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Systems Analysis of Zaragoza Urban Water - SWITCH - Managing ...

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<strong>Systems</strong> <strong>Analysis</strong> <strong>of</strong> <strong>Zaragoza</strong> UWS<br />

Guillermo Penagos<br />

Table 4. <strong>Zaragoza</strong> public WWTPs<br />

WWTP Cartuja<br />

Almozara<br />

Parameter<br />

Sewage Origin Industrial and domestic Industrial and domestic<br />

Average flow at design<br />

3.00 0.40<br />

(m 3 s -1 )<br />

Average actual flow in<br />

1.72 0.37<br />

2006 (m 3 s -1 )<br />

<strong>Water</strong> treatment<br />

Primary sedimentation, Biological Primary decantation, Biological<br />

treatment by activated sludge and treatment by activated sludge and<br />

secondary decantation<br />

secondary<br />

decantation,<br />

Phosphorus removal with Iron<br />

Chloride<br />

Sludge treatment Primary and secondary digestion<br />

plus dehydration by filter press<br />

Centrifuge dehydration flowed by<br />

incineration<br />

As it can be seen in table 4 “Almozara” is working near its actual capacity whereas<br />

“Cartuja” seems to be over dimensioned and is working at half <strong>of</strong> its actual capacity.<br />

4.3 Environmental performance <strong>of</strong> <strong>Zaragoza</strong> UWS<br />

4.3.1 Use <strong>of</strong> chemical products<br />

Figure 7 shows the annual consumption <strong>of</strong> chemical products by <strong>Zaragoza</strong> UWS<br />

from 2000 for DWT and from 2001 for WWT. There is a steady trend over these<br />

years, but Chlorine and Allum shows a clear reduction for 2005 and 2006, from<br />

around 3000 to 2500 ton and from 8000 to 6000 ton respectively. PAC use for DWT<br />

started in 2003 and it has not been steady since then.<br />

32

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