Measures for reduction of nutrient pollution and transboundary nutrients loads from territory
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Measures for reduction of nutrient pollution and transboundary - - PowerPoint PPT Presentation
Measures for reduction of nutrient pollution and transboundary nutrients loads from territory of Belarus to the Baltic Sea Aliaksandr Pakhomau Central Research Institute for Complex Use of Water Resources Minsk, Belarus Catchment area
GIWA 2004 Regional assessment 17 Transboundary basins in Belarus Western Dvina
Neman
Western Bug River
Catchment area upstream states (Central and Eastern Europe Region)
60.9 MEUR
Poultry farms Pig farms Cattle farms Source: Pesentation NEFCO project(Poyry Finland Oy)
For pollution reduction investments oxygen consumption potential (OCP) parameter has been used Calculation method: 1 kg BOD results in 1 kg primary oxygen consumption 1 kg total Nitrogen results in 4 kg primary oxygen consumption 1 kg total Phosphorus results in 100 kg secondary oxygen consumption 1 kg total Nitrogen results in 14 kg secondary oxygen consumption Phosphorus and nitrogen will be changed to biologically available P and N by using factors: untreated wastewater is 0.65*P biologically treated wastewater is 0.8*P nitrogen in all cases is 0.9*N Assumptions: 1 Livestock unit (LSU) = 1 cow or cattle = 10 pigs = 1000 poultry 1 LSU equals 100 kgN/year, 12 kgP/year, of which 10 kgN/year and 3.6 kgP/year leaches into environment
Source: FINAL REPORT AND ACTION PLAN (Poyry Finland Oy)
Source: FINAL REPORT AND ACTION PLAN (Poyry Finland Oy)
Calculation of OCP based on manure’s nutrients content resulting in TOP 30 Geographical location risk for nutrient loads into the Baltic Sea Investment capability based
NO YES YES Farm willingness to invest Urgency by regional administration and approval by Ministry NO YES NO YES Selection of TOP 5 farms for future disscussion at the project meeting
Source: Presentation NEFCO project(Poyry Finland Oy)
Estimation of influent loads: People served by WWTPs Per capita loads: BOD5 60 g/cap/d Tot-N 12 g/cap/d Tot-P 2 g/cap/d Estimation of effluent loads: BOD removal 90% Nitrogen removal 40% Phosphorus removal 40% Total nutrient loads from WWTP (2011): Tot-N 4 814 t/year Tot-P 882 t/year Water Cadastre (reporting 2011): Tot-N 3 485 t/year Tot-P 374 t/year
Source: FINAL REPORT AND ACTION PLAN (Poyry Finland Oy)
1 000 2 000 3 000 4 000 5 000 6 000 2011 2015 2020 tot-N without investments tot-N with planned investments
100 200 300 400 500 600 700 800 900 1 000 2011 2015 2020 tot-P without investments tot-P with planned investments
Main target for wastewater treatment has been the fulfillment of HELCOM recommendations after completion of the investments. In practice, the needed investments include construction of chemical dosing station, reconstruction of biological treatment processes but also other needed investments to improve preliminary treatment and sludge treatment units. Cost estimates for reconstruction of biological treatment units including increase of capacity if needed are as follows:
Other activated sludge plants: – PE 150,000 – 200,000 9.0 MEUR – PE 80,000 – 100,000 6.0 MEUR – PE 40,000 – 60,000 4.5 MEUR – PE 20,000 – 40,000 3.0 MEUR
Source: presentation NEFCO project(Poyry Finland Oy)
Other Criteria for Priority Investments
agreement with international financing institutions, the point source is excluded from the candidates (such as IFI loan and grants agreements for Vitebsk, Grodno and Brest)
the point source shows that the proposed investments can be afforded.
nitrogen)
Loading-based criteria The cost efficiency of each investment is proposed to be calculated by dividing the load reduction with the estimated investment cost. The parameter to be used in calculation of load reduction is the oxygen consumption potential (OCP). Total OCP values have been calculated for different type of investments in two situations: (i) before and (ii) after the investment is made. The environmental effects of the investments are the reductions in total OCP. Thereafter, the reduction in total OCP is divided by the life cycle costs to get the cost efficiency of the specific investment in reduction of OCP kg/EUR. Cost efficiencies of different investments have been compared with each other and the investment with the highest cost efficiency figure represents the highest priority investment.
Priority order of municipal wastewater treatment investments
Source: FINAL REPORT AND ACTION PLAN (Poyry Finland Oy)
Project implements the HELCOM Baltic Sea Action Plan’s Eutrophication Segment and its Recommendation 28E/5 on more stringent requirements for phosphorus removal from municipal WWTPs. Project demonstrates potentials of joint implementation and joint investments in the BSR in combating the eutrophication in a cost-effective way. Brest WWTP – pilot project Project PRESTO (Project on Reduction of the Eutrophication of the Baltic Sea Today) PRESTO combats eutrophication by improving municipal wastewater treatment with technical studies and concrete investments as well as by increasing human competence
Source: FINAL REPORT AND ACTION PLAN (Poyry Finland Oy)
Source: FINAL REPORT AND ACTION PLAN (Poyry Finland Oy)
Source: FINAL REPORT AND ACTION PLAN (Poyry Finland Oy)
Ntot load will be reduced by 367 t/year Ptot load will be reduced by 176 t/year Ntot load will be reduced by 166 t/year Ptot load will be reduced by 176 t/year
Proposed measures Kobrin WWTP Lida WWTP Lyakhovichy WWTP Novogrudok WWTP Polymir WWTP Oshmyany WWTP Pruzany WWTP Schuchin WWTP Skidel WWTP Smorgon WWTP Totally new wastewater treatment plant including mechanical dewatering of sludge Total reconstruction of existing wastewater treatment plant and construction of a new mechanical dewatering
Process changes in aeration tanks to provide JHB process Construction of chemical storing and dosing plant Construction of new screening building and secondary sedimentation tank Reconstruction of primary sedimentation tanks Structural repairs of almost all process tanks and reconstruction of one secondary sedimentation tank Replacement of all main equipment and electrical control boards Provision of automatic control system especially for the aeration system Reconstruction of sludge treatment process Construction of mechanical sludge dewatering plant Modification of secondary sedimentation tanks and supply of new scrapers and return sludge pumps Removal of sediments from biological ponds
Source: FINAL REPORT AND ACTION PLAN (Poyry Finland Oy)
Source: FINAL REPORT AND ACTION PLAN (Poyry Finland Oy)
Source: FINAL REPORT AND ACTION PLAN (Poyry Finland Oy)
Source: FINAL REPORT AND ACTION PLAN (Poyry Finland Oy)
Aliaksandr Pakhomau e-mail: Aliaksandr.pakhomau@cricuwr.by Central Research Institute for Complex Use of Water Resources Minsk, Belarus