IJA-2017v7n25 - page 12

International Journal of Aquaculture, 2017, Vol.7, No.25, 166-173
172
be a point source pollution for this element in the upper reaches of the river, which may be absorbed, or removed
by chemical binding to other substances.
Many organisms have been used as bioindicators of aquatic environmental pollution. As Oehlman and Schulte-
Oehlman (2003) posited, organisms which have limited range of mobility are good bioindicators.
Malletia
cumingii
is a benthic bivalve with proximity to bottom sand. Metal elements load or metal element concentrations
in the environment can be estimated from this kind of species. Similarly, it is the opinion of Khatri and Tyagi
(2015) that through the application of Bioindicators we can predict the natural state of a certain region or the
level/degree of contamination. It is also pointed out that the concentration of metals in an organism is not
necessarily an indication of the level of concentration in the water column. According to Elder and Collins (1991),
bioaccumulation and toxicity are extremely situation dependent; therefore, concentration levels should not be
extrapolated from one particular area to other situations where the biological species or environmental conditions
are different. That even within one species, individual characteristics such as size, life stage, sex, and genotype
can have significant effects on responses to contaminants.
The quantity of metals absorbed and maintained in an organisms’ body depends on a lot of factors as was
explained by Cheng (1987), Elder and Collins (1991), Ayotunde et al (2012) and Oehlman and Schulte-Oehlman
(2003) to include; concentrations and chemical characteristics of water, ecological needs, metabolism and feeding
patterns of organism tolerance, size, life stages, species, organic substances, pH, temperature, alkalinity, hardness,
inorganic ligands, interactions, sediments and season. These factors can equally alter metal toxicity in the aquatic
environment substantially by causing attenuating effect.
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