We use cookies to distinguish you from other users and to provide you with a better experience on our websites. Close this message to accept cookies or find out how to manage your cookie settings.
To save content items to your account,
please confirm that you agree to abide by our usage policies.
If this is the first time you use this feature, you will be asked to authorise Cambridge Core to connect with your account.
Find out more about saving content to .
To save content items to your Kindle, first ensure no-reply@cambridge.org
is added to your Approved Personal Document E-mail List under your Personal Document Settings
on the Manage Your Content and Devices page of your Amazon account. Then enter the ‘name’ part
of your Kindle email address below.
Find out more about saving to your Kindle.
Note you can select to save to either the @free.kindle.com or @kindle.com variations.
‘@free.kindle.com’ emails are free but can only be saved to your device when it is connected to wi-fi.
‘@kindle.com’ emails can be delivered even when you are not connected to wi-fi, but note that service fees apply.
Successful conservation depends on human attitudes, values, and support. Increasingly scientists and managers analyse not only species status and needs, but also the long-term cost, risk, and effectiveness of activities. Socioeconomic costs and benefits are integral to these analyses. Gorongosa National Park in Mozambique provides a case study of conservation integrated with local community needs. Endangered Delta smelt in California exemplify conflicts around water apportionment. Case studies demonstrating the importance of socioeconomic considerations are provided by management of gray wolves and grizzly bears in the United States. The story of sage grouse illustrates how a regional agreement that resulted from many years of collaboration among stakeholders can be nullified by political changes at the national level. The cultural and socioeconomic values and rights of indigenous people play a prominent role in salmon management that can run counter to the interests of hydroelectric companies and other water users. Case studies illustrate how habitat management can be facilitated by participation by non-governmental organizations. Socioeconomic and political consideration also underlie the question of who can take responsibility for managing conservation-reliant species.
A conservation-reliant species is vulnerable to threats that persist; it requires continued management intervention to prevent a decline toward extinction or to maintain a population. The degree of conservation reliance varies over time and among species. Globally, the extent of conservation reliance is accelerating faster than we can provide resources to combat extinctions and promote recovery. A species is recognized as being conservation reliant or emerging from that status based on a general assessment that includes status and threats, the potential for managing the threats, actions taken to manage the threats and the species itself, population monitoring, and monitoring of threats. Species differ in their susceptibility to threats and their potential to respond to management actions, and threats differ in manageability. We use California condor management as a case study for these features of conservation reliance.
Understanding threats and our ability to manage them is the first step in shepherding conservation-reliant species toward sustainability or recovery. This chapter contrasts situations in which a single threat dominates with more complex situations in which multiple threats interact. Interactions among threats raise the likelihood of conservation reliance, as this chapter illustrates in a case study of vultures. Several other case studies illustrate the effectiveness of different legal and management approaches to imperilment and the importance of identifying its root causes. Case studies, including some revolving around dams, also illustrate the complexities that attend socioeconomic drivers of imperilment and differences in the scale and manageability of threats. The chapter also describes several threats such as storms, tsunamis, or volcanic eruptions that are not manageable.
The array of tools for addressing the needs of imperiled and conservation-reliant species is increasing. This chapter provides case studies and examples of the use of translocation and captive breeding for addressing threats, and discuss attributes of receiving sites. Tools for tracking species movements and for remote sensing can efficiently provide large amounts of habitat and species data. Sometimes tools can be used to address common threats such as those created by habitat change or pesticide use, benefitting multiple species. We provide Old World vultures offer a case study. Managing for surrogate, umbrella, indicator, focal, keystone, or pollinator species may assist other species as well. Such roles should be acknowledged in prioritizing conservation activities. Emerging technologies, including genetic tools and artificial intelligence, can help to address imperilment and conservation reliance if ethical issues can be navigated.
Many nations have developed policies and enforced legal approaches for addressing the needs of species at risk of extinction. Generally, however, conservation reliance is not acknowledged legally and is therefore ignored. Increasingly, legal approaches reflect the importance of (1) values in addition to hunting and fishing, (2) wildlife as a shared resource, (3) intrinsic rather than instrumental value, (4) helping species to become self-sustaining, and (5) long-term support for imperiled species. The International Union for the Conservation of Naturehas provided an international standard for recognizing species status. In the United States, the Endangered Species Act and National Environmental Policy Act provide a legal framework for species conservation that has been effective (although these acts have also spawned many legal challenges that have consumed the time and resources of stakeholders). The effectiveness of imperiled species laws depends on funding that can vary, leading to varying implementation and enforcement. Conservation reliance is seldom addressed explicitly. Responsibility for implementation may be spread across national, state or province, and more local entities.
Current methods for making decisions about what to fund and at what level are not sufficiently transparent or objective. Acknowledging conservation reliance fosters a realistic approach and outcomes. Prioritization requires an agreed-upon pool of species to consider within a defined area. Defining and ranking prioritization criteria presents a variety of challenges, including accounting for the manageability of threats, species vulnerability, and species genetic and phenotypic traits. Including social and economic factors increases the probability that plans will be implemented. This chapter also considers how factor weightings are derived and means of dealing with uncertainty. Four examples of prioritization processes illustrate the variety of current approaches. Few approaches explicitly consider the long-term demands of conservation reliance. The ethics that underlie conservation triage affect how people undertake prioritization. This book advocates the use of explicit prioritization criteria that include uncertainties and derive from values and interests of diverse stakeholders. Models should acknowledge a wide array of ecological and socioeconomic costs and benefits, probabilities of success, and projected conservation reliance.
Conservation reliance exists along a spectrum from species extinction to species recovery; from requiring intensive to minimal management. This chapter provides case studies of full or partial recovery and explores what made this possible using the Oregon chub, Aleutian cackling goose, southern white rhinoceros, black-capped vireo, and Robbins’ cinquefoil. Toward the other end of the spectrum, continued translocations or releases are required to maintain Oregon silverspot butterflies and Chatham Island black robins. Management is not always successful, however, as seen for Australian woylies. Some species, such as the Guam kingfisher, are extinct in the wild but maintained in zoos. Finally, there are lessons to be learned from species such as the po’ouli, dusky seaside sparrow, and Christmas Island pipistrelle, for which investments were too little or too late. Management of imperiled species is a societal investment and people’s attitudes play an important role in successful recovery. Participation by citizens and non-governmental organizations is particularly important when species are conservation reliant, as the long-term investment required can rarely be sustained otherwise.
People differ in how and how much they value nature, and in their attitudes toward conservation. This affects the implementation of laws and regulations and the criteria used in prioritization of conservation actions. Yet collaboration is essential, especially when conservation reliance requires long-term commitments. Individuals, communities, government agencies, and non-governmental organizations must all be involved. Shepherding nature is about taking responsibility for watching over and caring for species and Earth’s biodiversity. Countering the rising rate of extinctions will require a transformative change in how people relate to the environment, nature, and one another.
Expanding the scope of conservation beyond species and taking a broader, more holistic approach can provide greater and more lasting benefits to a wider ecological community. However, doing so can reduce our capacity to understand and ameliorate threats to individual species. Factors that favor a broader approach can be used to prioritize areas for protection. Protected areas can benefit from appropriate management of surrounding areas and from connectivity to other protected or partially protected habitat. Eradicating invasive species can benefit multiple imperiled species—although fencing and monitoring entail long-term costs, contributing to conservation reliance. This chapter provides examples, especially from oceanic islands. Managing fire regimes, either by controlling or setting fires, is another way to improve habitat and benefit multiple species. There are trade-offs in both cost and effectiveness between single- and multi-species management.
Recognition of the existence and extent of conservation reliance in laws, regulations, and prioritization schemes has been slow to emerge. Mike Scott and Dale Goble put forth the concept based on their experiences with management and legal approaches, respectively. Recognizing conservation reliance will improve trust and support for conservation projects across a broad segment of society.