38 research outputs found

    Governance and benefits sharing in the swedish forest commons

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    Unlike forest commons in many other countries, within Europe and elsewhere, Swedish forest commons are for- med and organised in a particular way in that the parcels (or shares) of forestlands involved are privately owned but as commons they are jointly managed by forest pro- fessionals. Furthermore, shares in forest commons are considered as “set asides” of the private landholding (farm/forest) and thus cannot be owned or sold in isolation. This leaves little space for the shareholders to be ‘hands-on’ in the management of these commons, although they are involved in decision making through a management board they elect. Moreover, it has been claimed that the shareholders in the Swedish forest commons do not bear the costs (for management and governance) proportional to the benefits they receive from their commons.  In this paper, we use data from a mail survey directed to resident shareholders in three of the major forest com- mons in Sweden (Jokkmokk, TĂ€rna-Stensele, and Älvda- len) to assess their satisfaction on the governance and benefits sharing within their forest commons. This study shows that generally a significant majority of the share- holders in these three forest commons seem to be satis- fied with the status quo regarding the governance/ management of their commons and the benefits they accrue. However, women’s participation in most aspects of the forest commons seems to be significantly lower than their male counterpart leaving them benefiting less from their commons as a result

    Impact of land use and land use history on fruits production of Vitellaria paradoxa (Shea tree) according to agroclimatic zones in Mali (West Africa)

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    To understand how various factors influence phenological patterns like fruit production and the extent of phenological variability as survival strategy in different environments, fruit production of shea trees was studied in different agroclimatic zones (North Sudanian, South Sudanian and North Guinean) in Mali. Three sites were selected for this study and in each site; two stands (field and fallow) were concerned. For each stand, three “land use history or land management" i.e. new fields/fallows (1-5 years), medium (6-10 years) and old (10 years) were considered and permanent plots of 0.25 ha were established. 60 adult shea trees (DBH) ? 10 cm) were selected by site and monitored for fruit production assessment. The nested analysis of variance on the yield showed a significant site effect and significant effect of land use history within stand. However, stand effect within site was not significant. Factors like site and land management (land use history) appear to be determinant for fruit production of V. paradoxa. The site of Mperesso in the South Sudanian zone showed the highest fruit mean yield (11 kg/tree), significantly higher than the fruit mean yield observed at Daelan (7 kg/tree) in the North Sudanian zone and that observed at NafĂ©guĂ© (6 kg/tree) in the North Guinean zone. For field stand, old fields showed highest mean yield in all sites. For fallow stand, old fallows showed the lowest mean yield in most of cases. Different pattern was observed between field and fallow stands regarding the effect of land management. More fields are aged, more they influence positively fruit production whereas more fallows are aged, and more they influence negatively fruit production. This study highlighted the importance of land management practices and therefore, any domestication program to be successful should consider the potential effect of management practices

    Mind the gap:the use of research in protected area management in Madagascar

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    It is increasingly well recognised that a lot of conservation-related research is not being used to improve conservation practice. However, much of the research in this area has been conducted with conservation managers in high income countries, where the barriers to accessing and using research may be different. We conducted questionnaires (n=85) and face to face interviews (n=54) with managers of protected areas in Madagascar to explore their use of research results. Despite considering research results—including peer reviewed articles, theses, in-house research and research by other organisations—a very useful information source, many managers do not use research results regularly to inform their on-the-ground actions. Instead they tend to rely on experience, or advice from others. The reasons for the low use of research results are many and varied but include barriers to accessing research, especially peer-reviewed publications and reports published by other organisations. Managers also raised concern about the practical relevance of some of the research being conducted in their protected areas. We identify a series of resources which can be useful to managers to improve the access they have to research results and highlight a series of steps which researchers can follow to increase the likelihood of their research being used. We also suggest there is a role for the Malagasy authorities in improving the ways in which research reports— received as part of the conditions of research permits— are shared and archived. Researchers are increasingly aware of the moral imperative that research conducted should be available to inform practice, and protected area managers want access to the best possible information to inform their decisions. With such good intentions, overcoming the gap between research and practice should not be difficult with good communication and essential to improving conservation management in Madagascar

    Variation of Vitellaria paradoxa phenophases along the north-south gradient in Mali

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    We monitored flowering, fruiting and leafing of Vitellaria paradoxa (shea tree) along the north–south gradient in Mali (West Africa), using three study sites for a period of three years. In each site, adult shea trees were marked and monitored in permanent plots of both field and fallow stands. The chronology of phenophases and their mean length as well as flowering and fruiting were assessed. Our data revealed significant variation according to site and stand. The onset of events starts earlier in the south than in the centre or north, but the period covered by events was almost the same for all sites (3 to 6 months for flowering; 5 to 6 months for fruiting; and 2 to 4 months before full leafing).Flowering and fruiting were more regular in the south, but often as high in the north, with an almost similar trend in both fields and fallows. In the centre, flowering was also high in fields as well as in fallows, while the fruiting was medium to high. We also observed variations in the mean length of phenological events in study sites and stands. Sites in the south showed the highest average length of flowering and leafing (76 days and 44 days, respectively), while the central site showed the greatest length of mean fruiting (110 days).  We observed a significant site*stand interaction and noticeable variation over the years. Our study indicates that phenological events of shea tree could be influenced by several interacting biotic and abiotic factors. A future research challenge in shea phenology would be to discriminate these factors and thus help sustainable management of shea tree parklands

    Estimating welfare impacts where property rights are contested:methodological and policy implications

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    Where rights over natural resources are contested, the effectiveness of conservation may be undermined and it can be difficult to estimate the welfare impacts of conservation restrictions on local people. In particular, researchers face the dilemma of estimating respondents’ Willingness To Pay (WTP) for rights to resources, or their Willingness To Accept (WTA) compensation for foregoing these rights. We conducted a discrete choice experiment with respondents living next to a new protected area in Madagascar, using a split-sample design to administer both WTP and WTA formats, followed by debriefing interviews. We first examined the differences in response patterns to the formats and their performance in our study context. We also used the two formats to elicit respondents’ attitudes to conservation restrictions and property rights over forestlands. We found that the format affected the relative importance of different attributes: WTA respondents strongly favoured livelihood projects and secure tenure whereas neither attributes were significant for WTP respondents. The WTA format outperformed WTP format on three validity criteria: it was perceived to be more plausible and consequential; led to fewer protest responses; and was more appropriate given very low incomes. Seventy-three percent of respondents did not accept the legitimacy of state protection and strongly aspired to secure forest tenure. The use of a WTP format may thus be inappropriate even if respondents do not hold formal rights over resources. We conclude that estimating the opportunity costs of stopping de jure illegal activities is difficult and coercive conservation lacks procedural legitimacy and may not achieve full compensations. Our findings question the viability of the current conservation model and highlight the importance to conservation policy of locally legitimate property rights over forestlands

    Household economy, forest dependency & opportunity costs of conservation in eastern rainforests of Madagascar

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    The Government of Madagascar is trying to reduce deforestation and conserve biodiversity through creating new protected areas in the eastern rainforests. While this has many benefits, forest use restriction may bring costs to farmers at the forest frontier. We explored this through a series of surveys in five sites around the Corridor Ankeniheny Zahamena new protected area and adjacent national parks. In phase one a stratified random sample of 603 households completed a household survey covering demographic and socio-economic characteristics, and a choice experiment to estimate the opportunity costs of conservation. A stratified sub-sample (n = 171) then completed a detailed agricultural survey (including recording inputs and outputs from 721 plots) and wild-harvested product survey. The data have been archived with ReShare (UK Data Service). Together these allow a deeper understanding of the household economy on the forest frontier in eastern Madagascar and their swidden agricultural system, the benefits households derive from the forests through wild-harvested products, and the costs of conservation restrictions to forest edge communities

    Human migration to the forest frontier:implications for land use change and conservation management

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    Human migration is often considered an important driver of land use change and a threat to protected area integrity, but the reasons for in-migration, the effectiveness of conservation restrictions at stemming migration, and the extent to which migrants disproportionately contribute to land use change has been poorly studied, especially at fine spatial scales. Using a case study in eastern Madagascar (603 household surveys, mapping agricultural land for a subset of 167 households, and 49 focus group discussions and key informant interviews), we explore the patterns and drivers of migration within the lifetime of those currently alive. We investigate how this influences forest conversion on the border of established protected areas and sites without a history of conservation restrictions. We show that in-migration is driven, especially in sites with high migration, by access to land. There is a much higher proportion of migrant households at sites without a long history of conservation restrictions than around long-established protected areas, and migrants tend to be more educated and live closer to the forest edge than non-migrants. Our evidence supports the engulfment model (an active forest frontier later becoming a protected area); there is no evidence that protected areas have attracted migrants. Where there is a perceived open forest frontier, people move to the forest but these migrants are no more likely than local people to clear land (i.e., migrants are not “exceptional resource degraders”). In some parts of the tropics, out-migration from rural areas is resulting in forest regrowth; such a forest transition is unlikely to occur in Madagascar for some time. Those seeking to manage protected areas at the forest frontier will therefore need to prevent further colonisation; supporting tenure security for existing residents is likely to be an important step
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