Tatiane Micheletti, Frances E. C. Stewart, Samuel Hache, Eliot J. B. McIntire
{"title":"调和伞类评价中相反的结论","authors":"Tatiane Micheletti, Frances E. C. Stewart, Samuel Hache, Eliot J. B. McIntire","doi":"10.1111/cobi.70106","DOIUrl":null,"url":null,"abstract":"<p>With accelerating species decline, prioritizing protection of umbrella species is appealing. This strategy assumes that protecting one species confers a “protective umbrella” to co-occurring ones (Fleishman et al., <span>2000</span>), improving conservation efficiency. However, no standard criteria exist to quantify the value of an umbrella species. Consequently, evaluations of the same umbrella species may provide opposite conclusions, as boreal woodland caribou (<i>Rangifer tarandus caribou</i>) (henceforth caribou) exemplify. With important implications for conservation planning, literature should be carefully reconciled.</p><p>Over the past decades, caribou populations have significantly declined (Hebblewhite, <span>2017</span>), prompting legal listings, recovery efforts (Government of Canada, <span>2021</span>), and research, including quantifying their value as an umbrella species. For example, although Drever et al. (<span>2019</span>) and Labadie et al. (<span>2024</span>) suggest the caribou is a good umbrella species for boreal landbirds, Micheletti et al. (<span>2023</span>) conclude the umbrella may leak. We suggest that this apparent discrepancy likely stems from the different methods used to evaluate umbrella effectiveness—including their spatial scale—rather than different spatial scales or locations alone (Figure 1).</p><p>Umbrella species effectiveness is often determined based on whether varying levels of range-wide protection conferred on one species protect other species (Bichet et al., <span>2016</span>; Johnson et al., <span>2022</span>; Labadie et al., <span>2024</span>; Roberge & Angelstam, <span>2004</span>). In simple cases, an umbrella species’ value is tested by examining the level of overlap between that species range with other species ranges. A high amount of overlap is interpreted as a high umbrella value (e.g., Nicholson et al., <span>2013</span>; Roberge & Angelstam, <span>2004</span>; Figure 1a). In more complex cases, hypothetical umbrella species’ protection and conservation-oriented management (e.g., low-intensity forestry) are compared with no-protection and use-oriented management (e.g., high-intensity forestry) scenarios (e.g., Labadie et al., <span>2024</span>; Figure 1b). Wide-ranging species are common umbrella candidates (Bichet et al., <span>2016</span>; Johnson et al., <span>2022</span>; Labadie et al., <span>2024</span>; Nicholson et al., <span>2013</span>) because conservation of large areas—if properly implemented—can increase protection of other species (Roberge & Angelstam, <span>2004</span>).</p><p>The wide range of caribou in Canada's boreal forest overlaps with 90% of all boreal mammals and birds (Drever et al., <span>2019</span>), covering many hotspots (Johnson et al., <span>2022</span>) and high-quality areas for co-occurring species. Unsurprisingly, traditional analyses of caribou habitat (i.e., approaches based on range overlap and use scenarios) often conclude caribou are an effective umbrella (Bichet et al., <span>2016</span>; Labadie et al., <span>2024</span>), akin to other wide-ranging species (e.g., Nicholson et al., <span>2013</span>). However, land protection rarely covers a wide-ranging species’ entire distribution and caribou's high-quality habitat does not generally overlap with other species’ high-quality habitat. In the Northwest Territories, for example, caribou's high-quality habitat (i.e., 250 × 250-m cell; assessed using resource selection values [DeMars et al., <span>2020</span>]) overlaps with those of only a small proportion of the boreal landbird community (Micheletti et al., <span>2023</span>).</p><p>When a desired area for conservation is defined (e.g., 30% by 2030 [Eckert et al., <span>2023</span>]), as opposed to protecting all the land it is possible to protect, it becomes ineffective to assess an umbrella species based on the percentage of range overlap with co-occurring species or based on a comparison between no-protection versus protection scenarios. Instead, an umbrella candidate may be more effectively assessed by comparing outcomes of protecting its high-quality habitat (i.e., primary focus of protection within a species’ range) with outcomes protecting an equivalent area at random locations (i.e., a null model approach [Kerr, <span>1997</span>]), or other criteria (i.e., an alternative model approach). Determining whether conservation of a proposed umbrella species’ high-quality habitat would provide more conservation opportunities for other species than expected by chance alone could help promote more effective conservation planning. Such an umbrella index approach can reduce misinterpretation of results and enable more accurate assessments of conservation gains.</p><p>In their development and implementation of an umbrella index, Micheletti et al. (<span>2023</span>) found that caribou may not be an effective umbrella for boreal landbirds. Prioritizing caribou needs would be more beneficial than protecting random habitat for <20% of the focal landbird species (<i>n</i> = 71). Micheletti et al.’s (<span>2023</span>) results are consistent with the results of multiobjective studies. Martin et al. (<span>2022</span>) observed low overlap between priority areas for caribou conservation and other biodiversity objectives, except carbon stocks. Similarly, Johnson et al. (<span>2022</span>) concluded that, although caribou as an umbrella species could help protect, for example, carbon stocks, this strategy is unlikely to be efficient for achieving multiple conservation targets due to a lack of spatial overlap between caribou and most other values.</p><p>With conflicting findings about a species’ umbrella value, understanding the underlying assessment methods can help reconcile these findings. The umbrella index (Micheletti et al., <span>2023</span>; Figure 1c) provides a potential standardized method, but it could be improved by accounting for habitat size, configuration, and connectivity (Favreau et al., <span>2006</span>). Micheletti et al.’s (<span>2023</span>) “leaky umbrella” example hinges on a comparison of the candidate umbrella species’ high-quality habitat with equally sized random areas; altering the comparison criteria could change the results.</p><p>Using a widely distributed flagship species as an umbrella species is appealing because such species can provide conservation opportunities for otherwise unprotected areas (Runge et al., <span>2019</span>). Yet, single-species strategies rarely meet broad biodiversity targets (Andelman & Fagan, <span>2000</span>), especially in frameworks aiming to protect specific areas with finite resource allocations. Caribou could serve as an effective umbrella for the boreal ecosystem if large proportions of its range were effectively protected. However, resource constraints and competing land-use priorities often preclude this. Therefore, incorporating caribou into multiobjective assessments would provide an opportunity to enhance conservation planning efficiency (Martin et al., <span>2022</span>; Wiersma & Sleep, <span>2018</span>).</p><p>As a first step, an umbrella index can be valuable for identifying potential gaps in single-species conservation efforts, comparing efficiency of alternative umbrella species, understanding under what conditions the value of an umbrella species could be maximized, and supporting protected area network planning (e.g., informing the single-large-or-several-small debate [Fahrig et al., <span>2022</span>; May et al., <span>2019</span>]). Regardless of whether one uses overlapping ranges, scenarios, or null and alternative models, careful evaluation of the assessment method for inferring anticipated conservation gains (i.e., umbrella value) is key to correctly interpreting findings and better informing land-use planning.</p>","PeriodicalId":10689,"journal":{"name":"Conservation Biology","volume":"39 5","pages":""},"PeriodicalIF":5.5000,"publicationDate":"2025-08-11","publicationTypes":"Journal Article","fieldsOfStudy":null,"isOpenAccess":false,"openAccessPdf":"https://conbio.onlinelibrary.wiley.com/doi/epdf/10.1111/cobi.70106","citationCount":"0","resultStr":"{\"title\":\"Reconciling opposite conclusions in umbrella species evaluation\",\"authors\":\"Tatiane Micheletti, Frances E. C. Stewart, Samuel Hache, Eliot J. B. McIntire\",\"doi\":\"10.1111/cobi.70106\",\"DOIUrl\":null,\"url\":null,\"abstract\":\"<p>With accelerating species decline, prioritizing protection of umbrella species is appealing. This strategy assumes that protecting one species confers a “protective umbrella” to co-occurring ones (Fleishman et al., <span>2000</span>), improving conservation efficiency. However, no standard criteria exist to quantify the value of an umbrella species. Consequently, evaluations of the same umbrella species may provide opposite conclusions, as boreal woodland caribou (<i>Rangifer tarandus caribou</i>) (henceforth caribou) exemplify. With important implications for conservation planning, literature should be carefully reconciled.</p><p>Over the past decades, caribou populations have significantly declined (Hebblewhite, <span>2017</span>), prompting legal listings, recovery efforts (Government of Canada, <span>2021</span>), and research, including quantifying their value as an umbrella species. For example, although Drever et al. (<span>2019</span>) and Labadie et al. (<span>2024</span>) suggest the caribou is a good umbrella species for boreal landbirds, Micheletti et al. (<span>2023</span>) conclude the umbrella may leak. We suggest that this apparent discrepancy likely stems from the different methods used to evaluate umbrella effectiveness—including their spatial scale—rather than different spatial scales or locations alone (Figure 1).</p><p>Umbrella species effectiveness is often determined based on whether varying levels of range-wide protection conferred on one species protect other species (Bichet et al., <span>2016</span>; Johnson et al., <span>2022</span>; Labadie et al., <span>2024</span>; Roberge & Angelstam, <span>2004</span>). In simple cases, an umbrella species’ value is tested by examining the level of overlap between that species range with other species ranges. A high amount of overlap is interpreted as a high umbrella value (e.g., Nicholson et al., <span>2013</span>; Roberge & Angelstam, <span>2004</span>; Figure 1a). In more complex cases, hypothetical umbrella species’ protection and conservation-oriented management (e.g., low-intensity forestry) are compared with no-protection and use-oriented management (e.g., high-intensity forestry) scenarios (e.g., Labadie et al., <span>2024</span>; Figure 1b). Wide-ranging species are common umbrella candidates (Bichet et al., <span>2016</span>; Johnson et al., <span>2022</span>; Labadie et al., <span>2024</span>; Nicholson et al., <span>2013</span>) because conservation of large areas—if properly implemented—can increase protection of other species (Roberge & Angelstam, <span>2004</span>).</p><p>The wide range of caribou in Canada's boreal forest overlaps with 90% of all boreal mammals and birds (Drever et al., <span>2019</span>), covering many hotspots (Johnson et al., <span>2022</span>) and high-quality areas for co-occurring species. Unsurprisingly, traditional analyses of caribou habitat (i.e., approaches based on range overlap and use scenarios) often conclude caribou are an effective umbrella (Bichet et al., <span>2016</span>; Labadie et al., <span>2024</span>), akin to other wide-ranging species (e.g., Nicholson et al., <span>2013</span>). However, land protection rarely covers a wide-ranging species’ entire distribution and caribou's high-quality habitat does not generally overlap with other species’ high-quality habitat. In the Northwest Territories, for example, caribou's high-quality habitat (i.e., 250 × 250-m cell; assessed using resource selection values [DeMars et al., <span>2020</span>]) overlaps with those of only a small proportion of the boreal landbird community (Micheletti et al., <span>2023</span>).</p><p>When a desired area for conservation is defined (e.g., 30% by 2030 [Eckert et al., <span>2023</span>]), as opposed to protecting all the land it is possible to protect, it becomes ineffective to assess an umbrella species based on the percentage of range overlap with co-occurring species or based on a comparison between no-protection versus protection scenarios. Instead, an umbrella candidate may be more effectively assessed by comparing outcomes of protecting its high-quality habitat (i.e., primary focus of protection within a species’ range) with outcomes protecting an equivalent area at random locations (i.e., a null model approach [Kerr, <span>1997</span>]), or other criteria (i.e., an alternative model approach). Determining whether conservation of a proposed umbrella species’ high-quality habitat would provide more conservation opportunities for other species than expected by chance alone could help promote more effective conservation planning. Such an umbrella index approach can reduce misinterpretation of results and enable more accurate assessments of conservation gains.</p><p>In their development and implementation of an umbrella index, Micheletti et al. (<span>2023</span>) found that caribou may not be an effective umbrella for boreal landbirds. Prioritizing caribou needs would be more beneficial than protecting random habitat for <20% of the focal landbird species (<i>n</i> = 71). Micheletti et al.’s (<span>2023</span>) results are consistent with the results of multiobjective studies. Martin et al. (<span>2022</span>) observed low overlap between priority areas for caribou conservation and other biodiversity objectives, except carbon stocks. Similarly, Johnson et al. (<span>2022</span>) concluded that, although caribou as an umbrella species could help protect, for example, carbon stocks, this strategy is unlikely to be efficient for achieving multiple conservation targets due to a lack of spatial overlap between caribou and most other values.</p><p>With conflicting findings about a species’ umbrella value, understanding the underlying assessment methods can help reconcile these findings. The umbrella index (Micheletti et al., <span>2023</span>; Figure 1c) provides a potential standardized method, but it could be improved by accounting for habitat size, configuration, and connectivity (Favreau et al., <span>2006</span>). Micheletti et al.’s (<span>2023</span>) “leaky umbrella” example hinges on a comparison of the candidate umbrella species’ high-quality habitat with equally sized random areas; altering the comparison criteria could change the results.</p><p>Using a widely distributed flagship species as an umbrella species is appealing because such species can provide conservation opportunities for otherwise unprotected areas (Runge et al., <span>2019</span>). Yet, single-species strategies rarely meet broad biodiversity targets (Andelman & Fagan, <span>2000</span>), especially in frameworks aiming to protect specific areas with finite resource allocations. Caribou could serve as an effective umbrella for the boreal ecosystem if large proportions of its range were effectively protected. However, resource constraints and competing land-use priorities often preclude this. Therefore, incorporating caribou into multiobjective assessments would provide an opportunity to enhance conservation planning efficiency (Martin et al., <span>2022</span>; Wiersma & Sleep, <span>2018</span>).</p><p>As a first step, an umbrella index can be valuable for identifying potential gaps in single-species conservation efforts, comparing efficiency of alternative umbrella species, understanding under what conditions the value of an umbrella species could be maximized, and supporting protected area network planning (e.g., informing the single-large-or-several-small debate [Fahrig et al., <span>2022</span>; May et al., <span>2019</span>]). 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引用次数: 0
摘要
随着物种的加速减少,优先保护伞类物种是有吸引力的。该策略假设保护一个物种可以为共存的物种提供“保护伞”(Fleishman et al., 2000),从而提高保护效率。然而,目前还没有标准标准来量化伞类物种的价值。因此,对同一保护伞物种的评估可能会得出相反的结论,如北方林地驯鹿(Rangifer tarandus caribou)(以下简称北美驯鹿)的例子。文献对于保护规划具有重要意义,因此应当仔细地加以调和。在过去的几十年里,北美驯鹿的数量显著下降(Hebblewhite, 2017),这促使了法律的上市、恢复努力(加拿大政府,2021)和研究,包括量化它们作为保护伞物种的价值。例如,尽管Drever等人(2019)和Labadie等人(2024)认为北美驯鹿是北方陆鸟的良好保护伞物种,但Micheletti等人(2023)认为保护伞可能会泄漏。我们认为,这种明显的差异可能源于评估伞效的不同方法——包括它们的空间尺度——而不仅仅是不同的空间尺度或地点(图1)。保护伞物种的有效性通常取决于赋予一个物种的不同范围保护水平是否能保护其他物种(bicchet et al., 2016; Johnson et al., 2022; Labadie et al., 2024; Roberge & Angelstam, 2004)。在简单的情况下,通过检查该物种范围与其他物种范围之间的重叠程度来测试保护伞物种的价值。高重叠量被解释为高保护伞值(例如,Nicholson et al., 2013; Roberge & Angelstam, 2004;图1a)。在更复杂的情况下,将假设的伞形物种保护和以保护为导向的管理(如低强度林业)与不保护和以利用为导向的管理(如高强度林业)情景(如Labadie et al., 2024;图1b)进行比较。广域物种是常见的保护伞候选物种(bicchet et al., 2016; Johnson et al., 2022; Labadie et al., 2024; Nicholson et al., 2013),因为大面积的保护如果实施得当,可以增加对其他物种的保护(Roberge & Angelstam, 2004)。加拿大北方森林中的驯鹿种类繁多,与90%的北方哺乳动物和鸟类重叠(Drever等人,2019),覆盖了许多热点地区(Johnson等人,2022)和物种共存的高质量地区。毫不奇怪,对北美驯鹿栖息地的传统分析(即基于范围重叠和使用场景的方法)通常得出结论,北美驯鹿是一个有效的保护伞(bicchet等人,2016;Labadie等人,2024),类似于其他广泛的物种(例如,Nicholson等人,2013)。然而,土地保护很少覆盖广泛物种的整个分布,北美驯鹿的高质量栖息地通常不会与其他物种的高质量栖息地重叠。例如,在西北地区,北美驯鹿的高质量栖息地(即250 × 250 m的细胞;使用资源选择值进行评估[DeMars等,2020])与北方陆鸟群落的一小部分重叠(Micheletti等,2023)。当确定了理想的保护区域(例如,到2030年达到30% [Eckert et al., 2023]),而不是保护所有可能保护的土地时,基于与共生物种的范围重叠百分比或基于无保护与保护情景之间的比较来评估保护伞物种是无效的。相反,通过比较保护其高质量栖息地的结果(即在物种范围内的主要保护重点)与保护随机地点等效区域的结果(即零模型方法[Kerr, 1997])或其他标准(即替代模型方法),可以更有效地评估一个总体候选物种。确定保护某一伞形物种的优质生境是否会为其他物种提供更多的保护机会,而不是仅靠偶然的机会,有助于促进更有效的保护规划。这种总括指数方法可以减少对结果的误解,并使对保护成果的评估更加准确。Micheletti等人(2023)在制定和实施保护伞指数时发现,北美驯鹿可能不是北方陆鸟的有效保护伞。优先考虑驯鹿的需求将比保护20%的重点陆鸟物种(n = 71)的随机栖息地更有益。Micheletti et al.(2023)的结果与多目标研究的结果一致。Martin et al.(2022)观察到,除碳储量外,北美驯鹿保护的优先区域与其他生物多样性目标之间的重叠程度较低。同样,Johnson等人。 (2022)得出的结论是,尽管北美驯鹿作为保护伞物种可以帮助保护碳储量等,但由于北美驯鹿与大多数其他物种之间缺乏空间重叠,这种策略不太可能有效地实现多个保护目标。由于对物种保护伞价值的发现相互矛盾,了解潜在的评估方法可以帮助调和这些发现。保护伞指数(Micheletti et al., 2023;图1c)提供了一种潜在的标准化方法,但可以通过考虑栖息地的大小、配置和连通性来改进它(Favreau et al., 2006)。Micheletti等人(2023)的“漏伞”例子取决于对候选伞种的高质量栖息地与等大小随机区域的比较;改变比较标准可能会改变结果。使用广泛分布的旗舰物种作为保护伞物种是有吸引力的,因为这些物种可以为其他未受保护的地区提供保护机会(Runge等人,2019)。然而,单一物种策略很少能满足广泛的生物多样性目标(Andelman & Fagan, 2000),特别是在旨在保护资源分配有限的特定区域的框架中。如果驯鹿的大部分活动范围得到有效保护,它们可以作为北方生态系统的有效保护伞。然而,资源限制和相互竞争的土地使用优先次序往往使这种做法无法实现。因此,将北美驯鹿纳入多目标评估将为提高保护规划效率提供机会(Martin et al., 2022; Wiersma & Sleep, 2018)。作为第一步,保护伞指数对于识别单物种保护工作的潜在差距,比较替代保护伞物种的效率,了解在什么条件下保护伞物种的价值可以最大化,以及支持保护区网络规划(例如,为单个大或多个小的争论提供信息[Fahrig等,2022;May等,2019])具有重要价值。无论是否使用重叠范围、情景或无效和替代模型,对推断预期保护收益(即保护伞值)的评估方法进行仔细评估是正确解释研究结果和更好地为土地利用规划提供信息的关键。
Reconciling opposite conclusions in umbrella species evaluation
With accelerating species decline, prioritizing protection of umbrella species is appealing. This strategy assumes that protecting one species confers a “protective umbrella” to co-occurring ones (Fleishman et al., 2000), improving conservation efficiency. However, no standard criteria exist to quantify the value of an umbrella species. Consequently, evaluations of the same umbrella species may provide opposite conclusions, as boreal woodland caribou (Rangifer tarandus caribou) (henceforth caribou) exemplify. With important implications for conservation planning, literature should be carefully reconciled.
Over the past decades, caribou populations have significantly declined (Hebblewhite, 2017), prompting legal listings, recovery efforts (Government of Canada, 2021), and research, including quantifying their value as an umbrella species. For example, although Drever et al. (2019) and Labadie et al. (2024) suggest the caribou is a good umbrella species for boreal landbirds, Micheletti et al. (2023) conclude the umbrella may leak. We suggest that this apparent discrepancy likely stems from the different methods used to evaluate umbrella effectiveness—including their spatial scale—rather than different spatial scales or locations alone (Figure 1).
Umbrella species effectiveness is often determined based on whether varying levels of range-wide protection conferred on one species protect other species (Bichet et al., 2016; Johnson et al., 2022; Labadie et al., 2024; Roberge & Angelstam, 2004). In simple cases, an umbrella species’ value is tested by examining the level of overlap between that species range with other species ranges. A high amount of overlap is interpreted as a high umbrella value (e.g., Nicholson et al., 2013; Roberge & Angelstam, 2004; Figure 1a). In more complex cases, hypothetical umbrella species’ protection and conservation-oriented management (e.g., low-intensity forestry) are compared with no-protection and use-oriented management (e.g., high-intensity forestry) scenarios (e.g., Labadie et al., 2024; Figure 1b). Wide-ranging species are common umbrella candidates (Bichet et al., 2016; Johnson et al., 2022; Labadie et al., 2024; Nicholson et al., 2013) because conservation of large areas—if properly implemented—can increase protection of other species (Roberge & Angelstam, 2004).
The wide range of caribou in Canada's boreal forest overlaps with 90% of all boreal mammals and birds (Drever et al., 2019), covering many hotspots (Johnson et al., 2022) and high-quality areas for co-occurring species. Unsurprisingly, traditional analyses of caribou habitat (i.e., approaches based on range overlap and use scenarios) often conclude caribou are an effective umbrella (Bichet et al., 2016; Labadie et al., 2024), akin to other wide-ranging species (e.g., Nicholson et al., 2013). However, land protection rarely covers a wide-ranging species’ entire distribution and caribou's high-quality habitat does not generally overlap with other species’ high-quality habitat. In the Northwest Territories, for example, caribou's high-quality habitat (i.e., 250 × 250-m cell; assessed using resource selection values [DeMars et al., 2020]) overlaps with those of only a small proportion of the boreal landbird community (Micheletti et al., 2023).
When a desired area for conservation is defined (e.g., 30% by 2030 [Eckert et al., 2023]), as opposed to protecting all the land it is possible to protect, it becomes ineffective to assess an umbrella species based on the percentage of range overlap with co-occurring species or based on a comparison between no-protection versus protection scenarios. Instead, an umbrella candidate may be more effectively assessed by comparing outcomes of protecting its high-quality habitat (i.e., primary focus of protection within a species’ range) with outcomes protecting an equivalent area at random locations (i.e., a null model approach [Kerr, 1997]), or other criteria (i.e., an alternative model approach). Determining whether conservation of a proposed umbrella species’ high-quality habitat would provide more conservation opportunities for other species than expected by chance alone could help promote more effective conservation planning. Such an umbrella index approach can reduce misinterpretation of results and enable more accurate assessments of conservation gains.
In their development and implementation of an umbrella index, Micheletti et al. (2023) found that caribou may not be an effective umbrella for boreal landbirds. Prioritizing caribou needs would be more beneficial than protecting random habitat for <20% of the focal landbird species (n = 71). Micheletti et al.’s (2023) results are consistent with the results of multiobjective studies. Martin et al. (2022) observed low overlap between priority areas for caribou conservation and other biodiversity objectives, except carbon stocks. Similarly, Johnson et al. (2022) concluded that, although caribou as an umbrella species could help protect, for example, carbon stocks, this strategy is unlikely to be efficient for achieving multiple conservation targets due to a lack of spatial overlap between caribou and most other values.
With conflicting findings about a species’ umbrella value, understanding the underlying assessment methods can help reconcile these findings. The umbrella index (Micheletti et al., 2023; Figure 1c) provides a potential standardized method, but it could be improved by accounting for habitat size, configuration, and connectivity (Favreau et al., 2006). Micheletti et al.’s (2023) “leaky umbrella” example hinges on a comparison of the candidate umbrella species’ high-quality habitat with equally sized random areas; altering the comparison criteria could change the results.
Using a widely distributed flagship species as an umbrella species is appealing because such species can provide conservation opportunities for otherwise unprotected areas (Runge et al., 2019). Yet, single-species strategies rarely meet broad biodiversity targets (Andelman & Fagan, 2000), especially in frameworks aiming to protect specific areas with finite resource allocations. Caribou could serve as an effective umbrella for the boreal ecosystem if large proportions of its range were effectively protected. However, resource constraints and competing land-use priorities often preclude this. Therefore, incorporating caribou into multiobjective assessments would provide an opportunity to enhance conservation planning efficiency (Martin et al., 2022; Wiersma & Sleep, 2018).
As a first step, an umbrella index can be valuable for identifying potential gaps in single-species conservation efforts, comparing efficiency of alternative umbrella species, understanding under what conditions the value of an umbrella species could be maximized, and supporting protected area network planning (e.g., informing the single-large-or-several-small debate [Fahrig et al., 2022; May et al., 2019]). Regardless of whether one uses overlapping ranges, scenarios, or null and alternative models, careful evaluation of the assessment method for inferring anticipated conservation gains (i.e., umbrella value) is key to correctly interpreting findings and better informing land-use planning.
期刊介绍:
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