Determination of different Physico-chemical Parameters of ground and surface water of Rajshahi and Dinajpur District of Bangladesh

 

Hoore Jannat1, Md. Nasiruddin2, Md. Saidul Islam1, Md. Nazrul Islam1, Md. Abdul Mannan1, Md. Kudrat-E-Zahan1

1Department of Chemistry, University of Rajshahi, Rajshahi-6205, Bangladesh.

2Department of Chemistry, Bangabandhu Sheikh Mujibur Rahman Science and Technology University, Gopalgong-8100, Bangladesh.

*Corresponding Author E-mail: kudrat.chem@ru.ac.bd

 

ABSTRACT:

The physico-chemical properties of the underground and surface water samples collected from different locations of Rajshahi and Dinajpur district of Bangladesh were determined. The study was conducted for hand tube-wells (95-125 ft. depth) and surface (mainly ponds) water. For the comparative study of the qualities and quantities of ground and surface water of a particular location, underground water samples were collected around the surface water. Physical properties were involved with measurements of pH, conductivity, total solids, dissolved solids, suspended solids and total hardness. The chemical properties were associated with the determination of anions Cl-, SO, PO and HCOand cations Na+, K+, Ca2+ and Mg2+. The concentration of trace element such as arsenic was also determined in some water samples.

 

KEYWORDS: Physiochemical parameters, ground water, surface water, total hardness, water quality.

 

 


INTRODUCTION:

Almost 71% of the earth's total surface is covered with water, only 2.5% of this amount can be considered as freshwater [1]. At present, 1.6 billion of people are facing economic water shortage, and two-thirds of the world's population is experiencing water scarcity at least one month in a year [2, 3]. Almost 1.8 billion people living in various regions all over the world may face absolute water scarcity by 2025 [4].  All living organisms on the earth need water for their survival and growth. In a developing country like us people are under tremendous threat due to undesired changes in the physical, chemical and biological characteristics of air, water and soil [5].

 

Due to increased human population, industrialization, use of fertilizers and man-made activity water is highly polluted with different harmful contaminants.

 

Groundwater is an important water-supply source world-wide. Groundwater is commonly understood to mean water occupying all the voids within a geologic stratum. This saturated zone is to be distinguished from an unsaturated or aeration zone, where voids are filled with water and air. Water contained in saturated zones is important for engineering works, geologic studies [6] and water supply developments. Unsaturated zones are usually found above saturated zones and extend upward to the ground surface. No rigid demarcation of water between the two zones is possible, they possess an independent boundary and water can move from zone to zone in either direction. Practically all groundwater originates as surface water. Principal sources of natural recharge include precipitation, stream flow, lakes and reservoirs. Other contributions occur from excess irrigation, seepage from canals, and water purposely applied to argument groundwater supplies. Even seawater can enter underground along coats where hydraulic gradient slope downward in an inland direction. Water within the ground moves downward through the unsaturated zone under the action of gravity, whereas in the saturated zone it moves in a direction determined by the surrounding hydraulic situation [7].

 

The quality of ground water depends on various chemical constituents and their concentration, which are mostly derived from the geological data of the particular region [8]. Industrial waste and the municipal solid waste have emerged as one of the leading cause of pollution of surface and ground water. It is a known fact that when pure water is polluted its normal functioning and properties are affected. It is necessary that the quality of drinking water should be checked at regular time interval, because due to use of contaminated drinking water, human population suffers from varied of water borne diseases [9-10].

 

To establish quality criteria, measuring of chemical, physical, biological and radiological constituents must be specified, as well as standard methods for reporting and comparing results of water analysis. To meet these criteria we studied the qualities and quantities of ground and surface water of Rajshahi and Dinajpur district of Bangladesh. Physical properties were involved with measurements of pH, conductivity, total solids, dissolved solids, suspended solids and total hardness. The chemical properties were associated with the determination of anions Cl-, SO, PO and HCOand cations Na+, K+, Ca2+ and Mg2+. The concentration of trace element such as arsenic was also determined in some water samples.

 

METERIALS AND METHODS:

Reagents and Chemicals:

Mettler Toledo, MP-220 pH-meter and C.G. 857 No 71798 Schott Gerate GmbH Digital conductometer were used to determine the pH and conductance of water. UV-Visible spectrophotometer Perkin Elmer Lamer Lambda-II was used to determine the SO, PO. JE. Nway PEP-7 Flame photometer was used to determine. Na+ and K+. Atomic Absorption spectrophotometer (Perkin Elmer-3110) was used to determine the Ca2+, Mg2+ and As.

 

Sampling and sample collection stations:

About 30 water samples were collected in thirty cleaned glass bottles from the various locations of the district of Rajshahi and Dinajpur. Sampling stations were at least 1 KM distances from each other. The locations of the sampling points of various places are shown in Fig.1 Ground water samples were collected from hand tube wells (95-125 ft. depth) and the surface water is also collected. Each sample was collected in a well washed dark glass bottle. The bottle was lowered slowly into the surface water and its cork opened by hand marked according in cm at the desired depth. When the bottle was filled with water, it was closed and drawn up carefully. Then 100 ml of water was discharged from the glass bottle.

 

Fig.1: Collection of drinking water samples from different locations of Rajshahi and Dinajpur District of Bangladesh.

 

RESULTS AND DISCUSSION:

pH of water:

pH value is an important parameter, as it gives the indication whether the sample is acidic or basic, pure water should be neutral with pH value of 7.0, if pH > 7 the water is basic and if pH < 7, the water is acidic. The pH values of the samples are shown in Fig. 2 and the data are given in Table 1. The pH values of ground water were in the range 6.25 to 7.33 and the values of surface water were in the range 6.68-9.09, which are higher than those of ground water. From this study, it could be said that, the pH values of tube-wells & surface water were found to be within the admissible limit (pH 6.00 to 8.00).

 

Fig.2: Comparative study of pH in ground and surface water.

 

Conductivity of water:

The conductivity indicates the concentration of salts present in water sample. These results of the water sample are shown in Fig.3 and data are given in table 1. The specific conductance has been found to be in the range 94.40 to 172.10 and 29.40 to 71.20 μg/cm for tube-wells and surface water respectively. The concentration of the salts depends on the environment, movement and sources of water. The conductivity of water sample of Dinajpur district is higher than those of Rajshahi district but the conductivity of surface water was less than that of groundwater.

 

Fig.3: Comparative study of conductivity in ground and surface water.

 

Table 1. Comparative study of the physical properties of ground and surface water

Locations

pH Mean value

Conductivity (ms/cm) Mean value

Total solids (ppm) Mean value

Ground water

Surface water

Ground water

Surface water

Ground water

Surface water

Rajshahi University Campus

6.91

7.83

103.80

40.27

473.00

342.00

Puthia Thana

7.25

8.12

122.37

45.13

297.73

441.00

Poba Thana

7.32

7.61

101.67

42.20

695.33

290.00

RajshahiCity

6.83

7.25

133.47

44.30

538.33

177.33

Dinajpur District

6.54

6.80

141.53

53.53

921.67

155.00

 


Alkalinity of water:

This observation indicates that carbonate was absent in the water sample but alkalinity was entirely due to bicarbonate. The contents of bicarbonate in water (Table 2 and 3) were estimated by neutralization titration method with standard solution using methyl orange as an indicator. Most of the water sample has been found to vary in the range 169.80 to 642.00 ppm and 7.65 to 563.13 ppm for ground water and surface water respectively. The alkalinity of water in Dinajpur district is less than that of Rajshahi district. Bicarbonate is usually the major anion present in the ground water, Carbondioxide in solution, derived from the atmosphere and from organic processes in soil, reacts with carbonate containing minerals like limestone and dolomite as the water moves underground. This process generates bicarbonate in the water.

 

Table 2. Comparative study of the physical properties of ground and surface water

Locations

Dissolved solids (ppm)

Mean value

Suspended solids (ppm)

Mean value

Total hardness (ppm)

Mean value

Ground water

Surface water

Ground water

Surface water

Ground water

Surface water

Rajshahi University Campus

431.67

308.00

41.33

34.00

243.93

138.27

Puthia Thana

268.83

353.00

28.90

88.00

305.33

261.33

Poba Thana

397.83

226.00

56.00

24.00

351.07

214.27

Rajshahi City

507.00

158.67

31.33

18.67

412.33

173.47

Dinajpur District

708.00

103.67

213.67

51.33

197.20

67.73

 

Chloride content in water:

The chloride contents estimated by Mohr titration method and the results were found to be in the range 1.35-42.22 ppm and 0.00 to 4.22 ppm (Fig. 4) for ground and surface water respectively. Usually the range of chloride in Dinajpur district is higher than that of Rajshahi district. No definite trend of the content of the anion either with the depth of the tube- wells or with its location was observed. Chloride content in excess of 100 ppm imparts a salty taste and concentration greatly in excess of 100 ppm may cause physiological damage. Some industries like textile processing, paper manufacturing and synthetic rubber manufacturing desire a content of chloride anion in water less than 100 ppm. In view of the above facts, the chloride contents of the ground water in this investigation were within the recommended level for drinking and other household purposes.

 

Fig.4: Comparative study of chloride ion in ground and surface water.

 

Sodium and potassium contents of water:

In the present investigation, sodium contents in the water have been found to be in the ranges 11.50 to 57.50 and 1.95 to 7.80 ppm for ground and surface water respectively (Fig.5). The potassium contents were measured in the range 0.69 to 52.90 and 3.51 to 27.69 ppm for ground and surface water respectively (Fig.6). No relation whatsoever could be obtained between the contents of the elements and the depth or location of the tube-wells. The concentration of the elements found in the water are all standard and very much within the recommended range for drinking and household purposes. The range of sodium in Dinajpur district is higher than the Rajshahi district.

 

Fig.5: Comparative study of sodium ion in ground and surface water.

 

Fig.6: Comparative study of potassium ion in ground and surface water.

 

Sulfate content in water:

In the present investigation sulfate ion concentration in all the ground water sample and surface water samples were found in the range of 0.32 to 41.85 ppm and 0.64 to 13.41 ppm respectively (Table 3). These values are much lower (Table 3) than the recommended values [11] (<250 ppm) comparatively the concentration of sulfate ion in Dinajpur district is higher than that of Rajshahi district.


 

Table 3. Comparative study of the chemical properties of ground and surface water

Locations

Alkalinity (ppm)

Mean value

Cl-ion (ppm)

Mean value

SO42- ion (ppm)

Mean value

PO43-ion (ppm)

Mean value

G. water

S. water

G. water

S. water

G. water

S. water

G. water

S. water

Rajshahi University Campus

428.02

180.54

8.68

8.24

0.31

5.25

0.02

0.04

Puthia Thana

399.27

327.58

21.05

12.00

2.86

0.59

0.36

0.26

Poba Thana

613.22

162.76

7.54

5.69

3.18

5.20

0.13

1.24

RajshahiCity

571.88

182.13

14.52

10.75

0.67

13.28

0.04

4.87

Dinajpur District

526.44

20.40

18.24

1.60

40.01

2.63

0.08

0.08

 

Phosphate content in water:

The phosphate level of all the ground water and surface water samples in Rajshahi and Dinajpur districts were much lower than the recommended value (6.0 ppm). In the present investigation the concentration of phosphate ions of ground water and surface water samples were found 0.0 to 0.13 and 0.04 to 4.91 ppm respectively (Table 3). The higher concentration of phosphate in water arises may be due to the uses of phosphate fertilizers, soil erosion and decomposition products of organic wastes etc.

 

Calcium and magnesium ions contents in water:

In the present investigation, calcium ion concentration of all the ground and surface water was found 18 to 52.00 and 1.40 to 32.0 ppm respectively less than the recommended limit (<75 ppm). The hardness of water in chosen area may responsible for the higher concentration of calcium (Table 4). The concentration of magnesium ion was found to be in the range 8.52 to 27.0 and 0.48 to 4.56 ppm for ground and surface water respectively which is less than the recommended level (<30 ppm) of drinking water. It has been observed that the concentration of calcium was higher than that of magnesium which is characteristic feature of the ground water [12].

 


Table 4. Comparative study of the chemical properties of ground and surface water

Locations

Na+ ion (ppm)

Mean value

K+ ion (ppm)

Mean value

Ca2+ ion (ppm)

Mean value

Mg2+ion (ppm)

Mean value

G. water

S. water

G. water

S. water

G. water

S. water

G. water

S. water

Rajshahi University Campus

17.62

25.11

2.40

3.37

32.15

7.33

12.62

4.48

Puthia Thana

11.90

23.76

1.97

27.40

50.47

13.70

16.10

3.55

Poba Thana

37.70

23.22

3.21

23.07

43.03

16.00

14.02

3.47

RajshahiCity

22.97

52.87

7.77

27.22

34.07

31.98

15.69

10.18

Dinajpur District

57.27

0.61

6.97

8.20

17.83

1.33

9.95

0.42

G. water = ground water, S. water  = surface water.

 


Arsenic in water:

Arsenic becomes highly toxic beyond a certain level. It is an element that raises much concern from the both environmental and human health standpoints. Human may encounter arsenic in water from wells drilled into arsenic-rich ground strata or in water contaminated by industrial or agrochemical waste [13].

 

There is some evidence that this element is carcinogenic. The ‘recommended’ and ‘tolerance’ limits of the elements in drinking water are 0.01 and 0.05 ppm respectively [14].In the present investigation, it may be concluded that the arsenic level in surface water should be almost nil. We attempted to measure the arsenic contents of some surface water samples but the continents have been found below detection limits.

 

Total solids of water:

The total solids in hand tube-wells and surface water samples were determined. The calculated values are given in Table 1. It has been seen that the values of total solids for tube wells and surface water were in the range 259.20-1460.00 and 115.00-593.00 ppm respectively. The total solids vary from place to place of Dinajpur district than Rajshahi district.

 

Dissolved solids in water:

Dissolved solids contained in the tube-well and surface water samples were measured. The comparison (Table 2) of dissolved solid in tube well and surface water samples indicates that the tube wells water contained higher amount of dissolved solids than surface water. The concentration of dissolved solids in the selected areas was found as 239 to 1161 and 86 to 295 ppm for tube-well and surface water samples respectively. The admissible limit of dissolved solids in drinking water is 500 ppm. The present investigation indicates that most of the ground water in Rajshahi and Dinajpur districts contains solids within the recommended level.

 

Suspended solids of water:

The present investigation found that the suspended solids in the range 9.70 to 285.00 ppm and 12 to 198 ppm respectively (Table 2) of ground water and surface water, which were far above the recommended level of U.S. Public Health Drinking Water Standard (5.0 ppm).

 

Total hardness of water:

The hardness of water sample was calculated as CaCO3 in ppm. All the samples were found to be very hard and their values exceed the acceptable limit (Table 2). This indicates the abundance of calcium and magnesium in water probability in the form of bicarbonates (Table 3and 4). In the present investigation, the hardness of tube-wells and surface water samples were found in the range 109.40 to 476.00 and 10 to 349.60 ppm respectively. The comparison of the results showed that surface water was almost soft but other samples were very hard.

 

CONCLUSION:

The evolution of physico-chemical properties and arsenic contents in ground water as well as surface water in different locations of Rajshahi and Dinajpur district, Bangladesh, was carried out in order to have an insight about the gross water quality and the extent of arsenic toxicity in the study area. It was concluded that the alkalinity of water in Rajshahi district is higher than the Dinajpur district where the trend is reverse and found much lower than recommended level in case of chloride and sulphate contents. It has also been found that the range of sodium is higher in Dinajpur region than Rajshahi area and the contents of calcium, potassium, magnesium and sodium is within the permissible limit permitted by WHO. An interesting result was found in conductivity that the conductivity of water sample of Dinajpur district is higher than those of Rajshahi district but the conductivity of surface water was less than that of groundwater. Dissolved solids contents are within the recommended level where suspended solids results were unsatisfactory for drinking and household purposes and far more than the U.S Public Health Drinking Water Standard. However, more extensive studies will be required in these particular regions for building practical guidance for the local people as well as flora and fauna.

 

REFERENCES:

1.      I. Shiklomanov. Water in Crisis: A Guide to the World's Fresh Water Resources. Oxford University Press; New York: 1993.

2.      FAO. UN Water; 2007. Coping with Water Scarcity: Challenge of the Twenty-First century. 

3.      M.M. Mekonnen, A. Y. Hoekstra. Four billion people facing severe water scarcity. Sci. Adv. 2016; 2(2):1-6.

4.      WWAP. UNESCO; Paris: 2012. The United Nations World Water Development Report 4: Managing Water under Uncertainty and Risk. 

5.      P.N Patil, DV Sawant, RN Deshmukh. Physicochemical parameters for testing of water-A review. International Journal of Environmental Sciences. 2012; 3(3): 1194

6.      Moore, J. N., W. H. Ficklin, and C. Johns. 1988. Environ. Sci. Technol. 1988; 22: 432-437.

7.      T. Belk, S. Schock, J. Smith, and J. Trax. Handbook Groundwater and Wellhead Protection, 1994. EPA/625/R-94/001

8.      N Chandrasekar, NS Magesh, S Kaliraj. Groundwater quality and its suitability for drinking and irrigation use in the Southern Tiruchirappalli district, Tamil Nadu, India. Appl Water Sci. 2017; 7:411-420.

9.      N Rahman, D Sathiyanarayanan. Quality assessment of ground water in Pallavapuram municipal solid waste dumpsite area nearer to Pallavaram in Chennai, Tamilnadu. Journal of Chemistry 2011; 4(2): 481-487.

10.   N Abhineet, ERD Dohare. Physico-chemical parameters for testing of present water quality of Khan River at Indore, India. International Research Journal of Environment Sciences. 2014; 3(4): 78-81,

11.   M Claes, MB Povse, J Drinovec, B Holvnska, P Kump, B. Ostachowicz, M Necemer, M Olko, R Van Grieken, D Wegrzynek. Inventory of regulations and analysis techniques for trace elements in some water supply companies in Eastern and Western Europe. The Science of the Total Environment. 1997; 207 (2-3): 141-148.

12.   A Ismail, RD Robents. Arsenic in small, mammals. Environmental. Technology. 1992; 13(11): 1091-1095.

13.   JP Hughes, L Polissar and G Van Belle. Evaluation and synthesis of health effects studies of communities surrounding arsenic producing industries. International Journal of Epidemiol 1988; 17: 407-413.

14.   L Marcus-Wyner and DW Rains. Uptake, accumulation, and Translocation of Arsenical Compounds by Cotton. Journal of Environmental Quality. 1982; 11 (4): 715-719.

 

 

Received on 22.02.2020                    Modified on 25.03.2020

Accepted on 28.04.2020                   ©AJRC All right reserved

Asian J. Research Chem. 2020; 13(3):163-168.

DOI: 10.5958/0974-4150.2020.00032.2