Author(s): Effiong EE*, Ngah SA, Abam TKS and Ubong IU
This study was carried out to assess the impact or effect of industrial activities and refuse dump site on the quality of water used for domestic and sanitary purposes in parts of Port Harcourt metropolis, Rivers State Nigeria. The quality assessment was focused on physiochemical parameters. A total of twenty water samples were collected from twenty locations (randomly selected from industrial and refuse dump site areas) within the study area. Ten major physiochemical parameters which include: potency of hydrogen (PH), salinity, electrical conductivity, total dissolved solids (TDS), turbidity (NTU), calcium (Ca2+), magnesium (Mg2+), chloride (Cl), sulphate (SO42-) and nitrate (NO3-) were analyzed. The results obtained were compared with the standards of World Health Organization (WHO), and show that the water samples have PH values between 3.78 and 7.23 which is not within the permissible limit of WHO and thus, indicating that they are acidic and not fit for domestic purposes. Salinity values range between 0.018 and 0.202mg/L indicating that the water is fresh and good for sanitary purpose, electrical conductivity values range between 38.0 and 378.7μΩ/cm, total dissolved solid and turbidity values range from 32.7 to 263.0mg/L and 0.2 to 0.9NTU respectively which is within the limit prescribed by WHO. The concentration of nitrate and sulphate range between 0.47 and 3.00mg/L and <1.0 and 17.2mg/L respectively after analysis and are within the limit prescribed by WHO. The knowledge from this study can be applied in environmental and water management studies and hydrological activities.
Water is indispensable to all life on earth, in nature, water occurs underground, on land, in oceans, ice and glaciers. However, fresh water is constantly recharged through a process known as the hydrological cycle. It controls the temporal and spatial distribution of water in the form of evapotranspiration, precipitation and runoff [1]. Ground water is the process by which water percolates down the soil and reaches the table (aquifer). Water is a key resource for industrial and economic developments, it is used for domestic, recreation, industrial and agricultural purposes. It also plays an important role in sustaining the natural or eco systems [1].
Amongst other natural resources, water is the most vital resource on planet earth. It is the only chemical compound that exists in solid, liquid and gaseous form. Rainfall is the major source of ground water recharge, other sources are recharge from rivers, streams, irrigation water etc [2].
Water is the world’s most abundant natural substance and it is constant circulation, covers about 75% of the earth’s surface, mostly in oceans and other large water bodies, with about 1.6% of water found below the ground as groundwater in aquifers and about 0.001% found in the air as vapour, clouds and precipitation
It is a dispersion medium for all biochemical reactions which constitutes the living process and takes part in almost all of these reactions. Without water, life cannot survive; it is very paramount to life (humans, plants and animals) [3].
The quality of water is of vital concern for mankind since it is directly linked with human welfare. Groundwater is believed to be comparatively much clean and free from pollution than surface water. However, indiscriminate discharge of industrial effluents, domestic sewage and solid waste dump cause the pollution of groundwater and creates health problems for human beings [4].
The problem of water quality is much more acute in the areas which are densely populated, highly industrialized and have shallow water table. The rapid growth of urban areas has further affected water quality due to over exploitation of resources and improper waste disposal practices. Hence, there is always a need for and concern over the protection and management of water quality [5].
The study area for this research as shown in Figure 1 is Port Harcourt metropolis and covers about 260Km2. The area is located within Niger Delta Region of Nigeria and is between Latitudes 4°45?E - 4°60’E and Longitudes 6°50’E - 8°00’E [6].
Figure 1: Map of Port Harcourt Metropolis
The materials used for this research include borehole water samples, distilled water, white plastic containers of three liters capacity, detergents, analytical reagents, PH meter, conductivity meter, turbidimeter, thermometer and GPS.
The white plastic containers were washed with detergent and rinsed with distilled water. The water samples were collected using the plastic containers without any air bubble as per standard procedure and were taken, kept in the laboratory at normal room temperature. Water samples from twenty water boreholes (sampling points) at different locations within Port Harcourt metropolis were used for this study. Table 1 shows the sampling locations and sources.
The water samples were analyzed in the laboratory for the various physiochemical parameters, within 24 hours of sampling, using WHO standard procedure [7].
Physiochemical parameters examined are PH, salinity, electrical conductivity, total dissolved solids, turbidity and presence of calcium, magnesium, chloride, sulphate and nitrate.
S/N |
Sampling Location |
Source |
Sample Code |
1 |
Rukpokwu |
Borehole |
BH 1 |
2 |
Ozuoba |
Borehole |
BH 2 |
3 |
Odili road |
Borehole |
BH 3 |
4 |
Trans Amadi |
Borehole |
BH 4 |
5 |
Eneka |
Borehole |
BH 5 |
6 |
Rumuobiakani |
Borehole |
BH 6 |
7 |
Aluu |
Borehole |
BH 7 |
8 |
Woji Town |
Borehole |
BH 8 |
9 |
Borokiri |
Borehole |
BH 9 |
10 |
Rumuolumini |
Borehole |
BH 10 |
11 |
Choba |
Borehole |
BH 11 |
12 |
Iwofe road |
Borehole |
BH 12 |
13 |
Rumumasi |
Borehole |
BH 13 |
14 |
Mgbuoshimiri |
Borehole |
BH 14 |
15 |
Elimgbu |
Borehole |
BH 15 |
16 |
Rumuokwurushi |
Borehole |
BH 16 |
17 |
Igwuruta |
Borehole |
BH 17 |
18 |
Eliozu |
Borehole |
BH 18 |
19 |
Rumuagholu |
Borehole |
BH 19 |
20 |
Abuloma |
Borehole |
BH 20 |
The results of the physiochemical parameters obtained from the laboratory analysis are shown in Table 2, while Table 3 shows the highest and lowest values of the parameters as well as the water borehole sample.
From the values of PH recorded range between 3.69 and 7.70 which is not within the permissible limit of WHO and thus, indicating that the water samples are acidic and not fit for domestic purpose. Prolonged intake of acidic water may predispose an individual to the dangers of acidosis, which according to health experts, may lead to cancer or cardiovascular damage including the constriction of blood vessels and reduction in oxygen supply, even at mild levels [8]. Intake of acidic water, over time could also cause leaching of valuable minerals from the body. Examples of such minerals include calcium, magnesium and sodium [9].
Conductivity is due to ionizable salt content or ionizable dissolved substances in solution [9]. It depends on the quantity of dissolved salts present and for dilute solutions, it is approximately proportional to the TDS content in solution [10]. Electrical conductivity values for the water samples range between 38.0 and 378.7µ?/cm (micro-Ohms per centimeter) and is with the acceptable standard of 1000µ?/cm. Highest electrical conductivity value was recorded at BH4 indicating high amount of dissolved salt whereas lowest value was recorded at Bh4 7 indicating low amount of dissolved salt.
Salinity is the amount of salt present in a given volume of water. This implies that it indicates the degree of saltiness of water. Salinity values of the water samples is between 0.018 and 0.202mg/L indicating that the water is fresh and good for sanitary purposes. Highest salinity value was recorded at BH4 whereas the lowest value was recorded at Bh4 0 and Bh4 7.
Total dissolved solids gives the overall impression of the quality (purity) of water. Total dissolved solid values range from 32.7 to 263.0mg/L, the higher the TDS, the lower the quality (purity) of water whereas, the lower the TDS, the higher the quality of water. Water sample from BH4 recorded the highest value of TDS and thus is said to be the most impure and poorest in quality while BH9 recorded the lowest value of TDS and is said to be the most pure and best in quality amongst the water samples.
This is the measure of transparency or clarity of water, and it is reflected in all the water Ubong and Gobo (2001), turbidity is due to the presence of colloidal solids which give liquid a cloudy appearance and is aesthetically unattractive and may be harmful. Turbidity values of the water samples range from 0.2 to 0.9NTU which is within the limit prescribed by WHO.
The concentration of calcium in the water samples as analyzed range from 0.09-10.12mg/L. Bh4 9 recorded the highest concentration value whereas Bh4 8 recorded the lowest concentration of calcium in the water sample.
The concentration of magnesium in the water samples has range of value from 0.05mg/L-3.38mg/L. Bh4 9 recorded the highest magnesium concentration with a value whereas Bh4 7 recorded the lowest value.
The concentration of chloride in the water samples range from 0.4mg/L-24.0mg/L. The highest concentration was recorded at BH4 whereas the lowest concentration was recorded at BH9.
The concentration of sulphate in the water samples range from <1.0mg/L-17.2mg/L. BH 4 recorded the highest concentration whereas others recorded the lowest concentration of <1.0mg/L.
The nitrate concentration in the water samples range from 0.47mg/ L-3.00mg/L. The highest concentration was recorded from BH8 whereas the lowest value was recorded with BH9. Nitrate affects hemoglobin in blood and reduces babies’ ability to transport oxygen, infants so affected are said to have ‘Blue Baby Syndrome (BBS)’ [11]
S/N |
Sample Code |
P H |
EC µ?/cm
|
Salinity %
|
Turbidity NTU |
TDS mg/L
|
NO -3 mg/L
|
SO 2- 4 mg/L
|
Mg 2+mg/L
|
Cl- mg/L |
Ca 2+mg/L
|
Tempt.°C
|
1 |
BH 1 |
6.67 |
230.7 |
0.111 |
0.9 |
164.7 |
1.90 |
<1.0 |
0.19 |
11.4 |
5.07 |
29.4 |
2 |
BH 2 |
5.41 |
194.3 |
0.091 |
0.5 |
135.3 |
2.24 |
4.1 |
1.68 |
16.3 |
5.38 |
29.6 |
3 |
BH 3 |
4.08 |
266.3 |
0.125 |
0.3 |
185.7 |
2.24 |
4.5 |
0.91 |
12.8 |
3.12 |
29.5 |
4 |
BH 4 |
3.78 |
378.7 |
0.202 |
0.5 |
263.0 |
2.82 |
17.2 |
2.70 |
24.0 |
9.83 |
29.4 |
5 |
BH 5 |
4.66 |
210.3 |
0.100 |
0.3 |
146.7 |
2.69 |
<1.0 |
1.32 |
9.5 |
5.61 |
29.6 |
6 |
BH 6 |
3.87 |
322.7 |
0.152 |
0.3 |
225.0 |
2.86 |
3.5 |
0.96 |
15.2 |
0.81 |
29.7 |
7 |
BH 7 |
6.62 |
92.7 |
0.043 |
0.5 |
64.3 |
1.95 |
<1.0 |
1.14 |
5.3 |
0.13 |
29.7 |
8 |
BH 8 |
4.52 |
199.3 |
0.093 |
0.3 |
139.7 |
3.00 |
<1.0 |
1.41 |
9.3 |
3.79 |
29.8 |
9 |
BH 9 |
6.87 |
47.0 |
0.022 |
0.3 |
32.7 |
0.47 |
<1.0 |
0.13 |
0.4 |
0.43 |
30.4 |
10 |
BH 10 |
6.85 |
38.3 |
0.018 |
0.2 |
27.3 |
0.56 |
<1.0 |
0.13 |
1.0 |
0.27 |
30.3 |
11 |
BH 11 |
5.94 |
92.7 |
0.043 |
0.3 |
65.3 |
2.39 |
<1.0 |
0.33 |
3.3 |
0.26 |
30.4 |
12 |
BH 12 |
4.59 |
155.7 |
0.074 |
0.2 |
109.0 |
2.85 |
<1.0 |
0.97 |
6.8 |
4.32 |
30.4 |
13 |
BH 13 |
4.62 |
237.0 |
0.111 |
0.3 |
165.3 |
2.61 |
<1.0 |
1.38 |
20.7 |
1.09 |
30.4 |
14 |
BH 14 |
4.39 |
289.3 |
0.136 |
0.3 |
202.7 |
2.89 |
<1.0 |
1.01 |
23.5 |
0.42 |
30.4 |
15 |
BH 15 |
4.63 |
177.0 |
0.083 |
0.2 |
123.7 |
2.66 |
<1.0 |
0.65 |
9.6 |
1.25 |
30.6 |
16 |
BH 16 |
4.73 |
150.0 |
0.077 |
0.3 |
114.0 |
0.82 |
<1.0 |
0.54 |
6.5 |
1.46 |
30.5 |
17 |
BH 17 |
5.63 |
38.0 |
0.018 |
0.3 |
26.7 |
0.56 |
<1.0 |
0.05 |
1.4 |
0.22 |
30.4 |
18 |
BH 18 |
5.47 |
48.0 |
0.023 |
0.3 |
34.0 |
0.59 |
<1.0 |
0.17 |
1.1 |
0.09 |
30.4 |
19 |
BH 19 |
7.23 |
325.3 |
0.153 |
0.4 |
226.7 |
0.91 |
<1.0 |
3.38 |
17.9 |
10.12 |
30.4 |
20 |
BH 20 |
7.18 |
112.0 |
0.052 |
0.3 |
77.7 |
0.75 |
<1.0 |
0.46 |
6.6 |
1.47 |
30.5 |
S/N |
Parameter |
Highest value |
Lowest value |
1 |
PH |
7.23/BH9 |
3.78/BH4 |
2 |
Salinity |
0.202/BH4 |
0.018/Bh4 0,Bh4 7 |
3 |
EC |
378.7/BH4 |
38.0/Bh4 7 |
4 |
Turbidity |
0.9/Bh4 |
0.2/Bh4 2,Bh4 5 |
5 |
TDS |
263.0/BH4 |
32.7/BH9 |
6 |
Ca 2+ |
10.12/Bh4 9 |
0.09/Bh4 8 |
7 |
Mg 2+ |
3.38/Bh4 9 |
0.05/Bh4 7 |
8 |
Cl- |
24.0/BH4 |
0.4/BH9 |
9 |
SO 4 2- |
17.2/BH4 |
<1.0/others |
10 |
NO 3 - |
3.00/BH8 |
0.47/BH9 |
After a careful and successful physiochemical analysis of the water samples, the following conclusions are drawn: