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GPS-X Technical Reference

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Modelling Fundamentals 20<br />

COD overcomes the above-mentioned problems. It can be automated and measures all<br />

organic fractions of the wastewater. The sludge COD can also be easily determined. COD<br />

measures all organics in oxygen equivalent; that is the electron donating capacity of the<br />

organic matter. This way it provides a direct link between organic load and aeration<br />

requirement. The yield constant is truly constant only if expressed in COD units. Mass<br />

balance is easy to establish with COD in a non-nitrifying plant: in steady-state, the<br />

influent COD must equal the effluent COD plus the COD of the wasted sludge, plus the<br />

oxygen consumed in the degradation of organic matter.<br />

It is for this reason that the International Association on Water Quality (IAWQ)<br />

committee selected and endorses the use of COD as a measure of organic parameter in<br />

simulation of activated sludge plants.<br />

Data Requirements<br />

For modelling purposes, each unit process/operation is represented by a process model<br />

(mathematical model) that reflects the dynamic behaviour of that particular process. One<br />

of the main features of <strong>GPS</strong>-X is that it is model-independent, meaning that <strong>GPS</strong>-X is not<br />

limited to a specific process model. Accordingly, a variety of modelling approaches<br />

(process models) are available within <strong>GPS</strong>-X to handle a specific unit operation or unit<br />

process. For example, the activated sludge process can be modelled using any one of the<br />

following <strong>GPS</strong>-X activated sludge process models:<br />

<br />

IAWQ Task Group models of the activated sludge process (Henze et al.,1987a;<br />

Henze et al., 1994; Henze et al., 1998)<br />

The general (bio-P) model (Dold, 1990, Barker and Dold, 1997)<br />

<br />

<br />

Extended IAWQ (Mantis), described in Mantis Model (MANTIS) section of<br />

Chapter 6)<br />

Comprehensive plant-wide model developed by Hydromantis (Mantis2)<br />

Consequently, a general calibration/verification approach to <strong>GPS</strong>-X must be broadly<br />

defined. The calibration requirements of individual process models are established based<br />

on the nature of each model (i.e., its mechanistic basis). Alternatively, modellers may<br />

need to refer to the original literature reference to assess the calibration requirements of a<br />

particular model in more detail.<br />

Each calibration/verification study follows the same general principles. Accordingly, the<br />

purpose of this section is to provide some guidelines pertaining to the calibration of the<br />

models to full-scale wastewater treatment plants. The most popular process models have<br />

been selected for illustration purposes, including the IAWQ Task Group Activated<br />

Sludge Model No. 1 (Henze et al., 1987a) and layered settler model developed by<br />

Hydromantis (Takács et al., 1991).<br />

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

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