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GPS-X Technical Reference

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4 Appendix A – Prefermenter Petersen Matrix<br />

dC L<br />

dt<br />

r<br />

Hence, to obtain the respiration rate only the differential term has to be determined.<br />

This can be done by measuring the decrease in DO due to respiration as a function<br />

of time, which is equivalent to approximating the differential term with a finite<br />

difference term. The consequence of this approach is that the DO becomes<br />

exhausted so that for each new measurement of r a reaeration of the sludge is needed<br />

to bring the DO concentration to a higher level. DO and substrate are limiting when<br />

their concentrations become too low, causing a non-linear DO decrease. The<br />

procedure for the determination of respiration rate according to "Standard Methods"<br />

(APHA, 1989) is based on this principle. The principle can be used for manually<br />

measuring respiration rate or it may be implemented in an automatic respirometer,<br />

which samples activated sludge from an aeration basin and does one or more<br />

measurements of the DO decrease.<br />

The disadvantage of the need for reaeration can be eliminated when the sludge is<br />

continuously aerated. The oxygen mass transfer then has to be included into the<br />

mass balance:<br />

dC<br />

dt<br />

L<br />

K<br />

L<br />

a<br />

x<br />

C<br />

L C <br />

r<br />

L<br />

To obtain respiration rate both the differential term and the mass transfer term have<br />

to be determined. To calculate the latter, the mass transfer coefficient (KLa) and the<br />

DO saturation concentration (CL x ) must be known. These coefficients have to be<br />

determined regularly because they depend on environmental conditions such as<br />

temperature, barometric pressure and properties of the liquid. The simplest approach<br />

is to determine them by using separate reaeration tests and look-up tables. Another<br />

approach is to estimate the coefficients from the dynamics of the DO concentration<br />

whether or not in combination with a close loop adaptive control of the dissolved<br />

oxygen concentration. The advantage of the dynamic method is that the values of the<br />

aeration coefficients can be updated relatively easily. This respirometric principle<br />

allows the measurement of r at a constant DO concentration, thereby eliminating the<br />

dependency of r on the DO concentration. This principle can be implemented in a<br />

separate respirometer or directly in the aeration tank.<br />

Repetitive aeration or estimation of oxygen transfer coefficients, as with the above<br />

principles, can be avoided when activated sludge with a high enough DO<br />

concentration is pumped continuously through a closed completely mixed or plug<br />

flow cell without gas phase. The mass balance becomes:<br />

dC<br />

dt<br />

L<br />

Q<br />

<br />

V<br />

in<br />

L<br />

C<br />

C <br />

r<br />

Lin<br />

Lout<br />

Both DO concentrations CLin and CLout can be measured continuously to allow the<br />

calculation of r. In a respirometer Q and VL are instrument constants. This principle<br />

is in fact the continuous counterpart of the first one and it is as such also sensitive to<br />

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

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