Conservation Science and Practice in the Pantanal: From crisis to hope

IF 2.8 2区 环境科学与生态学 Q1 BIODIVERSITY CONSERVATION
Rafael Morais Chiaravalloti, Walfrido Morais Tomas, Peter Leimgruber, Tom Akre, Anthony J. Giordano
{"title":"Conservation Science and Practice in the Pantanal: From crisis to hope","authors":"Rafael Morais Chiaravalloti,&nbsp;Walfrido Morais Tomas,&nbsp;Peter Leimgruber,&nbsp;Tom Akre,&nbsp;Anthony J. Giordano","doi":"10.1111/csp2.70107","DOIUrl":null,"url":null,"abstract":"<p>The Pantanal is the largest continuous freshwater wetland in the world (Junk et al., <span>2011</span>). Located in central South America and encompassing 179,300 km<sup>2</sup>, it includes parts of Brazil, Paraguay, and Bolivia. The Paraguay River—for which the Pantanal serves as a floodplain—stretches for 2695 km, connecting Brazil with Bolivia, Paraguay, and Argentina (Girard et al., <span>2025</span>). The scale and magnitude of the Pantanal influence large parts of South America's hydrology, biodiversity, history, and culture (Wantzen et al., <span>2023</span>). The Pantanal has also always been a refuge for endangered and threatened species and for low-intensive use of natural resources (Tomas et al., <span>2019</span>). Recently, however, wildfires, deforestation, and infrastructure projects have increased conservation concerns (Tortato et al., <span>2022</span>) (Figure 1). But with government, NGOs - Non-Governmental Organizations, local people, and scientists' support, the Pantanal can still be a place of conservation hope.</p><p>Permanent human occupation in the Pantanal dates back more than 8000 years (Bespalez, <span>2015</span>), with the first signs of settlements in the northern Pantanal occurring approximately 27,000 years ago (Vialou et al., <span>2017</span>). Although the first European colonizers arrived there in the early 16th century, it was not until the late 18th century that the Portuguese began to establish a structured colonizing agenda in the region (de Fátima Costa, <span>1999</span>). During this time, most indigenous groups were replaced with (Peixoto, <span>2017</span>), cattle ranches (de Abreu et al., <span>2010</span>) and riverine fishing communities (Chiaravalloti, <span>2019</span>). Today, cattle ranches occupy over 90% of the Pantanal (Chiaravalloti et al., <span>2025</span>), with cattle stocks totaling approximately 3.8 million heads (Tomas et al., <span>2019</span>). There are also around 8000 people registered as professional fishers in the region (Fernando, Lopes, et al., <span>2024</span>), generating an estimated US$84 million per year (Girard et al., <span>2025</span>), and probably 10 times that number are unreported “sporadic” fishermen (Fernando, Lopes, et al., <span>2024</span>).</p><p>Despite long-standing, widespread human occupation and a violent history of colonization, the Pantanal continues to be well conserved, with &gt;80% of its native vegetation standing (Mapbiomas, <span>2022</span>). In addition, poaching represents a very low threat to native wildlife (Desbiez et al., <span>2011</span>). As such, the Pantanal is a refuge for many threatened species, such as jaguar (<i>Panthera onca</i>), giant otter (<i>Pteronura brasiliensis</i>), marsh deer (<i>Blastocerus dichotomus</i>), and hyacinth macaw (<i>Anodorhynchus hyacinthinus</i>) (Tomas et al., <span>2019</span>). There are also no indications of overfishing (Fernando, Lopes, et al., <span>2024</span>), as even areas of intensive use by local communities still show a relatively intact fish assemblage (Polaz et al., <span>2017</span>).</p><p>However, as presented in this special issue, the Pantanal is experiencing rapid change. The largest and one of the most conserved wetlands in the world is becoming a place of conservation concern. One-third of ecological corridors in the Pantanal have already disappeared (da Rosa Oliveira et al., <span>2025</span>) and should these trends continue, 14,000 km<sup>2</sup> of native vegetation could be lost by 2050 (Guerra et al., <span>2025</span>). Compound effects of the expansion and construction of infrastructure projects are starting to cascade through the ecosystem and present increasing and serious threats to the region (Tortato et al., <span>2022</span>). These developments appear bound to increase and accelerate. For example, proposals to transform the Paraguay River into a <i>Hidrovia</i> waterway by dredging, riverbank stabilization, course alteration, and port construction would severely disrupt the hydrology (Girard et al., <span>2025</span>), causing the collapse of the flooding cycle and its benefits for vegetation or biodiversity, and ultimately leading to a widespread reduction in fish abundances and diversity (Fernando et al., <span>2025</span>).</p><p>This special section also shows the pathway to change the current trend. The papers in this section show that the region and the local stakeholders have all the means to guarantee that the region continues to be a place of biodiversity conservation and sustainability: conservation hope. For example, as shown in Chiaravalloti et al. (<span>2025</span>) one cornerstone of the Pantanal's sustainable history has been its strong land tenure system with well-defined property rights, critical to the implementation of targeted and area-based conservation programs (Robinson et al., <span>2018</span>). Similarly, the people and institutions of the Pantanal have traditionally had a strong legacy of cooperation and even interdependence, largely due to the need for mutual reliance on one another across a highly variable and seasonally unpredictable landscape (Marchini et al., <span>2024</span>). For example, collective management schemes have always been part of the Pantanal's fishing and cattle ranching collaborative socio-ecological systems (Tomas et al., <span>2019</span>). These integrative approaches, together with the clear land tenure system, could be a path for the development of several community-based, landscape, and species conservation initiatives. They include a polycentric system of governance across different parts of the Pantanal; biodiversity offsetting programs (Lourival et al., <span>2025</span>), the cultivation of “other effective biodiversity conservation measures” (OECM), sustainable ranching certifications schemes (Chiaravalloti et al. <span>2025</span>), natural capital indicator frameworks (NCIF) (Fairbrass et al., <span>2025</span>), and species conservation programs based on coexistence and cooperation (Marchini et al., <span>2024</span>).</p><p>To implement these actions, nonetheless, it is critical to establish some baseline conservation principles, which we also describe in the special issue; they are: (i) consideration of the Paraguay River Basin as a single management unit; (ii) the establishment of rules in alignment with a “restricted use” approach or concept; (iii) ensuring that all natural resources across the region are used sustainably; (iv) maintenance of environmental heterogeneity and ecological functionality across varying landscapes; (v) maintenance of the region's hydrological integrity and connectivity; (vi) ensuring the ecological representativeness of the protected areas network; (vii) the provision of economic incentives for conservation of the land; and (viii) recognition for and protection of traditional peoples, their values and resources, and their way of life (Tomas et al., <span>2025</span>).</p><p>The Pantanal has been, for a long time, a showcase model for the coexistence of conservation and sustainable use. However, increasing economic pressures, climate change, infrastructure projects, and loss of traditional cultural knowledge are challenging its historical position. To regain its importance and position as a positive example in conservation, regional stakeholders, governments, and conservation practitioners have to create a foundation for a common sustainable future for the entire region.</p><p>This special section is the beginning of this process. The papers contained here contribute to our knowledge of how the system functions, how it is impacted by and responds to human activities, and to the development of effective management strategies to support a concurred sustainability agenda for the Pantanal. We invite everyone to keep contributing to this effort.</p><p>All the authors contributed to the editorial article, reviewing, and discussing key points.</p><p>The authors declare no conflict of interest.</p>","PeriodicalId":51337,"journal":{"name":"Conservation Science and Practice","volume":"7 7","pages":""},"PeriodicalIF":2.8000,"publicationDate":"2025-07-10","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://onlinelibrary.wiley.com/doi/epdf/10.1111/csp2.70107","citationCount":"0","resultStr":null,"platform":"Semanticscholar","paperid":null,"PeriodicalName":"Conservation Science and Practice","FirstCategoryId":"93","ListUrlMain":"https://onlinelibrary.wiley.com/doi/10.1111/csp2.70107","RegionNum":2,"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

The Pantanal is the largest continuous freshwater wetland in the world (Junk et al., 2011). Located in central South America and encompassing 179,300 km2, it includes parts of Brazil, Paraguay, and Bolivia. The Paraguay River—for which the Pantanal serves as a floodplain—stretches for 2695 km, connecting Brazil with Bolivia, Paraguay, and Argentina (Girard et al., 2025). The scale and magnitude of the Pantanal influence large parts of South America's hydrology, biodiversity, history, and culture (Wantzen et al., 2023). The Pantanal has also always been a refuge for endangered and threatened species and for low-intensive use of natural resources (Tomas et al., 2019). Recently, however, wildfires, deforestation, and infrastructure projects have increased conservation concerns (Tortato et al., 2022) (Figure 1). But with government, NGOs - Non-Governmental Organizations, local people, and scientists' support, the Pantanal can still be a place of conservation hope.

Permanent human occupation in the Pantanal dates back more than 8000 years (Bespalez, 2015), with the first signs of settlements in the northern Pantanal occurring approximately 27,000 years ago (Vialou et al., 2017). Although the first European colonizers arrived there in the early 16th century, it was not until the late 18th century that the Portuguese began to establish a structured colonizing agenda in the region (de Fátima Costa, 1999). During this time, most indigenous groups were replaced with (Peixoto, 2017), cattle ranches (de Abreu et al., 2010) and riverine fishing communities (Chiaravalloti, 2019). Today, cattle ranches occupy over 90% of the Pantanal (Chiaravalloti et al., 2025), with cattle stocks totaling approximately 3.8 million heads (Tomas et al., 2019). There are also around 8000 people registered as professional fishers in the region (Fernando, Lopes, et al., 2024), generating an estimated US$84 million per year (Girard et al., 2025), and probably 10 times that number are unreported “sporadic” fishermen (Fernando, Lopes, et al., 2024).

Despite long-standing, widespread human occupation and a violent history of colonization, the Pantanal continues to be well conserved, with >80% of its native vegetation standing (Mapbiomas, 2022). In addition, poaching represents a very low threat to native wildlife (Desbiez et al., 2011). As such, the Pantanal is a refuge for many threatened species, such as jaguar (Panthera onca), giant otter (Pteronura brasiliensis), marsh deer (Blastocerus dichotomus), and hyacinth macaw (Anodorhynchus hyacinthinus) (Tomas et al., 2019). There are also no indications of overfishing (Fernando, Lopes, et al., 2024), as even areas of intensive use by local communities still show a relatively intact fish assemblage (Polaz et al., 2017).

However, as presented in this special issue, the Pantanal is experiencing rapid change. The largest and one of the most conserved wetlands in the world is becoming a place of conservation concern. One-third of ecological corridors in the Pantanal have already disappeared (da Rosa Oliveira et al., 2025) and should these trends continue, 14,000 km2 of native vegetation could be lost by 2050 (Guerra et al., 2025). Compound effects of the expansion and construction of infrastructure projects are starting to cascade through the ecosystem and present increasing and serious threats to the region (Tortato et al., 2022). These developments appear bound to increase and accelerate. For example, proposals to transform the Paraguay River into a Hidrovia waterway by dredging, riverbank stabilization, course alteration, and port construction would severely disrupt the hydrology (Girard et al., 2025), causing the collapse of the flooding cycle and its benefits for vegetation or biodiversity, and ultimately leading to a widespread reduction in fish abundances and diversity (Fernando et al., 2025).

This special section also shows the pathway to change the current trend. The papers in this section show that the region and the local stakeholders have all the means to guarantee that the region continues to be a place of biodiversity conservation and sustainability: conservation hope. For example, as shown in Chiaravalloti et al. (2025) one cornerstone of the Pantanal's sustainable history has been its strong land tenure system with well-defined property rights, critical to the implementation of targeted and area-based conservation programs (Robinson et al., 2018). Similarly, the people and institutions of the Pantanal have traditionally had a strong legacy of cooperation and even interdependence, largely due to the need for mutual reliance on one another across a highly variable and seasonally unpredictable landscape (Marchini et al., 2024). For example, collective management schemes have always been part of the Pantanal's fishing and cattle ranching collaborative socio-ecological systems (Tomas et al., 2019). These integrative approaches, together with the clear land tenure system, could be a path for the development of several community-based, landscape, and species conservation initiatives. They include a polycentric system of governance across different parts of the Pantanal; biodiversity offsetting programs (Lourival et al., 2025), the cultivation of “other effective biodiversity conservation measures” (OECM), sustainable ranching certifications schemes (Chiaravalloti et al. 2025), natural capital indicator frameworks (NCIF) (Fairbrass et al., 2025), and species conservation programs based on coexistence and cooperation (Marchini et al., 2024).

To implement these actions, nonetheless, it is critical to establish some baseline conservation principles, which we also describe in the special issue; they are: (i) consideration of the Paraguay River Basin as a single management unit; (ii) the establishment of rules in alignment with a “restricted use” approach or concept; (iii) ensuring that all natural resources across the region are used sustainably; (iv) maintenance of environmental heterogeneity and ecological functionality across varying landscapes; (v) maintenance of the region's hydrological integrity and connectivity; (vi) ensuring the ecological representativeness of the protected areas network; (vii) the provision of economic incentives for conservation of the land; and (viii) recognition for and protection of traditional peoples, their values and resources, and their way of life (Tomas et al., 2025).

The Pantanal has been, for a long time, a showcase model for the coexistence of conservation and sustainable use. However, increasing economic pressures, climate change, infrastructure projects, and loss of traditional cultural knowledge are challenging its historical position. To regain its importance and position as a positive example in conservation, regional stakeholders, governments, and conservation practitioners have to create a foundation for a common sustainable future for the entire region.

This special section is the beginning of this process. The papers contained here contribute to our knowledge of how the system functions, how it is impacted by and responds to human activities, and to the development of effective management strategies to support a concurred sustainability agenda for the Pantanal. We invite everyone to keep contributing to this effort.

All the authors contributed to the editorial article, reviewing, and discussing key points.

The authors declare no conflict of interest.

Abstract Image

潘塔纳尔河的保护科学与实践:从危机到希望
潘塔纳尔是世界上最大的连续淡水湿地(Junk et al., 2011)。它位于南美洲中部,占地17.93万平方公里,包括巴西、巴拉圭和玻利维亚的部分地区。巴拉圭河——潘塔纳尔河是其泛滥平原——绵延2695公里,连接着巴西与玻利维亚、巴拉圭和阿根廷(Girard et al., 2025)。潘塔纳尔河的规模和幅度影响着南美洲大部分地区的水文、生物多样性、历史和文化(Wantzen et al., 2023)。潘塔纳尔也一直是濒危和受威胁物种的避难所,也是自然资源低强度利用的避难所(Tomas et al., 2019)。然而,最近野火、森林砍伐和基础设施项目增加了对保护的关注(Tortato et al., 2022)(图1)。但在政府、非政府组织、当地居民和科学家的支持下,潘塔纳尔仍然可以成为一个充满保护希望的地方。人类在潘塔纳尔的永久居住可以追溯到8000多年前(beespalez, 2015),在潘塔纳尔北部出现的第一个定居点迹象大约发生在27000年前(Vialou等人,2017)。虽然第一批欧洲殖民者在16世纪初就到达了那里,但直到18世纪后期,葡萄牙人才开始在该地区建立一个有组织的殖民议程(de Fátima Costa, 1999)。在此期间,大多数土著群体被(Peixoto, 2017)、牛场(de Abreu et al., 2010)和河流渔业社区(Chiaravalloti, 2019)所取代。如今,养牛场占据了潘塔纳尔地区90%以上的土地(Chiaravalloti等人,2025年),牲畜存储量总计约380万头(Tomas等人,2019年)。该地区还有大约8000人注册为专业渔民(Fernando, Lopes, et al., 2024),每年的收入估计为8400万美元(Girard et al., 2025),而未报告的“零星”渔民可能是这个数字的10倍(Fernando, Lopes, et al., 2024)。尽管有长期、广泛的人类占领和暴力的殖民历史,潘塔纳尔河仍然保存完好,80%的原生植被仍然存在(Mapbiomas, 2022)。此外,偷猎对本地野生动物的威胁非常低(Desbiez et al., 2011)。因此,潘塔纳尔是许多濒危物种的避难所,如美洲虎(Panthera onca)、巨型水獭(Pteronura brasiliensis)、沼泽鹿(Blastocerus dichotomus)和风信子金刚鹦鹉(Anodorhynchus hyacinthinus) (Tomas等人,2019)。也没有过度捕捞的迹象(Fernando, Lopes, et al., 2024),因为即使是当地社区集约利用的地区,仍然显示出相对完整的鱼类群落(Polaz et al., 2017)。然而,正如本期特刊所介绍的那样,潘塔纳尔正在经历迅速的变化。世界上最大和最受保护的湿地之一正在成为一个值得关注的地方。潘塔纳尔三分之一的生态走廊已经消失(da Rosa Oliveira等人,2025年),如果这种趋势继续下去,到2050年可能会失去14,000平方公里的原生植被(Guerra等人,2025年)。基础设施项目的扩张和建设的复合效应开始通过生态系统级联,并对该地区构成日益严重的威胁(Tortato et al., 2022)。这些发展似乎必然会增加和加速。例如,通过疏浚、河岸稳定、改道和港口建设将巴拉圭河改造成Hidrovia水道的建议将严重破坏水文(Girard et al., 2025),导致洪水循环的崩溃及其对植被或生物多样性的好处,并最终导致鱼类丰度和多样性的广泛减少(Fernando et al., 2025)。这个特别的部分还展示了改变当前趋势的途径。本节的论文表明,该地区和当地利益相关者拥有一切手段来保证该地区继续成为生物多样性保护和可持续性的地方:保护希望。例如,正如Chiaravalloti等人(2025)所示,潘塔纳尔可持续发展历史的基石之一是其强大的土地权属制度,具有明确的产权,这对实施有针对性和基于区域的保护计划至关重要(Robinson等人,2018)。同样,潘塔纳尔的人民和机构传统上有着强大的合作甚至相互依存的传统,这主要是由于在高度变化和季节不可预测的景观中需要相互依赖(Marchini et al., 2024)。例如,集体管理计划一直是潘塔纳尔渔业和畜牧业协作社会生态系统的一部分(Tomas等人,2019)。 这些综合方法与明确的土地权属制度一起,可以成为发展若干以社区为基础的、景观和物种保护倡议的途径。它们包括潘塔纳尔河不同地区的多中心治理体系;生物多样性抵消计划(Lourival et al., 2025)、“其他有效的生物多样性保护措施”(OECM)、可持续牧场认证计划(Chiaravalloti et al. 2025)、自然资本指标框架(NCIF) (Fairbrass et al., 2025)和基于共存与合作的物种保护计划(Marchini et al., 2024)。然而,为了实施这些行动,建立一些基本的保护原则是至关重要的,我们也在特刊中描述了这些原则;它们是:(i)考虑将巴拉圭河流域作为一个单一的管理单位;(ii)订立符合“限制使用”方法或概念的规则;(三)确保可持续地利用整个区域的所有自然资源;(iv)维持不同景观的环境异质性和生态功能;(五)维持该地区水文的完整性和连通性;(vi)确保保护区网络的生态代表性;(vii)提供经济诱因以保育土地;(八)承认和保护传统民族、他们的价值观和资源以及他们的生活方式(Tomas et al., 2025)。长期以来,潘塔纳尔河一直是保护与可持续利用并存的展示模式。然而,日益增长的经济压力、气候变化、基础设施项目和传统文化知识的丧失正在挑战其历史地位。为了重新获得其作为保护的积极榜样的重要性和地位,区域利益相关者、政府和保护从业者必须为整个地区共同的可持续未来奠定基础。这个特殊的部分是这个过程的开始。这里包含的文件有助于我们了解系统如何运作,它如何受到人类活动的影响和响应,并有助于制定有效的管理战略,以支持潘塔纳尔的可持续性议程。我们邀请每个人继续为这一努力做出贡献。所有作者都对社论文章、评论和讨论要点做出了贡献。作者声明无利益冲突。
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 Science and Practice
Conservation Science and Practice BIODIVERSITY CONSERVATION-
CiteScore
5.50
自引率
6.50%
发文量
240
审稿时长
10 weeks
×
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:604180095
Book学术官方微信