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Due to the additivity of baseline toxicity, this means an enhanced adverse effect with increasing organic pollution.
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Interestingly, the WQI scores for site S1 showed unsuitable water quality status during every sampling season mainly because of the lack of sufficient flow in addition to increased organic pollution load, thus reducing the self-purification capacity of the river at the site.
The groundwater involved in contamination of both drinking-water and non drinking-water systems was probably polluted by the river flowinon drinking-waterarby and by systemsr infiltration; the concentration gradient of chemical indicators of organic pollution (ammonia) increased from the coast towasd the inland area.
At S1, high organic pollution, low flow in the summer coupled with increased temperature caused a zero DO level.
The BOD is therefore a reliable gauge of the organic pollution of a body of water.
Organic Pollution Index (Wei et al. 2009) is an immediate and reliable measure of river water quality and pollution.
Thus, BOD is an indicator of organic pollution with higher values indicating higher levels of organic pollution (Patel et al. 1983).
From the AGPI score, it is revealed that Site 4 has probable high organic pollution and Site 2 and Site 3 have moderate organic pollution.
In order to measure the organic pollution in Ganga, biological oxygen demand (BOD5) and total organic carbon (TOC) were determined.
It contained excessive degree of organic pollution and affected environment (Saranraj and Stella 2012).
High concentration of chloride indicates a higher degree of organic pollution (Yogendra and Puttaiah 2008).
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