Water Treatment "Part 35": Water with colloidal and suspended particles.

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Among the most significant substances that pollute surface water and must be removed in order to generate drinking water are suspended particles, colloidal solids, and dissolved organic solids. Where solid contaminants are among the most prevalent in surface water. Depending to the size of their particles, two categories of solid pollutants in water may be distinguished, which are:

1- Suspended solids:

It consists of particles that are rapidly accumulated in still water without the use of any chemical reagents and have a diameter greater than 10 to the minus 6 meters.

2- Colloidal solids:

These are called colloids, and they are composed of tiny particles with diameters between 10 power minus 9 meters and 10 power minus 6 meters. Because of its sluggish sedimentation, colloids goes through an agglomeration step before beginning the step of sedimentation.
The term "agglomeration" refers to the collection of small particles by either chemical or physical effect and their transformation into greater sized particles with a sufficient sedimentation period in accordance with the settling time in water treatment basins.

Shared characteristics of suspended and colloidal substances:
-Due to the law of gravity, the particles settle to the bottom of the water basin. The particle diameter, the liquid's viscosity, and the difference between the specific mass of the substance in question and the specific mass of water are three of the most crucial parameters that affect the rate of sedimentation.
-The particles exhibit both adsorption and ion exchange properties.
-Particularly if they are tiny in size and are categorized as colloids with a very slow sedimentation rate, particles are subject to forces other than the earth's gravitational force. Both the ionization and dissociation of the molecules on their surfaces, as well as the adsorption of certain ions by the particles, cause the surfaces of the particles to become charged. This event causes a buildup of particles with opposite charges, which in turn causes the electrical double layer to develop.

In most cases, the size of the suspended particles have a direct relationship to the sedimentation velocity. Table-5 illustrates how long it takes for different-sized particles to sediment.


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