Evidence of anticipatory forest use behaviours under policy introduction: a systematic map protocol
Environmental Evidence volume 12, Article number: 20 (2023)
Forest conservation is a major global policy goal, due to the role forests play in climate change mitigation and biodiversity conservation. It is well recognized that the introduction of policies, whether aimed at forest conservation or with other objectives, has the potential to trigger unintended outcomes, such as displacement or leakage, which can undermine policy objectives. However, a set of outcomes that has escaped detailed scrutiny are anticipatory forest use behaviours, emerging when forest stakeholders anticipate policy implementation, deploying for example pre-emptive forest clearing, resulting in detrimental environmental outcomes. Lack of understanding of the extent and sectorial scope of these behaviours prevents us from devising strategies to address their potential detrimental consequences.
This protocol presents the methodology that will be followed to conduct a systematic map to identify, compile, review and describe the evidence available on anticipatory forest use behaviours in the context of policy introduction around the world. We will use two complementary search strategies, which we have tested before submitting this protocol. First, a systematic bibliographic search, and second, a citation chase approach. We will include articles based on a pre-defined set of criteria defined according to a Population, Intervention and Outcome (i.e. PIO) design. To support identification of knowledge gaps and clusters, we will report results of the systematic map in a narrative synthesis, an evidence atlas and other visualisations.
Sound forest conservation policy is needed to tackle the combined challenges of climate change and biodiversity decline , for which standing forests play a key role [6, 54]. The forest conservation agenda is receiving attention at the highest level of international policy making; for example at the United Nations Climate Conference of Parties 26, leaders from 141 countries pledged to stop deforestation by 2030 . However, the introduction of policy, whether aimed at forest conservation or other objectives, has the potential to trigger unexpected outcomes. In forest conservation approaches, such as the establishment of terrestrial protected areas, one of the best studied unexpected outcomes is displacement effects (also known as leakage), where avoided deforestation is spatially displaced elsewhere . The implications of these unintended outcomes of forest conservation policy are well understood and considered by policy makers [5, 46]. However, a set of unintended outcomes of forest conservation policy introduction that has so far escaped detailed scrutiny is that of anticipatory behaviours, where forest edge residents, landholders or forest users change behaviour in advance of policy implementation.
Anticipatory behaviours are well-known in other policy contexts, and have been investigated extensively in the economics literature, for example in the case of taxation [1, 7] or health policy reform , or housing markets under urban development dynamics . In the case of environmental policy introduction, anticipatory behaviours might result in what has been labelled in the climate policy sector the Green Paradox , where introduction of tighter regulation results in increasing pre-emptive extraction of fossil fuels , or a policy aimed at reducing pollution initially increases it . In the context of biodiversity conservation, anticipatory behaviours have been demonstrated in the case of international wildlife trade, with traders anticipating species-wide trade bans by increasing commercial transactions of the species targeted before the ban is implemented [38, 45]. A comparable phenomenon has been observed in cases of marine reserve establishment , or the management of fishing quotas : in both cases with fishers anticipating the implementation of the policy change by increasing their short-term fishing efforts.
In the context of introduction of policy directly aimed at forest conservation, several cases of anticipatory behaviours have been reported (Table 1) across biomes and country income levels (Fig. 1). A classic example is the case of the Endangered Species Act introduced in the United States in the 1970s and updated subsequently to include new species for habitat conservation. To avoid restrictive land use regulations, in several cases landowners pre-emptively destroyed an endangered species’ habitat within their property between the moment the species was listed for protection and the prohibition to damage its habitat was actually enforced [32, 35, 57]. A comparable situation emerged in Queensland, Australia, with landholders ‘panic clearing’ native forests and woodlands in advance of the implementation of and amendments to vegetation management regulations restricting land clearing from the 1990s to the 2010s [44, 48]. In the case of area-based forest conservation interventions, such as establishment of terrestrial protected areas, a related phenomenon was reported in Northeastern Madagascar, with forest edge populations increasing their forest clearing efforts before the protected area was in place, in an attempt to secure agricultural land [30, 33]. Such pre-emptive forest clearing was also found in voluntary participation in sustainability certification of agricultural commodities production, such as palm oil, in Sumatra and Kalimantan, Indonesia .
Policy changes that are not directly concerned with forest can also result in anticipatory behaviours negatively affecting forest cover or condition. For example, when a land registration initiative is being initiated, local populations might clear forest to access agricultural land in the expectation they will obtain a statutory recognition for that parcel, such as a title or certificate. This was found to have happened in the case of a nation-wide program in Cambodia , and likely also in Southern Madagascar , although land titling does not always result in such an effect .
These examples suggest that anticipatory forest use behaviours might be a common response to policy introduction, potentially undermining the intervention’s objectives. However, no systematic evidence synthesis has been conducted on the phenomenon. To fill in this knowledge gap, we will develop a systematic map to compile and synthesize the global evidence of the emergence of anticipatory forest use behaviours under policy introduction contexts detrimentally affecting forest cover or condition. Given that this is the first such evidence synthesis effort, a systematic map is the most appropriate approach because of uncertainty about the extent to which these behaviours have been studied and reported, as well as likely wide variation in the type and quality of the reports in the literature. Systematically mapping the evidence available on these behaviours might benefit environmental policy and management by providing an accessible and easy to consult repository of cases , helping increase decision-maker’s awareness of the risk of policies triggering such unintended behaviours, and may stimulate more formal study of the phenomenon. The evidence on anticipatory forest use behaviours under policy introduction already listed above has been compiled into an initial benchmark list (Fig. 1; Table 1, Additional file 1), which has helped to inform and test our search strategies (see below). This evidence was gathered by the authors over recent years, and expanded through a call for evidence from experts released by the first author on the social media network Twitter in April 2022.
Objective of this systematic map
The objective of this systematic map is to assemble and map the current state of evidence describing anticipatory forest use behaviours as a result of policy introduction, focusing on behaviours that detrimentally affect forest cover or condition.
The primary research question that will guide the systematic map is: What is the state of the evidence on anticipatory forest use behaviours in the context of policy introduction?
This question was defined by the reviewing team after consultation with relevant stakeholders consulted prior to submitting this protocol for review.
Elements of the primary question
This systematic map will follow a population-intervention-outcome (P.I.O) framework, with the question elements being the following.
We focus on global forests as the population of interest. The global nature of this systematic map is justified on the basis of the evidence on anticipatory forest use behaviours gathered so far (Additional file 1), which have been found across country income levels and biomes (Fig. 1).
The interventions of interest in this systematic map are the policies prompting anticipatory forest use behaviours that detrimentally affect forest cover or condition.
The outcome of interest in this systematic map is the anticipatory forest use behaviour the policy intervention triggered, that would have been regulated by the intervention, and that detrimentally affects forest cover or condition.
This evidence synthesis will follow guidance on systematic maps [28, 41], and will conform with ROSES reporting standards  (Additional file 3). This protocol has been compiled following the Collaboration for Environmental Evidence guidelines 8 .
Given the applied nature of this research, and the urgency to transfer the knowledge to relevant stakeholders, we will follow best practice guidance on stakeholder engagement . We have identified a group of stakeholders with expertise in each of the broad policy areas we have found to trigger anticipatory forest use behaviour so far. Concretely, we are consulting with an expert on terrestrial protected areas establishment and management, an expert on land tenure specializing in land rights formalization processes, and an expert on sustainable agricultural production at the forest frontier. Expert is understood here as an individual with practical experience in development or implementation of environmental policy or an established researcher who has focused much of his or her scientific career on the intervention we are interested in. We have shared the protocol with these stakeholders in parallel to the review process in the Environmental Evidence journal, and their input was implemented at the same time that we addressed the reviewers’ comments on the protocol. The author team will also request comments about the clarity of the final report from these stakeholders once the synthesis is conducted.
Our review team is also highly interdisciplinary with links to relevant areas of policy. We have one specialist in global land use policy (RG), an expert on protected areas (JPGJ), and an expert on pre-emptive forest clearing behaviours (BAS), as well as an expert on evidence syntheses (NRH).
For this systematic map we will follow two complementary search strategies: a bibliographic search, and a citation chasing strategy.
Strategy A—bibliographic search
We will conduct a comprehensive bibliographic search through four bibliographic and two dissertation platforms (Table 2), one search engine (Google Scholar) and 67 organisational websites (Additional file 4). We have developed a search string (Table 3) based on the terms employed by the initial benchmark articles to describe anticipatory forest use behaviours, including relevant synonyms to those terms, as well as extracting terms used to describe forest ecosystems in other systematic map protocols (e.g. ). We have included in the search string the population element of the research question (e.g. forest, woodlands, etc.), as well as the outcome element, separated into the forest use behaviour undertaken (e.g. deforestation, clearing, expansion, etc.) and terms which seek to capture the anticipatory character of the behaviour (e.g. pre-emptive, anticipatory, unprecedented, etc.). We have not included the intervention element given that, after testing different search string including it (Additional file 5), we realised that its inclusion produced a heavily inefficient string that resulted in insufficient specificity, thus returning a large number of results not relevant to the research question. The search string was tested and refined as explained in Additional file 5, to keep a balance between sensitivity and retrieving a manageable amount of articles. On a scoping search we conducted on 19/06/2023 in Web of Science Core Collection and Scopus on title, abstract and keywords (respectively TOPIC and TITLE-ABS-KEY), our search string returned 7407 and 9695 results respectively.
We will search in the bibliographic databases presented in Table 2. Some collections contained on certain platforms do not allow exporting results, so we will exclude those databases for our search. For the dissertation databases, we will restrict the search to items for which full text is available in the respective databases. For searching Google Scholar we will adapt the search string, and use the “Publish or Perish”  tool, including the first 300 results as recommended when using Google Scholar for this task .
The 67 organisational websites selected (Additional file 4) were chosen based on the research team’s expertise, complemented by retrieving the list of organisational websites employed in other forest-related systematic map protocols . Where the publications page does not provide an advanced search function, we will first use the search string for the population element (Table 3) and look into the first 50 records of each website. In the case of websites of forest-related organisations, we will instead use the string for the outcome element. Where the search options include searching by topics, only those most relevant to the objective of this systematic map will be searched into (e.g. forestry, rural livelihoods, etc.). We will not investigate scientific articles contained within organisational websites, as these will be captured by our search of bibliographic databases. Results from searching into organisational websites will be downloaded and merged with results from the bibliographic search when possible. In cases where downloading results in a .csv format is not possible, we will systematically download results using either the Grey Literature Search Recorder app (https://www.eshackathon.org/software/grey-lit-reporter.html), the greylitsearcher Shiny app , Publish and Perish , or the Data Miner Chrome extension (https://dataminer.io). If that is not possible in specific websites, we will screen the items online, and relevant results will be exported.
After screening results, the articles (see Article Screening section below), the articles found to be relevant will be merged with those in the initial benchmark list (Additional file 1), to elaborate an extended benchmark list, on which we will apply the citation chase approach (see below).
Strategy B—citation chasing
We will apply a citation chase strategy on the extended article benchmark produced from the bibliographic search. We will conduct both, backward citation chase (i.e. gathering the references cited by the benchmark articles), and forward citation chase (i.e. retrieving the articles citing those in the benchmark). When backward citation chasing on books (edited or otherwise), dissertations, and organisational reports, we will only explore references from the chapters or sections containing the information we are interested in (i.e. on anticipatory forest use behaviours). Second, we will remove results that are either newspaper articles, court hearings, government documents (e.g. including laws, decrees, official speeches, etc.), as well as results obviously not relevant to this study, such as references to datasets, methods, R packages, etc., and all results that are not in English language. Third, we will remove duplicates. And fourth, we will screen for relevance the remaining articles at title and abstract level (concurrently), and then proceed to full text screening those articles found relevant at title and abstract following the inclusion criteria listed below.
We tested the performance of the dedicated tool citationchaser , available as an R package and a Shiny app, on the initial article benchmark. For the backward citation chase we tested the performance of the citationchaser Shiny app against the same task conducted through Web of Science, Scopus and manually. Results (Additional file 6) indicate that citationchaser performed worse (it got fewer references from each benchmark article) than Web of Science or Scopus, while Scopus yielded nearly identical results to manually extracting the references. For the forward citation chase, we compared the performance of the citationchaser Shiny app in finding the articles citing those in the benchmark against the same task in Web of Science, Scopus and Google Scholar. We found that citationchaser performed better (it found more citations for the benchmark articles) than either Web of Science or Scopus, but worse than Google Scholar.
Based on these tests, we will therefore use Scopus for backward citation chasing; manually extracting references from those articles in the extended benchmark that are not found in that database (mostly those without a DOI), and those for which Scopus yielded fewer references than we manually counted in the benchmark article. For forward citation chase, we will use the citationchaser Shiny app, resorting to Scopus in the case citationchaser cannot find any citation for the specific article, and using as last option Google Scholar, which seems the appropriate sequence based on more in-depth tests conducted on using Google Scholar to obtain citations .
Estimating comprehensiveness of the search
To check how comprehensive our overall search approach is, we have tested the strength of the combined two search strategies at finding the articles in the initial benchmark (Fig. 2). The numbers presented are based on the search string test (Strategy A and Additional file 5) and the citation chase test (Strategy B and Additional file 6).
Citation chase is the strongest search strategy, finding 17 out of the 24 articles in the initial benchmark (Fig. 2). The bibliographic search managed to capture 12 benchmark articles. Together, the combined strategies captured 20 articles (83%). Of the benchmark articles that we could not detect, two were an organisational report , and a relatively old conference proceeding , both without a DOI and not indexed in any bibliographic dataset. The remaining two were Seghezzo et al.  and Milne  but which did not mention anticipatory forest use behaviours in title or abstract. We recognised that the search strategy is not perfect, although after extensive testing we believe our approach is as good as possible with the resources available.
Article screening and study inclusion criteria
We will retrieve title, abstract and all other information for all articles sought through search strategies A and B, import them into a reference manager software (i.e. Zotero or EndNote), and deduplicate results. Where different versions of the same article are found (e.g. a pre-print version and a definitive published version), we will keep the published version. Unique records will be then imported to an open access online tool designed for the management of systematic reviews and maps, either Rayyan  or CADIMA . After the consistency check (see below), screening articles will be performed by at least two members of the review team independently, with the full dataset of records distributed among the reviewers.
Checking consistency will be conducted across the screening process at both stages, i.e. title/abstract and full text. A random subset of 10% of the articles to be screened will be screened concurrently at title and abstract by all reviewers. We will then calculate the Cohen’s Kappa score , identify and discuss the reasons for disagreement article by article, and clarify the inclusion criteria. In the case the Kappa score does not reach a minimum of 0.6 in this first consistency check (indicating lack of consistency among reviewers), another 10% of articles will be then screened by all reviewers, and disagreements discussed. We will then calculate the corresponding Kappa score, again aiming at having a minimum of 0.6 to proceed to the next stage. In the case agreement between reviewers is still not achieved at this stage, we will repeat the procedure and check for consistency until agreement is reached. Once we have reached agreement among reviewers at the title/abstract screening stage, we will proceed to full text screening, conducting a similar consistency check.
We will decide whether to include screened articles in the systematic map according to clear inclusion criteria. First we will check whether the article focuses on the appropriate Population, Intervention and Outcomes (see below for expanded definitions). When screening at title/abstract level for inclusion to full text screening, we will tend towards inclusion where there is uncertainty, given that in many occasions, the articles found reporting on anticipatory forest use behaviours at full text do not do so on title or abstract. Only articles in English will be included, given resource constraints. We do not have a date range criterion for inclusion of articles, given that this is the first evidence synthesis conducted on anticipatory forest use behaviours.
The study mentions forest ecosystems or related concepts. Articles in the initial benchmark refer to forests in varied ways including ‘native vegetation’, ‘woodland’, or ‘habitat’ (see search string in Table 3). Given that most articles in the initial benchmark (Additional File 1) do not provide a definition of forest, providing such a definition is not an inclusion criterion. We will nonetheless compile definitions of forests from included articles whenever they are provided, and present them in the final systematic map report. We will not restrict inclusion by forest biome or country, given that the initial benchmark includes studies from a wide range of biomes and countries. However, included studies need to mention the place where the behaviour emerged, at least at the national level.
The study mentions the policy that triggered the anticipatory forest use behaviour. We will include studies that provide evidence on any of the policies already found to encourage anticipatory behaviours, either with direct forest conservation objectives or otherwise (See initial article benchmark in Additional file 1), and also any other policy not yet captured in the benchmark articles. Given that we found anticipatory behaviours triggered by a wide range of policies (Table 1), and that the articles compiled in the initial benchmark (Additional file 1) are unlikely to capture the entire range of possible interventions triggering such behaviours, we do not define a priori the potential interventions. Policy in this systematic map is understood in a broad sense, including implementation of new laws, regulations or guidance, and changes or updates to existing policy. The policies of interest include global, national or sub-national policy instruments with a broad sectorial scope, including those with conservation objectives (e.g. establishment of terrestrial protected areas, species conservation regulations, REDD + projects), and those which might indirectly influence forest dynamics (e.g. land registration programs, agrarian reform processes, sustainability certification of agricultural commodities).
We refer to policy introduction as the entire process of policy development, including policy design, political discussions preceding implementation, announcement of the policy and actual implementation. We understand policy implementation as the cut-off date when the policy took effect, such as when a protected area was established, or a policy enacted.
To be included in the systematic map, the study needs to provide information about the date when the policy (or policy change) was implemented, or at least when the policy was or is expected to be implemented in the case it is not yet in place. We will also include studies where anticipatory behaviours were found to emerge in the case of policies that were planned but eventually were not implemented.
The study describes anticipatory forest use behaviours, regardless of whether the term ‘anticipatory’ is used or not. The key inclusion criteria is that the study suggests anticipation of the policy as a likely explanation for the emergence of changes in land use which detrimentally affect forest cover or condition. These can include among others anticipatory behaviours that involve increases in the following forest cover dynamics: reduction of forest cover (e.g. clearing of forest for conversion to agriculture or other land use, clear cutting of timber), reduction of forest condition (e.g. selective logging, charcoal production) or others not yet identified in our benchmark.
Given that this is the first evidence synthesis on such type of complex behaviours, we will lean towards inclusion of all types of evidence on them. We will include articles where anticipatory forest use behaviours were explicitly expected to be emerge, but could not be detected (e.g. ), articles that provide anecdotal evidence on the behaviours, even if the article did not have them as the main focus of study (e.g. ), and articles where, the authors argue that they might be emerging and provide plausible mechanisms (e.g. ).
Relevant study design(s)
No study design types will be excluded during the screening stages. We will only include studies providing new evidence, and not those articles referring to secondary evidence (e.g. referring to other studies’ evidence). Exceptions to this rule will be made in the cases that the article screened reports evidence found in a type of source we are not screening, such as articles in languages others than English, government reports, books or newspaper articles. We will include articles where the primary data was collected elsewhere, but has not yet been reported.
Reasons for exclusion
We will include in the final systematic map report a list with the studies excluded after full text screening, with the reasons for exclusion for each of them. Each study must meet all the inclusion criteria presented above to be considered relevant for this systematic map. We will thus exclude articles that do not provide information on each of our research question’s elements, i.e. they do not focus on forests (population) and on forest cover change (outcome-forest use behaviour), do not mention policy introduction (intervention), or do not mention anticipation (outcome-character of the behaviour). We will also exclude articles in languages other than English, as well as review articles, unless the evidence reported there is not available elsewhere.
Data coding and extraction strategy
Data coding and extraction will be done to a large extent by the corresponding author (between 30% and 50% of the total included studies), as done in other systematic maps , who will then harmonize the way the data is extracted by the rest of the review team. For each included study, we will extract information on the variables presented in Table 4. One article can describe several studies, e.g. if the article is dealing with distinct locations, policy interventions or time periods. Where an article provides sufficient information to disaggregate into separate studies, we will extract and code information for studies separately. Also, several articles can refer to the same study, e.g. same location, policy and time period. In that case, and whenever the evidence provided is first hand, we will include all articles referring to the same study, classifying the study as a unique one, to make sure there are not duplicated studies in the final map. The metadata form has been tested on the 24 articles in the initial benchmark (Additional file 2).
Data synthesis and presentation
Narrative synthesis and presentation
We will summarize results through a narrative synthesis of the data provided by the included studies, supported by the following elements. We will present a ROSES flow diagram  detailing the systematic mapping process, including the number of articles obtained through each search strategy, those included and excluded at each screening stage, and the total number of relevant studies after full text level screening. We will provide a list of articles excluded after full text screening, with the reasons for exclusion. We will compute and present descriptive statistics on the distribution and trends of included studies. We will produce a world map presenting the location of the included studies, using the Shiny app EviAtlas , which allows to cluster points to aid visualization in the case the number of studies in a given region is too large. The world map will be provided in the final report of this systematic map and hosted online. Matrices or heatmaps presenting the number of studies for at least the following interactions between variables: type of intervention and anticipatory behaviour, country income level and anticipatory behaviour, and forest biome and anticipatory behaviour. In addition to the narrative report, world map, and accompanying figures and tables, we will upload the dataset online, with the possibility of filtering studies by for example, location, type of intervention, biome, or any other of the attributes extracted from the included studies (Table 4). The dataset will be free for users to download, which will be made available in a website we will create for this purpose, hosted in the first author’s GitHub account.
Knowledge gap and cluster identification strategy
We expect to be able to identify knowledge gaps on, for example, policy sectors, which might indicate where primary research is more urgently needed. Regarding knowledge clusters, given that this is the first evidence synthesis conducted on anticipatory forest use behaviours, we do not expect to be able to identify areas where the evidence base is large enough to be amenable to further, narrower systematic reviews. We will use all the knowledge gathered through this to elaborate hypotheses as of to why the evidence is more present or absent in certain regions or policies, and point to potential research and policy gaps accordingly.
Demonstrating procedural independence
No member of the review team will work on any articles authored by themselves, either at the screening or the data extraction stages.
Availability of data and materials
All data generated or analysed during this study will be included in the published article and its supplementary information files.
Ahmad N, Xiao W. End of double taxation: is the policy better when announced? J Policy Model. 2013;35(6):928–42. https://doi.org/10.1016/j.jpolmod.2012.12.004.
Aldrich S, Walker R, Simmons C, Caldas M, Perz S. Contentious land change in the Amazon’s Arc of Deforestation. Ann Assoc Am Geogr. 2012;102(1):103–28. https://doi.org/10.1080/00045608.2011.620501.
Alpert A. The anticipatory effects of Medicare Part D on drug utilization. J Health Econ. 2016;49:28–45. https://doi.org/10.1016/j.jhealeco.2016.06.004.
Alston LJ, Libecap GD, Mueller B. Land Reform Policies, the sources of violent conflict, and implications for Deforestation in the brazilian Amazon. J Environ Econ Manag. 2000;39(2):162–88. https://doi.org/10.1006/jeem.1999.1103.
Barnes MD, Glew L, Wyborn C, Craigie ID. Prevent perverse outcomes from global protected area policy. Nat Ecol Evol. 2018;2(5):759–62. https://doi.org/10.1038/s41559-018-0501-y.
Betts MG, Wolf C, Ripple WJ, Phalan B, Millers KA, Duarte A, Butchart SHM, Levi T. Global forest loss disproportionately erodes biodiversity in intact landscapes. Nature. 2017;547(7664):441–4. https://doi.org/10.1038/nature23285.
Bolster PJ, Janjigian V. Dividend policy and valuation effects of the Tax Reform Act of 1986. Natl Tax J. 1991;44(42):511–8. https://doi.org/10.1086/ntj41788937.
Börner J, Schulz D, Wunder S, Pfaff A. The effectiveness of forest conservation policies and programs. Annu Rev Resour Econ. 2020;12(1):45–64. https://doi.org/10.1146/annurev-resource-110119-025703.
Carlson KM, Heilmayr R, Gibbs HK, Noojipady P, Burns DN, Morton DC, Walker NF, Paoli GD, Kremen C. Effect of oil palm sustainability certification on deforestation and fire in Indonesia. Proceedings of the National Academy of Sciences. 2018;115(1): 121–126. doi: https://doi.org/10.1073/pnas.1704728114.
Cheng SH, Costedoat S, Sterling EJ, Chamberlain C, Jagadish A, Lichtenthal P, Nowakowski AJ, Taylor A, Tinsman J, Canty SWJ, Holland MB, Jones KW, Mills M, Morales-Hidalgo D, Sprenkle-Hyppolite S, Wiggins M, Mascia MB, Muñoz CL, Brenes. What evidence exists on the links between natural climate solutions and climate change mitigation outcomes in subtropical and tropical terrestrial regions? A systematic map protocol. Environ Evid. 2022;11(1):15. https://doi.org/10.1186/s13750-022-00268-w.
Chiwona-Karltun L, Kimanzu N, Clendenning J, Lodin JB, Ellingson C, Lidestav G, Mkwambisi D, Mwangi E, Nhantumbo I, Ochieng C, Petrokofsky G, Sartas M. What is the evidence that gender affects access to and use of forest assets for food security? A systematic map protocol. Environ Evid. 2017;6(1):2. https://doi.org/10.1186/s13750-016-0080-9.
Cohen J. A coefficient of Agreement for Nominal Scales. Educ Psychol Meas. 1960;20(1):37–46. https://doi.org/10.1177/001316446002000104.
Collaboration for Environmental Evidence. Guidelines and Standards for Evidence synthesis in Environmental Management. Version 5.0. 2018. Accessed 25 Apr 2022.
Dinerstein E, Olson D, Joshi A, Vynne C, Burgess ND, Wikramanayake E, Hahn N, Palminteri S, Hedao P, Noss R, Hansen M, Locke H, Ellis EC, Jones B, Barber CV, Hayes R, Kormos C, Martin V, Crist E, Sechrest W, Price L, Baillie JEM, Weeden D, Suckling K, Davis C, Sizer N, Moore R, Thau D, Birch T, Potapov P, Turubanova S, Tyukavina A, de Souza N, Pintea L, Brito JC, Llewellyn OA, Miller AG, Patzelt A, Ghazanfar SA, Timberlake J, Klöser H, Shennan-Farpón Y, Kindt R, Lillesø J-PB, van Breugel P, Graudal L, Voge M, K. F. Al-Shammari and, Saleem M. An Ecoregion-Based Approach to Protecting Half the Terrestrial Realm. BioScience. 2017;67(6): 534–545. 10.1093/biosci/bix014
Fiorini ACO, Swisher M, Putz FE. Payment for Environment Services to promote compliance with Brazil’s Forest Code: the case of “Produtores de Água e Floresta. Sustainability. 2020;12(19):8138.
Grimsditch M, Schoenberger L. New actions and existing policies: the implementation and impacts of Order 01. Phnom Penh, Cambodia: The NGO Forum on Cambodia, Land and Livelihoods Program; 2015.
Haddaway NR. Greylitsearcher: an R package and Shiny app for systematic and transparent searching for grey literature. Zenodo. 2022. https://doi.org/10.5281/zenodo.6451616.
Haddaway NR, Crowe S. Stakeholder engagement in environmental evidence synthesis. Mistra EviEM: Stockholm; 2018. p. 166.
Haddaway NR, Collins AM, Coughlin D, Kirk S. The role of Google Scholar in evidence reviews and its applicability to Grey Literature Searching. PLoS ONE. 2015;10(9):e0138237. https://doi.org/10.1371/journal.pone.0138237.
Haddaway NR, Bernes C, Jonsson B-G, Hedlund K. The benefits of systematic mapping to evidence-based environmental management. Ambio. 2016;45(5):613–20. https://doi.org/10.1007/s13280-016-0773-x.
Haddaway NR, Macura B, Whaley P, Pullin AS. ROSES flow diagram for systematic maps. Version 1 0. 2017. https://doi.org/10.6084/m9.figshare.6085940.
Haddaway NR, Macura B, Whaley P, Pullin AS. ROSES RepOrting standards for systematic evidence Syntheses: pro forma, flow-diagram and descriptive summary of the plan and conduct of environmental systematic reviews and systematic maps. Environ Evid. 2018;7(1):7. https://doi.org/10.1186/s13750-018-0121-7.
Haddaway NR, Feierman A, Grainger MJ, Gray CT, Tanriver-Ayder E, Dhaubanjar S, Westgate MJ. EviAtlas: a tool for visualising evidence synthesis databases. Environ Evid. 2019;8(1):22. https://doi.org/10.1186/s13750-019-0167-1.
Haddaway NR, Grainger MJ, Gray CT. Citationchaser: a tool for transparent and efficient forward and backward citation chasing in systematic searching. Res Synth Methods. 2022;13(4):533–45. https://doi.org/10.1002/jrsm.1563.
Harzing AW. Publish or perish. 2007. https://harzing.com/resources/publish-or-perish. Accessed 25 Jan 2023
Holzer J, DePiper G. Intertemporal quota arbitrage in multispecies fisheries. J Environ Econ Manag. 2019;93:185–207. https://doi.org/10.1016/j.jeem.2018.12.002.
Hyun D, Milcheva S. Spatio-temporal effects of an urban development announcement and its cancellation on house prices: a quasi-natural experiment. J Hous Econ. 2019;43:23–36. https://doi.org/10.1016/j.jhe.2018.09.008.
James KL, Randall NP, Haddaway NR. A methodology for systematic mapping in environmental sciences. Environ Evid. 2016;5(1):7. https://doi.org/10.1186/s13750-016-0059-6.
Jensen S, Mohlin K, Pittel K, Sterner T. An introduction to the Green Paradox: the Unintended Consequences of Climate policies. Rev Environ Econ Policy. 2015;9(2):246–65. https://doi.org/10.1093/reep/rev010.
Keller E. Beyond the Lens of Conservation. Malagasy and swiss imaginations of one another. New York and Oxford: Berghahn Books; 2015. p. 244.
Kohl C, McIntosh EJ, Unger S, Haddaway NR, Kecke S, Schiemann J, Wilhelm R. Online tools supporting the conduct and reporting of systematic reviews and systematic maps: a case study on CADIMA and review of existing tools. Environ Evid. 2018;7(8):1–17. https://doi.org/10.1186/s13750-018-0115-5.
List JA, Margolis M, Osgood DE. Is the endangered species act endangering species? working paper series 12777. Cambridge: National Bureau of Economic Research; 2006.
Llopis JC, Harimalala PC, Bär R, Heinimann A, Rabemananjara ZH, Zaehringer JG. Effects of protected area establishment and cash crop price dynamics on land use transitions 1990–2017 in north-eastern Madagascar. J Land Use Sci. 2019;14(1):52–80. https://doi.org/10.1080/1747423X.2019.1625979.
Lott CA, Akresh ME, Elmore AJ, Fiss CJ, Fitzpatrick MC, Joos CJ, King DI, McNeil DJ, Stoleson SH, Larkin JL. What evidence exists for landbird species-environment relationships in eastern temperate and boreal forests of North America? A systematic map protocol. Environ Evid. 2019;8(1):31. https://doi.org/10.1186/s13750-019-0170-6.
Lueck D, Jeffrey AM. Preemptive Habitat Destruction under the endangered Species Act. J Law Econ. 2003;46(1):27–60. https://doi.org/10.1086/344670.
Martín-Martín A, Orduna-Malea E, Thelwall M, Delgado López-Cózar E. Google Scholar, web of Science, and Scopus: a systematic comparison of citations in 252 subject categories. J Informetrics. 2018;12(4):1160–77. https://doi.org/10.1016/j.joi.2018.09.002.
McDermott GR, Meng KC, McDonald GG, Costello CJ. The blue paradox: Preemptive overfishing in marine reserves. Proceedings of the National Academy of Sciences. 2018;116(12): 5319–5325. 10.1073/pnas.1802862115
Mialon HM, Klumpp T, Williams MA. International trade and the survival of mammalian and reptilian species. Sci Adv. 2022;8(1):eabh3442. https://doi.org/10.1126/sciadv.abh3442.
Middleton K. Land rights and alien plants in dryland madagascar. In: Evers S, Campbell G, Lambek M, editors. Contest for land in madagascar. Leiden: Brill; 2013. p. 141–70.
Milne S. Under the leopard’s skin: Land commodification and the dilemmas of indigenous communal title in upland Cambodia. Asia Pac Viewp. 2013;54(3):323–39. https://doi.org/10.1111/apv.12027.
O’Leary BC, Woodcock P, Kaiser MJ, Pullin AS. Evidence maps and evidence gaps: evidence review mapping as a method for collating and appraising evidence reviews to inform research and policy. Environ Evid. 2017;6(1):19. https://doi.org/10.1186/s13750-017-0096-9.
Ouzzani M, Hammady H, Fedorowicz Z, Elmagarmid A. Rayyan — a web and mobile app for systematic reviews. Syst Reviews. 2016;5(1):210. https://doi.org/10.1186/s13643-016-0384-4.
Pfaff A, Robalino J. Spillovers from Conservation Programs. Annual Rev Resource Econ. 2017;9(1):299–315. https://doi.org/10.1146/annurev-resource-100516-053543.
Reside AE, Beher J, Cosgrove AJ, Evans MC, Seabrook L, Silcock JL, Wenger AS, Maron M. Ecological consequences of land clearing and policy reform in Queensland. Pac Conserv Biology. 2017;23(3):219–30. https://doi.org/10.1071/PC17001.
Rivalan P, Delmas V, Angulo E, Bull LS, Hall RJ, Courchamp F, Rosser AM, Leader-Williams N. Can bans stimulate wildlife trade? Nature. 2007;447(7144):529–30. https://doi.org/10.1038/447529a.
Secretariat of the Convention on Biological Diversity. Incentive Measures for the Conservation and Sustainable Use of Biological Diversity: Case Studies and Lessons Learned. CBD Technical Series No.56. 2011. pp. 65
Seghezzo L, Volante JN, Paruelo JM, Somma DJ, Buliubasich EC, Rodríguez HE, Gagnon S, Hufty M. Native forests and agriculture in Salta (Argentina): conflicting visions of development. J Environ Dev. 2011;20(3):251–77. https://doi.org/10.1177/1070496511416915.
Simmons BA, Law EA, Marcos-Martinez R, Bryan BA, McAlpine C, Wilson KA. Spatial and temporal patterns of land clearing during policy change. Land Use Policy. 2018;75:399–410. https://doi.org/10.1016/j.landusepol.2018.03.049.
Sinn H-W. The Green Paradox: a Supply-Side Approach to global warming. Cambridge, Massachusetts, and London, England: The MIT Press; 2012. p. 269.
Stroup RL. The Endangered Species Act: making innocent species the enemy. PERC Policy Series. 1995.
Tomich TP, Van Noordwijk M. What drives deforestation in Sumatra? Paper presented at the Regional Symposium on “Montane Mainland Southeast Asia in Transition” Chiang Mai, Thailand, 13–16 November 1995. Chiang Mai, Thailand. 1995.
UKCOP26. Glasgow Leaders’ Declaration on Forests and Land Use. 2021. https://ukcop26.org/glasgow-leaders-declaration-on-forests-and-land-use/. Accessed 29 Dec 2021
van der Werf E, Di Maria C. Imperfect environmental policy and polluting emissions: the green paradox and beyond. Int Rev Environ Resour Econ. 2012;6(2):153–94. https://doi.org/10.1561/101.00000050.
Watson JEM, Evans T, Venter O, Williams B, Tulloch A, Stewart C, Thompson I, Ray JC, Murray K, Salazar A, McAlpine C, Potapov P, Walston J, Robinson JG, Painter M, Wilkie D, Filardi C, Laurance WF, Houghton RA, Maxwell S, Grantham H, Samper C, Wang S, Laestadius L, Runting RK, Silva-Chávez GA, Ervin J, Lindenmayer D. The exceptional value of intact forest ecosystems. Nat Ecol Evol. 2018;2(4):599–610. https://doi.org/10.1038/s41559-018-0490-x.
World Bank. World Bank Country and Lending Groups. 2023. https://datahelpdesk.worldbank.org/knowledgebase/articles/906519-world-bank-country-and-lending-groups. Accessed 4 Jan 2023
Wren-Lewis L, Becerra-Valbuena L, Houngbedji K. Formalizing land rights can reduce forest loss: experimental evidence from Benin. Sci Adv. 2020;6(26):eabb6914. https://doi.org/10.1126/sciadv.abb6914.
Zhang D. Endangered species and timber harvesting: the case of red-cockaded woodpeckers. Econ Inq. 2004;42:150–65.
The authors thank the comments from editor and three anonymous reviewers, as well as the feedback received from the three policy experts we requested help from. This study contributes to the Global Land Programme (https://glp.earth).
JCL was funded by the Swiss National Science Foundation (SNSF) through grant P500PN_206846. Publication of this work was also funded by the SNSF.
Ethics approval and consent to participate
Consent for publication
The authors declare that they have no competing interests.
Springer Nature remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
Initial article benchmark.
Data extraction test.
ROSES form for systematic map protocol.
List of organisational websites for grey literature searches.
Search string tests.
Results from citation chasing test.
About this article
Cite this article
Llopis, J.C., Haddaway, N.R., Omirbek, N. et al. Evidence of anticipatory forest use behaviours under policy introduction: a systematic map protocol. Environ Evid 12, 20 (2023). https://doi.org/10.1186/s13750-023-00307-0