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Applying Benefit Transfer with Limited Data: Unit Value Transfers in Practice

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Book cover Benefit Transfer of Environmental and Resource Values

Part of the book series: The Economics of Non-Market Goods and Resources ((ENGO,volume 14))

Abstract

Unit value or point value transfers from individual source studies remain the oldest and most common form of benefit transfer. Although practitioners generally recommend benefit function transfers , these are not always possible. Where unit value transfers are to be performed, appropriate protocols must be followed to select source studies, transfer values, and perform necessary value adjustments. This chapter demonstrates the processes and challenges involved in the implementation of unit value transfers , using case studies of environmental values in a peri-urban community on the east coast of Australia where key ecosystems ranged from coastal beaches to inland forests . Key issues in evaluating the potential for benefit transfer included the availability and quality of source studies, the extent of overlap between source studies and the target site, the need for different forms of adjustment to account for variations in scope and scale, and the limitations to unit value transfers.

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Notes

  1. 1.

    Although sometimes values from several source studies are assessed before choosing a single unit value for transfer. Unit value transfers may also transfer a mean or median value from prior studies.

  2. 2.

    They note that value functions explicitly incorporate differences between sites and hence are appropriate where differences between source and target sites are involved, but may be over-parameterized when limited differences between sites exist.

  3. 3.

    See discussions of commodity consistency in Johnston and Rosenberger (2010).

  4. 4.

    This is related to the concept of the economic jurisdiction, or the size of the population that holds value for a given environmental change (Loomis 2000).

  5. 5.

    Note: in this chapter all dollar values refer to Australian dollars.

  6. 6.

    Choice modelling is a stated preference technique capable of estimating both use and nonuse values (Bateman et al. 2002; Rolfe and Bennett 2006).

  7. 7.

    Both Mallawaarachchi et al. (2001) and Morrison and Bennett (2004) included a wetlands attribute in their choice modelling studies, but in both cases riparian vegetation was also included in the description, making it unsuitable to transfer to the target site.

  8. 8.

    The higher value for study WW9 might be a reflection of the peri-urban context and/or higher values to avoid a loss than for a gain.

  9. 9.

    Note that the use of meta-analysis in this way is generally considered a type of benefit function transfer.

  10. 10.

    In the source study, the status quo was set as a future base, with a lower level of provision than the current situation. All alternative levels represented an improvement on the future base, but were lower than the current level. Consequently, it is not clear if respondents were indicating their WTP to avoid a loss or achieve a gain.

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Rolfe, J., Windle, J., Johnston, R.J. (2015). Applying Benefit Transfer with Limited Data: Unit Value Transfers in Practice. In: Johnston, R., Rolfe, J., Rosenberger, R., Brouwer, R. (eds) Benefit Transfer of Environmental and Resource Values. The Economics of Non-Market Goods and Resources, vol 14. Springer, Dordrecht. https://doi.org/10.1007/978-94-017-9930-0_8

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