Assessment of Surface Water Quality of Gonda Nallah and River Kharashrota Near Kalinga Nagar Industrial Complex in Jajpur District of Odisha

DOI : 10.17577/IJERTV4IS060863

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Assessment of Surface Water Quality of Gonda Nallah and River Kharashrota Near Kalinga Nagar Industrial Complex in Jajpur District of Odisha

[1]Patitapaban Dash

Centre of Biotechnology, Siksha O Anusandhan University,

Bhubaneswar, India

Abstract – An attempt has been made to assess the surface water quality of Gonda nallah and River Kharashrota so as to determine the safety level of their uses by the local people in the vicinity of an industrial climate. The study area is present in the Sukinda block of Odisha in India. The pollutant level in the surface water of these water-bodies is estimated by following the standard methods of APHA. The analysis of results expresses significantly higher oxidizable pollutants levels at all the twelve sampling stations during Pre-monsoon, Monsoon and Post-monsoon than the limits prescribed by World Health Organization. It indicates that surface water of the studied water bodies is polluted and is unsafe for use without treatment due to the presence of excessive quantity of oxidizable pollutants. Further study is needed in this context to reduce the pollutant load of these surface water bodies.

Keywords-Chemical oxygen demand, Effluents, Industrial, Pollution, River

  1. INTRODUCTION

    The people of the modern civilization are mostly depending on river water for meeting the demands from domestic, industrial, agricultural and energy sectors. All these activities exploit the river water resources of the country. The situation is alarming with the increase in population and industrialization. The surface water pollution is at high risk in the present scenario. Ninety percent of total drinking water is severely polluted [1]. The situation is compounded by the fact that the common man in most of these countries does not have access to potable water and in many instances; raw river water is used as the source of drinking water [2]. The chemical oxygen demand level of the surface water-bodies is one of the most important parameters that provide information regarding surface water pollution.

    The River Kharashrota, a branch of River Brahmani after Chakua is passing nearer to the Kalinga Nagar Industrial Complex in the Sukinda block of Jajpur district in Odisha. This Industrial

    [2]Bidyut Prava Das

    Department of Botany,

    R.D. Womens University, Bhubaneswar, India

    Complex is promoting the steel production in the north- eastern Odisha in India. It is situated at a distance of 110 kilometres from Bhubaneswar, the capital city of Odisha. The river Kharashrota flows from west to east on the southern side of this Industrial Complex. Many people of the villages such as Jokadia, Marthapur, Nelibari, Nuagaon and others are depending on the surface water of this river Kharashrota for multiple daily activities.

    Most of the rivers are constantly fed by drains carrying industrial effluents affecting the growth and germination of crop plants [3]. The Gonda nallah receives a number of small drainage channels from this industrial complex on both of its banks. The direction of flow of Gonda nallah is from north to south and it drains directly into river Kharashrota at Jokadia. Below the confluence, river Kharashrota heads its way in southeast direction up to the Bay of Bengal.

    The effluents have high salt concentration and toxic elements [4]. Heavy metals from compounds in the body can be carcinogenic and mutagenic even at very low concentration [5]. The major source of waste water during steel making is the cooling water that contains hexavalent chromium. Hexavalent form of chromium is more hazardous to biological activities [6]. These are extremely persistent in the environment, as these are non- biodegradable and non-thermo degradable and thus, readily accumulate to toxic levels [7], [8]. The contaminants are assimilated inside the living plants and animals quickly through the food chain, affecting the health of the animals and human beings [9]. Some of the contaminants such as domestic wastes, industrial wastes, fertilizers are man-made pollutants of water [10].

    This study area is covered under the Survey of India toposheet No. 73 L / 1. This area is bounded between the latitudes 20 57 N – 21 3 N and longitudes 85 59 E – 86 5 E.

  2. MATERIALS AND METHODS

    Survey was done to locate the sampling sites. The sampling sites were selected on the basis of suspected critical pockets of pollution in the vicinity of the Kalinga Nagar Industrial Complex. The station codes and description of the water sampling stations of the study area are presented in Table 1. In the current study, the

    assessment of surface water quality of Gonda nallah and River Kharashrota near Kalinga Nagar Industrial Complex in Jajpur district of Odisha was done by determining the chemical oxygen demand (COD) contents of these surface water-bodies. Water samples were collected from six locations each of Ganda nallah and River Kharashrota. Seasonal water samples were collected during Pre- monsoon, Monsoon and Post-monsoon seasons for three consecutive years from February, 2012 to January, 2015.

    The monitoring months in relation to the representative seasons are Pre-monsoon (February May), Monsoon (June September) and Post-monsoon (October January). Seasonal water samples were collected in pre-sterilized

    2 litres capacity polythene bottles, (soaked overnight in 2 percent nitric acid and washed well in distilled water) from each location at 11A.M. and the COD of the surface water samples were estimated following standard methods for the examination of water and wastewater [11].

    TABLE.1: Table showing the station code and description of the water sampling stations of the study area

    Station code of water sampling

    sites

    Description of the sampling station

    Distance from the previous water sampling station in the upstream

    SW 01

    Gonda nallah

    First sampling station

    SW 02

    Gonda nallah

    500 metres

    SW 03

    Gonda nallah

    500 metres

    SW 04

    Gonda nallah

    500 metres

    SW 05

    Gonda nallah

    500 metres

    SW 06

    Gonda nallah

    500 metres

    SW 07

    River Kharashrota

    500 metres

    SW 08

    River Kharashrota

    500 metres

    SW 09

    River Kharashrota

    500 metres

    SW 10

    River Kharashrota

    500 metres

    SW 11

    River Kharashrota

    500 metres

    SW 12

    River Kharashrota

    500 metres

  3. RESULTS AND DISCUSSION

    The chemical oxygen demand values of surface water of Gonda nallah and River Kharashrota during Pre- monsoon, Monsoon and Post-monsoon seasons at twelve sampling stations and their interactions is presented in Table 2.

    The analysis of variance indicates that the values for the seasons, surface water sampling stations and their interactions in respect of chemical oxygen demand of the water samples are significant (Table 2).

    The mean value of chemical oxygen demand of the surface water samples was found to be more during monsoon (46.708 mg/l) followed by pre-monsoon (45.492 mg/l). The level is at minimum during postmonsoon (42.570 mg/l). The maximum value during monsoon may be due to increase in the amount of pollutants with run-off water. The higher mean value of chemical oxygen demand of the surface water samples during pre-monsoon than that in the post-monsoon may be due to decrease in dilution with the evaporation of water.

    TABLE 2.: Table for seasons, surface water sampling stations and their interactions in respect of chemical oxygen demand (mg/l) of the water samples of the study area

    Pre-

    monsoon

    Monsoon

    Post-

    monsoon

    Mean

    SW 1

    72.640

    73.900

    69.430

    71.990

    SW 2

    68.670

    69.840

    65.300

    67.937

    SW 3

    66.580

    67.400

    62.820

    65.600

    SW 4

    63.550

    64.620

    60.760

    62.977

    SW 5

    63.200

    63.750

    60.000

    62.317

    SW 6

    62.920

    63.490

    59.670

    62.027

    SW 7

    29.340

    31.200

    27.000

    29.180

    SW 8

    27.100

    28.100

    23.880

    26.360

    SW 9

    25.330

    25.920

    21.930

    24.393

    SW 10

    22.590

    24.630

    20.740

    22.653

    SW 11

    22.020

    23.930

    19.790

    21.913

    SW 12

    21.970

    23.720

    19.520

    21.737

    Mean

    45.492

    46.708

    42.570

    SE(m) (±) for seasons

    0.038

    CD(0.05) for seasons

    0.231

    SE(m) (±) for sampling stations

    0.076

    CD(0.05) for sampling stations

    0.236

    SE(m) (±) for interactions of seasons and

    sampling stations

    0.132

    CD(0.05) for interactions of seasons and

    sampling stations

    0.386

    CV (%)

    0.72

    Maximum permissible value for COD as prescribed by WHO is 10 mg/l. Higher the level of chemical oxygen demand indicates higher the load of pollution in the river [12].

    The mean value of chemical oxygen demand of the surface water samples is more at water sampling station SW 1 (71.990 mg/l), followed by SW 2 (67.937 mg/l), SW

    3 (65.600 mg/l) and SW 4 (62.977 mg/l) on Gonda nallah. The minimum value 21.737 mg/l was recorded at SW 12 which is on River Kharashrota. The chemical oxygen demand levels of the surface water samples from sampling stations on Gonda nallah is more than that of River Kharashrota. It may be due to accumulation of non- degradable chemical pollutants. Exposure to these non- degradable chemical pollutants may affect the local people. Singanan et al. (2006) reported the toxicity of higher level of hexavalent chromium[13].

    The values of the interactions of the seasons and sampling stations in respect of chemical oxygen demand of the surface water samples range between 72.640 mg/l (SW

    1. and 21.970 mg/l (SW 12) during pre-monsoon. During monsoon the interaction values range from 73.900 mg/l (SW 1) to 23.720 mg/l (SW 12) and during post-monsoon the interactions values range from 69.430 mg/l (SW 1) to

      19.520 mg/l (SW 12).

      The variation in the mean values of chemical oxygen demand in respect of seasons and sampling stations indicate the amount of oxygen equivalent of the oxidizable organic matter present [11], [14]. Recorded higher value of chemical oxygen demand in the present study may be due to the entry of effluents from Kalinga Nagar Industrial Complex, which is supported by the findings of [15]Nayar et al. (2007); [16]Rajurkar et al. (2003) and [17]Dubey and Ujjania (2013) in the similar context.

  4. CONCLUSION

    Surface water pollution of major rivers in our country is caused by the discharge of untreated or partially treated effluent from industries. Probably the industrial wastes are discharged into the receiving water bodies without adequate treatment. The accidental release and deliberate discharge of partially treated effluents has the potentiality to disrupt the structure and function of the biological system as many effluents are complex in nature. Hence, the regulation of quality of industrial effluents is of utmost necessity in order to protect the aquatic environment from adverse effects caused by effluent discharge [18]. If this will continue for a longer period without any remedial measure, it is likely to accumulate in the nearby soil and water resources, leading to undesirable adverse effects on the living system in and around the industry. The living organisms take in water directly or indirectly for various metabolisms. In the words of Chakraborty et al. (2013) if the intake water is polluted, very seriously it will do harm to them ultimately affecting the food chain and ecosystem [10]. Further study is needed in this context to reduce the pollutant load of these surface water bodies.

    Deteriorating water quality of rivers is of major concern in India, which is especially true for rivers being used as drinking water sources. The main causes of deterioration in water quality were high interference of anthropogenic activities, lack of proper sanitation and industrial and domestic waste water inflow [19]. The present study indicates that the surface water of the studied water bodies is polluted and is unsafe for use without treatment due to the presence of excessive quantity of oxidizable pollutants.

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