Tasmanian landowner preferences for conservation incentive programs: A latent class approach
Highlights
Landowner and property characteristics affect landowner conservation incentive program choice. ► Program choice is also affected by program attributes and landowner attitudes. ► Choice experiment shows that compensation funding plays a smaller role than expected. ► Landowner attitudes are predictive of preferences for incentive program attributes. ► Higher likelihood of participation by landowners already engaged in environmental issues. ► Increased participation achieved by flexibility of legal arrangements and land use restrictions.
Introduction
Australia possesses flora and fauna that are both highly endemic and has great species richness compared to many other parts of the world. However, much of Australia’s rich biodiversity is threatened with extinction due to habitat loss or the degradation of habitat quality. As over 60 percent of land in Australia is managed by private landholders (Productivity Commission, 2001) many threatened ecosystems occur on private land.
Incentive programs for private forest conservation have existed in Australia for more than two decades (Figgis, 2004). Incentives currently comprise grants (including management and stewardship payments), subsidies, tax relief, rate relief, offset payments, development incentives, the creation of environmental markets, and market-based incentives (e.g. James, 1997, Bateson, 2001, Comerford and Binney, 2004, Department of Environment and Water Resources, 2006). Most conservation incentive programs in Australia are voluntary and in joining a program landowners will generally restrict the use of the land by legal agreements or other means (CSIRO Wildlife and Ecology, 2001).
Tasmanian incentive programs have added significantly to biodiversity conserved on privately owned land.4 Landowners in this State were paid, approximately one-third of the estimated market price, to secure covenants on 180 properties in 2005 (Smith, 2001, Department of Primary Industries and Water, n.d.). Nevertheless, in some regions more than 80 percent of land with conservation value remains unprotected and programs routinely fail to meet enrolment targets (Department of Environment and Water Resources, 2007). Targets are not being met even though there is flexibility in the amount of compensation that may be offered and available funds have not reached their limit. Considering the overall budget is adequate and the fact there is no evidence of a landowner waiting list, indications are that other landowner decision variables play a role. This has resulted in considerable debate not only about the design of programs but also around the question of whether landowners should be forced to protect land for conservation in order to achieve stated policy and conservation objectives. Due to the Australian constitution, even legislative or forced conservation in Australia would require some compensation to be paid to landowners. The option of forcing landowner entry into conservation incentive programs has already been considered in some Australian States (e.g. Stoneham et al., 2000). But before implementing compulsory schemes and to ensure Australian conservation targets will be met in the future, understanding landowners’ preferences for incentive program attributes is likely to become increasingly relevant.
Participation in incentive programs is dependent on many variables that can be loosely grouped into four areas: program characteristics; landowner characteristics; property and business characteristics; and landowner attitude (e.g. Ervin and Ervin, 1982, Esseks and Kraft, 1986, Purvis et al., 1989, Cooper and Keim, 1996, Drost et al., 1996). Some studies have considered one or more of these four groups of variables, but none have systematically considered all four together as is undertaken in this current research.
Our general aim is to investigate landowner preferences for conservation incentive program attributes to better understand the contribution of the different program attributes to the decision to voluntarily join conservation programs. We also focus our investigation on the contribution of latent attitudes to the role of conservation on private land to the likelihood of joining conservation incentive programs. The outcomes of the study are intended to provide information that is useful in the development of new incentive programs and thus ensuring conservation targets are met in the future.
The existing literature within each of the four groups of variables that contribute to landowner participation in incentive programs is reviewed below.
Section snippets
Literature overview
It is well established that landowner participation rates in incentive programs are affected by program characteristics and attributes including, for instance, tax relief or the level of compensation. Empirical studies confirm the relationship between the size of an inducement payment and the likelihood of participation (Esseks and Kraft, 1986, Chisholm and Dumsday, 1988, Purvis et al., 1989, Cooper and Keim, 1996, Lynch et al., 2002, Stevens et al., 2002, Greiner et al., 2003, Horne, 2004).
Theoretical framework and estimation method
The importance of understanding the decision-making process with regard to participation in policy programs has been recognised for many years (Brotherton, 1989). This early recognition has led to the development of theoretical behavioural models in economics (e.g. Lynne et al., 1988, Beedell and Rehman, 2000), psychology, and the other social sciences (e.g. Sinden and King, 1990). In economics, a utility-maximising framework is frequently applied to explain behaviour as it can include economic
Methodology
The data used to develop and estimate the landowner decision model was gathered by means of a Choice survey of 500 randomly selected Tasmanian landowners in 2004. A stratified sample (by commodity group) comprised approximately 12.5 percent of the estimated 4000 rural landowners in Tasmania. The response rate to this voluntary survey was 27 percent which is consistent with that of other landowner surveys in Tasmania (Jennings and van Putten, 2001, Jennings and van Putten, 2003, Jennings and van
Choice survey latent class results and analysis
In this research only 33 percent of landowners were willing to take up these incentives and the obligations that went with them. For those who were willing to take them up the model revealed that preferences for incentive program attributes differed between classes of landowner and that these classes of landowners could be described in terms of the member’s attitude to the role and outcome of establishing reserves on private land. There were three classes of landowner types in the model. There
Discussion and conclusions
Most conservation incentive programs in Australia and Tasmania are based on voluntary participation but this research showed that only a small proportion of landowners are willing to take up these incentives and the obligations that go with them. This may be because landowners, for a variety of reasons, are reluctant to change the basis of their land management (e.g. Wynn et al., 2001, Hazell and Williams, 2003). Our primary aim in this research was to find options for improving participation.
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