Water Pollution Index Modified
Uses and Limitation:
It has wide application and it is used as the indicator of the quality of sea (Filatov. et al., 2005) and river water (Lylko et al., 2001), as well as of drinking water (Nikoladis et al., 2008).
Categorization Table
The quality class according to WPI (lyulko et al. 2000, milijašević et al. 2011)
Standards Required
The standard threshold values for all parameters are specific for each country, given as national legislative (oFFiCial gazette RS 74/2011), which should minimize the bias caused by ecological and geographical differences.
Variables Selection
The following parameters are taken into consideration: dissolved O2, pH, suspended sediments, BOD5, nitrites, orthophosphates, ammonium, metals (Fe, Mn, Hg, Cu, Pb, Cd), sulfates and coliform germs.
Calculation of Water Pollution Index Modified:
The Water Pollution Index Modified is calculated as the sum of the ratio of the measured annual average value Ai and the standard threshold values T for each parameter, divided by the number of used parameters (n):
\begin{eqnarray*}
WPI=\sum_{n=1}^{n} \ \frac{A_{i}}{T} X \frac{1}{n}
\end{eqnarray*}
Case Studies based on Water Pollution Index Modified
Case Study 1
Water quality and status assessment of water bodies could be based on a large number of various parameters, including physical, chemical, hydromorphological, microbiological and biological. Often it is difficult to interpret the results of water status assessment when numerous quality elements are analysed, since each may indicate different quality class. The Water Pollution Index Modified (WPI) overcomes this problem by providing a single assessment score. Previously, WPI was calculated using physical and chemical parameters combined with microbiological parameters. Biological quality elements are recommended by the EU Water Framework Directive (WFD) as obligatory for the assessment of ecological status of water bodies. For the first time in this study, the index was modified to include also biological parameters. Sampling and field measurements were done in 2007–2011, at three sites on the Sava River in the Belgrade region. According to the obtained WPI values, the river was assessed as polluted in 2007, moderately polluted for the period 2008–2010 and slightly polluted (“pure”) in 2011. This result shows an overall improvement of the water quality during the period of examinations. Our study demonstrates that the WPI could be effectively used as a metric for ecological assessment according to the requirements of the WFD. It should be further elaborated to provide type- and stressor-specific assessment system.
Case Study 2
The Timok River (202 km long, 4547 km2 basin area) is located in East Serbia. It is a right tributary of the Danube River and one of the most polluted watercourses in Serbia. On the basis of the data provided by the Republic Hydrometeorological Service of Serbia, the paper presents an analysis of water quality and pollution using the combined physico-chemical WPI index (Water Pollution Index) calculated for two periods – 1993–96 and 2006–2009 at four hydrological stations: Zaječar-Gamzigrad (Crni Timok River), Zaječar (Beli Timok River), Rgotina (Borska Reka River) and Čokonjar (Timok River). The following parameters were taken into consideration: dissolved O2, O2 saturation, pH, suspended sediments, Five Day Biochemical Oxygen Demand (BOD5), Chemical Oxygen Demand (CODMn), nitrites, nitrates, orthophosphates, ammonium, metals (Cu, Fe, Mn, Hg, Ni, Zn, Cd), sulphates and coliform germs. The average WPI values were calculated for the observed periods based on the comparison of the annual average values of the listed parameters and defined standard values for the I water quality class (according to the Regulation on the Hygienic Acceptability of Potable Water of the Republic of Serbia). The highest pollution degree was recorded in the Borska Reka River, where heavy metal levels (especially manganese and iron) were significantly increased. These metals are indicators of inorganic pollution (primarily caused by copper mining). Also, increased values of the organic pollution indicators (ammonium, coliform germs, Five-Day Biological Oxygen Demand – BOD5) in the Borska Reka and the Timok rivers are the result of uncontrolled domestic wastewater discharge.
References
Brankov, Jovana, Milijašević, Dragana, Milanović, Ana (2012). The assessment of the surface water quality using the water pollution index: a case study of the Timok river (the Danube river basin), Serbia. Archives of Environmental Protection, 38 (1), 49-61.
Popović, Nataša Z., Đuknić, Jelena A., Čanak Atlagić, Jelena Ž., Raković, Maja J., Marinković, Nikola S., Tubić, Bojana P., Paunović, Momir M. (2016). Application of the Water Pollution Index in the Assessment of the Ecological Status of Rivers: a Case Study of the Sava River, Serbia. Acta zool. bulg., 68 (1), 97-102.