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Eighteen surfaces (of each material) were placed one hour later in the tank filled with water of study (Fig. 1).
All wastewater and storm water of study area are dumped into this river which gets released to the Arabian Sea.
The distribution of Cl− and SO4 2− in ground water of study area is shown in Fig. 2e, f for pre- and post-monsoon.
The poor correlation of Ca2+ with SO4 2− (0.30) indicates that gypsum dissolution could not be the major contributor for the dissolved ions in the water of study area.
Each two surfaces, with ten finger marks, were examined with enhancement techniques of black powder, SPR and CA. Open image in new window Fig. 1 non porous surfaces were placed in aquarium tank filled with type of water of study after fingerprints deposition.
The concentration of TAs in home drinking water of study participants ranged from 1 to 1,054 μg/L.
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The aquarium tank is filled with the water type of study (water temperature 18 °C).
In this article, the reactant composition was adjusted by changing the amount of water to study the variation of the size of polystyrene nanospheres.
Open image in new window Fig. 5 Piper diagram illustrating water facies of study area.
Wastewater effluent impacted the drinking water wells of study participants as early as 1966.
Arsenic concentrations in the drinking water of our study subjects were much higher than those of the study subjects selected for Wu's study.
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Justyna Jupowicz-Kozak
CEO of Professional Science Editing for Scientists @ prosciediting.com