• Ei tuloksia

Article III. Impacts of alternative nutrient abatement policies on utilities supplying water and abating nutrients

4 DISCUSSION AND CONCLUSIONS

Eutrophication causes changes in ecosystems, affects the usability of waters and influences the economy. To combat eutrophication in the Baltic Sea, nitrogen and phosphorus loads must be reduced. One of the main sources of nitrogen and phosphorus loads is WWTPs. The objective of this dissertation was to determine the physical potential of reducing nitrogen and phosphorus loads in WWTPs in the Baltic Sea littoral countries and to assess nitrogen and phosphorus abatement costs and build abatement cost functions for WWTPs.

Moreover, the objective was to find a cost-effective solution for reducing nitrogen and phosphorus loads in WWTPs in the Baltic Sea littoral countries.

Furthermore, how the costs are divided among the WWTPs and how the initial allocation of allowances impacts market and costs were assessed. Finally, the objective was to determine how nutrient tax and quantity constraint affect the behaviors of water utilities and thus households.

It is shown in this dissertation that there is a large reduction potential for nutrients in WWTPs in the Baltic Sea littoral countries. Additionally, the abatement costs are relatively low but unevenly distributed among the countries. The analyses show that the nutrient abatement costs are lower in WWTPs than has been reported in most of the previous studies, including those of the COWI (2007), Gren (2008a; 2008b), Hasler et al. (2012), Ahlvik et al. (2014), Wulff et al. (2014). Another finding is that phosphorus abatement costs are much lower for WWTPs than for agriculture (see Ollikainen et al.

2012).

In this dissertation, it is demonstrated that a cost-efficient solution under an NTS can even out the cost burden between WWTPs if designed properly.

Initial allocation can alleviate but not entirely eliminate the uneven distribution of costs between WWTPs. Comparing the abatement costs of the NTS and the uniform quantity constraint shows that the higher the aggregate abatement level in the whole region is, the closer the abatement costs are.

Moreover, taking transaction costs into account, the NTS would still yield lower abatement costs than the uniform quantity constraint approach.

Although the difference in the costs between these approaches is small, there is another advantage of the NTS. The timing of the investments can be optimized under the NTS, while under the uniform quantity constraint the installations are forced to invest immediately in abatement. This feature has also been found in practice (see Downing and White 1986; Milliman and Prince 1989; EPA 2008). Overall, 40% of the BSAP nitrogen reduction target and 20% of the BSAP phosphorus reduction target could be cost-efficiently achieved with an NTS between WWTPs.

It is shown in this dissertation that environmental policies aimed at nutrient reductions may decrease the price of potable water, and the wastewater tariff will correspondingly increase. Nevertheless, the aggregate

24

charge to households increases. Environmental policy may also unevenly treat individual water utilities and the households connected to them. Small utilities face higher costs from nutrient reduction policies than do large utilities, which in turn affects the prices households face. To distribute the burden evenly, small water utilities could be compensated to enable prices closer to those of households connected to large utilities. This could be done, for example, by nutrient trading or by side payments collected from nutrient taxes. Although water utilities charge separately for potable water and wastewater, the latter is also based on the consumption of potable water. While measuring the amount of wastewater generated in households, not to speak of its content, would be expensive, the water utilities currently charge for something they do not meter.

Reducing eutrophication in the Baltic Sea requires nutrient reductions from other sources, such as agriculture, and to intervene in the internal nutrient cycle. The means to tackle this issue include not only economic instruments but also innovations in technologies such as extracting phosphorus from wastewater for new products or using abatement process and sludge to produce energy (Ollikainen et al. 2019). The results shown in this dissertation should encourage decision makers to invest in WWTPs, as substantial nutrient reductions could be achieved without spending a large amount of money.

REFERENCES

Ahlvik L, Ekholm P, Hyytiäinen K, Pitkänen H (2014) An

economic-ecological model to evaluate impacts of nutrient abatement in the Baltic Sea. Environmental Modelling & Software 55:164-175. DOI

10.1016/j.ensoft.2014.01.027.

Ahlvik L, Pavlova Y (2013) A Strategic Analysis of Eutrophication Abatement in the Baltic Sea. Environmental and Resource Economics 56:353-378.

DOI 10.1007/s10640-013-9651-1.

Baumol W J, Oates W E (1971) The use of standards and prices for the

protection of the environment. Swedish Journal of Economics, 73, 42-54.

Berbeka K, Czajkowski M, Markowska A (2012) Municipal wastewater

treatment in Poland – efficiency, costs and returns to scale. Water Science

& Technology 66:394-401. DOI 10.2166/wst.2012.199.

Bode H, Lemmel P (2001) International product cost comparison in the field of water management. Water Science and Technology 44:85-93.

COWI (2007) Economic Analysis of the BSAP with Focus on Eutrophication.

Final Report. April 2007. HELCOM and NEFCO.

Crocker T (1966) Structuring of atmospheric pollution control systems. In Wolozin H (ed.) The Economics of Air Pollution. New York: W.W. Norton.

Dales J H (1968) Pollution, Property and Prices. Toronto. University of Toronto Press.

Downing P B, White L J (1986) Innovation in Pollution Control. Journal of Environmental Economics and Management 13:18-29.

Doyle M W, Patterson L A, Chen Y, et al (2014) Optimizing the scale of markets for water quality trading. Water Resources Research 50:7231-7244. DOI 10.1002/2014wr015395.

EC (2017) Urban Wastewater Treatment Directive for Europe.

http://uwwtd.oieau.fr/. Cited 26 Feb 2019.

EEA (2001) Eutrophication of Europe’s coastal waters. Topic Report No 7.

European Environment Agency, Copenhagen, Denmark.

http://www.eutro.org/documents/EEA%20Topic_report_7_2001.pdf.

Cited 22 Feb 2019.

EEC (1991) Council Directive 91/271/EEC of 21 May 1991 concerning urban waste-water treatment.

http://eur-lex.europa.eu/LexUriServ/LexUriServ.do?uri=CONSLEG:1991L0271:200 81211:EN:PDF. Cited 6 March 2019.

Elofsson K (2010) Cost-effectiveness of the Baltic Sea Action Plan. Marine Policy 34:1043-1050. DOI 10.1016/j.marpol.2010.03.003.

ENVTN (2014) Long Island Sound Watershed-Based Trading Demonstration Project. http://www.envtn.org/Long_Island_Sound.html. Cited 31 Jul 2019.

EPA (2008) EPA Water Quality Trading Evaluation. Final Report.

FINLEX (2006) Government Decree on Urban Waste Water Treatment 888/2006.

https://www.finlex.fi/fi/laki/kaannokset/2006/en20060888.pdf. Cited 11 Jan 2020.

26

Friedler E, Pisanty E (2006) Effects of design flow and treatment level on construction and operation costs of municipal wastewater treatment plants and their implications on policy making. Water Research 40:3751-3758. DOI 10.1016/j.watres.2006.08.015.

Gren I-M (2008a) Cost-effectiveness and Fairness of the HELCOM Baltic Sea Action Plan Against Eutrophication. Vatten 64:273-281.

Gren I-M (2008b) Costs and Benefits from Nutrient Reductions to the Baltic Sea. Report 5877. Naturvårdsverket.

Gren I-M, Elofsson K (2013) Market power and double-dipping in nutrient trading markets. Working paper 2013:02. Department of Economics.

SLU. Uppsala.

Hanley N, Shogren, J F, White B (1997) Environmental Economics – In Theory and Practice. MacMillan Press Ltd.

Hasler B, Smart J C R, Fonnesbech-Wulff A (2012) Deliverable 8.1. RECOCA.

Structure of BALTCOST Drainage Basin scale abatement cost minimisation model for nutrient reductions in Baltic Sea regions.

Hautakangas S, Ollikainen M, Aarnos K, Rantanen P (2014) Nutrient

abatement potential and abatement costs of waste water treatment plants in the Baltic Sea region. Ambio 43:352-360. DOI 10.1007/s13280-013-0435-1

HELCOM (2013) Summary notes for the 2013 HELCOM Ministerial Declaration. HELCOM Ministerial Meeting, Copenhagen, Denmark, 3 October 2013.

HELCOM (2009) Eutrophication in the Baltic Sea. An integrated thematic assessment of the effects of nutrient enrichment in the Baltic Sea region.

Helsinki Commission, Baltic Sea Environmental Proceedings No. 115B, Helsinki, Finland, 150 pp.

http://www.helcom.fi/Lists/Publications/BSEP115B.pdf. Cited 26 Feb 2019.

HELCOM (2007) HELCOM Baltic Sea Action Plan. HELCOM Ministerial Meeting, Krakow, Poland, 15 Nov. 2007.

http://www.helcom.fi/Documents/Baltic%20sea%20action%20plan/BSA P_Final.pdf. Cited 22 Feb 2019.

Lankoski J, Lichtenberg E, Ollikainen M (2008) Point/nonpoint effluent trading with spatial heterogeneity. American Journal of Agricultural Economics 90:1044–1058. DOI 10.1111/j.1467-8276.2008.01172.x.

Milliman S R, Prince R (1989) Firm Incentives to Promote Technological Change in Pollution Control. Journal of Environmental Economics and Management 17:247-265.

Montgomery W D (1972) Markets in Licenses and Efficient Pollution Control Programs. Journal of Economic Theory 5:395-418.

NEFCO (2008) Framework for a Nutrient Quota and Credits’ Trading System for the Contracting Parties of HELCOM in order to reduce Eutrophication of the Baltic Sea. Final Report. Green Stream Network.

Nixon, S W (1995) Coastal marine eutrophication: A definition, social causes and future concerns. Ophelia, 41:1, 199-219.

Ollikainen M, Hasler B, Elofsson K, Iho A, Andersen H E, Czajkowski M, Peterson K (2019) Toward the Baltic Sea Socioeconomic Action Plan.

Ambio 48:1377-1388. DOI 10.1007/s13280-019-01264-0.

Ollikainen M, Hautakangas S, Honkatukia J, Lankoski J (2012) Uusia

analyyseja ja välineitä Itämeren suojeluun (New analyses and tools for the Baltic Sea protection). In Hyytiäinen K, Ollikainen M (eds.) Taloudellinen näkökulma Itämeren suojeluun (Economic viewpoint for the Baltic Sea protection), 134 pp. Helsinki, Finland: Finnish Ministry of the

Environment, Ympäristöministeriön raportteja 22/2012 (In Finnish).

https://julkaisut.valtioneuvosto.fi/bitstream/handle/10138/41440/YMra 22_2012_Itameri_FINAL_web.pdf?sequence=2&isAllowed=y. Cited 26 Feb 2019.

Renzetti S (1999) Municipal Water Supply and Sewage Treatment: Costs, Prices, and Distortions. The Canadian Journal of Economics / Revue canadienne d’Economique, 32(3), 688-704.

Renzetti S, Kushner J (2004) Full Cost Accounting for Water Supply and Sewage Treatment: Concepts and Case Application. Canadian Water Resources Journal 01/2004, Vol.29(1), 13-22.

Shortle J S, Dunn J W (1986) The Relative Efficiency of Agricultural Source Water Pollution Control Policies. American Journal of Agricultural Economics 68(3), 668-677.

Tsagarakis K P, Mara D D, Angelakis A N (2003) Application of cost criteria for selection of municipal wastewater treatment systems. Water, Air and Soil Pollution 142:187-210.

Wulff F, Humborg C, Andersen H E, Blicher-Mathiesen G, Czajkowski M, Elofsson K, Fonnesbech-Wulff A, Hasler B, Hong B, Jansons V, Mörth C-M, Smart J C R, Smedberg E, Stålnacke P, Swaney D P, Thodsen H, Was A, Zylicz T (2014) Reduction of Baltic Sea Nutrient Inputs and Allocation of Abatement Costs Within the Baltic Sea Catchment. Ambio 43:11-25.

DOI 10.1007/s13280-013-0484-5.

Xepapadeas A (1997) Advanced Principles in Environmental Policy. New Horizons in Environmental Economics.

LIITTYVÄT TIEDOSTOT