Research Studies
Study Tracker
Focus on cognitive impairment induced by excessive fluoride: an update review.Abstract
Highlights
- 1.Excessive fluoride leads to cognitive impairment of the nervous system.
- 2.Excessive fluoride affects cognitive function differently across age groups.
- 3.Excessive fluoride reduces cognitive performance in several model organisms.
- 4.Excess fluoride impairs cognition by affecting the structure and function of brain.
Fluorosis is a global public health concern. Prolonged exposure to excessive fluoride causes fluoride accumulation in the hippocampus, resulting in cognitive dysfunction. Cell death is necessary for maintaining tissue function and morphology, and changes in the external morphology of nerve cells and the function of many internal organelles are typical features of cell death; however, it is also a typical feature of cognitive impairment caused by fluorosis. However, the pathogenesis of cognitive impairment caused by different degrees of fluoride exposure varies. Herein, we provide an overview of cognitive impairment caused by excessive fluoride exposure in different age groups, and the underlying mechanisms for cognitive impairment in various model organisms. The mechanisms underlying these impairments include oxidative stress, synaptic and neurotransmission dysfunction, disruption of mitochondrial and energy metabolism, and calcium channel dysregulation. This study aims to provide potential insights that serve as a reference for subsequent research on the cognitive function caused by excessive fluoride.
Graphical abstract
Excerpts:
Introduction
Fluoride is widely distributed in nature and ingested into the body through drinking water, air, food, and other media. The World Health Organization recommends a maximum fluoride concentration of 1.5 mg/L in drinking water (WHO 2004). The majority of fluoride ingested is absorbed by stomach and intestines, subsequently entering the bloodstream and being distributed to diverse regions of body. Approximately half of this is excreted via the kidneys, while only a small fraction(about 10%) is excreted in the form of feces, hair or perspiration(Johnston & Strobel 2020). In acidic conditions (pH<6), the permeability coefficient of hydrofluoric acid (HF) is approximately 106 times greater than that of fluoride ions (F–). Consequently, it predominantly crosses the biological membrane as molecular in the stomach(Gutknecht & Walter 1981). And fluoride absorption from the intestinethe is relatively unaffected by pH and may be facilitated by a carrier-mediated mechanism(Whitford 1994). Measure the fluoride concentrations in the urine of pregnant women, maternal serum and umbilical cord blood in two groups characterized by different fluoride concentrations in drinking water. The fluoride concentrations in the urine, maternal serum and umbilical cord blood of the high-fluoride group (2.65 mg/L) are approximately 10 times those of the low-fluoride group (0.5 mg/L)(Manjunathappa et al., 2023). Following a 60-day regimen of consuming water containing sodium fluoride, a marked increase in the plasma concentration of sodium fluoride was observed in both the high-dose group (50 mg/L) and the low-dose group (10 mg/L), when compared to the deionized water group(Miranda et al., 2018). Observe the content of sodium fluoride in different tissues after giving SD rats 300 mg/L sodium fluoride by gavage. The peak of it in the blood appeared 15 minutes later, with a concentration 24 times that of the control group, and returned to the normal level after 4 hours. The sodium fluoride within the tissues and organs commenced an upward trend 15 minutes later. The peak concentration of it manifested in the heart, liver, lung and intestine one hour after intragastric administration, in muscle tissues two hours later, in the stomach and kidneys eight hours later, and in bones fourteen hours later. After 24 hours, the fluoride contents in the liver, kidneys, intestine, stomach and bones were still significantly higher than those in the control group(Panpan et al., 2018). Human and animal in vivo studies show fluoride is disseminated throughout the body via the bloodstream, and exerts an influence on diverse tissues and organs. An appropriate amount of fluoride strengthens teeth and prevents dental caries; however, chronic exposure to a high fluoride environment leads to excessive fluoride intake, resulting in fluorosis. Approximately 500 million people worldwide are exposed to high fluoride, with 200 million affected by fluorosis (Yadav et al., 2019). Fluorosis is a systemic chronic cumulative poisoning that not damages bone structures, such as dental fluorosis and skeletal fluorosis, but also affects other non-bone tissues. Fluoride interferes with brain function in direct or indirect ways (National Research Council, 2006). Furthermore, fluoride concentrations exceeding 0.7 mg/L adversely affect learning and memory in animals (National Toxicology Program, 2016). However, the characteristics and mechanisms of fluoride effects on the nervous system remain unclear. Therefore, this review focuses on the cognitive impairment and pathological changes in the nervous system due to fluoride overexposure, and the potential mechanisms through which excessive fluoride affects the nervous system.
Based on the route of intake, endemic fluorosis can be classified into the following three types: drinking water type endemic fluorosis, coal-burning type endemic fluorosis, and drinking brick-tea type endemic fluorosis. Excessive fluoride intake adversely affects the physical and mental health of local residents, regardless of the route of intake or distribution of fluorosis. Excessive exposure to fluoride during the pre-natal period can cause developmental delays in infants and young children. Post-natal effects include attention deficits and reduced IQ in children, with reported memory loss in older adults. Excessive fluoride exposure is also a risk factor for Alzheimer’s disease (Court et al., 2001, Varner et al., 1998). Notably, neurological impairments associated with excessive fluoride exposure vary with age.
A meta-analysis of the association between excess fluoride exposure and IQ in children over the past 20 years reported that children living in fluoridated areas were five times more likely to have a low IQ than those living in non-fluoridated or mildly fluoridated areas (Tang et al., 2008). A 2018 study on the relationship between water fluoride and IQ in children showed that excessive water fluoride exposure was associated with lower IQ levels in subgroups stratified by country, age, sex, fluoride dose, and cognitive status (Duan et al., 2018). Children in high-fluoride areas have a lower IQ, indicating a dose-response relationship between the fluoride dose and IQ levels (Veneri et al., 2023, Yu et al., 2018). An analysis of the intelligence of children aged 8–12 years in coal-burning type of endemic fluorosis areas specific to China demonstrated that the intelligence level of children in the coal-burning type of endemic fluorosis areas differed significantly from that in non-patient areas. In addition, urinary fluoride concentrations were negatively correlated with intelligence level(Lou et al., 2021). A significant association between early-life fluoride exposure and cognitive deficits has been reported (Ando et al., 2001, Choi et al., 2012). The mental development index (MDI) and psychomotor development index (PDI) were significantly lower in 1-, 3-, 6-, and 12-month-old infants born to pregnant women in areas with coal-burning type of endemic fluorosis than in newborns born to pregnant women in unaffected areas (Wei et al., 2022). An ecological study in the United States showed that the prevalence of parent-reported attention-deficit hyperactivity disorder was positively correlated with the prevalence of state community water fluoridation (Malin & Till 2015). However, the Canadian Health Measures Survey data for children aged 3–12 years shows that the negligible but statistically significant association was no longer observed when using creatinine- and specific gravity-adjusted urinary fluoride as dilution corrections for urinary fluoride levels (Barberio et al. 2017). Furthermore, higher maternal urinary fluoride adjusted for creatinine (MUFcr) levels in pregnant women are associated with a lower risk of cognitive problems (lack of concentration) at 11 years of age, which is inconsistent with previous findings(Ibarluzea et al., 2023). This may be related to the quality of family background or sensitivity to other toxic levels during pregnancy; other population-based studies are needed to confirm or contradict these results (Ibarluzea et al., 2023). The discrepant results could be attributed to variations in race, dietary patterns, and educational levels. From the perspective of etiology, all the aforementioned cross-sectional studies demonstrate a correlation between fluoride and children’s intelligence; however, prospective studies are needed to further analyze the causal correlation(Gopu et al., 2022).
Because most research on the detrimental effects of fluoride exposure is initiated after birth, exposure during pregnancy is often overlooked, thereby missing the critical windows of fluoride neurotoxicity (Farmus et al., 2021). The ability of fluoride to pass through the placenta and blood-brain barrier to reach the fetal brain causes accumulation, thereby leading to adverse effects in the fetus (Dec et al., 2019, ?ukomska et al., 2020). In a prospective birth cohort in Spain, a positive correlation between MUFcr in the third trimester and measures of cognitive function, such as verbal, memory, and GCI scores, was observed among boys, whereas non-significant effects were observed in girls (p for interaction < 0.05) (Ibarluzea et al., 2022). Goodman et al. collected maternal urine samples in early pregnancy and adjusted for urinary creatinine to obtain maternal urinary fluoride exposure, excluding changes in urinary dilution, focusing not only on general cognitive indices (GCI) and Full-Scale IQ (FSIQ) but also on the McCarthy Scales of Children’s Abilities to examine differences in fluoride on the verbal scale (VIQ) and the perceptual-performance scale (PIQ) (Goodman et al., 2022). The results showed statistically significant negative associations between MUFcr concentrations and longitudinal GCI/FSI scores, mainly for nonverbal ability (Cantoral et al., 2021). No sex-specific effects were found in the Environmental Toxicants (ELEMENT) cohort of Mexico(Green et al., 2020). Two high-quality prospective birth cohort studies identified by the NTP are consistent with these results (Grandjean et al., 2022). At the 12-year visit, the researchers found that urinary fluoride concentrations in children were significantly associated with increased internalizing symptoms, particularly somatization. The association between fluoride concentration and internalizing symptoms was stronger in men when the exposure levels were similar (Adkins et al., 2022). Excessive exposure to fluoride via different routes adversely affects children at different growth stages.
Future research should focus on whether fluoride exposure is sex-sensitive and whether the effects of fluoride exposure have a dose-response relationship, particularly whether low levels of fluoride exposure are beneficial (Kumar et al., 2023). To help formulate a more reasonable public policy to achieve a balance between accruing dental benefits while minimizing the risk of detrimental effects, future research should focus more on school-age children, not only on composite scores but also on domain-specific intellectual abilities (CADTH, 2020, Grandjean, 2019). Furthermore, owing to the presence of several harmful substances in the environment and humans are co-exposed to multiple environmental contaminants, monitoring co-exposure to other pollutants (e.g., arsenic, mercury, lead, and aluminum) in addition to fluoride exposure is essential (Kinawy, 2019, Russ et al., 2019). Prospective studies can provide stronger evidence than ecological investigations. However, when conducting birth cohort studies, parental intelligence, education, diet, and medication intake during pregnancy may be innate factors affecting the intelligence of the offspring. In addition, acquired factors such as an unhealthy lifestyle, lack of essential nutrients (e.g., protein and iodine), and adverse drug reactions may have a negative impact on children’s neurological development (Wang et al., 2020). Considering the differences in renal function between individual researchers, adjusted indices should be used to reflect urinary fluoride levels and other biomarkers that can reflect long-term fluoride status, such as fingernails and deciduous milk teeth, in addition to collecting 24-h urine samples from the mother and child, especially for measuring the child’s fluoride exposure. Adjusting for covariates and collecting individual information can help researchers mitigate confounding variables (Guth et al., 2020, Sabour and Ghorbani, 2013). Sufficient and reliable evidence is needed to confirm whether excessive fluoride is a cognitive neurodevelopmental hazard in humans.
A study on the effects of fluoride exposure on cognitive function in older adults aged ? 60 years. This study conducted in Xuzhou City, Jiangsu Province, China, with different water fluoride concentrations (Ren et al., 2021) included 444 individuals who met the inclusion criteria. Cognitive assessment was analyzed using the Montreal Cognitive Assessment Basic (MoCA-B) and the Self-Assessment of Memory Impairment Scale (AD-8). The results showed that fluoride concentration was a risk factor for cognitive impairment in older adults, and the risk of cognitive impairment was higher among older adults in areas with high-fluoride drinking water. A simple mental status examination (MMSE) conducted in 511 older adults in Heilongjiang, Qinghai, Inner Mongolia, and Xinjiang Uyghur Autonomous Regions of China, reported that excessive fluoride exposure was a potential risk factor for cognitive impairment. In addition, intake of certain doses of low fluoride may have a potential protective effect on cognitive function (Li et al., 2016).
The current status survey of the population does not allow clarification of individual exposure levels. Factors such as breastfeeding, socioeconomic status, parental intelligence level, and other neurotoxic chemicals, were not given adequate focus. Only common confounders were excluded from the analysis to influence the results, which concluded that fluoride exposure was associated with neurological damage (Ren et al., 2022). Although the above findings support the idea that excessive fluoride exposure may be a risk factor for nerve injury, they are mostly cross-sectional investigations and lack direct evidence of fluoride-induced neuronal damage. Ethical constraints make it difficult to draw definitive conclusions about fluoride exposure and neurological injury in population studies; therefore, it is important to validate this effect using appropriate fluorosis models.
Section snippets
Experimental Study On The Biological Model Of Cognitive Impairment Induced By Excessive Fluoride Exposure
Biological consistency is a well-known theory of etiologic inference and Hill’s criteria (Morabia 2013). Researchers have validated the biological consistency of fluorine neurotoxicity using several biological models. Fluorosis models have been successfully established using Lymnaea stagnalis, Drosophila, mice, and rats to study the effects of excessive fluoride exposure on cognitive function.
For invertebrates, a 45-min exposure to a low concentration of sodium fluoride (0.7 mg/L sodium
Effects Of Excessive Fluoride Exposure On Morphology And Ultrastructure Of Brain Nerve Cells
The nervous system is primarily composed of nerve cells and glial cells. While the capacity of neurons in the central nervous system (CNS) to regenerate is limited, neuronal damage is often irreversible. Various organelles function according to their specific structures to maintain normal body function. Experiments on various cells and animals have demonstrated that excess fluoride alters the external morphology of nerve cells and the function of many internal organelles.
Effects of excessive fluoride exposure on neuronal protrusions and cytosolic ultrastructure
Excessive fluoride also affects ultrastructures, such as synapses, microtubules, and organelles. Sprague-Dawley rats were administered 15, 30, and 60 mg/L sodium fluoride solution, and the fluidity of the synaptic membrane gradually decreased with increasing concentration (Zhu et al., 2011); Kunming mice treated with 25, 50, and 100 mg/L sodium fluoride in drinking water had blurred presynaptic and postsynaptic membranes and changes in the synaptic cleft, during which electron-dense filling was
Oxidative stress
Excessive fluoride exposure can lead to oxidative stress damage in the nervous system, which manifests as cognitive deficits. However, an imbalance in the oxidative/antioxidant system is both a trigger for other mechanisms and a consequence of the damage. However, the causal relationship between oxidative stress and the other mechanisms requires further investigation.
Reactive oxygen species (ROS) are a general term for various metabolic natural products in the body, including singlet oxygen…
Conclusions
Moderate exposure to fluoride has beneficial effects, such as low doses of fluoride (0.5–1 mg/day) effectively prevents dental caries. However, excessive exposure to fluoride can lead to cognitive impairment, which remains a global health concern. This study summarizes the effects of excess fluoride on the nervous system based on epidemiological studies, morphologically characterized lesions, cellular ultrastructures, and molecular mechanisms. The mechanisms by which excess fluoride damages the…
ABSTRACT ONLINE AT
https://www.sciencedirect.com/science/article/abs/pii/S0306452224003919
_______________________________________________________