Abstract
With climate, biodiversity and inequity crises squarely upon us, never has there been a more pressing time to rethink how we conceptualize, understand and manage our relationship with Earth's biodiversity. Here, we describe governance principles of 17 Indigenous Nations from the Northwest Coast of North America used to understand and steward relationships among all components of nature, including humans. We then chart the colonial origins of biodiversity science and use the complex case of sea otter recovery to illuminate how ancestral governance principles can be mobilized to characterize, manage and restore biodiversity in more inclusive, integrative and equitable ways. To enhance environmental sustainability, resilience and social justice amid today's crises, we need to broaden who benefits from and participates in the sciences of biodiversity by expanding the values and methodologies that shape such initiatives. In practice, biodiversity conservation and natural resource management need to shift from centralized, siloed approaches to those that can accommodate plurality in values, objectives, governance systems, legal traditions and ways of knowing. In doing so, developing solutions to our planetary crises becomes a shared responsibility.
This article is part of the theme issue ‘Detecting and attributing the causes of biodiversity change: needs, gaps and solutions’.
Keywords: biodiversity, equity, environmental justice, governance, sea otters, kelp forest
According to the theory of tsawalk (one), any planetary stage of crisis must, by definition, be a shared responsibility, a shared experience … To this day, responsibility for the planet has not been shared. Umeek Richard Atleo, 2011 [1, pp. 57–58].
1. Introduction
The sciences face a reckoning in this moment of time defined by a rapidly changing climate, accelerating exploitation of Earth's biosphere, and increasing recognition of the role science plays in generating and institutionalizing inequity among people [2]. As a society, we are grappling with the systems of power that shape the aims, impacts and beneficiaries of the sciences tackling these global crises [3–5]. Consequently, the links between biodiversity, environmental change, equity and justice have come into sharp focus in local to global policy dialogues and scientific initiatives aiming to support them. At the heart of these introspections are questions surrounding the worldviews and associated values that motivate science, influence environmental decision making, and ultimately, determine who benefits and how.
Values are individually and collectively held evaluative beliefs that inform preferences for different states of being, ways of understanding and courses of action [6]. Values underlie governance principles, laws, policies and management actions. Values also shape the direction, funding and motivations for scientific inquiry and influence if and how basic science principles are adopted, applied and enshrined in institutions and practices. Yet, values are often unstated, unrecognized, assumed or overlooked. For example, the sciences that seek to quantify and understand biodiversity tend to be predicated on Eurocentric values, voices, and knowledge systems where people are considered external disruptors to and beneficiaries of biodiversity, rather than prominent components of it. Moreover, the management of biodiversity on land and in the sea tends to reflect individualistic and instrumentalist values such that populations of non-human species are termed ‘stocks’ or ‘natural resources’ available primarily for exploitation. Consequently, Western definitions and views of biodiversity hold fundamental assumptions that are largely unrecognized and thus unchallenged. While contemporary biodiversity science, laws, governance structures and management actions have an important role to play in environmental and species-at-risk decision-making, they tend to centre values that are aligned with neoliberal and colonial systems of power [7] and are thereby focused on a narrow set of policy objectives serving a narrow set of interests.
The need to broaden the values that inform contemporary biodiversity science and management is pressing, as is the need to widen our consideration of social–ecological relationships and baselines that are generally considered normative or widely agreed-upon. Millennia of reciprocal interactions between people and place throughout the Holocene have informed values that shape Indigenous governance principles, systems and management innovations, developed and honed over the long-term. In many cases these governance principles and systems consider humans as integral to ecosystems [8], and as such, see people as having a valuable role to play in enhancing biodiversity and the sustainability and resilience of societies [9,10].
In this essay, we begin by describing shared governance principles of 17 First Nations along the Pacific Coast of North America, developed since time immemorial to understand, describe and manage relationships among all components of nature, including humans. Principles are explicit expressions of values, in this case those that shape knowledge systems, laws and management practices. Next, we trace the relatively brief 250-year history of biodiversity science, the extractive value systems that shaped its origins, and how it has become institutionalized in some management applications and omitted from others. We then use the example of Canada's Pacific kelp forests and the recovery of a once endangered keystone predator, kuu (Xaayda Kil), K̓ʷak̓ʷaƛ (nuučaan̓uł), q̓asá (Haíɫzaqv), Enhydra lutris (Latin binomial), henceforth sea otters, to being to advance and understanding of how Indigenous values, governance principles, and laws can be used in practice to characterize, monitor and manage biodiversity change broadly in more inclusive, integrative, and equitable ways.
(a) . Positionality
We are a collective of hereditary leaders, Indigenous knowledge-holders, researchers, practitioners and artists applying Indigenous and Western knowledge and methodologies to inform conservation policies and governance arrangements that better reflect the social-ecological interactions and diverse values held by people along the Northwest Coast of North America. Collectively, we address interrelated questions on species recovery, fisheries management and food security amid climate uncertainty, and the negotiation of reconciliation between Indigenous and colonial governments. The Indigenous knowledge-holders among us represent hereditary leaders of the nuučaan̓uł (anglicized to Nuu-chah-nulth), Haíɫzaqv (anglicized to Heiltsuk) and Xaayda (anglicized to Haida) Nations, original and contemporary sovereign governments in this region responsible for managing the relationships between people, lands and waters prior to the incursion of settler-colonial laws and actively reclaiming that authority today. The researchers among us represent diverse disciplines, from marine ecology and fisheries science to anthropology and political ecology, each reflecting a distinct epistemology. All of us recognize the privilege and responsibility we hold in society broadly and in environmental decision-making specifically. Our diverse group of authors reflect a growing momentum to make biodiversity research and its application more inclusive and equitable than its historical origins, more prominent in contemporary natural resource management, and reflective of millennia of wisdom gained through long-term relationship with the natural world. The following essay reflects our shared experiences of engaging with and centering Indigenous governance principles, and the values they embody, within the context of our place-based research partnerships.
2. Indigenous values, governance principles and laws of the Northwest Coast
In the context of today's global crisis, an examination of the ancient nuučaan̓uł way of life may have something useful to contribute. - Umeek Richard Atleo, 2011 [1, pp. 5–6]
Contemporary challenges of climate disturbance, environmental change, equity, and justice are daunting in their enormity and relatedness, yet they are by no means new. Although their magnitude is unprecedented, Indigenous communities around the world have a long history of responding to extreme climatic events, ecological change and socio-political disruptions [11]. These perturbations to reciprocal relationships between people and place have spurred the development of governance systems and management practices that have supported social-ecological resilience and biodiversity over millennia [12–15]. The values-based principles upon which these governance systems are grounded provide a lens through which to reconsider, rethink and reframe how we approach, define and conduct biodiversity science, conservation and management.
For more than 12 000 years, human societies have been shaping and sustaining diverse landscapes and seascapes across Earth's ecosystems [8,16–18]. In fact, the most biodiverse areas on the planet, often characterized as ‘natural’, ‘intact’ and ‘wild’, are those that have long histories of use and stewardship by Indigenous people [18–20]. This is in part because people have been performing vital ecological functions for millennia, transporting seeds and animals to ensure viable populations [21,22], applying controlled fire to promote biodiversity and landscape heterogeneity [23,24], and terracing and tilling sediment to boost plant and animal production [25], all amid major biophysical disturbances.
Evidence of this abounds along the Northwest Coast of North America. For example, ancient stories and archaeological data reveal that people living along stretches of the Northwest Coast during the Holocene experienced and responded to dramatic sea level rise, at times more than half a metre over the course of one generation [26,27]. At the same time, people were actively cultivating, managing and caring for plants [28] and marine life [29,30]. For example, continued plant translocations and cultivation created biologically diverse and productive ancient forest gardens [20]. Similarly, the construction of intertidal rock-walled terraces created clam gardens known to double clam production [31]. These intertidal innovations required re-engineering to adapt to changing sea-levels [32]. Size and sex selective fishing practices for Pacific salmon, enacted at river mouths with wooden weir and stone trap technologies, sustained salmon productivity and resilience to climatic disturbances for thousands of years [33,34]. Foundational to these Northwest Coast innovations are governance systems and principles that embody explicit values. Governance systems are devised and refined by groups of people over time. As such, they reflect and are grounded in values, that in turn shape beliefs, practices and principles used often or deemed important by those people. Indigenous governance systems of the Northwest Coast centre around principles, laws, protocols and management practices that value the relationships among all forms of life in the natural (humans, plants, animals) and spiritual (ancestors, supernatural beings) worlds, all of which are viewed as kin with distinct roles, rights and responsibilities [1]. In a wide range of ways, these governance systems are acutely attuned to what Western science has come to understand as ‘biodiversity’, and they have been for millennia. Yet Indigenous governance systems permeate all aspects of society: environmental, social, political, economic, constitutional and philosophical [1]. Consequently, they reflect and attend to complexities of biodiversity, including humans as prominent components, and issues of equity and justice simultaneously.
Northwest Coast Nations share similar values that inform governance principles and laws, though each Nation has unique legal and political orders that guide relationships with all life forms in their territories including the management of those relationships by people (table 1; electronic supplementary material, video S1). For Xaayda, these are referred to as Xaayda Kil Yahdas, for nuučaan̓uł Nations they are ḥawiłmis, and for Haíɫzaqv they are Ǧvı̓ḷás, laws of the ancestors. These governance principles and laws (and the societal values they reflect), including respect, responsibility, reciprocity, making things right, interconnectedness, balance, stewardship and seeking wise counsel, among others, are consistent across these coastal Nations. Yet, each Nation has a unique expression of each governance principle in practice (table 1).
Table 1.
governance principles | X̱aayda Kil Yahdas - Haida Laws | nuučaan̓uł ḥawiłmis - Nuu-chah-nulth Laws | Ǧvı̓ḷás - Heiltsuk Laws (laws of the ancestors) |
---|---|---|---|
respect | Yahguudang—all acts must be done with respect. We respect each other and all living thingsa | ʔiisaak—greater respect. Understanding and accepting differencesb | Xáɫa—all life has equal value. We acknowledge and respect that all plants and animals have a life forcec,d |
responsibility | ’Laa guu ga kanhllns—we accept the responsibility to manage and care for the land and sea togethera | maamums—your role and responsibilities that match your standing within each Nation. Ex: hereditary leaders have responsibility as caretakers of the land | Sála—to be in control of your actions. Intelligent behavior to strive for. Thinking of the consequences before you do somethingc,e |
reciprocity | Isda ad diigii isda—giving and receiving. Reciprocity is an essential practice for interactions with each other and the natural and spiritual worldsa | hu?aa yii?ap—giving back. Giving and taking | giving back goodness receivedc |
make things right/ accountability | Tll'yahda—make it/things right. If an act is not done with respect or consent, you must make it right | caacim ‘high up’—make things right. Make things healthy | H̓aíkḷá—to make things right when needed. To make amendsc |
interconnectedness | Gina ‘waadluxan gud ad kwaagid—everything depends on everything elsea. All things are connected | hišukʔiš c̓awaak—everything is one, everything is interconnectedb | we are all one and our lives are interconnected. Our relationship with our territory is fundamental and we regard it as an extension of ourselvesd |
balance | Giid tlljuus—the world is as sharp as the edge of a knife. Balance is needed in our interactions with the natural worlda | qwaa?aqλin tiičmis—life in balance | Nuáqi—one's thoughts. Balance of mind, body, emotions and spiritc |
stewardship, to take care | TllXanda | ʔuuʔaałuk—taking care of. Caring and working for next generationsb | cĺísĺá to take care of; h̓íkila—to take good care of somethingc. We are steward of the land and sea from which we live, knowing that our health as a people and our society is intricately tied to the health of land and watersd |
seeking advice and counsel and sharing knowledge | Gina k'aadang.nga gii uu tll k'anguudang—seeking wise council. Xaayda elders teach about traditional ways and how to work in harmony with the natural worlda | ḥaaḥuupst̓ał—sharing teachings or teaching each other. For teachings to live on they must be taught and re-taughtb | Tq̓ílá—give advice on what to do and how things should bec |
land, ocean and people for which a hereditary chief has responsibility and authority to caretake | Tllgaay or Tllga | ḥaḥuułi—a Leader's territory which includes ocean, lands, and people for which they have responsibility to caretakeb | ɫáxvái—authority that underpins ǧvı̓ḷás and the strength received from enacting ǧvı̓ḷás |
aHlG̱aagilda X̱aayda Kil Ḵ’aalang Skidegate Haida Immersion Program X̱aayda Kil Glossary. 2021; Council of the Haida Nation and Government of Canada. 2018. Guiding principles from the Gwaii Haanas Gina ‘Waadlux̱an KilG̱uhlG̱a Land-Sea-People Management Plan.
cHeiltsuk Tribal Council. 2018. Dáduqvḷá qṇtxv Ǧvı̓ḷásax̌: To look at our traditional laws. Decision of the Heiltsuk (Haíɫzaqv) Dáduqvḷá Committee regarding the October 13, 2016, Nathan E.Stewart Spill [37].
dBrown F, Brown YK. 2009. Staying the course, staying alive. Coastal First Nations fundamental truths: biodiversity, stewardship and sustainability [34].
eReid, C 1988. Heiltsuk (Haíɫzaqv) Cultural Education Center.
Indigenous governance principles and laws are enacted and witnessed in public settings, and their persistence is recounted and preserved in oral histories, narratives and stories [38] (electronic supplementary material, video S1). While such established accounts act as accessible forms of public memory, they are also forms of legal precedent that can be drawn on to legitimately resolve issues in decentralized legal orders and specify management protocols (electronic supplementary material, video S2). Many laws and principles are often embedded in and learned about through stories because Indigenous laws themselves are interconnected and inseparable (figure 1; electronic supplementary material, video S3). While Indigenous oral histories are now recognized as evidence in Canadian courts, they have yet to make their way into judicial reasoning or written in Canadian jurisprudence [38]. Yet momentum is growing to revitalize Indigenous laws and the governance systems in which they are embedded, apply them to pressing biodiversity and environmental issues, and effect change [37,39].
Opportunity exists to learn from and apply these governance principles in the application of biodiversity and conservation science and environmental management. For example, we have the opportunity to: (i) Tll'yahda (make things right in Xaayda)—acknowledge historical injustices, overexploitation and past management mistakes, and aim to correct them; (ii) incorporate hišukʔiš c̓awaak (interconnectedness in nuučaan̓uł)—by considering species interactions, including humans, historical baselines and intergenerational thinking in our study and management of ecosystems; (iii) Xáɫa—(respect in Haíɫzaqv) respectfully consider the needs, objectives and rights of diverse species and sectors of society and our maamums (responsibility in nuučaan̓uł) to uphold them; and (iv) Gina k'aadang.nga gii uu tll k'anguudang (seek wise counsel in Xaayda)—inform decisions based on the best available information from diverse knowledge systems.
3. A reckoning of values underlying the colonial history of biodiversity science
For biodiversity researchers and practitioners to learn from and apply Indigenous governance principles today, we first must Tll'yahda—acknowledge the history of biodiversity science as an enabler of both colonial expansion and industrial exploitation of natural resources. The sciences of taxonomy, biodiversity and ecology that developed in the eighteenth and nineteenth centuries facilitated the expansion of European colonization of the globe by identifying and cataloguing natural resources (e.g. crops, wildlife, commodities and medicines) and associated knowledge systems of Indigenous people that could also be exploited, exported and used to support empires abroad [40–43]. Scientists look upon this era as one of discovery, scientific inquiry and enlightenment, often without recognizing colonial principles that motivated sciences of the era, and the indispensable and conscious role of naturalists in colonial expansion [42,44–47]. Yet institutions ranging from the Catholic Church to the Royal Society of London and the British Admiralty understood the value of biodiversity science as fundamental to the establishment and success of colonies. Naturalists' exploration and extraction of knowledge from Indigenous peoples abroad fuelled an era of bioprospecting and colonization legitimized by the now-discredited notion of Terra Nullius (nobody's land), and the Doctrine of Discovery that were used by Europeans to justify the exploitation and theft of land, Indigenous knowledge and natural resources. In this fashion, pioneers of biodiversity science (e.g. Joseph Banks, Hans Sloane, Alexander von Humboldt, Charles Darwin) and numerous others were instrumental in using nascent sciences of biodiversity for the successful establishment or expansion of colonies in the Americas, Australia, New Zealand and many islands in the Pacific [48–51]. Centuries after this era of colonization, biodiversity research as a colonial practice continues to manifest today in the form of, for example, ‘helicopter science’ [52,53], bioprospecting for extractive industries [54], and research that ignores Indigenous knowledge, intellectual property, and the governance systems in which that knowledge is embedded [55].
While early biodiversity research was used to identify diverse natural resources and knowledge systems that might be exploited, modern natural resource management has historically ignored biodiversity [56,57]. Management approaches in the twentieth century generally omitted both how biodiversity affects resources of interest and how resource exploitation affects biodiversity upon which human communities and other ecosystem constituents depend. Instead, Western resource management historically focused on compartmentalized goals for individual species or species assemblages rather than stewardship of complex ecosystems [58,59]. As a result, many of the scientific models, practices, agencies, laws and technologies used to manage complex systems like fisheries, agriculture, or recovery of endangered species have, until recently, focused on single species objectives. Species interacting within diverse assemblages and complex ecosystems became managed in isolation by centralized and siloed institutions that were geographically removed from the complex systems they were mandated to manage [5,60,61]. Western management driven by values such as efficiency, reductionism, and accumulation of wealth (i.e. maximization of economic rent), and the sciences that support it, are in opposition to, and often at the expense of, the Indigenous values expressed as governance principles such as respect, interconnectedness, balance, and responsibility.
While calls and mandates for ecosystem-based management from Western institutions are decades old [62,63], substantial inertia in the legal doctrines, institutional structures and scientific ‘best practices’ used in fisheries, wildlife, ocean, and landscape management, have precluded their uptake and application [5,64]. In the oceans, it was not until the notable collapse of several of the world's dominant fisheries and degradation of marine ecosystems that high level international advisory panels formed [65,66] and biodiversity science and objectives (in terms of ecosystems, populations, genetic, geographical and even human community diversity) would begin to be applied to marine fisheries in a substantive way.
Since the late 1990s, there have been significant efforts to move towards ecosystem-based management and apply frameworks that aim to incorporate biodiversity in decision-making. Yet, many of these efforts are still predicated largely on ‘stock and flow’ models and economic objectives. For example, the ecosystem services and natural capital approaches often fail to account for reciprocal interactions among various components of ecosystems and contrasting objectives among diverse communities of people, and thereby neglect issues of equity and justice among beneficiaries of said ‘services’ [67–74]. Science, management, and conservation practices are often motivated by a constrained set of Western values; these then continue to perpetuate the process of colonization and undermine the responsibilities of Indigenous peoples to manage their relationship with the land and sea in accordance with their ancestral governance principles. Moreover, these practices ignore broader issues of equity, access and values of both Indigenous and settler societies. This is notably evident in the case of the recovery of sea otters along the Northwest Coast of North America.
4. The complex case of sea otter recovery
Evidence of continuous human coexistence with sea otters following the arrival of maritime people to the Americas exists throughout the Holocene in oral histories and the archaeological record [75–77]. Highly valued, hunted, controlled and traded by Indigenous people for at least 12 000 years, it was not until nearly 200 years ago that sea otters were extirpated from the northeast Pacific by the international maritime trade in sea otter fur. Beginning in earnest by the 1750s in Alaska and the 1780s in British Columbia, the commercial trade in sea otter pelts and bioprospecting of the eighteenth and ninteenth centuries led to the introduction of a Western cash economy and the imposition of colonial settlement and laws. This eroded First Nations economies and governance structures that had been in place for millennia. These structures included well established trade networks, spatially explicit marine tenures, and complex traditional resource management protocols and governance principles designed to ensure sustainability [1,13,34,78]. The commercial trade and extirpation of sea otters from the Northwest Coast contributed to the transformation of Indigenous societies and triggered a social-ecological regime shift across much of the northern Pacific Rim [79]. Consequently, the recent recovery of sea otters and their continued range expansions create both challenges and opportunities to reconsider how biodiversity is understood, studied and managed in near shore ecosystems.
(a) . Challenges
As a keystone predator, sea otters can dramatically alter near shore biodiversity, ecosystem structure, primary production and the availability of resources upon which people and other organisms depend [80,81]. On rocky shores, sea otters effectively limit the densities and sizes of herbivorous sea urchins among other macroinvertebrate prey. The loss of sea otters from rocky reef ecosystems can therefore lead to increased urchin grazing and reduction in kelp forests [82,83], while recovery of sea otters has facilitated restoration of diverse assemblages of kelp and other algae [84] which provide shelter, habitat and food for many species of invertebrates and fishes [85,86]. In soft sediment habitats, the physical disturbance associated with sea otter foraging for bivalves and crabs, for example, significantly reduces densities and size of these food sources, but the associated physical disturbance can also increase genetic diversity of seagrass beds or alter food web interactions so as to increase seagrass abundance [87–91].
In one sense, the recovery of this once endangered keystone predator is a remarkable conservation success story, owing in large part to international and national policies that stopped the commercial exploitation and trade of sea otters and protected them from all hunting. Yet when contrasted against historical baselines where sea otter hunting and shellfish harvest were sustained by people over millennia and when viewed through the lens of social justice and food sovereignty today, it becomes an example of a policy failure that has imposed severe inequities among coastal communities. For place-based Indigenous communities, many shellfish species that are consumed by sea otters, as well as fishes that benefit from their indirect effects on kelp habitat, are essential sources of food, micronutrients, medicine, livelihoods, social practices and cultural identity [92]. Prior to the maritime fur trade, Indigenous communities had governance and management protocols in place that secured both the persistence of sea otters and human access to shellfish for food, tools, and trade. Today in Canada, Indigenous peoples have a constitutionally protected right to access shellfish for food, social and ceremonial purposes, but they are not permitted to hunt or scare sea otters as they once did, with the explicit purpose of protecting key shellfish areas. As a result, after decades of sea otter recovery, there are now long stretches of coastline where certain shellfish populations have become so depleted that community members can no longer harvest shellfish locally [93]. Sea otter recovery and range expansion in the Pacific Northwest has therefore introduced significant governance, management, legal and ethical challenges regarding biodiversity [94].
Federal laws, institutions, and scientists in both the United States and Canada are ill-equipped to handle the social, economic and ecological trade-offs associated with the vast direct and indirect ecosystem-wide consequences of unchecked sea otter recovery. Instead, both countries have independent management agencies, laws and paradigms for fisheries, species at risk, and their habitats. As a result, modern management of sea otter recovery in Canada and the United States occurs largely in isolation of fisheries, justice, health and Indigenous sovereignty considerations. Yet, a management decision in any one space, or set of spaces, regarding sea otter recovery, near shore fisheries and Indigenous access rights, affects the others.
(b) . Opportunities
New, spatially nuanced knowledge of sea otter interactions has widened the operating space in which to re-envision how society might meet competing social-ecological objectives associated with the recovery of this keystone species. Studies of sea otter movements and spatial ecology have demonstrated that sea otter populations are structured at small spatial scales [95], and thus regional abundance and distribution is better understood as a mosaic of semi-discrete, localized populations whose density can vary greatly [96,97]. Local scale variation in sea otter abundance, and the strength of their top-down influences, can allow for the emergence of spatial mosaics of kelp and urchin dominated reefs. In some locations, this pattern of contrasting reef habitats, combined with the tendency of individual sea otters to exhibit specialized diets [98,99], leads to increased foraging by otters on energy-rich urchins along the margins of kelp forests and urchin barrens, thereby enhancing the resistance of remnant kelp forests to overgrazing by sea urchins [100]. Moreover, in places where sea otter occupancy is low owing to both hunting by people and the perceived risk of hunting, shellfish prey can recover [101]. Critically, these contemporary findings mirror those found in the archaeological record in multiple areas of the Northwest Coast.
Data from coastal archaeological sites suggests that for much of the mid to late Holocene, sea otters were rare or absent from stretches of coastline where people gathered shellfish. This suggests that spatial mosaics of sea otter presence and absence, and their ensuing indirect effects on kelp habitat, were also a feature of the past coastlines [102]. This spatial patterning may have been one mechanism by which humans and sea otters coexisted for millennia, each prominent predator having its own spatial domain. The revitalization of Indigenous sea otter hunting practices and governance authority to spatially manage the relationships between people, sea otters, shellfish and kelp can enable sea otter and human coexistence again today [92]. Collectively, these lines of evidence highlight the critical consequences of spatially explicit sea otter foraging behaviour, and the prominent role humans played historically, and can play again today, in this complex set of relationships. Importantly, they also chart an established path forward to the possibility of human-sea otter coexistence and regional stability of kelp and shellfish-dominated reef mosaics amid disturbances, like extreme climatic events and disease epidemics.
To confront the complex challenges associated with sea otter recovery, it is essential to equip coastal communities and management institutions with shared and current knowledge, alternative ecosystem-based management strategies and equitable governance structures to navigate the social-ecological regime shifts triggered by the recovery of this keystone predator. The case of sea otter recovery, emblematic of natural resource management issues more broadly, demands innovative models of shared governance based on clear and comprehensive recognition of peoples' values and objectives both in the research process and its application to management. Below we offer an example of how one might apply Indigenous values, governance principles and ancient laws to characterize, monitor and manage biodiversity change associated with sea otter recovery in more inclusive, integrative and equitable ways.
5. An Indigenous governance approach to sea otter recovery
Here, our collective understanding of how Haíɫzaqv, nuučaan̓uł and Xaayda governance principles apply to management of sea otter recovery in these Nations’ territories has come through transdisciplinary workshops, listening circles, in-person meetings, online dialogues and decades of research among the authors and other Indigenous scholars, hereditary leaders, and Indigenous knowledge holders. The following discussion reflects our shared experiences of engaging with and centring these governance principles within the context of our place-based, enduring, and evolving research partnerships. We recognize however that our discussion of these governance principles is in its infancy and fails to capture many aspects (e.g. the spiritual and supernatural) that are central to Indigenous ways of knowing and being. We also recognize that these governance principles and our understanding of how they may be applied are embedded in and are inseparable from Haíɫzaqv, nuučaan̓uł and Xaayda worldviews and territories.
(a) . Making things right
Among Haíɫzaqv, nuučaan̓uł, and Xaayda Nations, the mechanism by which people are held accountable for their actions is specified through the law of ‘making things right.’ If an act is done without respect or consent among Xaaydas, one must Tll'yahda (make things right) [103]. This includes publicly acknowledging what was done that was wrong and reaching consensus on how to make it right. Similarly, among the Haíɫzaqv, one must H̓aíkḷá (make amends) if one blunders [37]. This same principle of accountability is captured by the word caacim in nuučaan̓uł, which means to ‘make things right’ and ‘make things healthy’.
In the context of sea otter recovery, and natural resource management more broadly, applying the principle of ‘making things right’ means researchers, managers, and policy makers must acknowledge past transgressions and take actions to correct them. ‘Making things right’ when it comes to sea otter research and its application, means acknowledging the original colonial laws and international industrial-scale trade leading to regional sea otter extirpation. To ‘make things right’ we must acknowledge colonial economic drivers of their population collapse and consider values of nature other than those rooted in capitalism. One way we, the authorship team, have sought to do this is by publishing research that describes the role of colonialism, neoliberalism and capitalism in environmental governance [5].
‘Making things right’ also means acknowledging the colonial dispossession of Indigenous lands and waters, attempted erasure of Indigenous stewardship practices, and erosion of Indigenous governance authority. Canada's Indian Act still gives the federal government sweeping powers with regards to First Nations membership, political structures, governance, education and cultural practices. To make progress towards ‘making things right’, all aspects of society, including biodiversity and natural resource research initiatives engaging at the science policy interface, must respect Indigenous sovereignty. Within our research partnerships, we have done this by seeking ʕapaak (free, prior and informed consent in nuučaan̓uł) throughout our research process from decision-making bodies identified by communities. In the case of sea otters specifically, ‘making things right’ also means supporting the revitalization of cultural practices and Indigenous-led stewardship initiatives like sea otter hunting for the purpose of maintaining shellfish harvesting sites [92] and the revitalization of sea gardens to increase the production of shellfish and seaweed, and access to fish [30].
‘Making things right’ also means acknowledging the outcomes of state management systems and current federal laws that fail to account for shifting baselines [104], ecosystem interactions, spatial variation in species recovery and dynamics [105] and Indigenous management objectives [5,74]. For example, a lack of monitoring and export-oriented fisheries policies in the twentieth century enabled and failed to act quickly enough to halt the commercial overexploitation and collapse of northern abalone. It remains listed as ‘endangered’ under Canada's Species at Risk Act today. This conservation status, owing to declines that happened under federal management, restricts harvest of this culturally important food by people [106]. Moreover, abalone are managed in isolation of one of its major predators, the recovering sea otter, which is listed as a ‘species of special concern’. Hunting sea otters in Canada for the purpose of protecting shellfish like abalone is currently prohibited.
(b) . Interconnectedness
The principle of interconnectedness within the natural world is shared among these Nations. This is captured by hišukʔiš c̓awaak in nuučaan̓uł, meaning everything is one, everything is interconnected [1] and Gina ‘waadluxan gud ad kwaagid in Xaayda, meaning everything depends on everything else [103]. The Haíɫzaqv describe their connection to nature as a fundamental truth such that their relationship with their territory is regarded as an extension of themselves [34]. For research and policy related to sea otters, the application of ‘interconnectedness’ means incorporating species interactions, including humans, in our understanding of species recovery and conservation targets. It also means supporting connections among generations, past, present and future, like supporting intergenerational knowledge transfer of ancestral stewardship practices through culture camps, engaging with local schools and initiatives that support emerging Indigenous stewards. Through our research partnerships, we connect generations of all species by integrating archaeological data, Indigenous knowledge and quantitative ecological and social analyses to broaden our understanding of social-ecological dynamics operating on temporal and spatial scales that are impossible to study in real-time.
In the context of biodiversity science and natural resource management more broadly, applying the principle of ‘interconnectedness’ demands systems thinking. It requires disrupting the culture of reductionism that propelled twentieth century science [107]. For socially relevant research to have meaningful outcomes, the disconnect between science as the producer of knowledge and society as the passive recipient of knowledge will need to be replaced by processes that support the co-design, co-production and co-delivery of knowledge.
(c) . Balance and reciprocity
Balance and reciprocity are foundational values and governance principles that guide how the relationships among people, lands and waters are managed. For the Xaayda, Giid tlljuus (balance) is needed in our interactions with the natural world as is Isda ad diigii isda (giving and receiving) [103]. Specifically, care must be taken to avoid reaching a point of no return and active restoration should be used to restore balance where it has been lost [108]. These same concepts are held by the nuučaan̓uł as qʷaaʔaqƛin tiičmis meaning life in balance (wiicuckum Anne Mack 2022, personal communication) and hu?aa yii?ap [35]. Ǧvı̓ḷás of the Haíɫzaqv specifies the law of Nuáqi, meaning balance of mind, body, emotions and spirit, and the act of ‘giving back goodness received’. Both are foundational principles that are needed to sustain interactions among people and the natural world [37].
With respect to sea otter recovery and natural resource management, the governance principles of ‘balance’ and ‘reciprocity’ means articulating and considering the trade-offs among competing species, management objectives and people's viewpoints given the existence of predator–prey interactions, competition among species for shared resources and differences in people's interests. This translates into managing the relationships between species like sea otters, endangered abalone, kelp and people as a collective of interactions rather than on a species-by-species basis. It means restoring the role of humans in coastal food webs as these relationships endured for much of the Holocene. In our research, we explicitly invoke balance and reciprocity by experimenting with and deciphering prevailing ecosystem interactions and accounting for multiple objectives that reflect diverse values rather than the dominant ones. We are also transparent about who benefits from which trade-offs. For example, increased livelihoods associated with sea otter recovery, like jobs from tourism and commercial finfish fisheries [86], do not compensate for lost shellfish food security and food sovereignty among subsistence-based communities [92].
In natural resource management, the practice of ‘reciprocity’ or ‘giving back goodness received’ implies active and intentional stewardship and restoration of lands and waters by people. In terrestrial systems this may include the cultivation of productive berry forests, camas fields and estuarine root gardens via intentional burning and weeding [25]. In coastal marine ecosystems it could include the restoration or creation of clam gardens by terracing and tilling intertidal soft sediment habitat, enriching sediment conditions with crushed shell, and transplanting clams, sea urchins and other species [30]. These examples and the principle of reciprocity are tightly connected to ‘stewardship’ or ‘taking care of’ (table 1; figure 1; electronic supplementary material, video S2).
(d) . Respect and responsibility
Respect and responsibility are foundational governance principles for the Haíɫzaqv, nuučaan̓uł and Xaayda Nations, each with their own word and nuanced meaning. For the Xaayda, Yahguudang (respect) is expected to be given to all people and all living things [103]. In practice, it means always asking for permisson first, harvesting only what is needed, giving thanks to that which is taken and received, and acknowledging those who behave accordingly. It also includes transparency in discussion and actions. To the Haíɫzaqv, Xáɫa acknowledges that all life has equal value and a life force that must be acknowledged and respected [34,37]. The word ʔiisaak, meaning respect among nuučaan̓uł Nations, is practised by respecting all begins as well as the Hawiih's (hereditary leader's) role in the management of their ḥaḥuułi (territory), by being community oriented, and understanding and accepting differences [1,35]. Similarly, the Xaayda must Laa guu ga kanhll; accept the responsibility to manage and care for the land and sea often in collaboration with others [109]. Among the nuučaan̓uł maamums describes one's role and responsibility within the Nation that match your standing. For example, hereditary leaders have responsibility as caretakers of the land.
‘We both have the right to food.’ – Kii'iljuus Barbara Wilson, St'awaas Xaaydaga, 2013
Because sea otters are valued and respected as kin under nuučaan̓uł, Xaayda and Haíɫzaqv laws, they like people, hold rights to space and food. Therefore, when it comes to sea otter recovery, the laws of ‘respect’ and ‘responsibility’ in practice translate into ensuring that both people and sea otters have access to enough habitat and food to sustain themselves in perpetuity. Practically, this means not only excluding sea otter from specific shellfish harvesting sites for people via hunting and creating a seascape of fear, but it also means identifying areas where sea otter populations can have free access to a reliable source of food and thrive. The laws of ‘making things right’ and keeping ‘balance’ requires that we enable the co-existence of people and sea otters by intentionally delineating spaces and clear boundaries where both can thrive. Among the Tlingit and Xaayda of Southeast Alaska, sea otters had their own areas ‘on the outside waters' and boundaries between outside and inshore areas were maintained [110].
‘A young man going out to hunt and he looks over, and he says to the [sea] otter bobbing, he says, ‘You better go out to the outside waters, or you are gonna end up as a headman's…headman's headdress!’ … There was an understanding between the Otter People and the people that inhabited an area and they saw them and they talked to them. … We had Otter people. We had Wolf people. Eagle People. We had Raven people. The spirit of all these creatures, the Killer Whale People, there was always an understanding between the people and the other people. And they held their boundaries.’ – Deborah Head, Tlingit, Sháan Séet Craig, Alaska [110, p. 184]
These ancestral laws and practices have been successfully enacted in Sitka, Alaska today, where the localized reduction of sea otters by 70% via hunting and its associated risk caused an increase in sea urchins and decline in kelp that matches the spatial pattern of otter occupancy [101]. The result is a regional spatial mosaic of patches, some dominated by kelp and sea otters, others dominated by sea urchin, a spatial pattern in habitat types that probably existed on the coast for thousands of years [102]. These management practices would have led to habitat diversity that could have buffered the effects of disturbances like extreme climatic events or disease epidemics, thereby enabling productive and resilient social-ecological systems for millennia.
(e) . Seeking wise counsel
Finally, these coastal Nations also share the governance principle of upholding and sharing knowledge. Gina k'aadang.nga gii uu tll k'anguudang means seeking wise counsel among the Xaayda [103]. Through the millennia, elders taught the youth about traditional ways and how to work in harmony with the natural world. In practice today, we employ this principle by working with traditional knowledge and scientific information so that communities can respond to change while upholding culture, values and laws [109]. Among the Haíɫzaqv, Tq̓ílá is to give advice on what to do and how things should be [37].
6. Looking forward
With a rapidly changing climate and rampant loss of biodiversity across the planet, there remains substantial debate about how to quantify, understand, manage and conserve biodiversity in the face of numerous threats [71,72]. The governance principles described above for 17 coastal First Nations have historically been excluded from the applied sciences and management associated with biodiversity. We advocate for an alternative approach: broadening who benefits from and participates in sciences of biodiversity by diversifying the values underlying such work. Recently, calls in the biodiversity research and conservation world have been made to shift from or expand current frameworks and practices to include a far more broad and equitable view of what constitutes nature's contributions and who those contributions benefit [72]. In the case of the First Nations represented here, this may occur by centring communities and their expression of values embodied in governance principles at the heart of biodiversity research, conservation and management. These governance principles and the values they reflect are shared by a broader cross section of communities globally, and their formal adoption into biodiversity research and its applications may present a pathway towards more equitable and just science and management practices and outcomes. Yet how does such a shift in principles and values that motivate science and management occur in practice? Solutions, we think, require pluralism in worldviews, scientific methodologies [111], environmental governance [112] and legal systems [37,39,113–115].
No approach for detecting and attributing causes of change in biodiversity can claim independence of human values nor perspectives. Rather, what is measured, how, by whom, and for what purpose not only affects the research but also its outcomes and its applications. The history of Western biodiversity science, and indeed its present practice, remains rooted in colonialism and exploitation. Indigenous and place-based peoples bring deep time knowledge of natural history, phenology, ecosystem connections, dynamic historical conditions and reciprocal relationships with humans. Rather than ignore such knowledge, or extract it for asymmetric gains, we advocate for a more inclusive and introspective process. Transdisciplinary research initiatives co-designed with communities, knowledge-holders and decision-makers offer a venue to engage in and learn from diverse worldviews, values, epistemologies and types of data and knowledge. Biodiversity research conducted in true collaboration with communities and in accordance with their values and/or governance principles has the potential to generate both better science and more equitable and just scientific processes and outcomes. Importantly, these approaches involve jointly framing issues and knowledge gaps, and require building relationships based on trust, mutual respect and long-term commitment. Democratizing the research process by way of knowledge co-design, co-production and co-delivery lends legitimacy to the science and knowledge that is produced, empowers local communities and decision-makers, increases societal relevance of the work, and can lead to new perspectives and discoveries [116,117]. We contend that locally rooted biodiversity and observation networks that are co-designed and co-produced from conception through implementation will be better equipped to detect and inform global biodiversity change with increased legitimacy and societal relevance. However, systems of science, knowledge and power are not easily shifted and co-production processes can reflect the institutional (colonial) settings in which they are embedded [118,119].
For biodiversity conservation and natural resource management, there is a need to move from centralized, singular approaches to those that can incorporate a plurality of values, principles and ways of knowing [120,121]. Co-management (or co-governance) is one context in which diverse values regarding biodiversity can be reconsidered. For instance, co-management arrangements (i.e. the sharing of responsibility and decision-making authority among Indigenous governments and state entities within a defined context) are often sites of knowledge ‘co-production’ and shared learning about conservation and management issues [122]. In many jurisdictions, such processes have reduced conflict because they create space for dialogue, require (often formally) inclusion of Indigenous knowledges and identification of shared interests. Still, many co-management arrangements are premised on the logics of colonialism (i.e. ministerial approval and regulatory oversight), are responding to conditions created by colonialism in the first place (e.g. dispossession of resources), and hinge on dominant forms of science (models, single-species, economic optimization) and scientific hegemony [61].
Another approach exists, in which management and science are decentralized into community-based and Indigenous-led approaches. Rather than accommodating colonial institutions, this latter approach requires, at least in part, either their deconstruction, the explicit devolution of their authorities and responsibilities and/or their willingness to accommodate pluralism in legal orders. It also requires that current colonial institutions support, fund and incentivize science, management and governance of biodiversity that is shaped by rather than extracted from Indigenous communities. Examples of legal pluralism and Indigenous resurgence [123] are currently being enacted along the Northwest Coast with the explicit purpose of protecting biodiversity [124]. For example, Indigenous protected areas [125], and their management plans, are being established based on local Indigenous legal principles and governance systems [39], as are environmental impact assessments [37]. Fortunately, there are shared principles of learning and adjusting perspectives in both science and Indigenous governance where expanded knowledge and historical depth regarding the role Indigenous peoples had in managing these systems can now be included in legal orders and policies.
Regardless of the arrangement among groups, there are many ways to accommodate diverse values and governance principles into the study, conservation and management of biodiversity. To be effective in the face of global crises, those of us working at the nexus of biodiversity science, management, and policy cannot remain agnostic to the plurality of values and ways of knowing that permeate societies around the world. We need to critically evaluate biodiversity science initiatives and the conservation and management decisions they aim to support, against all three dimensions of justice, including distributive justice—who benefits? procedural justice—who is included in the science and decision-making processes? and recognitional justice—which groups' responsibilities and rights are recognized [126]? Regardless of what systems we study, biodiversity and natural resource management science and application will benefit from a greater focus on the governance principles of respect, responsibility, reciprocity, interconnectedness, balance, stewardship, seeking wise counsel and making things right among all forms of life.
Acknowledgements
This work is dedicated to the ancestors who, over thousands of years, developed these foundational governance principles and passed them on to the next generation of stewards. Kleco to Umeek Dr Richard Atleo Sr for sharing his knowledge of nuučaan̓uł governance principles through story and reviewing earlier drafts of this manuscript. Haawa to Taalgyaa'adad Dr Betty Richardson for sharing her knowledge of Xaayda Kil Yahdas in the Xaayda language. ʔatakšiƛ ʔaʔasmucy`ak Thank you to Marge Touchie, for sharing her knowledge of nuučaan̓uł and walas ǧiáxsix̌a to Káníɫkás Desiree Lawson for sharing her knowledge of Haíɫzaqv. Huy ch q'u to Hwsyun'yun Skye Augustine for hosting our first Listening Circle in 2021 and modelling these principles in all her work and relationships. Kleco to Dawn Foxcroft and Kelly Foxcroft-Poirier for their wisdom and insightful guidance of the Coastal Voices 2022 summer gathering, where the impetus to broadly share these governance principles originated.
Contributor Information
Anne K. Salomon, Email: anne_salomon@sfu.ca.
Daniel K. Okamoto, Email: dokamoto@bio.fsu.edu.
Ethics
All required ethics approvals were acquired by A.K.S. and H.M.K. through Simon Fraser University and the First Nations participating in this work.
Data accessibility
The data are provided in the electronic supplementary material [127].
Authors' contributions
A.K.S.: conceptualization, writing—original draft, writing—review and editing; D.K.O.: conceptualization, writing—original draft, writing—review and editing; K.B.J.W.: writing—original draft, writing—review and editing; h.T.H.: writing—review and editing; W.: writing—review and editing; w.A.M.: writing—review and editing; S.H.A.D.: writing—review and editing; G.G.: writing—review and editing; W.W.H.L.H.: writing—review and editing; T.M.H.: writing—review and editing; W.C.C.: writing—review and editing; H.F.G.: writing—review and editing; n.S.C.: writing—review and editing; D.D.: writing—review and editing; H.M.K.: writing—review and editing; L.C.L.: writing—review and editing; M.T.T.: writing—review and editing; J.J.S.: writing—review and editing; D.A.: writing—review and editing; I.M.: writing—review and editing; A.M.: writing—review and editing; D.H.: writing—review and editing; E.-K.M.: writing—review and editing; E.J.G.: writing—review and editing; C.J.C.C.: writing—review and editing; A.A.: visualization, writing—review and editing.
All authors gave final approval for publication and agreed to be held accountable for the work performed therein.
Conflict of interest declaration
We declare we have no competing interests.
Funding
This collaboration was supported by the Natural Sciences and Engineering Research Council of Canada (grant no. NSERC NETGP 523374-18), the US National Science Foundation (grant no. NSF OCE grant 2023649), Social Sciences and Humanities Research Council of Canada, Pew Fellows Program in Marine Conservation, Parks Canada Conservation and Restoration Program funding and Simon Fraser University's Community Engagement Initiative.
References
- 1.Atleo ER. 2011. Principles of tsawalk: an indigenous approach to global crisis . Vancouver, Canada: UBC Press. [Google Scholar]
- 2.Graves JL Jr, Kearney M, Barabino G, Malcom S. 2022. Inequality in science and the case for a new agenda. Proc. Natl Acad. Sci. USA 119, e2117831119. ( 10.1073/pnas.2117831119) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 3.Trisos CH, Auerbach J, Katti M. 2021. Decoloniality and anti-oppressive practices for a more ethical ecology. Nat. Ecol. Evol. 5, 1205-1212. ( 10.1038/s41559-021-01460-w) [DOI] [PubMed] [Google Scholar]
- 4.Jacobs S, et al. 2020. Use your power for good: plural valuation of nature–the Oaxaca statement. Glob. Sustain. 3 e8. ( 10.1017/sus.2020.2) [DOI] [Google Scholar]
- 5.Silver JJ, et al. 2022. Fish, people, and systems of power: understanding and disrupting feedback between colonialism and fisheries science. Am. Nat. 200, 168-180. ( 10.1086/720152) [DOI] [PubMed] [Google Scholar]
- 6.Hitlin S, Piliavin JA. 2004. Values: reviving a dormant concept. Annu. Rev. Sociol. 30, 359-393. ( 10.1146/annurev.soc.30.012703.110640) [DOI] [Google Scholar]
- 7.DePuy W, Weger J, Foster K, Bonanno AM, Kumar S, Lear K, Basilio R, German L. 2021. Environmental governance: broadening ontological spaces for a more livable world. Envir. Plan. E: Nat. Space 5, 947–975. 25148486211018565. [Google Scholar]
- 8.Bliege BR, Nimmo D. 2018. Restore the lost ecological functions of people. Nat. Ecol. Evol. 2, 1050-1052. ( 10.1038/s41559-018-0576-5) [DOI] [PubMed] [Google Scholar]
- 9.Boivin N, Crowther A. 2021. Mobilizing the past to shape a better Anthropocene. Nat. Ecol. Evol. 5, 273-284. ( 10.1038/s41559-020-01361-4) [DOI] [PubMed] [Google Scholar]
- 10.Artelle KA, Stephenson J, Bragg C, Housty JA, Housty WG, Kawharu M, Turner NJ. 2018. Values-led management: the guidance of place-based values in environmental relationships of the past, present, and future. Ecol. Soc. 23, 35. ( 10.5751/ES-10357-230335) [DOI] [Google Scholar]
- 11.Atleo MR. 2022. Canadian Indigenous leadership for social justice in the face of social group apraxia: renovating the state colonization built. In Leading for equity and social justice: systemic transformation in Canadian education (eds Gelinas-Proux A, Shields CM), pp. 173-193. Toronto, Canada: University of Toronto Press. [Google Scholar]
- 12.Trosper RL. 2002. Northwest coast indigenous institutions that supported resilience and sustainability. Ecol. Econ. 41, 329-344. ( 10.1016/S0921-8009(02)00041-1) [DOI] [Google Scholar]
- 13.Trosper R. 2009. Resilience, reciprocity and ecological economics. New York, NY: Routledge. [Google Scholar]
- 14.Jackley J, Gardner L, Djunaedi AF, Salomon AK. 2016. Ancient clam gardens, traditional management portfolios, and the resilience of coupled human-ocean systems. Ecol. Soc. 21, 20. ( 10.5751/es-08747-210420) [DOI] [Google Scholar]
- 15.Lepofsky D, Salomon AK.. In press. Clam gardens across generations and places support social-ecological resilience to global change. In Climatic and ecological change in the americas: a perspective from historical ecology (eds Whitaker JA, Armstrong CG, Odonne G). London, UK: Taylor and Francis Group. [Google Scholar]
- 16.Boivin NL, Zeder MA, Fuller DQ, Crowther A, Larson G, Erlandson JM, Denham T, Petraglia MD. 2016. Ecological consequences of human niche construction: examining long-term anthropogenic shaping of global species distributions. Proc. Natl Acad. Sci. USA 113, 6388-6396. ( 10.1073/pnas.1525200113) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 17.Dick CA, Sewid-Smith D, Recalma-Clutesi K, Deur D, Turner N. 2022. ‘From the beginning of time’: the colonial reconfiguration of native habitats and Indigenous resource practices on the British Columbia Coast. Facets 7, 543-570. ( 10.1139/facets-2021-0092) [DOI] [Google Scholar]
- 18.Ellis EC, et al. 2021. People have shaped most of terrestrial nature for at least 12,000 years. Proc. Natl Acad. Sci. USA 118. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 19.Fletcher M.-S., Hamilton R, Dressler W, Palmer L. 2021. Indigenous knowledge and the shackles of wilderness. Proc. Natl Acad. Sci. USA 118, e2022218118. ( 10.1073/pnas.2022218118) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 20.Armstrong CG, Earnshaw J, McAlvay AC. 2022. Coupled archaeological and ecological analyses reveal ancient cultivation and land use in Nuchatlaht (Nuu-chah-nulth) territories, Pacific Northwest. J. Archaeol. Sci. 143, 105611. ( 10.1016/j.jas.2022.105611) [DOI] [Google Scholar]
- 21.Ross PM, Knox MA, Smith S, Smith H, Williams J, Hogg ID. 2018. Historical translocations by Māori may explain the distribution and genetic structure of a threatened surf clam in Aotearoa (New Zealand). Sci. Rep. 8, 1-8. [DOI] [PMC free article] [PubMed] [Google Scholar]
- 22.Kondo T, Crisp MD, Linde C, Bowman DM, Kawamura K, Kaneko S, Isagi Y. 2012. Not an ancient relic: the endemic Livistona palms of arid central Australia could have been introduced by humans. Proc. R. Soc. B 279, 2652-2661. ( 10.1098/rspb.2012.0103) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 23.Hoffman KM, et al. 2021. Conservation of Earth's biodiversity is embedded in Indigenous fire stewardship. Proc. Natl Acad. Sci. USA 118, e2105073118. ( 10.1073/pnas.2105073118) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 24.Kimmerer RW, Lake FK. 2001. The role of Indigenous burning in land management. J. Forest. 99, 36-41. [Google Scholar]
- 25.Lepofsky D, Armstrong CG, Greening S, Jackley J, Carpenter J, Guernsey B, Mathews D, Turner NJ. 2017. Historical ecology of cultural keystone places of the Northwest Coast. Am. Anthropol. 119, 448-463. ( 10.1111/aman.12893) [DOI] [Google Scholar]
- 26.Fedje DW, Mathewes RM. 2005. Haida gwaii: human history and environment from the time of loon to the time of the iron people. Vancouver, Canada: University of British Columbia Press. [Google Scholar]
- 27.Letham B, Lepofsky D, Greening S. 2021. A post-glacial relative sea level curve for the central Douglas Channel area, British Columbia, Canada. Quat. Sci. Rev. 263, 106991. ( 10.1016/j.quascirev.2021.106991) [DOI] [Google Scholar]
- 28.Deur D, Turner NJ. 2005. Keeping it living: traditions of plant use and cultivation on the northwest coast of North America. Seattle, WA: University of Washington Press. [Google Scholar]
- 29.Ḵii'iljuus Wilson BJ, Smith N, Salomon AK, Augustine S. 2022. Naw NaaGaland - Octopus Houses of Haida Gwaii. In Sea gardens across the Pacific: reawakening ancestral mariculture innovations, version 1 edn (ed. PSG Collective). Seattle, WA: Washington Sea Grant at the University of Washington. [Google Scholar]
- 30.Pacific Sea Garden Collective. 2022. Sea gardens across the Pacific: reawakening ancestral mariculture innovations, version 1 edn. Seattle, WA: Washington Sea Grant at the University of Washington. [Google Scholar]
- 31.Groesbeck AS, Rowell K, Lepofsky D, Salomon AK. 2014. Ancient clam gardens increased shellfish production: adaptive strategies from the past can inform food security today. PLoS ONE 9, e91235. ( 10.1371/journal.pone.0091235) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 32.Holmes K, Lepofsky D, Smith NF, Crowell TD, Salomon AK. 2022. Ancestral sea gardens supported human settlements for at least 3,800 years on the Northwest Coast of North America. Front. Earth Sci. 10, 988111. ( 10.3389/feart.2022.988111) [DOI] [Google Scholar]
- 33.Atlas WI, et al. 2021. Indigenous systems of management for culturally and ecologically resilient Pacific salmon (Oncorhynchus spp.) fisheries. BioScience 71, 186-204. ( 10.1093/biosci/biaa144) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 34.Brown F, Brown YK.. 2009. Staying the course, staying alive - coastal First Nations fundamental truths: biodiversity, stewardship and sustainability. Victoria, Canada: Biodiversity BC. [Google Scholar]
- 35.Uu-a-thluk. 2018. Uu-a-thluk strategic plan: building on our successes 2018–2023. See https://uuathluk.ca/uu-a-thluk-strategic-plan/.
- 36.Nuu-chah-nulth Tribal Council. 1991. Our World-Our Ways: T'aat'aaqsapa Cultural Dictionary, edited by Jay V. Powell, and Andrew Callicum. Learning Taat'aaqsapa Series. Nuu-chah-nulth Tribal Council, Port Alberni. [Google Scholar]
- 37.Heiltsuk Tribal Council. 2018. Dáduqvĺá qṇtxv Ǧvı̓ĺásax̌: to look at our traditional laws. Decision of the heiltsuk (haíɫzaqv) dáduqvĺá committee regarding the 13 October 2016 nathan E. Stewart spill. Bella Bella, Canada: Heiltsuk Tribal Council. [Google Scholar]
- 38.Napoleon V, Friedland H. 2016. An inside job: engaging with Indigenous legal traditions through stories. McGill Law J./Revue de droit de McGill 61, 725-754. (https://lawjournal.mcgill.ca/article/an-inside-job-engaging-with-indigenous-legal-traditions-through-stories/) [Google Scholar]
- 39.Kitasoo Xai'xais Nation. 2022. Declaration of the Gitdisdzu Lugyeks marine protected area. (Kitasoo Xai'xais Hereditary Chiefs Council).
- 40.Müller-Wille S. 2005. Walnuts at Hudson Bay, coral reefs in Gotland: the colonialism of Linnaean botany. In Colonial botany: science, commerce, and politics in the early modern world (eds Schiebinger L, Swan C), pp. 34-48. Philadelphia, PA: University of Pennsylvania Press. [Google Scholar]
- 41.Vos PD. 2007. Natural history and the pursuit of empire in eighteenth-century Spain. Eighteenth-Century Studies 40, 209-239. [Google Scholar]
- 42.Cañizares-Esguerra J. 2005. Iberian colonial science. Isis 96, 64-70. ( 10.1086/430679) [DOI] [PubMed] [Google Scholar]
- 43.Schiebinger L, Swan C. 2007. Colonial botany: science, commerce, and politics in the early modern world. Philadelphia, PA: University of Pennsylvania Press. [Google Scholar]
- 44.Hennessy E, McCleary AL. 2011. Nature's Eden? The production and effects of'Pristine'Nature in the Galápagos Islands. Island Stud. J. 6. 131–156. [Google Scholar]
- 45.Willems–Braun B. 1997. Buried epistemologies: the politics of nature in (post) colonial British Columbia. Ann. Assoc. Am. Geogr. 87, 3-31. ( 10.1111/0004-5608.00039) [DOI] [Google Scholar]
- 46.Eichler L, Baumeister D. 2021. Settler colonialism and the US conservation movement: contesting histories, indigenizing futures. Ethics , Pol. Environ. 24, 209-234. [Google Scholar]
- 47.Miriti MN, Rawson AJ, Mansfield B. 2023. The history of natural history and race: decolonizing human dimensions of ecology. Ecol. Appl. 33, e2748. ( 10.1002/eap.2748) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 48.Brockway LH. 1979. Science and colonial expansion: the role of the British Royal Botanic Gardens. Am. Ethnol. 6, 449-465. ( 10.1525/ae.1979.6.3.02a00030) [DOI] [Google Scholar]
- 49.Chambers N. 2000. The letters of Sir Joseph Banks, a selection, 1768–1820. Singapore: World Scientific. [Google Scholar]
- 50.Fara P. 2004. Sex, botany and empire: the story of Carl Linnaeus and Joseph Banks. London, UK: Icon Books. [Google Scholar]
- 51.Gascoigne JPD, Gascoigne J. 1998. Science in the service of empire: Joseph Banks, the British state and the uses of science in the age of revolution. Cambridge, UK: Cambridge University Press. [Google Scholar]
- 52.Asase A, Mzumara-Gawa TI, Owino JO, Peterson AT, Saupe E. 2022. Replacing ‘parachute science’ with ‘global science’ in ecology and conservation biology. Conserv. Sci. Pract. 4, e517. ( 10.1111/csp2.517) [DOI] [Google Scholar]
- 53.Ramírez-Castañeda V, et al. 2022. A set of principles and practical suggestions for equitable fieldwork in biology. Proc. Natl Acad. Sci. USA 119, e2122667119. ( 10.1073/pnas.2122667119) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 54.Merson J. 2000. Bio-prospecting or bio-piracy: intellectual property rights and biodiversity in a colonial and postcolonial context. Osiris 15, 282-296. ( 10.1086/649331) [DOI] [PubMed] [Google Scholar]
- 55.Mohammed RS, et al. 2022. Colonial legacies influence biodiversity lessons: how past trade routes and power dynamics shape present-day scientific research and professional opportunities for Caribbean scientists. Am. Nat. 200, 140-155. ( 10.1086/720154) [DOI] [PubMed] [Google Scholar]
- 56.Hanna SS. 1999. From single-species to biodiversity–making the transition in fisheries management. Biodivers. Conserv. 8, 45-54. ( 10.1023/A:1008852906430) [DOI] [Google Scholar]
- 57.Link JS. 2002. What does ecosystem-based fisheries management mean. Fisheries 27, 18-21. [Google Scholar]
- 58.Simberloff D. 1998. Flagships, umbrellas, and keystones: is single-species management passé in the landscape era? Biol. Conserv. 83, 247-257. ( 10.1016/S0006-3207(97)00081-5) [DOI] [Google Scholar]
- 59.Pikitch EK, et al. 2004. Ecosystem-based fishery management, pp. 346-347. Washington, DC: American Association for the Advancement of Science. [DOI] [PubMed] [Google Scholar]
- 60.Todd Z. 2018. Refracting the state through human-fish relations. Decolonization: Indigeneity , Educ. Soc. 7, 60-75. [Google Scholar]
- 61.Nadasdy P. 2003. Hunters and bureaucrats: power, knowledge, and aboriginal-state relations in the southwest Yukon. Vancouver, Canada: UBC Press. [Google Scholar]
- 62.Christensen NL, et al. 1996. The report of the Ecological Society of America committee on the scientific basis for ecosystem management. Ecol. Appl. 6, 665-691. [Google Scholar]
- 63.Slocombe DS. 1993. Implementing ecosystem-based management. BioScience 43, 612-622. ( 10.2307/1312148) [DOI] [Google Scholar]
- 64.Telesca JE. 2017. Accounting for loss in fish stocks: a word on life as biological asset. Environ. Soc. 8, 144-160. ( 10.3167/ares.2017.080107) [DOI] [Google Scholar]
- 65.Pikitch EK, et al. 2004. Ecosystem-based fishery management. Science 305, 346-347. ( 10.1126/science.1098222) [DOI] [PubMed] [Google Scholar]
- 66.Ecosystem Principles Advisory Panel. 1999. Ecosystem-based fishery management: a report to congress by the ecosystem principles advisory panel. Washington, DC: US National Marine Fisheries Service. [Google Scholar]
- 67.Vira B, Adams WM. 2009. Ecosystem services and conservation strategy: beware the silver bullet. Conserv. Lett. 2, 158-162. ( 10.1111/j.1755-263X.2009.00063.x) [DOI] [Google Scholar]
- 68.Maes J, Burkhard B, Geneletti D. 2018. Ecosystem services are inclusive and deliver multiple values. A comment on the concept of nature's contributions to people. One Ecosys. 3, e24720. [Google Scholar]
- 69.Norgaard RB. 2010. Ecosystem services: from eye-opening metaphor to complexity blinder. Ecol. Econ. 69, 1219-1227. ( 10.1016/j.ecolecon.2009.11.009) [DOI] [Google Scholar]
- 70.Polasky S, Kling CL, Levin SA, Carpenter SR, Daily GC, Ehrlich PR, Heal GM, Lubchenco J. 2019. Role of economics in analyzing the environment and sustainable development. Proc. Natl Acad. Sci. USA 116, 5233-5238. ( 10.1073/pnas.1901616116) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 71.Masood E. 2018. The battle for the soul of biodiversity. Nature 560, 423-426. ( 10.1038/d41586-018-05984-3) [DOI] [PubMed] [Google Scholar]
- 72.Díaz S, et al. 2018. Assessing nature's contributions to people. Science 359, 270-272. ( 10.1126/science.aap8826) [DOI] [PubMed] [Google Scholar]
- 73.Ojeda J, Salomon AK, Rowe JK, Ban NC. 2022. Reciprocal contributions between people and nature: a conceptual intervention. BioScience 72, 952-962. ( 10.1093/biosci/biac053) [DOI] [Google Scholar]
- 74.Okamoto DK, et al. 2020. Attending to spatial social–ecological sensitivities to improve trade-off analysis in natural resource management. Fish Fish. 21, 1-12. ( 10.1111/faf.12409) [DOI] [Google Scholar]
- 75.McKechnie I, Wigen RJ. 2011. Toward a historical ecology of pinniped and sea otter hunting traditions on the coast of southern British Columbia. In Human impacts on seals, sea lions, and sea otters: integrating archaeology and ecology in the northeast Pacific (eds Braje TJ, Rick TC), pp. 129-166. Berkeley, CA: University of California Press. [Google Scholar]
- 76.Szpak P, Orchard TJ, McKechnie I, Grocke DR. 2012. Historical ecology of late Holocene sea otters (Enhydra lutris) from northern British Columbia: isotopic and zooarchaeological perspectives. J. Archaeol. Sci. 39, 1553-1571. ( 10.1016/j.jas.2011.12.006) [DOI] [Google Scholar]
- 77.Fedje DW, Mackie AP, Wigen RJ, Mackie Q, Lake C. 2005. Kilgii Gwaay: An early maritime site in the south of Haida Gwaii. In Haida Gwaii: human history and environment from the time of loon to the time of the iron people (ed. D. W. F. a. R. W. Mathewes), pp. 187-203. Vancouver, Canada: UBC Press. [Google Scholar]
- 78.Ḵii'iljuus Wilson B, Luu Gaahlandaay Borserio KJ. 2011. Gam tluu tllgaay aa k'iixa Gang ga; There is no land strange. In That which makes us Haida-The Haida language book (eds Steedman S, Collison N), pp. 187-196. Skidegate, Canada: Haida Gwaii Museum. [Google Scholar]
- 79.Salomon AK, Ḵii'iljuus Wilson BJ, Xanius White E, Tanape N Sr, Happynook TM. 2015. First Nations perspectives on sea otter conservation in British Columbia and Alaska: insights into coupled human-ocean systems. In Sea otter conservation (eds Larson SE, Bodkin JL, VanBlaricom GR), pp. 301-331. Amsterdam, The Netherlands: Elsevier. [Google Scholar]
- 80.Estes JA, Palmisano JF. 1974. Sea otters: their role in structuring nearshore communities. Science 185, 1058-1060. ( 10.1126/science.185.4156.1058) [DOI] [PubMed] [Google Scholar]
- 81.Estes JA, Duggins DO. 1995. Sea otters and kelp forests in Alaska: generality and variation in a community ecology paradigm. Ecol. Monogr. 65, 75-100. ( 10.2307/2937159) [DOI] [Google Scholar]
- 82.Estes JA, Tinker MT, Williams TM, Doak DF. 1998. Killer whale predation on sea otters linking oceanic and nearshore ecosystems. Science 282, 473-476. ( 10.1126/science.282.5388.473) [DOI] [PubMed] [Google Scholar]
- 83.Tinker MT, et al. 2021. Sea otter population collapse in southwest Alaska: assessing ecological covariates, consequences, and causal factors. Ecol. Monogr. 91, e01472. ( 10.1002/ecm.1472) [DOI] [Google Scholar]
- 84.Hind KR, Starko S, Burt JM, Lemay MA, Salomon AK, Martone PT. 2019. Trophic control of cryptic coralline algal diversity. Proc. Natl Acad. Sci. USA 116, 15080-15085. ( 10.1073/pnas.1900506116) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 85.Markel RW, Shurin JB. 2015. Indirect effects of sea otters on rockfish (Sebastes spp.) in giant kelp forests. Ecology 96, 2877-2890. ( 10.1890/14-0492.1) [DOI] [PubMed] [Google Scholar]
- 86.Gregr EJ, et al. 2020. Cascading social-ecological costs and benefits triggered by a recovering keystone predator. Science 368, 1243-1247. ( 10.1126/science.aay5342) [DOI] [PubMed] [Google Scholar]
- 87.Foster E, et al. 2021. Physical disturbance by recovering sea otter populations increases eelgrass genetic diversity. Science 374, 333-336. ( 10.1126/science.abf2343) [DOI] [PubMed] [Google Scholar]
- 88.Jackson JR. 2021. Sea otter (Enhydra lutris) impacts to seagrass (Zostera marina) communities across the northeast Pacific. Rohnert Park, CA: Sonoma State University. [Google Scholar]
- 89.Hessing-Lewis M, Rechsteiner EU, Hughes BB, Tinker MT, Monteith ZL, Olson AM, Henderson MM, Watson JC. 2018. Ecosystem features determine seagrass community response to sea otter foraging. Mar. Pollut. Bull. 134, 134-144. ( 10.1016/j.marpolbul.2017.09.047) [DOI] [PubMed] [Google Scholar]
- 90.Raymond WW, Hughes BB, Stephens TA, Mattson CR, Bolwerk AT, Eckert GL. 2021. Testing the generality of sea otter-mediated trophic cascades in seagrass meadows. Oikos 130, 725-738. ( 10.1111/oik.07681) [DOI] [Google Scholar]
- 91.Hughes BB, Eby R, Van Dyke E, Tinker MT, Marks CI, Johnson KS, Wasson K.. 2013. Recovery of a top predator mediates negative eutrophic effects on seagrass. Proc. Natl Acad. Sci. USA 110, 15 313-15 318. ( 10.1073/pnas.1302805110) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 92.Burt JM, Ḵii'iljuus BJ. W., Malchoff T, Wii-tsts-koom AM, Skil Hiilans AD, Salomon AK. 2020. Enabling coexistence: navigating predator-induced regime shifts in human-ocean systems. People Nat. 2, 557-574. ( 10.1002/pan3.10090) [DOI] [Google Scholar]
- 93.Pinkerton E, Salomon AK, Dragon F. 2019. Reconciling social justice and ecosystem-based management in the wake of a successful predator reintroduction. Can. J. Fish. Aquat. Sci. 76, 1031-1039. ( 10.1139/cjfas-2018-0441) [DOI] [Google Scholar]
- 94.Popken LR, Griffin PJ, Coté C, Angel E. 2023. Indigenous food sovereignty through resurgent self-governance: centering Nuu-chah-nulth principles in sea otter management in Canada. Ecology and Society 28(2). [Google Scholar]
- 95.Breed GA, Golson EA, Tinker MT. 2017. Predicting animal home-range structure and transitions using a multistate Ornstein-Uhlenbeck biased random walk. Ecology 98, 32-47. ( 10.1002/ecy.1615) [DOI] [PubMed] [Google Scholar]
- 96.Tinker MT, et al. 2021. Habitat features predict carrying capacity of a recovering marine carnivore. J. Wildl. Manage. 85, 303-323. ( 10.1002/jwmg.21985) [DOI] [Google Scholar]
- 97.Tinker MT, Gill VA, Esslinger GG, Bodkin J, Monk M, Mangel M, Monson DH, Raymond WW, Kissling ML. 2019. Trends and carrying capacity of sea otters in southeast Alaska. J. Wildl. Manage. 83, 1073-1089. ( 10.1002/jwmg.21685) [DOI] [Google Scholar]
- 98.Estes J, Riedman M, Staedler M, Tinker M, Lyon B. 2003. Individual variation in prey selection by sea otters: patterns, causes and implications. J. Anim. Ecol. 72, 144-155. ( 10.1046/j.1365-2656.2003.00690.x) [DOI] [Google Scholar]
- 99.Tinker MT, Bentall G, Estes JA. 2008. Food limitation leads to behavioral diversification and dietary specialization in sea otters. Proc. Natl Acad. Sci. USA 105, 560-565. ( 10.1073/pnas.0709263105) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 100.Smith JG, Tomoleoni J, Staedler M, Lyon S, Fujii J, Tinker MT. 2021. Behavioral responses across a mosaic of ecosystem states restructure a sea otter–urchin trophic cascade. Proc. Natl Acad. Sci. USA 118, e2012493118. ( 10.1073/pnas.2012493118) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 101.Gorra TR, Garcia SC, Langhans MR, Hoshijima U, Estes JA, Raimondi PT, Tinker MT, Kenner MC, Kroeker KJ. 2022. Southeast Alaskan kelp forests: inferences of process from large-scale patterns of variation in space and time. Proc. R. Soc. B 289, 20211697. ( 10.1098/rspb.2021.1697) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 102.Slade E, McKechnie I, Salomon AK. 2022. Archaeological and contemporary evidence indicates low sea otter prevalence on the Pacific Northwest Coast during the Late Holocene. Ecosystems 25, 548-566. ( 10.1007/s10021-021-00671-3) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 103.Skidegate Haida Immersion Program (SHIP). 2021. HlGaagilda Xaayda Kil K'aalang: SHIP Xaayda Kil Glossary. Journal of the Council of Haida Nation, Haida, Gwaii.
- 104.Lee LC, Thorley J, Watson J, Reid M, Salomon AK. 2019. Diverse knowledge systems reveal social–ecological dynamics that inform species conservation status. Conserv. Lett. 12, e12613. [Google Scholar]
- 105.Okamoto DK, Hessing-Lewis M, Samhouri JF, Shelton AO, Stier A, Levin PS, Salomon AK. 2020. Spatial variation in exploited metapopulations obscures risk of collapse. Ecol. Appl. 30, e02051. ( 10.1002/eap.2051) [DOI] [PubMed] [Google Scholar]
- 106.Lee LC, Reid M, Jones R, Winbourne J, Rutherford M, Salomon AK. 2019. Drawing on indigenous governance and stewardship to build resilient coastal fisheries: people and abalone along Canada's northwest coast. Mar. Pol. 109, 103701. ( 10.1016/j.marpol.2019.103701) [DOI] [Google Scholar]
- 107.Mauser W, Klepper G, Rice M, Schmalzbauer BS, Hackmann H, Leemans R, Moore H. 2013. Transdisciplinary global change research: the co-creation of knowledge for sustainability. Curr. Opin. Environ. Sustain. 5, 420-431. ( 10.1016/j.cosust.2013.07.001) [DOI] [Google Scholar]
- 108.Lee LC, et al. 2021. Chiixuu Tll iinasdll: indigenous ethics and values lead to ecological restoration for people and place in Gwaii Haanas. Ecol. Restor. 39, 45-51. ( 10.3368/er.39.1-2.45) [DOI] [Google Scholar]
- 109.Council of Haida Nation and Government of Canada. 2018. Gwaii Haanas Gina 'Waadluxan KilGuhlGa Land-Sea-People Management Plan, Haida, Gwaii. See publications.gc.ca/pub?id=9.860259&sl=0.
- 110.Ibarra SN. 2021. Addressing a complex resource conflict: humans, sea otters, and shellfish in southeast Alaska. Fairbanks, AK: University of Alaska Fairbanks. [Google Scholar]
- 111.Norgaard RB. 1989. The case for methodological pluralism. Ecol. Econ. 1, 37-57. ( 10.1016/0921-8009(89)90023-2) [DOI] [Google Scholar]
- 112.Armitage DR, et al. 2019. Integrating governance and quantitative evaluation of resource management strategies to improve social and ecological outcomes. BioScience 69, 523-532. ( 10.1093/biosci/biz059) [DOI] [Google Scholar]
- 113.Richardson BJ. 2009. The ties that bind: Indigenous peoples and environmental governance. In: Indigenous peoples and the law: comparative and critical perspectives (eds BJ Richardson, S Imai, K McNeill). Portland, OR: Hart Publishing. [Google Scholar]
- 114.Cash DW, Adger WN, Berkes F, Garden P, Lebel L, Olsson P, Pritchard L, Young O. 2006. Scale and cross-scale dynamics: governance and information in a multilevel world. Ecol. Soc. 11, 8. [Google Scholar]
- 115.Kleinhans M.-M, Macdonald RA. 1997. What is a critical legal pluralism? Can. J. Law Soc./La Revue Canadienne Droit et Société 12, 25-46. ( 10.1017/S0829320100005342) [DOI] [Google Scholar]
- 116.Norström AV, et al. 2020. Principles for knowledge co-production in sustainability research. Nat. Sustain. 3, 182-190. ( 10.1038/s41893-019-0448-2) [DOI] [Google Scholar]
- 117.Stirling A. 2012. Opening up the politics of knowledge and power in bioscience. PLoS Biol. 10, e1001233. ( 10.1371/journal.pbio.1001233) [DOI] [PMC free article] [PubMed] [Google Scholar]
- 118.Liboiron M. 2021. Pollution is colonialism. Durham, NC: Duke University Press. [Google Scholar]
- 119.Todd Z. 2018. Refracting the state through human-fish relations: fishing, indigenous legal orders and colonialism in north/western Canada. Decolonization: Indig. Educ. Soc. 7, 60-75. [Google Scholar]
- 120.Hull B. 2009. Environmental pluralism. Detroit, MI: Macmillan Reference USA. [Google Scholar]
- 121.Kimmerer RW. 2013. Braiding sweetgrass: indigenous wisdom, scientific knowledge and the teachings of plants. Minneapolis, MN: Milkweed Editions. [Google Scholar]
- 122.Armitage D, Berkes F, Doubleday N. 2010. Adaptive co-management: collaboration, learning, and multi-level governance. Vancouver, Canada: UBC Press. [Google Scholar]
- 123.Corntassel J. 2012. Re-envisioning resurgence: Indigenous pathways to decolonization and sustainable self-determination. Decolonization: Indigeneity, Edu. Soc. 1.
- 124.No'kmaq MS, et al. 2021. ‘Awakening the sleeping giant’: re-Indigenization principles for transforming biodiversity conservation in Canada and beyond. Facets 6, 839-869. ( 10.1139/facets-2020-0083) [DOI] [Google Scholar]
- 125.Reid M, Collins ML, Hall SR. J., Mason E, McGee G, Frid A. 2022. Protecting our coast for everyone's future: Indigenous and scientific knowledge support marine spatial protections proposed by Central Coast First Nations in Pacific Canada. People Nat. 4, 1052-1070. ( 10.1002/pan3.10380) [DOI] [Google Scholar]
- 126.Parsons M, Taylor L, Crease R. 2021. Indigenous environmental justice within marine ecosystems: a systematic review of the literature on indigenous peoples' involvement in marine governance and management. Sustainability 13, 4217. ( 10.3390/su13084217) [DOI] [Google Scholar]
- 127.Salomon AK, et al. 2023. Disrupting and diversifying the values, voices, and governance principles that shape biodiversity science and management. Figshare. ( 10.6084/m9.figshare.c.6627280) [DOI]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Data Availability Statement
The data are provided in the electronic supplementary material [127].