Avoiding an impending collision in international conservation

IF 5.2 1区 环境科学与生态学 Q1 BIODIVERSITY CONSERVATION
Lovemore Sibanda, Amy Dickman, Courtney Hughes, Jessica Tacey, Emily Madsen, Lessah Mandoloma, Moreangels M. Mbizah, Yolanda Mutinhima, Betty Rono, Salum Kulunge, David Kimaili, Trisha Bhujle, David W. Macdonald, Darragh Hare
{"title":"Avoiding an impending collision in international conservation","authors":"Lovemore Sibanda,&nbsp;Amy Dickman,&nbsp;Courtney Hughes,&nbsp;Jessica Tacey,&nbsp;Emily Madsen,&nbsp;Lessah Mandoloma,&nbsp;Moreangels M. Mbizah,&nbsp;Yolanda Mutinhima,&nbsp;Betty Rono,&nbsp;Salum Kulunge,&nbsp;David Kimaili,&nbsp;Trisha Bhujle,&nbsp;David W. Macdonald,&nbsp;Darragh Hare","doi":"10.1111/cobi.14450","DOIUrl":null,"url":null,"abstract":"<p>There are long-standing tensions between 2 major movements in international conservation: one emphasizes increasing the area set aside for conservation and the other emphasizes an inclusive, people-centered approach to conservation. The degree to which these movements harmonize or contradict depends largely on how decision makers balance strictly protected areas (PAs) with flexible other effective area-based conservation measures (OECMs).</p><p>Over 190 countries have ratified the CBD and committed to the GBF (WWF &amp; IUCN WCPA, <span>2023</span>), but opinions regarding the motivations for and implications of 30×30 are mixed. Proponents are optimistic that it will deliver substantial positive impacts for biodiversity (Waldron et al., <span>2020</span>; Wolff et al., <span>2023</span>), whereas critics argue that it risks prioritizing the goals and interests of people living far from biodiversity-rich areas over those of marginalized IPLCs (Green Economy Coalition, <span>2021</span>; Rudd et al., <span>2021</span>).</p><p>The discourse illuminates tensions between traditional area-based conservation via formal PAs and calls for more inclusive, people-centered approaches (Bakarr, <span>2023</span>; IUCN Africa Protected Areas Congress, <span>2022</span>). The people-centered approach, or inclusive conservation, contends that conservation has traditionally excluded IPLCs from PAs, for example, by preventing sustainable access to and use of wildlife resources (Lo &amp; Jang, <span>2022</span>). Therefore, the people-centered approach seeks to simultaneously conserve biodiversity and improve outcomes for IPLCs who have been or continue to be marginalized by area-based conservation (Raymond et al., <span>2022</span>).</p><p>As conservation researchers and practitioners working in multiple landscapes, we have seen how global conservation movements influence decisions that affect PAs and OECM management and, therefore, IPLCs. We appreciate that 30×30 recognizes OECMs and formal PAs (Cook, <span>2024</span>), but we are concerned that achieving inclusive conservation under 30×30 will depend on how decision makers define and interpret PAs and OECMs. If new PAs and OECMs are designated following traditional exclusionary methods or if PA and OECM management strategies are defined without fully incorporating the rights, values, needs, and concerns of IPLCs, efforts to deliver 30×30 might unintentionally reproduce historical inequalities and reinforce power imbalances associated with colonial forms of conservation (Rudd et al., <span>2021</span>; Willow, <span>2016</span>).</p><p>We therefore see an impending collision at the heart of 30×30. To avoid this collision, the voices of IPLCs must be included in ongoing debates and decision-making about how and where to conserve biodiversity (Sandbrook et al., <span>2023</span>). This could involve establishing, supporting, and expanding comanagement models to ensure conservation measures are aligned with IPLCs’ knowledge and needs (Rocha et al., <span>2017</span>). One example is Yaigojé Apaporis National Park in Colombia, which was created at the request of Indigenous Peoples and managed in collaboration with them (Huaiquimilla-Guerrero et al., <span>2023</span>).</p><p>Conservation efforts (including PAs and OECMs) can better reflect local interests by implementing governance models that decentralize power dynamics (Cebrián-Piqueras et al., <span>2023</span>). Without meaningful collaborative decision-making with IPLCs, local resentment and opposition to conservation are likely and could result in neither biodiversity conservation nor social justice (Bennett et al., <span>2019</span>; Sandbrook et al., <span>2023</span>). This risk challenges conservation scientists, practitioners, and decision makers to better define <i>effective conservation</i> and evaluate effectiveness over time (Lee &amp; Abdullah, <span>2019</span>).</p><p>To meet commitments under target 3, national decision makers must find a balance between strict PAs and more flexible OECMs. They must also create a delicate balance among the needs, interests, and concerns of people living in high-biodiversity areas and those living elsewhere in a country (Dawson et al., <span>2024</span>). Doing so could help ensure that 30×30 produces practical area-based solutions to the worldwide biodiversity crisis without further marginalizing IPLCs (IUCN Africa Protected Areas Congress, <span>2022</span>). This should also involve recognizing and respecting IPLCs’ expertise and ability to effectively conserve biodiversity outside formal PAs (ICCA Consortium, <span>2021</span>) and respecting IPLCs’ agency via shared leadership, as opposed to treating IPLCs as convenient partners in delivering a vision for area-based conservation defined by others (Busck-Lumholt et al., <span>2024</span>; Dawson et al., <span>2024</span>).</p><p>Realistically, the costs of delivering 30×30 will largely fall on IPLCs living near biodiversity-rich areas, even though more powerful—often distant—actors in the Global North champion the target (Earsom, <span>2023</span>). Therefore, to avoid 30×30 reproducing colonial inequalities, such as displacing and further marginalizing IPLCs, politicians, businesses, nongovernmental organizations, and funding organizations could provide more direct financial support to IPLCs (Sangha, <span>2020</span>). Such financial support could empower IPLCs to manage and preserve their natural resources effectively, according to their own cultures and values (Jeanty, <span>2021</span>).</p><p>Although IPLCs receive financial support from multiple sources (approximately US$270 million per year over the last 10 years [United Nations Environment Programme, <span>2021</span>]), there remains a huge gap between available funding and actual needs on the ground (Larson et al., <span>2022</span>). Ensuring that IPLC conservation efforts receive adequate funding and that IPLCs are directly involved in decision-making could foster a more equitable and sustainable approach to global biodiversity conservation (Busck-Lumholt et al., <span>2024</span>; Milner-Gulland, <span>2024</span>).</p><p>The potential collision between expanding area-based conservation measures and inclusive conservation is avoidable. However, there is an urgent need to consider how expanding PAs and OECMs to achieve 30×30 can meet ethical aspirations for more inclusive conservation. This is especially pertinent for IPLCs, who are most directly affected by conservation policies and programs but whose voices are seldom accounted for in global decisions (Martinelli &amp; Martinelli, <span>2024</span>). Respecting IPLCs’ perspectives and incorporating them meaningfully into decisions on expanding PAs will help ensure national and international conservation efforts are equitable and effective and do not perpetuate historical injustices.</p>","PeriodicalId":10689,"journal":{"name":"Conservation Biology","volume":"39 2","pages":""},"PeriodicalIF":5.2000,"publicationDate":"2025-02-10","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://onlinelibrary.wiley.com/doi/epdf/10.1111/cobi.14450","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Conservation Biology","FirstCategoryId":"93","ListUrlMain":"https://onlinelibrary.wiley.com/doi/10.1111/cobi.14450","RegionNum":1,"RegionCategory":"环境科学与生态学","ArticlePicture":[],"TitleCN":null,"AbstractTextCN":null,"PMCID":null,"EPubDate":"","PubModel":"","JCR":"Q1","JCRName":"BIODIVERSITY CONSERVATION","Score":null,"Total":0}
引用次数: 0

Abstract

There are long-standing tensions between 2 major movements in international conservation: one emphasizes increasing the area set aside for conservation and the other emphasizes an inclusive, people-centered approach to conservation. The degree to which these movements harmonize or contradict depends largely on how decision makers balance strictly protected areas (PAs) with flexible other effective area-based conservation measures (OECMs).

Over 190 countries have ratified the CBD and committed to the GBF (WWF & IUCN WCPA, 2023), but opinions regarding the motivations for and implications of 30×30 are mixed. Proponents are optimistic that it will deliver substantial positive impacts for biodiversity (Waldron et al., 2020; Wolff et al., 2023), whereas critics argue that it risks prioritizing the goals and interests of people living far from biodiversity-rich areas over those of marginalized IPLCs (Green Economy Coalition, 2021; Rudd et al., 2021).

The discourse illuminates tensions between traditional area-based conservation via formal PAs and calls for more inclusive, people-centered approaches (Bakarr, 2023; IUCN Africa Protected Areas Congress, 2022). The people-centered approach, or inclusive conservation, contends that conservation has traditionally excluded IPLCs from PAs, for example, by preventing sustainable access to and use of wildlife resources (Lo & Jang, 2022). Therefore, the people-centered approach seeks to simultaneously conserve biodiversity and improve outcomes for IPLCs who have been or continue to be marginalized by area-based conservation (Raymond et al., 2022).

As conservation researchers and practitioners working in multiple landscapes, we have seen how global conservation movements influence decisions that affect PAs and OECM management and, therefore, IPLCs. We appreciate that 30×30 recognizes OECMs and formal PAs (Cook, 2024), but we are concerned that achieving inclusive conservation under 30×30 will depend on how decision makers define and interpret PAs and OECMs. If new PAs and OECMs are designated following traditional exclusionary methods or if PA and OECM management strategies are defined without fully incorporating the rights, values, needs, and concerns of IPLCs, efforts to deliver 30×30 might unintentionally reproduce historical inequalities and reinforce power imbalances associated with colonial forms of conservation (Rudd et al., 2021; Willow, 2016).

We therefore see an impending collision at the heart of 30×30. To avoid this collision, the voices of IPLCs must be included in ongoing debates and decision-making about how and where to conserve biodiversity (Sandbrook et al., 2023). This could involve establishing, supporting, and expanding comanagement models to ensure conservation measures are aligned with IPLCs’ knowledge and needs (Rocha et al., 2017). One example is Yaigojé Apaporis National Park in Colombia, which was created at the request of Indigenous Peoples and managed in collaboration with them (Huaiquimilla-Guerrero et al., 2023).

Conservation efforts (including PAs and OECMs) can better reflect local interests by implementing governance models that decentralize power dynamics (Cebrián-Piqueras et al., 2023). Without meaningful collaborative decision-making with IPLCs, local resentment and opposition to conservation are likely and could result in neither biodiversity conservation nor social justice (Bennett et al., 2019; Sandbrook et al., 2023). This risk challenges conservation scientists, practitioners, and decision makers to better define effective conservation and evaluate effectiveness over time (Lee & Abdullah, 2019).

To meet commitments under target 3, national decision makers must find a balance between strict PAs and more flexible OECMs. They must also create a delicate balance among the needs, interests, and concerns of people living in high-biodiversity areas and those living elsewhere in a country (Dawson et al., 2024). Doing so could help ensure that 30×30 produces practical area-based solutions to the worldwide biodiversity crisis without further marginalizing IPLCs (IUCN Africa Protected Areas Congress, 2022). This should also involve recognizing and respecting IPLCs’ expertise and ability to effectively conserve biodiversity outside formal PAs (ICCA Consortium, 2021) and respecting IPLCs’ agency via shared leadership, as opposed to treating IPLCs as convenient partners in delivering a vision for area-based conservation defined by others (Busck-Lumholt et al., 2024; Dawson et al., 2024).

Realistically, the costs of delivering 30×30 will largely fall on IPLCs living near biodiversity-rich areas, even though more powerful—often distant—actors in the Global North champion the target (Earsom, 2023). Therefore, to avoid 30×30 reproducing colonial inequalities, such as displacing and further marginalizing IPLCs, politicians, businesses, nongovernmental organizations, and funding organizations could provide more direct financial support to IPLCs (Sangha, 2020). Such financial support could empower IPLCs to manage and preserve their natural resources effectively, according to their own cultures and values (Jeanty, 2021).

Although IPLCs receive financial support from multiple sources (approximately US$270 million per year over the last 10 years [United Nations Environment Programme, 2021]), there remains a huge gap between available funding and actual needs on the ground (Larson et al., 2022). Ensuring that IPLC conservation efforts receive adequate funding and that IPLCs are directly involved in decision-making could foster a more equitable and sustainable approach to global biodiversity conservation (Busck-Lumholt et al., 2024; Milner-Gulland, 2024).

The potential collision between expanding area-based conservation measures and inclusive conservation is avoidable. However, there is an urgent need to consider how expanding PAs and OECMs to achieve 30×30 can meet ethical aspirations for more inclusive conservation. This is especially pertinent for IPLCs, who are most directly affected by conservation policies and programs but whose voices are seldom accounted for in global decisions (Martinelli & Martinelli, 2024). Respecting IPLCs’ perspectives and incorporating them meaningfully into decisions on expanding PAs will help ensure national and international conservation efforts are equitable and effective and do not perpetuate historical injustices.

在国际自然保护中避免即将发生的碰撞。
在国际自然保护的两个主要运动之间存在着长期的紧张关系:一个强调增加留出用于自然保护的区域,另一个强调包容的、以人为本的保护方法。这些运动协调或矛盾的程度在很大程度上取决于决策者如何平衡严格保护区(PAs)与灵活的其他有效的基于区域的保护措施(oecm)。已有190多个国家批准了《生物多样性公约》,并承诺加入GBF(世界自然基金会)。IUCN WCPA, 2023),但关于30×30的动机和影响的意见是混合的。支持者乐观地认为,它将对生物多样性产生实质性的积极影响(Waldron et al., 2020;Wolff等人,2023),而批评者认为,它有可能优先考虑远离生物多样性丰富地区的人们的目标和利益,而不是边缘化的iplc(绿色经济联盟,2021;Rudd et al., 2021)。这一论述阐明了传统的以区域为基础的、通过正式行动纲领的保护与呼吁更包容、以人为本的方法之间的紧张关系(Bakarr, 2023;世界自然保护联盟非洲保护区大会,2022年)。以人为本的方法,或包容性保护,认为保护传统上将iplc排除在保护区之外,例如,通过阻止可持续获取和利用野生动物资源(Lo &amp;张成泽,2022)。因此,以人为本的方法寻求在保护生物多样性的同时,改善已经或继续被基于区域的保护边缘化的iplc的结果(Raymond et al., 2022)。作为在多个景观中工作的保护研究人员和实践者,我们已经看到全球保护运动如何影响影响保护区和OECM管理的决策,从而影响iplc。我们赞赏30×30承认oecm和正式保护区(Cook, 2024),但我们担心,在30×30下实现包容性保护将取决于决策者如何定义和解释保护区和oecm。如果新的保护区和OECM是按照传统的排他性方法指定的,或者如果保护区和OECM的管理策略没有完全纳入iplc的权利、价值观、需求和关注,那么提供30×30的努力可能会无意中再现历史上的不平等,并加强与殖民形式的保护相关的权力不平衡(Rudd等人,2021;柳树,2016)。因此,我们在30×30的中心看到了即将发生的碰撞。为了避免这种冲突,必须将iplc的声音纳入正在进行的关于如何以及在何处保护生物多样性的辩论和决策中(Sandbrook et al., 2023)。这可能涉及建立、支持和扩展管理模式,以确保保护措施符合iplc的知识和需求(Rocha et al., 2017)。一个例子是哥伦比亚的yaigoj<s:1> Apaporis国家公园,该公园是应土著人民的要求创建的,并与他们合作管理(Huaiquimilla-Guerrero et al., 2023)。通过实施分散权力动态的治理模式,保护工作(包括保护区和oecm)可以更好地反映地方利益(Cebrián-Piqueras等人,2023)。如果没有与iplc进行有意义的协作决策,当地可能会对保护产生不满和反对,并可能导致生物多样性保护和社会正义都无法实现(Bennett等人,2019;Sandbrook et al., 2023)。这种风险对保护科学家、从业者和决策者提出了挑战,要求他们更好地定义有效的保护,并随着时间的推移评估其有效性。阿卜杜拉,2019)。为了履行具体目标3下的承诺,各国决策者必须在严格的行动纲领和更灵活的东经合组织机制之间找到平衡。他们还必须在生活在高生物多样性地区的人们和生活在一个国家其他地方的人们的需求、利益和关注之间建立微妙的平衡(Dawson et al., 2024)。这样做有助于确保30×30为全球生物多样性危机提供切实可行的基于区域的解决方案,而不会进一步边缘化iplc(世界自然保护联盟非洲保护区大会,2022年)。这还应包括承认和尊重iplc在正式保护区之外有效保护生物多样性的专业知识和能力(ICCA Consortium, 2021),并通过共同领导尊重iplc的机构,而不是将iplc视为实现由他人定义的基于区域的保护愿景的便利合作伙伴(Busck-Lumholt等人,2024;Dawson et al., 2024)。实际上,实现30×30的成本将主要落在生活在生物多样性丰富地区附近的IPLCs身上,尽管全球北方更强大(通常是遥远的)的参与者支持这一目标(Earsom, 2023)。 因此,为了避免30×30再现殖民不平等,例如驱逐和进一步边缘化iplc,政治家、企业、非政府组织和资助组织可以向iplc提供更直接的财政支持(Sangha, 2020)。这种财政支持可以使iplc能够根据自己的文化和价值观有效地管理和保护其自然资源(Jeanty, 2021)。尽管iplc获得了多个来源的财政支持(过去10年每年约2.7亿美元[联合国环境规划署,2021]),但在可用资金与实地实际需求之间仍然存在巨大差距(Larson等人,2022)。确保IPLC的保护工作获得足够的资金,并确保IPLC直接参与决策,可以促进更公平和可持续的全球生物多样性保护方法(Busck-Lumholt等人,2024;Milner-Gulland, 2024)。扩大区域保护措施与包容性保护之间的潜在冲突是可以避免的。然而,迫切需要考虑如何扩大保护区和oecm以实现30×30才能满足更具包容性的保护的道德愿望。这对iplc来说尤其重要,他们最直接受到保护政策和项目的影响,但他们的声音很少在全球决策中得到考虑(Martinelli &amp;Martinelli, 2024)。尊重国际自然保护机构的观点,并将其有意义地纳入扩大保护区的决定中,将有助于确保国家和国际保护工作的公平和有效,不会使历史上的不公正永久化。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
求助全文
约1分钟内获得全文 求助全文
来源期刊
Conservation Biology
Conservation Biology 环境科学-环境科学
CiteScore
12.70
自引率
3.20%
发文量
175
审稿时长
2 months
期刊介绍: Conservation Biology welcomes submissions that address the science and practice of conserving Earth's biological diversity. We encourage submissions that emphasize issues germane to any of Earth''s ecosystems or geographic regions and that apply diverse approaches to analyses and problem solving. Nevertheless, manuscripts with relevance to conservation that transcend the particular ecosystem, species, or situation described will be prioritized for publication.
×
引用
GB/T 7714-2015
复制
MLA
复制
APA
复制
导出至
BibTeX EndNote RefMan NoteFirst NoteExpress
×
提示
您的信息不完整,为了账户安全,请先补充。
现在去补充
×
提示
您因"违规操作"
具体请查看互助需知
我知道了
×
提示
确定
请完成安全验证×
copy
已复制链接
快去分享给好友吧!
我知道了
右上角分享
点击右上角分享
0
联系我们:info@booksci.cn Book学术提供免费学术资源搜索服务,方便国内外学者检索中英文文献。致力于提供最便捷和优质的服务体验。 Copyright © 2023 布克学术 All rights reserved.
京ICP备2023020795号-1
ghs 京公网安备 11010802042870号
Book学术文献互助
Book学术文献互助群
群 号:481959085
Book学术官方微信