Private forest owners and property tax incentive programs in the United States: A national review and analysis of ecosystem services promoted, landowner participation, forestland area enrolled, and magnitude of tax benefits provided
“…Reasons for this lack of uptake include technical difficulties, organizational barriers that do not facilitate a culture of evaluation, and political obstacles (Keene & Pullen, 2011). Most studies still rely on the assessment of program outputs (e.g., how many landowners are enrolled in the program, or, how many landowner workshops were held) instead of program outcomes (e.g., has the program caused a change in landowners' conservation behaviors, or, has the program led to a recovery of ecological function) (Kilgore et al, 2018). Most studies still rely on the assessment of program outputs (e.g., how many landowners are enrolled in the program, or, how many landowner workshops were held) instead of program outcomes (e.g., has the program caused a change in landowners' conservation behaviors, or, has the program led to a recovery of ecological function) (Kilgore et al, 2018).…”
Section: Discussionmentioning
confidence: 99%
“…Especially, impact evaluations of governmental conservation incentive programs for private landowners are lacking (but see York, Janssen, & Carlson, 2006 for an institutional assessment of several incentive programs in Indiana). Most studies still rely on the assessment of program outputs (e.g., how many landowners are enrolled in the program, or, how many landowner workshops were held) instead of program outcomes (e.g., has the program caused a change in landowners' conservation behaviors, or, has the program led to a recovery of ecological function) (Kilgore et al, 2018). The current study is a rare exception from this pattern and stands out for its analysis of the reported behavior of participants in two conservation programs as well as for its quasi-experimental design utilizing two treatment levels (CLTIP and MFTIP) and a control group (not participating in either program) (but see Josefsson et al, 2017).…”
Section: Discussionmentioning
confidence: 99%
“…Because of the importance of private land for conservation in southern Ontario, conservation legislation and programs that aim specifically at private land (agricultural and nonagricultural) are of major importance in this region. Accordingly, instead of using penal legislation to punish conservationdetrimental behaviors, increasingly conservation incentive programs are used to reward conservation-friendly behaviors, including conservation tax incentive programs (Kamal, Grodzi nska-Jurczak, & Brown, 2015;Kilgore, Ellefson, Funk, & Frey, 2018). Provincial conservation legislation does apply to private land, but in many cases provincial legislations is not enforced either due to financial resource constraints that limit government agencies' enforcement efficacy or because of governmental concern for political backlash if conservation legislation would be enforced strictly (e.g., Melstrom, Lee, & Byl, 2018).…”
Section: Introductionmentioning
confidence: 99%
“…Provincial conservation legislation does apply to private land, but in many cases provincial legislations is not enforced either due to financial resource constraints that limit government agencies' enforcement efficacy or because of governmental concern for political backlash if conservation legislation would be enforced strictly (e.g., Melstrom, Lee, & Byl, 2018). Accordingly, instead of using penal legislation to punish conservationdetrimental behaviors, increasingly conservation incentive programs are used to reward conservation-friendly behaviors, including conservation tax incentive programs (Kamal, Grodzi nska-Jurczak, & Brown, 2015;Kilgore, Ellefson, Funk, & Frey, 2018).…”
Invasive species are a large and growing threat to biodiversity and ecosystem service provisioning globally as well as in southern Ontario, Canada's most biodiverse region. As in many other world regions, most land in southern Ontario is privately owned and therefore conservation programs that aim at private lands are important.
“…Reasons for this lack of uptake include technical difficulties, organizational barriers that do not facilitate a culture of evaluation, and political obstacles (Keene & Pullen, 2011). Most studies still rely on the assessment of program outputs (e.g., how many landowners are enrolled in the program, or, how many landowner workshops were held) instead of program outcomes (e.g., has the program caused a change in landowners' conservation behaviors, or, has the program led to a recovery of ecological function) (Kilgore et al, 2018). Most studies still rely on the assessment of program outputs (e.g., how many landowners are enrolled in the program, or, how many landowner workshops were held) instead of program outcomes (e.g., has the program caused a change in landowners' conservation behaviors, or, has the program led to a recovery of ecological function) (Kilgore et al, 2018).…”
Section: Discussionmentioning
confidence: 99%
“…Especially, impact evaluations of governmental conservation incentive programs for private landowners are lacking (but see York, Janssen, & Carlson, 2006 for an institutional assessment of several incentive programs in Indiana). Most studies still rely on the assessment of program outputs (e.g., how many landowners are enrolled in the program, or, how many landowner workshops were held) instead of program outcomes (e.g., has the program caused a change in landowners' conservation behaviors, or, has the program led to a recovery of ecological function) (Kilgore et al, 2018). The current study is a rare exception from this pattern and stands out for its analysis of the reported behavior of participants in two conservation programs as well as for its quasi-experimental design utilizing two treatment levels (CLTIP and MFTIP) and a control group (not participating in either program) (but see Josefsson et al, 2017).…”
Section: Discussionmentioning
confidence: 99%
“…Because of the importance of private land for conservation in southern Ontario, conservation legislation and programs that aim specifically at private land (agricultural and nonagricultural) are of major importance in this region. Accordingly, instead of using penal legislation to punish conservationdetrimental behaviors, increasingly conservation incentive programs are used to reward conservation-friendly behaviors, including conservation tax incentive programs (Kamal, Grodzi nska-Jurczak, & Brown, 2015;Kilgore, Ellefson, Funk, & Frey, 2018). Provincial conservation legislation does apply to private land, but in many cases provincial legislations is not enforced either due to financial resource constraints that limit government agencies' enforcement efficacy or because of governmental concern for political backlash if conservation legislation would be enforced strictly (e.g., Melstrom, Lee, & Byl, 2018).…”
Section: Introductionmentioning
confidence: 99%
“…Provincial conservation legislation does apply to private land, but in many cases provincial legislations is not enforced either due to financial resource constraints that limit government agencies' enforcement efficacy or because of governmental concern for political backlash if conservation legislation would be enforced strictly (e.g., Melstrom, Lee, & Byl, 2018). Accordingly, instead of using penal legislation to punish conservationdetrimental behaviors, increasingly conservation incentive programs are used to reward conservation-friendly behaviors, including conservation tax incentive programs (Kamal, Grodzi nska-Jurczak, & Brown, 2015;Kilgore, Ellefson, Funk, & Frey, 2018).…”
Invasive species are a large and growing threat to biodiversity and ecosystem service provisioning globally as well as in southern Ontario, Canada's most biodiverse region. As in many other world regions, most land in southern Ontario is privately owned and therefore conservation programs that aim at private lands are important.
“…On the opposite, also tax programs exist, that are implemented as added land tax or sanction to protect forests from being converted to other uses (Hibbard et al 2001;Kilgore et al 2007;Šálka et al 2017). Land tax incentives are politically feasible because of their less demanding implementation, meaning that no direct expenditure is required, the administration is easier, and no additional action is required (Weimer & Vining 2011;Kilgore et al 2018).…”
Preferential land tax programs are used over 50 years and are mainly connected with nature protection and environmental goals. Nowadays, they are also considered as a way how to promote and support forest ecosystem services that arise from exempted forest land. In Slovak Republic national forest land tax reduction scheme exists for special purpose and protection forests, as well for other forests with special importance. The goal of the paper was to develop a multidimensional evaluation of this economic instrument for ecosystem service support in Slovakia. We evaluated how the forest land tax reduction fits into the payments for ecosystem services theory, which services are supported and what is the potential and implementation effectiveness according to theory of policy analysis. Even though, the forest owners and enterprises benefit from tax reductions, evidence regarding its visibility as payment for ecosystem service is low. Forest land tax reductions are considered as other economic incentive for ecosystem services support with moderate potential effectiveness. Despite the instrument have low visibility of FES supported from both sides – sellers and beneficiaries, its potential effectiveness is high, due its automatic and stable implementation without relevant implementation gaps.
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