The element carbon has been in existence since the dawn of time. It has a diverse presence in our world, with coal being the most familiar example. Diamonds, with their very ordered structure, are the purest form of carbon. Chains of carbon atoms also make up the backbone of all molecules in the human body and all living material around us. It is from these sources, particularly the botanical materials, that another form of activated carbon has been derived.
Structure Of Activated Carbon
Activated carbon is widely used as an adsorbent in gas purification, refining pulp, and also for the purification of food products, among others, oil purification, refining cane sugar, beet sugar, and corn sugar, eliminating the taste and odor of drinking water.
Specifications for activated carbon include particle size or mesh, surface area, pore volume, moisture range, adsorption characteristics, pH, water solubility, and tamped bulk density. The percentage of ash, iron, and phosphates is also important to consider. For high-purity applications, activated carbon filters should contain very low amounts of iron, typically 100 parts per million (ppm). Activated carbon with extremely high adsorptive capacities is suitable for decolorizing applications and may carry product specifications for methylene blue adsorption and have a molasses decolorizing number.
Factors that affect the performance of activated carbon are:
As the molecular weight increases, the activated carbon adsorbs more effectively because the molecules are lea soluble in water. However, the pore structure of the carbon must be large enough to allow the molecules to migrate within. A mixture of high and low molecular weight molecules should be designed for the removal of the more difficult species.
Most organics are less soluble and more readily adsorbed at a lower pH. As the pH increases, removal decreases. A rule of thumb is to increase the size of the carbon bed by twenty percent for every pH unit above neutral (7.0).
Contaminant concentration: The higher the contaminant concentration, the greater the removal capacity of activated carbon. The contaminant molecule is more likely to diffuse into a pore and become adsorbed. As concentrations increase, however, so do effluent leakages. The upper limit for contaminants is a few hundred parts per million. Higher contaminant concentrations may require more contact time with the activated carbon. Also, the removal of organics is enhanced by the presence of hardness in the water, so whenever possible, place activated carbon units upstream of the ion removal units. This is usually the case anyway since activated carbon is often used upstream of ion exchange or membranes to remove chlorine.
It is commonly available in 8 by 30 mesh (largest), 12 by 40 mesh (most common), and 20 by 50 mesh (finest). The finer mesh gives the best contact and better removal but at the expense of higher pressure drop. A rule of thumb here is that the 8 by 30 mesh gives two to three times better removal than the 12 by 40, and 10 to 20 times better kinetic removal than the 8 by 30 mesh.
Generally, the lower the flow rate, the more time the contaminant will have to diffuse into a pore and be adsorbed. Adsorption by activated carbon Indonesia is almost always improved by a longer contact time. Again, in general terms, a carbon bed of 20 by 50 mesh can be run at twice the flow rate of a bed of 12 by 40 mesh, and a carbon bed of 12 by 40 mesh can be run at twice the flow rate of a bed of 8 by 30 mesh.В Whenever considering higher flow rates with finer mesh carbons, watch for an increased pressure drop!
Higher water temperatures decrease the solution viscosity and can increase the die diffusion rate, thereby increasing adsorption. Higher temperatures can also disrupt the adsorptive bond and slightly decrease adsorption. It depends on the organic compound being removed, but generally, lower temperatures seem to favor adsorption.