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Riverscape and Groundwater Preservation: A Choice Experiment

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Abstract

This study presents a quantitative approach to support policy decision making for the preservation of riverscapes, taking into account the EC Water Framework Directive (2000/60/EC) and the EC Nitrates Directive (91/676/EEC) concerning the protection of waters against nitrate pollution from agricultural sources. A choice experiment was applied to evaluate the benefits, as perceived by inhabitants, of the implementation of policies aiming to reduce the concentration of nitrates in groundwater, preserve the riverscape by maintaining a minimum water flow and increasing hedges and woods along the Serio River in central northern Italy. Findings suggested that people were particularly concerned about groundwater quality, probably because it is strongly linked to human health. Nevertheless, it was interesting to observe that people expressed a high willingness to pay for actions that affect the riverscape as a whole (such as the minimum water flow maintenance plus reforestation). This is probably due to the close connection between the riverscape and the functions of the river area for recreation, health purposes, and biodiversity preservation.

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Notes

  1. Flood protection, groundwater recharge, biodiversity preservation, water for drinking and for production purposes both in agriculture and industry.

  2. See Platt (2001, p. 33, Table 1) for a synthesis of the studies.

  3. For comparison purposes with other studies in the international literature, the purchasing power parity for private consumption (PPPPRC) between Italy and United States in 2011 was 0.850671 taking the United States as reference (US = 1) (source OECD statistics: http://stats.oecd.org/). The average exchange rate between € and US$ was 1 € = 1.3898 USD in 2011 (source European Central Bank, http://goo.gl/qDWUo).

  4. The IIA assumption is namely that the ratio of the probabilities of choosing one alternative over another (given that both alternatives have a non-zero probability of choice) is unaffected by any additional alternative in the choice set (Louviere and others 2000).

  5. The icons used are inspired by some “proxy” indicators for the policy objective they refer to. In particular, the presence of fish has been used as a proxy of river water quality and the drinkability of water as a proxy for groundwater quality.

  6. Despite the introduction of a new law—Decreto legislativo 30 giugno 2003, n. 196—that protects the privacy of people in the phonebook from phone marketing offers, it was found that people were still really reluctant to respond to the phone approach, probably assuming that it was a sales call. Many of those that passed the introductory approach were not available for an interview declaring to be interested in the topic but to do not have time for an in-person interview and do not want to lose their anonymity.

  7. This result is in line with the data reported by the European Commission (2008).

  8. Cross tabulation statistics of respondents’ opinions with their socioeconomic variables are available from the authors upon request.

  9. According to the data provided by the European Commission (2012), 93 % of Italians think that agricultural chemicals have a negative impact on the status of water sources, while only 76 % think that this is due to overexploitation of water for irrigation purposes. For 92 % of Italians, chemical pollution is the main threat to the water environment, while only 48 % considers that the change in ecosystems is a risk factor (European Commission 2012).

  10. Italy (49.9 gallons per capita, equivalent to 188.9 l) is second behind Mexico in the world ranking of bottled water consumption according to De França Doria (2010, p. 4) 2011 data.

References

  • Aulong S, Rinaudo J, Bouscasse H (2006) Assessing the costs and benefits of groundwater quality improvement in the Upper Rhine valley quaternary aquifer (France). BRIDGE Deliverable D25, 1 December 2006, BRGM, France

  • Bateman IJ, Carson RT, Day B, Hanemann M, Hanley N, Hett T, Jones-Lee M, Loomes G, Mourato S, Özdemiroglu E, Pearce D, Sugden R, Swanson J (2002) Economic valuation with stated preference techniques: a manual. Elgar, Cheltenham

    Book  Google Scholar 

  • Batsell R, Louviere JJ (1991) Experimental analysis of choice. Mark Lett 2(3):199–214. doi:10.1007/BF02404072

    Article  Google Scholar 

  • Bech M, Gyrd-Hansen D (2005) Effects coding in discrete choice experiments. Health Econ 14(10):1079–1083. doi:10.1002/hec.984

    Article  Google Scholar 

  • Bergstrom JC, Boyle KJ, Yabe M (2001) Groundwater quality valuation and subjective risk perceptions: Georgia and Maine case study. In: Bergstrom JC, Boyle KJ, Poe LG (eds) Valuation of water quality. Edward Elgar Publisher, Brookfield

    Google Scholar 

  • Birol E, Koundouri P, Kountouris Y (2008) Applications of the choice experiment method in Europe: a review. In: Birol E, Koundouri P (eds) Choice experiments informing environmental policy: a European perspective. Edward-Elgar, Cheltenham, pp 12–57

    Chapter  Google Scholar 

  • Boxall PC, Adamowicz WL (1999) Understanding heterogeneous preferences in random utility models: the use of latent class analysis. University of Alberta, Department of Resource Economics and Environmental Sociology, Edmonton

    Google Scholar 

  • Boyle KJ, Poe GL, Bergstrom JC (1994) What do we know about groundwater values? Preliminary implications from a meta-analysis of contingent-valuation studies. Am J Agric Econ 76(5):1055–1061. doi:10.2307/1243391

    Article  Google Scholar 

  • Brander L, Florax R, Vermaat J (2006) The empirics of wetland valuation: a comprehensive summary and a meta-analysis of the literature. Environ Resou Econ 33(2):223–250. doi:10.1007/s10640-005-3104-4

    Article  Google Scholar 

  • Brauman KA, Daily GC, Duarte T, Mooney HA (2007) The nature and value of ecosystem services: an overview highlighting hydrologic services. Ann Rev Environ Resour 32(1):67–98. doi:10.1146/annurev.energy.32.031306.102758

    Article  Google Scholar 

  • Brouwer R, Langford IH, Bateman IJ, Turner RK (1999) A meta-analysis of wetland contingent valuation studies. Reg Environ Changes 1(1):47–57. doi:10.1007/s101130050007

    Article  Google Scholar 

  • Brouwer R, Hess S, Bevaart M, Meinardi K (2006) The socio-economic costs and benefits of environmental groundwater threshold values in the Scheldt basin in the Netherlands. BRIDGE Deliverable D26. 24 November 2006, Institute for Environmental Studies (IVM), Vrije Universiteit Amsterdam. Institute for Environmental Studies (IVM), Vrije Universiteit Amsterdam

  • Caudill JD (1992) The valuation of ground water pollution policies: the differential impacts of prevention and remediation. Michigan State University, East Lansing

    Google Scholar 

  • Costanza R, d’Arge R, de Groot R, Farber S, Grasso M, Hannon B, Limburg K, Naeem S, O’Neill RV, Paruelo J, Raskin RG, Sutton P, van den Belt M (1998) The value of the world’s ecosystem services and natural capital. Ecol Econ 25(1):3–15. doi:10.1016/S0921-8009(98)00020-2

    Article  Google Scholar 

  • Crutchfield SR, Cooper JC, Hellerstein D (1997) Benefits of safer drinking water: the value of nitrate reduction. Agricultural economic report no. 752. US Department of Agriculture. Washington DC

  • Davis J (2004) Assessing community preferences for development projects: are willingness-to-pay studies robust to mode effects? World Dev 32(4):655–672. doi:10.1016/j.worlddev.2003.09.007

    Article  Google Scholar 

  • De França DM (2010) Factors influencing public perception of drinking water quality. Water Policy 12(1):1–9. doi:10.2166/wp.2009.051

    Article  Google Scholar 

  • De Zoysa AD (1995) A benefit evaluation of programs to enhance groundwater quality, surface water quality and wetland habitat in northwest Ohio. Ph. D. Dissertation. The Ohio State University, Columbus

  • Edwards SF (1988) Option prices for groundwater protection. J Environ Econ Manag 15(4):475–487. doi:10.1016/0095-0696(88)90040-x

    Article  Google Scholar 

  • Epp DJ, Delavan W (2001) Measuring the value of protecting ground water quality from nitrate contamination in southeastern Pennsylvania. In: Bergstrom JC, Boyle KJ, Poe GL (eds) The economic value of water quality. Edward Elgar, Northampton

    Google Scholar 

  • European Commission (2008) Special eurobarometer 295/wave 68.2—attitudes of European citizens towards the environment. http://goo.gl/7iWPt. Accessed 23 Sept 2013

  • European Commission (2012) Flash eurobarometer 344—attitudes of European toward water-related issues. European Commission. http://goo.gl/UhreL. Accessed 23 Sept 2013

  • Farber SC, Costanza R, Wilson MA (2002) Economic and ecological concepts for valuing ecosystem services. Ecol Econ 41(3):375–392. doi:10.1016/S0921-8009(02)00088-5

    Article  Google Scholar 

  • Ferrini S, Scarpa R (2007) Designs with a priori information for nonmarket valuation with choice experiments: a Monte Carlo study. J Environ Econ Manag 53(3):342–363. doi:10.1016/j.jeem.2006.10.007

    Article  Google Scholar 

  • Ghermandi A, van den Bergh J, Brander LM, de Groot HL, Nunes P (2009) The values of natural and constructed wetlands: a meta-analysis. Tinbergen Institute discussion paper. Tinbergen Institute, Amsterdam

  • Görlach B, Interwies E (2003) Economic assessment of groundwater protection: a survey of the literature. ecologic. Institute for International and European Environmental Policy, Berlin

    Google Scholar 

  • Greene WH, Hensher DA (2003) A latent class model for discrete choice analysis: contrasts with mixed logit. Transp Res B Methodol 37(8):681–698. doi:10.1016/S0191-2615(02)00046-2

    Article  Google Scholar 

  • Hanley N (1989) Contingent valuation as a method for valuing charges in environmental service flow. University of Stirling, Department of Economics, Stirling

    Google Scholar 

  • Hanley N, MacMillan D, Wright RE, Bullock C, Simpson I, Parsisson D, Crabtree B (1998a) Contingent valuation versus choice experiments: estimating the benefits of environmentally sensitive areas in Scotland. J Agric Econ 49(1):1–15. doi:10.1111/j.1477-9552.1998.tb01248.x

    Article  Google Scholar 

  • Hanley N, Wright R, Adamowicz V (1998b) Using choice experiments to value the environment. Environ Resour Econ 11(3):413–428. doi:10.1023/A:1008287310583

    Article  Google Scholar 

  • Hasler B, Lundhede T, Martinsen L, Neye S, Schou JS (2005) Valuation of groundwater protection versus water treatment in Denmark by choice experiment and contingent valuation. NERI technical report. Ministry of the Environment. Denmark

  • Hensher DA (1994) Stated preference analysis of travel choices: the state of practice. Transportation 21(2):107–133. doi:10.1007/BF01098788

    Article  Google Scholar 

  • Hensher DA, Rose JM, Greene WH (2005) Applied choice analysis: a primer. Cambridge University Press, Cambridge

    Book  Google Scholar 

  • Holmes TP, Bergstrom JC, Huszar E, Kask SB, Orr Iii F (2004) Contingent valuation, net marginal benefits, and the scale of riparian ecosystem restoration. Ecol Econ 49(1):19–30. doi:10.1016/j.ecolecon.2003.10.015

    Article  Google Scholar 

  • Hoyos D (2010) The state of the art of environmental valuation with discrete choice experiments. Ecol Econ 69(8):1595–1603. doi:10.1016/j.ecolecon.2010.04.011

    Article  Google Scholar 

  • ISTAT (2011) Italian families average expenditures—data warehouse. Istituto nazionale di statistica. http://dati.istat.it/. Accessed 23 Sept 2013

  • Jordan JL, Elnagheeb AH (1993) Willingness to pay for improvements in drinking water quality. Water Resour Res 29(2):237–245. doi:10.1029/92wr02420

    Article  Google Scholar 

  • Lancaster KJ (1966) A new approach to consumer theory. J Political Econ 74(2):132. doi:10.1086/259131

    Article  Google Scholar 

  • Lieber RL (1990) Statistical significance and statistical power in hypothesis testing. J Orthop Res 8(2):304–309. doi:10.1002/jor.1100080221

    Article  CAS  Google Scholar 

  • Loomis J, Kent P, Strange L, Fausch K, Covich A (2000) Measuring the total economic value of restoring ecosystem services in an impaired river basin: results from a contingent valuation survey. Ecol Econ 33(1):103–117. doi:10.1016/s0921-8009(99)00131-7

    Article  Google Scholar 

  • Louviere JJ (1988a) Conjoint analysis modelling of stated preferences. A review of theory, methods, recent developments and external validity. J Transp Econ Policy 10:93–119

    Google Scholar 

  • Louviere JJ (1988b) Analyzing decision making: metric conjoint analysis. Sage Publications, Newbury Park

    Google Scholar 

  • Louviere JJ (1991) Experimental choice analysis: introduction and overview. J Bus Res 23(4):291–297. doi:10.1016/0148-2963(91)90015-P

    Article  Google Scholar 

  • Louviere JJ, Hensher DA (1982) Design and analysis of simulated choice or allocation experiments in travel choice modeling. Transp Res Rec 890:11–17

    Google Scholar 

  • Louviere JJ, Hensher DA, Swait JD (2000) Stated choice methods: analysis and applications. Cambridge University Press, Cambridge

    Book  Google Scholar 

  • Lusk JL, Norwood FB (2005) Effect of experimental design on choice-based conjoint valuation estimates. Am J Agric Econ 87(3):771–785. doi:10.1111/j.1467-8276.2005.00761.x

    Article  Google Scholar 

  • Lyttle-N’Guessan CJ (2003) An economic evaluation of nitrate in groundwater: a contingent valuation survey in Northwest Florida. MS Thesis, Florida A&M University, Tallahassee, FL

  • Manassaram DM, Backer LC, Moll DM (2007) A review of nitrates in drinking water: maternal exposure and adverse reproductive and developmental outcomes. Ciência Saúde Coletiva 12:153–163

    Article  Google Scholar 

  • Manski CF (1977) The structure of random utility models. Theory Decision 8(3):229–254

    Google Scholar 

  • Marangon F, Tempesta T (1999) Obiettivi pubblici e privati nella gestione delle aree protette. Il caso della Riserva Naturale delle « Cascate di Molina » (VR). Aestimum 38:107–133 (in Italian)

    Google Scholar 

  • Marangon F, Tempesta T (2004) L’inquinamento da atrazina delle acque sotterranee. Un confronto tra metodi alternativi per la stima monetaria del danno ambientale. Aestimum 44:1–24 (in Italian)

    Google Scholar 

  • Martin-Ortega J, Giannoccaro G, Berbel J (2011) Environmental and resource costs under water scarcity conditions: an estimation in the context of the European Water Framework Directive. Water Resour Manag 25(6):1615–1633. doi:10.1007/s11269-010-9764-z

    Article  Google Scholar 

  • McClelland GH, Schulze WD, Lazo JK, Waldman DW, Elliott SR, Irwin JR (1992) Methods for measuring non-use values: a contingent valuation study of ground water cleanup. Final Report, Office of Policy, Planning and Evaluation, U.S. Environmental Protection Agency, Cooperative Agreement #CR-815183

  • McFadden D (1974) Conditional logit analysis of qualitative choice behavior. In: Zarembka P (ed) Frontiers in econometrics. Academic Press, New York, pp 105–142

    Google Scholar 

  • McFadden D (1986) The choice theory approach to market research. Mark Sci 5(4):275–297. doi:10.1287/mksc.5.4.275

    Article  Google Scholar 

  • Millennium Ecosystem Assessment (2005) Ecosystem and human well-being: wetlands and water synthesis. World Resources Institute, Washington, DC

    Google Scholar 

  • Milon JW, Scrogin D (2006) Latent preferences and valuation of wetland ecosystem restoration. Ecol Econ 56(2):162–175. doi:10.1016/j.ecolecon.2005.01.009

    Article  Google Scholar 

  • Miraldo Ordens C, Bertin S, Brouwer R, Condesso Melo T (2006) The socio-economic costs and benefits of groundwater protection in the Aveiro Quaternary Aquifer in Portugal. BRIDGE Deliverable D28. 10 December 2006. Universidade de Aveiro, Portugal

  • Morrison M, Bennett J (2004) Valuing New South Wales rivers for use in benefit transfer. Aust J Agric Resour Econ 48(4):591–611. doi:10.1111/j.1467-8489.2004.00263.x

    Article  Google Scholar 

  • Ojeda MI, Mayer AS, Solomon BD (2008) Economic valuation of environmental services sustained by water flows in the Yaqui River Delta. Ecol Econ 65(1):155–166. doi:10.1016/j.ecolecon.2007.06.006

    Article  Google Scholar 

  • Pacifico D (2012) Fitting nonparametric mixed logit models via expectation-maximization algorithm. Stata J 12(2):284–298

    Google Scholar 

  • Pakalniete K, Strosser P, Bouscasse H (2006) Assessing the costs and benefits of groundwater quality improvement in and around Riga, Latvia. BRIDGE Deliverable D29. 10 December 2006, Acteon, France

  • Piva C (2011) Stima del carico di azoto e dei costi sostenuti per lo smaltimento dei reflui zootecnici da parte delle aziende agricole del territorio del Parco del Serio. Piacenza (in Italian)

  • Platt J (2001) Economic nonmarket valuation of instream flows. U.S. Department of Interior, Bureau of Reclamation

  • Poe GL, Bishop RC (1992) Measuring the benefits of groundwater protection from agricultural contamination: results from a two-stage contingent valuation study. Agricultural Economics Staff Paper, University of Wisconsin-Madison, USA

  • Poe GL, Boyle KJ, Bergstrom JC (2001) A preliminary meta analysis of contingent values for ground water quality revisited. In: Bergstrom JC, Boyle KJ, Poe GL (eds) The economic value of water quality. Edward Elgar, Northampton

    Google Scholar 

  • Powell JR (1991) The value of ground water protection: measurement of willingness-to-pay information, and its utilization by local government decision-makers. Cornell University, Ithaca

  • Press J, Söderqvist T (1998) On estimating the benefits of groundwater protection: a contingent valuation study in Milan. In: Swanson TM, Vighi M (eds) Regulating chemical accumulation in the environment: the integration of toxicology and economics in environmental policy-making. Cambridge University Press, New York, pp 121–182. doi:10.1017/CBO9780511535994

  • Rocchi L (2009) Choice experiments ed eterogeneità delle preferenze per i bacini ad uso plurimo: un’applicazione al lago di Montedoglio. Aestimum 54:69–85 (in Italian)

    Google Scholar 

  • Roeder K, Lynch KG, Nagin DS (1999) Modeling uncertainty in latent class membership: a case study in criminology. J Am Stat Assoc 94(447):766–776. doi:10.2307/2669989

    Article  Google Scholar 

  • Shultz SD, Lindsay BE (1990) The willingness to pay for groundwater protection. Water Resour Res 26(9):1869–1875. doi:10.1029/WR026i009p01869

    Article  Google Scholar 

  • Stampini M (1998) Il metodo delle valutazioni contingenti e la valutazione del danno ambientale: applicazione a un caso di inquinamento di acque pubbliche. Econ Pubblica 1:89–117 (in Italian)

    Google Scholar 

  • Stenger A, Willinger M (1998) Preservation value for groundwater quality in a large aquifer: a contingent-valuation study of the Alsatian aquifer. J Environ Manag 53(2):177–193. doi:10.1006/jema.1998.0197

    Article  Google Scholar 

  • Strosser P, Bouscasse H (2006) Assessing the socio-economic impacts of different groundwater protection regimes—Slovenian case study report. BRIDGE Deliverable D42, November 2006, ACTeon, France

  • Sun H, Bergstrom JC, Dorfman JH (1992) Estimating the benefits of groundwater contamination control. South J Agric Econ 24(2):63–71

    Google Scholar 

  • Swait J (1994) A structural equation model of latent segmentation and product choice for cross-sectional revealed preference choice data. J Retail Consum Serv 1(2):77–89. doi:10.1016/0969-6989(94)90002-7

    Article  Google Scholar 

  • Tempesta T, Vecchiato D (2013) An analysis of the territorial factors affecting milk purchase in Italy. Food Qual Prefer 27(1):35–43. doi:10.1016/j.foodqual.2012.06.005

    Article  Google Scholar 

  • Tentes G, Damigos D (2012) The lost value of groundwater: the case of Asopos river basin in central Greece. Water Resour Manag 26(1):147–164. doi:10.1007/s11269-011-9910-2

    Article  Google Scholar 

  • Thurstone LL (1927) A law of comparative judgement. Psychol Rev 34(4):273–286

    Article  Google Scholar 

  • Train K (2008) EM algorithms for nonparametric estimation of mixing distributions. J Choice Model 1(1):40–69

    Article  Google Scholar 

  • Train K (2009) Discrete choice methods with simulation, 2nd edn. Cambridge University Press, Cambridge

    Book  Google Scholar 

  • Travisi CM, Nijkamp P (2008) Valuing environmental and health risk in agriculture: a choice experiment approach to pesticides in Italy. Ecol Econ 67(4):598–607. doi:10.1016/j.ecolecon.2008.01.011

    Article  Google Scholar 

  • Turner K, Georgiou S, Clark R, Brouwer R (2004) Economic valuation of water resources in agriculture. From the sectoral to a functional perspective of natural resource management. Water report no 27. FAO, Rome

  • van Grinsven H, Ward M, Benjamin N, de Kok T (2006) Does the evidence about health risks associated with nitrate ingestion warrant an increase of the nitrate standard for drinking water? Environ Health 5(1):26

    Article  Google Scholar 

  • Van Houtven G, Powers J, Pattanayak SK (2007) Valuing water quality improvements in the United States using meta-analysis: is the glass half-full or half-empty for national policy analysis? Resour Energy Econ 29(3):206–228

    Article  Google Scholar 

  • van Kooten GC, Athwal R, Arthur LM (1998) Use of public perceptions of groundwater quality benefits in developing livestock management options. Can J Agric Econ/Revue canadienne d’agroeconomie 46(3):273–285. doi:10.1111/j.1744-7976.1998.tb00085.x

    Article  Google Scholar 

  • Visintin F, Marangon F (2007) Economic and touristic aspects of Isonzo River Mouth Regional Natural Reserve. In: Guidelines and case studies for the management of Natura 2000 sites in transitional environments: proceedings of the workshop held in Grado, Palazzo dei congressi, 7–8 June 2006, Trieste, EUT Edizioni Università di Trieste, 2007, pp 425–429. http://hdl.handle.net/10077/6270. Accessed 27 Aug 2013

  • Willis KG, Garrod GD (1999) Angling and recreation values of low-flow alleviation in rivers. J Environ Manag 57(2):71–83. doi:10.1006/jema.1999.0292

    Article  Google Scholar 

  • Woodward RT, Wui Y-S (2001) The economic value of wetland services: a meta-analysis. Ecol Econ 37(2):257–270. doi:10.1016/s0921-8009(00)00276-7

    Article  Google Scholar 

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Acknowledgments

This study has been financed by the Cariplo Foundation (“Fondazione Cariplo”—http://www.fondazionecariplo.it/) as part of the project “Water quality protection” (“Tutelare la qualità delle acque”) 2009 edition. The project has been coordinated by Azienda Sperimentale Vittorio Tadini and realized in conjunction with Consorzio Regionale Parco del Serio, Dipartimento TESAF—Università degli Studi di Padova and Agrisilva Scrl (Piacenza). The authors are grateful to three anonymous reviewers for their constructive comments and suggestions. All errors and omissions are the responsibility of the authors alone.

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Appendix: Choice Experiment Introduction

Appendix: Choice Experiment Introduction

Interventions for the Improvement of Water Body Quality and of the Rural Environment

The Regione Lombardia is willing to establish practices to improve water and environmental quality in rural areas. These interventions will be related to

  1. 1.

    The quality of the river ecosystem.

  2. 2.

    Groundwater quality.

  3. 3.

    Re-afforestation and rural hedge planting.

Before starting these policies, the Regione would like to know the opinion of its citizens with regard to the type of interventions that should be realized and the costs that could be supported by the population.

For each of the above objectives, the following alternatives are considered:

Quality of the River Ecosystem

  1. (a)

    Guarantee of a minimum instream flow of 20 % in every water body (river). This would insure good conservation of the river fauna (e.g., good presence of fish) and water quality. Keeping such an objective would imply quite high costs given that some economic activities would have to considerably reduce water withdrawal in some periods of the year.

  2. (b)

    Guarantee of a minimum instream flow of 10 % in every water body (river). This would imply some conservation of the river fauna (e.g., presence of fish) and water quality. Keeping such an objective would imply lower costs than the previous case (20 % minimum instream flow).

  3. (c)

    Maintain the current situation without any maintenance of minimum instream flow in rivers so that in certain periods, drought could threaten the flora and fauna. This choice would not imply any damage to the economic activities that rely on the river water for production.

Quality of Groundwater

  1. (a)

    The presence of nitrates in groundwater at a concentration lower than 10 mg/l. This would insure the maximum level of water quality, making tap water drinkable for all without restrictions for babies. To achieve this target, very high constraints on agricultural activities and zootechnology are necessary, meaning a consistent increase in production costs. It will be necessary to give high compensation to the farmers to avoid discontinuation of their activities. If farmers were to discontinue their activity, the majority of milk consumed would have to be imported.

  2. (b)

    The presence of nitrates in groundwater at a concentration between 10 and 50 mg/l. This concentration of nitrates would make water drinkable, but with precautions for babies. The constraints for farmers would be less and therefore the compensation for their business losses lower.

  3. (c)

    The presence of nitrates in groundwater which is not guaranteed and could be higher than 50 mg/l. In this scenario, the water taken directly from artesian wells would not be suitable for drinking and cooking purposes or it should be necessary to bear high depuration costs before introducing water in aqueducts. This policy standard does not imply costs for farmers’ compensation.

Re-afforestation and Rural Hedge Planting

  1. (a)

    A 10 % increase in the extent of countryside hedges. This would imply a substantial improvement of the landscape quality, the environment, and the fauna, but at the cost of high subsidies to farmers.

  2. (b)

    A 5 % increase in the extent of countryside hedges. This would imply a fair (discrete) improvement of the landscape quality, the environment, and the fauna, and the cost of subsidies to farmers would be lower.

  3. (c)

    No intervention.

Given the actual economic situation, all costs of the proposed policies would be paid in the form of a new yearly tax for every family in the interested territory.

We will now show you some alternative hypotheses of intervention, characterized by different levels of achievable environmental quality and their cost.

We ask you to indicate which, among each of the following sets of alternatives, is your preferred solution.

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Tempesta, T., Vecchiato, D. Riverscape and Groundwater Preservation: A Choice Experiment. Environmental Management 52, 1487–1502 (2013). https://doi.org/10.1007/s00267-013-0163-0

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