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Author(s): Aditi Shivhare, Akash Upadhyay, Pallavi Sinha

Email(s): pallavi.sinha10@gmail.com

Address: Department of Zoology, Govt. Nagarjuna Post Graduate College of Science, Raipur, Chhattisgarh.
Department of Zoology, Govt. Nagarjuna Post Graduate College of Science, Raipur, Chhattisgarh.
Department of Zoology, Govt. Nagarjuna Post Graduate College of Science, Raipur, Chhattisgarh.
*Corresponding Author: pallavi.sinha10@gmail.com

Published In:   Volume - 38,      Issue - 2,     Year - 2025


Cite this article:
Shivhare, Upadhyay and Sinha (2025). Study of Physio- Chemical Parameter of Kharun River and Concentration of Heavy Metal (Iron). Journal of Ravishankar University (Part-B: Science), 38(2), pp. 66-75. DOI:https://doi.org/10.52228/JRUB.2025-38-2-6



Study of Physio- Chemical Parameter of Kharun River and Concentration of Heavy Metal (Iron)

Aditi Shivhare1, Akash Upadhyay2, Pallavi Sinha3, *

1,2,3 Department of Zoology, Govt. Nagarjuna Post Graduate College of Science, Raipur, Chhattisgarh.

 

*Corresponding Author: pallavi.sinha10@gmail.com

Abstract:

The water is most essential part of daily life the main sources of water are rain, rivers and ponds, etc. Kharun river is main river that flows in many urban and rural area of Raipur. Due to increased anthropogenic activities, such as discharge of industrial wastes and untreated sewage along with environmental effects have significantly contaminated the water in last decade. Water quality problems influence human and environmental health, therefore the more we monitor our water the better we will be able to recognize and prevent contamination issues. In present study water sample was collected in three different seasons (Summer, Rainy, Winter) from five different sites of Kharun river (Approx. 25 km stretch) to analyses for Physio- chemical parameter and Iron concentration in river. The results so obtained shows that the value of all parameter is above the permissible limits of World Health Organization (WHO), United Nations Environment Programme (UNEP), Global Environment Monitoring System (GEMS) so the contamination in river has negative health effect on the rural and the urban area. Kharun river water is polluted and not safe to use without treatment. 

Keywords: Heavy Metals, Kharun River, Physio- Chemical Parameter, Iron.

Introduction

A significant problem in developing countries is the shortage of enough drinkable water, particularly for rural residents who depend on streams, rivers, and ponds as their primary sources of drinking water. Rivers are vital freshwater systems that are fragile and necessary for the existence of all species. They serve as the main sources of water for domestic, industrial, and agricultural needs (Farah et al., 2002; Oboh and Agbala, 2017). River waters are unfortunately being contaminated by sewage discharge, industrial waste, and a range of human activities that change their physicochemical qualities (Koshy and Nayar, 1999). Human health is at risk from water pollution caused by pathogenic organisms, chemicals, heavy metals, pesticides, and disinfectants that seep from soil, rocks, and atmospheric deposition as a result of industrial and agricultural operations (Kumar and Puri, 2012). Even more dangerous metal-natural complex contaminations have been discovered to develop when heavy metal contaminations react to specific natural substances under specific conditions (Maceda-Veiga et al., 2013; Chowdhury et al., 2016; Hong et al., 2020).

Site and Sample Collection:

The Kharun River is also known as the Kharua River, Situated in Raipur District, Chhattisgarh, India. The Kharun River is geotechnically located in the Raipur area between 21° 33' 38" N latitude and 81° 55' 25" E longitude. The Kharun River is situated in an industrial and urban area that is near Raipur and Durg, two significant cities (Kumar et al., 2023). The sample was collected from five different sites of Kharun River i.e., Site1 (S1), Site2 (S2), Site3 (S3), Site4 (S4), Site5 (S5) along the stretch of 25 km in sampling bottles in three different seasons i.e., summer, rainy and winter respectively.

 

    Fig. Five different sites of sampling from Kharun River

Materials and Methods

Iron Detection and Physio- Chemical Analysis of Water Sample

Water collected from different sites, mentioned above at different seasons i.e. summer, rainy and winter in triplicate, were examined by below methods in testing laboratory (Center for Groundwater Recharge Testing Laboratory, Geetanjali Nagar, Raipur).

Physio- Chemical Analysis: -

S.No.

PARAMETERS

METHODS

1.                  

Color

Physical Analysis.

2.                  

Odor

Smell.

3.                  

Temperature

Thermometer.

4.                  

Turbidity

Turbidimeter.

5.                  

pH

pH meter

6.                  

Conductivity

Conductometer.

7.                  

Hardness

EDTA Titration (APHA, 2017).

8.                  

BOD

Hanna Analyzer.

9.                  

COD

Hanna Analyzer.

10.               

DO

Hanna Analyzer.

 

a.      Color: Water sample was examined by physical method by seeing whether its milky, muddy, clear etc.

b.     Odor:  Identified by smelling it i.e., No odor, pungent, fishy etc.

c.      Temperature: Temperature was identified by dipping thermometer in water at different site to a particular depth at different time interval and reading was noted down.

d.     Turbidity: Turbidity of water sample was measured by using following methods

o   Clean and clear sampling bottle was taken (glass or special plastic).

o   Before collecting the final sample, bottle was washed 2–3 times with river water.

o   Bottle was filled up to the mark (usually marked on the vial).

o   Shaking or disturbing sediment during water collection was avoided.

o   Now after that sample was tested in turbidimeter and reading is noted down.

e.      pH: For testing the pH of water portable pH meter was used.

o   pH meter was calibrated before using with standard buffer solutions according to the manufacturer's instructions.

o   Clean and clear sampling bottle was taken (glass or special plastic).

o   Before collecting the final sample, bottle was rinsed 2–3 times with river water.

o   Probe was dipped in water sample, ensuring the electrode is fully submerged and not touching the sides or bottom of the bottle.

o   Reading was allowed to stabilize it takes 30 seconds to 2 minutes for reading.

f.      Conductivity: Conductivity is measured by using conductometer

o   Clean, non-reactive sample collecting bottle (e.g., plastic or glass) was taken for water collection, bottle was rinsed three times with river water from the sampling site before taking the final sample.

o   Probe was washed with distilled water and then with sample water prior to immersion.

o   Conductivity probe was immersed fully in sample, making it sure that probe does not touch the sides or bottom of the bottle.

o    Waited till the reading became stabilize (usually 30 seconds to 2 minutes).

g.     Hardness: The method used for measuring this parameter is EDTA titration method (APHA, 2017)

h.     DO (Dissolved Oxygen): Was measured by hanna analyzer

o   Water sample is collected in clean dry sampling bottle.

o   DO probe was calibrated in air or saturated water indicated in hanna manual.

o   Probe was washed with distilled water and gently blot dry.

o   Probe was induced in to the water sample (avoid air bubbles).

o   Reading was allowed to stabilize.

o   DO value (mg/L) and temperature (°C) was recorded.

     i.    BOD (Biological Oxygen Demand): Was measured by hanna analyzer

o   300 ml of BOD bottle was filled with river water (avoid trapping air).

o   Immediately initial DO was measured (Day 0) using the Hanna DO probe.

o   Sample was incubated at 20°C in the dark for 5 days.

o   After 5 days, final DO (Day 5) was measured.

o   Calculate BOD₅:

                 BOD5​=DO initial​−DO final​ (mg/L)

     j.    COD (Chemical Oxygen Demand): Was measured by hanna analyzer

o   Appropriate Hanna COD vial was taken, 2 ml of water sample was taken in it and capped, inverted gently to mix.

o   Vial was placed in COD reactor at 150°C for 2 hours, after digestion, vials cooled down to room temperature.

o   Vial was inserted into the Hanna photometer or compatible multiparameter reading was noted down, the COD value (mg/L) displayed.

k.     Analysis of Heavy Metal Iron: -

o   Heavy metal Iron was analyzed in Flame Atomic Absorption Spectrophotometer.

o   In a clean beaker 50 ml of water sample was taken.

o   5ml of Conc. Nitric Acid was added in to the water.

o   Then after beaker was kept on a hot plate for digestion of the sample at 80-100°C (Until the solution has became transparent).

o   After that sample was filtered (if necessary) and kept for cooling down.

o   Then filtrate was transferred to a 100 ml of volumetric flask and diluted with distilled water up to the mark.

o   Finally, sample was processed for FAAS analysis.

Results

Summer Season: -

In summer season the color of river is some greenish due to algal blooms. Smells like fishy and unpleasant odour. The temperature rises in this season ranges from 25.9- 26.5°C minimum at (S3) and maximum at (S1) due to high temperature the water gets warm. Turbidity of the water ranges from 15.7- 18.4 NTU minimum in (S5) and maximum at (S1) due to low flow of water the turbidity of water increases in this season. The pH of water in summer season ranges from 7.8- 8.5 which is lowest in (S3) and highest in (S5) not properly treated sewage and waste changes the pH of river. Conductivity is the indicator of dissolve salts in water which is seen from range of 794.5- 1345 µS/cm noted least in (S3) and peak in (S5) stable water condition and underwater flow of wastewater. Hardness of water effect the taste of water the range is seen in between 408.7- 681.2 mg/L minimum in (S3) and maximum in (S1). Biological Oxygen Demand (BOD) values suggest the potential impact of organic pollution on the water body range is seen in between 17.4- 21.8 mg/L lowest in (S1) and highest in (S4). Chemical Oxygen Demand (COD)value indicates the organic content of water it ranges from 18.5- 21.4 and minimum in (S1) and maximum in (S3). Dissolved Oxygen (DO) in water helps in respiration of aquatic fauna and flora it ranges between 1.2- 1.8 low in (S4) and high in (S3).

Table 1. Physio- chemical parameter of Kharun River in summer season

  S.No.

Parameters

Sampling Sites

Min.

Max.

Mean

SD

S1

S2

S3

S4

S5

1.

Temperature (°C)

26.5± 1.4

26.3±1.8

25.9±1.4

26.2±2.0

26.4±2.5

25.9

26.5

26.26

0.2302

2.

Turbidity (NTU)

18.4±0.38

16.2±0.33

17.9±0.29

17.3±0.39

15.7±0.21

15.7

18.4

17.1

1.1335

3.

pH

8.1±0.18

8.3±0.12

7.8±0.10

7.9±0.14

8.5±0.18

7.8

8.5

8.12

0.2863

4.

Conductivity (µS/cm)

1284±34.1

1035±33.8

794.5±28.4

997.1±30.3

1345±35.2

794.5

1345

1091.1

224.51

5.

Hardness (mg/L)

681.2±25.7

471.4±24.7

408.7±23.6

440.1±24.9

565.2±25.3

408.7

681.2

513.32

110.61

6.

BOD (mg/L)

17.4±0.18

19.2±0.44

18.5±0.43

21.6±0.54

21.8±0.58

17.4

21.8

19.7

1.936

7.

COD (mg/L)

18.5±0.41

19.3±0.45

21.4±0.53

20.7±0.46

19.7±0.42

18.5

21.4

19.92

1.145

8.

DO (mg/L)

1.6± 0.2

1.7±

0.2

1.8±

0.1

1.2±

0.1

1.3±

0.2

1.2

1.8

1.52

0.26

 

Table 2. Physio- chemical parameter of Kharun River in rainy season

 

S.No.

Parameters

Sampling Sites

Min.

Max.

Mean

SD

S1

S2

S3

S4

S5

1.

Temperature (°C)

20.3±1.3

20.4±1.5

20.3±1.4

20.7±1.9

20.2±1.6

20.2

20.7

20.38

0.1923

2.

Turbidity

7.4±0.33

6.2±0.5

5.3±0.1

7.9±0.52

8.5±0.58

5.3

8.5

7.06

1.2973

3.

pH

7.8±0.2

7.9±1.1

8.4±0.9

7.5±1.4

7.3±0.7

7.3

8.4

7.78

0.4207

4.

Conductivity (µS/cm)

558.1±41.0

384.6±35.2

391.1±45.1

401.2±32.8

541.1±36.4

391.1

558.1

455.2

86.568

5.

Hardness (mg/L)

301.4±23.2

284.5±21.4

258.4±22.8

264.1±37.2

271.4±31.5

258.4

301.4

275.96

17.247

6.

BOD (mg/L)

16.4±1.4

18.9±2.4

16.5±2.3

17.5±2.8

18.0±1.5

16.4

18.9

17.46

1.050

7.

COD (mg/L)

17.8±2.6

18.3±2.8

17.6±3.4

19.6±3.2

19.3±4.1

17.6

19.6

18.52

6.355

8.

DO (mg/L)

1.9±

0.2

1.4±

0.3

1.6±

0.8

1.8±

0.8

1.5±

0.7

1.4

1.9

1.64

0.21

Rainy Season: -

In rainy season the color of river is some light brown muddy and murky due to mud and sediments come through erosion by heavy rainfall and mixes in water body. Smells like musty and decaying plants. The temperature in this season ranges from 20.2- 20.7°C minimum at (S5) and maximum at (S4). Turbidity of the water ranges from 5.3- 8.5 NTU minimum in (S3) and maximum at (S5) due to high flow of water the turbidity of water decreases in this season. The pH of water in rainy season ranges from 7.3- 8.4 which is lowest in (S5) and highest in (S3) many sediments from water flow comes in river stream due to which the pH of river slightly increases. Conductivity is dissolving salts in water which is seen from range of 391.1- 558.1 µS/cm noted least in (S3) and peak in (S1). Hardness of water shows mineral range and level is seen in between 258.4- 301.4 mg/L minimum in (S3) and maximum in (S1). Biological Oxygen Demand (BOD) shows organic pollution indication on the water body range is seen in between 16.4- 18.9 mg/L lowest in (S1) and highest in (S2). Chemical Oxygen Demand (COD) ranges from 17.6- 19.6 and minimum in (S3) and maximum in (S4). Dissolved Oxygen (DO) ranges between 1.4- 1.9 low in (S2) and high in (S1).

Winter Season: -

In winter season the color of river is some clearer and blueish. Smells like stagnant and milder. The temperature in this season ranges from 15.8- 16.6°C minimum at (S3) and maximum at (S5). Turbidity of the water ranges from 11.8- 15.9 NTU minimum in (S3) and maximum at (S1). The pH of water in winter season ranges from 7.6- 8.3 which is lowest in (S5) and highest in (S2). Conductivity is salts in water which range from 580.6- 690.1 µS/cm noted least in (S3) and peak in (S2). Hardness of water is seen in between 298.9- 351.4 mg/L minimum in (S3) and maximum in (S5). Biological Oxygen Demand (BOD) shows organic pollution indication on the water body range is seen in between 17.1- 20.1 mg/L lowest in (S1) and highest in (S4). Chemical Oxygen Demand (COD) ranges from 17.7- 20.3 and minimum in (S1) and maximum in (S3). Dissolved Oxygen (DO) ranges between 1.9- 2.8 low in (S4) and high in (S1).

Table 3. Physio- chemical parameter of Kharun River in winter season.

 

 

S.No.

Parameters

Sampling Sites

Min.

Max.

Mean

SD

S1

S2

S3

S4

S5

1.

Temperature (°C)

16.7±1.5

16.3±1.9

15.8±2.7

16.3±2.0

16.6±2.3

15.8

16.6

16.34

0.3507

2.

Turbidity

15.9±1.4

14.3±1.2

11.8±1.0

12.4±1.8

14.9±1.4

11.8

15.9

13.86

1.7184

3.

pH

7.7±0.81

8.3±0.52

8.1±0.44

7.8±0.68

7.6±1.32

7.6

8.3

7.9

0.2915

4.

Conductivity (µS/cm)

571.2±41.3

690.1±43.8

580.6±39.9

650.8±41.5

633.2±43.6

580.6

690.1

625.18

49.589

5.

Hardness (mg/L)

341.3±28.3

322.3±21.5

298.9±23.4

338.0±35.1

351.4±29.9

298.9

351.4

330.38

20.465

6.

BOD (mg/L)

17.1±2.37

17.9±3.12

19.4±2.61

20.1±1.96

18.8±2.89

17.1

20.1

18.66

4.063

7.

COD (mg/L)

17.7±2.55

18.1±3.24

20.3±3.11

19.8±2.85

20.0±2.49

17.7

20.3

19.18

1.190

8.

DO (mg/L)

2.8±

1.2

2.2±

1.4

2.4±

0.8

1.9±

0.9

2.5±

1.6

1.9

2.8

2.36

0.34

Heavy Metal (Iron): -

The Iron (Fe) is an important metal in water for growth of plants and animals but above the permissible limit is harmful for animals and plants both in summer iron is high i.e. Avg.  0.10528, in rainy days its Avg. concentration is 0.05516, winter season the Avg. of iron is 0.07404 which indicates that the iron is found in above permissible limit in every season.

Table 4: Concentration of heavy metal Iron (Fe) in (mg/L)

S.NO.

HEAVY METAL IRON

(mg/L)

SUMMER

RAINY

WINTER

WHO PERMISSIBLE

LIMIT

(mg/L)

S1

S2

S3

S4

S5

S1

S2

S3

S4

S5

S1

S2

S3

S4

S5

1.

Fe

0.1007±0.332

0.1020±0.312

0.1113±0.325

0.1003±0.29.3

0.1121±0.32.4

0.0698±0.125

0.0413±0.210

0.0484±0.193

0.0531±0.182

0.0632±0.215

0.0845±0.021

0.0831±0.051

0.0532±0.038

0.0783±0.058

0.0711±0.052

0.03

 

Graphical Representation of Physio- Chemical Parameter of Kharun River: -

  


Discussion

Permissible limit for water (UNEP/WHO, 1996) (WHO, 2004)

 

S.No.

PARAMETERS

WHO/UNEP/GEMS LIMIT

1.      

Turbidity (NTU)

05 NTU

2.      

pH

6.5- 8.5

3.      

Conductivity (µS/cm)

750 (µS/cm)

4.      

Hardness (mg/L)

500 (mg/L)

5.      

BOD (mg/L)

02 (mg/L)

6.      

COD (mg/L)

<10 (mg/L)

7.      

DO (mg/L)

4-6 (mg/L)

8.      

Fe (Iron)

0.03 (mg/L)

 

The physicochemical parameters of river water were monitored across three seasons— summer, monsoon, and winter—and compared to the permissible limits established by the United Nations Environment Programme and World Health Organization (UNEP/WHO, 1996; WHO, 2004; Carr and Neary, 2008) to evaluate the quality of the water and its pollution levels.The color and odor of water in summer season shows greenish coloration and algal blooms, accompanied by a fishy, unpleasant odor, suggesting increased biological activity and organic decomposition and in the rainy season showed muddy coloration due to silt and runoff, and the winter season reflected clearer waters with minimal visual contamination which differ from healthy water appearance and causes the disturbance in flora and fauna of aquatic life, following with this temperature changes in every season effect the aquatic life which is high in summer time and low at winter. The consistently elevated turbidity, particularly in summer and winter, indicates sediment resuspension due to low water flow and increased algal biomass and due to high turbidity sunlight can’t reach in the bottom of river lac of photosynthetic activities. pH levels remained within the acceptable WHO range (6.5–8.5) across seasons, though slightly alkaline Fluctuations may be attributed to sewage discharge, photosynthetic activity, and sediment influx during rainy periods. Conductivity levels reflect ionic content and were found to exceed the WHO limit (750 µS/cm) during summer (up to 1345 µS/cm) and remain elevated in winter, especially at stagnant points. Lower values in the rainy season (391.1–558.1 µS/cm) suggest dilution effects from stormwater runoff. Hardness of water, although within WHO limits (500 mg/L) in rainy and winter seasons, exceeded permissible levels in summer at S1 (681.2 mg/L), affecting taste and scaling potential. The high values may be linked to increased evaporation, concentrating dissolved minerals. BOD values far exceeded the WHO permissible limit of 2 mg/L in all seasons This consistently high BOD suggests heavy organic pollution, likely due to untreated sewage, agricultural runoff, and algal respiration, particularly in summer and winter when flow is reduced. COD levels also surpassed the UNEP/WHO standard of <10 mg/L, with readings between 17.6–21.4 mg/L across seasons. The high COD indicates a significant presence of oxidizable organic and inorganic matter, corroborating high BOD values and reflecting cumulative pollution from domestic and industrial discharges. These DO levels decreased due to high BOD levels hint at short-term oxygen demand spikes.

Iron (Fe) is an essential micronutrient for aquatic ecosystems, playing a vital role in the metabolic processes of plants and animals. It aids in chlorophyll synthesis, enzyme functions, and oxygen transport in aquatic fauna. However, in present situation concentrations exceeding the permissible limit, it can have toxicological and ecological implications.

Conclusion

Conclusion

The assessment indicates that the quality of water in the river is inadequate for various uses, including drinking. The total dissolved solids (TDS) levels, conductivity, hardness, BOD, COD, DO and pH values of the samples were found to deviate significantly from the standards established by the World Health Organization (WHO), United Nations Environment Programme (UNEP), Global Environment Monitoring System (GEMS). The elevated pollution levels resulting from industrial discharges and municipal waste contribute to environmental challenges that adversely affect both flora and fauna, as well as human health. Direct consumption of Kharun River water without any treatment poses serious health risks to the population. It is suggested to treat water before discharging it directly in river and also treated before consuming.

 Acknowledge

I express my sincere gratitude to our supervisor, Dr. Pallavi Sinha, for her invaluable guidance, insightful feedback, and unwavering support throughout this research. I acknowledge the contributions of Testing Laboratory (Center for Groundwater Recharge Testing Laboratory, Geetanjali Nagar, Raipur) for providing facilities and expertise in sample analysis. Their precision and reliability in conducting experiments, significantly enhanced the quality of results.



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