墨西哥低收入儿童氟牙症与瓶装水和地下水中氟化物浓度的关系。

Maria Esther Irigoyen-Camacho, Nora Perez-Perez, Marco Antonio Zepeda-Zepeda, Maria Consuelo Velazquez-Alva, Antonio Castaño-Seiquer, Ignacio Barbero-Navarro, Leonor Sanchez-Perez
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引用次数: 2

摘要

前言:本研究的目的是调查生活在墨西哥低社会经济地区的儿童氟牙症与自来水中的氟化物浓度、瓶装水中的氟化物浓度以及体重指数(BMI)之间的关系。方法:在墨西哥南部一个州地下水氟含量大于0.7 ppm的社区进行了一项涉及585名8-12岁学童的横断面研究。采用Thylstrup和Fejerskov指数(TFI)评估氟牙症,采用世界卫生组织生长标准计算年龄校正和性别校正BMI z评分。以BMI Z-score≤-1 SD作为瘦度的分界点,构建氟牙症(TFI≥4)的多元logistic回归模型。结果:自来水中氟的平均浓度为1.39 ppm (SD 0.66),瓶装水中氟的平均浓度为0.32 ppm (SD 0.23)。84例(14.39%)患儿BMI Z-score≤-1 SD。超过一半(56.1%)的儿童表现为氟牙症,TFI分类≥4。生活在自来水[比值比(OR) 1.57, p = 0.002]和瓶装水[比值比(OR) 3.03, p]中氟化物浓度较高的地区的儿童的重度氟牙症患病率较高。对瓶装水中氟化物浓度的认识可能有助于预防氟牙症,特别是接触几种高氟化物来源的儿童。体重指数低的儿童可能更容易患氟牙症。
本文章由计算机程序翻译,如有差异,请以英文原文为准。

Relationships between dental fluorosis and fluoride concentrations in bottled water and groundwater in low-income children in Mexico.

Relationships between dental fluorosis and fluoride concentrations in bottled water and groundwater in low-income children in Mexico.

Relationships between dental fluorosis and fluoride concentrations in bottled water and groundwater in low-income children in Mexico.

Relationships between dental fluorosis and fluoride concentrations in bottled water and groundwater in low-income children in Mexico.

Introduction: The aim of the current study was to investigate associations between dental fluorosis in children living in low socioeconomic areas in Mexico, and fluoride concentrations in tap water, fluoride concentrations and in bottled water, and body mass index (BMI).

Methods: A cross-sectional study involving 585 schoolchildren aged 8-12 years was conducted in communities in a southern state of Mexico with >0.7 parts per million (ppm) fluoride in the groundwater. The Thylstrup and Fejerskov index (TFI) was used to evaluate dental fluorosis, and the World Health Organization growth standards were used to calculate age-adjusted and sex-adjusted BMI Z-scores. A BMI Z-score ≤ -1 SD was used as the cut-off point for thinness, and multiple logistic regression models for dental fluorosis (TFI ≥ 4) were constructed.

Results: The mean fluoride concentration in tap water was 1.39 ppm (SD 0.66), and the mean fluoride concentration in bottled water was 0.32 ppm (SD 0.23). Eighty-four children (14.39%) had a BMI Z-score ≤ -1 SD. More than half (56.1%) of the children presented with dental fluorosis in TFI categories ≥ 4. Children living in areas with higher fluoride concentrations in the tap water [odds ratio (OR) 1.57, p = 0.002] and bottled water (OR 3.03, p < .001) were more likely to have dental fluorosis in the severe categories (TFI ≥ 4). BMI Z-score was associated with the probability of dental fluorosis (TFI ≥ 4; OR 2.11, p < 0.001), and the effect size was 29.3%.

Discussion: A low BMI Z-score was associated with a higher prevalence of dental fluorosis in the severe category. Awareness of the fluoride concentrations in bottled water may help prevent dental fluorosis, particularly in children exposed to several high fluoride content sources. Children with a low BMI may be more vulnerable to dental fluorosis.

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