1 / 19

Luke Brander Institute for Environmental Studies (IVM), VU University Amsterdam

Luke Brander Institute for Environmental Studies (IVM), VU University Amsterdam Division of Environment, Hong Kong University of Science and Technology Email: lukebrander@gmail.com. Scaling up ecosystem service values: methodology and applications. II – Value of changes in water quality.

devin
Download Presentation

Luke Brander Institute for Environmental Studies (IVM), VU University Amsterdam

An Image/Link below is provided (as is) to download presentation Download Policy: Content on the Website is provided to you AS IS for your information and personal use and may not be sold / licensed / shared on other websites without getting consent from its author. Content is provided to you AS IS for your information and personal use only. Download presentation by click this link. While downloading, if for some reason you are not able to download a presentation, the publisher may have deleted the file from their server. During download, if you can't get a presentation, the file might be deleted by the publisher.

E N D

Presentation Transcript


  1. Luke Brander Institute for Environmental Studies (IVM), VU University Amsterdam Division of Environment, Hong Kong University of Science and Technology Email: lukebrander@gmail.com Scaling up ecosystem service values: methodology and applications. II – Value of changes in water quality Co-authors: Roy Brouwer, Tjasa Bole, Dolf de Groot, Salman Hussain, Onno Kuik, Alistair McVittie, Sander van der Ploeg, Peter Verburg, Alfred Wagtendonk

  2. Outline • Introduction • Methodology: meta-analysis and GIS • Water quality value data • Water quality value function • TEEB case study: global value of water quality changes • Conclusions and discussion

  3. Introduction • Need for value information at large spatial scales (e.g. river basin) • CBA of investments in water quality improvements • Assess disproportionate costs • Value of water quality improvements varies with body body, context and beneficiary characteristics

  4. Proposed method for scaling up values • Construct database of primary value estimates • Estimate a meta-analytic value function (including water abundance variable) • Construct database of water bodies using GIS • Estimate site-specific values for changes in water quality • Aggregate across relevant population and spatial level Meta- analysis Spatial Data (GIS) Estimate values

  5. Valuation of changes in water quality $/annum Change in value P1 Marginal value curve P0 Q1 Q0 Water quality

  6. Water quality value data • AquaMoney database of water quality values • 154 contingent valuation studies (1981 – 2006) • 54 with complete information for meta-analysis • 388 value estimates • Wide variety of descriptions of water quality change standardised to 10-point water quality index • Standardised values to WTP/household/year (USD 2007 prices) • Mean = 130 USD/household/year • Median = 78 USD/household/year

  7. Location of water quality value study sites

  8. Ecosystem services valued

  9. Meta-analytic value function • Dependent variable y: Annual WTP per household (USD 2007) • Study characteristics Xsi: • Valuation method • Water characteristics Xwi: • Baseline water quality • Change in water quality • Water body type • Context characteristics Xci: • GCP per capita • Abundance of lakes and rivers within 10km radius • Accessibility index • Urban extent within 20km radius

  10. Meta-analytic value function

  11. TEEB case study: global value of water quality change • TEEB Quantitative Assessment • Change in water quality 2000 - 2050 • OECD baseline scenario of population and development • IMAGE/GLOBIO model • Global coverage at 50km grid cell resolution • Nitrogen and phosphorous concentrations • Converted to 10-point water quality index • Large variation in positive and negative changes in water quality

  12. Changes in water quality 2000-2050

  13. Changes in water quality 2000 - 2050 • Water quality changes combined with global map of lakes and rivers • Global lakes and wetlands database GLWD (1x1km grid) • 375,316 water bodies (lakes and rivers) • Site specific characteristics are substituted into value function • Household WTP is aggregated across number of households in 50km grid cell

  14. Annual values in 2050 (billions USD 2007)

  15. Discussion and conclusions • Value transfer on a large scale • GIS to account for spatial variation • Scale, substitutes, and income effects • Limitations: • Does not produce service specific values • Partial valuation: value data is focussed on recreational uses • Partly accounts for changes in water quantity • Restricted measure of water quality • Difficult to identify relevant population for aggregation

More Related