Public Perspective on Increasing the Numbers of an Endangered Species, Loggerhead Turtles in South Korea: A Contingent Valuation
Abstract
:1. Introduction
2. Materials and Methods
2.1. Method: CV Technique
2.2. Survey Questionnaire and Field Survey
2.3. How to Elicit WTP Responses
- (i)
- If the response is “no,” ;
- (ii)
- If the response is “yes–no,” ;
- (iii)
- If the response is “yes–yes,” .
- (iv)
- If the response is “no–no,” ;
- (v)
- If the response is “no–yes,” ;
- (vi)
- If the response is “yes,” .
2.4. Econometric Model for Analyzing the WTP Responses
- (i)
- If the response is “no–no,” WTP = 0;
- (ii)
- If the response is “no–yes,” 0 < WTP ≤ ;
- (iii)
- If the response is “yes–no,” < WTP ≤ ;
- (iv)
- If the response is “yes–yes,” < WTP.
- (v)
- If the response is “no–no–no,” WTP = 0;
- (vi)
- If the response is “no–no–yes,” 0 < WTP ≤ ;
- (vii)
- If the response is “no–yes,” < WTP ≤ ;
- (viii)
- If the response is “yes,” < WTP.
2.5. Data
- First, the sample size was set at 1000. This was because Arrow et al. [34] proposed 1000 as the number of observations needed for policy decision-making, and the Korean Ministry of Strategy and Finance and the Korea Development Institute, a government-run think tank, have also provided a guideline on the size of a nationwide sample needed for policy decision-making as 1000.
- Second, we tried to make certain the representativeness of the sample by implementing sampling based on the census data gathered in 2015 by Statistics Korea. As individual estimates of mean WTP have been derived, we could estimate aggregate benefits, which Arrow et al. [33] identified as one of the significant issues in using CV results. When expanding the sample to the population, one critical concern is the representativeness of the sample. In this regard, a comparison of the characteristics of the sample with those of the population is reported in Table 2. It can be seen that there was not much difference between the values for the sample and those for the population.
- Third, a professional polling firm was commissioned to conduct the CV survey to ensure fairness in sampling and implementing face-to-face surveys, despite its high cost.
- Fourth, we chose the yearly income tax as a payment vehicle to help respondents reveal their actual WTP without difficulty. In addition, the payment period presented in the CV survey was 10 years.
3. Results
3.1. Estimation Results
3.2. Discussion of the Results
4. Conclusions
Author Contributions
Funding
Conflicts of Interest
References
- Korea Ministry of Oceans and Fisheries. Conservation and Management of Marine Ecosystems Act. Available online: http://www.mof.go.kr/eng/index.do (accessed on 3 February 2020).
- International Union for Conservation of Nature. IUCN Red List of Threatened Species. Available online: https://www.iucnredlist.org/ (accessed on 3 February 2020).
- Convention on International Trade in Endangered Species of Wild Fauna and Flora. The CITES Species. Available online: https://www.cites.org/eng/disc/species.php (accessed on 3 February 2020).
- Korea Marine Environment Management Corporation. Species Increase and Restoration of Marine Endangered Species; Korea Marine Environment Management Corporation: Seoul, Korea, 2014. (In Korean) [Google Scholar]
- Mazaris, A.D.; Matsinos, G.; Pantis, J.D. Evaluating the impacts of coastal squeeze on sea turtle nesting. Ocean Coast. Manag. 2009, 52, 139–145. [Google Scholar] [CrossRef]
- Lutcavage, M.E. Human impacts on sea turtle survival. In The Biology of Sea Turtles; CRC Press: Boca Raton, FL, USA, 2017; Volume 1, pp. 387–409. [Google Scholar]
- Lovich, J.E.; Ennen, J.R.; Agha, M.; Gibbons, J.W. Where have all the turtles gone, and why does it matter? BioScience 2018, 68, 771–781. [Google Scholar] [CrossRef] [Green Version]
- Yoo, S.-H.; Kwak, S.-J. Using a spike model to deal with zero response data from double bounded dichotomous contingent valuation survey. Appl. Econ. Lett. 2002, 9, 929–932. [Google Scholar] [CrossRef]
- Kriström, B. Spike models in contingent valuation. Am. J. Agric. Econ. 1997, 79, 1013–1023. [Google Scholar] [CrossRef]
- Samples, K.C.; Hollyer, J.R. Contingent valuation of wildlife resources in the presence of substitutes and complements. In Economic Valuation of Natural Resources: Issues, Theory and Application, 1st ed.; Johnson, R.L., Johnson, V.G., Eds.; Westview Press: Boulder, CO, USA, 1989; pp. 177–192. [Google Scholar]
- Whitehead, J. Ex ante willingness to pay with supply and demand uncertainty: Implications for valuing a sea turtle protection program. Appl. Econ. 1992, 24, 981–988. [Google Scholar] [CrossRef]
- Loomis, J.B.; Larson, D. Total economic values of increasing gray whale populations: Results from a contingent valuation survey of visitors and households. Mar. Resour. Econ. 1994, 9, 275–286. [Google Scholar] [CrossRef]
- Giraud, K.; Turcin, B.; Loomis, J.; Cooper, J. Economic benefit of the protection program for the Steller sea lion. Mar. Policy 2002, 26, 451–458. [Google Scholar] [CrossRef]
- Jin, J.; Indab, A.; Nabangchang, O.; Thuy, T.D.; Harder, D.; Subade, R.F. Valuing marine turtle conservation: A cross-country study in Asian cities. Ecol. Econ. 2010, 69, 2020–2026. [Google Scholar] [CrossRef]
- Boxall, P.C.; Adamowicz, W.L.; Olar, M.; West, G.E.; Cantin, G. Analysis of the economic benefits associated with the recovery of threatened marine mammal species in the Canadian St. Lawrence Estuary. Marine Policy 2012, 36, 189–197. [Google Scholar] [CrossRef]
- Lim, S.Y.; Jin, S.J.; Yoo, S.H. The economic benefits of the Dokdo Seals restoration project in Korea: A contingent valuation study. Sustainability 2017, 9, 968. [Google Scholar] [CrossRef] [Green Version]
- Cazabon-Mannette, M.; Schuhmann, P.W.; Hailey, A.; Horrocks, J. Estimates of the non-market value of sea turtles in Tobago using stated preference techniques. J. Environ. Manag. 2017, 192, 281–291. [Google Scholar] [CrossRef] [PubMed]
- Habb, T.C.; McConnell, K.E. Valuing Environmental and Natural Resources; Edward Elgar: Cheltenham, UK, 2002. [Google Scholar]
- Brent, R.J. Applied Cost-Benefit Analysis, 2nd ed.; Edward Elgar: Cheltenham, UK, 2006. [Google Scholar]
- Varian, H.R. Intermediate Microeconomics: A Modern Approach, 9th ed.; W. W. Norton & Company: New York, NY, USA, 2014. [Google Scholar]
- Freeman III, A.M.; Herriges, J.A.; Kling, C.L. The Measurement of Environmental and Resource Values: Theory and Methods, 3rd ed.; Routledge: New York, NY, USA, 2014. [Google Scholar]
- Garrod, G.; Willis, K.G. Economic Valuation of the Environment; Edward Elgar: Cheltenham, UK, 1999. [Google Scholar]
- Mitchell, R.C.; Carson, R.T. Using Surveys to Value Public Goods: The Contingent Valuation Method; Resources for the Future: Washington, DC, USA, 1989. [Google Scholar]
- Kim, J.H.; Kim, H.J.; Yoo, S.H. Willingness to pay for fuel-cell electric vehicles in South Korea. Energy 2019, 174, 497–502. [Google Scholar] [CrossRef]
- Lim, S.Y.; Kim, H.J.; Yoo, S.H. Assessing the external benefits of contaminated soil remediation in Korea: A choice experiment study. Environ. Sci. Pollut. Res. 2018, 25, 17216–17222. [Google Scholar] [CrossRef] [PubMed]
- Kim, J.H.; Yoo, S.H. South Koreans’ perspective on assisting the power supply to North Korea: Evidence from a contingent valuation. Energy Policy 2020, 139, 111336. [Google Scholar] [CrossRef]
- Rodella, I.; Madau, F.A.; Carboni, D. The willingness to pay for beach scenery and its preservation in Italy. Sustainability 2020, 12, 1604. [Google Scholar] [CrossRef] [Green Version]
- Bamwesigye, D.; Hlavackova, P.; Sujova, A.; Fialova, J.; Kupec, P. Willingness to pay for forest existence value and sustainability. Sustainability 2020, 12, 891. [Google Scholar] [CrossRef] [Green Version]
- Just, R.E.; Hueth, D.L.; Schmitz, A. The Welfare Economics of Public Policy: A Practical Approach to Project and Policy Evaluation; Edward Elgar: Cheltenham, UK, 2004. [Google Scholar]
- Venkatachalam, L. The contingent valuation method: A review. Environ. Impact Assess. Rev. 2004, 24, 89–124. [Google Scholar] [CrossRef]
- Carson, R.T.; Hanemann, W.M. Contingent valuation. In Handbook of Environmental Economics: Valuing Environmental Changes; Maler, K.G., Vincent, J.R., Eds.; Elsevier: Amsterdam, The Netherlands, 2005; Volume 2, pp. 821–936. [Google Scholar]
- Bigerna, S.; Polinori, P. The Economic Valuation of Green Electricity; Springer: Dordrecht, The Netherlands, 2018. [Google Scholar]
- Fisher, A. The Conceptual Underpinnings of the Contingent Valuation Method. In The Contingent Valuation of Environmental Resources; Bjornstad, D.J., Kahn, J.R., Eds.; Edward Elgar: Cheltenham, UK, 1996; pp. 19–37. [Google Scholar]
- Arrow, K.; Solow, R.; Portney, P.R.; Leamer, E.E.; Radner, R.; Schuman, H. Report of the NOAA panel on contingent valuation. Fed. Regist. 1993, 58, 4601–4614. [Google Scholar]
- Johnston, R.J.; Boyle, K.J.; Adamowicz, W.; Bennett, J.; Brouwer, R.; Cameron, T.A.; Hanemann, W.M.; Hanley, N.; Ryan, M.; Scarpa, R.; et al. Contemporary guidance for stated preference studies. J. Assoc. Environ. Resour. Econ. 2017, 4, 319–405. [Google Scholar] [CrossRef] [Green Version]
- Hanemann, W.; Kanninen, B. The statistical analysis of discrete-response CV data. In Valuing Environmental Preferences: Theory and Practice of the Contingent Valuation Method in the US, EC and Developing Countries; Bateman, J., Willis, K.G., Eds.; Oxford University Press: Oxford, UK, 1996. [Google Scholar]
- Hanemann, W.M. Welfare evaluations in contingent valuation experiments with discrete responses. Am. J. Agric. Econ. 1984, 66, 332–341. [Google Scholar] [CrossRef]
- Hanemann, M.; Loomis, J.; Kanninen, B. Statistical efficiency of double-bounded dichotomous choice contingent valuation. Am. J. Agric. Econ. 1991, 73, 1255–1263. [Google Scholar] [CrossRef]
- Cooper, J.C.; Hanemann, M.; Signorello, G. One-and-one-half bound dichotomous choice contingent valuation. Rev. Econ. Stat. 2002, 84, 742–750. [Google Scholar] [CrossRef] [Green Version]
- McFadden, D. Contingent valuation and social choice. Am. J. Agric. Econ. 1994, 76, 689–708. [Google Scholar] [CrossRef]
- Cooper, J.C.; Hanemann, W.M. Referendum Contingent Valuation: How Many Bounds are Enough? Working Paper; USDA Economic Research Search Service, Food and Consumer Economics Division: Washington, DC, USA, 1995. [Google Scholar]
- Krinsky, I.; Robb, A.L. On approximating the statistical properties of elasticities. Rev. Econ. Stat. 1986, 68, 715–719. [Google Scholar] [CrossRef] [Green Version]
- Statistics Korea. Korea Statistical Information Service. Available online: http://kosis.kr (accessed on 5 February 2020).
- Kim, J.; Lim, S.Y.; Yoo, S.H. Measuring the economic benefits of designating Baegnyeong Island in Korea as a marine protected area. Int. J. Sustain. Dev. World Ecol. 2017, 24, 205–213. [Google Scholar] [CrossRef]
- Lee, M.K.; Kim, J.H.; Yoo, S.H. Public willingness to pay for increasing photovoltaic power generation in Korea. Sustainability 2018, 10, 1196. [Google Scholar] [CrossRef] [Green Version]
- Jorgensen, B.; Syme, G.; Bishop, B.; Nancarrow, B. Protest responses in contingent valuation. Environ. Resour. Econ. 1999, 14, 131–150. [Google Scholar] [CrossRef]
- Pennington, M.; Gomes, M.; Donaldson, C. Handling protest responses in contingent valuation surveys. Med Decis. Mak. 2017, 37, 623–634. [Google Scholar] [CrossRef]
Sources | Object to Be Valued | Countries | Main Results | Method a |
---|---|---|---|---|
Samples and Hollyer [10] | Humpback whale | United States | USD 239.53 per household for avoiding the loss of humpback whales | CV |
Samples and Hollyer [10] | Monk seal | United States | USD 165.80 per household for preserving the population of monk seals | CV |
Whitehead [11] | Loggerhead turtle | United States | Overall, 32% of the respondents had willingness to pay for the loggerhead turtle protection program | CV |
Loomis and Larson [12] | Gray whale | United States | USD 23.65 and 26.53 per household for 50% and 100% increases in whale populations | CV |
Giraud et al. [13] | Steller sea lion | United States | USD 100.22 per household for an expanded federal protection program for the Steller sea lion | CV |
Jin et al. [14] | Marine turtle | China, The Philippines, Thailand, Vietnam | USD 0.96 to 1.44 per household for marine turtle conservation | CV |
Boxall et al. [15] | Marine mammal species b | Canada | USD 77 to 229 per household for recovering the populations of three marine mammal species | CV and CE |
Lim et al. [16] | Dokdo seal | South Korea | USD 4.86 per household for implementation of the Dokdo seal restoration project | CV |
Cazabon-Mannette et al. [17] | Sea turtles | Tobago | USD 28.14 to 31.13 per visitor for conserving the sea turtles in Tobago | CV |
Variables | Sample a | Population b |
---|---|---|
Gender | ||
Female | 50.0% | 49.9% |
Male | 50.0% | 50.1% |
Region | ||
Seoul | 19.8% | 19.1% |
Pusan | 6.8% | 6.7% |
Daegu | 4.7% | 4.8% |
Incheon | 5.5% | 5.7% |
Gwangju | 2.8% | 2.9% |
Daejeon | 2.8% | 3.0% |
Ulsan | 2.1% | 2.3% |
Sejong | 0.4% | 0.5% |
Gyunggi | 23.4% | 24.7% |
Gangwon | 3.3% | 3.0% |
Chungbuk | 3.2% | 3.1% |
Chungnam | 4.2% | 4.2% |
Jeonbuk | 3.7% | 3.6% |
Jeonnam | 4.0% | 3.5% |
Gyungbuk | 5.6% | 5.2% |
Gyungnam | 6.5% | 6.5% |
Jeju | 1.2% | 1.2% |
Household income c | KRW 4.33 million | KRW 4.42 million |
Lower Bid Is Given First (%) b | Higher Bid Is Given First (%) b | |||||||||
---|---|---|---|---|---|---|---|---|---|---|
Bid Amount a | “yes-yes” | “yes-no” | “no-yes” | “no-no” | “yes” | “no-yes” | “no-no-yes” | “no-no-no” | Sample Size | |
1000 | 3000 | 9(6.3) | 19(13.3) | 5(3.5) | 39(27.3) | 31(21.7) | 15(10.5) | 5(3.5) | 20(14.0) | 143(100.0) |
2000 | 4000 | 6(4.2) | 8(5.6) | 10(7) | 47(32.9) | 10(7) | 6(4.2) | 5(3.5) | 51(35.7) | 143(100.0) |
3000 | 6000 | 11(7.7) | 10(6.9) | 5(3.5) | 45(31.5) | 11(7.7) | 8(5.6) | 11(7.7) | 42(29.4) | 143(100.0) |
4000 | 8000 | 5(3.5) | 13(9.1) | 10(7) | 44(30.8) | 13(9.1) | 11(7.7) | 6(4.2) | 41(28.7) | 143(100.0) |
6000 | 10,000 | 2(1.4) | 11(7.7) | 12(8.5) | 46(32.4) | 8(5.6) | 9(6.3) | 8(5.6) | 46(32.4) | 142(100.0) |
8000 | 12,000 | 3(2.1) | 9(6.3) | 16(11.3) | 43(30.3) | 1(0.7) | 6(4.2) | 17(12) | 47(33.1) | 142(100.0) |
10,000 | 15,000 | 1(0.7) | 6(4.2) | 18(12.5) | 47(32.6) | 5(3.5) | 5(3.5) | 19(13.2) | 43(29.9) | 144(100.0) |
Totals | 37(3.7) | 76(7.6) | 76(7.6) | 311(31.1) | 66(6.6) | 59(5.9) | 68(6.8) | 307(30.7) | 1000(100.0) |
Variables | Coefficient Estimates (t-Values) |
---|---|
Constant | −0.4751 (−7.35) # |
Bid amount a | −0.2049 (−17.33) # |
Spike | 0.6166 (40.37) # |
Mean additional willingness to pay per household per year t-value 95% confidence interval b 99% confidence interval b | KRW 2360 (USD 1.99) 14.69 # KRW 2066 to 2710 (USD 1.74 to 2.29) KRW 1992 to 2834 (USD 1.68 to 2.39) |
Number of observations Log-likelihood Wald statistic (p-value) b | 1,000 −1075.10 432.76 (0.000) |
Variables | Definitions | Mean | Standard Deviation |
---|---|---|---|
Gender | Interviewee’s gender (0 = male; 1 = female) | 0.50 | 0.50 |
Education | Interviewee’s education level in years | 14.01 | 2.42 |
Income | Interviewee’s households’ income per month (units: million Korean won) | 4.33 | 1.82 |
Variables a | Coefficient Estimates (t-Values) |
---|---|
Constant | −2.9831 (−6.95) # |
Bid amount b | −0.2106 (−18.02) # |
Gender Education Income Spike | 0.2575 (1.98) # 0.1342 (4.59) # 0.1094 (3.04) # 0.6227 (39.81) # |
Mean additional willingness to pay per household per year t-value 95% confidence interval c 99% confidence interval c | KRW 2249 (USD 1.90) 14.84 # KRW 1985 to 2570 (USD 1.68 to 2.17) KRW 1909 to 2695 (USD 1.61 to 2.27) |
Number of observations Log-likelihood Wald statistic (p-value) d | 1,000 −1053.21 220.13 (0.000) |
Estimates | 95% Confidence Intervals | |
---|---|---|
Mean additional WTP per household per year | KRW 2360 (USD 1.99) | KRW 2066 to,710 (USD 1.74 to 2.29) |
Total annual WTP | KRW 44.72 billion (USD 37.74 million) | KRW 39.15 to 51.35 billion (USD 33.04 to 43.33 million) |
© 2020 by the authors. Licensee MDPI, Basel, Switzerland. This article is an open access article distributed under the terms and conditions of the Creative Commons Attribution (CC BY) license (http://creativecommons.org/licenses/by/4.0/).
Share and Cite
Kim, J.-H.; Choi, K.-R.; Yoo, S.-H. Public Perspective on Increasing the Numbers of an Endangered Species, Loggerhead Turtles in South Korea: A Contingent Valuation. Sustainability 2020, 12, 3835. https://doi.org/10.3390/su12093835
Kim J-H, Choi K-R, Yoo S-H. Public Perspective on Increasing the Numbers of an Endangered Species, Loggerhead Turtles in South Korea: A Contingent Valuation. Sustainability. 2020; 12(9):3835. https://doi.org/10.3390/su12093835
Chicago/Turabian StyleKim, Ju-Hee, Kyung-Ran Choi, and Seung-Hoon Yoo. 2020. "Public Perspective on Increasing the Numbers of an Endangered Species, Loggerhead Turtles in South Korea: A Contingent Valuation" Sustainability 12, no. 9: 3835. https://doi.org/10.3390/su12093835
APA StyleKim, J. -H., Choi, K. -R., & Yoo, S. -H. (2020). Public Perspective on Increasing the Numbers of an Endangered Species, Loggerhead Turtles in South Korea: A Contingent Valuation. Sustainability, 12(9), 3835. https://doi.org/10.3390/su12093835