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GPS-X Technical Reference

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303 Others Models<br />

With a large overdose of metal ion to wastewater, most of the phosphorus would be<br />

removed; however, there would still be trace amounts of phosphorus. To model this<br />

phenomenon, a saturation function was incorporated in the model. The amount of<br />

phosphorus removed (or soluble organic component, si and ss, that would flocculate)<br />

becomes a function of the phosphorus concentration (or soluble organic component<br />

concentration). The stoichiometric amount of removal is only achieved when the<br />

phosphorus concentration is large (with respect to the half-saturation coefficient).<br />

Removal is less than the maximum stoichiometric amount when the phosphorus<br />

concentration is small (with respect to the half-saturation coefficient). This phenomenon<br />

is depicted in Figure 11-3.<br />

Figure 11-3 - Removal as a Function of P Concentration<br />

The mass of chemical precipitant formed is also calculated and added to the particulate<br />

inert inorganic component (xii). The stoichiometric amount of chemical sludge produced<br />

is based on the stoichiometry of the basic reaction. For example, in Equation 11.1, the<br />

mass of chemical precipitant (AlPO 4) is 4.52 g per 1g of aluminum ion reacted.<br />

The model provides the user with two dosage methods: mass flow based and flow<br />

proportional. The former requires the user to specify a continuous flow rate for the<br />

chemical, while the latter allows the user to specify a flow rate of chemical per unit flow<br />

of liquid entering the basin. The dosage rate can be set up as a manipulated variable to<br />

maintain the phosphorus at a specified set point at any location downstream of the<br />

chemical addition.<br />

<strong>GPS</strong>-X <strong>Technical</strong> <strong>Reference</strong>

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