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This study intends to develop a high performance liquid chromatography-diode array detection(HPLC-DAD) method for simultaneous determination of chlorogenic acid, 2-hydroxymethyl-3-hydroxyl-1-butene-4-O-β-D-(6″-O-caffeoyl)-glucopyranoside, pubescenoside B, huazhongilexone-7-O-β-D-glucopyranoside, rutin, isochlorogenic acid B, isochlorogenic acid A, isochlorogenic acid C in Ilex hainanensis. The HPLC conditions are as follows: Waters XBridge C_(18 )column(4.6 mm×250 mm, 5 μm), mobile phase of 0.5% formic acid in water(A)-acetonitrile(B), gradient elution(0-8 min, 5%-12% B; 8-18 min, 12%-18% B; 18-30 min, 18%-25% B; 30-40 min, 25%-30% B; 40-42 min, 30%-80% B; 42-45 min, 80% B) at the flow rate of 0.8 mL·min~(-1), detection wavelengths of 282, 324, and 360 nm, column temperature of 25 ℃, and injection volume of 5 μL. The content of the 8 phenols in 8 samples was 0.30-6.29, 0.29-3.27, 0.15-10.4, 0.51-5.85, 0.49-9.02, 0.51-4.68, 1.93-13.4, and 0.87-5.95 mg·g~(-1), respectively. Moreover, the content of phenols in the samples collected in October was higher than that of samples harvested in other months. The established method is accurate and sensitive for the determination of phenols in I. hainanensis, which is useful for the quality improvement of this herbal medicine.
Subject(s)
Chromatography, High Pressure Liquid , Drugs, Chinese Herbal , Ilex , PhenolsABSTRACT
Objective To study the effects of sample digestion conditions on measurement results of urinary iodine determined by As(Ⅲ)-Ce4+ catalytic spectrophotometry with ammonium persulfate digestion,and to promote the application of newly revised (the 2012 edition) national standard method for determination of urinary iodine.Methods According to the newly revised national standard method,various digestion conditions,such as ammonium persulfate concentration (0.8-1.3 mol/L,group interval 0.1),digestion instruments (heating block and drying oven) and standing time after digestion(0.5,1.0,2.0,4.0 and 22.0 h),were studied.The samples included 3 standard materials,which were GWB09108k,GWB09109f and GWB09110m containing iodine of (68.2 ± 9.0),(138.0 ± 10.0) and (221.0 ± 10.0) μg/L,and 5 urine samples with iodine concentration of 100-300 μg/L.Results Measurement results among the three groups of 0.9,1.0 and 1.1 mol/L ammonium persulfate digestion fluid showed no significant difference(P > 0.05).The digestive effect showed no significant difference between heating block and drying oven (P > 0.05) except one standard material in low concentration (GBW09108k).After digestion,samples were placed 0.5-22.0 h,the measurement results between groups showed no significant difference (P > 0.05).Conclusions Appropriate concentrations of ammonium persulfate are from 0.9 mol/L to 1.1 mol/L.Heating block is recommended for the digestion,however,when absent,drying oven can be used alternatively.The standing times from 0.5 h to 22 h after digestion have not affected the measurement results.
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Objective To understand the situation of iodized salt consumption at the household level and non-iodized salt distribution in those areas with low iodized salt coverage.Methods In 2010,iodized salt was monitored in 31 provinces and Xinjiang Production and Construction Corps in accordance with the Monitoring Program of the National Iodine Deficiency Disorders (Trial) (hereinafter referred to as the Program) requirements.Under the jurisdiction of counties (cities,districts,banners) with more than 9 townships (towns,street offices),based on the location of east,west,south,north and center,9 townships (town,district offices) were selected using simple random sampling method; 4 administrative villages (neighborhoods) were selected in each township (town,district office); and 8 residents in each administrative village (neighborhood) were selected.Under the jurisdiction of counties (cities,districts,banners) with less than 9 townships (towns,street offices),based on the location of east,west,south,north and center,1 township(town,district office) was selected using simple random sampling method; 4 administrative villages(neighborhoods) were selected in each township(town,district office);and 15 residents in each administrative village(neighborhood) were selected.Iodized salt coverage rate,qualification rate of iodized salt and consumption rate of qualified iodized salt were calculated in various provinces.The salt samples were tested by semi-quantitative method on the spot and then tested with quantitative method in laboratories.The standard of qualified iodized salt was set as 20-50 mg/kg and that of non-iodized salt was set as < 5 mg/kg (GB/T 13025.7-1999).Results In 2010,a total of 2862 counties(districts,cities and banners) and 14 divisions of Xinjiang Production and Construction Corps,reported the monitoring results,and the monitoring coverage rate was 99.79%(2876/2882).A total of 826 696 copies of edible salt samples were tested,the coverage rate of iodized salt was 98.63%,the consumption rate of qualified iodized salt was 97.95%,and the coverage rate of qualified iodized salt was 96.63%.At province level,only in Tibet iodized salt coverage rate was < 90%.At county level,2755 counties qualified iodized salt coverage rate was ≥90%,and 33 counties iodized salt coverage rate was < 80%.The counties with qualified iodized salt coverage rate of 90% or more accounted for 96.63%(2785/2882) of the total counties.Conclusions The counties where non-iodized salt coverage is higher than 20% mainly distributed in the western or coastal areas and adjacent areas with higher iodine.These areas need policy and funding support from governments at all levels to reducc the gap between these areas and other areas.
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Objective To explore the iodine nutrition level of people, prevalence of iodine deficiency disorders and the thyroid function of women of childbearing age in pasturing areas of Tibet. Methods Thirty families were selected respectively in pastoral Dangxiong county and agricultural Qushui county of Lhasa in 2009,drinking water and edible salt samples were collected to test iodine content; at least 50 people from each crowd of the following populations including children aged 8 - 10, women of childbearing age of 18 - 49 old and male adults aged 18 - 60 were randomly sampled and to measure their urinary iodine content and for thyroid palpation. Direct titrimetric method was used to test salt iodine(GB/T 13025.7-1999); As3+-Ce4+ oxidation reduction process to test water iodine (GB/T 5750.1-2006); As3+-Ce4+ catalytic spectrophotometry using ammonium persulfate digestion to test urine iodine(WS/T 107-2006), and goiter examination was based on Diagnostic and Classificatory Criteria of Endemic Goiter (WS 276-2007). Results The median of water iodine was 1.3 μg/L in pasturing area and 0.7 μg/L in agricultural areas, there was no statistical significant difference between them(Z =- 1.809, P > 0.05).There was no iodized salt used in pastoral people, but iodized salt coverage rate was 90.0%(27/30) in agricultural residents. The median of urinary iodine among people of pasturing areas was 50.2 μg/L, lower than that of agricultural areas( 193.2 μg/L, Z =- 10.48, P < 0.01 ). However, the goiter rate in pasturing area[1.0%(1/100)]was significantly lower than that of agricultural areas[18.0%(18/100) , x2 =16.8, P < 0.01]. Serum level of FT4 and TT4 in pastoral population[(14.0 ± 2.0)pmol/L, (85.6 ± 17.5)nmol/L] was significantly lower than that of agricultural areas[(16.2 ± 6.3)pmol/L, (95.4 ± 21.1)nmoL/L, t =- 2.06, - 2.20, all P < 0.05]. The thyroid dysfunction rate[5.9% (2/34)]and subclinical hypothyroidism rate[2.9% (1/34)]in pastoral population was significantly lower than that of agricultural areas[25.5%(12/47), 21.3%(10/47), x2 =5.328, 5.651, all P < 0.05]. Conclusions Pastoral areas of iodine intake is significantly lower than the agricultural areas, urinary iodine levels reflect a serious iodine deficiency in pastoral people, but the blood biochemical and urinary iodine and goiter rate does not match,and shows hidden iodine hunger, which does not constitute a goiter epidemic.
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Objective To study the national surveillance results and learn the current situation of iodized salt consumption at household level in 2008, and to find out the remaining problems and to provide scientific basis for developing control strategies against iedine deficiency disorders. Methods In 2008, in accordance with the requirements of the "National Iodine Deficiency Disorders Surveillance Program (Trial)", the surveillance was conducted at county level in 31 provinces and at division level in Xinjiang Production and Construction Corps. In each county 9 townships were randomly selected according to their sub-area positions of east, west, south, north and center;4 villages were randomly sampled in each chosen township;8 households were randomly selected in each chosen village. In every county with 9 or less townships, 1 township was randomly selected respectively in the east, west, south,north and center sub-areas;4 villages were randomly sampled in each chosen township;15 households were randomly selected in each chosen village. Edible salt from these households was collected. Iodized salt coverage rate, proportion of qualified iodized salt and consumption rate of the qualified iodized salt of the households in each province were counted and analyzed. Iodized salt was determined by direct titration;the salt samples from Sichuan and other enhanced salt were detected by arbitration. Results Totally 2817 counties (districts, cities, banners) and 14 divisions of the Xinjiang Production and Construction Corps reported the monitoring results, monitoring coverage reached 99.96%(2831/2832). Mean of iodine content was 31.51 mg/kg.Sixteen provinces had a variation coefficient of iodine content for more than 20%. A total of 826 968 households were tested of their edible salt, in which iodized salt 798 725 copies, non-iodized salt 28 243 copies, and unqualified iodized salt 20 270 copies. Weighted by population,at national level, the coverage rate of iodized salt was 97.48%, qualified rate of iodized salt 97.16%, and consumption rate of qualified iodized salt was 94.79%.Twenty seven provinces (autonomous regions and municipalities) and Xinjiang Production and Construction Corps had a qualified iodized salt coverage rate of above or equal 90.00%. Tibet, Hainan, Xinjiang and Tianjin provinces (regions) had a qualified iodized salt coverage rate lower than 90.00%. Further, 2487 counties had the rate high or equal 90.00% accounting for 87.82% (2487/2831) of complementing monitoring counties. One hundred and four counties and 1 division of the Xinjiang Production and Construction Corps had the coverage rate of iodized salt below 80.00%. Conclusions Sixteen provinces(autonomous regions and municipalities) have relatively a high degree of variation coefficient in salt iodine content. The quality of iodized salt needs to be improved. The coverage rate of iodized salt and the qualified iodized salt at national level are both above or equal 90.00%. However, the non-iodized salt problem is still serious and have a relatively lower coverage of iodized salt in Tibet, Hainan and Xinjiang.
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Objective To explore the status of iodine nutrition and iodine deficiency disorders in the pasturing areas and agricultural regions in Tibet. Methods 30 families were selected respectively in pastoral Dangxiong county and agricultural Qushui county of Lasa. Drinking water and edible salt were collected for testing the iodine contents. In each type of the following populations including children aged 8-10, women of child-bearing age and male adults, 50 subjects were randomly sampled to examine their urinary iodine contents. Among them, 50 children and 50 women were randomly selected for goiter examination by palpation. Results Water iodine content was less than 2μg/L, both in pasturing area and in agricultural areas. There was no iodized salt used in the families of pasturing areas, while 90% people consumed iodized salt in agricultural areas. The median of urinary iodine in pasturing area was 50.2 μg/L, significantly lower than that of agricultural area (193.2μg/L). However, the goiter rate of children and women in pasturing area was significantly lower than that in agricultural area. Conclusion Although iodine intake of populations in pasturing area of Tibet was severely deficient, there was no epidemic of Iodine Deficiency Disorders. This phenomenon noticed by the researchers deserved further investigation.
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Objective To understand the current level of iodized salt coverage in areas with intensified monitoring measure in China in 2008. Methods In accordance with the "National Iodine Deficiency Disorders Surveillance Program (Trial)" of Ministry of Health issued in 2007, the selected key counties (cities, districts and banner) were divided into 5 sub-areas, 1 non-iodine townships(towns, street offices) was sampled randomly in each sub-area, 4 administrative villages (neighborhood committees) were sampled from each selected township;15households salt samples in each selected village were randomly collected. All salt samples were detected by semiquantitative kit at first. The salt samples that can not be determined by the kit were tested by direct titration and the arbitration act (GB/T 13025.7-1999) detection. Iodized salt determination criteria: reagent color change in semiquantitative test kit or iodine content ≥ 5 mg/kg were identified as iodized salt. Otherwise, the salt samples were identified as non-iodized salt. Results All the provinces(autonomous regions, municipalities) except Tibet in China had conducted a specific survey on iodized salt coverage in non-iodized salt high-risk areas, which revealed that the national coverage rate of iodized salt was 93.01%(130 928/140 770). At the provincial level, twenty provinces and the Xinjiang Production and Construction Corp had a iodized salt coverage over 90%, while the other six provinces (Beijing, Xinjiang, Zhejiang, Fujian, Tianjin and Jiangxi) between 80% - < 90% and the rest four provinces,such as Guangxi, Qinghai, Guangdong and Hainan, lower than 80%. At the county level, 64.57%(277/429) of all the surveillance counties had a iodized salt coverage over 95% while 10.02%(43/429) lower than 80%. Among all the six types of areas where specific survey were conducted, areas with incomplete iodized salt distribution network and areas with crude salt production had a iodized salt coverage lower than 90%, 81.74%(4978/6090) and 86.53%(17 098/19 759), respectively. In raw salt production area, there were 10 out of 21 provinces with iodized salt coverage rate below 90%, it consisted of 47.6%(10/21) of the total monitoring provinces in the same type areas.There were 8 out of 16 provinces with iodized salt coverage rate lower than 90% in the areas with faultiness iodized salt network, it consisted of 50.0%(8/16) of the sampling provinces in the same type area. Conclusions Most provinces(21) in China have a relatively high iodized salt coverage at household level during this specific survey.Areas with incomplete iodized salt distribution network and crude salt production are the most affected areas by noniodized salt. Aiming at the high-risk non-iodized salt areas discovered during this survey, corresponding intervention measures should be implemented with joint efforts from sectors concerned.
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Objective To explore the association between excessive iodine intake and lipid disorder in human bodies. Methods Based on the NTTST sample survey on water iodine in Suining of Jiangsu province, this study involved 81 residents whose drinking water containing excessive iodine and 101 residents who drank water with normal iodine content. Blood samples were tested and compared on lipids (TG, TC, HDL-C, LDL-C, apoAl, apoB) between the two groups, after adjusting the influences of age and gender. The study also compared the abnormal rate of each lipid indicator between the two groups. Corresponding RR values and 95% confidence interval were calculated. Correlation between iodine content in drinking water and blood lipid was also studied. Results apoA1 in the group with excessive iodine intake was significantly lower than that in the normal iodine group, while there were no significant differences between the two groups in other lipid indicators. The abnormal rate of HDL-C of excess iodine group (16.88%) was significantly higher than the rate of normal iodine group (7.22%) while there were no significant differences between the two groups in other lipid indicators. Both apoAl and HDL-C in the excess iodine group had a negative correlation with water iodine, while the other indicators of two groups had no correlation with water iodine. Conclusion Drinking water with excess iodine might increase the risk of lipid disorder.
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<p><b>OBJECTIVE</b>To compare the changes of urinary iodine levels among the family members with iodine content of 5 - 150 microg/L in drinking water, before and after non-iodized salt intervention through a field trail study.</p><p><b>METHODS</b>Family members who routinely drank water with iodine content 5 - 150 microg/L were chosen to substitute non-iodized salt for their current iodized salt for 2 months, and urine samples of the family members were collected for determination of iodine change before and after intervention was carried out.</p><p><b>RESULTS</b>Median urinary iodine of school children, women with productive age and male adults exceeding 370 microg/L before intervention and the frequency distribution of urinary iodine were all above 70%. Our results revealed that iodine excess exited in three groups of family members. After intervention, all median urinary iodine level seemed to have decreased significantly, and groups with drinking water iodine 5.0 - 99.9 microg/L reduced to adequate or close to adequate while the group that drinking water iodine was 100 - 150 microg/L reached the cut-off point of excessive iodine level (300 microg/L).</p><p><b>CONCLUSION</b>Results from your study posed the idea that the iodine adequate areas should be defined as the areas with iodine content of 5.0 - 100 microg/L in drinking water, and edible salt not be iodized in these areas. Areas with iodine content of 100 - 150 microg/L in drinking water should be classified as iodine excessive.</p>
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Adolescent , Adult , Child , Female , Humans , Male , Middle Aged , Young Adult , Iodides , Urine , Iodine , Urine , Sodium Chloride, Dietary , Urine , Water SupplyABSTRACT
<p><b>OBJECTIVE</b>To investigate the amount of daily iodine intake in the diet of the target population in drinking water with areas of excessive iodine after stopping supply of iodized salt, to provide evidence for developing strategies on control and prevention of excessive iodine.</p><p><b>METHODS</b>335 objectives were selected by a two-stage sampling method in 4 administrative villages with different iodine contents in drinking water. The amount of drinking water intake and dietary survey for 335 people were done by a door-to-door survey,while the iodine contents in the drinking water of each selected family, local staple food and vegetable were measured.</p><p><b>RESULTS</b>The median level of iodine in drinking water was 431.5 microg/L while the daily amount of iodine intake among the three groups of waters with different iodine contents were all greater than RNI. The daily iodine intake of local people was all greater than UL in the areas where the water iodine contents were more than 300 microg/L. It was of statistical sense that the iodine mean intake per capita per day of the three groups differed at different water iodine levels (P < 0.01). The iodine mean intake per capita per day of the three groups of different water iodine levels increased along with water iodine and showed a uptrend (P < 0.01). 83.2%-98.7% of the daily iodine intake of the three groups was from drinking water and 1.3%-16.8% came from food. The iodine intake had high-positive correlation relation with the content of water iodine (P < 0.01).</p><p><b>CONCLUSION</b>It was concluded that drinking water was the main source of iodine intake in areas with iodine excessive water by the percentage of over 80%. It was necessary to adopt measures to improve the quality of water to decrease the iodine content other than just stopping supplies of iodized salt in the areas where the water iodine contents were greater than 300 microg/L, in order to prevent and control excessive intake of iodine.</p>
Subject(s)
Humans , China , Diet , Iodine , Sodium Chloride, Dietary , Water SupplyABSTRACT
<p><b>OBJECTIVE</b>To evaluate the influence of different salt iodine concentration on urinary iodine excrition among the target population and to determine the appropriate level of salt iodization to the local people.</p><p><b>METHODS</b>In the 31-day random control trial, 1099 subjects from 399 families were randomly distributed into four groups and were supplied with iodized-salt with different iodine concentration of (6 +/- 2)mg/kg, (15 +/- 2)mg/kg, (24 +/- 2)mg/kg and (34 +/- 2)mg/kg, respectively. The original family salt was retrieved, whose iodine content was determined in those subjects' families with single-blind method. Baseline survey was conducted including salt and urinary iodine of the subjects. From the 27th day after the intervention, the urinary samples of the subjects were continuously collected for 5 days and urinary iodine was tesed respectively. Meanwhile, daily meal investigation was conducted to evaluate the influences originated from food.</p><p><b>RESULTS</b>The median of local water iodine content was 3.05 microg/L and the average salt iodine concentration was (36.4 +/- 5.4)mg/kg while 98.8% of the household consumed sufficient iodized-salt. The medians of baseline urinary iodine of the subjects were 293.6 microg/L in city, and 508.8 microg/L in the countryside. The urinary iodine medians of four groups in the day of 28th after intervention were 97.2 microg/L, 198.6 microg/L, 249.4 microg/L, and 330.7 microg/L respectively in the city group, while they were 100.5 microg/L, 193.0 microg/L, 246.3 microg/L and 308.3 microg/L seperately in the countryside group. There was no statistically significant differences among the medians of urine iodine in the 27th, 28th, 29th, 30th and 31st day after intervention (P > 0.05).</p><p><b>CONCLUSIONS</b>The target areas were with iodine deficiency which possessed high coverage of qualified iodized-salt at household level. The average urinary iodine level of the subjects was slightly higher than the standard level, according to the baseline survey. The intervetion trail showed that the salt iodine concentration of 15-24 mg/kg was sufficient to the local people.</p>