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GPS-X Technical Reference

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23 Modelling Fundamentals<br />

Primary and Final Effluent Response Variables<br />

Water quality constituents such as BOD 5 (inhibited), Total Suspended Solids (TSS),<br />

Total Kjeldahl Nitrogen (TKN), ammonia (NH 3) and nitrates (NO 3) are necessary for the<br />

calibration of the various unit processes. For example, BOD (in lack of COD) is used to<br />

calibrate and verify the carbonaceous component of the IAWQ activated sludge model,<br />

while suspended solids measurements can be useful in identifying the settling parameters<br />

of Hydromantis' layered settler model. The nitrogenous compounds are needed to<br />

calibrate the nitrification-denitrification component of the model.<br />

INFLUENT WASTEWATER CHARACTERISTICS<br />

Basic Parameters<br />

Basic influent wastewater characteristics such as BOD 5, BOD u, COD, TSS, VSS, and<br />

TKN are important to know in that they allow us to establish mass balances across the<br />

system. The biochemical oxygen demand (BOD) provides only partial information on the<br />

influent organic load (see Why COD is Important to Know). COD measurements are not<br />

readily available in some wastewater treatment plants. In this case, the BOD 5/BOD u ratio<br />

can better estimate the influent organic load. Suspended solids, influent VSS and BOD<br />

together, can be used to determine the different influent organic fractions, which are<br />

critical for the proper use of the IAWQ activated sludge model, as discussed in <strong>GPS</strong>-X<br />

Objects. Influent TKN is generally more useful than ammonia concentration alone<br />

BIOLOGICAL REACTOR AND FINAL SETTLER<br />

Organic Compounds<br />

The IAWQ activated sludge model contains a large number of stoichiometric and kinetic<br />

parameters, which describe the degradation of organic matter in the activated sludge<br />

process (Henze et al., 1987a). Some of the analytical tests are laborious and are not<br />

discussed here. Many of the default model parameters can be used with a high degree of<br />

confidence. Site-specific model parameters include the maximum growth rate and the<br />

yield coefficient of the heterotrophs. If the data described in the previous sections are<br />

known (e.g., sludge wastage rate and wastewater influent fractions), it is relatively easy<br />

to optimize the maximum growth rate and yield coefficient of the heterotrophs to match<br />

the measured MLSS, sludge production, and oxygen uptake rate.<br />

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

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