and 'DMFS' for permanent teeth); proportion of caries-free participants for both primary and permanent dentition; adverse events. We stratified the results of the meta-analyses according to whether data were collected before or after the widespread use of fluoride toothpaste in 1975. For our second objective, we included dental fluorosis (of aesthetic concern, or any level of fluorosis), and any other adverse events reported by the included studies.
We included 157 studies. All used non-randomised designs. Given the inherent risks of bias in these designs, particularly related to management of confounding factors and blinding of outcome assessors, we downgraded the certainty of all evidence for these risks. We downgraded some evidence for imprecision, inconsistency or both. Evidence from older studies may not be applicable to contemporary societies, and we downgraded older evidence for indirectness. Water fluoridation initiation (21 studies) Based on contemporary evidence (after 1975), the initiation of CWF may lead to a slightly greater change in dmft over time (mean difference (MD) 0.24, 95% confidence interval (CI) -0.03 to 0.52; P = 0.09; 2 studies, 2908 children; low-certainty evidence). This equates to a difference in dmft of approximately one-quarter of a tooth in favour of CWF; this effect estimate includes the possibility of benefit and no benefit. Contemporary evidence (after 1975) was also available for change in DMFT (4 studies, 2856 children) and change in DMFS (1 study, 343 children); we were very uncertain of these findings. CWF may lead to a slightly greater change over time in the proportion of caries-free children with primary dentition (MD -0.04, 95% CI -0.09 to 0.01; P = 0.12; 2 studies, 2908 children), and permanent dentition (MD -0.03, 95% CI -0.07 to 0.01; P = 0.14; 2 studies, 2348 children). These low-certainty findings (a 4 percentage point difference and 3 percentage point difference for primary and permanent dentition, respectively) favoured CWF. These effect estimates include the possibility of benefit and no benefit. No contemporary data were available for adverse effects. Because of very low-certainty evidence, we were unsure of the size of effects of CWF when using older evidence (from 1975 or earlier) on all outcomes: change in dmft (5 studies, 5709 children), change in DMFT (3 studies, 5623 children), change in proportion of caries-free children with primary dentition (5 studies, 6278 children) or permanent dentition (4 studies, 6219 children), or adverse effects (2 studies, 7800 children). Only one study, conducted after 1975, reported disparities according to socioeconomic status, with no evidence that deprivation influenced the relationship between water exposure and caries status. Water fluoridation cessation (1 study) Because of very low-certainty evidence, we could not determine if the cessation of CWF affected DMFS (1 study conducted after 1975; 2994 children). Data were not available for other review outcomes for this comparison. Association of water fluoridation with dental fluorosis (135 studies) The previous version of this review found low-certainty evidence that fluoridated water may be associated with dental fluorosis. With a fluoride level of 0.7 parts per million (ppm), approximately 12% of participants had fluorosis of aesthetic concern (95% CI 8% to 17%; 40 studies, 59,630 participants), and approximately 40% had fluorosis of any level (95% CI 35% to 44%; 90 studies, 180,530 participants). Because of very low-certainty evidence, we were unsure of other adverse effects (including skeletal fluorosis, bone fractures and skeletal maturity; 5 studies, incomplete participant numbers).
AUTHORS' CONCLUSIONS: Contemporary studies indicate that initiation of CWF may lead to a slightly greater reduction in dmft and may lead to a slightly greater increase in the proportion of caries-free children, but with smaller effect sizes than pre-1975 studies. There is insufficient evidence to determine the effect of cessation of CWF on caries and whether water fluoridation results in a change in disparities in caries according to socioeconomic status. We found no eligible studies that report caries outcomes in adults. The implementation or cessation of CWF requires careful consideration of this current evidence, in the broader context of a population's oral health, diet and consumption of tap water, movement or migration, and the availability and uptake of other caries-prevention strategies. Acceptability, cost-effectiveness and feasibility of the implementation and monitoring of a CWF programme should also be taken into account.
在大多数工业化国家,龋齿是一个主要的公共卫生问题,影响到 60%至 90%的学龄儿童。目前,大约有 25 个国家在实施社区饮水氟化(CWF);卫生当局认为这是预防龋齿的关键策略。CWF 引起了卫生专业人员、政策制定者和公众的兴趣。这是对 2015 年首次发表的 Cochrane 综述的更新,重点是关于 CWF 对龋齿影响的当代证据。
评估 CWF 计划的启动或停止对预防龋齿的效果。评估水氟化(人工或天然)与氟斑牙的关联。
我们检索了 CENTRAL、MEDLINE、Embase 和其他四个数据库,截至 2023 年 8 月 16 日。我们还检索了两个临床试验登记处,并进行了回溯引文搜索。
我们纳入了所有年龄段的人群。对于我们的第一个目标(CWF 计划的启动或停止对龋齿的影响),我们纳入了比较接受氟化水和未氟化或天然低氟水人群的前瞻性对照研究。为了评估龋齿状况的变化,研究在氟化物状态变化后的三年内和研究随访结束时都测量了龋齿。对于我们的第二个目标(水氟化与氟斑牙的关系),我们纳入了任何设计的研究,包括同期对照,比较了暴露于不同水氟浓度的人群。在本次更新中,我们没有搜索或纳入这个目标的新证据。
我们使用了 Cochrane 预期的标准方法程序。对于我们的第一个目标,我们纳入了以下作为基线变化的结果:龋齿、缺失或填充的牙齿(乳牙的 dmft,恒牙的 DMFT);龋齿、缺失或填充的牙面(乳牙的 dmfs,恒牙的 DMFS);无龋齿参与者的比例,包括乳牙和恒牙;不良事件。我们根据数据是在 1975 年氟化物牙膏广泛使用之前还是之后收集的,对荟萃分析的结果进行了分层。对于我们的第二个目标,我们纳入了氟斑牙(美观问题,或任何程度的氟斑牙),以及纳入研究报告的任何其他不良事件。
我们纳入了 157 项研究。所有研究均采用非随机设计。鉴于这些设计固有的偏倚风险,特别是与混杂因素的管理和结果评估者的盲法有关,我们对所有这些证据的确定性都进行了降级。由于不精确、不一致或两者兼而有之,我们对一些证据进行了降级。较旧的研究可能不适用于当代社会,我们对间接性的较旧证据进行了降级。水氟化启动(21 项研究)基于当代证据(1975 年后),CWF 的启动可能会导致 dmft 在一段时间内略有增加(平均差异(MD)0.24,95%置信区间(CI)-0.03 至 0.52;P = 0.09;2 项研究,2908 名儿童;低确定性证据)。这相当于 CWF 中每颗牙齿的龋齿减少大约四分之一;这个效果估计包括受益和无受益的可能性。1975 年后也有关于 DMFT(4 项研究,2856 名儿童)和 DMFS(1 项研究,343 名儿童)变化的当代证据;我们对这些发现非常不确定。CWF 可能会导致乳牙(MD-0.04,95%CI-0.09 至 0.01;P=0.12;2 项研究,2908 名儿童)和恒牙(MD-0.03,95%CI-0.07 至 0.01;P=0.14;2 项研究,2348 名儿童)中无龋齿儿童的比例略有增加。这些低确定性发现(乳牙和恒牙分别为 4%和 3%的差异)有利于 CWF。这些效果估计包括受益和无受益的可能性。没有关于不良影响的当代数据。由于非常低的确定性证据,我们无法确定 CWF 对所有结果的影响大小,使用的是较旧的证据(1975 年或更早):dmft 的变化(5 项研究,5709 名儿童)、DMFT 的变化(3 项研究,5623 名儿童)、乳牙无龋齿儿童比例的变化(5 项研究,6278 名儿童)或恒牙无龋齿儿童比例的变化(4 项研究,6219 名儿童),或不良影响(2 项研究,7800 名儿童)。只有一项 1975 年后进行的研究报告了根据社会经济地位的差异,没有证据表明贫困影响了水暴露与龋齿状况之间的关系。水氟化停止(1 项研究)由于证据的确定性非常低,我们无法确定 CWF 的停止是否会影响 DMFS(1975 年后进行的一项研究;2994 名儿童)。该比较没有其他审查结果的数据。水氟化与氟斑牙的关系(135 项研究)先前的版本发现,低确定性证据表明氟化物水可能与氟斑牙有关。氟化物水平为 0.7 毫克/升时,约有 12%的参与者出现美观问题的氟斑牙(95%CI 8%至 17%;40 项研究,59630 名参与者),约有 40%的参与者出现任何程度的氟斑牙(95%CI 35%至 44%;90 项研究,180530 名参与者)。由于证据的确定性非常低,我们不确定其他不良影响(包括骨骼氟中毒、骨折和骨骼成熟;5 项研究,不完整的参与者人数)。
当代研究表明,CWF 的启动可能会导致 dmft 略有减少,并且可能会导致无龋齿儿童的比例略有增加,但效果比 1975 年前的研究小。目前没有足够的证据来确定 CWF 的停止是否会影响龋齿,以及水氟化是否会导致龋齿根据社会经济地位的差异而改变。我们没有发现报告成年人龋齿结果的合格研究。CWF 的实施或停止需要仔细考虑这一当前证据,同时还要考虑到人群的口腔健康、饮食和对自来水的消耗、流动或迁移,以及预防龋齿策略的可用性和采用情况。实施和监测 CWF 计划的可接受性、成本效益和可行性也应予以考虑。