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The role of tourism impacts on cultural ecosystem services.

thesis cultural ecosystem services

1. Introduction

1.1. facilitating cultural ecosystem services–well-being through nature experiences, 1.2. current study, 2.1. participants, 2.2. materials and measures, 2.3. procedure, 4. discussion, limitations and future research, 5. conclusions, author contributions, acknowledgments, conflicts of interest.

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Click here to enlarge figure

Dependent VariableTestFdf df p-ValuePartial η
Overall AffectImpact Scene22.6851209<0.0010.098
Impact Level45.9943.18665.38<0.0010.180
Scene * Impact Level10.3473.06638.46<0.0010.047
ActivationImpact Scene32.0121292<0.0010.099
Impact Level47.7443.19931.82<0.0010.141
Scene * Impact Level8.9322.93856.33<0.0010.030
Positive–Negative ValenceImpact Scene23.6321288<0.0010.076
Impact Level63.5873.11896.25<0.0010.181
Scene * Impact Level10.4062.96852.54<0.0010.035
Dependent VariableImpact SCENEImpact LevelMeanStd. Error95% Confidence Interval
Lower BoundUpper Bound
Overall AffectMeadow (Social Trails)No impact4.490.0514.3914.590
14.260.0574.1504.373
24.070.0603.9544.189
33.990.0673.8544.117
43.940.0713.7984.078
Hillside
(Visitor-Created Site)
No impact4.460.0574.3454.569
14.540.0474.4514.635
24.400.0544.2934.507
34.310.0574.2024.426
44.110.0643.9824.237
ActivationMeadow (Social Trails)No impact78.201.27175.70080.703
173.361.28870.82875.896
271.261.35268.60173.925
369.171.39266.43171.910
468.661.40965.88571.432
Hillside
(Visitor-Created Site)
No impact78.971.32876.35381.579
179.861.22877.44282.278
277.611.27275.10580.110
375.741.33273.11678.358
472.151.39569.40274.891
Positive–Negative ValenceMeadow (Social Trails)No impact82.021.10079.85284.813
178.301.18475.97180.631
273.801.33071.17876.414
371.301.34968.64273.952
471.431.35668.75774.094
Hillside
(Visitor-Created Site)
No impact82.541.19280.19484.885
183.281.06181.19285.369
280.411.20778.03682.788
378.751.21576.35781.138
473.601.37870.88776.310

Share and Cite

Taff, B.D.; Benfield, J.; Miller, Z.D.; D’Antonio, A.; Schwartz, F. The Role of Tourism Impacts on Cultural Ecosystem Services. Environments 2019 , 6 , 43. https://doi.org/10.3390/environments6040043

Taff BD, Benfield J, Miller ZD, D’Antonio A, Schwartz F. The Role of Tourism Impacts on Cultural Ecosystem Services. Environments . 2019; 6(4):43. https://doi.org/10.3390/environments6040043

Taff, B. Derrick, Jacob Benfield, Zachary D. Miller, Ashley D’Antonio, and Forrest Schwartz. 2019. "The Role of Tourism Impacts on Cultural Ecosystem Services" Environments 6, no. 4: 43. https://doi.org/10.3390/environments6040043

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Article Contents

Five frontiers of ces, conclusions, acknowledgments, references cited.

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Frontiers in Cultural Ecosystem Services: Toward Greater Equity and Justice in Ecosystem Services Research and Practice

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Rachelle K Gould, Leah L Bremer, Pua'ala Pascua, Kelly Meza-Prado, Frontiers in Cultural Ecosystem Services: Toward Greater Equity and Justice in Ecosystem Services Research and Practice, BioScience , Volume 70, Issue 12, December 2020, Pages 1093–1107, https://doi.org/10.1093/biosci/biaa112

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Cultural ecosystem services (CES) are associated with diverse and profound values, such as spiritual fulfillment, cultural heritage, and identity-related phenomena. Early ecosystem services research often omitted these deep meanings, but they are increasingly explored in recent studies through a range of disciplinary and epistemological perspectives. In the present article, we distill emerging frontiers of CES research. These frontiers help to characterize varied sources of meaning that are central to the CES ethos. They represent both advances in and opportunities for CES research, especially as related to justice and equity. The frontiers are: broadening definitions and conceptualizations of CES; addressing collective aspects of CES and attending to process; acknowledging that CES are reciprocal, relational, and dynamic; embracing narrative; and better connecting CES to biophysical attributes. We focus on the implications of these frontiers for equity and justice and suggest future research that can help ecosystem services work better address both legacies and current manifestations of injustice.

For millennia, people have recognized that spiritual, identity-based, and culturally rich connections to ecosystems are crucially important. Through these nonmaterial connections (which are often deeply intertwined with material connections), ecosystems enrich human well-being in diverse ways. However, in general, much decision-making has not fully honored these relationships. In response, recent scholarly and policy work strives to create mechanisms to better include such connections. 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 not always obviously—to multiple dimensions of equity in diverse contexts. In urban areas, for example, who has access to the benefits of green space? In rural regions, whose values are considered when decisions about mining are made? Such issues of justice profoundly and systemically intertwine with environmental research and must be addressed across every subfield and in many ways (Schell et al. 2020 ). We suggest that CES can provide an important workspace to address equity-related challenges as they manifest in the environmental field generally and the ES field specifically. We therefore argue that well-designed and implemented CES research has the potential to represent diverse viewpoints so that they can be better included in decision-making that supports thriving socioecological systems.

In the present article, we synthesize emerging frontiers in the developing interdisciplinary body of research on CES and related concepts. We focus on how emerging CES research addresses issues of equity and justice because we see these normative goals as central and crucial. The frontiers we identify suggest a fundamental role CES research can play: It can provide a framework to bring diverse worldviews and values to bear on land-use decisions in transparent ways (Hirons et al. 2016 ). This role responds to an oversight of or a problem with decision-making frameworks: When values are implicit, decisions will, by default, reflect the worldviews and values of those with power (Ernstson 2013 , Berbés-Blázquez et al. 2016 ). Because they can make diverse values explicit, CES have the potential—if they are implemented with many caveats (e.g., in ways that align with the frontiers below, such as expanding beyond purely instrumental forms of value; James 2016 )—to counteract injustices in the way environmental management actions proceed.

The present article and its origins

We describe five intertwined frontiers we identify as in-progress developments in the CES field. We emphasize the frontiers’ potential to advance justice and equity in ES research and practice (table  1 ) and suggest future research that they inspire (table  2 ). In the process, we address many critiques of CES and offer ways that CES research is responding (and can further respond) to them.

Relationships between the frontiers we describe and equity and justice.

FrontierPotential contributions to equity and justice in ES research and practice
Broadening and deepening conceptualizations of CESInclude 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 processInclude 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 dynamicAcknowledge reciprocal values and relationships (often especially important for Indigenous communities)
Include values that do not align with the producer–consumer ES framework
Embracing narrativeExpress values that nonnarrative methods characterize poorly
Acknowledge different methods and preferences for communicating CES
Better connecting to biophysical attributesElucidate 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
FrontierPotential contributions to equity and justice in ES research and practice
Broadening and deepening conceptualizations of CESInclude 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 processInclude 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 dynamicAcknowledge reciprocal values and relationships (often especially important for Indigenous communities)
Include values that do not align with the producer–consumer ES framework
Embracing narrativeExpress values that nonnarrative methods characterize poorly
Acknowledge different methods and preferences for communicating CES
Better connecting to biophysical attributesElucidate 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 frontierPossible 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 CESWhat 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 processAre 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 dynamicHow 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 narrativeWhat 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 attributesDo 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 frontierPossible 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 CESWhat 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 processAre 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 dynamicHow 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 narrativeWhat 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 attributesDo 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.

Background: CES as a contested concept

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.

Broadening and deepening definitions and conceptualizations of CES

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.

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.

Addressing collective aspects of CES and attending to process

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.

Acknowledging that CES are reciprocal, relational, and dynamic

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.

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?).

Embracing narrative

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.

Better connecting to biophysical attributes

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.

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 findingsExampleWhere to find more information
Websites that highlight community members active in ES or CES workSuppliers 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 communitiesThe 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 performancesCollaboration 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 membersCommunity 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 storiesCompelling 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 discussOn 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 bookletsThe 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 storytellingCollaboratively 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 findingsExampleWhere to find more information
Websites that highlight community members active in ES or CES workSuppliers 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 communitiesThe 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 performancesCollaboration 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 membersCommunity 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 storiesCompelling 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 discussOn 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 bookletsThe 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 storytellingCollaboratively 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.

Author Biographical

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.

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Resilient Geographies: An Atlas of Cultural Ecosystem Services in the Land of Spirit Waters.

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.

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thesis cultural ecosystem services

  • A-Z Publications

Annual Review of Environment and Resources

Volume 41, 2016, review article, valuing cultural ecosystem services.

  • Mark Hirons 1,2 , Claudia Comberti 1 , and Robert Dunford 1,3
  • View Affiliations Hide Affiliations Affiliations: 1 School of Geography and the Environment, University of Oxford, Oxford OX1 3QY, United Kingdom; email: [email protected] 2 School of Agriculture, Policy and Development, University of Reading, Reading RG6 6AR, United Kingdom 3 Centre for Ecology and Hydrology, Wallingford OX10 8BB, United Kingdom
  • Vol. 41:545-574 (Volume publication date October 2016) https://doi.org/10.1146/annurev-environ-110615-085831
  • First published as a Review in Advance on July 14, 2016
  • © Annual Reviews

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 several conceptual and methodological difficulties, it is of huge interest and importance because of the linkages between cultural values, valuation methods, and the individual and collective decision-making that influence ecosystems and human wellbeing. This review is not a how-to guide, but rather examines key conceptual issues and maps critical areas of debate. There is a range of potential approaches to assessing CES; however, choices regarding valuation methods and their role in decision-making are shaped by cultural and political dynamics. CES are at a crossroads. They can potentially act as a fruitful conceptual container for a broad range of interdisciplinary research into human-environment relations and transform how decisions regarding the environment are made, but they can also be used to legitimize and entrench modes of decision-making that marginalize and undermine the very values they are intended to protect.

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Cultural Ecosystem Services of Urban Green Spaces. How and What People Value in Urban Nature?

  • Discipline of Landscape Architecture

Research output : Chapter in Book/Conference paper › Conference paper › peer-review

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 parks in Xi’an). Both case studies conducted face-to-face interviews of park visitors and stakeholders (in Xi’an) and utilized questionnaires as well as observational studies of people’s activities within parks and their infrastructure. This paper aims to explore how urban dwellers perceive and value urban green spaces (parks) and what particular CES/benefits can be drawn as being most important. CES of urban green spaces (especially urban parks) are discussed from the following viewpoints: a) visitors’ perception and behaviour, b) indicators and methods adapted to CES research and c) identifying and understanding the ecosystem service capacity of an urban green space for attracting visitors of different cultural backgrounds. The results highlight the importance of CES which are provided by urban green spaces for quality of life and human health in cities, and the role of CES in raising environmental awareness and social cohesion and interaction. This paper also provides suggestions for a research framework and conceptual models that can be applied in future studies of CES and provides useful tools for indicators selection and assessment.

Original languageEnglish
Title of host publicationAdvanced Technologies for Sustainable Development of Urban Green Infrastructure
Subtitle of host publicationProceedings of Smart and Sustainable Cities 2020
EditorsViacheslav Vasenev, Elvira Dovletyarova, Riccardo Valentini, Zhongqi Cheng, Carlo Calfapietra, Luis Inostroza, Michael Leuchner
Place of PublicationSwitzerland
Publisher
Pages292-318
Number of pages27
ISBN (Electronic)978-3-030-75285-9
ISBN (Print)978-3-030-75284-2, 978-3-030-75287-3
DOIs
Publication statusPublished - 11 May 2021
Event - RUDN University, Moscow, Russian Federation
Duration: 8 Jul 202010 Jul 2020

Publication series

NameSpringer Geography
ISSN (Print)2194-315X
ISSN (Electronic)2194-3168
ConferenceSmart and Sustainable Cities 2020
Abbreviated titleSSC-2020
Country/TerritoryRussian Federation
CityMoscow
Period8/07/2010/07/20

This output contributes to the following UN Sustainable Development Goals (SDGs)

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T1 - Cultural Ecosystem Services of Urban Green Spaces. How and What People Value in Urban Nature?

AU - Dushkova, Diana

AU - Ignatieva, Maria

AU - Konstantinova, Anastasia

AU - Yang, Fengping

PY - 2021/5/11

Y1 - 2021/5/11

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 parks in Xi’an). Both case studies conducted face-to-face interviews of park visitors and stakeholders (in Xi’an) and utilized questionnaires as well as observational studies of people’s activities within parks and their infrastructure. This paper aims to explore how urban dwellers perceive and value urban green spaces (parks) and what particular CES/benefits can be drawn as being most important. CES of urban green spaces (especially urban parks) are discussed from the following viewpoints: a) visitors’ perception and behaviour, b) indicators and methods adapted to CES research and c) identifying and understanding the ecosystem service capacity of an urban green space for attracting visitors of different cultural backgrounds. The results highlight the importance of CES which are provided by urban green spaces for quality of life and human health in cities, and the role of CES in raising environmental awareness and social cohesion and interaction. This paper also provides suggestions for a research framework and conceptual models that can be applied in future studies of CES and provides useful tools for indicators selection and assessment.

AB - 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 parks in Xi’an). Both case studies conducted face-to-face interviews of park visitors and stakeholders (in Xi’an) and utilized questionnaires as well as observational studies of people’s activities within parks and their infrastructure. This paper aims to explore how urban dwellers perceive and value urban green spaces (parks) and what particular CES/benefits can be drawn as being most important. CES of urban green spaces (especially urban parks) are discussed from the following viewpoints: a) visitors’ perception and behaviour, b) indicators and methods adapted to CES research and c) identifying and understanding the ecosystem service capacity of an urban green space for attracting visitors of different cultural backgrounds. The results highlight the importance of CES which are provided by urban green spaces for quality of life and human health in cities, and the role of CES in raising environmental awareness and social cohesion and interaction. This paper also provides suggestions for a research framework and conceptual models that can be applied in future studies of CES and provides useful tools for indicators selection and assessment.

KW - Cultural ecosystem services

KW - Human health and well-being

KW - Landscape perception

KW - Nature-based recreation

KW - Urban green spaces

UR - http://www.scopus.com/inward/record.url?scp=85105677789&partnerID=8YFLogxK

U2 - 10.1007/978-3-030-75285-9_28

DO - 10.1007/978-3-030-75285-9_28

M3 - Conference paper

AN - SCOPUS:85105677789

SN - 978-3-030-75284-2

SN - 978-3-030-75287-3

T3 - Springer Geography

BT - Advanced Technologies for Sustainable Development of Urban Green Infrastructure

A2 - Vasenev, Viacheslav

A2 - Dovletyarova, Elvira

A2 - Valentini, Riccardo

A2 - Cheng, Zhongqi

A2 - Calfapietra, Carlo

A2 - Inostroza, Luis

A2 - Leuchner, Michael

PB - Springer

CY - Switzerland

T2 - Smart and Sustainable Cities 2020

Y2 - 8 July 2020 through 10 July 2020

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The inclusion of stakeholders and cultural ecosystem services in land management trade-off decisions using an ecosystem services approach

  • Research Article
  • Published: 23 August 2015
  • Volume 31 , pages 533–545, ( 2016 )

Cite this article

thesis cultural ecosystem services

  • Rachel Darvill 1 , 3 &
  • Zoë Lindo 2  

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An ecosystem service approach for land-use or conservation decisions normally uses economic or biophysical assessments for valuating nature’s services. In contrast, even though ecosystem services are required for human well-being, the actual use of services by differing stakeholder groups are rarely considered in typical ecosystem service assessments, especially the more intangible, cultural ecosystem services.

The aim of this research was to quantify different uses for 15 cultural and provisioning ecosystem service indicators across seven stakeholder groups in a watershed proposed with large hydroelectric dam development.

We used a large-scale survey to quantify use and frequency of use for ecosystem services.

We demonstrate that different stakeholder groups use ecosystem services differently, both in terms of specific ecosystem service indicators, as well as for frequency of ecosystem service use. Across all stakeholder groups, specific cultural ecosystem services were consistently more important to participants when compared to provisioning ecosystem services, especially aesthetic/scenic values.

Conclusions

This work is of global importance as it highlights the importance of considering cultural ecosystem services (e.g. aesthetic/scenic, sense-of-place values) along with multiple stakeholder groups to identify the trade-offs and synergies during decision-making processes for land-use or conservation initiatives.

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Acknowledgments

The authors would like to thank all survey participants whom reside in the study area of the Upper Peace River Watershed. The comments of two anonymous reviewers were gratefully appreciated. Funding is from the Natural Sciences and Engineering Research Council of Canada (NSERC) Discovery Grants Program to ZL (#418241-2012). RD was funded by the NSERC Industrial Postgraduate Scholarships Program, the McLean Foundation, and was supported by Wildsight Golden and Wildsight Regional. Our funding sources had no involvement in study design, data collection, analysis or interpretation of data, nor in writing of the report or in the decision to publish these results.

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Darvill, R., Lindo, Z. The inclusion of stakeholders and cultural ecosystem services in land management trade-off decisions using an ecosystem services approach. Landscape Ecol 31 , 533–545 (2016). https://doi.org/10.1007/s10980-015-0260-y

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Cultural ecosystem services of Chinese typical landscapes: Rethinking non-material links between people and their landscapes

  • Landscape Architecture and Spatial Planning

Research output : Thesis › internal PhD, WU

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. The concept of Ecosystem Services (ES) has been widely adopted by scientists and policymakers as a framework to assess the consequences of landscape interventions, on provisioning, regulating, supporting, and cultural ecosystem services. CES refer to the benefits people receive from ecosystems in the form of spiritual, religious, recreational, inspirational and educational experiences.

To inform decision-making for sustainable landscape management, an elicitation of people’s concerns associated with their landscapes from socio-cultural perspectives is. However, current approaches of investigating CES have been criticized for voluntary self-exclusion of disciplines, over-valuing tourist-attractive landscapes and neglecting critical social impacts or dynamics. Moreover, due to the limitation of accessible data and applicable methods, rarely does research capture the cultural diversity of CES perceived by local communities and little is known about how CES change under human interventions.

The objective of this research was to investigate the non-material links between people and landscapes by analysing CES from an interdisciplinary perspective, in four typical Chinese landscapes (Dryland agricultural landscape, wetlands, grasslands and coastal wetlands). The research especially addresses the subjective nature of CES perception and the socio-cultural consequences of ecological restoration and conservation projects through their influence on CES perception. The approach incorporates the perceived values that local communities attach to landscapes and overcomes the limited application of non-spatiality explicit CES in broader ecosystem assessment by assessing the perceptions of local communities. Data were gathered by questionnaires survey or semi-structured interviews depending on the local context, as well as participatory mapping and field observations to further diagnose CES appraisal and their spatial distribution.

Synthesizing the findings of this research, there are several conclusions we can draw: 1) In general, Aesthetic services, Recreational services, Education and science, Inspirations, Sense of place, Cultural heritage, Religious and spiritual services and Physical and mental health are all highly perceived in China’s typical landscapes including wetlands, grassland, cultivated lands and coastal wetlands. Social relations were only identified in wetlands and coastal wetlands. 2) Demographic characteristics affect the perception of CES, especially ethnicity, age and education. Although demographic characteristics determine how people perceive CES, no generic rules such as “women tend to perceive more CES than men” or “old people tend to perceive more CES than young people” could be found. 3) Landscape features play a different role in different landscapes, but dominant landscape features are perceived as more important by local communities. The appreciation appeared to be closely linked to the intensity of the interaction and common landscape features are more appreciated than special landscape features. 4) Human interventions, including ecological restoration, conservation and local economic development influence CES perception, by influencing the opportunities for local people to engage with their landscapes, as well as potentially influencing the demographic characteristics of local communities (such as occupation, income and even age composition). Ecological restoration tends to have a positive effect on recreational services but a negative effect on sense of place.

Despite the limitations of data and methods, we showed that considering cultural ecosystem services, local communities, and the way they interact with different landscape features in ecological conservation and landscape management can help to improve conservation effectiveness, and pioneer new co-management arrangements.

Original languageEnglish
QualificationDoctor of Philosophy
Awarding Institution
Supervisors/Advisors , Promotor , Co-promotor
Award date8 Sept 2020
Place of PublicationWageningen
Publisher
Print ISBNs9789463954631
DOIs
Publication statusPublished - 8 Sept 2020

This output contributes to the following UN Sustainable Development Goals (SDGs)

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  • Communities Social Sciences 100%
  • Chinese Social Sciences 100%
  • Ecosystem Service Social Sciences 100%
  • Demographic Characteristic Psychology 100%
  • Sense of Place Social Sciences 33%
  • Recreation Business Social Sciences 33%
  • Grassland Social Sciences 33%
  • Landscape Management Social Sciences 33%

Projects per year

Cultural ecosystem services of Chinese coastal landscapes and their vulnerability to global change

Dou, Y., Bakker, M. & Carsjens, G.

16/01/16 → 8/09/20

Project : PhD

  • Chinese 100%
  • Communities 100%
  • Ecosystem Service 100%
  • Demographic Characteristic 100%
  • Sense of Place 33%

T1 - Cultural ecosystem services of Chinese typical landscapes

T2 - Rethinking non-material links between people and their landscapes

AU - Dou, Yuehan

N1 - WU thesis 7583 Includes bibliographical references. - With summary in English

PY - 2020/9/8

Y1 - 2020/9/8

N2 - 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. The concept of Ecosystem Services (ES) has been widely adopted by scientists and policymakers as a framework to assess the consequences of landscape interventions, on provisioning, regulating, supporting, and cultural ecosystem services. CES refer to the benefits people receive from ecosystems in the form of spiritual, religious, recreational, inspirational and educational experiences.To inform decision-making for sustainable landscape management, an elicitation of people’s concerns associated with their landscapes from socio-cultural perspectives is. However, current approaches of investigating CES have been criticized for voluntary self-exclusion of disciplines, over-valuing tourist-attractive landscapes and neglecting critical social impacts or dynamics. Moreover, due to the limitation of accessible data and applicable methods, rarely does research capture the cultural diversity of CES perceived by local communities and little is known about how CES change under human interventions.The objective of this research was to investigate the non-material links between people and landscapes by analysing CES from an interdisciplinary perspective, in four typical Chinese landscapes (Dryland agricultural landscape, wetlands, grasslands and coastal wetlands). The research especially addresses the subjective nature of CES perception and the socio-cultural consequences of ecological restoration and conservation projects through their influence on CES perception. The approach incorporates the perceived values that local communities attach to landscapes and overcomes the limited application of non-spatiality explicit CES in broader ecosystem assessment by assessing the perceptions of local communities. Data were gathered by questionnaires survey or semi-structured interviews depending on the local context, as well as participatory mapping and field observations to further diagnose CES appraisal and their spatial distribution.Synthesizing the findings of this research, there are several conclusions we can draw: 1) In general, Aesthetic services, Recreational services, Education and science, Inspirations, Sense of place, Cultural heritage, Religious and spiritual services and Physical and mental health are all highly perceived in China’s typical landscapes including wetlands, grassland, cultivated lands and coastal wetlands. Social relations were only identified in wetlands and coastal wetlands. 2) Demographic characteristics affect the perception of CES, especially ethnicity, age and education. Although demographic characteristics determine how people perceive CES, no generic rules such as “women tend to perceive more CES than men” or “old people tend to perceive more CES than young people” could be found. 3) Landscape features play a different role in different landscapes, but dominant landscape features are perceived as more important by local communities. The appreciation appeared to be closely linked to the intensity of the interaction and common landscape features are more appreciated than special landscape features. 4) Human interventions, including ecological restoration, conservation and local economic development influence CES perception, by influencing the opportunities for local people to engage with their landscapes, as well as potentially influencing the demographic characteristics of local communities (such as occupation, income and even age composition). Ecological restoration tends to have a positive effect on recreational services but a negative effect on sense of place.Despite the limitations of data and methods, we showed that considering cultural ecosystem services, local communities, and the way they interact with different landscape features in ecological conservation and landscape management can help to improve conservation effectiveness, and pioneer new co-management arrangements.

AB - 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. The concept of Ecosystem Services (ES) has been widely adopted by scientists and policymakers as a framework to assess the consequences of landscape interventions, on provisioning, regulating, supporting, and cultural ecosystem services. CES refer to the benefits people receive from ecosystems in the form of spiritual, religious, recreational, inspirational and educational experiences.To inform decision-making for sustainable landscape management, an elicitation of people’s concerns associated with their landscapes from socio-cultural perspectives is. However, current approaches of investigating CES have been criticized for voluntary self-exclusion of disciplines, over-valuing tourist-attractive landscapes and neglecting critical social impacts or dynamics. Moreover, due to the limitation of accessible data and applicable methods, rarely does research capture the cultural diversity of CES perceived by local communities and little is known about how CES change under human interventions.The objective of this research was to investigate the non-material links between people and landscapes by analysing CES from an interdisciplinary perspective, in four typical Chinese landscapes (Dryland agricultural landscape, wetlands, grasslands and coastal wetlands). The research especially addresses the subjective nature of CES perception and the socio-cultural consequences of ecological restoration and conservation projects through their influence on CES perception. The approach incorporates the perceived values that local communities attach to landscapes and overcomes the limited application of non-spatiality explicit CES in broader ecosystem assessment by assessing the perceptions of local communities. Data were gathered by questionnaires survey or semi-structured interviews depending on the local context, as well as participatory mapping and field observations to further diagnose CES appraisal and their spatial distribution.Synthesizing the findings of this research, there are several conclusions we can draw: 1) In general, Aesthetic services, Recreational services, Education and science, Inspirations, Sense of place, Cultural heritage, Religious and spiritual services and Physical and mental health are all highly perceived in China’s typical landscapes including wetlands, grassland, cultivated lands and coastal wetlands. Social relations were only identified in wetlands and coastal wetlands. 2) Demographic characteristics affect the perception of CES, especially ethnicity, age and education. Although demographic characteristics determine how people perceive CES, no generic rules such as “women tend to perceive more CES than men” or “old people tend to perceive more CES than young people” could be found. 3) Landscape features play a different role in different landscapes, but dominant landscape features are perceived as more important by local communities. The appreciation appeared to be closely linked to the intensity of the interaction and common landscape features are more appreciated than special landscape features. 4) Human interventions, including ecological restoration, conservation and local economic development influence CES perception, by influencing the opportunities for local people to engage with their landscapes, as well as potentially influencing the demographic characteristics of local communities (such as occupation, income and even age composition). Ecological restoration tends to have a positive effect on recreational services but a negative effect on sense of place.Despite the limitations of data and methods, we showed that considering cultural ecosystem services, local communities, and the way they interact with different landscape features in ecological conservation and landscape management can help to improve conservation effectiveness, and pioneer new co-management arrangements.

UR - https://edepot.wur.nl/526721

U2 - 10.18174/526721

DO - 10.18174/526721

M3 - internal PhD, WU

SN - 9789463954631

PB - Wageningen University

CY - Wageningen

ORIGINAL RESEARCH article

Evaluating cultural ecosystem services of urban residential green spaces from the perspective of residents' satisfaction with green space.

\nQizheng Mao

  • 1 Department of Resource and Environmental Science, Henan University of Economics and Law, Zhengzhou, China
  • 2 School of Civil Engineering and Architecture, Zhejiang Sci-Tech University, Hangzhou, China
  • 3 Jiyang College, Zhejiang Agricultural & Forestry University, Zhuji, China

Green spaces in residential areas provide multiple cultural ecosystem services (CES), which can contribute to human health by increasing the frequency of residents' visits. We evaluated the CES of residential green spaces by assessing residents' satisfaction with these spaces in the city of Zhengzhou, China. The data reveal the supply capacity of CES in residential green spaces: the results suggest that the level of recreational services is low, whereas the residents' satisfaction with the sense of place and neighborhood relations is high. The lower the frequency of residents who visit a park outside the residential area, the higher the satisfaction with the CES. This suggests that residential green spaces can effectively compensate for the lack of nearby parks owing to their proximity to residents' living quarters. The CES in residential communities increased as vegetation coverage increased, indicating that natural vegetation is a source of CES. In addition, the results showed that residents' perceptions of plant decoration, landscape patterns, and management and infrastructure in particular can effectively improve the level of CES, and this could compensate for CES that have shrunk owing to low green space coverage. This study has practical significance and value for the planning and design of residential green spaces, offering suggestions for urban landscape planners and decision makers. Future research should combine the residents' perception of demand and supply of CES and should clarify the gap and trade-off between them.

Introduction

The ecosystem services of urban green spaces can be defined as services that improve the welfare of urban residents who enjoy green spaces ( 1 ). These services include support, regulation, supply, and cultural ecosystem services (CES) ( 2 ). CES can be provided by green spaces for leisure, tourism, cultural education, aesthetic appreciation, and spiritual needs ( 3 ), all of which account for a large proportion of the ecosystem services in an urban green space ( 4 ). Residents' physical and mental health, especially social belonging, group identity, and social integration, are closely related to environmental services ( 5 ). In recent years, CES have become a trending topic in urban ecosystem services research. However, compared with other types of ecosystem services, research on CES is still in its infancy because its intangible characteristics are difficult to quantify.

Currently, several researchers are exploring various means to study the CES of urban green spaces (6–13). Survey questionnaires, the most commonly used evaluation method, can be direct or indirect. Direct methods includes face-to-face ( 5 , 6 ), email ( 7 , 8 ), or network ( 9 , 10 ) surveys, which evaluate CES according to residents' visit frequency to green spaces, activity types, and perceptions of CES. Indirect methods capture pictures of the target place and then invite residents to give scores to the CES reflected by the different green space landscapes or land use types in the pictures ( 11 , 12 ). Although face-to-face questionnaires are an effective way to evaluate urban ecosystem services, they are also difficult, mainly because of the high cost ( 8 ).

Previous studies have quantified CES in green areas from the residents' perceptions ( 10 , 13 ), producing CES scores for subjective cognition and distinguishing the importance of different CES ( 9 , 14 – 16 ). Moreover, by detecting the population's perspective on need, this research has described the demand for CES. The trade-off between the demand and supply of CES is also a popular research topic that can provide constructive suggestions for urban management and planning. CES supply in urban areas is characterized by the spatial distribution and physical attributes of urban green spaces, such as the amount, size, type, water bodies, facilities, and biodiversity ( 17 ). Residents' satisfaction with their surrounding physical environment is commonly used in studies concerning the well-being of humans ( 18 , 19 ); such parameters objectively portray the status (i.e., positive or negative) of an urban environment from the residents' perspective. Therefore, the evaluation of residents' satisfaction with CES can directly present the supply capacity of CES, which will facilitate any adjustment of the physical characteristics of green spaces. However, few studies have assessed CES from the perspective of residents' satisfaction with green spaces.

Urban residents around the world express a desire for contact with nature and one another, including attractive environments, recreational and play areas, privacy, active roles in the design of the community, and a sense of community identity ( 20 ). A positive correlation exists between human health and urban green spaces ( 21 – 23 ). Urban green spaces refer to natural vegetation in cities, including highly artificial green spaces, such as roadside green parks, residential green space, and natural woodland, which provide a variety of ecosystem services, especially recreational and entertainment areas with CES. Numerous studies have focused on the CES of urban parks, forests, wetlands, and other popular green spaces ( 6 , 24 , 25 ), whereas residential areas have received minimal attention. With the rapid expansion of cities and resultant growth of the urban population, as well as the limited natural vegetation in cities, urban residential areas are becoming gradually dominated by environments that have a high population density and a low green space density. In particular, the green areas of urban residential areas in developing countries are often correlated with real estate prices ( 26 ), which leads directly to the prevalence of urban human settlements and environmental inequity ( 27 ). Scholars have therefore pointed out that the remaining green spaces should make up for the shortage of other green land types, such as roadside and residential green spaces ( 9 ). The distance between urban green spaces (e.g., parks) and residents determines the use frequency of these spaces ( 10 , 28 , 29 ). Residential green spaces are the most common and frequently used land types and have multiple ecosystem functions and services (e.g., biodiversity protection, climatic adjustment, energy saving, and recreation). Therefore, evaluating and exploring the CES characteristics of green areas in high-density residential areas can provide valuable references for urban ecosystem research. As an essential component of urban green spaces, residential green spaces are characterized particularly by high fragmentation and heterogeneity, and huge differences exist among residential districts, which are correlated with various landscape planners, property managers, and residents with different socioeconomic status. Hence, research on CES in urban residential green spaces is difficult to conduct. Many studies have reported that the design of urban landscapes greatly influences the well-being and behavior of users and nearby inhabitants ( 18 , 30 ). CES in high-density residential areas are thus more important than the regulative and supporting services of green spaces. Moreover, magnifying the CES in limited spaces is significant. Investigating and assessing CES in residential areas can further enrich the theories and practices of ecosystem services in urban green spaces.

The influencing factors of CES in urban green spaces are a key research topic, which could provide important and practical information for the planning and management of urban green spaces. The CES in urban green spaces are often related to residents' socioeconomic status (e.g., age, income level, marriage, and profession) ( 14 , 31 – 34 ). Specifically, residents' socioeconomic status is closely related to the subjectivity and intangibility of CES. In addition, urban morphologies and land use may affect CES in large-scale green spaces. For instance, CES in wetlands are better than in other land types ( 9 , 35 ). The quality and quantity of green space landscapes are the important influencing factors of CES ( 36 ), along with green space size ( 37 ), green space accessibility ( 38 ), natural properties of green spaces ( 9 , 14 , 39 ), and species composition and biodiversity ( 40 , 41 ). Studies have found that cleanliness and proper management ( 9 ), as well as infrastructure ( 42 ), contribute greatly to improvement of CES in green spaces. Green spaces in residential areas offer various CES, such as walking, exercise, aesthetic appreciation, neighborhood exchanges, stress-relieving activities, and activities that foster a good mood. Hence, exploring the influencing factors of CES in residential green spaces should provide important practical guidance for landscape planning and the design of green spaces in residential areas.

Previous studies have focused on residents' satisfaction with their living environment ( 10 , 14 , 33 , 42 ). Physical and natural environments exert significant effects on residential satisfaction with the aspects of the natural environment, convenient transportation, environmental health, urban security, the convenience of public facilities, and the sociocultural environment. However, the following questions remain: (1) How does the natural environment affect the human perspective of the residential environment? (2) How satisfied are people with urban green spaces in residential areas? (3) What is the current level of CES in the residential green spaces of high-density communities? (4) Is the vegetation coverage of green spaces a major factor that affects CES? (5) What physical environment of residential green spaces contributes the most to CES? These questions can be answered by evaluation of CES and exploration of the possible determinant factors of CES in residential green spaces.

This study aimed to evaluate the level of CES in green spaces of residential areas by examining the satisfaction of residents and to explore the possible factors affecting the function of residential green spaces (e.g., coverage of green space in the residential areas, social factors, residents' use of green spaces, and management) and the key issues that should be addressed.

Materials and Methods

A total of 40 residential communities in Jinshui District, Zhengzhou City, Henan Province, China, comprised the study area. Zhengzhou, the capital of Henan Province, is Henan's largest and most populated city and has an area of 7,446 km 2 and 9.88 million inhabitants as at 2018. Most housing estates in the Jinshui District are relatively mature, containing not only medium vegetation coverage but also housing built before 2010. We assumed that these housing estates would provide a stable and objective level of CES.

Among the 40 major cities in China, Zhengzhou has the highest population density at 15,000 people/km 2 , and the urban land conflict is most prominent. The current urbanization rate of Zhengzhou is 78.2%, ranking 30th in China, and the urbanization process in this city is advancing rapidly. Many real estate resources have been built, but their overall quality is low. In particular, Zhengzhou has low green space coverage and property management with different levels. Gaps between the living environment of Zhengzhou's urban residents and other first-tier cities in China (e.g., Beijing, Shanghai, Shenzhen, and Guangzhou) are evident; that is, Zhengzhou lags behind in terms of urbanization and economic development. Evaluating the current supply capacity of the CES of residential areas can provide a scientific reference for improving the living environment and well-being of Zhengzhou residents.

Zhengzhou is divided into six administrative districts and seven provincial direct counties. Jinshui District is one of the most economically developed urban areas in the province, with a total area of 135.3 km 2 and a population of 1.402 million. Jinshui District is the area with the largest population and the most developed economy in Zhengzhou ( Figure 1 ). Compared with the other districts' residential areas, the real estate development area in Jinshui District is the largest, earliest, and most mature. The residential projects developed in the Jinshui District are composed of 50% ordinary housing and almost 40% villas and affordable housing. These patterns are closely related to the comprehensive functions undertaken by the Jinshui District and the spatial development strategy of “Northward and Eastward Expansion.” The dominant type of residential area in the Jinshui District is the reason why this area was chosen for the case study ( 43 ).

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Figure 1 . The geographical locations of the selected 40 residential communities.

Jinshui District is also the most active urban expansion area in Zhengzhou. The demand for residential areas from the urban population is increasing, leading to development of high-density residential areas in the region at the expense of green spaces and a reduction of ecosystem services.

Classification and Evaluation Indicators of Cultural Ecosystem Services in Green Spaces in Residential Areas

CES can be classified under the non-material benefits provided by ecosystems ( 44 ). CES in urban green spaces are globally categorized into seven types: aesthetic information, recreation, cultural heritage, education, social relations, health, and spiritual/religious values ( 2 , 45 , 46 ). In residential areas, CES could be defined as opportunities for residents to enjoy recreational activities, aesthetic appreciation, social contact with neighbors, and stress-relieving activities and to strengthen the sense of belonging. CES in residential green spaces are divided into five types: recreation, aesthetics, social relations, a sense of belonging, and spiritual demand ( Table 1 ). Recreational services refer to various recreational activities available in the residential green space for the residents, including exercise, walking, dog walking, childcare, and running. Recreational services are evaluated by measuring the frequency and duration of residents' participation and their satisfaction. Aesthetic services are residents' aesthetic perceptions of the overall landscape and plant collocation in residential green spaces, and they are evaluated by the residents' overall satisfaction with the aesthetics of the above two factors. Social relations services provide residents with opportunities to communicate with neighbors and release emotional stress. This service is evaluated through the communication frequency of residents with family members, friends, or neighbors, as well as their satisfaction with neighborhood relations. The evaluation index for the sense of belonging involves residents' satisfaction with respect to how welcoming and nurturing the environment is. Finally, spiritual services involve spiritual experience and spiritual release in residential green spaces. The evaluation indexes for spiritual services include satisfaction with pressure relief features and the quietness of the environment. The quality of urban green spaces is widely evaluated by residents' satisfaction with various functions ( 15 , 19 , 34 ). Therefore, in our study, we applied the satisfaction with CES to identify the level of CES.

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Table 1 . Selected CES and their indicators.

Data Collection

A face-to-face survey was used to explore the attitudes of residents in Zhengzhou City toward the different types of CES in the residential green spaces. To ensure the adequacy of the sample size, as well as the authenticity of the questionnaire, we selected 40 sites from the 215 residential communities in Jinshui. These sites, all of which were built after 2000, have at least 600 households. The area of the 40 residential estates ranged from 0.38 to 33 hm 2 , and the vegetation cover ratio was between 13 and 58%. In China, a residential community is the smallest residential unit within a limited space ( Figure 1 ). Each residential community has unique characteristics, such as vegetation coverage, water bodies, public activity spaces, management, infrastructure, vegetation structure, and plant species. Moreover, different communities are relatively independent and closed. Therefore, our study investigated residents' overall satisfaction with different types of CES and the use of green spaces in these sites.

To truly express the impact of green spaces on residents' activities, the data were collected on weekends and official holidays from June 2017 to August 2018. The survey was conducted between 09:00 and 19:00. Our interviewees were mainly residents who are inactive in the green spaces of the community. A household survey was used as a supplement to ensure a sufficient sample size. A total of 4,519 respondents were interviewed, with between 93 and 135 interviewees from each of the 40 communities. First, residents' use of green spaces and satisfaction with different types of CES were collected to evaluate the cultural service levels of the green spaces. Then, the residents' satisfaction with green space management and infrastructure was investigated. Finally, the most satisfying and unsatisfying factors with regard to the residential green spaces were collected, covering management, water services, public activity spaces, green coverage, facilities, plant collocation, and the landscape pattern of the green spaces, to analyze the subjective physical environment of the residential areas by investigating the influencing factors of CES in the residential green spaces. The collected physical environment indicators included real vegetation coverage, the number of public activity spaces, including the existence of water bodies, and the management level. With the use of Google's high-definition imagery, object-oriented automatic classification was applied to extract the real vegetation coverage, which refers to the vertical projection area of vegetation (including leaves, stems, and branches) on the ground as a percentage of the total area of the residential area. The number of public activity spaces (e.g., squares, water bodies, children's play facilities, gazebos, promenades, and places for physical exercise) was obtained during the survey of residents' satisfaction with CES. A total of 40 residential areas were categorized into two groups: residential areas with water body settings and those without. The management of residential green spaces was subjectively divided into three levels: good, medium, and poor.

Data Analysis

All data aggregation and statistical analyses were conducted in Microsoft Excel and SPSS v21. First, we analyzed the descriptive statistics to explore the socioeconomic characteristics of the respondents (gender, age, income, education, and the use of residential green spaces) and their ways of using green areas ( Table 2 ). The level of respondents' satisfaction with the various CES in the residential green spaces was scored 1–10, with 1 indicating poor satisfaction and 10 maximum. The overall satisfaction with CES was calculated as an average of satisfaction with seven types of CES, including recreation, the aesthetics of the green space landscapes and plant collocation, neighborhood relations, the sense of place, stress-relieving features, and the quietness of the environment. Pearson's correlation analysis was used to investigate the relationship among the various CES in the residential green spaces (Pearson's coefficient) ( Table 3 ). Linear regression analyses were applied to test the possible variables affecting the level of CES. The analysis process was as follows ( 47 ): single-factor results were derived from a univariate linear regression model that included a single variable ( Table 4 ), and significant variables emerging from the single-factor models ( p < 0.05) were then included in subsequent multivariate linear models (i.e., social–economic attributes, green spaces' use, frequency of visits to parks outside the residential area, and the subjective and objective physical environmental variables) ( Table 5 ), which were examined in a series of backward stepwise elimination procedures. The final multivariate linear regression models included all the demographic variables and the successive inclusion of significant variables from the socioeconomic factors, use of green space, and the physical environmental variables selected by the backward stepwise procedures ( p < 0.05).

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Table 2 . Respondents' demographic characteristics and use of residential green spaces.

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Table 3 . Pearson's correlation coefficient of the different CES.

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Table 4 . Relationship between residents' satisfaction on different CES and demographic characteristics, use frequency of green spaces and variables of physical environment with the univariate linear regression analysis.

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Table 5 . Effects of residents' socioeconomic attributes, use characteristic and physical environment of green spaces on the total level of CES with the multivariate linear regression analysis.

Ethics Approval

This study was carried out in accordance with the recommendations of the ethical standards of Henan University of Economics and Law. The protocol was approved by Henan University of Economics and Law. All subjects gave written informed consent in accordance with the Declaration of Helsinki.

Social and Economic Characteristics of the Respondents

Table 2 presents the demographic characteristics of the survey respondents and their mean satisfaction with the CES in their residential green spaces. A total of 4,519 residents in 40 residential areas were interviewed. The percentage of female respondents (50.28%) was slightly higher than that of the male ones (49.72%). Most respondents were within the age range of 30–39 years (24.36%), followed by 21–29 (19.7%), <20 (17.1%), 40–49 (15.17%), >60 (13.6%), and 50–59 years (10.07%). In terms of educational attainment, most of the respondents had an undergraduate degree (28.54%) or had completed junior high school or lower (27.73%), junior college (21.3%), or high school (18.05%). The smallest percentage of respondents had a post-graduate degree (4.38%). As for monthly income, respondents with no income represented the largest percentage (31.6%); followed by those earning 3,000–5,000 RMB (29.25%), 1,000–3,000 RMB (25.5%), and 5,000–10,000 RMB (18.55%); and last those earning above 10,000 RMB (5.1%). Almost half of the respondents had lived in the community area for more than 5 years (40.16%), followed by those residing in the area for 1–3 (24.45%) and 3–5 years (22.54%), and last those living in the community for <1 year (14.68%).

Cultural Ecosystem Services Satisfaction Levels in the Residential Green Spaces

Figure 2 shows the residents' satisfaction level with CES in the residential green spaces, which is based on the respondents' reported usage and satisfaction regarding residential green spaces. Satisfaction with neighborhood relations obtained the highest average score of 7.73 (from a scale of 1 to 10), followed by the sense of belonging (6.81), vegetation landscape aesthetics (6.62), and plant collocation aesthetics (6.56). Satisfaction with recreation services, the quietness of the environment, and stress-relieving features obtained the lowest average scores (6.36, 6.40, and 6.52, respectively). The average overall residents' satisfaction score was 6.71. These results reveal that the residents' satisfaction with various types of CES is relatively similar. The relationship between different CES of green spaces was analyzed using Pearson's correlation ( Table 3 ), which revealed significant positive correlations ( p < 0.01). The main activities of residents in residential green spaces include walking, childcare, and resting ( Figure 2 ), which accounted for 48.24, 33.89, and 27.17% of the activities, respectively. In addition, residents exercise (18.47%), meet and chat with friends (10.56%), walk their dogs (7.34%), participate in cultural activities (e.g., singing, dancing, calligraphy, playing chess or cards, and painting) (5.69%), ride bicycles (4.04%), and drink tea (1.24%).

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Figure 2 . Residents' satisfaction score on cultural ecosystem services (CES) and the main recreational activities in the residential green spaces.

Residents frequently visit residential green spaces ( Table 2 ). Approximately 40% of the interviewed residents visit residential green spaces every day, and 30.87% visit at least three times per week. In addition, 11.68% of residents visit residential green spaces at least three times per month, and 18.07% pay occasional visits. However, most residents stay in residential green spaces for a short time: 44.05% stay for nearly half an hour, whereas 37.65% stay for 1–2 h. The proportion of residents staying for a longer time than this is relatively low, with 5.91 and 3.87% staying for 3 and >3 h, respectively. Walking is the major activity of the residents who stay in the residential green spaces for 1–2 h, whereas engaging in social communications and drinking tea are the primary activities of residents who stay for roughly 3 h. Moreover, social communication is the reason why residents stay longer than 3 h.

A statistical analysis of the residents' frequency of communicating with neighbors and friends in the residential green spaces was also performed. The results returned a high overall frequency: 27.95 and 30.71% of the residents chat with others every day and at least three times a week, respectively, and 11.58% chat with other people at least three times every month. Only 17.18 and 12.56% of residents occasionally and hardly chat with neighbors and friends, respectively. In addition, almost half of the respondents pay occasional visits to parks outside the residential areas (43.58%), whereas the lowest proportion visits these parks every day (10.26%). In addition, several people visit parks at least three times a week (24.37%) or at least three times a month (21.79%).

Determinants of Cultural Ecosystem Services in Residential Green Spaces

According to the univariate linear regression model between the socioeconomic characteristics and residents' satisfaction with CES ( Table 4 ), gender, length of stay, and education background showed no significant correlations. Interestingly, the proportion of people in the age group 21–29 years was negatively correlated with multiple CES, whereas that in the age group 50–59 years was positively correlated with the satisfaction of neighborhood relations and sense of belonging, whereas the age group >60 years was significantly correlated with satisfaction with a quiet environment and a sense of belonging. With respect to income level, residents earning 1,000–3,000 RMB were only slightly satisfied with plant collocation aesthetics.

Most residents were dissatisfied with the management, water facilities, and the public activity spaces in the residential green spaces ( Figure 3 ), accounting for 27.53, 19.10, and 14.44% of the total resident population. Moreover, 11.21, 6.89, 5.05, and 4.11% of the residents were not satisfied with the green space coverage, infrastructure, plant collocation, and landscape patterns, respectively. The residents viewed vegetation coverage, public activity spaces, and management as the most important factors that should be considered in the selection of future residential green spaces ( Figure 4 ). The proportions of residents highly concerned with vegetation coverage, public activity spaces, and management were highest, reaching 46.45, 44.29, and 39.73%, respectively. Moreover, those concerned about water facilities, landscape patterns, basic facilities, and plant collocation were 34.62, 33.78, 29.38, and 28.76%, respectively. The basic facilities in residential green spaces include ornamental, artistic, functional, or other equipment for services.

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Figure 3 . Proportion of respondents who are satisfied and dissatisfied with the quality of residential green spaces.

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Figure 4 . Proportion of respondents who are concerned about the future quality of residential green spaces.

The total level of CES was significantly affected by both the objective and subjective physical environments of the residential green spaces ( Table 4 ). The results from a univariate linear regression showed that the vegetation coverage, management level, number of public activity spaces, and settings of water bodies in residential green spaces were significantly correlated with CES. The proportion of residents who were satisfied with the physical environment, including plant decoration, the coverage of green spaces, the water bodies for public activities, and the landscape patterns of residential green spaces, was significantly correlated with almost all types of CES.

The real vegetation coverage and the proportion of residents who were satisfied with plant decorations and landscape patterns were the only physical environment variables to emerge as significant in the multivariate analysis ( Table 5 ), and their association with the total level of CES was examined after progressive adjustment for different blocks of variables. The proportion of residents who were satisfied with the coverage of green space was removed in the final model; we supposed it could be attributed to the multicollinearity between landscape pattern, plant decoration, and coverage of green spaces. However, the relationship between objective physical environment variables and CES attenuated after adjustment for other variables, indicating that CES was mainly influenced by residents' subjective perception of the physical environment. In addition, the percentage of residents occasionally visiting parks outside the residential areas was also significantly correlated with the level of CES.

Although some studies have suggested that CES in residential green spaces are less valuable than those in urban green spaces, many researchers have stated that the inherent cultural value does not determine the use frequency of residents and that the distance to green spaces is closely related to individual interests ( 6 , 10 , 24 , 34 , 48 , 49 ). Therefore, evaluating CES will further enrich the study of urban ecosystem services.

We defined the satisfaction level with CES <4 as low, 4–7 as medium, and >7 as high. The total satisfaction level with CES in the residential green spaces in Zhengzhou was medium (6.71), whereas residents' satisfaction with different types of CES varied. Satisfaction with the recreational services obtained the lowest score, which can be attributed to the absence of public activity spaces and facilities in most residential green spaces. Satisfaction with the overall landscape aesthetics of residential green spaces and plant collocation was relatively high, signifying the good aesthetic service level in residential green spaces in Zhengzhou. The level of spiritual services was complicated. Satisfaction with neighborhood relations and sense of belonging was the highest, whereas satisfaction with stress-relieving features and quietness was lower than the previous two factors.

Unlike previous studies, our study evaluated CES by examining residents' satisfaction, which was lowest for recreational services and highest for sense of place and neighborhood relations ( Figure 2 ). Previous studies have highlighted that recreational services in urban green spaces have the highest value among all relevant factors ( 10 , 50 ), whereas other studies have discovered that aesthetic features are most important ( 13 , 14 , 51 ). In this study, residents' satisfaction with the different CES in residential green spaces was analyzed to evaluate the supply capacity of CES. Gaps between the supply and demand of CES mostly account for the significant difference between our results and other research. However, identification of CES is mainly based on the subjective perception of residents, which produces great variability. Cultural background, customs, social status, and other socioeconomic factors influence people's perception of CES. In addition, the type of green space involved in different research also has an effect.

Multiple CES originate from the natural attributes of urban green spaces. Significantly positive correlations have commonly been observed among the different types of CES ( 9 , 10 , 13 , 52 ). However, other studies have also discovered significantly negative correlations ( 14 ). Respondents might find it difficult to distinguish between the different types of CES, indicating that various types of CES are concentrated in a specific space ( 13 , 53 ). This finding implies internal correlation and inseparable natural attributes of the various types of CES and further proves the binding effect of different CES, which might be related to the fact that the different types of CES derive from the natural attributes of the ecosystem (i.e., the surrounding natural environment).

In dense urban regions, CES provided by residential green spaces can stimulate the residents' positive attitude toward neighborhood relations, which could compensate for environmental inequality in the urban area that is, the insufficiency of other popular or large green spaces. Urban parks and woods are the most important among the different types of green spaces ( 10 ), providing high social, economic, environmental, and ecological services and values. However, the spatial distribution of these green spaces varies widely in urban areas, thereby contributing to widespread environmental inequities. The relationship between CES and residents' visit frequency to parks outside their communities in our study demonstrated that residential green spaces can effectively compensate for the lack of nearby parks owing to their proximity to residents' living areas. Therefore, the construction, investment, planning, and design of residential green spaces should be paid additional attention.

Socioeconomic Attributes of Cultural Ecosystem Services in Residential Green Spaces

CES in green spaces are stable and can be directly determined by the green landscape. Initially, we suppose the length of living in a community was believed to have caused polarization of residents' subjective evaluation of CES in green spaces. Residents who live in a community for a long time frequently visit residential green spaces, are more familiar with the surrounding environment than other groups, and thus make extensive subjective evaluations. Moreover, such residents are more socially integrated than residents who have been living in the community for a short time ( 42 ). However, residents may eventually become increasingly dissatisfied with the unreasonable characteristics of green spaces, resulting in low satisfaction with the different CES. Conversely, a short time of residence may easily polarize evaluation owing to the freshness of the residential environment. However, no significant correlation between residents' interest in CES and length of residence was observed in the present study, which can be attributed to the stability of the cultural service characteristics of the landscape in the residential green spaces of the 40 residential communities selected. In other words, established CES characteristics are difficult to change once the landscape is formed. Previous studies have reported that the landscapes in urban green spaces play an important role in improving the CES in an ecosystem ( 51 , 54 – 57 ). Given this fact, reasonable and scientific planning and design of the landscape become extremely important for the future. Nassauer et al. stated that the ecologically innovative designs of metropolitan residential landscapes were conducive to the enhancement of long-term cultural sustainability ( 58 ).

Age is the main influence on satisfaction with CES in residential green spaces in this study. The proportion of residents who were 21–29 years old demonstrated significantly negative correlations with recreation, aesthetics, neighborhood relations, stress-relieving features, and sense of belonging ( p < 0.001). This finding reveals that these young residents are the least satisfied with the different CES among the other residents of the community. This phenomenon can be attributed to the low satisfaction of this age group with the management and infrastructure of residential green spaces, which are key factors that determine residents' satisfaction with the CES in green spaces. The age group 21–29 years showed significantly negative correlations with the management and infrastructure of green spaces. Moreover, this age group was mainly composed of single individuals. Compared with married residents, single residents are less satisfied with CES and the surrounding residential environment ( 33 , 58 , 59 ). The respondents in the age group >50 years exhibited positive correlation with satisfaction regarding sense of belonging. Previous studies have reported that, compared with other age groups, older people possess a stronger sense of belonging ( 14 ) and aesthetic appreciation ( 60 ) of the urban environment, which can be attributed to their higher visit frequency to urban green spaces.

The low-income groups in our study demonstrated dissatisfaction with CES. The higher the proportion of residents with a 1,000–3,000 RMB income level, the lower the satisfaction with plant collocation. This result is consistent with the findings of Riechers et al., who discovered that residents with lower incomes had weaker natural cognition, cultural heritage, sense of social belongingness, and satisfaction with urban green spaces than those with higher incomes ( 14 ). Several studies have reported that low-income groups, or those with low socioeconomic status, were more frustrated than high-income individuals ( 28 , 61 ), which may affect their satisfaction with the surrounding green spaces and thus causes negative impacts on their health. Moreover, studies have proven that income level is positively related to interpersonal relationships and the physiological and psychological health of residents ( 28 ). However, the present study determined that the gender and cultural level of residents had no significant impact on satisfaction with CES in residential green spaces.

Cultural Ecosystem Services and Visit Duration in Residential Green Spaces

Urban residents frequently visit residential green spaces; hence, CES in the green spaces within residential areas cannot be ignored. In this study, ~40% of residents visited residential green spaces every day. The visit frequency of residents has been a focus of studies on CES in urban green spaces. The higher the visit frequency, the higher the CES level in the green spaces, which is because visiting green spaces is conducive to physiological and psychological health ( 29 , 42 , 62 , 63 ). Many studies have measured the CES level in green spaces using the visit frequency of urban residents ( 9 , 48 , 53 , 58 , 64 ). This study discovered that the visit frequency of residents showed no significant effect on their satisfaction with CES. This result is consistent with other studies, in which the visit frequency of residents to urban green spaces was discovered to have no significant correlation with the CES value ( 10 ), satisfaction with green spaces ( 6 ), or people's psychological health ( 47 ). Subjective evaluation of residents' demand for CES emphasizes the attributes of green spaces, such as their type, area, distance, and landscape pattern, whereas the evaluation of CES supply is influenced not only by the physical characteristics of green spaces but also by the individual differences of residents, such as age ( 14 ), individual emotional factors ( 6 ), social group ( 65 ), and even survey research methods ( 6 ). In this study, respondents belonging to the age group 21–29 years only occasionally visit green spaces. These respondents showed the lowest satisfaction with the aesthetics of the green spaces, which explains the correlation between visit frequency and CES.

Visit time, especially of 1–2 h of duration, is important in the investigation of the satisfaction with CES in green spaces. The proportion of residents in this study staying in the residential green spaces for this duration was high, and the satisfaction of these residents with the recreational services and stress-relieving features was proportionally high. Previous study have revealed that the visit time of residents and the flow duration of cultural services in the residential green spaces last for 1–2 h ( 6 ), and we also found that the proportion of residents visiting green spaces for 1–2 h was positively correlated with the percentage of residents walking ( Table 4 ). Walking was the main activity of residents staying for this duration, and this activity can greatly improve the physiological and psychological health of residents. However, many roads in residential areas have mixed purposes that include sidewalks, car lanes, facilities for bicycles and electric bicycles, and private car parking lots. In the 10 residential areas with the highest proportion of walking, six areas implement a sidewalk–car lane separated system. Although the remaining four areas adopt a sidewalk–car lane mixed system, large gardens or clustered green spaces hinder walking activities. Therefore, future planning and design of residential green spaces should create landscapes that are appropriate and safe for walking (e.g., designated sidewalks). If the green spaces in the community are limited, then public activity spaces should be enlarged to meet the residents' demands for walking activities.

Effects of Vegetation Coverage in Residential Green Spaces on Cultural Ecosystem Services

CES can be improved by increasing green coverage in residential green spaces. Increasing the area of urban green spaces can effectively optimize the biodiversity and carbon fixation of soils ( 66 ), regulate the urban microclimate, and reduce surface runoff. However, few studies have focused on the relationship between urban vegetation coverage and CES. Given similar demographic conditions, socioeconomic factors, and living conditions, residents have been found to be happier in larger surrounding green spaces and more satisfied with the surrounding environment than in smaller ones ( 67 ). The size of urban green spaces may directly influence their popularity ( 16 ). In this study, both objective and subjective green coverage were significantly related to total satisfaction with CES ( Figures 5 , 6 ). This inference can explain why residents show great concern with the green coverage in residential communities ( Figure 4 ). Natural vegetation is the source of CES that can increase spiritual and aesthetic services. High green coverage can provide many chances for residents to engage with nature and provide space for water bodies, in particular. In addition, public activity spaces are frequently used in residential communities to stimulate the residents' recreational activities: our study found that both the number and diversity of public activity spaces were higher in residential communities with high green coverage than in those with low green coverage.

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Figure 5 . Correlation between the total satisfaction on cultural ecosystem services (CES) and the real vegetation coverage.

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Figure 6 . Correlation between the total satisfaction on cultural ecosystem services (CES) and the proportion of residents who are satisfied with residential vegetation coverage.

With the increase in urban populations and the growing need for housing, urban residential areas are often dominated by high-density communities at the expense of green space. Hence, increasing CES and improving the living environment of residents in a limited green space are an important issue that must be addressed. We found that both residents' perception of plant decoration and landscape patterns in the residential green spaces could directly increase CES ( Tables 4 , 5 ). Several studies have suggested that vegetation characteristics (e.g., diversity, vegetation types, abundance, color, new species, morphology, density, and configuration structure) ( 7 , 16 , 37 ), spatial structure, and layout of urban green spaces ( 6 ) can influence CES. The close-to-nature attribute of green spaces has been widely accepted as an effective means to improve urban green spaces ( 9 , 16 , 37 ). Moreover, numerous studies have proved that the quality of green spaces is extremely important in improving the physiological and psychological health of residents ( 47 , 68 ). In this study, residential communities with high green coverage and large lawn areas are popular with residents owing to their accessibility and aesthetics. By contrast, dense shrub vegetation is not conducive to the improvement of green space CES owing to non-accessibility and the possibility of mosquito infestation. In Zhengzhou, half of the residential communities with high green coverage are dominated by dense shrub, which may be due to the low management cost, easy pruning, and accessible irrigation. Therefore, we recommend the cultivation of trees is economical and practical in dense urban residential areas. For communities with low green coverage, the lack of CES can be compensated for by increasing the public activity spaces.

Perception of Infrastructure and Management as the Key Influencing Factors of Cultural Ecosystem Services in Green Spaces

Infrastructure in residential green spaces includes public activity spaces (e.g., small squares, gardens, and pavilions), water facilities (e.g., fountains, pools, and artificial lakes), recreation facilities (e.g., fitness and integrated playground equipment), and artistic decorations (e.g., sculptures, chairs, streetlights, and other indicators). The results of this study suggest that satisfaction with the infrastructure in residential green spaces exhibits a significant positive correlation with the overall satisfaction with CES ( Figure 7 ). The positive effects of infrastructure and the convenience of urban green spaces in improving satisfaction with CES have been established by several research studies ( 10 , 13 , 34 , 59 , 69 ). Furthermore, public activity spaces in residential areas, especially green spaces in squares and gardens, can improve satisfaction with CES. These spaces were the second most important consideration of residents when selecting communities to live in, next to green spaces coverage. Moreover, the water facilities in residential green spaces, which is the fourth most important resident concern, can improve satisfaction with CES in green spaces ( Figure 4 ). Many studies have established the crucial role of wetlands (artificial or natural) in urban green spaces in improving CES ( 35 , 49 , 70 – 72 ). Plieninger observed that urban residents in Eastern Germany frequently visit water bodies ( 13 ) and often give a high evaluation ( 51 ). In summary, urban residents highly prefer wetland and water bodies. However, the water facilities in many communities in Zhengzhou are wasted or improperly managed. Therefore, residential green spaces should receive efforts to strengthen the layout and management of water landscapes and water facilities in the future.

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Figure 7 . Correlation between the satisfaction on cultural ecosystem services (CES) and satisfaction on management and infrastructure.

Management of residential green spaces could improve CES greatly in residential green spaces ( Figure 7 ). Many studies have proved that satisfaction with urban residential spaces is closely related to a graceful visual landscape ( 34 , 37 ). However, the management of green spaces, such as irrigation, clipping, cleaning, and tidying, can directly influence the aesthetic characteristics of green spaces. These characteristics ( Figure 8 ) include (1) cleanliness, which is the top concern of residents ( 9 ) and can directly influence the satisfaction with the residential environment ( 59 ); (2) standardization, which involves preventing the use of green spaces for other purposes, such as hanging out clothes and providing parking lots for bicycles, electric bicycles, and even motor vehicles; and (3) uneven heights of vegetation, drought events, and weed spreading, which may be present in residential green spaces owing to inadequate daily management (e.g., lack of clipping, irrigating, and weeding). Management was the third concern of residents in residential green spaces ( Figure 4 ): therefore, additional attention and effort should be dedicated to performing regular high-quality maintenance and management of residential green spaces in the future.

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Figure 8 . Differences in the management level between the residential communities with the lowest (above) and highest (below) satisfaction on the cultural ecosystem services (CES) in green spaces.

Limitations

Our study has several major limitations. This study only selected five types of CES, namely, leisure and entertainment services, spiritual services, aesthetic services, sense of belonging, and social relations. Other CES (e.g., landscape identity, education, history, religion, and heritage values), which are popularly involved in other research, were not included in our study. The main reason for this exclusion was that the residential areas selected in this study were built only after 2000. We hypothesized that the values of cultural heritage, education, history, and religion would be relatively weak. All 40 residential areas are located in the populated areas of Zhengzhou, which are mainly characterized by dense buildings, as determined by the socioeconomic status levels of developing countries. Future studies should explore the influences of spatial infrastructure arrangements in green spaces on CES, including vegetation type, quantity and area of public activity spaces, type and amount of infrastructure, form and area of water landscapes, and other objective factors. Moreover, landscape and species composition and structure (landscape and vegetation) should also be investigated because such factors could influence residents' contribution to CES in the residential green spaces. The answers to these issues could provide direct scientific references for the landscape planning and design of residential green spaces. Moreover, we chose 40 residential areas within neighboring cells to ensure a sufficient sample size (number of families > 600) and minimize the impact of the surrounding environment on the CES satisfaction of residential green spaces. However, these residential areas include high-rise buildings (>18 floors), mid-rise buildings (7–18 floors), and low-rise buildings (4–6 floors) and are characterized by various types and styles of buildings. These conditions may have affected residents' direct perception and satisfaction with green space landscapes. We suggest that future research focuses on residential areas with consistent socioeconomic levels, including housing prices, architectural styles, green space coverage, management levels, geographical locations, and surrounding green space distribution, to explore the rational arrangement of the green space landscape pattern in a limited space. Such selection will further improve the green space ecosystem services and human well-being and provide a direct theoretical basis for the spatial planning and design of urban green space landscapes.

Conclusions

Exploring CES in residential green spaces could greatly enrich urban ecosystem services research. The most important research is to clarify the relationship between ecosystem services and human well-being. In this study, we found that walking, childcare, and resting were the most common recreational activities of residents. The results of the analysis show that satisfaction with recreational services in the residential green spaces was the lowest (6.26, 1–10), which can be attributed to the absence of public activity spaces. In contrast, satisfaction with neighborhood relations and the sense of place was the highest at 7.73 and 6.81, respectively, followed by aesthetic services (6.59), indicating that the spiritual and aesthetic services in the residential green spaces are excellent. Age and income status can influence residents' satisfaction with CES: young individuals (21–29 years old) expressed the lowest satisfaction with residential green spaces than did other groups, which might be influenced by their single status and their low satisfaction with the infrastructure in the residential environment.

Satisfaction with CES significantly increased with vegetation coverage, indicating that green vegetation is a source of high CES satisfaction. Compared with other factors, high green coverage is mostly preferred by residents. In addition, public activity spaces, management, infrastructure, and water landscapes are the other key influencing factors of CES satisfaction. Therefore, to maximize CES in residential green spaces, we suggest that public activity spaces should be increased and the daily management of residential areas should be improved when green coverage is limited. Moreover, basic facilities, particularly water landscapes, should be encouraged during the planning and design of residential green spaces. These steps are more effective and realistic in improving the CES of green spaces within areas of dense building density than increasing green space areas.

We suggest that the subjective indicators perceived by residents contribute more to CES than the objective physical environment of residential green spaces. The main reason is that CES refers to human well-being provided by green spaces, which implies residents' demand for green spaces. Future research on the relationship between green spaces' characteristics and CES should consider the physical environment (e.g., biodiversity, green space coverage, species matching, and landscape characteristics) preferred by residents, especially the gaps between the actual and the preferred characteristics favored by residents. For example, understanding the socioeconomic attributes of CES could clarify the demand characteristics of different social groups for urban green space. We suggest future research should pay more attention to different social groups' diverse demands of CES, for example, the use characteristics of the different types of urban green spaces and the diverse landscapes of the same green type. Such consideration will help ameliorate the existing planning and management of urban green spaces, maximize CES, and then protect human health. We suggest the future evaluation of urban green spaces should combine the residents' perception of demand and supply of CES, clarify the gap and trade-off between them, and then determine the key elements that affect the demand of residents, which is the fundamental purpose of urban ecosystem service research. We suggest that the answers to the above research questions will help provide constructive suggestions for building a multifunctional urban green space landscape, which is a path to urban environmental equality and a sustainable urban landscape.

Data Availability Statement

The raw data supporting the conclusions of this article will be available from the corresponding author upon reasonable request.

Author Contributions

All authors listed have made a substantial, direct and intellectual contribution to the work, and approved it for publication.

This work was supported by the Chinese National Natural Science Foundation under Grant Nos. 31600375, 31872688, and 41901238 and the Key Scientific and Technological Project of Henan Province (192102310003).

Conflict of Interest

The authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

Acknowledgments

We would like to thank Tingzhen Zhang, Yizhen Hong, and other students from the Department of Resource and Environmental Science, Henan University of Economics and Law, for their contributions to the survey during 2017–2018. We are also grateful to the reviewers for their valuable comments that helped improve this manuscript.

Supplementary Material

The Supplementary Material for this article can be found online at: https://www.frontiersin.org/articles/10.3389/fpubh.2020.00226/full#supplementary-material

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Keywords: cultural ecosystem services, residential districts, green space, satisfaction, physical environment

Citation: Mao Q, Wang L, Guo Q, Li Y, Liu M and Xu G (2020) Evaluating Cultural Ecosystem Services of Urban Residential Green Spaces From the Perspective of Residents' Satisfaction With Green Space. Front. Public Health 8:226. doi: 10.3389/fpubh.2020.00226

Received: 12 December 2019; Accepted: 14 May 2020; Published: 17 July 2020.

Reviewed by:

Copyright © 2020 Mao, Wang, Guo, Li, Liu and Xu. This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY) . The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.

*Correspondence: Guanghua Xu, guanghua0418@163.com

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At the Center for Quantum Nanoscience (QNS), nestled in the hilly campus of Seoul’s Ewha Womans University, director of operations, Michelle Randall, shows off the facilities. “This is where we isolate our scanning tunnelling microscopes (STM) from any vibrations,” she says, pointing to an 80-tonne concrete damper, a mechanism that reduces interfering movements to near zero. Researchers at QNS are using STMs to image and manipulate individual atoms and molecules, chasing breakthroughs akin to last year’s assembly of a device made from single atoms that allows multiple qubits — the fundamental units of quantum information — to be controlled simultaneously ( Y. Wang et al. Science 382 , 87–92; 2023 ). The work, done by QNS in collaboration with colleagues in Japan, Spain and the United States, could have applications in quantum computing, sensing and communication.

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thesis cultural ecosystem services

Nature Index 2024 South Korea

The diversity of the QNS team offers a glimpse of what research looks like in a country that is betting big on international collaboration. For 2024, South Korea has more than tripled its budget for global research and development (R&D) collaboration, committing to 1.8 trillion won (US$1.3 billion), up from 2023’s 500 billion won. The investment, which represents an increase from 1.6% to 6.8% of the government’s overall R&D budget, could see a shift away from using metrics such as university rankings, quantified research outputs and international student and faculty recruitment in favour of boosting ties with leading overseas research institutions in strategic areas. “There’s a huge amount of money that has suddenly been assigned to international research. With this comes many opportunities,” says Meeyoung Cha, scientific director of the Max Planck Institute for Security and Privacy, in Bochum, Germany, who holds joint positions at the Korea Advanced Institute of Science and Technology (KAIST) and the Korean Institute for Basic Science, in Daejeon.

The budget increase is part of the Korean Ministry of Science and ICT’s (MSIT) wider R&D Innovation Plan, announced in November 2023 . It includes a new Global R&D Strategy Map, which will guide tailored collaboration strategies with specific countries based on their strengths in 12 critical and emerging technologies, such as semiconductors, artificial intelligence (AI) and quantum science. Industry strengths in 17 technologies related to achieving carbon neutrality and mitigating climate change will also be considered. In addition, MSIT has amended laws to allow overseas research institutions to directly participate in state R&D projects and aims to develop Global R&D Flagship Projects in key areas that will receive prioritized allocation of government funds.

Such moves are designed to refocus South Korea’s R&D, which has become stagnant over the past decade, according to MSIT, despite the country being the world’s second highest spender on R&D as a percentage of GDP, after Israel. In 2023, South Korea’s legislative national assembly approved a 14.7% cut to the overall 2024 R&D budget, from 31.1 trillion won in 2023. The cuts include shifting some more general funds for universities to a separate budget.

Students wait in line to submit their applications at a local job fair

Foreign students line up to submit their applications at a job fair in Busan, South Korea. Credit: YONHAP/EPA-EFE/Shutterstock

“It seems that the term ‘budget cut’ really means redistributing money to more applied projects and international research initiatives,” says computational biologist, Martin Steinegger, based at Seoul National University. Steinegger experienced a 15–25% reduction in existing grants, paid annually from the National Research Foundation of Korea, the country’s main funding agency. This forced him to reduce conference travel for his students and use older hardware for research. “I have effectively less money than I did last year, but I can apply to many new things, it seems,” says Steinegger.

Changes could come next year, as South Korea continues to adjust its spending in science. In June, the government proposed a record 24.8 trillion won for R&D focused on basic and applied scientific research in 2025 , which is up from 2024’s 21.9 trillion won, although further details were not available at the time of writing.

Global collaborator

Off the back of such policy shifts, becoming the first Asian country to join the European Union’s Horizon Europe programme, the world’s largest research-funding scheme, is a major win for South Korea. Announced in March, the new partnership will drive collaborations between South Korean and European researchers in areas such as quantum technologies, semiconductors and next-generation wireless networks. South Korea is also forging bilateral cooperation agreements across Europe, such as with Denmark on clean-energy technologies and Germany on basic sciences, including the launch of a joint centre with the Max Planck Society, Germany’s flagship basic-research organization, at Yonsei University in Seoul.

Taking on more joint projects with Europe could help to diversify South Korea’s internationally collaborative outputs in the Nature Index. The United States, which has deep historic ties with South Korea dating back to the Korean War in the 1950s, is the country’s most important research partner in natural-sciences output, with a collaborative Share — a measure of joint contribution to research tracked by the Index — of 639.94 in 2023. China forms South Korea’s second-strongest partnership, with a collaborative Share of 300.81, followed by Japan, at 114.88 (see ‘Research ties’).

The number of natural-sciences articles in the Nature Index that have been co-authored by China- and South Korea-based researchers has grown considerably in recent years, up 222% between 2015 and 2023, compared with US–South Korean output, which dropped by 4% over the same period. But South Korean researchers report that collaborations with China are becoming more difficult, particularly in technology areas. According to data from South Korea’s national police agency, of the 78 cases of industrial technology leaks recorded between 2018 and mid-2023, 51 involved leaks to places or people in China. There is now also more oversight of collaborations with China than with other major research partners. “Researchers occasionally receive requests from their institutions or the government asking who is collaborating with China, says Cha. “They are aware that any collaboration may be monitored, creating a sense of censorship.”

In order to minimize its exposure to any supply-chain disruptions or political risks associated with ongoing US–China tensions, South Korea must look farther afield when establishing research links, says Lee Myung-hwa, who studies policy and innovation at the Science and Technology Policy Institute think tank, in Sejong. “The key is building trust with collaboration partners, which needs to be long-term, stable and maintained without being swayed by policy directions,” she says.

Cha highlights southeast Asia, a region that has long been of strategic and diplomatic interest to South Korea, as a place with untapped potential for joint innovation projects. “For instance, in Indonesia, there’s no governmental institution in charge of AI,” she says, which could open up the possibility of future collaborations around ethical and strategic development of AI technologies.

In 2023, the South Korean government committed to boosting cooperation with southeast Asia in areas including cybersecurity and communications technologies, and with individual nations, such as Vietnam, to help advance digital transition and clean-energy sectors. “Huge collaboration could happen if we work together,” says Cha.

Domestic challenges

With more than 10 million visitors moving between southeast Asian nations and South Korea each year, the region could also be important to South Korea in dealing with its dual demographic challenge: attracting overseas scientists in a country that is traditionally conservative towards immigration, and retaining homegrown talent. Solving these problems is paramount, as South Korea contends with the world’s lowest birthrate, driven by factors such as the rising costs of housing, education and childcare, a highly competitive and demanding work culture, and gender inequality issues, including the biggest gender pay gap among Organisation for Economic Co-operation and Development members. Student numbers are also in steep decline, which is putting some universities at risk of closure. An analysis of 195 Korean universities published by Seoul-based institute Jongro Academy in March showed that 51 had failed to fill their enrolment quotas for 2024. Of those, 43 were located outside the Seoul metropolitan area, accounting for 98% of the total unfilled seats.

To boost numbers, the South Korean Ministry of Education has announced new initiatives, including annual financial support for master’s, doctoral and postdoctoral researchers. These measures, which are part of the overall R&D budget, aim to incentivize mostly local students to continue their careers in research. For foreign students, the ministry wants to attract 300,000 of them by 2027 through its ‘Study Korea 300K Project’. Students will be targeted at events and language centres abroad and science graduates may be offered an easier pathway to permanent residency and South Korean citizenship. Language proficiency requirements for admission will also be reduced. Scholarship programmes are being expanded, including the government-funded Global Korea Scholarship invitation programme, which will increase recipient numbers from 4,543 in 2022 to 6,000 by 2027. The ministry has identified India and Pakistan in particular as important sources of science and engineering talent.

It’s unclear whether efforts to attract international students will bring more of a spotlight to the challenges faced by those who are already in the country. Lewis Nkenyereye, who studies computer and information security at Sejong University in Seoul, expresses concern for the many foreign students who work part-time to satisfy the minimum bank balance requirements of their enrolments. Language barriers and administrative hurdles have led to some of them being deported for not having adequate permits, says Nkenyereye, who is originally from Burundi. “The government is aware that most foreign students have part-time jobs and should adapt its policies to better accommodate their needs,” he says.

Religious and cultural differences also pose difficulties. Muaz Razaq, a student, who left Pakistan to pursue his PhD in computer science at Kyungpook National University in Daegu, is involved in a small mosque-reconstruction project next to his university that has ignited strong opposition from segments of the local community. Razaq says he’s heard many stories from other Muslim students across South Korea who describe being taunted by their peers over food choices and who lack designated spaces for practices such as ablution before prayers.

Challenging conditions for foreign students might be contributing to South Korea’s low levels of retention after graduation. According to a 2022 report by the Korea Research Institute for Vocational Education and Training in Seoul, the number of foreign students that are earning doctorates in South Korea quadrupled in the period 2012 to 2021. But the proportion of foreign students who returned to their home country after graduation has consistently increased, from 40.9% in 2016 to 62.0% in 2021.

A stacked bar chart showing the proportion of South Korea’s internationally collaborative output in Nature Index in 2023, compared to the five leading countries in the database.

Source: Nature Index

It is hoped that government-funded initiatives such as the Brain Pool programme, which gives doctoral researchers access to up to 300 million won annually for three years, and Brain Pool Plus, which offers outstanding researchers with expertise in core technology fields up to 600 million won annually for up to ten years, can help to attract and retain foreign talent. MSIT also plans to introduce support programmes to help new arrivals settle in and build networks.

Recent updates to visa rules for foreign researchers and students could make it easier for universities to attract overseas talent. In July, the Korean Ministry of Justice, which oversees immigration, greatly expanded the number of universities that are eligible to recruit foreign postgraduate and undergraduate students on D-2-5 research study visas and waived the three-year work-experience requirement for international master’s and PhD holders to obtain E-3 research visas.

New opportunities

The relatively low levels of English used at South Korean universities and research institutions is a major hurdle in the country’s drive towards internationalization. The number of university courses taught in English has increased in recent years, but Korean remains the primary language of instruction at many institutions. This affects foreign researchers at all career stages because they often require help from others or full-time assistance to navigate the environment, particularly in administrative matters, says Steinegger, who can manage daily life in Korean, but needs staff to help him with paperwork.

Seoul Robotics, a company that develops AI-powered software for autonomous driving and traffic management, has mandated an English-speaking work environment to attract international talent. Such a culture is unusual in South Korea; although many companies have English-speaking requirements, these are often not enforced, says Evan Thomas, business development manager at Seoul Robotics. “The ability to communicate in English without constant translation and cultural interpretation has been a significant advantage compared to more traditional South Korean companies,” he says.

Cultural attitudes towards foreigners can also hinder long-term retention, says Thomas. “Many South Koreans view foreigners as temporary visitors rather than potential long-term residents, discouraging them from settling in,” he says. A 2023 survey by the Korea Institute of Public Administration, a government-sponsored research institute in Seoul, seems to back this up, reporting that less than half of the respondents say they accept foreign nationals as members of South Korean society.

Given the shortages of local staff that are being recorded in strategic industries such as semiconductors and AI, it’s a problem that South Korea needs to address. Another report, by the University of Science and Technology in Daejon and the Korea Industrial Technology Association in Seoul, found that just 24% of 300 South Korean companies surveyed had foreign staff. Many cited a lack of information about foreign students as the reason, suggesting that there is a disconnect between academia and industry regarding graduate careers.

Hong Bui, a student from Vietnam, accepted a postdoctoral position at the Swiss Federal Institute of Technology Zurich in April, after completing her PhD at QNS. Bui cites the limited permanent career opportunities that are available to international researchers in Seoul as one of her reasons for wanting to leave, despite having a positive experience in QNS’s internationally focused environment. “South Korean companies often value overseas experience more than domestic experience, and many workplaces require Korean language proficiency,” she says.

As South Korea devotes record levels of resources to building ties with overseas institutions and attracting foreign researchers and students, its leaders hope that stronger research performance and innovation prowess will follow. But the success of such efforts hinges on the country’s ability to foster a more diverse research ecosystem, with fewer cultural challenges for foreigners to contend with.

“If the barriers are lowered and support is provided for overseas researchers to utilize South Korea’s leading research facilities and equipment, I think South Korea will become an attractive country for conducting research activities,” says Lee.

Nature 632 , S2-S5 (2024)

doi: https://doi.org/10.1038/d41586-024-02685-y

This article is part of Nature Index 2024 South Korea , an editorially independent supplement. Advertisers have no influence over the content. For more information about Nature Index, see the homepage .

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IMAGES

  1. A conceptual framework for cultural ecosystem services. Source: Fisher

    thesis cultural ecosystem services

  2. (PDF) Evaluation of Cultural Ecosystem Service Functions in National

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  3. (PDF) Mapping cultural ecosystem services in the Wet Tropics

    thesis cultural ecosystem services

  4. (PDF) Cultural Ecosystem Services Research Progress and Future

    thesis cultural ecosystem services

  5. A cultural ecosystem service perspective on the interactions between

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  6. (PDF) The Integration of Cultural Ecosystem Services and Cultural

    thesis cultural ecosystem services

COMMENTS

  1. Cultural ecosystem services: A review of methods and tools for economic

    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.

  2. A systematic review of cultural ecosystem services and human wellbeing

    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 et al., 2005, Milcu et al., 2013) provided the basis ...

  3. Cultural ecosystem services: Characteristics, challenges and lessons

    While the MEA (2005) defined ecosystem services as benefits people obtain from ecosystems, ecosystem 'services' have also been variously defined as being: the ecosystem processes or functions that underpin benefits (Chan et al., 2012b, Mace et al., 2012); ecosystem assets that are used directly and/or are of benefit to humans (Wallace, 2007 ...

  4. The Role of Tourism Impacts on Cultural Ecosystem Services

    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.

  5. 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 ...

  6. The contribution of cultural ecosystem services on tourism: a review

    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.

  7. Cultural ecosystem services and decision‐making: How researchers

    Cultural ecosystem services (CES) are "ecosystems' contributions to the nonmaterial benefits … that people derive from human-ecological relations" (Chan et al., 2011, p. 206). Whether or not people are familiar with the term, the concept resonates with nearly every human being, though precisely what resonates varies between people.

  8. Frontiers in Cultural Ecosystem Services: Toward Greater Equity and

    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 ...

  9. Cultural Ecosystem Services of Urban Green Spaces. How and ...

    Analysis and aggregation of the methodology to assess cultural ecosystem services were supported by German Academic Exchange Service - DAAD (Program of East Partnership) project between Humboldt University Berlin and Lomonosov Moscow State University "Urban ecosystem services and their assessment: exchange of experiences between Germany and ...

  10. PDF Exploring the potential of cultural ecosystem services in social impact

    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.

  11. Cultural Ecosystem Services: A Literature Review and Prospects for

    Cultural ecosystem services constitute a growing field of research that is characterized by an increasing number of publications from various academic disciplines. ... Navigating marine ecosystems services and values. Master of Science thesis. Faculty of Graduate Studies, Resource Management and Environmental Studies, University of British ...

  12. (PDF) Cultural Ecosystem Services of Urban Green Spaces ...

    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 ...

  13. (Pdf) Overview Analysis of Cultural Ecosystem Services: Mapping

    Mapping of Cultural Ecosystem Services (CES) emphasizes the spatial contribution to landscape characteristics like land cover and human wellbeing. This review paper aims to build an overview of ...

  14. Evaluation of cultural ecosystem services using GIS

    "Valuation of cultural ecosystem services based on contributions to quality of life" at Lund University. In this thesis, Cultural Ecosystem Services (CES) are evaluated from people's own perceptions. The very aim of the study is to develop a method to assess CES non-monetarily by using a bottom-up perspective.

  15. The importance of cultural ecosystem services in natural resource

    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 ...

  16. Resilient Geographies: An Atlas of Cultural Ecosystem Services in the

    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 ...

  17. Valuing Cultural Ecosystem Services

    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 ...

  18. Cultural Ecosystem Services of Urban Green Spaces. How and What People

    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 ...

  19. The inclusion of stakeholders and cultural ecosystem services in land

    Cultural ecosystem services can be more important to people than ecosystem services from other categories (Raymond et al. 2009; ... M.Sc. Thesis, Royal Roads University. Darvill R, Lindo Z (2015) Quantifying and mapping spatial ecosystem service use locations across stakeholder groups: implications for conservation with priorities for cultural ...

  20. Cultural ecosystem services of Chinese typical landscapes: Rethinking

    Synthesizing the findings of this research, there are several conclusions we can draw: 1) In general, Aesthetic services, Recreational services, Education and science, Inspirations, Sense of place, Cultural heritage, Religious and spiritual services and Physical and mental health are all highly perceived in China's typical landscapes ...

  21. The role of cultural ecosystem services in landscape management and

    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 ...

  22. Frontiers

    Introduction. The ecosystem services of urban green spaces can be defined as services that improve the welfare of urban residents who enjoy green spaces ().These services include support, regulation, supply, and cultural ecosystem services (CES) ().CES can be provided by green spaces for leisure, tourism, cultural education, aesthetic appreciation, and spiritual needs (), all of which account ...

  23. What will it take to open South Korean research to the world?

    Efforts to join the global ecosystem depend on greater diversity and a more open culture.

  24. Classifying and valuing ecosystem services for urban planning

    Highlights Urban ecosystems provide multiple ecosystem services for human well-being and can increase resilience to shocks. Loss of urban ecosystems involve long-term economic and insurance costs and can affect many social and cultural values. Valuation should not only take into account benefits from ecosystem services but also costs from ecosystem disservices. Economic and non-economic values ...