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MASTER'S THESIS - SuSanA

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5 Learning from already implemented CWs (in Albania and the Balkan region)<br />

5.2.4 Financial aspects of construction and O&M<br />

The costs for the plant were around 60,000 €. This can be divided into 50,000 € for construction and<br />

material, 5,000 € for supervision and training and 3,000 € for documentation and public relations (Gjinali et<br />

al. 2011). The cost estimation, that was given by the construction company Gener2 counted only around<br />

40,000 € for the construction works and the material. Analysing the cost estimation, the construction works<br />

counted for around 30 % and the material for around 70 %. As O&M is done by the SOS children’s village<br />

technician, no extra costs arise. The bill of quantities with the cost estimation prepared by the construction<br />

company Gener2 is attached in Appendix A.<br />

5.2.5 Problems of the pilot plant and recommendation for reconstruction<br />

in 2010<br />

In September 2010, the German engineer Jens Nowak visited the pilot plant in the SOS children’s village and<br />

proved the well-functioning of the plant. In his report to the GIZ “Reconstruction of Constructed Wetland<br />

SOS children’s village Tirana” (Nowak 2010,b), he describes the state of the plant in 2010 and the problems<br />

that occurred at that time. The document includes also recommendations for reconstruction. The main<br />

findings are presented in the following section.<br />

Some of the concrete shafts have holes and are located in a way that rainwater can infiltrate into the sewer<br />

system while heavy rainfall. This can cause hydraulic overload and washing-out of sludge from the pretreatment<br />

to the filter, what causes clogging of the filter bed and the distribution pipes. Another reason for<br />

clogging could have been the large amount of grease in the influent to the vertical filter.<br />

The old septic tank with three chambers was reconstructed as one Imhoff tank and one pumping chamber,<br />

not using the third chamber. This was changed during the re-construction in 2010, to use the third chamber<br />

as additional settling chamber because sludge separation in the Imhoff tank was assumed to be insufficient<br />

due to the design. The Imhoff tank was built too shallow, only 2.8 m deep, and with an insufficient slope of<br />

the funnel, which should be at least 1:1.7. The influent pipe could not be equipped with a knee-fitting as it<br />

is usual, as the top of it would have been above the water level. The distance between the water level in the<br />

Imhoff tank and the sludge pipe, that should normally be more than 1 m, counted only 0.2 m. The sludge<br />

pipe going from the bottom of the Imhoff tank to the sludge drying bed was built with a pipe DN 100 only,<br />

instead of at least DN 200. Additionally, the pipe had no valve at the outlet like it was planned. Therefore,<br />

the sludge pipe was replaced by a pipe DN 160 (as DN 200 was not available) and a free accessible valve at<br />

the end of pipe was recommended. The pipe was built with T-fitting in DN 160.<br />

Because the pre-treatment was not working satisfying and therefore solid matter was in the water that was<br />

pumped to the vertical filters, the valves for feeding the vertical beds were clogged and could not be closed<br />

completely. This led to a permanent feed flow of wastewater to both vertical filter beds. Additionally,<br />

distribution pipes and the holes in the pipes were partly clogged and only the front part of the vertical filter<br />

beds was fed with wastewater. Cleaning of both valves for wastewater discharge to the vertical filter beds<br />

took place in 2010 in order to be able to close them again.<br />

As some plant roots were growing in some of the shafts, it was recommended to remove them from time to<br />

time to avoid the risk of destroying the concrete. To increase the pressure in the distribution pipes in each<br />

vertical filter, one distribution pipe was removed and closed. The discharge holes were on top of the<br />

distribution pipe and high fountains up to 2 m caused aerosol and smell. For improvement of the plant, they<br />

had to be turned so that the holes were on the side and not at the top. Also extra discharge holes with the<br />

diameter of 8 mm had to be added on the other site with a distance between the holes of at least 1 m to<br />

guarantee an even distribution of the wastewater on the vertical filter bed.<br />

62

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