Literature DB >> 30338283

Fluoride concentration data in groundwater resources of Gonabad, Iran.

Abbasali Karimi1, Majid Radfard2, Morteza Abbasi3, Ali Naghizadeh4, Hamed Biglari5, Vida Alvani6, Mokhtar Mahdavi7.   

Abstract

The data was obtained from fluoride ion concentrations determined in groundwater sources of Gonabad. A number of 144 samples from 12 drinking groundwater wells located in different regions at the mid of spring, summer, autumn and winter from each regions, were collected from spring 2016 to spring of 2017. The fluoride ions in the samples were determined through the SPADNS colorimetric method at a wavelength of 580 nm. Dispersion of fluoride ions in terms of concentration in groundwater resources of Gonabad was planned using geographic information system (GIS) base on inverse distance weighted (IDW) method. The data showed that lowest and highest concentration of fluoride ions were determined 0.46 in winter and 1.56 mg/l in summer season, respectively. The average, max and min amount of fluoride concentration in groundwater resources of Gonabad were 0.67 ± 0.03, 1.56 and 0.46 mg/L, respectively. The average chemical parameters concentration of Potassium, Sodium, Magnesium, Calcium, Phosphate, Nitrate, Bicarbonate, Sulfate and Chloride were 6.61 ± 1.2, 281.17 ± 3.08, 26.75 ± 2.55, 68.14 ± 3.89, 0.2 ± 0.04, 10 ± 1.83, 275.02 ± 7.20, 282.08 ± 5.04 and 235 ± 5.83 mg/L, respectively.

Entities:  

Keywords:  Fluoride; Fluorosis; GIS; Gonabad; Groundwater; Water quality

Year:  2018        PMID: 30338283      PMCID: PMC6186961          DOI: 10.1016/j.dib.2018.09.062

Source DB:  PubMed          Journal:  Data Brief        ISSN: 2352-3409


Specifications table Value of the data Managing drinking water quality is crucial for treatment plant operators. The data can be used by drinking water quality researchers [1], [2]. Accreditation to a recognized flouride quality standard may be essential for dealing with certain customers or complying with legislation. This data can be used to illustrate the dispersion of flouride ions concentration in groundwater resources of Gonabad county [3]. This data can be used to show how much fluoride ion levels from this drinking water may affect the consumer [4]. The data can be used to show the fluoride ions concentration at risk level where it is, since it may affect the health of consumers for operators to make better decision in treatment method selection [5].

Data

The data in Table 1, Table 2 shows the descriptive statistics of fluoride ions and other chemical parameters concentration in samples. Fig. 1 shows the distribution of fluoride ions in Gonabad groundwater resources. Fig. 2 shows the average along with Standard deviation of fluoride ions concentration in groundwater resources of Gonabad. The fluoride ions concentration in critical regions illustrated with dark red color in Fig. 1 Standards set for the concentration of fluoride in drinking water by various organizations are different. The differences are associated with seasonal changes [6]. Factors affecting the standard concentration of fluoride ions in drinking water have a direct relationship with air temperature and water consumption per capita [7], [8], [9]. In other words, the amount of drinking water intake in the warm months is more than its amount in the cold months [10], [11]. According to the standard of drinking water in Iran, the optimum concentration of fluoride in drinking water is 0.7 mg/L in warm months while it is 2.1 mg/L in the cold months [12]. The average fluoride concentration of groundwater resources in Gonabad falls in the range of 0.66–0.67 mg/L. Table 1 shows the fluoride ions concentration in different groundwater regions. The maximum and minimum concentration of fluoride ions in all regions were 1.62 and 0.44 mg/L, respectively. The average of maximum was 0.7 mg/L, the minimum was 0.64 mg/L and the average fluoride concentration was 0.67 mg/L. The average concentration of fluoride in groundwater resources used for drinking water in Gonabad is higher than the standards of the World Health Organization, and the current standard of United States of America and Europe [13], [14], [15]. In comparison to the standard of drinking water in Iran, the annual average of fluoride ion deficiency is about 0.5 to 1 mg/L [16]. The data also showed that the average, max and min amount of fluoride concentration in groundwater resources of Gonabad were 0.562 ± 0.23, 0.18 and 1.08 mg/L, respectively. The average chemical parameters concentration of Potassium, Sodium, Magnesium, Calcium, Phosphate, Nitrate, Bicarbonate, Sulfate and Chloride were 6.61 ± 1.2, 281.17 ± 3.08, 26.75 ± 2.55, 68.14 ± 3.89, 0.2 ± 0.04, 10 ± 1.83, 275.02 ± 7.20, 282.08 ± 5.04 and 235 ± 5.83 mg/L, respectively.
Table 1

The chemical parameters concentration in groundwater resources of Gonabad, mg/L.

NoK+
Na+
Mg++
Ca++
PO4-3
NO3-
HCO3-
SO4-2
Cl-
AveSTDAveSTDAveSTDAveSTDAveSTDAveSTDAveSTDAveSTDAveSTD
1712303.2326.463.5678.44.60.150.02111324.1510.3423042203.7
230.51971.7819.682.648.82.90.420.0493304.656.221505.21407.45
3822702.5434.085.188.86.10.160.05121333.918.452557.13005
420.71921.3414.881.5637.62.390.120.09143246.1610.2602.9556.4
5411903.115.363.5532.81.780.160.0482233.979.13801.51009.3
6101.54025.0239.362.89104.15.50.220.03121283.454.454802.23682.7
741.574203.8724.961.336.82.370.160.0251275.435.563604.63504
892.13424.6541.284.0285.22.550.140.0482411.897.3232063005.2
950.482400.225.922.478.48.20.170.07102219.356.652708.52309.8
10513092.3318.720.3268.31.630.250.0383202.528.243805.12452.4
11121.53125.3235.361.8958.45.20.210.03111262.454.254504.22987.7
1252.12703.624.961.45100.13.40.260.05122202.295.63509.22146.3
Ave6.1671.29281.173.0826.752.5568.1423.890.20.04101.83275.027.201282.085.042355.83
Min20.481900.214.880.3232.81.630.120.0251202.294.25601.5552.4
Max122.14205.3241.285.1104.18.20.420.09143411.8910.344809.23689.8

** NO2 and CO3 in all samples were zero.

Table 2

The fluoride concentration in groundwater resources of Gonabad, mg/L.

NOSpringSummerAutumnWinterAverageSDMinMax
10.600.490.480.580.530.060.480.60
20.450.510.470.500.480.030.450.51
30.520.480.490.530.510.020.480.53
40.520.530.490.440.500.040.440.52
50.470.450.480.450.460.020.440.48
60.480.500.510.530.510.020.480.53
70.750.750.830.810.790.040.750.83
80.580.630.600.610.610.020.580.63
90.530.480.510.540.520.030.480.54
100.600.700.630.650.650.040.600.70
110.870.880.920.940.900.030.880.94
121.561.621.491.541.560.051.571.62
Min0.450.450.470.440.460.020.440.48
Average0.660.670.660.680.670.030.640.70
Max1.561.621.491.541.560.061.561.62
Fig. 1

Fluoride ions dispersion in groundwater resources of Gonabad.

Fig. 2

Average of fluoride ions concentration in groundwater resources of Gonabad.

The chemical parameters concentration in groundwater resources of Gonabad, mg/L. ** NO2 and CO3 in all samples were zero. The fluoride concentration in groundwater resources of Gonabad, mg/L. Fluoride ions dispersion in groundwater resources of Gonabad. Average of fluoride ions concentration in groundwater resources of Gonabad.

Experimental design, materials and methods

Gonabad, with an area of 5902 square kilometres, lies up the north of Birjand and 270 km off the south of Mashhad and it is near Pakistan (Fig. 2). The city has three towns with the names of Kakhk, Bajestan and Bidokht. With consideration to the geographical location of the Gonabad county, it becomes clear that this city has a hot and dry climate and with an average annual rainfall of 65 mm and temperature –14 up to 44.6 °C, the city suffers from water shortages. Water samples were prepared from different dug wells. Selected locations were quite close to water wells that are used for drinking. All of the sampling, transferring and analyzing methods have been carried out according to the water and wastewater standard methods. The water samples were prepared from 12 drinking water wells out of 18 wells that allowed for sampling and reporting due to security issues. Four samples (three repetitions) were collected at the mid of spring, summer, autumn and winter from each well, and 144 samples were totally taken overall (one year monitoring (from spring 2016 to spring of 2017)). Water samples were taken from the well water pipe in the middle of the day. The water samples were transferred to chemical laboratory of the Gonabad University of medical sciences in a cool box immediately. Sampling was conducted with one‑liter polyethylene bottles which were immersed in nitric acid for 24 h then washed with 10 percent HCL and finally washed with distilled water. It has to be mentioned that before the collection of the samples, sampling containers had been rinsed at least three times with water [16], [17]. In the laboratory the fluoride ions in the samples were measured using the SPADN method at a wavelength of 580 nm by HACH (spectrophotometer DR 5000 Company, USA). The SPADN reaction is based on the degree of red color loss resulting from zirconium SPADN reaction in proportion to the concentration of fluoride ion [18], [19]. The scatter of fluoride concentration were mapped by Geographic Information System software v 10.3 using IDW method for illustrate the critical fluoride concentration level in groundwater area [20].
Subject areaEnvironmental Sciences
More specific subject areaGroundwater chemistry
Type of dataTable and figure
How data was acquiredThe concentration of fluoride ions were determined by the SPADNS colorimetric method. The dispersion of fluoride ions was planned using GIS software v10.3 base on inverse distance weighted (IDW) method.
Data formatRaw, analyzed
Experimental factorsGroundwater samples from 12 different areas of Gonabad were collected from drinking water wells sources, private and government hand pumps in the year 2016–17. All sampling sites were selected with a view to cover the entire area of the study area.
Experimental featuresThe samples collection and fluoride ions analysis conducted according to the standards methods of water and wastewater treatment analyze handbook.
Data source locationGonabad, Iran
Data accessibilityData are included in this article
  7 in total

1.  Fluoride content of infant formulas prepared with deionized, bottled mineral and fluoridated drinking water.

Authors:  M A Buzalaf; J M Granjeiro; C A Damante; F de Ornelas
Journal:  ASDC J Dent Child       Date:  2001 Jan-Feb

2.  Total daily fluoride intake and fractional urinary fluoride excretion in 4- to 6-year-old children living in a fluoridated area: weekly variation?

Authors:  Narges Omid; Anne Maguire; William T O'Hare; Fatemeh V Zohoori
Journal:  Community Dent Oral Epidemiol       Date:  2016-09-21       Impact factor: 3.383

3.  Surface microhardness changes, enamel fluoride uptake, and fluoride availability from commercial toothpastes.

Authors:  Craig S Newby; Jonathan E Creeth; Gareth D Rees; Bruce R Schemehorn
Journal:  J Clin Dent       Date:  2006

4.  WHO water quality standards Vs Synergic effect(s) of fluoride, heavy metals and hardness in drinking water on kidney tissues.

Authors:  Hewa M S Wasana; Gamage D R K Perera; Panduka De S Gunawardena; Palika S Fernando; Jayasundera Bandara
Journal:  Sci Rep       Date:  2017-02-14       Impact factor: 4.379

5.  Fluoride concentration of drinking waters and prevalence of fluorosis in iran: a systematic review.

Authors:  Saber Azami-Aghdash; Morteza Ghojazadeh; Fatemeh Pournaghi Azar; Mohammad Naghavi-Behzad; Mostafa Mahmoudi; Zahra Jamali
Journal:  J Dent Res Dent Clin Dent Prospects       Date:  2013-02-21

6.  Data for factor analysis of hydro-geochemical characteristics of groundwater resources in Iranshahr.

Authors:  Hamed Biglari; Mehdi Saeidi; Kamaleddin Karimyan; Mohammad Reza Narooie; Hooshmand Sharafi
Journal:  Data Brief       Date:  2018-05-18

7.  Data on fluoride concentration levels in cold and warm season in City area of Sistan and Baluchistan Province, Iran.

Authors:  Akazem Neisi; Majid Mirzabeygi Radfard; Ghader Zeyduni; Asghar Hamzezadeh; Davoud Jalili; Abbas Abbasnia; Mahmood Yousefi; Rouhollah Khodadadi
Journal:  Data Brief       Date:  2018-03-16
  7 in total
  3 in total

1.  Clofibrate, a Peroxisome Proliferator-Activated Receptor-Alpha (PPARα) Agonist, and Its Molecular Mechanisms of Action against Sodium Fluoride-Induced Toxicity.

Authors:  Ademola Adetokunbo Oyagbemi; Olumuyiwa Abiola Adejumobi; Theophilus Aghogho Jarikre; Olumide Samuel Ajani; Ebunoluwa Racheal Asenuga; Idayat Titilayo Gbadamosi; Aduragbenro Deborah A Adedapo; Abimbola Obemisola Aro; Blessing Seun Ogunpolu; Fasilat Oluwakemi Hassan; Olufunke Olubunmi Falayi; Iyanuoluwa Omolola Ogunmiluyi; Temidayo Olutayo Omobowale; Oluwatosin Adetola Arojojoye; Olufunke Eunice Ola-Davies; Adebowale Benard Saba; Adeolu Alex Adedapo; Benjamin Obukowho Emikpe; Matthew Olugbenga Oyeyemi; Sanah Malomile Nkadimeng; Lyndy Joy McGaw; Prudence Ngalula Kayoka-Kabongo; Oluwafemi Omoniyi Oguntibeju; Momoh Audu Yakubu
Journal:  Biol Trace Elem Res       Date:  2021-04-24       Impact factor: 3.738

2.  Factors associated with dental fluorosis in three zones of Ecuador.

Authors:  Ana Del Carmen Armas-Vega; Farith-Damián González-Martínez; Mercedes-Silvana Rivera-Martínez; María-Fernanda Mayorga-Solórzano; Valeria-Elizabeth Banderas-Benítez; Osmani-Fabricio Guevara-Cabrera
Journal:  J Clin Exp Dent       Date:  2019-01-01

3.  The correlation between the mineral drinking water composition and the relevance of dentine in health - A pilot study.

Authors:  Creteanu Razvan; Monica Popa; Ana-Maria Incze; Creteanu Cristina
Journal:  Pak J Med Sci       Date:  2020 Mar-Apr       Impact factor: 1.088

  3 in total

北京卡尤迪生物科技股份有限公司 © 2022-2023.