17.09.2013 Views

Problematik vid höga flöden - Gästrike Vatten AB

Problematik vid höga flöden - Gästrike Vatten AB

Problematik vid höga flöden - Gästrike Vatten AB

SHOW MORE
SHOW LESS

Create successful ePaper yourself

Turn your PDF publications into a flip-book with our unique Google optimized e-Paper software.

primary sludge hydrolysis. For the same reasons the maximum influx-flow was also lowered<br />

from 3000 m 3 /h to 2500 m 3 /h to both the primary sludge hydrolysis and the biological stage.<br />

During both december 2007 and 2008, the WWTP experienced exceptional high-flow<br />

conditions with a slightly higher mean influx flow during 2008 compared to 2007. In figure 7<br />

the effluent phosphorus load and the usage of precipitation chemicals for the two periods are<br />

plotted, as well as three months afterwards, when the operation conditions had returned to<br />

normal. At december 2008, the bypass point had been changed, and this year less than half the<br />

amount of phosphorus was discharged and less than one third of precipitation chemicals were<br />

used compared to the year before. After the high-flow event 2007 the EBPR process was<br />

deteriorated for about three months. 2008 the process recovered much faster, which led to a<br />

lower effluent phosphorus load with only one fifth of precipitation chemicals.<br />

P (kg)<br />

1600<br />

1200<br />

800<br />

400<br />

0<br />

(a) Effluent phosphorus load<br />

December January-March<br />

Bypass at 3000 m3/h, 2007 Bypass at 2500 m3/h, 2008<br />

Figure 7. (a) Effluent phosphorus load and (b) usage of precipitation chemicals before and after optimization<br />

changes in the process. During (December) and after (January to March) high-flow conditions in 2007 and 2008.<br />

The overall results from the changes implemented were: a more stable process, smaller<br />

effluent peaks, a minimal usage of precipitation chemicals, avoiding need for external carbon<br />

source and less energy consumption. In figure 8, a plot of the usage of precipitation chemicals<br />

and the effluent phosphorus load during the years 2006 to 2009 is presented. In 2009 the<br />

effluent phosphorus load and the usage of precipitation chemicals were the lowest since the<br />

WWTP was rebuilt for EBPR, and this makes the prospects for managing the stringed<br />

demands 2012 optimistic.<br />

Effluent P (tonne)<br />

8<br />

6<br />

4<br />

2<br />

0<br />

Figure 8. Overall effluent phosphorus load and total usage of precipitation chemicals from the year 2006 to 2009.<br />

61<br />

FeCl 3 (tonne)<br />

60<br />

40<br />

20<br />

0<br />

(b) Chemical precipitation<br />

December January-March<br />

chemical<br />

300<br />

200<br />

Precipitation<br />

100<br />

0<br />

2006 2007 2008 2009<br />

Year<br />

Effluent P Precipitation chemical<br />

(tonne)

Hooray! Your file is uploaded and ready to be published.

Saved successfully!

Ooh no, something went wrong!