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GPS-X Technical Reference

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137 Suspended Growth Models<br />

Although there is no well accepted definition of the state of colloidal substrate in<br />

wastewater, for the purpose of modelling, it is assumed that this fraction represents the<br />

portion of the substrate COD which lies in the size range of 0.45 micrometers to 1.2<br />

micrometers. These are typically macromolecules which require hydrolysis before<br />

oxidation. This fraction of COD is assumed to behave differently in different unit<br />

processes for example the colloidal COD will behave:<br />

<br />

<br />

<br />

as soluble in solid liquid separation in settlers<br />

as particulate in biological degradation<br />

as particulate or soluble in membrane separation<br />

Soluble Inorganic<br />

In addition to the soluble organic states, the MANTIS2 model considers inorganic states<br />

of soluble inorganic carbon (stic), soluble nitrite-N (snoi), soluble nitrate-N (snoa),<br />

soluble Ammonia-N (snh), soluble Organic nitrogen (snd), soluble ortho-P (sp),<br />

dissolved calcium (sca), dissolved (smg), dissolved potassium (spot), dissolved anion<br />

(sana) and dissolved cation (scat). These inorganic states are chosen so as to<br />

appropriately describe the N and P transformation, inorganic precipitation and pH<br />

changes across the various unit processes in wastewater treatment plant.<br />

The soluble inorganic carbon, stic, represents the sum of carbon in all the ionic species in<br />

the carbonic acid system i.e. H 2CO 3, HCO 3- , CO 3<br />

2-<br />

. In previous models like ASM2D and<br />

New General, the alkalinity (salk) is used to express the buffer capacity in the<br />

wastewater. In MANTIS2, soluble inorganic carbon is used instead of alkalinity as the<br />

state variable as it is a conserved quantity. The alkalinity in the model is estimated by<br />

considering the soluble inorganic carbon and the estimated pH of the system.<br />

Two oxidized form of soluble nitrogen, (i.e. soluble nitrite and nitrate) are considered in<br />

the model. This choice is necessary to model the two step nitrification process.<br />

The additional inorganic states like soluble calcium (sca), soluble magnesium (smg) are<br />

introduced to model the key precipitation reaction involving these ionic species. The state<br />

variable of soluble potassium (spot) is included to model the uptake and release of<br />

potassium during polyphosphate formation and degradation. The dissolved anion (sana)<br />

and cation (scat) represent all other strong anion and cation in the wastewater. These<br />

states are used in formulating the charge balance equation for estimating the pH in the<br />

wastewater.<br />

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

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