Move beyond recreation and aesthetics, which tend to be most important and catered to particular people
Frontier . | Potential contributions to equity and justice in ES research and practice . |
---|---|
Broadening and deepening conceptualizations of CES | Include value conceptions, values, and perspectives that resonate with diverse communities Move beyond recreation and aesthetics, which tend to be most important and catered to particular people |
Addressing collective aspects of CES and attending to process | Include values that are held collectively, not just individually Attend to value elicitation processes and how they include or exclude value systems, perspectives, and human groups |
Acknowledging that CES are reciprocal, relational, and dynamic | Acknowledge reciprocal values and relationships (often especially important for Indigenous communities) Include values that do not align with the producer–consumer ES framework |
Embracing narrative | Express values that nonnarrative methods characterize poorly Acknowledge different methods and preferences for communicating CES |
Better connecting to biophysical attributes | Elucidate how biophysical features connect to nonmaterial values; therefore allow for better distribution of diverse values from ecosystems Honor that biophysical attributes are important for nonmaterial reasons |
Suggested future research questions at the frontiers of CES research.
CES research frontier . | Possible future research questions . |
---|---|
[Overarching issues that apply across frontiers] | How does including CES information affect real-world decisions? How do CES relate to foundational social science concepts and areas of inquiry: attitudes, preferences, motivations, and behavior (or practices or action)? In the characterization of CES, what is possible to standardize? Is a standardized set of rules or guidelines—a toolbox—possible? How would such a toolbox affect equity? How would the described frontiers affect such rules or guidelines? How can research address the challenges created by the often context-specific nature of CES? |
Broadening and deepening conceptualizations of CES | What types of CES tend to be universal, and which are place or context specific? What important nonmaterial benefits that people receive from ecosystems are not captured by current CES conceptions? What creative metrics can be used to represent CES other than aesthetics and recreation? How do CES and CES research differ when examined outside of neoliberal framings? Is this different for different CES? What are the pros and cons of using flexible conceptualizations of CES? |
Addressing collective aspects of CES and attending to process | Are there types of CES that exist only in the collective? How do they differ from CES that are individual? What forms of deliberation are best suited to CES elicitation in different contexts? How do different valuation and governance contexts make space for different CES to manifest or rise to prominence? What role do CES play in environmental conflicts? How do aspects of process (e.g., power considerations) affect where and how CES are included in responses to conflict? How can portrayals of the collective aspects of CES be vetted with a group? |
Acknowledging that CES are reciprocal, relational, and dynamic | How do outcomes differ if research or elicitation uses CES versus relational values framings? How can ES analysis incorporate the temporal dynamism of CES? What role does social learning play in ES research and practice? How do phase shifts in social–ecological systems (e.g., such as those caused by natural disasters, extreme climatic events, pandemics) affect CES (e.g., make some more prominent? Create new CES?)? Do CES lead to change, respond to change, or have another relationship? |
Embracing narrative | What methods or processes (many of which exist in other fields) can facilitate rich and useful CES narratives? How do decision-makers perceive narrative-based presentations of CES? What features or analysis make narrative useful to decision-makers? What are ways to feasibly articulate diverse narratives from equally diverse communities? How can multiple narratives be integrated to affect decision-making? How can the concept from critical race theory that “narratives provide a language to bridge… gaps in imagination and conception” (Delgado and Stefancic : 52) inspire and inform the use of narrative in CES studies? Can narrative help to deal with the fact that CES are often intertwined (with each other and with material ES)? What mechanisms have other fields used to include narrative in decision-making processes, and what can CES research or practice learn from this? Do these mechanisms go beyond putting the narrative on the table? How can narrative integrate with other forms of data? |
Better connecting to biophysical attributes | Do the ecological attributes of landscapes and seascapes matter to CES provision? If so, how? Do CES differ on the basis of ecological attributes? For instance, from ecosystems with different species mixes (mostly native versus mostly nonnative species versus mixes of culturally valuable species of multiple origins)? From ecosystems that are degraded versus not? Why and for whom? What are the trade-offs in connecting CES to different ecosystem service providers? How do CES–biophysical connections of different types help decision-makers? What factors affect how decision-makers use research that connects CES and biophysical attributes? What biophysical features are important for CES in different contexts, and how do social, cultural, and technical factors mediate them? What is, or would be, required to be able to use remotely sensed data to assess or characterize CES? |
CES research frontier . | Possible future research questions . |
---|---|
[Overarching issues that apply across frontiers] | How does including CES information affect real-world decisions? How do CES relate to foundational social science concepts and areas of inquiry: attitudes, preferences, motivations, and behavior (or practices or action)? In the characterization of CES, what is possible to standardize? Is a standardized set of rules or guidelines—a toolbox—possible? How would such a toolbox affect equity? How would the described frontiers affect such rules or guidelines? How can research address the challenges created by the often context-specific nature of CES? |
Broadening and deepening conceptualizations of CES | What types of CES tend to be universal, and which are place or context specific? What important nonmaterial benefits that people receive from ecosystems are not captured by current CES conceptions? What creative metrics can be used to represent CES other than aesthetics and recreation? How do CES and CES research differ when examined outside of neoliberal framings? Is this different for different CES? What are the pros and cons of using flexible conceptualizations of CES? |
Addressing collective aspects of CES and attending to process | Are there types of CES that exist only in the collective? How do they differ from CES that are individual? What forms of deliberation are best suited to CES elicitation in different contexts? How do different valuation and governance contexts make space for different CES to manifest or rise to prominence? What role do CES play in environmental conflicts? How do aspects of process (e.g., power considerations) affect where and how CES are included in responses to conflict? How can portrayals of the collective aspects of CES be vetted with a group? |
Acknowledging that CES are reciprocal, relational, and dynamic | How do outcomes differ if research or elicitation uses CES versus relational values framings? How can ES analysis incorporate the temporal dynamism of CES? What role does social learning play in ES research and practice? How do phase shifts in social–ecological systems (e.g., such as those caused by natural disasters, extreme climatic events, pandemics) affect CES (e.g., make some more prominent? Create new CES?)? Do CES lead to change, respond to change, or have another relationship? |
Embracing narrative | What methods or processes (many of which exist in other fields) can facilitate rich and useful CES narratives? How do decision-makers perceive narrative-based presentations of CES? What features or analysis make narrative useful to decision-makers? What are ways to feasibly articulate diverse narratives from equally diverse communities? How can multiple narratives be integrated to affect decision-making? How can the concept from critical race theory that “narratives provide a language to bridge… gaps in imagination and conception” (Delgado and Stefancic : 52) inspire and inform the use of narrative in CES studies? Can narrative help to deal with the fact that CES are often intertwined (with each other and with material ES)? What mechanisms have other fields used to include narrative in decision-making processes, and what can CES research or practice learn from this? Do these mechanisms go beyond putting the narrative on the table? How can narrative integrate with other forms of data? |
Better connecting to biophysical attributes | Do the ecological attributes of landscapes and seascapes matter to CES provision? If so, how? Do CES differ on the basis of ecological attributes? For instance, from ecosystems with different species mixes (mostly native versus mostly nonnative species versus mixes of culturally valuable species of multiple origins)? From ecosystems that are degraded versus not? Why and for whom? What are the trade-offs in connecting CES to different ecosystem service providers? How do CES–biophysical connections of different types help decision-makers? What factors affect how decision-makers use research that connects CES and biophysical attributes? What biophysical features are important for CES in different contexts, and how do social, cultural, and technical factors mediate them? What is, or would be, required to be able to use remotely sensed data to assess or characterize CES? |
Before presenting our content, we briefly describe this article's origins. We generated the idea for this article following a session on CES at the 2018 Natural Capital Project symposium, in which all of the present authors participated. Our varied backgrounds (which include combinations of research, consultancy, and work with communities) encompass ongoing and varied experiences that engage CES and led us to the frontiers we present. During these experiences, we detected gaps in ES research and practice, especially as related to equity and justice. Because we see not only equity-related gaps but also some progress toward filling them, we wished to crystallize our thoughts on existing and future work that addresses these gaps. We categorize the results of that crystallization—that is, promising directions in the field—as frontiers. We discuss a subset of CES research: a selection of CES research that which in some way contributes to the role of CES in increasing equity, justice, and inclusion.
We immediately acknowledge two closely related challenges to this article's conceptual foundation: First, critiques of the CES concept and, next, recent suggestions that the concept of nature's contributions to people (NCP) should replace ES (and, by extension, CES). We discuss critiques of the CES concept in this section, then address NCP in our description of the first frontier because we see the NCP concept as intertwined with the trend to broaden and deepen definitions of CES.
We divide critiques of the CES concept into two categories: problems with ES in general and problems with CES specifically. First, some critiques of ES in general may be especially applicable to CES. One such critique is that ES approaches often ignore or exacerbate uneven power relations; this is more likely when data are seen as subjective and soft, as is often the case with CES (Berbés-Blázquez et al. 2016 ). Second, some scholars have argued that ES valuation encourages neoliberal approaches to environmental management that result in commodification of ecosystems, which is especially problematic for many CES (Büscher et al. 2012 , Dempsey and Robertson 2012 ). Third, others have suggested that ES language and concepts do not match how people truly value ecosystems, particularly the nonmaterial relationships that CES aim to represent (Bull et al. 2016 , De Vreese et al. 2019 ). Finally, some argue that ES, because they focus on instrumental value, detract from biodiversity conservation efforts (Miller et al. 2014 ), or cannot adequately capture the many noninstrumental reasons that people value ecosystems (James 2016 ). This final critique interacts with CES in complex ways because CES often imperfectly fit the definition of instrumental value and also encompass relational values (Chan et al. 2018 ).
A second set of challenges address CES specifically in the context of research that embraces ES perspectives, but finds CES challenging to incorporate. A central difficulty lies in quantifying CES and integrating them into broader ES analyses of synergies and trade-offs (Hirons et al. 2016 ). Two underlying issues that make CES challenging to integrate into ES analyses are the problematic one-way service metaphor, which inadequately represents many human–nature reciprocal relationships (Raymond et al. 2013 , Comberti et al. 2015 ), and the deep incommensurability of many CES (Satz et al. 2013 ).
These and other often related incompatibilities, such as the inappropriateness of the ecosystem concept's focus on functional systems rather than aesthetic, symbolic phenomena, have led some scholars to argue that we should abandon the CES concept altogether (Kirchhoff 2019a , 2019b ).
We agree that these myriad challenges and incompatiblities are important. But we think they are surmountable and worth overcoming for intertwined intellectual, practical, and ethical reasons. The intellectual reasons include that decades (if not centuries) of research demonstrate the profound importance of nonmaterial aspects of human–nature connections for human fulfillment and well-being (Russell et al. 2013 , Hirons et al. 2016 ). The practical reasons include that decision-making increasingly employs ES frameworks (Guerry et al. 2015 ), which creates a clear need for some permutation of the concepts that underlie CES. The ethical reasons include that without any way to represent CES, decision-making processes that use ES approaches (and many others) will continue to omit nonmaterial values, with sometimes dramatic justice-related consequences.
CES is one of many possible lenses to interpret and express human–environment relationships—but one that, because of the popularity of the ES concept, currently has potential to influence policy and planning decisions. Although critiques of ES (such as those listed above) are important, it seems that, in practice, the concept can be a larger container for understanding why the nonhuman world matters to people; as the concept continues to evolve, the use of ES may not always fit a strict instrumental, service-provider definition. Indeed, scholars have been working to develop ES to bring about what may be its ultimate goal: to better incorporate into decision-making the diverse ways in which nature matters to people. The frontiers below represent some of—and can perhaps guide future permutations of—this collective work.
Here we describe the five frontiers of CES research that we have identified.
Most CES research that enters ES assessments has focused on recreation and aesthetic values (Hermes et al. 2018 ), which are easier to quantify (and therefore more readily integrate into ES models) than many other CES. These values are important to many people, but the breadth and depth of CES expand well beyond them. Recent scholarship has shown that widely used typologies of CES (e.g., that of the 2005 Millennium Ecosystem Assessment) may not capture the full array of concepts that could be considered CES. Most notably, Indigenous and local knowledge often play an essential role in CES, but Millennium Ecosystem Assessment–based categories do not capture many nuances of these perspectives. To describe this frontier, we first address recent work to reframe ES as NCP, then discuss two reasons that this frontier is important.
Scholars have recently suggested that the NCP concept replace ES (and by extension CES), partly in response to critiques raised above (e.g., a primary goal of the move to NCP is to address limitations of the transactional and economics-derived essence of the language involving services ; Díaz et al. 2018 ). This proposed lexicon change is probably the most well-defined example of the trend to broaden and deepen conceptualizations of CES. For this reason and also because the NCP versus ES discussion is of current interest, we will elaborate on the suggested transition to NCP.
Like many others, we do not see the distinction between NCP and ES as conceptually consequential (de Groot et al. 2018 , Kenter 2018 ). The NCP framing addresses issues that, although not a focus of the first iteration of ES, were not total blind spots (de Groot et al. 2018 ), as the examples in this article demonstrate. An issue more substantial than which term we use is the unidirectionality implicit in both terms: They both focus on how ecosystems affect people, not the reverse (Comberti et al. 2015 ). In presenting our next frontier, we describe emerging evidence that researchers within ES or NCP communities are working to address this problem.
Our understanding of CES is highly consistent with published descriptions of both nonmaterial NCP and CES. Díaz and colleagues ( 2018 : 271) defined nonmaterial NCP as “nature's effects on subjective or psychological aspects underpinning people's quality of life, both individually and collectively.” One distinction between NCP and ES, they noted, is that culture permeates the NCP categories (material, nonmaterial, and regulating), rather than, in their perception, being isolated to one category in the ES framework. But this very idea of culture permeating ES categories and the separate category having nonmateriality at its core has been part of the published CES conversation for nearly a decade. Chan and colleagues ( 2011 : 206) defined CES as “ecosystems’ contribution to the nonmaterial benefits (e.g., experiences, capabilities) that people derive from human–ecological relations.” Another group led by Chan (Chan et al. 2012a : 745) discussed how CES are “everywhere” in ES: “Most ES, cultural and otherwise, have nonmaterial or intangible dimensions.” This understanding of CES is quite consistent with the ethos of nonmaterial NCP. The primary distinction is between nature's effects (NCP) and its benefits (CES)—that is, how nature's negative impacts are treated. The term effects includes negative impacts; benefits does not. We do not see this distinction as central to the conversation for two main reasons: because the classification of impacts as negative or positive can be contextually dependent and also because scholarly work on ecosystem disservices addresses negative impacts (e.g., von Döhren and Haase 2015 , Shackelton et al. 2016 ).
The prior two paragraphs demonstrate that the thinking underlying NCP and CES is quite similar. We do not have a strong preference for either term. More importantly, we advocate for the richness inherent in the understanding evident in much CES work and detailed in the present article (Schaubroeck 2019 ). We use CES because it is more parsimonious and currently more established than nonmaterial NCP. As we embrace the concept's richness, however, we should also address the following question: If we wish to broaden and deepen definitions of CES, where does the concept end? We therefore accompany our call for expanded definitions of CES with a suggestion of where the concept might locate its outer bounds. We suggest that CES research must include three core concepts: how nonmaterial aspects of human-nature relationships influence human well-being . If the question does not address nonmateriality, human–nature relationships and human well-being, it is not CES.
Engagement with broader and deeper definitions of CES may entail substantial deviations from typical ES research, and the remainder of our discussion of this frontier focuses on innovations related to these divergences. We focus on two fundamental differences between research on ES generally and on broadly defined CES, and on responses to these differences. The first difference is that many CES are based on people's interactions and experiences with particular ecosystems and are therefore locally nuanced and place based (Pascua et al. 2017 ). Much ES research, conversely, seeks to generalize across larger geographic regions. The second difference is that understanding rich experiences of CES can require epistemological and methodological approaches distinct from those that ES research typically employs (Adamowicz et al. 1998 , Winthrop 2014 , van Riper et al. 2017 ). In the present article, we discuss two overarching ways that CES scholars have embraced these differences: place-based research and expanded types of valuation.
Place-based research is a clear response to the place-specific nature of many CES. The process of identifying particular CES concepts relevant to a given place, especially when conducted in close coordination with Indigenous peoples and local communities, may not only provide the most accurate understanding but may also deepen existing perspectives and reveal new ideas of what CES can be. Once identified, these concepts might resonate with other communities, even in distinct contexts. As one example, a community-based process in Hawai´i identified the CES concept of “opportunities to learn place-based practices by actually doing them” (Pascua et al. 2017 : 471). This may manifest in some places (e.g., Hawai´i) as reviving double-hulled canoe celestial navigation practices and in others (e.g., Japan) as embracing responsibilities that come with being a third-generation ama diver (a freediving fisherwoman). This suggests that there are roles both to allow local language and cultural concepts to inform place-based CES frameworks and categorical groupings and to find commonalities between places.
Expanding conceptualizations of CES also requires that we address challenges and opportunities with valuation, broadly construed. The shortcomings of monetary valuation, including deep epistemological and methodological concerns, are particularly salient for CES (Satz et al. 2013 , Hirons et al. 2016 ). Classical economic valuation methods account poorly for linked and overlapping values (Lo and Spash 2013 ) and values held by communities or groups (Kenter et al. 2015 , and see next section). The place-based and relational nature of CES may also conflict with the hypothetical, often abstract situations typical of stated-preference methods (Kenter et al. 2016a ; e.g., survey questions about individuals’ willingness to pay to support a hypothetical new park).
These challenges mean that CES must engage with diverse forms of valuation or value elicitation; that is, they must broaden and deepen approaches to valuation. CES researchers have explored multiple options; we cite two examples. The first is deliberative democratic monetary valuation, which maintains economic valuation as a goal but also attends to power dynamics and representation through, as the name suggests, deliberative and democratic participatory processes (Orchard-Webb et al. 2016 ). A second example, this from the field of biocultural approaches, is to first identify specific attributes that connect culture and the environment and then, as appropriate, to use economic valuation tools (e.g., choice experiments) to compare those attributes (Baulcomb et al. 2015 ). One application of a biocultural approach relates to the 2013 large-scale oil spill on Otaiti Reef (Aotearoa, New Zealand). After the spill, tribal authorities used an Indigenous-person–led and culturally grounded decision-making tool to assess the impacts of the spill on the cultural, social, and environmental well-being of their communities using the customary concept of mauri (life force or life-sustaining capacity) as the unit of measurement (Morgan and Fa´aui 2018 ).
Why is it important to broaden and deepen interpretations of CES? One vitally important reason is that expanded interpretations (and operationalizations) of CES may increase the visibility of perspectives, categories, and conceptualizations that are particularly important in contexts less heavily influenced by Western European thought. The role of nature as a valued teacher (Comberti et al. 2015 , Gould and Lincoln 2017 , Pascua et al. 2017 , Ching 2018 ) provides an example. A broader example—one that integrates profound issues related to Indigenous perspectives, cosmovisions (i.e., how a person understands their place in the world), and priorities—is found in Berta Cáceres's work (figure 1 ). These examples, chosen from among thousands, make clear that in order to access the richness and depth of the CES concept, research must engage with definitions beyond recreation and aesthetics.
Tribute to Berta Cácares. The description illuminates relationships between Cácares work, Indigenous world views, and the types of values that CES research strives to represent to the extent possible. Photograph: Goldman Environmental Prize.
This section demonstrates that many scholars are converging on a concept of CES (or nonmaterial NCP) that broadens from how CES were frequently operationalized in the early years of ES research but still limits CES work to address human–nature relationships, human well-being, and nonmaterial phenomena. This expanded but still bounded conception includes deep engagement with place-based values and diverse ways to understand and represent value. This is an important step in advancing equity and environmental justice, especially in places in which some CES values have long been undermined. One primary reason is that an important dimension of social equity is recognition: an acknowledgement of and respect for local knowledge, values, and norms (McDermott et al. 2013 , Pascual et al. 2014 ). In both theory and practice, broad meanings of CES will allow CES research to help make manifest the diverse values of underrepresented communities.
In many cases, CES are experienced as shared cultural phenomena that are best expressed and characterized collectively (Kenter et al. 2015 , 2016a , 2016b ). Of course, individual and collective experiences and values are in “dynamic interplay” (Kenter et al. 2015 : 97); individuals absorb shared and cultural values from their surroundings but interpret them through individual experience (Bachika and Schulz 2011 ). A basic tenet of welfare economics is that aggregating individual preferences adequately represents overall value to society. Although this tenet may be relevant for certain types of values (e.g., economic use values), it may not apply in the case of values that are more often experienced and, therefore, more accurately described at community levels (Parks and Gowdy 2013 ). Research suggests that concepts of collective or shared experiences and values, although they are certainly important in communities of many types, may be particularly important in communities whose perspectives and worldviews differ from dominant Western ones—for instance, among Indigenous peoples (Adamowicz et al. 1998 , Pascua et al. 2017 ).
There are fundamental theoretical reasons why collective valuation techniques make sense in ES-related processes (Wilson and Howarth 2002 ); these reasons are likely even more applicable to highly socially defined CES. Primary among them is that ES are, in economic terms, public goods (i.e., they are “collectively consumed and indivisible among individuals”; Wilson and Howarth 2002 : 441). Individual valuations of such public goods are unlikely to represent collective well-being, and they are unlikely to address social equity in meaningful ways (Wilson and Howarth 2002 ). Another reason relates to the fact that many ecosystem-related values are not pre-formed but emerge through discussion and consideration (Kenter et al. 2016 c). Scholars recognize permutations of this phenomenon in many fields—for instance, in social learning (Wals 2007 , Reed et al. 2010 , Kenter et al. 2011 ), education (Dewey 2007 ), and economics (constructed preferences; Simon et al. 2008 ). Finally, research on ecosystem valuation demonstrates that outcomes—for example, the mix and relative weight of various ES—differ when individual versus collective methods are used (Kaplowitz and Hoehn 2001 ).
Research on how best to elicit collective values—at least as they relate to the environment—has blossomed in recent decades. Much of this work has been focused on participatory and deliberative processes (e.g., Raymond et al. 2014 ). It has used diverse methods: in-depth discussions of various types, citizens’ juries, deliberative opinion polls, deliberative monetary valuation, and deliberative multicriteria analysis (Fish 2011 , Kenter et al. 2015 ). Creative methods also expand from more conventional or established forms of deliberation and include participatory geographic information system (Brown and Fagerholm 2015 ), film- and arts-based approaches (Edwards et al. 2016 , Ranger et al. 2016 ), participatory workshops (Pascua et al. 2017 ), and the use of ethnographic methods during community workdays (Ching 2018 ). Research also suggests that it is often helpful to offer diverse routes to convey values, because various modes can appeal to different social groups (Ernstson 2013 ).
CES research has acknowledged the collective, constructed nature of values in many contexts. Collective methods of characterizing CES can create fruitful spaces of interaction—for example, among managers and participants in watershed management programs (Wilburn 2017 ) or among people interested in more opportunities for collective reflection among busy lives (Ching 2018 ).
Methods that rely on collective engagement have limitations that are important to consider. Most notably, collective methods are especially sensitive to considerations of power (Bickerstaff and Walker 2005 ). The impacts of power differentials include peer pressure, dominance of certain opinions, and avoidance of controversy. These influences can make it difficult to validate results with an entire community and to figure out what entire community means in a given context. Skilled facilitators and local collaborators can help minimize these impacts and work toward more inclusive valuation.
It is worthwhile to address these limitations because acknowledging collective aspects may be crucial to the ability of CES to affect issues of equity and justice. Individual, independent perspectives tend to align with white, Western (especially American), and male identities (Markus and Connor 2014 ); collective approaches to and representations of CES may better represent how many communities think about meaning and importance. Future work could address the limitations above while allowing for collective approaches by focusing on research that inspires, listens, and contributes (University of Hawai´i 2018 ). When performed with place-appropriate and socially aware methods, characterizing CES collectively may lead to more accurate and rich understandings of these services in diverse contexts. In some cases, this type of work can even empower participants and catalyze action—both of which are important components of equity.
Research described in the previous sections has been linked closely to conceptions of CES as reciprocal, relational, and dynamic. Empirical work on CES has repeatedly revealed that the unidirectional, producer–consumer, and instrumental metaphor of services is often inadequate. In Madagascar, for example, ancestral spiritually imbued relationships with land dictate management practices, which in turn provide ES (von Heland and Folke 2014 ). In both British Columbia and Hawai´i (contexts that differ in many ways), the importance of kinship—a relationship but not exactly a service, benefit, or impact—arose repeatedly in semistructured interviews about CES (Gould et al. 2015 ). In an Indigenous-scholar-led study in Hawai'i, Pascua and colleagues ( 2017 ) framed CES research from the beginning as concerning reciprocal relationships, which resulted in meaningful community engagement with the framework and approach.
The concept of reciprocal relationships incorporates the reality that people all over the world steward, manage, or otherwise care for ecosystems that provide various services (Diver et al. 2019 ). Therefore, for many communities, services that people provide to ecosystems are just as relevant as those that ecosystems provide to people; the concept of reciprocity is more relevant than that of services (Comberti et al. 2015 , Kimmerer 2013 ). To recognize that ideas of reciprocity and relationships with nature are central to the ontologies and operation of many communities has important equity implications, especially among Indigenous peoples, local communities, and other groups with profound ties to ecosystems. The Native Hawaiian expression I ola ´ oe, i ola mākou nei (“When you thrive, so too do we,” said between people and their natural environment), exemplifies the idea that care for the environment, which encompasses living and nonliving elements in the natural system, will, in turn, lead to care for all occupants of that system, whether they be human or nonhuman (McGregor 2007 ). Relational thinking is also central to the Indigenous Andean concept of sumak kawsay , which roughly translates to “ buen vivir ” and “the good life.” Sumak kawsay encompasses ideas of what good living means, and it addresses the important role that nature–society interactions play in that good living. Because the Indigenous ontology that underlies it is inherently relational, the concept (unlike the ES framework) does not involve clear distinctions between nature and human society; it therefore also does not foreground either nature or humans (Villalba 2013 ). This means that sumak kawsay encompasses many of the concepts that CES addresses, such as living in harmony with nature, but without using a services metaphor. The same pattern exists in numerous other cultures (Diver et al. 2019 ). Recognition that the services framing is problematic is widespread, and scholars have suggested multiple alternatives (e.g., metaphors of a closed-loop system, stewardship, or a web of life; Raymond et al. 2013 ).
Closely connected to the idea that CES are reciprocal and relational is that they are often intertwined with long-term human–nature connections. In other words, many CES do not exist at a point in time but, instead, extend over periods or cycles. Therefore, to measure CES at one temporal point often does not capture their full meaning. Many CES, especially those associated with values other than recreation and aesthetics, often involve engagement of some duration. Long-term relationships can take multiple forms, and the CES concept allows for relationships that span the temporal spectrum (figure 2 ).
Spectrum of types of long-term engagement that people may have with place.
The importance of relationships and reciprocity in experiences of CES-related concepts has led to recent conversations in the sustainability literature about relational values (Muraca 2016 , Chan et al. 2018 , Himes and Muraca 2018 ). Instrumental framings of ES can clash with some concepts under the CES umbrella, because those concepts are not exactly and not always benefits that ecosystems provide to people (or, in NCP framings, impacts that ecosystems have on people). Spirituality, which is included in most typologies of CES, provides an example. Spirituality is a phenomenon that can be tightly intertwined with ecosystems, and it represents a crucial component of well-being for many people. However, it is rarely considered a benefit or contribution that nature provides to humans. This may be because phenomena such as spirituality, for many people, are “inherently relational: [They] are valued in the context of desired and actual relationships” (Chan et al. 2016 : 1464). The relational values concept creates conceptual space for values that are grounded in relationships and that are important to human well-being but that are not exactly benefits or contributions. It is important to note is that values that could be called relational values have been addressed in a variety of fields for decades and, in some cases, for centuries (Saxena et al. 2018 ). Burgeoning empirical and theoretical work under the relational values umbrella attempts to provide a meeting space and policy-relevant language for those ideas (see Chan et al. 2018 and the special issue it introduces).
To allow that CES are relational and involve reciprocity links naturally to acknowledgement of their dynamism. Studies on how CES may change in the absence of ecosystem change (e.g., through education or experience) are just emerging. Constructs closely related to CES and relational values (but not labeled as such) can change in a relatively short time (days to months) following educational initiatives (Britto dos Santos and Gould 2018 , Gould et al. 2018 ). Change in CES also occurs over historical and generational timescales. This often involves complex interactions of biophysical and social change; examples include changes in benefits from forests in the Mediterranean basin (Holmgren and Scheffer 2017 ) or from mangroves in Singapore (Thiagarajah et al. 2015 ). Longer-term dynamism is important to consider for at least two reasons: first, to better understand a context and its current state and, next, because changes in some CES may affect long-term goals of ecosystem management.
Complications arise when we recognize that CES may not always fit the service or benefit framing and can change independently of ecosystem change. Both characteristics pose additional challenges to inclusion of CES within ES analyses. Ways forward that acknowledge the complex realities inherent in CES can simultaneously honor these complexities and address issues of equity. One possibility would be to include more thorough consideration of the reciprocal relationships that underpin resource management in many places. To ignore such relationships risks imposition of outside ways of conceptualizing conservation. Another approach would be to better consider the nonecological factors that affect CES (e.g., timescales, extent of engagement, education). Increased attention to nonecological factors may enable more direct connections to decision-making by shedding light on how societal changes (e.g., a global pandemic) interact with CES, and particularly on equity-related concerns (e.g., how do CES support people during a pandemic, and how does that support vary?).
The methods used to elicit and characterize values influence what is shared (Chan et al. 2012b , Jax et al. 2013 ); the choice of method can obscure or make visible entire value systems (Turner et al. 2008 ). ES researchers, at least in the field's early stages, designed many findings to fit cost–benefit frameworks. The conclusions were therefore quantitative and sometimes monetary (e.g., Fisher et al. 2009 ). This can be problematic for CES, which are often difficult to describe and even more difficult to quantify. Quantitative, monetary values can be particularly inadequate to represent the perspectives of communities for which the language of ES may not resonate (Ernstson 2013 ). In Tarituba, Brazil, for example, local communities express value in ways that align poorly with ES language and categories (de Oliveira and Berkes 2014 ). To speak of fish or fishing-based lifestyles as a benefit does not make much sense; instead, people narrate the actions or occupations that allow them to access fish. Through stories, people express how fish are intimately connected with identity, cultural practices, and occupation. This example illuminates how elicitation methods that permit people to convey their relationships with nature in diverse ways may be necessary to capture diverse CES. Narrative-based approaches offer one such method; they allow participants to define and describe their experiences in their own terms. They also offer a way to connect CES to the rich theoretical foundations of diverse social science fields that are often obscured by economic, quantitative frameworks (Winthrop 2014 ).
Narrative can be central to how people understand and share nonmaterial relationships with ecosystems and, in particular, may help to understand the reciprocal, relational, and dynamic aspects of CES. The concept of narrative has hundreds of definitions, but most are similar to storytelling: “someone telling someone else that something has happened” (Smith 1981 : 232). Although scholars have not extensively explored the potential of narrative in the CES sphere, research in other fields suggests that it may serve as an effective method of expressing values. Below, we summarize this work from multiple fields and note its relevance to CES. We then present a few examples of CES research based on narrative.
An important reason to embrace narrative in CES research is that it can be central to fields that have justice as a guiding principle. Conflict resolution studies use narrative as a tool and suggest that narrative is powerful because it requires listening, is accessible, mobilizes new voices, and democratizes conversations (Senehi 2002 ). Critical feminist ethnographic methods from political science demonstrate how narrative can lead to more empathetic decision-making (Wiebe 2016 ). In critical race theory, narrative is a central tool for comprehending historical trauma and “opening a window onto ignored or alternative realities” (Delgado and Stefancic 2017 : 46). Narrative can be a particularly powerful and effective means to express deeply complex concepts such as identity and cultural heritage (Winthrop 2014 ). For these types of value especially, narrative can offer unique and crucial insight because it can convey profound meaning that is otherwise difficult to share. Peace and reconciliation commissions, as developed in South Africa and later widely implemented elsewhere, provide a prominent global example. These commissions foreground the importance of listening to stories of past trauma and have confronted injustice in many places. The relevance of this diverse past work to CES is obvious when one considers the ways that CES intertwine with historical trauma—notably colonialism and postcolonialism (which often cleave people–place relationships; Gould et al. 2014 )—and with nuanced concepts such as identity that is inseparable from place (Pascua et al. 2017 ).
The ES field has also employed narrative in multiple contexts, and at least one framework for CES analysis suggests the use of narrative (Chan et al. 2012b ). Three examples illustrate ways that CES research can employ narrative. The participants in watershed ES initiatives in the Cauca Valley, Colombia, use stories to explain why they participate in these programs. Their stories, which are deeply infused with CES such as identity and sense of place, suggest that these services strongly influence sustained participation (Meza Prado et al. 2018 ). A second example, from the United Kingdom, used storytelling to elicit personal stories of important experiences at marine sites; the participants’ shared stories then formed the basis of deliberative discussion about the meaning and value of marine protected areas (Kenter et al. 2016a ). A third example, from Germany, involves analysis of stories submitted to a contest about a natural reserve. The stories collectively reveal rich evidence of multiple CES, and also demonstrate that many CES “are explicitly connected to specific biophysical features” (Bieling 2014: 207).
People collect and share narratives in myriad ways. Many standard semistructured interview formats leave space for stories to emerge; other methods specifically target stories. Methods that target stories include StoryMaps, an ESRI platform that links maps, images, and text; creative writing; theater performances; and community storytelling events. These narrative-focused methods can aid both data collection and sharing of findings.
Narrative has many benefits but also has limitations. The most obvious one is that interpreting and analyzing narrative to distill values may require substantial time and specialized training. In addition, although the researchers’ identities affect the research process in many types of CES research, those impacts may be even more pronounced in studies that rely on narrative.
It is worthwhile to address these challenges because narrative approaches are an important way to address equity and justice concerns through CES research and practice. Earlier, we described the prominent role that narrative plays in multiple fields that foreground justice concerns. CES research, being highly interdisciplinary, can take cues from this justice-forward work to understand why narrative may contribute to advancing equity and how to engage with narrative in productive, enriching ways.
Connecting ecosystem functions and processes with human well-being is a central—yet still largely unrealized (Chan and Satterfield 2020 ; Mandle et al. 2020 )—goal of ES research. Indeed, one of the reasons ES analyses can be so powerful is that they are able to pinpoint biophysical elements and characterize how and by how much those elements relate to human well-being. One way researchers make these links is through the concept of ES providers—that is, “the component populations, species, functional groups (guilds), food webs or habitat types that collectively produce” ES (Kremen 2005 : 469). As this definition of ES providers indicates, connections between ES and biophysical attributes can be studied in many ways, from species specific to landscape encompassing. CES are no different in this regard, and therefore, we use the concept of ES providers to organize a subset of CES research that engages with biophysical attributes. We hope that this structure may help to reveal gaps and ways forward.
Despite the similar applicability of ES providers, CES obviously differ in many ways from other ES; their nonmateriality often necessitates distinct methods. One result of these different methods is that CES work often engages with specific biophysical attributes far less than most other ES research.
Although this biophysically specific CES research is rare, it is on the rise; researchers have recently related many types and scales of ES providers to CES. Figure 3 summarizes a selection of CES studies as they relate to various categories of providers. We describe a few of those studies, starting from the left side of the figure. Research in Hawai´i has documented how CES are intertwined with the presence and recognition of ´ aumākua , familial ancestor guardians who assume the physical form of individual nonhuman organisms (e.g., a particular shark, a specific owl; Pascua et al. 2017 ). Some studies have focused on the CES associated with particular species or taxa (Amberson et al. 2016 , Cortés-Avizanda et al. 2018 , Echeverri et al. 2019 ). In a few studies, ecological traits or attributes have been examined: One showed that species evenness and color diversity, but not species richness, predict the aesthetic appeal of wildflower displays (Graves et al. 2017 ), and another indicated that avian functional traits (e.g., diet, plumage color) can predict CES (Echeverri et al. 2019 ). One study showed a positive association between CES and biodiversity in grassland landscapes (King et al. 2017 ). Another described how socioecological landscape characteristics (views, accessibility, historical sites, woodland size) influence the delivery of CES (Ridding et al. 2018 ). Larger temporal and geographic scales were explored in other studies; they demonstrate how seasonal and landscape dynamics influence CES (Graves et al. 2017 , 2019 ) or how dryland systems, including their abiotic components such as geodiversity, provide CES (Teff-Seker and Orenstein 2019 ).
Types of ecosystem service providers addressed in CES research, with examples. The examples are associated with the following publications: 1Pascua et al. 2017 ; 2Amberson et al. 2016 ; 3Cortés-Avizanda et al. 2018 ; 4Graves et al. 2017 ; 5Echeverri et al. 2019 ; 6King et al. 2017 ; 7Graves et al. 2019 , 2017b; 8Plieninger et al. 2013 ; 9Keeler et al. 2015 ; 10Willis et al. 2018 ; 11Baulcomb et al. 2015 .
There may be multiple reasons why a specific biophysical focus is pertinent to a study context; sometimes authors make this explicit, and sometimes they do not. Interests in species-specific explorations, for instance, may be driven by ecological classifications (e.g., threatened and endangered species) or by local and cultural connections to a particular species (e.g., cultural keystone species, Garibaldi and Turner 2004 ). Many CES studies focus on larger-scale areas (e.g., a specific forest area or park); these may or may not constitute ES providers. The tendency to generalize on the ecological side is one distinction between research on CES and ES more generally: In CES research, ecological granularity is often much more coarse.
A small segment of researchers have explored how CES may change on the basis of a specific type of biophysical detail: the condition of the ES provider (as affected by, e.g., pollution or habitat modification). This work can span the range of ES providers, from specific organisms to landscapes. It asks the following question: How do different ecosystem conditions affect CES? As two examples, research demonstrates that harmful algal blooms in marine ecosystems decrease a suite of multiple CES (Willis et al. 2018 ) and that lakes with clearer water receive more visitors (Keeler et al. 2015 ). This work can add to research on how ecosystem condition affects ES generally (e.g., McLaughlin and Cohen 2013 ).
Another permutation of this frontier—that is, an approach that better links biophysical attributes but with a focus different than that of ES providers—relates to an improved connection between CES and material ES (because the latter tend to be more commonly and obviously connected to specific biophysical attributes). This work takes two forms. The first is inclusion of CES in broader ES assessments (Raudsepp-Hearne et al. 2010 , Bremer et al. 2018a , 2018b ). This inclusion brings CES into larger conversations about ES; it brings CES to the table alongside other ES. The second avenue to better connect CES with material ES goes a step further: Beyond presenting the two alongside one another, it explores potential causal relationships between material ES and CES. In some ways, this second avenue can be considered a meta-approach, because a material ES may itself be analogous to an ES provider. As one example, communities participating in the Ecuadorian Andes’ Socio Bosque conservation incentive program recognize the páramo (alpine tundra) as the source of water essential to their livelihoods. They also describe how these grasslands are deeply connected to community identity and culture, which demonstrates the links between material and nonmaterial values (Farley and Bremer 2017 ). It seems likely that some of the CES associated with the páramo draw power and importance from the crucial role played by that specific ecosystem in material livelihoods; that is, the provider of the CES is the material ES of water provision. Future research could explore this type of connection between particular material ES and particular CES (e.g., how might water-flow regulation relate to spirituality?).
A primary challenge of efforts to link biophysical attributes and CES is that these efforts must address two highly complex arenas: social preferences and values and ecosystems’ biophysical properties. To date, much CES-related research explores detail in only one of the two. Much research focused on CES has described and parsed nuance on the social side of that relationship but has minimally treated ecological attributes. Much current CES research that engages with ecological nuance, however, does the reverse: It uses holistically important or novel measures of ES providers but relatively simple or superficial measures for CES. For the most part, the work we present in this section aligns more closely with the second group: It engages with ecological nuance but less so with social nuance.
We perceive a need to develop approaches that capture increased nuance in both cultural and ecological attributes; indeed, doing so may open possibilities for CES research to address equity in novel ways. The reason that increased attention to biophysical attributes may address equity issues stems from the fact that different beneficiaries—that is, groups or individuals who perceive or experience CES in a particular way—may value biophysical attributes in different ways and to different degrees. To offer two extreme examples: A jogger may experience the same CES while exercising in a highly diverse native forest or a forest filled with invasive species, whereas a forager may experience dramatically different CES as a result of changes in spatial or temporal abundance of valued species. The forager's case is one of many possibilities: Biophysical attributes can affect a broad range of CES (e.g., those related to spirituality, ceremony, identity) in crucial ways. These impacts may be particularly important for communities that are highly aware of nuanced ecological condition (e.g., hunters, foragers, cultural practitioners). Specific biophysical attributes may also be especially relevant in and among Indigenous peoples and local communities who place high value on both human and nonhuman kinship bonds (Salmón 2000 ); in some such contexts, humanity and nature are less (or not) distinct, and biophysical features, conditions, and attributes may be just as important as human ones. The challenge is how to carefully and respectfully identify then monitor these connections. One approach is in emerging research on biocultural indicators, which capture aspects of linked biological and cultural systems (Sterling et al. 2017 ). Other potential pathways will likely include drawing on diverse methods, working closely with place-connected communities, and honoring Indigenous and local knowledge and worldviews.
Building on the promising work we describe in this section, we argue that scholars continue to improve the ability of CES to achieve that central goal of ES research: to understand how particular biophysical elements benefit human well-being. We also emphasize that this work should acknowledge its potential blind spots and complications and should strongly consider whether and how different knowledge systems and worldviews approach biophysical attributes (e.g., that those attributes may be inseparable from each other or social systems). To advance in this way may simultaneously achieve two goals: that CES research become more management-relevant and better able to address equity issues rooted in deep connections to ES providers, whether or not that particular term is used. This kind of increased attention to connections between biophysical attributes and CES may bring equity issues to the forefront in management and planning related to ethically complex issues—for example, important debates such as those around novel ecosystems (Burnett et al. 2019 ), or restoration strategies that are focused on biocultural goals rather than solely on native species (Winter et al. 2020 ).
To describe and value CES is complicated. However, without explicit attention to CES, the ideas they represent may be ignored in some decision-making circles. This omission can have important justice-related consequences (Maru et al. 2012 ). In this article, we emphasize how recent advances in CES research can address past deficiencies in the ES conceptual framework—particularly those that have failed to address or even have exacerbated structural inequalities and injustice.
An important question in many CES analyses is how they relate to decision-making. Links to decision-making are still nascent in many cases (Gould et al. 2019 ), and strengthening them will require intentionality from both researchers and decision-makers (Chan and Satterfield 2020 , Mandle et al. 2020 ). Researchers, to achieve that strengthening, must think creatively about how to work with decision-makers at various stages of the research process. One aspect of that collaboration—albeit one much less involved than sustained transdisciplinary collaboration—is to share findings in various formats and for various audiences. Flexibility is important because not all decision-making contexts function the same way, nor do they use the same forms of evidence. To spur ideas related to this aspect of collaboration with decision-makers, table 3 presents multiple examples of ways to share findings related to CES. Notably, many underscore the importance of sharing findings with participants as a precursor to broader dissemination. Just as researchers must make this conscious effort, decision-makers may need to reconsider the types of information they use. They also likely need to pay special attention, in the case of complex CES and their justice implications, to whose voices are included in value- or CES-elicitation processes and to the ways values are characterized.
Examples of ways to more broadly share findings from CES and CES-related research.
Way to share findings . | Example . | Where to find more information . |
---|---|---|
Websites that highlight community members active in ES or CES work | Suppliers on the Map shares experiences of upstream land managers, including local farmers and indigenous communities participating in a water fund in Colombia. Participants and staff narrate what drives participation in a program that offers in-kind (rather than monetary) payments for ecosystem services (e.g., home gardens). | |
Websites by communities, for communities | The Húýat website showcases the beauty and depth of Húýat's history, and the past, present, and future of the Heiltsuk people. On the basis of community-initiated research, ethnographic sources, and archival documents. | |
Community-based performances | Collaboration with local practitioners of hula to share research results related to CES connected to Hawaii's forests. A live Saturday night show attended by more than 300 community members. | ; Gould et al. |
Visual workshop summaries for community members | Community workshop summaries to share outcomes of a Hawai´i-based CES exploration, shared with all community participants. The plain-language summary documents focused primarily on visual content (workshop photos and codeveloped diagrams). | Researchers did not disseminate this output beyond the community participant audience (community members were invited to share the summaries as desired; Pascua et al. ). |
Short films that highlight places and cultural stories | Compelling video portrayals of the intimate relationship between people and place. Videos are based on interviews and involve collaboration between artists and academics. | |
Aggregate individual maps to share with community and discuss | On the basis of individual surveys, created heat maps that demonstrate aggregate spatial patterns of cultural importance. These heat maps provided fodder for group discussion about CES. | Fish et al. |
Community mapping projects that produce widely distributed maps or booklets | The New Social Cartography of the Amazon Project (PNCSA) explores processes of territorialization. Through the project, several communities produce “social mapping… about their own territories [which] translates this strong environmental consciousness and its effects into cartographic representations.” | |
Collaborative, mixed-media storytelling | Collaboratively created mixed-media stories that interrogate hegemonic stereotypes and narratives, create space for policy dialogue, and cocreate alternative counternarratives with affected communities. | |
StoryMaps that highlight histories of places | ´Ike Wai researchers and the Institute for Hawaiian Language Research and Translation created StoryMaps including translations of Hawaiian language newspapers in two areas that have become focal points for water research in Hawai´i. | Na¯ Ho´onanea: = a56b71ff1eb446b29c4d750f71c50daa Na¯ Hunahuna: = 77d250737aac4096bfd745b904320787 Pu´uloa: = 5dac7448c1074113bd28dba4637308dd |
Way to share findings . | Example . | Where to find more information . |
---|---|---|
Websites that highlight community members active in ES or CES work | Suppliers on the Map shares experiences of upstream land managers, including local farmers and indigenous communities participating in a water fund in Colombia. Participants and staff narrate what drives participation in a program that offers in-kind (rather than monetary) payments for ecosystem services (e.g., home gardens). | |
Websites by communities, for communities | The Húýat website showcases the beauty and depth of Húýat's history, and the past, present, and future of the Heiltsuk people. On the basis of community-initiated research, ethnographic sources, and archival documents. | |
Community-based performances | Collaboration with local practitioners of hula to share research results related to CES connected to Hawaii's forests. A live Saturday night show attended by more than 300 community members. | ; Gould et al. |
Visual workshop summaries for community members | Community workshop summaries to share outcomes of a Hawai´i-based CES exploration, shared with all community participants. The plain-language summary documents focused primarily on visual content (workshop photos and codeveloped diagrams). | Researchers did not disseminate this output beyond the community participant audience (community members were invited to share the summaries as desired; Pascua et al. ). |
Short films that highlight places and cultural stories | Compelling video portrayals of the intimate relationship between people and place. Videos are based on interviews and involve collaboration between artists and academics. | |
Aggregate individual maps to share with community and discuss | On the basis of individual surveys, created heat maps that demonstrate aggregate spatial patterns of cultural importance. These heat maps provided fodder for group discussion about CES. | Fish et al. |
Community mapping projects that produce widely distributed maps or booklets | The New Social Cartography of the Amazon Project (PNCSA) explores processes of territorialization. Through the project, several communities produce “social mapping… about their own territories [which] translates this strong environmental consciousness and its effects into cartographic representations.” | |
Collaborative, mixed-media storytelling | Collaboratively created mixed-media stories that interrogate hegemonic stereotypes and narratives, create space for policy dialogue, and cocreate alternative counternarratives with affected communities. | |
StoryMaps that highlight histories of places | ´Ike Wai researchers and the Institute for Hawaiian Language Research and Translation created StoryMaps including translations of Hawaiian language newspapers in two areas that have become focal points for water research in Hawai´i. | Na¯ Ho´onanea: = a56b71ff1eb446b29c4d750f71c50daa Na¯ Hunahuna: = 77d250737aac4096bfd745b904320787 Pu´uloa: = 5dac7448c1074113bd28dba4637308dd |
Note: The examples primarily encompass approaches and outputs that stem from collaborative, community-based research projects codesigned with community members.
The issues that CES address are weighty and call for transdisciplinary problem-solving. We hope that CES research can provide flexible, powerful avenues to address equity-related concerns that often accompany these issues. We suggest that in order to reach its full potential, CES work should continue and deepen work aligned with the five frontiers described above. These frontiers suggest that CES research, if it maintains its connections with diverse methodologies and epistemologies, may help to strengthen ES approaches, both in general and as they relate to issues of justice and equity (table 1 ). In table 2 , we offer future research questions for each of the frontiers. We suggest and hope that CES work that builds on these frontiers, by answering the questions in table 2 and many others, can include diverse views and voices. By continuing to develop along these frontiers, CES work may begin to address social power relations, representational justice, and other equity concerns that surround and infuse ES research and practice (Berbés-Blázquez et al. 2016 ).
We are grateful for the many people and places that have shared time and ideas with us and with the hundreds of other people conducting CES-related research. We also thank the Natural Capital Project Symposium for hosting the session that inspired this paper.
Rachelle Gould ( [email protected] ) is an assistant professor in the Sustainability and Global Equity Cluster at the University of Vermont, in Burlington; she is a faculty member of the Rubenstein School of Environment and Resources and the Environmental Program and is a fellow of the Gund Institute for the Environment, also in Burlington, Vermont. Leah Bremer is an environmental science and policy specialist at the University of Hawai´i Economic Research Organization and Water Resources Research Center, in Honolulu, Hawai'i; she is also a cooperating faculty member with the Department of Geography and Environment, the Department of Natural Resources and Environmental Management, and the Biocultural Initiative of the Pacific and is an affiliate of the Gund Institute for the Environment, at the University of Vermont, in Burlington, and a research associate with Fundación Cordillera Tropical in Ecuador, in Cuenca. Pua´ala Pascua is a biodiversity scientist and a biocultural specialist at the Center for Biodiversity and Conservation of the American Museum of Natural History, in New York, New York. Kelly Meza Prado is a public health student at the London School of Hygiene and Tropical Medicine, at the University of London, in London, England, and was previously a researcher at the University of Minnesota, in Minneapolis, and with the Natural Capital Project, at Stanford University, in Stanford, California.
Adamowicz W , Beckley T , Hatton Macdonald D , Just L , Luckert M , Murray E , Phillips W . 1998 . In search of forest resource values of Indigenous peoples: Are nonmarket valuation techniques Applicable? Society and Natural Resources 11 : 51 – 66 .
Google Scholar
Amberson S , Biedenweg K , James J , Christie P . 2016 . “The Heartbeat of Our People”: Identifying and measuring how salmon influences quinault tribal well-being . Society and Natural Resources 29 : 1389 – 1404 .
Bachika R , Schulz MS. 2011 . Values and culture in the social shaping of the future . Current Sociology 59 : 107 – 118 .
Baulcomb C , Fletcher R , Lewis A , Akoglu E , Robinson L , von Almen A , Hussain S , Glenk K . 2015 . A pathway to identifying and valuing cultural ecosystem services: An application to marine food webs . Ecosystem Services 11 : 128 – 139 .
Berbés-Blázquez M , González JA , Pascual U . 2016 . Towards an ecosystem services approach that addresses social power relations . Current Opinion in Environmental Sustainability, Sustainability Science 19 : 134 – 143 .
Bickerstaff K , Walker G. 2005 . Shared visions, unholy alliances: Power, governance and deliberative processes in local transport planning . Urban Studies 42 : 2123 – 2144 .
Birling C. 2014 . Cultural ecosystem services as revealed through short stories from residents of the swabian Alb (Germany) . Ecosystem Services 8 : 207 – 215 .
Bremer LL , Falinski K , Ching C , Christopher Wada A , Kimberly Burnett M , Kukea-Shultz K , Reppun N , Chun G , Kirsten Oleson L , Ticktin T . 2018a . Biocultural restoration of traditional agriculture: Cultural, environmental, and economic outcomes of lo'i kalo restoration in He'eia, O'ahu . Sustainability 10 : 4502 .
Bremer LL et al. 2018b . Bringing multiple values to the table: Assessing future land-use and climate change in North Kona, Hawai'i . Ecology and Society 23 : 33 .
Britto dos Santos N , Gould RK . 2018 . Can relational values be developed and changed? investigating relational values in the environmental education literature . Current Opinion in Environmental Sustainability 30 : 124 – 131 .
Brown G , Fagerholm N. 2015 . Empirical PPGIS/PGIS mapping of ecosystem services: A review and evaluation . Ecosystem Services 13 : 119 – 133 .
Burnett KM et al. 2019 . Restoring to the future: Environmental, cultural, and management trade-offs in historical versus hybrid restoration of a highly modified ecosystem . Conservation Letters 12 : e12606 .
Bull JW et al. 2016 . Strengths, weaknesses, opportunities, and threats: A SWOT analysis of the ecosystem services framework . Ecosystem Services 17 : 99 – 111 .
Büscher B , Sullivan S , Neves K , Igoe J , Brockington D . 2012 . Towards a synthesized critique of neoliberal biodiversity conservation . Capitalism Nature Socialism 23 : 4 – 30 .
Chan KM , Goldstein J , Satterfield T , Hannahs N , Kikiloi K , Naidoo R , Vadeboncoeur N , Woodside U . 2011 . Cultural services and non-use values . Pages 206 – 228 in Kareiva P , Tallis H , Ricketts TH , Daily GC , Polasky S , eds. Natural Capital: Theory and Practice of Mapping Ecosystem Services . Oxford University Press .
Google Preview
Chan KMA , Guerry AD , Balvanera P , Klain S , Satterfield T , Basurto X , Bostrom A , Chuenpagdee R , Gould RK , Halpern BS . 2012a . Where are cultural and social in ecosystem services? a framework for constructive engagement . BioScience 62 : 744 – 756 .
Chan KMA , Satterfield T , Goldstein J . 2012b . Rethinking ecosystem services to better address and navigate cultural values . Ecological Economics 74 : 8 – 18 .
Chan KMA , Satterfield T. 2020 . The maturation of ecosystem services: Social and policy research expands, but whither biophysically informed valuation? People and Nature . Online first .
Chan KMA et al. 2016 . Why protect nature? Rethinking values and the environment . Proceedings of the National Academy of Sciences 113 : 1462 – 1465 .
Chan KMA , Gould RK , Pascual U . 2018 . Relational values: What are they, and what's the fuss about? Current Opinion in Environmental Sustainability 35 : A1 – A7 .
Ching C. 2018 . Exploring the Underlying Drivers of the Ecosystem Services Offered in the Wetland of He'eia . Masters thesis , University of Hawai'i .
Comberti C , Thornton TF , Wyllie de Echeverria V , Patterson T . 2015 . Ecosystem services or services to ecosystems? Valuing cultivation and reciprocal relationships between humans and ecosystems . Global Environmental Change 34 : 247 – 262 .
Cortés-Avizanda A , Martín-López B , Ceballos O , Pereira HM . 2018 . Stakeholders perceptions of the endangered Egyptian vulture: Insights for conservation . Biological Conservation 218 : 173 – 180 .
Delgado R , Stefancic J. 2017 . Critical Race Theory: An Introduction . New York University Press .
Dempsey J , Robertson MM. 2012 . Ecosystem services: Tensions, impurities, and points of engagement within neoliberalism . Progress in Human Geography 36 : 758 – 779 .
Dewey J. 2007 . Experience and Education . Simon and Schuster .
de Groot R et al. 2018 . Ecosystem Services are Nature's Contributions to People . Science 359 .
De Vreese R , Van Herzele A , Dendoncker N , Fontaine CM , Leys M . 2019 . Are stakeholders’ social representations of nature and landscape compatible with the ecosystem service concept? Ecosystem Services 37 : 100911 .
Díaz S et al. 2018 . Assessing nature's contributions to people . Science 359 : 270 .
Diver S , Vaughan M , Baker-Médard M , Lukacs H . 2019 . Recognizing “reciprocal relations” to restore community access to land and water . International Journal of the Commons 13 : 400 – 429 .
Echeverri A , Naidoo R , Karp DS , Chan KMA , Zhao J . 2019 . Iconic manakins and despicable grackles: Comparing cultural ecosystem services and disservices across stakeholders in Costa Rica . Ecological Indicators 106 : 105454 .
Edwards DM , Collins TM , Goto R . 2016 . An arts-led dialogue to elicit shared, plural and cultural values of ecosystems . Ecosystem Services 21 : 319 – 328 .
Ernstson H. 2013 . The social production of ecosystem services: A framework for studying environmental Justice and ecological complexity in urbanized landscapes . Landscape and Urban Planning 109 : 7 – 17 .
Farley KA , Bremer LL. 2017 . “Water is life”: Local perceptions of Páramo grasslands and land management strategies associated with payment for ecosystem services . Annals of the American Association of Geographers 107 : 371 – 381 .
Fish RD 2011 . Environmental decision making and an ecosystems approach: Some challenges from the perspective of social science . Progress in Physical Geography 35 : 671 – 680 .
Fish R , Church A , Willis C , Winter M , Tratalos JA , Haines-Young R , Potschin M . 2016 . Making space for cultural ecosystem services: Insights from a study of the UK nature improvement initiative . Ecosystem Services 21 : 329 – 343 .
Fisher B , Kerry Turner R , Morling P . 2009 . Defining and classifying ecosystem services for decision making . Ecological Economics 68 : 643 – 653 .
Garibaldi A , Turner N. 2004 . Cultural keystone species: Implications for ecological conservation and restoration . Ecology and Society 9 : 1 .
Gould RK , Lincoln NK. 2017 . Expanding the suite of cultural ecosystem services to include ingenuity, perspective, and life teaching . Ecosystem Services 25 : 117 – 27 .
Gould RK , Ardoin NM , Woodside U , Satterfield T , Hannahs N , Daily GC . 2014 . The forest has a story: Cultural ecosystem services in Kona, Hawai'i . Ecology and Society 19 : 55 .
Gould RK , Klain SC , Ardoin NM , Satterfield T , Woodside U , Hannahs N , Daily GC , Chan KM . 2015 . A protocol for eliciting nonmaterial values through a cultural ecosystem services frame: Analyzing cultural ecosystem services . Conservation Biology 29 : 575 – 586 .
Gould RK , Coleman K , Gluck SB . 2018 . Exploring dynamism of cultural ecosystems services through a review of environmental education research . Ambio 47 : 1 – 15 . https://doi.org/10.1007/s13280-018-1045-8 .
Gould RK , Morse JW , Adams AB . 2019 . Cultural ecosystem services and decision-making: How researchers describe the applications of their work . People and Nature 1 : 457 – 475 .
Graves RA , Pearson SM , Turner MG . 2017 . Species richness alone does not predict cultural ecosystem service value . Proceedings of the National Academy of Sciences 114 : 3774 – 3779 .
Graves RA , Pearson SM , Turner MG . 2019 . Effects of bird community dynamics on the seasonal distribution of cultural ecosystem services . Ambio 48 : 280 – 292 .
Guerry AD et al. 2015 . Natural capital and ecosystem services informing decisions: From promise to practice . Proceedings of the National Academy of Sciences 112 : 7348 .
Heland J , Folke C . 2014 . A social contract with the ancestors: Culture and ecosystem services in southern Madagascar . Global Environmental Change 24 : 251 – 264 .
Hermes J , Van Berkel D , Burkhard B , Plieninger T , Fagerholm N , von Haaren C , Albert C . 2018 . Assessment and valuation of recreational ecosystem services of landscapes . Assessment and Valuation of Recreational Ecosystem Services 31 : 289 – 295 .
Himes A , Muraca B. 2018 . Relational values: The key to pluralistic valuation of ecosystem services . Current Opinion in Environmental Sustainability 35 : 1 – 7 .
Hirons M , Comberti C , Dunford R . 2016 . Valuing cultural ecosystem services . Annual Review of Environment and Resources 41 : 545 – 574 . https://doi.org/10.1146/annurev-environ-110615-085831 .
Holmgren M , Scheffer M. 2017 . To tree or not to tree: Cultural views from ancient Romans to modern ecologists . Ecosystems 20 : 62 – 68 .
[IPBES] Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services . 2019 . Summary for Policymakers of the Global Assessment Report on Biodiversity and Ecosystem Services of the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services . IPBES .
James S. 2016 . Ecosystem services and the value of places . Ethical Theory and Moral Practice 19 : 101 – 113 .
Jax K et al. 2013 . Ecosystem services and ethics . Ecological Economics 93 : 260 – 268 .
Kaplowitz MD , Hoehn J . 2001 . Do focus groups and individual interviews reveal the same information for natural resource valuation? Ecological Economics 36 : 237 – 247 .
Keeler BL , Wood SA , Polasky S , Kling C , Filstrup CT , Downing JA . 2015 . Recreational demand for clean water: Evidence from geotagged photographs by visitors to lakes . Frontiers in Ecology and the Environment 13 : 76 – 81 .
Kenter JO , Hyde T , Christie M , Fazey I . 2011 . The importance of deliberation in valuing ecosystem services in developing countries: Evidence from the Solomon Islands . Global Environmental Change 21 : 505 – 521 .
Kenter JO et al. 2015 . What are shared and social values of ecosystems? Ecological Economics 111 : 86 – 99 .
Kenter JO , Jobstvogt N , Watson V , Irvine KN , Christie M , Bryce R . 2016a . The impact of information, value-deliberation and group-based decision-making on values for ecosystem services: Integrating deliberative monetary valuation and storytelling . Ecosystem Services 21 : 270 – 290 .
Kenter JO et al. 2016b . Shared values and deliberative valuation: Future directions . Ecosystem Services 21 : 358 – 371 .
Kenter JO , Reed MS , Fazey I . 2016 . The deliberative value formation model . Ecosystem Services 21 : 194 – 207 .
Kenter JO. 2018 . IPBES: Don't throw out the baby whilst keeping the bathwater; Put people's values central, not nature's contributions . Ecosystem Services 33 : 40 – 43 .
Kenter JO et al. 2019 . Loving the mess: Navigating diversity and conflict in social values for sustainability . Sustainability Science 14 : 1439 – 1461 .
Kimmerer R. 2013 . Braiding Sweetgrass: Indigenous Wisdom, Scientific Knowledge and the Teachings of Plants . Milkweed Editions .
King HP , Morris J , Graves A , Bradbury RB , McGinlay J , Bullock JM . 2017 . Biodiversity and cultural ecosystem benefits in lowland landscapes in southern England . Journal of Environmental Psychology 53 : 185 – 197 .
Kirchhoff T. 2019a . Abandoning the concept of cultural ecosystem services, or against natural–scientific imperialism . BioScience 69 : 220 – 227 .
Kirchhoff T. 2019b . Concepts, not words, are at the core of science and of the ecosystem services framework . BioScience 69 : 585 – 586 .
Kremen C. 2005 . Managing ecosystem services: What do we need to know about their ecology? Ecology Letters 8 : 468 – 479 .
Lo AY , Spash CL. 2013 . Deliberative monetary valuation: In search of a democratic and value plural approach to environmental policy . Journal of Economic Surveys 27 : 768 – 789 .
Mandle L , Shields-Estrada A , Chaplin-Kramer R , Mitchell MGE , Bremer LL , Gourevitch JD , Hawthorne P , Johnson JA , Robinson BE , Smith JR , Sonter LJ , Verutes GM , Vogl AL , Daily GC , Ricketts TH . 2020 . Increasing decision relevance of ecosystem service science . Nature Sustainability. Online first .
Markus HR , Conner A. 2014 . Clash! How to Thrive in a Multicultural World . Penguin .
Maru YT , Fletcher CS , Chewings VH . 2012 . A synthesis of current approaches to traps is useful but needs rethinking for indigenous disadvantage and poverty research . Ecology and Society 17 : 7 .
McLaughlin DL , Cohen MJ 2013 . Realizing ecosystem services: Wetland hydrologic function along a gradient of ecosystem condition . Ecological Applications 23 : 1619 – 1631 .
McDermott M , Mahanty S , Schreckenberg K . 2013 . Examining equity: A multidimensional framework for assessing equity in payments for ecosystem services . Environmental Science and Policy 33 : 416 – 427 .
McGregor D. 2007 . Nā Kua’āina: Living Hawaiian Culture . University of Hawai'i Press .
Meza Prado AK , Vargas M , Bremer L , Brauman K , Hoyos Villada F . 2018 . Putting suppliers on the map: The stories of people conserving water upstream . Suppliers on the Map. http://suppliersonthemap.org/ .
Millennium Ecosystem Assessment . 2005 . Ecosystems and Human Well-Being . Island Press .
Miller B , Soulé ME , Terborgh J . 2014 . “New conservation” or surrender to development? Animal Conservation 17 : 509 – 515 .
Morgan TeKKB , Fa´aui TN . 2018 . Empowering indigenous voices in disaster response: Applying the mauri model to New Zealand's worst environmental maritime disaster . European Journal of Operational Research 268 : 984 – 995 .
Muraca B. 2016 . Relational values: A whiteheadian alternative for environmental philosophy and global environmental justice . Balkan Journal of Philosophy 8 : 19 – 38 .
Oliveira LEC , Berkes F. 2014 . What value São Pedro's procession? Ecosystem services from local people's perceptions . Ecological Economics 107 : 114 – 121 .
Orchard-Webb J , Kenter JO , Bryce R , Church A . 2016 . Deliberative democratic monetary valuation to implement the ecosystem approach . Ecosystem Services 21 : 308 – 318 .
Parks S , Gowdy J. 2013 . What have economists learned about valuing nature? A review essay . Ecosystem Services 3 : e1 – e10 .
Pascua P , McMillen H , Ticktin T , Vaughan M , Winter KB . 2017 . Beyond services: A process and framework to incorporate cultural, genealogical, place-based, and indigenous relationships in ecosystem service assessments . Ecosystem Services 26 : 465 – 475 .
Pascual U , Phelps J , Garmendia E , Brown K , Corbera E , Martin A , Gomez-Baggethun E , Muradian R . 2014 . Social equity matters in payments for ecosystem services . BioScience 64 : 1027 – 1036 .
Plieninger T , Dijks S , Oteros-Rozas E , Bieling C . 2013 . Assessing, mapping, and quantifying cultural ecosystem services at community level . Land Use Policy 33 : 118 – 129 .
Ranger S , Kenter JO , Bryce R , Cumming G , Dapling T , Lawes E , Richardson PB . 2016 . Forming shared values in conservation management: An interpretive-deliberative-democratic approach to including community voices . Ecosystem Services 21 : 344 – 357 .
Raudsepp-Hearne C , Peterson GD , Bennett EM . 2010 . Ecosystem service bundles for analyzing tradeoffs in diverse landscapes . Proceedings of the National Academy of Sciences 107 : 5242 – 5247 .
Raymond CM , Singh GG , Benessaiah K , Bernhardt JR , Levine J , Nelson H , Turner NJ , Norton B , Tam J , Chan KMA . 2013 . Ecosystem services and beyond: Using multiple metaphors to understand human-environment relationships . BioScience 63 : 536 – 546 .
Raymond CM , Kenter JO , Plieninger T , Turner NJ , Alexander KA . 2014 . Comparing instrumental and deliberative paradigms underpinning the assessment of social values for cultural ecosystem services . Ecological Economics 107 : 145 – 156 .
Reed M , Evely AC , Cundill G , Fazey IRA , Glass J , Laing A , Newig J , Parrish B , Prell C , Raymond C . 2010 . What is social learning? Ecology and Society 15 ( 4 ): r1 .
Ridding LE , Redhead JW , Oliver TH , Schmucki R , McGinlay J , Graves AR , Morris J , Bradbury RB , King H , Bullock JM . 2018 . The importance of landscape characteristics for the delivery of cultural ecosystem services . Journal of Environmental Management 206 : 1145 – 1154 .
Russell R , Guerry AD , Balvanera P , Gould RK , Basurto X , Chan K , Klain S , Levine J , Tam J . 2013 . Humans and nature: How knowing and experiencing nature affect well-being . Annual Review of Environment and Resources 38 : 473 – 502 .
Salmón E. 2000 . Kincentric ecology: Indigenous perceptions of the human–nature relationship . Ecological Applications 10 : 1327 – 1332 .
Satz D et al. 2013 . The challenges of incorporating cultural ecosystem services into environmental assessment . Ambio 42 : 675 – 684 .
Saxena AK , Chatti D , Overstreet K , Dove MR . 2018 . From moral ecology to diverse ontologies: Relational values in human ecological research, past, and present . Current Opinion in Environmental Sustainability 35 : 54 – 60 . https://doi.org/10.1016/j.cosust.2018.10.021 .
Schaubroeck T . 2019 . The concept of cultural ecosystem services should not be abandoned . BioScience 69 : 585 – 585 .
Schell CJ , Guy C , Shelton DS , Campbell-Staton SC , Sealey BA , Lee DN , Harris NC . 2020 . Recreating Wakanda by promoting Black excellence in ecology and evolution . Nature Ecology and Evolution. doi:10.1038/s41559-020-1266-7
Senehi J. 2002 . Constructive storytelling: A peace process . Peace and Conflict Studies 9 : 3 .
Shackleton CM , Ruwanza S , Sanni GS , Bennett S , De Lacy P , Modipa R , Mtati N , Sachikonye M , Thondhlana G . 2016 . Unpacking Pandora's box: Understanding and categorising ecosystem disservices for environmental management and human wellbeing . Ecosystems 19 : 587 – 600 .
Simon D , Krawczyk DC , Bleicher A , Holyoak KJ . 2008 . The transience of constructed preferences . Journal of Behavioral Decision Making 21 : 1 – 14 .
Smith BH. 1981 . Narrative version, narrative theories . Pages 213 – 236 in Thomas Mitchell WJ , Thomas J , eds. On Narrative . University of Chicago Press .
Sterling EJ et al. 2017 . Biocultural approaches to well-being and sustainability indicators across scales . Nature Ecology and Evolution 1 : 1798 – 1806 .
Teff-Seker Y , Orenstein DE. 2019 . The “desert experience”: Evaluating the cultural ecosystem services of drylands through walking and focusing . People and Nature 1 : 234 – 248 .
Thiagarajah J , Wong SKM , Richards DR , Friess DA . 2015 . Historical and contemporary cultural ecosystem service values in the rapidly urbanizing city state of Singapore . Ambio 44 : 666 – 777 .
Turner N , Gregory R , Brooks C , Failing L , Satterfield T . 2008 . From invisibility to transparency: Identifying the implications . Ecology and Society 13 : 7 .
University of Hawai´i . 2018 . Kūlana Noi´i . Hawai'I Sea Grant. http://seagrant.soest.hawaii.edu/wp-content/uploads/2018/06/Kulana-Noii-low-res-web.pdf .
van Riper CJ , Landon AC , Kidd S , Bitterman P , Fitzgerald LA , Granek EF , Ibarra S , Iwaniec D , Raymond CM , Toledo D . 2017 . Incorporating sociocultural phenomena into ecosystem-service valuation: The importance of critical pluralism . BioScience 67 : 233 – 244 .
von Döhren P , Haase D . 2015 . Ecosystem disservices research: A review of the state of the art with a focus on cities . Ecological Indicators 52 : 490 – 497 .
Villalba U. 2013 . Buen vivir versus development: A paradigm shift in the Andes? Third World Quarterly 34 : 1427 – 1442 .
Wals AEJ 2007 . Social Learning towards a Sustainable World: Principles, Perspectives, and Praxis . Wageningen Academic.
Wiebe SM. 2016 . Everyday Exposure: Indigenous Mobilization and Environmental Justice in Canada's Chemical Valley . University of British Columbia Press .
Wilburn E. 2017 . Voices from the Field: Participant Perspectives on Growth and Sustainability Opportunities for Water Producer Projects . Natural Capital Project.
Willis C , Papathanasopoulou E , Russel D , Artioli Y . 2018 . Harmful algal blooms: The impacts on cultural ecosystem services and human well-being in a case study setting, Cornwall, UK . Marine Policy 97 : 232 – 238 .
Wilson MA , Howarth RB 2002 . Discourse-based valuation of ecosystem services: Establishing fair outcomes through group deliberation . Ecological Economics 41 : 431 – 443 .
Winter KB , Ticktin T , Quazi SA . 2020 . Biocultural restoration in Hawai´i also achieves core conservation goals . Ecology and Society 25 : 26 .
Winthrop RH 2014 . The strange case of cultural services: Limits of the ecosystem services paradigm . Ecological Economics 108 : 208 – 214 .
Month: | Total Views: |
---|---|
November 2020 | 65 |
December 2020 | 42 |
January 2021 | 66 |
February 2021 | 32 |
March 2021 | 16 |
April 2021 | 9 |
May 2021 | 16 |
June 2021 | 12 |
July 2021 | 12 |
August 2021 | 6 |
September 2021 | 9 |
October 2021 | 9 |
November 2021 | 12 |
December 2021 | 15 |
January 2022 | 7 |
February 2022 | 47 |
March 2022 | 46 |
April 2022 | 42 |
May 2022 | 36 |
June 2022 | 46 |
July 2022 | 33 |
August 2022 | 25 |
September 2022 | 77 |
October 2022 | 67 |
November 2022 | 60 |
December 2022 | 113 |
January 2023 | 36 |
February 2023 | 31 |
March 2023 | 48 |
April 2023 | 48 |
May 2023 | 44 |
June 2023 | 29 |
July 2023 | 31 |
August 2023 | 24 |
September 2023 | 43 |
October 2023 | 39 |
November 2023 | 42 |
December 2023 | 83 |
January 2024 | 45 |
February 2024 | 26 |
March 2024 | 87 |
April 2024 | 104 |
May 2024 | 61 |
June 2024 | 45 |
July 2024 | 71 |
August 2024 | 35 |
Citing articles via.
Oxford University Press is a department of the University of Oxford. It furthers the University's objective of excellence in research, scholarship, and education by publishing worldwide
Sign In or Create an Account
This PDF is available to Subscribers Only
For full access to this pdf, sign in to an existing account, or purchase an annual subscription.
This thesis explores the relationship between and the impact of cultural ecosystem services on resilience planning by examining public spaces in San Antonio, Texas. Existing studies have recognized that evaluating cultural ecosystem services is challenging, but continued research as well as the development and testing of new methods are necessary to enhance our understanding. To support this aim, this thesis utilized participant observation and an inductive research approach to examine how cultural ecosystem services – the intangible benefits that communities gain from their natural environments – influence levels of social interaction and social cohesion. Three public urban green spaces in San Antonio were selected for observation because they function as spaces for cultural engagement and social resilience in the city. The findings of this study indicate that cultural ecosystem services are invaluable to fostering social cohesion and greater levels of social interaction in public spaces. Further, mapping observations of use and behavior from each of the three selected public green spaces coupled with historical research reveal the extent to which planning, and design interventions can influence cultural ecosystem services, the number of people engaging with them, and the who those people are in a general sense. Although it was not possible for this thesis, future studies should employ post-observation interviews with individuals making use of public green spaces to enrich and contextualize the observational data.
1_Van_Brian_2024_MUEP.pdf
Uploaded: May 09, 2024
Downloads: 81
2_Van_Brian_2024_MUEP.png
Downloads: 13
3_Van_Brian_2024_MUEP.png
Downloads: 15
4_Van_Brian_2024_MUEP.png
5_Van_Brian_2024_MUEP.png
6_Van_Brian_2024_MUEP.png
Downloads: 11
7_Van_Brian_2024_MUEP.png
Downloads: 12
8_Van_Brian_2024_MUEP.png
9_Van_Brian_2024_MUEP.png
Downloads: 21
10_Van_Brian_2024_MUEP.png
Downloads: 16
11_Van_Brian_2024_MUEP.png
12_Van_Brian_2024_MUEP.png
13_Van_Brian_2024_MUEP.png
14_Van_Brian_2024_MUEP.png
Downloads: 10
15_Van_Brian_2024_MUEP.png
16_Van_Brian_2024_MUEP.png
17_Van_Brian_2024_MUEP.png
18_Van_Brian_2024_MUEP.png
19_Van_Brian_2024_MUEP.png
20_Van_Brian_2024_MUEP.png
Innovation clinic—significant achievements for 2023-24.
The Innovation Clinic continued its track record of success during the 2023-2024 school year, facing unprecedented demand for our pro bono services as our reputation for providing high caliber transactional and regulatory representation spread. The overwhelming number of assistance requests we received from the University of Chicago, City of Chicago, and even national startup and venture capital communities enabled our students to cherry-pick the most interesting, pedagogically valuable assignments offered to them. Our focus on serving startups, rather than all small- to medium-sized businesses, and our specialization in the needs and considerations that these companies have, which differ substantially from the needs of more traditional small businesses, has proven to be a strong differentiator for the program both in terms of business development and prospective and current student interest, as has our further focus on tackling idiosyncratic, complex regulatory challenges for first-of-their kind startups. We are also beginning to enjoy more long-term relationships with clients who repeatedly engage us for multiple projects over the course of a year or more as their legal needs develop.
This year’s twelve students completed over twenty projects and represented clients in a very broad range of industries: mental health and wellbeing, content creation, medical education, biotech and drug discovery, chemistry, food and beverage, art, personal finance, renewable energy, fintech, consumer products and services, artificial intelligence (“AI”), and others. The matters that the students handled gave them an unparalleled view into the emerging companies and venture capital space, at a level of complexity and agency that most junior lawyers will not experience until several years into their careers.
While the Innovation Clinic’s engagements are highly confidential and cannot be described in detail, a high-level description of a representative sample of projects undertaken by the Innovation Clinic this year includes:
More information regarding other types of transactional projects that we typically take on can be found here .
Thanks to another generous gift from Douglas Clark, ’89, and managing partner of Wilson, Sonsini, Goodrich & Rosati, we were able to operationalize the second Innovation Trek over Spring Break 2024. The Innovation Trek provides University of Chicago Law School students with a rare opportunity to explore the innovation and venture capital ecosystem in its epicenter, Silicon Valley. The program enables participating students to learn from business and legal experts in a variety of different industries and roles within the ecosystem to see how the law and economics principles that students learn about in the classroom play out in the real world, and facilitates meaningful connections between alumni, students, and other speakers who are leaders in their fields. This year, we took twenty-three students (as opposed to twelve during the first Trek) and expanded the offering to include not just Innovation Clinic students but also interested students from our JD/MBA Program and Doctoroff Business Leadership Program. We also enjoyed four jam-packed days in Silicon Valley, expanding the trip from the two and a half days that we spent in the Bay Area during our 2022 Trek.
The substantive sessions of the Trek were varied and impactful, and enabled in no small part thanks to substantial contributions from numerous alumni of the Law School. Students were fortunate to visit Coinbase’s Mountain View headquarters to learn from legal leaders at the company on all things Coinbase, crypto, and in-house, Plug & Play Tech Center’s Sunnyvale location to learn more about its investment thesis and accelerator programming, and Google’s Moonshot Factory, X, where we heard from lawyers at a number of different Alphabet companies about their lives as in-house counsel and the varied roles that in-house lawyers can have. We were also hosted by Wilson, Sonsini, Goodrich & Rosati and Fenwick & West LLP where we held sessions featuring lawyers from those firms, alumni from within and outside of those firms, and non-lawyer industry experts on topics such as artificial intelligence, climate tech and renewables, intellectual property, biotech, investing in Silicon Valley, and growth stage companies, and general advice on career trajectories and strategies. We further held a young alumni roundtable, where our students got to speak with alumni who graduated in the past five years for intimate, candid discussions about life as junior associates. In total, our students heard from more than forty speakers, including over twenty University of Chicago alumni from various divisions.
The Trek didn’t stop with education, though. Throughout the week students also had the opportunity to network with speakers to learn more from them outside the confines of panel presentations and to grow their networks. We had a networking dinner with Kirkland & Ellis, a closing dinner with all Trek participants, and for the first time hosted an event for admitted students, Trek participants, and alumni to come together to share experiences and recruit the next generation of Law School students. Several speakers and students stayed in touch following the Trek, and this resulted not just in meaningful relationships but also in employment for some students who attended.
More information on the purposes of the Trek is available here , the full itinerary is available here , and one student participant’s story describing her reflections on and descriptions of her experience on the Trek is available here .
The Innovation Clinic is grateful to all of its clients for continuing to provide its students with challenging, high-quality legal work, and to the many alumni who engage with us for providing an irreplaceable client pipeline and for sharing their time and energy with our students. Our clients are breaking the mold and bringing innovations to market that will improve the lives of people around the world in numerous ways. We are glad to aid in their success in any way that we can. We look forward to another productive year in 2024-2025!
COMMENTS
We conducted a semiquantitative review of publications explicitly dealing with cultural ecosystem services. Our aims were: (1) to provide an overview of the current state of research, (2) to classify the diversity of research approaches by identifying clusters of publications that address cultural ecosystem services in similar ways, and (3) to ...
Abstract. Cultural ecosystem services (CES) are non-material intangible benefits that humans derive from ecosystems, which are indispensable for the well-being of communities and directly influence the quality of life. CES are deeply interconnected to each other and to providing and regulating services, thus influencing everyday life.
Abstract. During the last decade, we have witnessed an increased interest in Ecosystem Services (ES), including the so-called 'cultural ecosystem services' and its subcategory of 'cultural heritage'. In this article, a review of academic literature of ES and cultural heritage is carried out. ES has primarily been developed by scholars ...
3.2. 'Cultural' 'ecosystem' 'services' The difference between 'culture' in an anthropological sense and that applied by the most common classification systems has led some to question whether 'CES' should be called 'cultural' at all.
Ecosystem services are the benefits that natural environment and functioning ecosystems provide to human well-being. These services include provisioning, regulating, supporting and cultural services. This thesis project explores the latter, cultural services, which are often referred to as cultural ecosystem services.
The term "cultural ecosystem services" is defined within a wider framework of ecosystem services as "non-material benefits that people obtain from ecosystems through spiritual enrichment, cognitive development, reflection, recreation and aesthetic experience" (MA 2005).. These are tangible and intangible "goods and chattel" that people gain through their own experience in ...
The paper builds on systematic review and map methodology (James et al., 2016, Petticrew and Roberts, 2006) to offer an overview of peer-reviewed journal articles on cultural ecosystem services and human wellbeing (Fig. 1). A scoping review of key literature and recent reviews (Fatorić and Seekamp, 2017, Fleuret and Atkinson, 2007, McMichael ...
Abstract and Figures. Cultural ecosystem services constitute a growing field of research that is characterized by an increasing number of publications from various academic disciplines. We ...
When studying CES in the local context, it is important to determine what categories of CES should be actually incorporated, exploring cultural means and connected values (Fig. 1).In order to highlight the non-material outputs from ecosystems that affect the psychological and physical state of people, CES aims to distinguish those values from others [].
A second major challenge is the lack of specific connections between CES and landscape elements - that is, making concrete links to the ecosystem portion of cultural ecosystem services (Tilliger et al., 2015). Not fully understanding these connections, or even when they do or do not exist, makes it difficult for decision-makers to account for ...
Cultural Ecosystem Services (CESs), as non-material benefits and well-being provided by ecosystems to humans, possess the ability to bridge nature and human society and interpret their complex interrelationships. Coastal areas are regions with concentrated human activities, where coastal zones are often subject to human development, pollution, and degradation. Compared to other ecosystems ...
Southwest University, Chongqing, China. [email protected]. Abstract. This paper discusses the concept of cultural ecosystem services (CES) as a part of a broader framework of ecosystem ...
Parks and protected areas are recognized for the important ecosystem services, or benefits, they provide society. One emerging but understudied component is the cultural ecosystem services that parks and protected areas provide. These cultural ecosystem services include a variety of benefits, such as cultural heritage, spiritual value, recreation opportunities, and human health and well-being ...
The ecosystem services (ES) framework was developed to articulate and measure the benefits humans receive from ecosystems. Cultural ecosystem services (CES), usually defined as the intangible and nonmaterial benefits ecosystems provide, have been relatively neglected by researchers and policy-makers compared to provisioning, supporting, and regulating services. Although valuing CES poses ...
In defining cultural ecosystem services as the recreational, aesthetic, and spiritual benefits people obtain from ecosystems, the Millennium Ecosystem Assessment conveyed a key aspect of nature-society relationships. Yet, it is reasonable to suppose that this aspect may apply more to to contexts where people enjoy more leisure time to admire a ...
One approach, part of the increasing use of the ecosystem services (ES) concept in decision-making at multiple scales, is to label the nonmaterial aspects of these connections as nature's nonmaterial contributions to people, or cultural ecosystem services (CES; Millennium Ecosystem Assessment 2005, IPBES 2019). Many CES link intimately—but ...
This thesis explores the relationship between and the impact of cultural ecosystem services on resilience planning by examining public spaces in San Antonio, Texas. Existing studies have recognized that evaluating cultural ecosystem services is challenging, but continued research as well as the development and testing of new methods are ...
Cultural ecosystem services (CES), which includes many components regarding humans, and is defined as benefits and services that ecosystems provide to humanity. Tourism experiences provide a unique opportunity for people and tourism interactions influence human well-being. This study evaluates CES studies made for Anatolia between 2017-2022.
N2 - This paper discusses the concept of cultural ecosystem services (CES) as a part of a broader framework of ecosystem services provided by urban green spaces. It is based on literature review and evaluation of results from two research projects of urban green spaces conducted in Russia (three public parks in Moscow) and China (six public ...
of the cultural (human-created) block. In relation to the all-Russia assessment of ecosystem services, a spe-cific feature of urban areas is a significant share (on average, 25%) of the cultural block in the total cost of ecosystem services and a decrease in the cost of regula tory services by about 30%. The results of the economic
Maintaining and enhancing landscapes' beneficial contributions to a good quality of life is a major challenge of our time. Landscapes have been and are being changed by processes such as urbanization, economic development and ecological restorations which may sharply change the landscapes, and these changes may affect the ways in which people interact with their landscapes.
Cultural ecosystem services influence ownership and management of land. Cultural services provide community benefits and inform landscape planning. Cultural ecosystem services contribute to the maintenance of valuable landscapes. Cultural services may in some cases impede transformations to sustainability. There is increasing concern that the ...
Overview of selected urban ecosystem services (ES) and indicators used in the modelling. ES are defined in compliance with the Common International Classification of Ecosystem Services (CICES; version 5.1), which provides a systematic framework for indicator development (Haines-Young and Potschin Citation 2018).
1.Introduction. Ecosystem services (ES) are the benefits that human derive from nature, and can be generally classified as provisioning (e.g., food, water, and shelters), regulating (e.g., climate regulation and water purification), cultural services (e.g., recreation and aesthetics), and supporting services (MEA, 2005).Supporting services refer to ecosystem processes or functions that produce ...
General The Innovation Clinic continued its track record of success during the 2023-2024 school year, facing unprecedented demand for our pro bono services as our reputation for providing high caliber transactional and regulatory representation spread. The overwhelming number of assistance requests we received from the University of Chicago, City of Chicago, and even national startup and ...
The Cultural Ecosystem Services (CES) field provides a methodological framework for identifying the "non-material" services that ecosystems can offer to people, such as aesthetic values, educational values or tourism and recreation posibilities. In areas of significant cultural value, the so-called Cultural Landscapes, these type of ...