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ORIGINAL RESEARCH article

Front. Ecol. Evol., 15 April 2022
Sec. Conservation and Restoration Ecology
This article is part of the Research Topic Ecosystem Services, Policy, and Human Well-Being View all 8 articles

Ecosystem Services and Human Wellbeing-Based Approaches Can Help Transform Our Economies

  • 1Research Institute for the Environment and Livelihoods, Charles Darwin University, Darwin, NT, Australia
  • 2College of Science, The Australian National University, Canberra, ACT, Australia
  • 3Institute for Global Prosperity, University College London, London, United Kingdom

Despite wider recognition of human interdependence with the rest of nature, our economies continue to fail to adequately value ecosystem services. This failure is largely attributed to the economic frameworks and related measures that focus on the production and consumption of marketed goods and services, but do not consider the other essential elements upon which our lives depend. This paper highlights how the Ecosystem Services approach can shift the focus to human wellbeing while remaining within biophysical planetary boundaries. An Ecosystem Services approach applies three fundamental principles of Ecological Economics: sustainable scale, efficient allocation, and fair distribution, which are vital for sustainable economies and societies. We provide case studies, from both a local and national scale, demonstrating how such an approach offers a holistic perspective of understanding what “development” actually means. Transforming our economies to appropriately consider planetary limits, overcome societal addictions, learn from Indigenous and local communities about ways of sustainable living, and realizing the importance of ecosystem services will contribute to developing economies that are resilient, and that enhance sustainable human wellbeing.

Introduction

Over the past 50–60 years of extensive use and exploitation, natural resources have become severely limiting. Coupled with rapid climate change, the situation at present is alarming if we are to sustain modern economies at the same pace as has happened in recent decades (Daly, 1996, 2015; Costanza et al., 1997, 2014a; Millennium Ecosystem Assessment [MA], 2003, 2005 and various reports by the Intergovernmental Panel on Biodiversity and Ecosystem Services (IPBES) including a conceptual report in Intergovernmental Platform on Biodiversity and Ecosystem Services [IPBES], 2019a). Yet, our modern economies persist with their old tools and measures such as GDP, focusing on marketed production and consumption, with little consideration of degrading natural resources and related consequences for human health and wellbeing, and the mounting threats to the survival of civilization. The current settings have led us to operate within a very much “engineered economy”—based on GDP measures, which focuses on increasing choices of materials, while excluding, disregarding, and exploiting the very foundation that delivers those materials (Costanza et al., 2014a), and ignoring the economic ethics for people and the planet (Sen, 1989, 1999a,b).

Many natural scientists, some progressive economists, and ecological economists (trans-disciplinary professionals who focus on linking nature and economies) have been calling for a transformation to reform modern economic approaches so that future policies and programs are designed to enhance human wellbeing, not utility, choices of materials, or production values. Human wellbeing, beyond income, materials, or resources, encompasses the fair, equitable, and ethical principles of a society, living sustainably and in harmony with nature (Sen, 1989; Daly, 1996). Costanza et al. (2014a) argued that GDP ignores those broader aspects of human wellbeing such as social costs and environmental impacts, leading to the continued destruction of natural resources on which all life on this planet depends. The authors further state that “GDP is dangerously inadequate as a measure of “quality of life”— the latter indeed should be the focus for our modern economies, not the utility values or production as is the case now.

The key question we face at present is: How to re-design and re-shape modern economies to appropriately incorporate the role of nature in supporting and developing sustainable, wellbeing-based economies? This is an essential mission so that future programs and policies focus on sustainable “development” that is within the ecological boundaries of planet earth. Addressing this issue of transforming modern economies further requires the comprehension of “development” beyond “increasing utility/materials choices.” The economics Nobel Laureate, Prof Amartya Sen says that development is about enabling people to lead the lives that they want to lead, with freedom and choice, i.e., enhancing overall human wellbeing, including social, natural, and other ethical considerations (Sen, 1989). The challenge is how to achieve development that is sustainable, equitable, and efficient.

Recently, with the COVID-19 pandemic, many local, regional, and national governments are considering reconstructing their economies. Some are using the opportunity to be innovative, and are investing in regenerative, green, circular economies, for example the European Union has drafted a circular economy strategy for recovery from COVID-19 related economic crisis (Material Economics, 2021), while many others, such as Australia, are still following the conventional approach with little changes, if any. This paper offers practical insights as to how such a transformation can be realized, i.e., by focusing on human wellbeing-based economies and applying ecosystem services (ES) approaches while acknowledging the planetary limits. It further demonstrates the application of proposed transformative economies at a local scale—a case study of Indigenous fire management in northern Australia; and at a national scale—the kingdom of Bhutan where the Gross National Happiness index is preferred over Gross Domestic Product to measure economic progress and that index is now playing a key role in determining country’s future policies and programs.

How to Transform Modern Economies?

A key factor for the continuity of conventional economies to date is the GDP against which countries compare each other’s progress. In recent years, some alternative metrics have been proposed for GDP which focus on 1. Adjusting GDP: for example, the Gross Progress Indicators which included all spending by individuals, volunteer work, etc. (Talberth et al., 2007; Kubiszewski et al., 2013); 2. Subjective measures of wellbeing: for example, the World Values Survey1; and, 3. Composite measures: for example, the Inclusive Wealth Index including manufactured, human and natural capitals2 (by the UNEP; United Nations University–International Human Dimensions Programme [UNU-IHDP] and United Nations Environment Programme [UNEP], 2014), or the Happy Planet Index which includes life satisfaction, expectancy and ecological impact3, or the System of Environmental-Economic (SEEA) Ecosystem Accounting which includes accounting for the ecological assets and ES (United Nations, 2021). These alternative measures are discussed by Costanza et al. (2014a), however, as the authors indicate, none of these measures is uniformly accepted as a clear alternative to GDP for reasons including bureaucracy, tendency of academics and government professionals to work in isolation, or a lack of acceptance of the diversity and complexity that exists among various human societies.

The role of nature for sustaining modern economies is now well recognized, including a recent report on “the economics of biodiversity: the Dasgupta review” (DasGupta, 2020) asking businesses to put biodiversity at the top of the ladder when developing business plans; the UN-led initiatives such as the Finance Initiative (since 1992); the Intergovernmental Platform on Biodiversity and Ecosystem Services (Intergovernmental Platform on Biodiversity and Ecosystem Services [IPBES], 2012 onward); and the Millennium Ecosystem Assessment (MA; 2000–2005). Many studies have demonstrated that human—nature connections enhance human wellbeing (Costanza et al., 1997, 2007, 2018; Millennium Ecosystem Assessment [MA], 2005; Intergovernmental Platform on Biodiversity and Ecosystem Services [IPBES], 2019b; many others). Some global institutions have recently formed a Taskforce on Nature-related Financial Disclosures (TNFD) which supports a shift, in global financial flows, from nature negative- to nature-positive outcomes by reducing the risk to natural assets4. To continue enhancing the wellbeing of people, nature and its resources need to be managed appropriately to ensure the delivery and flow of ecosystem services (ES)—the services and goods humans receive from functioning ecosystems (Costanza et al., 1997). These ES include direct and indirect contributions of nature toward human wellbeing. Including the role of ES in policy decision making is crucial at present, particularly for designing transformational sustainable economies. We posit that the ES approach can assist in this transformation toward sustainable economies.

Understanding the importance of ES, their sources, limits, and levels of supply or flows, at a sustainable level, can help us plan for “development” for present and future generations, that operates within planetary boundaries, reduces the risks from climate change, natural hazards (cyclones, floods, storms, bushfires, sea-level rise, etc.), and contributes toward better-managed biodiversity, soil and water resources (Costanza et al., 2017a). However, we acknowledge that the connections between ES and human wellbeing are complex, dynamic, and require a pluralistic approach for measuring and/or understanding the interactions (Figure 1; Costanza et al., 2017a).

FIGURE 1
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Figure 1. Complex and dynamic interactions between natural capital and build, human, and social capital, which generate ES for enhancing human wellbeing (Costanza et al., 2017a).

The Ecosystem Services approach provides us with a lens to view of how nature forms the foundation of the economy. Meadows et al. (1972) [The first “limits to growth” report], Daly (1973; 1991; 1996; 2005; 2015), Daly and Farley (2011), Costanza et al. (2014b,2018); Costanza (2020), and others have suggested that our social, built, and human capitals are indeed embedded in the rest of nature or natural capital (Figure 2). The ES approach affords tools and techniques to understand the value of ecosystems and their services that support modern economies, for influencing policies, governments, and other organizations (for various valuation approaches, see Millennium Ecosystem Assessment [MA], 2003, 2005; Intergovernmental Platform on Biodiversity and Ecosystem Services [IPBES], 2019a,b; and many articles published in the journals of Ecological Economics, Ecosystem Services, and others). This approach has evolved significantly over the past 20 years since its inception and is effectively contributing to bridge the gap between economics and ecology (Costanza et al., 2017a). Importantly, it has also been contributing to influence policy decision making at many local, national, and global scales. For example, at a local scale, the United States state of Vermont developed a “Common Assets Trust” which aims to sustainably use, manage, and protect State’s natural assets through establishing a Trust under eight key guiding governing principles (Farley et al., 2015; Costanza et al., 2021). At a broader national scale, several European countries have conducted their National Ecosystem Assessments to date, e.g., the United Kingdom, Spain, Portugal, Norway, Germany, the Netherlands, and Finland, which inform their policies to protect and sustain ES (Schröter et al., 2016). There are also targeted policies, applied at various national and global levels, such as REDD+ (Reducing Emissions from Deforestation and Forest Degradation).

FIGURE 2
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Figure 2. Natural capital as the foundation for social, built, and human capitals, the latter are typically considered for measuring economy, however, the foundation is omitted. It is important to note that interactions between different capitals deliver human wellbeing—a much better target to improve and measure economies (adapted from Costanza et al., 2014b).

A major global effort to apply the ES approach was the Millennium Ecosystem Assessment (MA) program from 2000 to 2005. The MA proposed a framework to assess and link the role of ES with human wellbeing (Millennium Ecosystem Assessment [MA], 2003). In 2010, the MA research was followed by IPBES, especially for connecting science with policy (Intergovernmental Platform on Biodiversity and Ecosystem Services [IPBES], 2019b). As of March 2022, 137 nations are signatories to the IPBES. The Platform particularly emphasizes the inclusion of nature and its resources in the public and economic policy domains through developing targeted policy documents and frameworks. However, none of these frameworks directly account for or extend the role of nature and its ES for the modern economy frameworks, which can be assisted by the ES approach. Transforming the existing economic frameworks, applying the ES approach for appropriately incorporating and integrating the role of nature, considering planetary boundaries, for policy decision making and future development programs, can deliver this much needed change.

Overall, the ES approach:

1. Supports an integrated, long-term, perspective for including efficient allocation, equitable distribution, and sustainable use of resources, for enhancing human wellbeing;

2. Highlights and integrates the importance of nature and its services for policy decision making on economies and development; and,

3. Evaluates how nature and its services contribute toward human wellbeing which typically remain unaccounted for in the present economic frameworks.

The ES approach can be applied in a stepwise process. The first step is a state or local scale economic assessment for evaluating the status of ecosystems and their services. The second step integrates that ecosystem assessment into built, human, and social economies, including embedding the cost of polluting, extracting, and mining natural resources. And the last step re-designs economies by incorporating ES assessments and containing each sector within the limits of ecological boundaries. This ensures the development of circular, desirable, and sustainable economies. Currently, several European countries (e.g., the United Kingdom, Scotland, Spain, Finland) and others have conducted the assessments of ecosystems and their services, following the Millennium Ecosystem Assessment [MA] (2003) [various MAES (Mapping and Assessment of ES) reports by the European Commission since 2005, e.g., Maes et al., 2012; URL: https://biodiversity.europa.eu, with a recent report published in 2018]. However, integration of ES assessments with the state economies is still lacking which can inform the type, extent, and expansion of different economic activities in each sector i.e., built, social, human, and natural systems.

Case Studies Demonstrating ES-Based Sustainable Economies

Application of the Ecosystem Services Approach to Understand Indigenous Peoples and Local Communities’ Economies

Many Indigenous peoples and local communities (IPLCs), across the globe, directly depend on nature and its services for a range of their economic and livelihoods activities. However, most of their economic activities flow outside the standard market mechanisms and remain unrecognized and unaccounted for in formal economic approaches and frameworks. Thus, the value of people’s local economies and their role in affording wellbeing is largely overlooked when planning for policies or programs, especially in developed countries.

In Australia, Indigenous peoples’ connections with country (i.e., traditional or clan land with which people have familial connections), and associated benefits for wellbeing are well documented (Grieves, 2007; Russell-Smith et al., 2009, 2013, 2015; Altman et al., 2011; Sangha et al., 2011, 2017, 2021). Yet, various state/territory and federal government agencies fail to incorporate these connections in Indigenous welfare, health, education, and employment policies (Grieves, 2007; Sangha et al., 2019). We here present the value and importance of these connections for Indigenous peoples living in the Northern Territory, Australia. We further illustrate how understanding such connections can create economically viable, culturally appropriate, country-based, sustainable economies that enhance Indigenous peoples’ wellbeing as well as maintain the flow of ES that contribute toward the wellbeing of wider Australian and global public.

The Northern Territory (NT) is the only place in Australia where Indigenous peoples have legal rights to freehold land, and hence have been able to maintain and continue their cultural practices and knowledges over generations, despite experiencing the impacts of colonization since the 1850s (Garde et al., 2009; Ritchie, 2009). The Indigenous population comprises 30% (i.e., 74,546 people) of the total NT population (246,500; Australian Bureau of Statistics [ABS], 2016, Census 2016), with legal rights to > 60% of the land (Sangha et al., 2019). Out of that Indigenous population, 77% (∼58,000) of people live in remote areas, and 16,300 of them live on homelands/outstations—out in the bush typically in a shed, far away from a town (Australian Bureau of Statistics [ABS], 2012–13). About 40,000 Indigenous peoples feel proud of their connections to country—a valuable, but unrecognized, aspect of Indigenous living that supports our thesis that an area of ∼650,000 km2 Indigenous-owned land in the NT (Figure 3) offers a suitable, enabling environment for people to utilize their country-related capabilities, and to advance economic enterprises which can contribute substantially toward peoples’ wellbeing.

FIGURE 3
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Figure 3. Indigenous land rights and distribution of communities across the NT, Australia.

There are only few opportunities for Indigenous peoples to work in conventional economic settings that exist in remote communities, but peoples’ traditional knowledges and skills help them to manage the vast, highly fire-prone landscape in the NT, covering an area of 1.34 M km2 (Russell-Smith et al., 2013; Russell-Smith and Sangha, 2018; Sangha et al., 2021). The wildfires alone emit >16,000 G tons of greenhouse gases (GHG) per year across northern Australia. Managing this vast, fiery, sparsely populated (0.16 people/km2 or 1 person/6 km2) area is a challenge for the territory and federal governments.

In 2007, Australia ratified the Kyoto Protocol, confirming its commitment to reduce GHG emissions, and wildfires in the north became a logical target. With this, a new opportunity emerged for Indigenous communities, across northern Australia, to apply their knowledges and skills of fire management to abate GHG emissions, leading to a world recognized “Savanna Burning Methodology” under which Indigenous Australians could claim carbon credits for managing their country (details in Russell-Smith et al., 2013, 2015; Sangha, 2020). As a result, more than a quarter of land is now managed across the north for wildfires, abating more than seven million tons of GHG emissions per annum (Sangha et al., 2021).

We assessed the value of ES from 103,263 km2, i.e., less than one-tenth area of the total NT landscape that is managed for wildfires by the Indigenous peoples, just for the abatement of GHG emissions alone (i.e., 3.45 million tons). The value of GHG emissions abatement is worth > USD 6 million over the past 6 years since the beginning of the program funded by the Australian Government under Savanna Burning methodology (for details see Sangha et al., 2021). For a bundle of ES from the same fire-managed area [following The Economics of Ecosystems and Biodiversity (TEEB) database developed by van der Ploeg and de Groot, 2010; Sangha et al., 2017], we applied the commonly used Basic Value Transfer technique (using local and regionally relevant values), and the value of ES was estimated at USD 5,361 million per year (Sangha et al., 2021). If the Indigenous peoples, in remote communities, were offered the opportunities to manage their land following traditional practices, the value of ES flowing from managing their 650,000 km2 will be multi-fold.

Moreover, managing the landscape for ES delivers many socio-cultural and wellbeing benefits for the Indigenous communities. The cost savings for the government for three key wellbeing components, i.e., safe, and supportive communities, creating economic opportunities, and healthy lives, were estimated at USD 81 million per year for involving 25% of the eligible workforce in the NT (Sangha et al., 2021). This value is much greater when considering the entire Indigenous estate for maintaining the flow of ES, for the local and greater public good.

This ES assessment case study, from Indigenously managed lands in the NT, indicates the role of ES in welfare and emerging economies such as carbon which is expected to expand to include carbon sequestration and other socio-cultural benefits (Sangha et al., 2021). Assessing this value, for less than one-tenth part of the NT landscape, is just a first step. Understanding Indigenous wellbeing values in relation to nature is the second step that our case study demonstrated. But, integrating these values into the economic model that currently dominates the NT economy is a difficult and much needed step, yet to do, for which transformational thinking, across different economic sectors, is essential to appropriately comprehend connections between country-based non-market economy and people’s wellbeing.

National Scale: “Economies-in-Society-in-Nature”—Integrating Ethics, Economics, and Societal Values

To develop national economies that are embedded in society, which is itself embedded in natural systems we need in-depth understanding of each interaction between economy, society, and nature (Costanza et al., 2012). As Ruskin et al. (2002) says, developing “economies-in-society-in-nature” is the pragmatic necessity. We offer a case study on how to develop such economies that help achieve sustainable wellbeing which includes protecting and restoring nature, achieving societal and intergenerational fairness, and recognizing nature’s contributions to our economies.

A small country, the kingdom of Bhutan, with 754,000 people living across 38,000 km2 of land, sets an example to the rest of world demonstrating how sustainable economies-in-society-in-nature operate. The foundation for Bhutan’s economy is people’s wellbeing and nature. The measure for such an economy is Bhutan’s unique Gross National Happiness (GNH) index, not GDP as for many countries across the globe. The fourth King, King Jigme Singye Wangchuck, in 1972 indeed declared that the GNH index is more important to his kingdom than GDP (Revkin, 2005; Centre for Bhutan Studies and GNH Research, 2016). Since then, the GNH index has laid the foundation, and philosophical background, to determine the developmental foci for the kingdom, which emphasizes people’s wellbeing and biodiversity as the core. Unlike the exclusive socio-economic indicators applied by many developed and developing countries, the GNH index has nine domains (Figure 4), including Ecological Diversity and Resilience, Cultural Diversity and Resilience, which focus on balancing the physical world with mental health, the material wealth with spirituality, within a safe and stable environment, with the purpose of realizing happiness. Each domain has a set of indicators (Thinley and Hartz-Karp, 2019):

1. Psychological wellbeing: Life satisfaction, Positive emotions, Negative emotions, and Spirituality;

2. Health: Self-reported health, Healthy days, Disability, and Mental health;

3. Time Use: Work and Sleep;

4. Education: Literacy, Schooling. Knowledge, and Value;

5. Cultural Diversity and Resilience: Community skills and Cultural participation;

6. Good Governance: Political participation, Services, Government performance, and Fundamental rights;

7. Community vitality: Donation (time and money), Safety, Community relationship, Family;

8. Ecological Vitality and Resilience: Wildlife damage, Urban issues, Responsibility toward environment, Ecological issues; and,

9. Living standard: Per capita income, Assets, and Housing.

FIGURE 4
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Figure 4. Gross National Happiness (GNH) Index, applied in the kingdom of Bhutan.

This index serves as a tool to inform various public and welfare policies in Bhutan (Centre for Bhutan Studies and GNH Research, 2016), so that the purpose of happiness is achieved for each Bhutanese through promoting conditions of equity and sustainability (Thinley and Hartz-Karp, 2019). Overall, the GNH framework enables government to exercise authority, develop plans, rules and processes that focus on people’s wellbeing and nature, and provides a clear sense of purpose what to be achieved, with a degree of accountability.

Bhutan’s economy is driven by nature and biodiversity—people value the abundance of nature’s resources not just for agriculture, traditional food, but also for culture, traditions, and spirituality. People’s livelihoods, ethics and morale to respect nature is deeply influenced by their Buddhist traditions. Importantly, these values are protected through Bhutanese legislation, i.e., protect 60% of its forest, remain carbon neutral, and pursue environmentally sustainable development.

Hydropower, agriculture, and ecotourism are key components of Bhutan’s economy which have contributed to rapid economic growth in the last decade, especially through foreign investment, export earnings, and contributions to the national budget in hydropower (the 11th and the 12th Five Year Plans by the Gross National Happiness Commission, 2013, 2019). The 11th and 12th Plans focus specifically on the diversification of income generation, particularly from hydropower, on “Self Reliance and Inclusive Green Socio-economic Development” (11th Plan), and on creating a “Just, harmonious and sustainable society,” targeting marginalized population, decentralization, and creating right job opportunities. Nature-based initiatives such as Payments for Ecosystem Services (PES), Biodiversity Finance (BIOFIN), and REDD+ are promising for a state like Bhutan where protection of biodiversity is legally and culturally enshrined.

From a GDP perspective, Bhutan’s GDP is worth USD 2.535 billion, with agriculture comprising only 16.2% of the total GDP while employing 51% of the workforce (Royal Monetary Authority of Bhutan, 2020). The industry and service sectors constitute 42% each, employing 23 and 35% of the workforce. The unemployment rate, amongst a population of 771,000 people, is less than 2.45% (which is significantly lower than Bhutan’s neighbors such as India and Bangladesh). Notably, 51% of the total workforce being employed in agriculture also indicates that agriculture is a vital sector, however, its contribution toward main economy is often not measured appropriately due to the lack of tools and measures (The Economics of Ecosystems and Biodiversity [TEEB], 2018).

Overall, the Bhutan economy—the first of its kind in the world with minimal exposure to the outside economic forces, and driven by the paradigm of sustainable, just, and happy societal values—demonstrates new ways of fostering human wellbeing to the rest of the world. To measure the total value of such an economy requires innovative tools and techniques that are beyond the GDP measures.

Key overarching principles for building such an economy-in-society-in-nature from ecological economic perspectives essentially include: 1. Sustainable scale of economies; 2. Efficient allocation of resources so that these are used, protected, and restored to meet the planetary limits for supporting sustainable living; and 3. Fair distribution of resources among the present and future generations, i.e., intergenerational equity. Bhutan’s comprehensive approach demonstrates how these principles could be embedded in the overall economic framework to inform policy decision making, for which political will and governance are the critical elements. The unique and deep understanding that the King of Bhutan has demonstrated for adopting the GNH index over GDP should inspire wealthy nations to transform their economies for environmental sustainability and enhanced wellbeing, much beyond the materialistic choices.

Discussion

The wellbeing of humans is well beyond materials comforts, yet economic progress measures continue to rely on GDP to inform development paradigms, policies, and related programs. Consequently, in developed countries, despite people having access to materials and services over the recent decades, social, mental, and emotional issues are rapidly emerging (Organisation for Economic Co-operation and Development [OECD], 2021). In key OECD countries such as the US, UK, Portugal, Australia, and others, increasing income inequity is leading to social problems (Costanza et al., 2012; Organisation for Economic Co-operation and Development [OECD], 2017, 2019). As the past Secretary-General of the OECD, Angel Gurría, warned “high levels of inequality generate high costs for society, dampening social mobility, undermining the labor market prospects of vulnerable social groups, and creating social unrest” (cited in Keeley, 2015). The consequences of modern economic development focusing on GDP growth, large scale investments and monetary returns while imperiling the livelihoods of world’s rural populations, are socially, environmentally, and politically devastating.

Understanding and highlighting the role of ecosystems and their ES for our modern economies and human wellbeing is an important task that will help inform policy decision makers. We acknowledge that our ES values presented in Table 1 may not represent an exact figure, but these do suggest the importance of Indigenous land management for delivering many benefits that are not traded in the conventional market. Such ES assessments can inform future policy developments and programs to invest in supporting Indigenous and local community efforts. There are many successful examples of PES across the globe such as Costa Rica’s PES program, UN’s REDD+, various global Biodiversity offsets and credits programs, and the Reef Credits program in Australia (some of these examples can be found on The Economics for Ecosystems and Biodiversity webpage: http://teebweb.org/publications/).

TABLE 1
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Table 1. The value of GHG emission abatement, ES, and wellbeing benefits from Indigenously managed land in the NT, Australia.

To support efficient allocation of resources, we acknowledge that the ES approach should be considered in conjunction with sustainable use of resources (a key principle of ecological economics). Embedding the long-term availability of ES into policy decision making, can help sustain the ecological assets that provide these services (Bennett and Chaplin-Kramer, 2016). Our case studies also indirectly provide insights on how these transformed economies contribute toward the equitable distribution of resources for supporting marginalized communities to manage their natural resources and enhance local economies (Sangha et al., 2021).

The word “development” requires re-evaluation for its correct understanding, particularly among the political and policy domains. It is often applied in economics to suggest the advancement or betterment in material standards. “Development Economics” particularly deals with advancing fiscal capacity of a state to accelerate the rate of growth of per capita income, mainly to meet the set material standards (Sangha, 2018). Changing this contemporary widespread perception of development to embrace human wellbeing perspectives, well beyond material standards, is crucial if we want our future generations to continue to enjoy access to clean water, air, and healthy food. This includes transforming existing economic frameworks and policies, as has been done in Bhutan, and taking the lead, mainly for the state agencies to develop policies that focus on enhancing human wellbeing (Costanza et al., 2014a). Extending development to emphasize and advance human wellbeing (both qualitative and quantitative standards) should be the focus if we want to really develop and improve people’s quality of life (Costanza et al., 2007, 2017b).

An integrated, modernized concept of development, that considers planetary boundaries and enables people to lead their lives sustainably, within resource limits is essential, as advocated by Sen (1999a; 1999b) and Costanza et al. (2014a; 2014b). But to facilitate this paradigm, key reforms are required. First, we need a new vision for development where people’s freedoms and rights, suitable opportunities, local governance, and better social justice are warranted (Sen, 1999a). Second, the notion of development needs to be linked with the supplier of fundamental services supporting our living—nature, by incorporating the principles of sustainable scale, efficient allocation, and fair distribution of resources (Daly, 1996). Linking development with the state and use of natural resources can help us develop the ideal integrated framework to improve both human wellbeing and the state of nature’s resources, while staying within the planetary boundaries.

Informing and changing societal attitudes to understand the urgency and adjusting material standards and related resource use within the planetary limits is equally essential (Costanza et al., 2017a, 2014b). Along with changes in policy areas, modern societies need to act fast to address the rapidly changing climate and the degradation of natural resources, to mitigate wide-ranging impacts on human populations (Millennium Ecosystem Assessment [MA], 2005; Intergovernmental Platform on Biodiversity and Ecosystem Services [IPBES], 2019b). Conducting community-based scenario planning meetings to inform people about how human actions impact on the human-nature system, can help people realize their dependence on natural resources, improve their attitudes toward nature, and to develop a collective plan for a desirable future which is sustainable, equitable, and enhances people’s wellbeing.

Limiting human needs to the necessary materials for affording sustainable living, and applying integrated knowledge systems to manage and improve natural systems that supply those materials, is a much-needed approach at the individual and societal scales (Sangha, 2018). To do so, a radical change for how we value materials and nature, is absolutely required. As the 14th Dalai Lama says “Human happiness and human satisfaction must ultimately come from within oneself. It is wrong to expect some final satisfaction to come from money (materials)…” Satisfaction for materials “fulfillment or gratification, just the right amount—lagom (in Swedish) or contentment—Santushti (in Hindi)” is a key element of human ethics that can prove useful in transforming the paradigms of development and valuing nature, but how do we seek it?

Satisfaction or the feeling of being well and contented is linked to spirituality (Shiva, 2013). Spirituality, irrespective of religious beliefs, is a vital aspect of human life allowing the constant exploration of the meaning of our lives and striving to improve ourselves. Nature offers us this exceptional service and delivers multitude benefits such as health, resilience, compassion, self-esteem, and equitability. Spiritual experiences help us to habitually meditate on the entire vista and to explore the main purpose of our living while evoking the end of life. Consequently, such a day-to-day realization can help us inculcate a moral responsibility to look after nature.

Many traditional societies (Indigenous and local communities), who continue to apply their knowledges and skills to manage resources and lead their lives in harmony with nature, offer principles that could help the mainstream population to adopt sustainable ways of living. One of these principles is to be the custodians, not the owners, of land, as applies for Indigenous societies in Australia (Dodson, 1997; Grieves, 2009). The two-way relationship with the landscape, meaning if a person obtains a service/good from land then looking after that land is also mandatory, is another key ethic embedded in many traditional societies (Sangha and Russell-Smith, 2017). Such a two-way perspective is unique and highly valuable in the modern context where human activities mainly involve extraction from nature or using nature’s resources, without considering any repay or duty of care.

Some examples of traditional societies, emphasizing living in harmony with nature and sustainable pathways, include the worldview of the Quechua peoples of the Andes, sumak kawsay—or buen vivir which means “good living” that is community centered, ecologically balanced, and culturally sensitive (Artaraz et al., 2021). Similarly, the Pachamama (Mother Earth) concept of the Indigenous peoples of Andes endorses how nature’s processes sustain life on earth (Pacari, 2009). Gaia is another popular hypothesis that posits how nature, and its biological systems behave as a single entity—suggesting holistic approaches to manage and use the system (Lovelock and Margulis, 1974). Realization of our dependence on nature and how our wellbeing is linked to nature in its entirety is vital to sustain human and other beings living on planet earth.

We suggest that a much more integrated, dynamic, connected nature-human systems thinking is needed to radically transform the current economy and related frameworks. However, achieving an economy-in-society-in-nature is not feasible without applying sustainable governance (the Lisbon) principles which are critical to govern the common natural and social capital assets (Costanza et al., 1998). These principles include: 1. Responsibility; 2. Scale matching; 3. Precaution; 4. Adaptive management; 5. Full cost allocation; and 6. Participation (details in Costanza et al., 1998). Blending sustainable governance with development, and sustainable and efficient use of natural resources, can help us develop an ideal integrated framework to improve both human wellbeing and nature’s resources which can help sustain human wellbeing.

In conclusion, transforming our economies while adjusting to the planetary boundaries at the local, national, and global scales, can lead to innovative enterprises. Such economies will also deliver almost all the Sustainable Development Goals which target a “blueprint to achieve a better and more sustainable future for all” by The United Nations [UN] (2015). With the recent COP26 Climate Change Conference in Glasgow (1–12 November), there is evidently much wider recognition of the need to transform economies now than ever before and many organizations are committing to follow that path.

Data Availability Statement

The raw data supporting the conclusions of this article will be made available by the authors, without undue reservation.

Author Contributions

KS worked on the outline and framed the manuscript, which was followed up by IC and RC. IC and RC provided comments and feedback. All authors contributed to this article and online discussion about the outline and content of this manuscript, and discussed the final version together for submission.

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.

Publisher’s Note

All claims expressed in this article are solely those of the authors and do not necessarily represent those of their affiliated organizations, or those of the publisher, the editors and the reviewers. Any product that may be evaluated in this article, or claim that may be made by its manufacturer, is not guaranteed or endorsed by the publisher.

Footnotes

  1. ^ https://www.worldvaluessurvey.org/wvs.jsp
  2. ^ http://www.managi-lab.com/iwp/iwp_iw.html
  3. ^ http://happyplanetindex.org
  4. ^ https://tnfd.global/about/

References

Altman, J., Kerins, S., Hunt, J., Ens, E., May, K., Russell, S., et al. (2011). Indigenous Cultural and Natural Resource Management Futures. CAPER Topical Issue No. 9/2011. Canberra: Australian National University.

Google Scholar

Artaraz, K., Calestani, M., and Trueba, M. L. (2021). Introduction: vivir bien/Buen vivir and Post-Neoliberal development paths in Latin America: scope, strategies, and the realities of implementation. Latin Am. Perspect. 48, 4–16. doi: 10.1177/0094582x211009461

CrossRef Full Text | Google Scholar

Australian Bureau of Statistics [ABS] (2012–13). Australian Aboriginal and Torres Strait Islander Health Survey: First Results, Australia, 2012-13. Catalogue no. 4727.0.55.001. Canberra: The Australian Bureau of Statistics.

Google Scholar

Australian Bureau of Statistics [ABS] (2016). Census 2016. Canberra: The Australian Bureau of Statistics.

Google Scholar

Bennett, E., and Chaplin-Kramer, R. (2016). Science for the sustainable use of ecosystem services. F1000Research 5:2622. doi: 10.12688/f1000research.9470.1

PubMed Abstract | CrossRef Full Text | Google Scholar

Centre for Bhutan Studies, and GNH Research (2016). A Compass Towards a Just and Harmonious Society: 2015 GNH Survey Report. Bhutan: Centre for Bhutan Studies & GNH Research.

Google Scholar

Costanza, R. (2020). Valuing natural capital and ecosystem services toward the goals of efficiency, fairness, and sustainability. Ecosyst. Serv. 43:101096. doi: 10.1016/j.ecoser.2020.101096

CrossRef Full Text | Google Scholar

Costanza, R., Alperovitz, G., Daly, H. E., Farley, J., Franco, C., Jackson, T., et al. (2012). Building a Sustainable and Desirable Economy-in-Society—-in–Nature. New York, NY: United Nations Division for Sustainable Development.

Google Scholar

Costanza, R., Andrade, F., Antunes, P., van den Belt, M., Boersma, D., Boesch, D. F., et al. (1998). Principles for sustainable governance of the oceans. Science 281, 198–199. doi: 10.1126/science.281.5374.198

PubMed Abstract | CrossRef Full Text | Google Scholar

Costanza, R., Atkins, P. W. B., Bolton, M., Cork, S., Grigg, N. J., Kasser, T., et al. (2017b). Societal addiction therapy: from motivational interviewing to community engaged scenario planning. Curr. Opin. Environ. Sustain. 2, 47–53. doi: 10.1016/j.cosust.2017.02.011

CrossRef Full Text | Google Scholar

Costanza, R., Atkins, P. W. B., Hernandez-Blanco, M., and Kubiszewski, I. (2021). Common asset trusts to effectively steward natural capital and ecosystem services at multiple scales. J. Environ. Manage. 280:111801. doi: 10.1016/j.jenvman.2020.111801

PubMed Abstract | CrossRef Full Text | Google Scholar

Costanza, R., d’ Arge, R., de Groot, R., Farber, S., Grasso, M., Hannon, B., et al. (1997). The value of the world’s ecosystem services and natural capital. Nature 387, 253–260.

Google Scholar

Costanza, R., de Groot, R., Braat, L., Kubiszewski, I., Fioramonti, L., Sutton, P., et al. (2017a). Twenty years of ecosystem services: how far have we come and how far do we still need to go? Ecosyst. Serv. 28, 1–16. doi: 10.1016/j.ecoser.2017.09.008

CrossRef Full Text | Google Scholar

Costanza, R., de Groot, R., Sutton, P., van der Ploeg, S., Anderson, S. J., Kubiszewski, I., et al. (2014b). Changes in the global value of ecosystem services. Glob. Environ. Change 26, 152–158. doi: 10.1016/j.gloenvcha.2014.04.002

CrossRef Full Text | Google Scholar

Costanza, R., Fioramonti, L., Kubiszewski, I., Henry, L., Lovins, H., McGlade, J., et al. (2018). Toward a sustainable well-being economy. Solut. J. 9. Available online at: https://thesolutionsjournal.com/2018/04/17/toward-sustainable-wellbeing-economy/

Google Scholar

Costanza, R., Fisher, B., Ali, S., Beer, C., Bond, L., Boumans, R., et al. (2007). Quality of life: an approach integrating opportunities, human needs, and subjective well-being. Ecol. Econ. 61, 267–276. doi: 10.1016/j.ecolecon.2006.02.023

CrossRef Full Text | Google Scholar

Costanza, R., Kubiszewski, I., Giovannini, E., Lovins, H., McGlade, J., Pickett, K.E., et al. (2014a). Development: time to leave GDP behind. Nature 505, 283–285. doi: 10.1038/505283a

PubMed Abstract | CrossRef Full Text | Google Scholar

Daly, H. (2005). Economics in a full world. Sci. Am. 293, 100–107. doi: 10.1038/scientificamerican0905-100

PubMed Abstract | CrossRef Full Text | Google Scholar

Daly, H. E. (1973). Toward a Steady State Economy. San Francisco, CA: Freeman.

Google Scholar

Daly, H. E. (1991). Steady State Economics, Second Edn. Washington, DC: Island Press.

Google Scholar

Daly, H. E. (1996). Beyond Growth: The Economics of Sustainable Development. Boston, MA: Beacon Press.

Google Scholar

Daly, H. E. (2015). Economics for a Full World, Great Transition Initiative (June 2015). Available online at: http://www.greattransition.org/publication/economics-for-a-full-world (accessed on August 9, 2021)

Google Scholar

Daly, H. E., and Farley, J. (2011). Ecological Economics: Principles and Applications, 2nd Edn. Washington, DC: Island Press.

Google Scholar

DasGupta, P. (2020). The Dasgupta Review—Independent Review on the Economics of BiodiversityEconomics (Interim Report), UK Government, London. 81.

Google Scholar

Dodson, M. (1997). “Land rights and social justice,” in Our Land is Our Life : Land Rights : Past, Present and Future, ed. G. Yunupingu (St. Lucia: University of Queensland Press), 39–51.

Google Scholar

Farley, J., Costanza, R., Flomenhoft, G., and Kirk, D. (2015). The vermont common assets trust: an institution for sustainable, just and efficient resource allocation. Ecol. Econ. 109, 71–79. doi: 10.1016/j.ecolecon.2014.10.016

CrossRef Full Text | Google Scholar

Garde, M., Nadjamerrek, L. B., Kolkkiwarra, M., Kalarriya, J., Djandjomerr, J., Birriyabirriya, B., et al. (2009). “The language of fire: seasonality, resources and landscape burning on the arnhem land plateau,” in Managing Fire Regimes in North Australian Savannas – Ecology, Culture, Economy, eds J. Russell-Smith and P. Whitehead (Canberra: CSIRO Publishing).

Google Scholar

Grieves, V. (2007). Indigenous Well-Being: A Framework for Governments’ Aboriginal Cultural Heritage Activities., Minimbah Consultants and Education Providers’ Report for the NSW Department of Environment and Conservation, Sydney South.

Google Scholar

Grieves, V. (2009). Aboriginal Spirituality: Aboriginal Philosophy. The Basis of Aboriginal Social and Emotional Well-being. Discussion Paper no. 9. Casuarina NT: Cooperative Research Centre for Aboriginal Health.

Google Scholar

Gross National Happiness Commission (2013). 11th Five Year Plan, Bhutan Government 2013-18. Royal Government of Bhutan. Available online at: https://www.gnhc.gov.bt/en/wp-content/uploads/2017/05/Eleventh-Five-Year-Plan.pdf (accessed on September 30, 2021)

Google Scholar

Gross National Happiness Commission (2019). 12th Five Year Plan, Bhutan Government 2018-23. Royal Government of Bhutan. Available online at: https://www.gnhc.gov.bt/en/wp-content/uploads/2019/05/TWELVE-FIVE-YEAR-WEB-VERSION.pdf (accessed on September 30, 2021)

Google Scholar

Intergovernmental Platform on Biodiversity and Ecosystem Services [IPBES] (2019a). IPBES Conceptual Framework. Available online at: https://www.ipbes.net/conceptual-framework (accessed on October 23, 2019)

Google Scholar

Intergovernmental Platform on Biodiversity and Ecosystem Services [IPBES] (2019b). Global Assessment Report on Biodiversity and Ecosystem Services of the Intergovernmental Science-Policy Platform on Biodiversity and Ecosystem Services, eds E. S. Brondizio, J. Settele, S. Díaz, and H. T. Ngo (Bonn: IPBES secretariat), 1148.

Google Scholar

Keeley, B. (2015). Income Inequality: The Gap between Rich and Poor, OECD insights. Paris: OECD Publishing.

Google Scholar

Kubiszewski, I., Costanza, R., Franco, C., Lawn, P., Talberth, J., Jackson, T., et al. (2013). Beyond GDP: measuring and achieving global genuine progress. Ecol. Econ. 93, 57–68. doi: 10.1016/j.ecolecon.2013.04.019

CrossRef Full Text | Google Scholar

Lovelock, J. E., and Margulis, L. (1974). Atmospheric homeostasis by and for the biosphere: the gaia hypothesis. Tellus 26, 2–10. doi: 10.3402/tellusa.v26i1-2.9731

CrossRef Full Text | Google Scholar

Maes, J., Hauck, J., Paracchini, M., Ratamäki, O., Termansen, M., PÈrez-Soba, M., et al. (2012). A Spatial Assessment of Ecosystem Services in Europe: Methods, Case Studies and Policy Analysis - Phase 2 Synthesis Report. PEER Report No. 4. Ispra: Partnership for European Environmental Research.

Google Scholar

Material Economics (2021). The Circular Economy and Covid-19 Recovery: How Pursuing a Circular Future for Europe Fits With Recovery from the Economic Crisis. Available online at: https://materialeconomics.com/publications/publication/circular-recovery (accessed on November 10, 2021).

Google Scholar

Meadows, D. H., Meadows, D. L., Randers, J., and Behrens, W. W. III (1972). The Limits to Growth. New York, NY: Universe Books.

Google Scholar

Millennium Ecosystem Assessment [MA] (2003). Ecosystems and Human Well-being: A Framework for Assessment. Washington, D.C: Island Press.

Google Scholar

Millennium Ecosystem Assessment [MA] (2005). Ecosystems and Human Well-Being: Synthesis. Washington, DC: Island press.

Google Scholar

Organisation for Economic Co-operation and Development [OECD] (2017). Income Inequality. Paris: Organisation for Economic Co-operation and Development.

Google Scholar

Organisation for Economic Co-operation and Development [OECD] (2019). Under Pressure: The Squeezed Middle Class. Available online at: https://www.oecd-ilibrary.org/sites/689afed1-en/index.html?itemId=/content/publication/689afed1-en (accessed on August 1, 2021)

Google Scholar

Organisation for Economic Co-operation and Development [OECD] (2021). Income Inequality (Indicator). OECD Report. Paris: Organisation for Economic Co-operation and Development.

Google Scholar

Pacari, N. (2009). “Naturaleza y Territorio Desde la Mirada de los Pueblos Indigenas [Nature and land from the perspective of indigenous people],” in Derechos de la naturaleza: el futuro es ahora [The Rights of Nature: The Future is Now], eds A. Acosta and E. Martínez (Quito: Abya-Yala), 31–37.

Google Scholar

Revkin, A. (2005). A New Measure of Well-Being From a Happy Little Kingdom. ISSN 0362-4331. New York, NY: The New York Times.

Google Scholar

Ritchie, D. (2009). “Things fall apart: the end of an era of systematic indigenous fire management (Chapter 2),” in Culture, Ecology and Economy of Fire Management in North Australian Savannas: Rekindling the Wurrk Tradition, eds J. Russell-Smith, P. Whitehead, and P. Cooke (Collingwood, VIC: CSIRO Publishing).

Google Scholar

Royal Monetary Authority of Bhutan (2020). Annual Report 2019-2020. Royal Monetary Authority of Bhutan. https://www.rma.org.bt/RMA%20Publication/Annual%20Report/RMA%202020%20report.pdf (accessed September 30, 2021).

Google Scholar

Ruskin, P., Banuri, T., Gallopin, G., Gutman, P., Hammond, A., Kates, R., et al. (2002). Great Transition: The Promise and Lure of the Times Ahead. Boston, MA: Stockholm Environment Institute.

Google Scholar

Russell-Smith, J., and Sangha, K. K. (2018). Emerging opportunities for developing a diversified land sector economy in Australia’s northern savannas. Rangel. J. 40, 315–330. doi: 10.1071/RJ18005

CrossRef Full Text | Google Scholar

Russell-Smith, J., Bristow, M., Brocklehurst, P., Cook, G. D., Cuff, N., Edwards, A. C., et al. (2015). “Chapter 15 Epilogue—where to from here?,” in Savanna Burning: Delivering Carbon and Greenhouse Benefits in Fire Prone Northern Australia, eds B. P. Murphy, A. C. Edwards, C. P. Meyer, and J. Russell-Smith (Melbourne: CSIRO Publishing).

Google Scholar

Russell-Smith, J., Cook, G. D., Cooke, P. M., Edwards, A. C., Lendrum, M., Meyer, C. P., et al. (2013). Managing fire regimes in north Australian savannas: applying Aboriginal approaches to contemporary global problems. Front. Ecol. Environ. 11:e55–e63. doi: 10.1890/120251

CrossRef Full Text | Google Scholar

Russell-Smith, J., Whitehead, P., and Cooke, P. (eds) (2009). Culture, Ecology and Economy of Fire Management in North Australian Savannas: Rekindling the Wurrk Tradition (Collingwood, VIC: CSIRO Publishing).

Google Scholar

Sangha, K. K. (2018). What kind of development we want to afford sustainable living? J. Environ. Sci. Eng. A 7, 34–48.

Google Scholar

Sangha, K. K. (2020). New economic opportunities in Northern Australia: a case study of carbon economy. N. Econ. J. 2, 1–10.

Google Scholar

Sangha, K. K., Evans, J., Edwards, A., Russell-Smith, J., Fisher, R., Yates, C., et al. (2021). Assessing the value of ecosystem services delivered by prescribed fire management in Australian tropical savannas. Ecosyst. Serv. 51:101343. doi: 10.1016/j.ecoser.2021.101343

CrossRef Full Text | Google Scholar

Sangha, K. K., Gerritsen, R., and Russell-Smith, J. (2019). Repurposing government expenditure for enhancing Indigenous well-being in Australia: a scenario analysis for a new paradigm. Econ. Anal. Policy 63, 75–91. doi: 10.1016/j.eap.2019.04.011

CrossRef Full Text | Google Scholar

Sangha, K. K., Russell-Smith, J., Morrison, S. C., Costanza, R., and Edwards, A. (2017). Challenges for valuing ecosystem services from an Indigenous estate in Northern Australia. Ecosystem Services 25, 167–178. doi: 10.1016/j.ecoser.2017.04.013

CrossRef Full Text | Google Scholar

Sangha, K., and Russell-Smith, J. (2017). Towards an indigenous ecosystem services valuation framework: a North Australian example. Conserv. Soc. 15, 255–269.

Google Scholar

Sangha, K., Butler, J., Delisle, A., and Stanley, O. (2011). Identifying links between ecosystem services and Aboriginal well-being and livelihoods in north Australia: applying the Millennium ecosystem assessment framework. J. Environ. Sci. Eng. 5, 381–387.

Google Scholar

Schröter, M., Albert, C., Marques, A., Tobon, W., Lavorel, S., Maes, J., et al. (2016). National ecosystem assessments in Europe: a review. BioScience 66, 813–828. doi: 10.1093/biosci/biw101

PubMed Abstract | CrossRef Full Text | Google Scholar

Sen, A. (1989). On Ethics and Economics. Hoboken, NJ: Wiley-Blackwell publishers.

Google Scholar

Sen, A. (1999a). Development as Freedom. Oxford: Oxford University Press.

Google Scholar

Sen, A. (1999b). Commodities and Capabilities. Oxford: Oxford University Press.

Google Scholar

Shiva, V. (2013). Making Peace With The Earth. London: Pluto Press.

Google Scholar

Steering Committee for the Review of Government Service Provision [SCRGSP] (2017). Indigenous Expenditure Report 2017. Canberra: Steering Committee for the Review of Government Service Provision.

Google Scholar

Talberth, J., Cobb, C., and Slattery, N. (2007). The Genuine Progress Indicator 2006: A Tool for Sustainable Development (Redefining Progress, 2007). Oakland, CA: Redefining Progress.

Google Scholar

The Economics of Ecosystems and Biodiversity [TEEB] (2018). TEEB for Agriculture & Food: Scientific and Economic Foundations. TEEB Agriculture & Food, UN Environment. Geneva: UN Environment.

Google Scholar

The United Nations [UN] (2015). Sustainable Development Goals. Available online at: http://www.undp.org/content/undp/en/home/sustainable-development-goals.html (accessed on May 27, 2018)

Google Scholar

Thinley, J. Y., and Hartz-Karp, J. (2019). National progress, sustainability and higher goals: the case of Bhutan’s Gross National Happiness. Sustainable Earth 2:11. doi: 10.1186/s42055-019-0022-9

CrossRef Full Text | Google Scholar

United Nations (2021). System of Environmental-Economic Accounting— Ecosystem Accounting (SEEA EA). White cover publication, pre-edited text subject to official editing. Available online at: https://seea.un.org/sites/seea.un.org/files/documents/EA/seea_ea_white_cover_final.pdf.

Google Scholar

United Nations University–International Human Dimensions Programme UNU-IHDP, and United Nations Environment Programme UNEP (2014). Inclusive Wealth Report 2014. Measuring Progress Toward Sustainability. Summary for Decision-Makers. United Nations University – International Human Dimensions Programme on Global Environmental Change. Delhi: UNU-IHDP.

Google Scholar

van der Ploeg, S., and de Groot, R. (2010). The TEEB Valuation Database – A Searchable Database of 1310 Estimates of Monetary Values of Ecosystem Services. Wageningen: Foundation for Sustainable Development.

Google Scholar

Keywords: human wellbeing, ecosystem services, development, Indigenous communities, Gross National Happiness index, Gross Domestic Product

Citation: Sangha KK, Gordon IJ and Costanza R (2022) Ecosystem Services and Human Wellbeing-Based Approaches Can Help Transform Our Economies. Front. Ecol. Evol. 10:841215. doi: 10.3389/fevo.2022.841215

Received: 22 December 2021; Accepted: 18 March 2022;
Published: 15 April 2022.

Edited by:

Martin Drechsler, Helmholtz Centre for Environmental Research, Helmholtz Association of German Research Centres (HZ), Germany

Reviewed by:

Susanna B. Hecht, University of California, Los Angeles, United States
Julia M. Touza, University of York, United Kingdom

Copyright © 2022 Sangha, Gordon and Costanza. 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: Kamaljit K. Sangha, Kamaljit.Sangha@cdu.edu.au

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