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Protected area targets post-2020

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Abstract

Outcome-based targets are needed to achieve biodiversity goals.
Cite as: P. Visconti et al., Science
10.1126/science.aav6886 (2019).
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Protected area targets post-2020
Yanosky and James E. M. Watson
Piero Visconti, Stuart H. M. Butchart, Thomas M. Brooks, Penny F. Langhammer, Daniel Marnewick, Sheila Vergara, Alberto
published online April 11, 2019
ARTICLE TOOLS http://science.sciencemag.org/content/early/2019/04/10/science.aav6886
REFERENCES http://science.sciencemag.org/content/early/2019/04/10/science.aav6886#BIBL
This article cites 12 articles, 1 of which you can access for free
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... Bien qu'un objectif quantitatif tel que celui de 17 % de la surface terrestre protégée soit nécessaire et ait permis la création de nombreuses nouvelles aires protégées (Stokstad, 2020), il est également important de maximiser leur efficacité en matière de préservation des enjeux de biodiversité dans le processus de désignation (Carroll and Noss, 2022). Il est ainsi préférable de créer de nouvelles aires protégées en priorité dans des sites d'importance pour la biodiversité ou à enjeux de conservation, tels que les Zones Clés pour la Biodiversité (Key Biodiversity Areas, KBAs) (Eken et al., 2004;IUCN, 2016, Visconti et al., 2019, les sites maximisant la représentation d'écorégions ou d'espèces au sein du réseau d'aires protégées Kukkala et al., 2016;Pimm et al., 2018;Rodrigues et al., 2004b) et notamment d'espèces menacées d'extinction (Dinerstein et al., 2020;Venter et al., 2018;), ou encore les sites très peu influencés par les activités humaines (wilderness areas) (Allan et al., 2017;Watson and Venter, 2017). Malheureusement, ces sites-là ont trop peu fait l'objet d'implémentation de mesures de protection dans les dernières décennies en comparaison avec les sites peu accessibles (i.e., en altitude, éloignés des routes et des villes, avec des pentes raides) (Joppa and Pfaff, 2009) ou minimisant le conflit avec l'agriculture (Venter et al., 2018), et un grand nombre d'entre eux ne font pas encore l'objet de mesures de protection Kukkala et al., 2016;Maxwell et al., 2020;Ricketts et al., 2005;UNEP-WCMC & IUCN, 2021;Venter et al., 2018). ...
... Les Zones Clés pour la Biodiversité sont « des sites qui contribuent de manière significative à la persistance de la biodiversité mondiale » définis à partir de critères quantitatifs, par exemple de vulnérabilité ou d'irremplaçabilité (IUCN, 2016). A ce titre, les Zones Clés pour la Biodiversité devraient faire l'objet de mesures de conservation et notamment de protection (CBD, 2010;Eken et al., 2004;Margules and Pressey, 2000;Smith et al., 2019a;Visconti et al. 2019), d'autant plus que la création d'aires protégées dans ces sites est un outil de conservation de la biodiversité efficace (Butchart et al., 2012). Cependant, peu d'articles les ont hiérarchisées afin d'orienter la création d'aires protégées (voir toutefois Rogers et al., 2010). ...
... S'il est difficile de remettre en question un objectif quantitatif aussi ambitieux, bien qu'au passage certains en préconisent un qui l'est encore plus (Crist et al., 2021;Watson and Venter, 2017;Wilson, 2016), il me semble légitime de s'interroger sur sa mise en oeuvre. En effet, alors que les moyens financiers et humains de gestion d'aires protégées sont déjà insuffisants (Appleton et al., 2022;Coad et al., 2019;Geldmann et al., 2018), cet objectif pourrait entraîner la création de paper parks, des aires protégées avec peu ou pas de mesures de conservation mises en oeuvre et donc inefficaces (Di Minin and Toivonen, 2015 ;Visconti et al., 2019). C'est par exemple le cas de la côte méditerranéenne française où certaines aires marines protégées ne sont pas financées et n'impliquent aucune réglementation (Lauret, 2021) mais où la surface en protection forte devrait passer de moins de 1 % actuellement à 10 % d'ici 2030 (Macron, 2021). ...
Thesis
Climate change and land-use changes are major direct drivers of biodiversity loss, whose future impact must be anticipated. Mediterranean wetlands, which host an outstanding biodiversity, are highly vulnerable to these drivers but are not sufficiently targeted by conservation measures. The designation of new protected areas in these habitats can locally reduce the impact of climate and land-use changes on biodiversity, and especially on waterbird communities. It is necessary to identify wetlands of importance for biodiversity conservation for which the future changes are expected to be most severe in order to make the most of the effectiveness of protected areas. Assessing the exposure of Mediterranean wetlands to these drivers can help anticipate future variations of intensity and distribution of climate and land-use changes under several pathways of our societies. In this thesis, I aimed to assess whether existing protected areas cover the wetlands of importance for conservation most exposed to future climate and land-use changes in the Mediterranean region, and to identify where to designate new protected areas in order to lessen the future impact of these two drivers on waterbird communities. To this end, I computed various metrics of exposure to these drivers, derived from late 21st century projections under four future scenarios used by the IPCC. These metrics were intersected with winter abundance data of 151 waterbird species collected over 25 years at 5891 sites (25 countries) as part of the International Waterbird Census. First, I highlighted the high exposure to climate and land-use changes of Key Biodiversity Areas - sites of importance for biodiversity conservation - in the Mediterranean region, especially in countries where the protection of this network is low. In order to complement our knowledge on sites of importance for waterbirds, I subsequently applied three criteria of identification of wetlands of international importance to winter count data. As a result, I identified 161 sites of international importance for waterbirds whose status is not officially acknowledged, of which 95 are not protected. Then, I assessed the potential thermal adjustment limitations of waterbird communities to future temperature changes by combining their thermal specialization with their exposure to climate warming and natural habitat conversion. I thereby demonstrated the relevance of the location of existing protected areas that should overall be able to facilitate the future thermal adjustment of waterbird communities. However, I also identified 490 non-protected wetlands at risk, including 32 of international importance for waterbirds. Finally, assessing the exposure of coastal wetlands to sea-level rise highlighted the high threats to these sites, especially those protected and of international importance for waterbirds. Taken together, these exposure assessments to climate and land-use changes highlighted the overall relevance of the location of existing protected areas network in the Mediterranean region. However, these methods also identified important protection gaps of highly exposed wetlands of importance for waterbird conservation, especially in Maghreb countries. The results of this thesis could help guide the implementation of protection measures in Mediterranean wetlands and thereby improve the conservation of waterbird communities.
... This is despite it having been recently identified as an urgent priority for the long-term success of area-based conservation . Under the post-2020 global biodiversity framework, attention is increasingly focusing beyond quantity (total PA coverage) and including the quality of PAs (Visconti et al. 2019), providing targets that are often more important for species occurrence and persistence. ...
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Protected areas (PAs) are crucial conservation tools implemented worldwide to conserve biodiversity. Although PAs can positively impact wildlife populations, their ecological outcomes vary substantially depending on PA management and governance. Recent calls have highlighted the need to better assess the role of area-based conservation in preventing biodiversity loss. This is crucial to improve PA effectiveness in order to meet global biodiversity goals. Here we take advantage of a unique dataset composed of 2230 surveys conducted with koala detection dogs across Eastern Australia, to assess how protection status affected the occurrence of a threatened specialist folivore. We assessed if coverage of protected forest influenced koala presence or absence at two spatial scales (1 and 3 km), for (i) strictly and (ii) all protected areas. We also investigated if PA effects were explained by differences in habitat composition (percentage of secondary forest) between protected and unprotected areas. Taking confounding factors into account, we showed that forest protection (all IUCN categories) had a significant positive effect on koala occurrence, which increased by ~ 10% along the forest protection gradient. Contrarily, koala occurrence was not affected by strictly protected areas. In addition, adding the percentage of secondary forests in our models did not modify the statistical effect of PAs on koala occurrence, suggesting that forest composition is not the driver of the observed difference along the protection gradient. Our results contribute to a broader understanding of the effects of PAs on a threatened marsupial and call for further attention to assessments of PA effectiveness in Eastern Australia, a global biodiversity hotspot.
... In addition to ambiguities in biodiversity response, there are other factors that make it difficult to draw firm conclusions about whether a particular PA is meeting conservation expectations. Often, no explicit conservation targets or indicators to assess progress have been identified or the identification process was not sufficiently precise (e.g., SMARTspecific, measurable, ambitious, realistic, and time-bound) to allow for a meaningful evaluation (Green et al. 2019;Visconti et al. 2019). Because monitoring the effectiveness of PA management is critical to conserving biodiversity , there has been a recent call to track progress in a more highly structured and defensible manner . ...
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Protected areas (PAs) are a key component of most conservation strategies because they are thought to enhance biodiversity value relative to similar habitats in working landscapes. To examine whether PAs in Nova Scotia are functioning to enhance the biodiversity value of the landscapes in which they are embedded, we surveyed breeding bird communities in forested wetlands inside and outside of a large PA during 2018 and 2019. We found significantly higher species richness and diversity at sites in the working landscape relative to those inside the PA. Bird communities from different wetland types inside the PA were distinct from each other and those outside the PA, whereas bird communities at outside sites were homogenized and comprised of more early-successional species. There were numerous species of conservation concern at both inside and outside sites, indicating that both types of sites are playing important conservation roles. Abundances of these key species were driven by a combination of local (e.g., water table depth, herb, and shrub cover) and landscape scale factors (e.g., edge density and human disturbance). The higher abundance of long-distance migrants and insectivores at inside sites suggests PAs are providing critical additional support to key guilds that are in steep decline.
... Protected Areas (PAs) are very important indicators for meeting global biodiversity targets which are threatened by unsustainable resources used by humans all over the world (Visconti et al., 2019). Conservation strategies must be followed by certain regulations for effective management (Rashid et al., 2017). ...
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Policy and practice around protected areas are poorly aligned with the basic purpose of protection, which is to make a difference. The difference made by protected areas is their impact, defined in program evaluation as the outcomes arising from protection relative to the counterfactual of no protection or a different form of protection. Although impact evaluation of programs is well established in fields such as medicine, education and development aid, it is rare in nature conservation. We show that the present weak alignment with impact of policy targets and operational objectives for protected areas involves a great risk: targets and objectives can be achieved while making little difference to the conservation of biodiversity. We also review potential ways of increasing the difference made by protected areas, finding a poor evidence base for the use of planning and management ‘levers’ to better achieve impact. We propose a dual strategy for making protected areas more effective in their basic role of saving nature, outlining ways of developing targets and objectives focused on impact while also improving the evidence for effective planning and management.
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Protected area coverage has reached over 15% of the global land area. However, the quality of management of the vast majority of reserves remains unknown, and many are suspected to be “paper parks”.Moreover, the degree to which management can be enhanced through targeted conservation projects remains broadly speculative. Proven links between improved reserve management and the delivery of conservation outcomes are even more elusive. In this paper we present results on how management effectiveness scores change in protected areas receiving conservation investment, using a globally expanded database of protected area management effectiveness, focusing on the “management effectiveness tracking tool” (METT). Of 1934 protected areas with METT data, 722 sites have at least two assessments. MeanMETT scores increased in 69.5% of siteswhile 25.1% experienced decreases and 5.4% experienced no change over project periods (median 4 years). Low initial METT scores and longer implementation time were both found to positively correlate with larger increases in management effectiveness. Performance metrics related to planning and context aswell as monitoring and enforcement systems increased the most while protected area outcomes showed least improvement. Using a general linear mixed model we tested the correlation between change in METT scores and matrices of 1) landscape and protected area properties (i.e. topography and size), 2) human threats (i.e. road and human population density), and 3) socio-economics (i.e. infant mortality rate). Protected areas under greater threat and larger protected areas showed greatest improvements in METT. Our results suggest that when funding and resources are targeted at protected areas under greater threat they have a greater impact, potentially including slowing the loss of biodiversity.
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Governments have committed to conserving ≥17% of terrestrial and ≥10% of marine environments globally, especially “areas of particular importance for biodiversity” through “ecologically representative” Protected Area (PA) systems or other “area-based conservation measures,” while individual countries have committed to conserve 3–50% of their land area. We estimate that PAs currently cover 14.6% of terrestrial and 2.8% of marine extent, but 59–68% of ecoregions, 77–78% of important sites for biodiversity, and 57% of 25,380 species have inadequate coverage. The existing 19.7 million km2 terrestrial PA network needs only 3.3 million km2 to be added to achieve 17% terrestrial coverage. However, it would require nearly doubling to achieve, cost-efficiently, coverage targets for all countries, ecoregions, important sites, and species. Poorer countries have the largest relative shortfalls. Such extensive and rapid expansion of formal PAs is unlikely to be achievable. Greater focus is therefore needed on alternative approaches, including community- and privately managed sites and other effective area-based conservation measures.This article is protected by copyright. All rights reserved.
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Originally conceived to conserve iconic landscapes and wildlife, protected areas are now expected to achieve an increasingly diverse set of conservation, social and economic objectives. The amount of land and sea designated as formally protected has markedly increased over the past century, but there is still a major shortfall in political commitments to enhance the coverage and effectiveness of protected areas. Financial support for protected areas is dwarfed by the benefits that they provide, but these returns depend on effective management. A step change involving increased recognition, funding, planning and enforcement is urgently needed if protected areas are going to fulfil their potential.
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To contribute to the aspirations of recent international biodiversity conventions, protected areas (PAs) must be strategically located, and not simply established on economically marginal lands as they have in the past. With refined international commitments under the Convention of Biodiversity to target protected areas in places of 'importance to biodiversity', this may now be the case. Here we analyze location biases in PAs globally over both historic (pre-2004) and recent time periods. Discouragingly, we find that both old and new protected areas are not targeting places with high concentration of threatened vertebrate species. Instead, they appear to be established in locations that minimize conflict with agriculturally suitable lands. This entrenchment of past trends has significant implications for the contributions these protected areas are making to international commitments to conserve biodiversity. We discover that if protected area growth between 2004 and 2014 had strategically targeted unrepresented threatened vertebrates, it would have been possible to protect >30 times more species (3086 or 2553 potential vs 85 actual new species represented) for the same area or the same cost as the actual expansion that occurred. With the land available for conservation declining, nations must urgently focus new protection on places that provide for the conservation outcomes outlined in international treaties. This article is protected by copyright. All rights reserved.