Regression modelEnvironmental EconomicsEnvironmental / non-market valuationModel

Ecosystem-Service Choice Experiment

Also known as: Discrete Choice Experiment for Ecosystem Services, Stated-Preference Choice Modelling, Attribute-Based Environmental Valuation, Choice Modelling of Ecosystem Services

OriginatorNick Hanley, Robert E. Wright & Vic AdamowiczYear1998Sources1Related methods5

A discrete choice experiment is a survey-based, stated-preference method for valuing changes in ecosystem services that have no market price. As set out by Hanley, Wright and Adamowicz in 1998, respondents are shown a series of choice sets, each offering alternatives described by a common set of attributes — including environmental features such as water quality, biodiversity, or habitat area, and a cost or price attribute — and asked to pick their preferred option. Grounded in random utility theory and Lancaster's view of goods as bundles of attributes, the method models each choice as the selection of the highest-utility alternative and estimates how much utility each attribute contributes. Dividing an attribute's coefficient by the cost coefficient yields the marginal willingness to pay for that attribute, allowing economists to put a monetary value on ecosystem-service improvements.

Key highlights

  • Recovers an implicit price for each environmental attribute, valuing multiple marginal changes simultaneously rather than one bundled good.
  • Grounded in random utility theory, so estimates link directly to welfare measures usable in cost-benefit analysis.
  • Captures non-use and existence values that revealed-preference methods cannot reach, broadening the scope of valuation.
  • Flexible design supports policy-relevant scenarios and, with mixed logit, accommodates preference heterogeneity across respondents.

Intuition

This section is available to Pro members. Upgrade to Pro

How it works

This section is available to Pro members. Upgrade to Pro

When to use it

Use an ecosystem-service choice experiment when you need monetary values for non-marketed environmental goods whose change can be described by a manageable set of attributes, and when you want implicit prices for each attribute rather than a single bundled value. It is well suited to policy questions involving trade-offs — how much water-quality improvement, habitat, or biodiversity people will pay for — and to designs that must value multiple, marginal changes at once. It is less appropriate when the good cannot be sensibly decomposed into attributes, when respondents cannot meaningfully imagine the scenarios, or when use values dominate and revealed-preference methods such as travel cost are available. Like all stated-preference methods, it requires careful design to mitigate hypothetical and strategic bias.

Strengths & limitations

Strengths
  • Recovers an implicit price for each environmental attribute, valuing multiple marginal changes simultaneously rather than one bundled good.
  • Grounded in random utility theory, so estimates link directly to welfare measures usable in cost-benefit analysis.
  • Captures non-use and existence values that revealed-preference methods cannot reach, broadening the scope of valuation.
  • Flexible design supports policy-relevant scenarios and, with mixed logit, accommodates preference heterogeneity across respondents.
Limitations
  • As a stated-preference method it is vulnerable to hypothetical bias, where stated willingness to pay exceeds what people would actually pay.
  • Results are sensitive to experimental design, attribute framing, and the choice of cost vehicle, requiring careful and costly survey development.
  • The basic conditional logit imposes restrictive assumptions (independence of irrelevant alternatives, homogeneous preferences) that often need relaxing.
  • Cognitive burden and respondent fatigue can degrade choice quality, and protest or lexicographic responses complicate estimation.

Common pitfalls

This section is available to Pro members. Upgrade to Pro

Applications

This section is available to Pro members. Upgrade to Pro

Frequently asked

How does a choice experiment differ from contingent valuation?

Contingent valuation typically asks for willingness to pay for a single, bundled environmental change, often via a referendum-style question. A choice experiment instead describes options as bundles of attributes and asks respondents to choose among them repeatedly, so it recovers an implicit price for each attribute rather than one global value. Hanley, Wright and Adamowicz promoted choice experiments precisely because this attribute-based structure values multiple marginal changes at once and can sidestep some criticisms of contingent valuation, though both are stated-preference methods sharing vulnerability to hypothetical bias.

Why is a cost attribute essential?

The cost or price attribute is what makes monetary valuation possible. Because utility is modeled as linear in the attributes and in cost, the marginal willingness to pay for any environmental attribute is the negative ratio of that attribute's coefficient to the cost coefficient. Without a cost attribute there is no common monetary metric to convert estimated preferences into willingness to pay. The cost coefficient should come out negative, confirming respondents dislike paying more, and because every welfare estimate divides by it, its plausibility and precision are critical.

What is hypothetical bias and how is it handled?

Hypothetical bias is the tendency for stated willingness to pay in a hypothetical survey to exceed what respondents would actually pay in a real transaction. Because choices in a choice experiment carry no real financial consequence, this bias can inflate value estimates. Common mitigations include cheap-talk scripts that warn respondents about the tendency, consequentiality reminders that stress the survey may influence policy, certainty follow-up questions, and, where feasible, calibration against revealed-preference or actual-payment benchmarks. Careful, realistic scenario design is the first line of defense.

Sources

  1. 1.
    Hanley, N., Wright, R. E., & Adamowicz, V. (1998). Using Choice Experiments to Value the Environment. Environmental and Resource Economics, 11(3-4), 413-428.

You have read it. What now?

Cite this page

ScholarGate. (2026, June 23). Ecosystem-Service Choice Experiment. ScholarGate. https://scholargate.app/environmental-economics/choice-experiment-ecosystem-services