Supply and Demand for Ecosystem Services from Private Forests:
Examining Preferences in Germany

Nino Cavallaro, Martin Quaas and Daniela Thrän

DCE Colloquium · November 2026

Motivation

A walk through two forests

What the UN is demanding

What society and policy are demanding

  • Forests are a central element of a sustainable economy but under high environmental pressure due to climate change (Hanewinkel et al. 2013)
  • High societal demands on forests (recreation, climate, biodiversity, timber) → fulfillment depends on forest management
  • Germany’s Waldstrategie 2050: „Die Ökosystemleistungen des Waldes werden angemessen von der Gesellschaft honoriert“ (BMEL 2021)
  • Milestone 2030: payment schemes for climate protection, nature conservation and recreation are established

Who supplies German forests?

Share of forest area

Who supplies German forests?

  • About 1.8 million private owners hold 48 % of Germany’s forest (BMEL 2021) → large and important stakeholder group
  • One quarter of Germany’s total forest area is managed by small-scale private forest owners (< 20 ha), a very heterogeneous group (Stockmann et al. 2024)
  • Private owners’ management decisions shape forest ecosystem service supply, yet it is unclear whether their preferences align with those of the wider public

Current incentives: Klimaangepasstes Waldmanagement

Federal program since 2022 for private and municipal forest owners

  • Flat rate of 85–100 €/ha/yr (forests ≤ 100 ha) for a package of 11–12 management criteria, e.g. no clear-cuts, ≥ 5 habitat trees/ha, deadwood, natural regeneration
  • Whole forest, 10–20 years, certification required
  • About 1.7 M ha enrolled: 60 % municipal, 40 % private (12 % of total private area)
  • Budget rises to 200 M€/yr from 2027 (target ≥ 2 M ha)

What KWM does not tell us

  • It pays for a bundle of practices, not for individual services
  • It is tax-financed: we do not know what households would pay, and for which service
  • It offers one rate: we do not know what small private owners need per service
  • Recreation and timber are not part of the scheme

Sources: kwm.fnr.de (press release 18.09.2026; funding scheme overview 05/2023)

Understanding private supply vs. public demand

  • Sustainable future forest use depends strongly on private forest management
  • Incentives exist (KWM), but pay a flat rate for a package of management practices → recreation and timber not included at all so far
  • Designing efficient payments (and evaluating the efficiency of the current program) requires information on demand and supply prices (Engel, Pagiola, and Wunder 2008; Wunder 2015)
  • Little evidence comparing the preferences of both groups (Nordén et al. 2017; Müller et al. 2020)

Main research questions and hypotheses

  • R1: Does the population’s demand for forest ecosystem services match the supply offered by private forest owners?
    • H1: The aggregate willingness to pay of households covers the compensation demanded by private forest owners (for each forest ecosystem service for which owners require compensation).
  • R2: Do the preferences of the general population and of private forest owners for forest ecosystem services differ?
    • H2a/b: The general population has a higher willingness to pay for habitat trees (a) and recreation infrastructure (b) than forest owners.
    • H2c: The general population has a higher willingness to pay for a reduction in timber use than forest owners.
  • R3: Which socio-demographic and structural factors explain differences in preferences for forest ecosystem services?
    • H3: Private forest owners have different preferences than individuals from the general population with a similar socio-demographic and structural background.

Research contribution

  • Improve understanding of private forest owners’ management choices
  • Identify differences and similarities in demand and supply of forest ecosystem services
  • Provide service-specific prices as input for the further development of KWM-type payment schemes
  • Estimate demand and supply curves over enrolled hectares → efficient program size
  • Add to the literature on combining demand and supply in a single valuation study (Tienhaara et al. 2020)

Survey and Discrete Choice Experiment

Project timeline

Nov 2026 Focus groups

Nov/Dec 2026 Internal + external
survey pre-test

Jan 2027 Data
collection

Feb 2027 Start of
data analysis

From Mar 2027 Results presentation
in the Jour Fixe

Survey and sample

  • Collaboration with a panel provider → Bilendi
  • Survey in LimeSurvey
  • Survey with 1,600–2,000 respondents, up to 75 % from the general population, at least 25 % private forest owners (N ≥ 400)
  • Coverage of the program randomly 20, 40 or 60 % of the private forest, between-subject split
  • General population randomly split: one third answers a coverage follow-up after each card, two thirds do not
  • Additionally distribute the survey via forest owners’ associations → different link

Combination with BWI data

  • Use of the latest BWI data in the analysis of the survey data
  • Status quo on the cards from BWI 2022 (harvest 2012–2022 and habitat trees, private forest per state)
  • Interactions with forest condition variables at the federal state/district level

Survey structure

1 Screening
ScreeningForest ownership, forest visits
↓
Socio-demographicsAge, gender, education, region
O = forest owners
V = forest visitors
N = non-visitors
P = random third of the public
→
2 Forest module
O  Own forestCharacteristics, management, harvest, KWM participation
V  Most visited forestCharacteristics, use
N  Forests in districtCharacteristics, reasons for no visit
→
3 Information
Forest knowledgeQuiz question
↓
InformationForests in Germany, forests and society
↓
Choice scenario· Program, 10 years
· 4 ES attributes + levy
· Levy → forest fund
· Voting rule, cheap talk
→
4 Choice experiment
Common DCE (all respondents)10 binary cards: program vs. SQ, household levy (€/yr)
Coverage 20/40/60 % of the private forest, between-subject
↓ after each card
↓ after each card
O  EnrollmentJoin at p €/ha?
Area enrolled (slider)
P  CoverageStill for it at one step lower / higher coverage?
then next card, ×10
→
5 Follow-up
Follow-upProtest, consequentiality, attitudes
↓
Socio-economicsHousehold, income

Choice scenario: a private forest support program

The program
Additional program of the respondent's federal state for private forests
Complements existing funding (federal Klimaangepasstes Waldmanagement, state programs)
Goal: more societal benefits from private forests, support forest owners
Owners who participate and implement measures receive payments; the program covers 20, 40 or 60 % of the private forest area
  Duration: 10 years, from 1 January 2028
Four objectives = four attributes
Timber use
Biodiversity
Climate adaptation
Recreation

Payment vehicle: the forest fund

All householdsin the federal state
(incl. forest owners)
Levy
Forest fundmoney is earmarked
Payment
Forest ownersonly if they implement
the agreed measures
  Unclaimed money is returned to households
5–200 €
levy per household and year (cost attribute)
10 years
levy paid over the full program duration
Same for all
owners vote on the same levy; payments are only shown in their enrollment question

Attributes and levels

AttributeDescriptionTodayLevels
Annual timber use
m³ per ha and year, average over 10 years
Change in the yearly harvest per ha compared with today. Some programs aim for more domestic wood (construction, energy), others for less harvest, so that more carbon and old trees stay in the forest. 6.8DE (4.0–10.3) −1.2−0.6±0+0.6+1.2
Habitat trees
per ha, program minimum
Trees with special ecological features (cavities, deadwood, coarse bark) that remain permanently in the forest. Program minimum = state status quo + Δ, but at least 5 (KWM standard). 8DE (4–11) SQ ±0+2+4+6min. 5
Climate-adapted planting
% of regeneration area, additional
Share of the regeneration area where climate-adapted trees are actively planted in addition to today; natural regeneration keeps priority. 0 % 0+2 %+4 %+6 %+8 %
Recreation infrastructure
% of program area
Share of the program area on which recreation opportunities are expanded. Expansions may include new or repaired paths, benches and signs. Building, upkeep and safety are handled by a program agency and paid by the forest fund. 0 % 010 %20 %30 %40 %
Annual levy
€ per household and year
Earmarked levy your household pays into the forest fund. Only without a program (status quo) does your household pay nothing. 0 € 5101520305080120200 €
Payment to owners
€ per ha and year, owners only
Per enrolled hectare and year (owners only); timber revenue stays with the owner. 0 € 2550100150200250300400 €
Today: BWI 2022, private forest; Germany (range across states). Cards show the value of the respondent's state; owners additionally see their own forest in the enrollment step. Coverage: 20, 40 or 60 % of the private forest, random per respondent and fixed across cards; a third of the public answers a follow-up one step lower or higher (10/20/40/60/80 %).
  Click an attribute for details

How the vote works: explanation shown to respondents

In each task, all households in your federal state vote on a program. You decide between the program and the current situation.

Your vote
for the program
or against it
Majority
for the
program?
yes ↗
no ↘
Yes: the program is introduced
· every household pays the levy for 10 years
· forest owners can take part and receive payments
No: nothing changes
· no levy, no program
· forests develop as today (status quo)
  Each task is a separate vote
Consider each program on its own, independent of earlier tasks.
  Think of your budget
Money spent on the levy is no longer available for other things.
  Your vote counts
Results are passed on to policymakers. Voting against is just as valuable as voting for.

Example choice task, 1st stage: vote (all respondents)

Example choice task, 2nd stage: enrollment (owners only)

Example choice task, 2nd stage: coverage (public)

Methodology

Methodology

  • Vote (all): conditional and mixed logit → preferences, WTP, MRS
    • Pooled model with owner interactions; split-sample models
    • Timber as change vs. status quo, separate coefficients for increase and decrease
    • Habitat trees as increase Δ over the state status quo (program minimum ≥ 5)
    • Two models: A = owners + control group (H2, H3); B = follow-up group (demand)
  • Enrollment (owners): two-part model
    • Part 1, join? Conditional and mixed logit → WTA
    • Part 2, how much? Share of own forest enrolled, fractional logit
    • Habitat trees as gap between program minimum and own baseline; KWM participation and coverage as interactions
    • Supply curve: part 1 × part 2, predicted for all owners and payments
  • Matching (H3): owners vs. comparable non-owners (PSM / ML) → split-sample mixed logit
  • Design: Bayesian efficient design for binary choices incl. payment \(p\); power simulation

Model equations

Vote (all respondents)

\[ U_{nt} = \alpha + \boldsymbol{\beta}_n' X_t + \beta_{cv} \log cv_{nt} + \kappa\, FU_{nt} + (\beta_{levy} + \tau_{levy} D_n)\, levy_t + \varepsilon_{nt}, \qquad U^{SQ}_{nt} = \varepsilon^{SQ}_{nt} \] \[ \boldsymbol{\beta}_n = \boldsymbol{\beta} + \boldsymbol{\tau} D_n + \boldsymbol{\rho} \log cv_{nt} + \boldsymbol{\eta}_n \]

Model A (owners + control group): main votes, \(cv_n\) as ASC interaction. Model B (follow-up group): main votes + follow-ups (\(FU_{nt}=1\)).

Enrollment, part 1: join? \[ U^{J}_{nt} = \alpha^{J} + \boldsymbol{\gamma}_n' \tilde X_{nt} + \delta\, p_t + \omega \log cv_n + \varepsilon^{J}_{nt}, \quad U^{no}_{nt} = \varepsilon^{no}_{nt}, \quad \boldsymbol{\gamma}_n = \boldsymbol{\gamma} + \boldsymbol{\lambda}\, KWM_n + \boldsymbol{\nu}_n \]

Enrollment, part 2: how much? (if joined) \[ s_{nt} = \Lambda\big(\theta_0 + \boldsymbol{\theta}' \tilde X_{nt} + \theta_p\, p_t + \theta_{cv} \log cv_n + \boldsymbol{\varphi}' z_n\big) + u_{nt} \]

\(D_n = 1\) forest owner · \(X_t\): timber (change vs. SQ, split into \(\Delta^{+}\) and \(\Delta^{-}\)), habitat increase over state SQ, planting, recreation · \(\tilde X_{nt}\): same, habitat gap \(\max(0,\ \text{min}_t - \text{own SQ}_n)\), \(\text{min}_t = \max(5,\ \text{state SQ} + \Delta_t)\) · \(\boldsymbol{\eta}_n, \boldsymbol{\nu}_n\): random taste variation · \(\varepsilon\): Gumbel → logit · \(s_{nt}\in[0,1]\): share of own forest · \(z_n\): owner characteristics · \(cv_{nt}\): coverage shown (20/40/60 %; follow-up one step lower/higher); \(\boldsymbol{\rho}\): attribute values change with coverage; \(\kappa\): follow-up shift; \(\omega, \theta_{cv}\): owners react to announced coverage

Supply curve of forest owners

For a program \(X\) and a payment \(p\):

  1. Join: predict for every owner \(n\) the probability of joining, \(P_n(p)\), from the mixed logit (own baseline, KWM status, averaged over draws)
  2. Share: predict the share of their forest that owner \(n\) would enroll if joining, \(s_n(p)\), from the fractional logit
  3. Hectares: expected enrolled area of owner \(n\) \(=\; P_n(p) \cdot s_n(p) \cdot area_n\)
  4. Scale up: sum over owners and scale to the private forest area \(A_{PF}\) \[S(p) = A_{PF}\cdot \frac{\sum_n w_n\, P_n(p)\, s_n(p)\, area_n}{\sum_n w_n\, area_n}\]
  5. Curve: repeat for \(p = 25, 50, \dots, 400\) €/ha → \(S(p)\); confidence bands by Krinsky–Robb
  6. Inverse: \(p^*(A)\) = payment needed to enroll area \(A\) → compared with the demand curve (next slides)

From survey answers to supply and demand curves

Build a program: how large should it be?

Formal hypothesis testing: H1 (supply vs. demand)

H1: public demand covers owners’ compensation, per attribute \(X\) with \(WTA_X > 0\), per federal state

\[ \underbrace{WTP_X(cv) \cdot N_{HH}}_{\text{benefit, €/yr}} \;\geq\; \underbrace{\big[p^*(X{+}1) - p^*(X)\big]\cdot cv\,A_{PF}}_{\text{extra cost, €/yr}}, \qquad S\big(p^*(X);X\big) = cv\,A_{PF} \]

  • \(p^*(X)\): payment at which the supply curve reaches the target area (previous slide)
  • Logit: \(p^*(X{+}1)-p^*(X) \approx WTA_X = -\gamma_X/\delta\), the vertical shift of the supply curve per unit of \(X\)
  • \(WTP_X(cv) = -(\beta_X + \rho_X \log cv)/\beta_{levy}\): value of \(X\) depends on the area covered
  • Tested at \(cv = 40\,\%\); also: up to which coverage does H1 hold? CIs by Krinsky–Robb
  • Timber: decrease (\(\Delta^{-}\)) and increase (\(\Delta^{+}\)) tested separately

Formal hypothesis testing: H2 (households vs. owners)

H2: households have a higher WTP than owners (one-sided, in WTP space)

\[ WTP^{HH}_{k} > WTP^{FO}_{k}, \qquad WTP^{HH}_{k} = -\frac{\beta_{k}}{\beta_{levy}},\quad WTP^{FO}_{k} = -\frac{\beta_{k}+\tau_k}{\beta_{levy}+\tau_{levy}} \]

  • \(k\): habitat trees (H2a), recreation infrastructure (H2b), timber decrease \(\Delta^{-}\) (H2c)
  • Both groups answer the same vote cards; \(\tau\) are the owner interactions in model A (owners + control group)
  • Full public sample if the main votes of the follow-up group show no preference differences
  • WTP ratios remove differences in error scale between the groups

Formal hypothesis testing: H3 (ownership effect)

H3: the owner difference remains after controlling for characteristics \(z_n\)

\[ \beta_{kn} = \beta_k + \boldsymbol{\pi}_k' z_n + \tau_k D_n + \eta_{kn}, \qquad \exists\, k:\ \tau_k \neq 0 \]

  • \(z_n\): socio-demographic and structural characteristics (e.g. age, education, income, wealth, nature relatedness, rural residence)
  • Robustness: owners vs. comparable non-owners (PSM / ML matching) → split-sample mixed logit

Next Steps

Focus group topics

  • Credibility of the policy framework
    • Forest fund: known, trustworthy? Federal state as the right level?
    • Does the support program seem plausible and feasible? Is an additional program realistic?
    • KWM: known? Participation? Concerns about double funding? Other funding schemes that are used?
  • Attributes and status quo
    • Are attributes and levels understandable? Is the federal-state status quo plausible?
    • Timber use up or down: is it clear and credible that programs can raise or lower harvest?
    • Do attribute combinations seem plausible or contradictory?
  • Two-stage choice task
    • Binary vote: one program per card plausible? 10 cards manageable?
    • Owners: enrollment question after each card understandable? Payment levels and levy–payment combinations credible? Minimum acceptable payment (€/ha/yr)?
    • Is partial enrollment (slider) realistic for small-scale owners?
    • Coverage: is 20/40/60 % of the private forest meaningful? Public: follow-up understandable and credible (fewer/more owners join, same levy)? Does it change the next card?

Voices from the owner focus group

Self-determination
Ich möchte selbst bestimmen, was ich mit meinem Wald mache oder auch unterlasse.
Owner, 10 ha, nature-oriented
Payment vs. effort
… so ein Monster zu erzeugen für 150 Euro, glaube ich jetzt nicht.
Owner, 10 ha, actively managing
Habitat trees
Soll der Förster die Bäume zählen, soll ich sie zählen?
Owner, 2.5 ha, bought with the house
Timber use
Holzeinschlag ist ja nicht planbar.
Owner, 10 ha, actively managing
Legitimacy of the vote
Die wenigsten werden da überhaupt zur Abstimmung gehen.
Owner, 3 ha, inherited
Design wish
Ich finde es schade, dass man nicht auswählen kann, welche der Merkmale man für seinen Wald umsetzen will.
Owner, community of heirs
Online focus group with five private forest owners, 2 November 2026 (Bilendi panel). Quotes verbatim from the transcript.

Strong views from the owner focus group

Political backlash
Und die AfD stellt sich womöglich hin und sagt, hier wieder so eine Abzocke von den Altparteien …
Owner, 10 ha, nature-oriented
Financing
Für Militär ist unbegrenzt Geld da, aber für unsere Natur und unsere Zukunft, da müssen wir noch extra bezahlen.
Owner, 3 ha, inherited
Regulation
Das ist Privatwaldbesitz und das reguliert sich selber. […] Der Markt reguliert sich selbst.
Owner, 10 ha, actively managing
Administration
Tatsächlich werden die Bürokratiekosten die Hälfte davon auffressen, mindestens.
Owner, 2.5 ha, bought with the house
Property rights
… mir sind das zu viele tiefgreifende Eingriffe in meine Bürgerrechte.
Owner, 10 ha, nature-oriented
Public goods
Aber alles andere ist zwar toll, aber im Prinzip mein Privatvergnügen.
Owner, 2.5 ha, bought with the house
Online focus group with five private forest owners, 2 November 2026 (Bilendi panel). Quotes verbatim from the transcript.

Focus group: key takeaways and implications for the survey

What we heardWhat we do in the survey
Goals yes, instrument no: support for biodiversity and climate adaptation, but strong rejection of a household levy decided by vote
Keep protest and financing follow-ups; add an item on the preferred way of financing (levy, existing budget, CO₂ revenues)
Legitimacy and fairness: worries about low turnout and an equal levy for poor and rich households
State that the result is binding; make the hardship exemption visible; change to a progressive payment structure
Timber and habitat trees: harvest is driven by necessity; owners do not know how many habitat trees they have
Timber as a 10-year average incl. calamities; explain how compliance is checked and that existing trees count
Recreation: liability is the deciding question
Say explicitly that owners are not liable; the program agency takes over safety
Participation barriers: bureaucracy, ten-year commitment, self-determination; wish to choose single measures
Describe the administrative effort; explain why measures come as one bundle; ask which measures owners would accept individually
Abstraction: „20 % mehr Naherholung“ read as 20 % more benches
Test the units (share of program area) in the general population focus group

How to proceed

  • Update the survey for the focus group with the general public

  • Use feedback from the second focus group to design the pre-test

  • Finalize the experimental design

  • Circulate the pre-test internally

Appendix

References

BMEL. 2021. “Waldstrategie 2050: Nachhaltige Waldbewirtschaftung – Herausforderungen und Chancen für Mensch, Natur und Klima.” Bonn: Bundesministerium für Ernährung und Landwirtschaft.
Engel, Stefanie, Stefano Pagiola, and Sven Wunder. 2008. “Designing Payments for Environmental Services in Theory and Practice: An Overview of the Issues.” Ecological Economics 65 (4): 663–74.
Hanewinkel, Marc, Dominik A Cullmann, Mart-Jan Schelhaas, Gert-Jan Nabuurs, and Niklaus E Zimmermann. 2013. “Climate Change May Cause Severe Loss in the Economic Value of European Forest Land.” Nature Climate Change 3 (3): 203–7.
Müller, Alexandra, Roland Olschewski, Christian Unterberger, and Thomas Knoke. 2020. “The Valuation of Forest Ecosystem Services as a Tool for Management Planning–a Choice Experiment.” Journal of Environmental Management 271: 111008.
Nordén, Anna, Jessica Coria, Anna Maria Jönsson, Fredrik Lagergren, and Veiko Lehsten. 2017. “Divergence in Stakeholders’ Preferences: Evidence from a Choice Experiment on Forest Landscapes Preferences in Sweden.” Ecological Economics 132: 179–95.
Stockmann, Johannes, Kristin Franz, Björn Seintsch, and Christoph Neitzel. 2024. “Factors Explaining the Willingness of Small-Scale Private Forest Owners to Engage in Forestry—a German Case Study.” Forests 15 (2): 319.
Tienhaara, Annika, Emmi Haltia, Eija Pouta, Kyösti Arovuori, Ioanna Grammatikopoulou, Antti Miettinen, Kauko Koikkalainen, Heini Ahtiainen, and Janne Artell. 2020. “Demand and Supply of Agricultural ES: Towards Benefit-Based Policy.” European Review of Agricultural Economics 47 (3): 1223–49.
Wunder, Sven. 2015. “Revisiting the Concept of Payments for Environmental Services.” Ecological Economics 117: 234–43. https://doi.org/10.1016/j.ecolecon.2014.08.016.

Other sources

Status quo per federal state (BWI 2022, private forest)

State Harvest 2012–2022
m³ Efm o.R./ha/yr
Habitat trees 2022
per ha
Habitat levels on the cards
minimum = max(5, SQ + Δ)
Baden-Württemberg 8.6 8 8, 10, 12, 14
Bayern 7.8 8 8, 10, 12, 14
Brandenburg (also BE) 4.0 7 7, 9, 11, 13
Hessen 8.7 8 8, 10, 12, 14
Mecklenburg-Vorpommern 4.7 9 9, 11, 13, 15
Niedersachsen (also HB) 5.5 9 9, 11, 13, 15
Nordrhein-Westfalen 10.3 5 5, 7, 9, 11
Rheinland-Pfalz 5.4 11 11, 13, 15, 17
Saarlanda 4.6 7 7, 9, 11, 13
Sachsen 5.5 5 5, 7, 9, 11
Sachsen-Anhalt 5.1 10 10, 12, 14, 16
Schleswig-Holstein (also HH) 5.4 10 10, 12, 14, 16
Thüringen 6.9 4 5, 6, 8, 10
Germany 6.8 8

Source: Thünen-Institut, BWI 2022 result database (bwi.info), tables 43Z1PA_L417of_1222_bi and 43Z1JI_L247of_2022, retrieved 15.10.2026. City states take the values of the surrounding state. a All forest (private forest: 13 plots only).

Status quo: private vs. public forest (BWI 2022)

Harvest (m³/ha/yr, 2012–2022)Habitat trees (per ha, 2022)
StatePrivatePublicΔPrivatePublicΔ
Baden-Württemberg8.67.6+1.0880
Bavaria7.86.2+1.689−1
Brandenburg4.04.4−0.4770
Hesse8.77.9+0.886+2
Mecklenburg-W. Pom.4.74.4+0.397+2
Lower Saxony5.56.7−1.297+2
North Rhine-Westphalia10.38.5+1.856−1
Rhineland-Palatinate5.45.7−0.311110
Saarland†2.55.4−2.976+1
Saxony5.57.0−1.553+2
Saxony-Anhalt5.16.8−1.71012−2
Schleswig-Holstein5.45.3+0.11011−1
Thuringia6.98.1−1.243+1
Germany6.86.6+0.2880
Values as shown on bwi.info. Public = federal, state and municipal forest. Δ = private − public; bold: larger than the combined 95 % CIs. † Fewer than 100 private plots; Berlin, Hamburg, Bremen omitted. Source: Thünen-Institut, BWI 2022 (bwi.info), tables 6.01 and L247of.
Germany: almost no difference; states differ in both directions. Cards use private-forest values.

Timber use: why it can go up or down

Both directions are discussed in forest policy
  Some programs: more timber
· Mobilize timber in small private forests, a long-standing policy goal
· Regional wood for construction and energy, replacing concrete, steel and fossil fuels
 
  Other programs: less timber
· Keep more carbon in the forest; the forest carbon sink has weakened (BWI 2022)
· More old trees and deadwood for biodiversity
Shown to respondents (attribute explanation)
In den Programmen kann die jährliche Holznutzung steigen oder sinken. Manche Programme sollen mehr heimisches Holz bereitstellen, z. B. für Bau und Energie. Andere sollen weniger Holz ernten, damit mehr Kohlenstoff im Wald gespeichert bleibt und mehr alte Bäume stehen bleiben. Beides wird derzeit politisch diskutiert.

Owners additionally: Die Holzerlöse auf der angemeldeten Fläche bleiben bei Ihnen.
What we learn
· Symmetric levels around the state status quo: −1.2, −0.6, ±0, +0.6, +1.2 m³/ha/yr
· Would households pay for less harvest, or publicly fund more harvest?
· Separate coefficients for increase and decrease → asymmetry (loss aversion)
· Owners: WTA for harvest cuts vs. interest in harvesting more
Cavallaro, Quaas, Thrän
DCE Colloquium Nov 26
November 2026