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ObjectiveTo investigate the effect of drinking brick tea with low-fluoride level on prevention of tea type fluorosis.MethodsHandahangacha,Hadayinggegacha,Dalainuoyi town,in Keshiketengqi Inner Mongolia endemic fluorosis area were selected as test points,and brick tea with fluoride [(204.5 ± 10.2),(308.2 ±15.4)mg/kg] was given for 12 months.Dental fluorosis,clinical skeletal fluorosis,and X-ray diagnosis of skeletalfluorosis [according to “Endemic Skeletal Fluorosis Diagnostic Criteria” (WS 192-2008)] of adults 20 to 70 years of age were examined and level of fluoride before and after the prevention trial,in brick tea,drinking water,milk tea and urine were tested (fluoride ion selective electrode method),and fluoride intake through tea was calculated.ResultsDetection rate of adult dental fluorosis in Handahangacha was 68.89% (62/90),clinical detection of skeletal fluorosis was 55.32% (52/94),and X-ray detection of skeletal fluorosis was 65.17% (58/89); adult dental fluorosis detection rate in Hadayinggegacha was 54.84%(51/93),clinical detection of skeletal fluorosis was 65.69%(67/102),and X-ray detection rate of skeletal fluorosis was 61.36% (54/88).Brick tea fluoride was (831.4 ±138.9),(864.3 ± 134.6)mg/kg before the prevention trial in Handahangacha and Hadayinggegacha,respectively,drinking water fluoride content was (0.27 ± 0.05),(0.54 ± 0.24)mg/L,fluoride content of milk tea was (216 ± 1.12),(2.82 ± 1.38)mg/L,adult urine fluoride content was (2.78 ± 1.57),(2.96 ± 1.80)mg/L,and fluoride intake through milk tea was (8.12 ± 5.84),(6.42 ± 5.04)mg/d,respectively; after the prevention trial the fluoride content of brick tea was (204.5 ± 10.2),(308.2 ± 15.4)mg/kg,fluoride content of drinking water (0.34 ± 0.11),(0.62 ± 0.30)mg/L,fluoride content of milk tea(0.97 ± 0.33),(1.83 ± 0.66)mg/L,fluoride content in urine(1.29 ± 0.55),( 1.47 ±0.62)mg/L,fluoride intake through milk tea (3.45 ± 2.05),(3.71 ± 2.07)mg/d,respectively; in Handahan and Hadayinggegacha after the prevention trial the fluoride in brick tea,milk tea,urine fluoride,and fluoride intake through milk tea was significantly lower than that before the trial (t =14.30,12.97 ;6.46,3.95;6.69,5.72;6.27,3.57,all P < 0.01 ).Fluoride intake in Handahangacha through milk tea was within the state heath standard limits( < 3.5mg/d).ConclusionDrinking low-fluoride brick tea can prevent drinking brick tea type fluorosis,the preventive effect is especially more reliable with low fluoride brick tea (204.5 ± 10.2)mg/kg.
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Objective To observe the absorption, excretion and retention of fluoride and aluminum after drinking brick tea in healthy adults. Methods The study was conducted in ten healthy volunteers by drinking brick tea solution in which the fluoride and aluminum concentrations were 5.97, 7.53 mg/L, respectively. The concentrations of fluoride and aluminum were determined in serum samples collected before and at 0.5,1.0,2.0,3.0,and 24.0 h, and in urine samples collected before and during the periods 1.0,2.0,4.0, > 4.0 - < 24.0 h and 24 h after drinking brick tea solution by ion-selective electrode, inductively coupled plasma atomic emission spectrometry (ICP-AES) and inductively coupled plasma atomic mess spectrometry. The total amounts of intake and excretion of fluoride and aluminum in healthy volunteers during 24.0 h were calculated from their corresponding fluoride and aluminum ingesting from brick tea and excreting from urine. Results Before and during the periods 1.0,2.0,4.0,> 4.0 - < 24.0 h and 24.0 h after drinking brick tea solution, the urinary fluoride concentrations were (0.50 ±0.14), (2.14 ± 0.90), (1.57 ± 0.93), (2.43 ± 1.49), (1.91 ± 0.69), (0.58 ± 0.20)mg/L, respectively, and the aluminum concentrations in the urine samples were (0.35 ± 0.15), (0.65 ± 0.37), (0.50 ± 0.25), (0.52 ± 0.21 ),(0.50 ± 0.23), (0,46 ± 0.27)mg/L, respectively; the 24.0 h excreting rates of fluoride and aluminum from urine were 52.90%(4.64/8.77) and 12.38% (1.37/11.07), respectively. The fluoride concentrations in serum samples collected before and at 0.5,1.0,2.0,3.0,24.0 h after drinking brick tea solution were (0.06 ± 0.02), (0.14 ± 0.01 ), (0.21 ±0.04), (0.17 ± 0.04), (0.10 ± 0.03), (0.04 ± 0.01 )mg/L, respectively, and aluminum in those were (0.30 ± 0.05),(0.27 ± 0.01 ), (0.30 ± 0.12), (0.34 ± 0.19), (0.30 ± 0.10), (0.27 ± 0.09)mg/L, respectively. Conclusions Fluoride in brick tea is easyly to be absorbed and excreted through kidney, and the kidney excretory capacity of aluminum in brick tea is limited. Levels of fluoride and aluminum in urine could be taken as the indicators for monitoring the prevalent extent and evaluating preventive experiment's effect on the brick tea fluoride-aluminum toxicity; and fasting serum fluoride and aluminum levels could be taken as indicators for estimating the toxic condition of the brick tea fluoride-aluminum toxicity.
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Objective To investigate the dynamics and development trends of drinking water type of endemic fluorosis after water improvement in Xinbaerhuyouqi of Hulunbeir city, Inner Mongolia and to provide a scientific evidence for the development of countermeasures. Methods We mainly selected Adunchulusumu and Kerlunsumu in Xinbaerhuyouqi of Hulunbeir city as the two monitoring points after water improvement in 2000 -2009. Of these, 1 sample of centralized water supply source water and 3 samples of tap water and 5 samples of noncentralized water supply source water according to water well locations of east, west, south, north and center were collected and the levels of water fluoride were tested; the prevalence of dental fluorosis of school children aged 8 to 12 were examined; from 2002 onwards, the urine samples of 30 children aged 8 to 12(five age groups, six urine samples for each age group) were collected, and all urine samples were collected in the case of less than 30, and urine fluoride was tested. Dental fluorosis was diagnosed using Dean method; water fluoride was tested using fluoride ion selective electrode(WS/T 106-1999); urinary fluoride was tested by determination of fluoride in urine using ion-selective electrode(WS/T 89-1996). Results In 2000 - 2009, the mean levels of fluorine in drinking water in Adunchulusumu and Kerlunsumu were 1.79 - 4.35 mg/L and 1.38 - 3.18 mg/L, respectively; the detection rate of dental fluorosis of children aged 8 to 12 were 45.24%(19/42) - 89.78%(123/137) and 40.00% (28/70) - 74.47% (70/94), respectively; the median urinary fluoride of them were 2.30 - 4.15 mg/L and 2.73 - 4.55 mg/L, respectively. ConclusionsThe detection rate of children's dental fluorosis remains high in Xinbaerhuyouqi during the past 10 years after changing water. The endemic fluorosis remains a serious disease. Effective prevention and control measures must be taken to control the occurrence of fluorosis in the future.