German Centre for Integrative Biodiversity Research (iDiv) Halle-Jena-Leipzig
Leipzig University
2026-07-06
Natural capital plays a critical role in sustaining human life and economic activities (Chiesura and De Groot 2003; Dasgupta 2021), but values are still poorly understood (Guerry et al. 2015; Costanza 2020)
Important to assess natural capital values to track nations’ wealth and guide policymakers (Brandon et al. 2021)
Values of stocks and flows of natural capital are highly spatially dependent (Addicott and Fenichel 2019)
Spatial complexities in the values of natural capital are not (fully) incorporated in most valuation approaches (Glenk et al. 2020)
Develop and apply spatially explicit valuation approach accounting for endowment with natural capital using a discrete choice experiment
Improve understanding of heterogeneity of natural capital values across space and groups
Map distribution of willingness to pay for natural capital (protected areas and high nature value farmland) across Germany
How do people value changes in the stock of natural capital, in the form of protected areas and high nature value farmland, across space?
How can we aggregate willingness to pay (WTP) values to provide spatially explicit natural capital values?
🌱 H1: Natural Capital has Value
People place significant value on natural capital
📊 H2: Diminishing Marginal Utility
The marginal value of natural capital decreases as endowment increases
🏕️ H3: Use vs. Non-Use
Use-related values are higher than non-use-related values
📍 H4: Distance Decay
The marginal value decreases as distance increases
Good to be valued
Changes in the area of protected areas and high nature value farmland
Local changes near the respondent’s home
Binary referendum choice; repeated 10 times
Features of the experiment
Individualized maps of the land-use change
Generated from CORINE land cover data with an R algorithm
Full factorial design; alternatives and attributes randomised
Program financed by a mandatory annual payment per household
Half is paid by European Union
Payment duration varied with split samples
| Attribute | Levels | Description |
|---|---|---|
| Size of protected areas | Vector A: status quo, +100, +200, +300, +500, +800 hectares Vector B: status quo, +200, +400, +600, +1000, +1600 hectares |
The total area designated as protected area. Levels indicate the expansion in hectares from the current status. |
| High nature value farmland | The total area of high nature value farmland. Levels indicate the expansion in hectares from the current status. | |
| Accessibility of new protected areas | Not accessible, Half accessible, Fully accessible | The extent to which the public can access newly designated protected areas, ranging from no access to full access. |
| Visibility of new high nature value farmland | Barely visible, Clearly visible | Indicates how visible the new areas of high nature value farmland are from public roads or paths. |
| Annual payment into a nature conservation fund | 5, 10, 20, 40, 60, 80, 120, 150, 200, 250 euros | The amount each household contributes annually to a fund dedicated to nature conservation efforts. |
Note: Each respondent is assigned either Vector A or Vector B; the assignment applies to both size attributes (protected areas and high nature value farmland).
Utility is a function of natural capital and cost, and a status quo effects (ASC):
\[U_i = -\beta_c \left[ \alpha\,\text{ASC} + \sum_{NC} f(NC,\Phi) - C \right] + \epsilon_i\]
Different shapes for the value function \(f(NC,\Phi)\):
| Function Type | Function \(f(\text{NC},\Phi)\) | Parameters (‘\(\Phi\)‘) |
|---|---|---|
| Linear | \(\beta_{\text{NC}} \cdot \text{NC}\) | \(\{\beta_{\text{NC}}\}\) |
| Quadratic Utility | \(\beta_{\text{NC}} \cdot \text{NC} + \beta_{\text{NC}_{\text{sq}}} \cdot \text{NC}^2\) | \(\{\beta_{\text{NC}}, \beta_{\text{NC}_{\text{sq}}}\}\) |
| Logarithmic | \(\beta_{\text{NC}} \cdot \log(\text{NC})\) | \(\{\beta_{\text{NC}}\}\) |
| Box-Cox | \(\beta_{\text{NC}} \cdot \frac{\text{NC}^\lambda - 1}{\lambda}\) | \(\{\beta_{\text{NC}}, \lambda\}\) |
| Log-Linear | \(\beta_{\text{NC}} \cdot \text{NC} + \beta_{\text{NC}_{\text{log}}} \cdot \log(\text{NC})\) | \(\{\beta_{\text{NC}}, \beta_{\text{NC}_{\text{log}}}\}\) |
| Model | AIC | BIC | LLout |
|---|---|---|---|
| Quadratic Utility Function | 128533.25 | 128809.48 | -64238.63 |
| Log Utility Function | 128773.39 | 128950.97 | -64368.7 |
| Linear Utility Function | 128574.99 | 128752.57 | -64269.5 |
| Box Cox Utility Function | 128548.7 | 128775.6 | -64251.35 |
| Log-Linear Utility Function | 128554.29 | 128830.52 | -64249.15 |
| Cubic Utility Function | 128565.43 | 128940.32 | -64244.72 |
The value declines with distance \(D\) to it:
\[U_i = -\beta_c \left[ \alpha\,\text{ASC} + \sum_{NC} \left(1 + \delta_{NC}\,\log D\right) f(NC,\Phi) - C \right] + \epsilon_i\]
\(U_i\): utility of choice option \(i\); \(\epsilon_i\): random error
\(\text{ASC}\): status-quo indicator (\(=1\) for the status-quo option)
\(\alpha\): status-quo parameter vector: base effect and its shift with income, distance & scope, \(\alpha = (\alpha_0, \alpha_{\text{Inc}}, \alpha_{\text{Dist}}, \alpha_{\text{Scope}})\)
\(f(NC,\Phi)\): value of a change in natural capital, one of five types \(NC \in \{\text{PA}_{\text{no}}, \text{PA}_{\text{half}}, \text{PA}_{\text{full}}, \text{HNV}_{\text{hidden}}, \text{HNV}_{\text{visible}}\}\) (Protected Areas by access, High Nature Value farmland by visibility); \(\Phi\) set of parameters
\(C\): annual payment; \(\beta_c\): price coefficient
\(D\): distance from home to the change; \(\delta_{NC}\): distance-decay parameter
Use split sample variation in maximum distance of new areas
\(\text{WTP}_{PA_i} = (1 + \delta_{PA_i} \cdot log(\text{D}))\left(\beta_{\text{PA}_i} + 2 \cdot \beta_{\text{PA}_{i,sq}} \cdot \text{PA}_i\right)\)
Utility scales with household income \(I\):
\[U_i = -\beta_c \left[ \alpha\,\text{ASC} + \sum_{NC} \left(1 + \delta_{NC}\,\log D + \gamma\,\log I\right) f(NC,\Phi) - C \right] + \epsilon_i\]
\(U_i\): utility of choice option \(i\); \(\epsilon_i\): random error
\(\text{ASC}\): status-quo indicator (\(=1\) for the status-quo option)
\(\alpha\): status-quo parameter vector: base effect and its shift with income, distance & scope, \(\alpha = (\alpha_0, \alpha_{\text{Inc}}, \alpha_{\text{Dist}}, \alpha_{\text{Scope}})\)
\(f(NC,\Phi)\): value of a change in natural capital, one of five types \(NC \in \{\text{PA}_{\text{no}}, \text{PA}_{\text{half}}, \text{PA}_{\text{full}}, \text{HNV}_{\text{hidden}}, \text{HNV}_{\text{visible}}\}\) (Protected Areas by access, High Nature Value farmland by visibility); \(\Phi\) set of parameters
\(C\): annual payment; \(\beta_c\): price coefficient
\(D\): distance from home to the change; \(\delta_{NC}\): distance-decay parameter
\(I\): local income; \(\gamma\): common income-scaling parameter
Use GIS data on available income to incorporate differences in income
\(\text{WTP}_{PA} = (1 + \delta_{PA} \cdot log(\text{D}) + \gamma \cdot log(\text{I}))\left(\beta_{\text{PA}} + 2 \cdot \beta_{\text{PA}_{sq}} \cdot \text{PA}\right)\)
| Mean | SD | Distance | |
|---|---|---|---|
| Protected Areas NA | 11.34 (1.03)*** | -8.51 (0.78)*** | -0.37 (0.22)* |
| Protected Areas NA Squared | -0.08 (0.03)*** | 0.07 (0.03)** | |
| Protected Areas HA | 16.99 (0.80)*** | -1.22 (0.24)*** | -0.28 (0.14)** |
| Protected Areas HA Squared | 0.03 (0.03) | -0.18 (0.02)*** | |
| Protected Areas FA | 21.76 (0.74)*** | -4.82 (0.40)*** | -0.29 (0.10)*** |
| Protected Areas FA Squared | -0.09 (0.02)*** | 0.30 (0.01)*** | |
| High Nature Value NV | 12.21 (0.44)*** | -8.46 (0.28)*** | -0.36 (0.07)*** |
| High Nature Value NV Squared | -0.09 (0.01)*** | -0.07 (0.01)*** | |
| High Nature Value V | 15.60 (0.68)*** | -4.31 (0.27)*** | -0.25 (0.12)** |
| High Nature Value V Squared | -0.10 (0.01)*** | -0.02 (0.01)** | |
| Annual Payment | -3.25 (0.03)*** | -1.97 (0.04)*** | |
| Scope high | 6.46 (0.89)*** | -79.50 (0.26)*** | |
| ASC SQ | -50.57 (0.63)*** | 121.13 (0.40)*** | |
| ASC Distance Interaction | 14.85 (2.10)*** | ||
| ASC Income Interaction | -21.22 (0.36)*** | ||
| Income Scale Factor | 0.24 (0.02)*** | ||
| No Observations | 131,440 | ||
| No Respondents | 13,144 | ||
| Log Likelihood (Null) | -91,107.27 | ||
| Log Likelihood (Converged) | -59,821.95 | ||
| *** p < 0.005; ** p < 0.025; * p < 0.05. Robust standard errors in parentheses. | |||
🌱 H1: Natural Capital has Value
Willingness to pay for protected areas and high nature value farmland is positive and significant
📊 H2: Diminishing Marginal Utility
Marginal willingness to pay falls as the endowment rises, magnitute depends on functional form choosen
🏕️ H3: Use vs. Non-Use
Accessible protected areas and visible farmland are valued more
📍 H4: Distance Decay
Marginal willingness to pay declines with distance to the change
Implementation of biodiversity policies should incorporate spatial heterogeneities
Endowment, income and number of beneficiaries are important drivers of aggregated values
Joint work within the ValuGaps Team since 2020
Several institutions and collaborators involved
Visit https://valugaps.de/en/ for more information
Pre-registration, questionnaire, data, code and estimated models and intermediate data available on Open Science Framework (link on request)
🎲 Randomised
🚧 Restrictions