Forest banking and forest landowners forgoing management rights for guaranteed financial returns

https://doi.org/10.1016/j.forpol.2003.07.001Get rights and content

Abstract

Forest banking provides a new tool for forest conservation in which a landowner cedes development rights on their forested property in exchange for an annual payment, based on the assessed value of the timber. The Nature Conservancy is in the process of establishing a Forest Bank in Virginia, Indiana, and possibly elsewhere in the US to protect water quality and imperiled species. This study examines monetary willingness to accept payments for enrollment in the Forest Bank through a referendum-type survey of forest landowners in Southwestern Virginia. A logistic regression model that predicts the probability of enrollment is estimated using survey data that includes the landowner acceptance or rejection of a given annual payment level, landowner demographic characteristics, and tract characteristics. Findings suggest that landowners are responsive to annual payment bid levels and that financially viable bid levels (relative to local land prices) may generate reasonable probabilities of Forest Bank enrollment. Further, some tract and landowner characteristics are significant in predicting enrollment probability, including the desire to bequeath land to heirs, which suggests that forest-banking arrangements should take the target owners and properties into account—especially recognizing the potential reluctance to accept perpetual arrangements.

Introduction

Historically, government and non-government organizations have been the source through which forest landowners could receive incentives for conservation and stewardship activities. Often in the US, government intervention has taken the form of reforestation incentives or tax exemptions for planting.1 A new approach for providing private forest landowner incentives, called forest banking, is currently being advocated by some environmental interest groups in the US with the objective being encouragement of forest stewardship through sustainable forest management. A major proponent (and originator) of this program is the Nature Conservancy, a large non-government organization operating within the United States and around the world. The Nature Conservancy is best known for purchasing sensitive habitats on private land to ensure continued preservation of imperiled species or promotion of water quality (US Environmental Protection Agency, 2001).

Forest banking may be administered through the private sector and is intended to ensure environmentally—sensitive forest management, while guaranteeing forest landowners a regular source of income. Landowners who enroll in the program waive development rights (e.g. timber harvesting, construction or mining) to at least a portion of the forest land in their possession, and the collection of forest land enrolled by landowners who participate is instead managed by the bank. The bank determines the method, timing and intensity of harvesting and replanting for all forest lands enrolled in the program. Revenues from timber harvesting are deposited in private investment funds. Participating landowners receive an annual payment from these funds that depends on the returns secured by the investments.

Forest banking has characteristics that are similar to many other approaches aimed at cooperative control of forest resources throughout the world. In the US, private forest land has restricted use access, but the non-timber benefits produced from this land (i.e. species habitat and water quality) represent national and global public goods. Forest banking is a means to encourage continued production of these public goods, through the sharing of rents generated from harvesting on selected areas for all landowners enrolled. Thus, the program is similar to rent-sharing programs in many other developing and developed country settings. Consider community forestry programs in Nepal or joint forest management contracts in India, where management of forest land is transferred to a group that manages the forest sustainably, in return for revenue-sharing guarantees that result from production of marketable forest products. In most cases, these cooperative agreements are made between governments, i.e. at local and national levels. The involvement of the private investment sector makes forest banking unique among cooperative forest incentive-based approaches policies where management rights are transferred from one party to another.

In this paper, we use data from a survey of Virginia landowners to examine incentives to enroll in a forest banking program. We do this by estimating an equivalent variation, or willingness to accept, for landowners to forgo management rights on their land in return for guaranteed financial returns. We show how this willingness to accept depends on landowner preferences and characteristics, as well as characteristics of the forest tract. The study is unique in that we uncover a value (or cost) that landowners attach to the management rights for their forest land. Our findings will be useful in future forest policy work where cooperation is forwarded as a means to protect forest habitat.

Our approach for estimating the equivalent variation follows accepted guidelines developed in the referendum voting literature, however, given that the market returns of forest harvesting are known and do not constitute a non-market good, there should be fewer of the biases associated with referendum methods applied to valuing non-market goods. Nevertheless, we follow the survey design methods outlined in the literature to ensure any biases are minimized.

The remainder of the paper proceeds as follows. First, we provide additional discussion of the Nature Conservancy Forest Bank as it is envisioned in Virginia. We then outline a simple model to identify the equivalent variation for a landowner who is considering enrollment in the program, and we characterize an econometric approach, based on referendum voting elicitation, that can be used to examine a landowner's willingness to accept a bid proposed to enroll their land in a forest bank. Following the model discussion, we present our results, which include descriptive statistics, logistic estimation results of our enrollment model, and a discussion of the relationship between bid levels and enrollment probabilities. Finally, we offer four conclusions based on our findings.

Section snippets

The nature conservancy forest bank

The Nature Conservancy conceived of the Forest Bank in 1995 as a way to protect non-timber benefits from forests, such as water quality, while providing incentives for landowners to enroll through guaranteed annual payments related to timber harvesting on enrolled forest land. Currently, the program is in its infancy, with initial applications in Virginia and Indiana, but possibly expanding to Wisconsin and New York (US Environmental Protection Agency, 2001). In the past, the Nature Conservancy

A simple model of forest bank enrollment

Consider a representative landowner who is facing the decision to enroll land in a forest banking program. Suppose that in the absence of enrollment in a forest bank, the landowner possesses an indirect utility function given by,Vp,I,F0=Vp,IF0where V() is indirect utility, p is the value of timber on the property, I is landowner's income, F0 is the forest stock in possession of the landowner, φ measures non-timber benefits obtained from the forest stock. Note that the utility function is

Survey design and data

To assess non-industrial forest landowner willingness to accept enrollment in the Nature Conservancy Forest Bank, a mail survey of Southwestern Virginia landowners was conducted in 1999. Landowner name lists were obtained from the Commissioners of Revenue in the five county study area. These lists named the owners of 10 acre or larger parcels within each county. Duplicate landowners and landowners with the same address as well as corporate and government property owners were eliminated, so that

Descriptive statistics

Our descriptive statistics (Table 1) depict a landowner who is similar to those found in earlier studies in varying locations (e.g. Dennis, 1989, Hodge, 1993, Birch, 1996, Shaffer and Meade, 1997). Slightly over one-half of our respondents live on the property, and those who live off the property live approximately 90 miles away, on average. The age of our landowner is approximately 60 years, and this age is also reflected in retirement (50% retired) and employment (35% engaged in full-time

Logistic estimation results

Econometric estimation of the parameters of Eq. (8) should give us a better understanding of the role that bid price, tract and owner characteristics play in influencing enrollment in a forest bank. Coefficients on the following variables are significant in predicting probability of enrollment in the Nature Conservancy Forest Bank at the 10% significance level or better: bid price, tract size, the owner holding multiple parcels, presence of roads, gender of respondent, and the bequest intent of

Bid level and enrollment probability

Considering the relationship between bid price and the probability of enrollment in the Forest Bank (Fig. 1), it is evident that positive probabilities do occur for modest annual payments, which is a good news for Forest Bank establishment. Although getting a high probability of acceptance appears to require a very high bid (e.g. approximately $200/acre/year is required to get a 50% probability of bid acceptance), the Bank may not be able to or be interested in enrolling large numbers of

Conclusions

Our results support at least four conclusions about enrollment of non-industrial private forest lands in forest banking arrangements. Firstly, it appears that financial incentives are important in encouraging Forest Bank enrollment. Although financial gain was found at the bottom of the stated landowner motivations list, owners did seem to respond positively to increasing bid levels. Apparently, being bottom on the priority list does not make financial incentives irrelevant.

Secondly, bid levels

References (17)

  • T.A. Cameron

    A new paradigm for valuing non-market goods using referendum data: maximum likelihood estimation by censored logistic regression

    Journal of Environmental Economics and Management

    (1988)
  • Birch, T.W., 1996. Private forest landowners of the United States, 1994. Resource Bulletin NE-134. USDA Forest Service,...
  • J.C. Bliss et al.

    In the mainstream: environmental attitudes of mid-south forest owners

    Southern Journal of Applied Forestry

    (1997)
  • J.P. Dedrick et al.

    The forest bank: an experiment in managing fragmented forests

    Journal of Forestry

    (2000)
  • D.F. Dennis

    An economic analysis of harvest behavior: integrating forest and ownership characteristics

    Forest Science

    (1989)
  • D.A. Dillman

    Mail and Telephone Surveys: The Total Design Method

    (1978)
  • Hodge, S.S., 1993. Beliefs, attitudes, demographics and knowledge: the social dimensions of harvesting decisions made...
  • L. Hultkrantz

    Informational efficiency of markets for stumpage

    American Journal of Agricultural Economics

    (1993)
There are more references available in the full text version of this article.

Cited by (36)

  • Do forest property characteristics reveal landowners' willingness to accept payments for ecosystem services contracts in southeast Georgia, U.S.?

    2019, Ecological Economics
    Citation Excerpt :

    Naturally, residence forest owners' opportunity costs to enroll the property in PES programs would be lower than non-resident owners. Many studies have found that size of forest holding affected forest owners' participation in PES programs (Langpap, 2004; Mäntymaa et al., 2009; Rabotyagov and Lin, 2013; Sullivan et al., 2005). However, both the MNL and RPL model estimation results show that the size of the property does not affect forest owners' willingness to participate in incentive programs.

  • Family forest land availability for the production of ecosystem services in Mississippi, United States

    2016, Forest Policy and Economics
    Citation Excerpt :

    A better understanding of factors influencing land-use decisions of family forest landowners will help develop more effective strategies for increasing production of multiple ecosystem services from family forest lands. Several research studies showed mixed results for factors such as gender, education, household income, property taxes, and population density in terms of their effect on forest land allocated for the production of ecosystem services (Meng and Zhang, 2013; Chen et al., 2012; Sullivan et al., 2005). However, while many previous studies analyzed forest land availability for ecosystem services production, they did not determine the proportion of family forest land that can be managed for ecosystem services in the future and what forest ecosystem types might be allocated to ecosystem service production.

  • Payments for ecosystem services and rural development: Landowners' preferences and potential participation in western Mexico

    2013, Ecosystem Services
    Citation Excerpt :

    Landowner's participation in PES could be increased if higher cash payments are offered in areas with higher opportunity costs. However if higher payments are offered it can be the case that the net present value of the incentives paid can overcome land prices (Sullivan et al., 2005). This can compromise long term efficiency of the program if high enrollment rates are required, since purchase of land for conservation may be the least cost option in areas with low opportunity costs (Fig. 4).

  • Cost sharing for pre-commercial thinning in southern pine plantations: Willingness to participate in Virginia's pine bark beetle prevention program

    2013, Forest Policy and Economics
    Citation Excerpt :

    This strong financial motivation may be explained in part by the difficult economic conditions occurring during the study period, along with our focus on private forests in the coastal plain and piedmont physiographic provinces where commercial forestry activities are common. We do see owners who are strongly motivated to provide an estate for future generations (60%), though this is not as high as found by Sullivan et al. (2005), with the lower level perhaps reflecting a stronger commercial ownership preference of our respondents compared with that earlier study. The commercial focus may also be reflected in our finding that 70% have harvested timber in the past, though only 19% have invested in a management plan for their property.

View all citing articles on Scopus

We would like to thank the USDA Fund for Rural America for financial support and the Nature Conservancy for help with the project.

View full text