11.10.2013 Views

2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures

2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures

2. ENVIRONMENTAL ChEMISTRy & TEChNOLOGy 2.1. Lectures

SHOW MORE
SHOW LESS

You also want an ePaper? Increase the reach of your titles

YUMPU automatically turns print PDFs into web optimized ePapers that Google loves.

Chem. Listy, 102, s265–s1311 (2008) Environmental Chemistry & Technology<br />

with perspective for 2036 follows also the dynamic effluent<br />

standard values. It can be expected that upgraded WWTP will<br />

meet current legislation also with regard to dynamics of the<br />

processes.<br />

The first task was to investigate what could happen if the<br />

reconstruction in 2003 had not been carried out. The effluent<br />

concentration values are shown in Table I. The load in 2007<br />

and consequently the effluent concentration values are lower<br />

than in 2002 due to industrial activities reduction. This result<br />

could lead to the conclusion that there had been no need for<br />

the reconstruction of the WWTP in 2003. However, because<br />

of the more stringent requirements (Regulation of the Slovak<br />

government, 2005) which permits 10.0 mg dm –3 for ammonium<br />

nitrogen for effluent of WWTP with corresponding load,<br />

it was necessary to carry out the reconstruction. Therefore, it<br />

should be stressed that the WWTP without this reconstruction<br />

would not be able to meet current effluent standards.<br />

The second task was to study what would happen if the<br />

pollution load of actual biological stage of the WWTP increased<br />

to values expected in 2036. The results of dynamic simulations<br />

show that even if the load will increase, the WWTP<br />

will be able to meet current effluent requirements.<br />

Table I<br />

Results of simulations<br />

WWTP 2002 1 st task WWTP 2007 2 nd task<br />

plant layout 2002 2007<br />

load situation 2002 2007 2007 2036<br />

n-nH 4<br />

[mg dm –3 ]<br />

n-nO 3<br />

[mg dm –3 ]<br />

25.06 20.89 0.81 4.05<br />

0 0 7.47 3.91<br />

Conclusions<br />

Two time-variable influent and effluent data sets of wastewater<br />

flow and composition were measured for different<br />

technological arrangements of the WWTP and were applied<br />

for dynamic simulations.<br />

It can be concluded from the work that the mathematical<br />

model ASM1 is suitable for the description of the process<br />

s354<br />

dynamics of the WWTP biological stage. Good fit between<br />

experimental and calculated effluent concentration values<br />

resulted from performed dynamic simulations.<br />

The results of dynamic simulation confirmed the necessity<br />

of the WWTP reconstruction carried out in 2003 in order<br />

to comply with actual legislation requirements.<br />

Compliance with actual effluent limits follows for previous<br />

steady state design and upgrading of the WWTP when<br />

investigating dynamics of the process.<br />

According to results of dynamic simulations it can be<br />

expected that the existing WWTP will comply with actual<br />

discharge standards also for pollution load as expected in<br />

2036.<br />

This work has been supported by the Slovak Grant<br />

Agency for chemical and chemical-technological science<br />

(Grant No. 1/0866/08). The authors would also like to<br />

thank Ľubomír Krcho and Monika Polláková for the help by<br />

acquirement influent, effluent and operational data from the<br />

WWTP.<br />

REFEREnCES<br />

1. Chem. Pap. 56, 117 (2002).<br />

<strong>2.</strong> Derco J., Kovács A., Gulyásová A., Dercová K., Horňák<br />

M.: Reserch report No. 4272, Bratislava, Slovakia,<br />

2002<br />

3. Derco J., Drtil M., Bodík I., Hutňan M.: Technológia<br />

vody a ochrana vodných zdrojov I. Časť. ÚVTIP nitra,<br />

Bratislava 2004.<br />

4. Derco J., Schütze M.: Odpadové vody 2004. Október<br />

20–22, Tatranské Zruby 2004, p. 111<br />

5. Henze M., Grady Jr. C. P. L., Gujer W., Marais G. R.,<br />

Matsuo T.: Activated Sludge Model No. 1, Scientific and<br />

Technical Report no. 1., IAWPRC, London 1987.<br />

6. ifak. SIMBA 5 – Manual. Institut für Automation und<br />

Kommunikation e. V., Magdeburg 2005.<br />

7. Regulation of the Government of the Slovak Republic<br />

n° 296/2005 on Quality Objectives of Surface Waters<br />

and on Limit Values for Pollution Indicators of Waste<br />

Waters and Special Waters.

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

Saved successfully!

Ooh no, something went wrong!