FROM COEXISTENCE TO MUTUALISM: MAINSTREAMING BIODIVERSITY IN THE SUSTAINABLE DEVELOPMENT GOALS
Repositioning Biodiversity as the Foundation for All Development Goals
ARTICLE HIGLIGHTS
- Mutualism paradigm aligns biodiversity with sustainable development.
- Biodiversity acts as a driver for prosperity rather than a constraint.
- Integrated policy mixes unlock powerful synergies for global goals.
- Reciprocal benefits are vital to moving beyond mere coexistence.
ABSTRACT
Mainstreaming biodiversity into the Sustainable Development Goals (SDGs) is currently hampered by a prevailing “coexistence” paradigm, which treats conservation and economic development as separate, often conflicting domains. This fragmentation leads to persistent policy silos and unresolved trade-offs, undermining long-term sustainability. This study aimed to critically diagnose the structural limitations of this approach and proposes a transition toward “mutualism”—a framework where biodiversity and development objectives are mutually reinforcing. Adopting a critical review methodology, we synthesized evidence from policy, economic, and scientific sectors. We analyzed specific instruments, such as Nature-based Solutions (NbS) and Payments for Ecosystem Services (PES), to identify the institutional, financial, and social barriers currently constraining their effectiveness. The novelty of this paper lies in the conceptualization of ‘mutualism’ not merely as an ecological metaphor, but as an operational framework for the SDGs that moves beyond the traditional “do no harm” principle to actively engineering reciprocal benefits. We concluded that while existing instruments show promise, they fail to achieve systemic change due to a lack of strategic alignment. To operationalize mutualism, we recommend a strategic shift focusing on three pillars: implementing coherent policy mixes that integrate regulatory and fiscal instruments, establishing inclusive governance to manage trade-offs, and mobilizing finance that rewards verifiable ecological and social synergies.
INTRODUCTION
The global consensus embodied in the Sustainable Development Goals (SDGs) and international biodiversity targets underscores the urgency of aligning human well-being with the preservation of the biosphere. This effort has recently been crystallized in the landmark Kunming-Montreal (Kedia & Anand, 2021), which serves as the new global roadmap to ‘live in harmony with nature’. Biodiversity is not merely an environmental amenity but an essential foundation supporting vital systems for civilization, including food security, public health, and economic stability. Nevertheless, efforts to mainstream biodiversity conservation into the broader development agenda have yielded limited progress.
The fundamental problem lies in the dominant paradigm, which operates at the level of coexistence a framework wherein nature protection and economic development are treated as separate and often antagonistic pursuits. Consequently, short-term economic gains are systematically prioritized overlong-term ecological sustainability. This fragmented approach has led to specific implementation failures within the SDG framework. For instance, the pursuit of food security (SDG 2) often drives agricultural expansion that directly degrades natural habitats (SDG 15), creating a “policy incoherence” where the achievement of one goal undermines another. Similarly, economic decision- making frequently relies on cost-benefit analyses that fail to account for long-term societal interests, thereby exacerbating poverty and social inequality for communities dependent on natural resources from protected areas. This practice, ironically, exacerbates social inequality, food insecurity, and poverty, particularly for communities whose livelihoods are directly dependent on natural resources from protected areas (Frank & Schäffler, 2019); (Clémençon, 2021).
This insufficient integration stems from a series of complex structural barriers. First, an excessive prioritization of economics in decision- making means that the valuation of ecosystem services through cost-benefit analysis often fails to accommodate long-term societal interests (Clémençon, 2021). Second, weaknesses at the level of policy and governance are manifested in non-binding legal regulations and a multiplication of overlapping and ineffective policy instruments (Thool, 2023); (Azizi et al., 2019). Third, the presence of vague and conflicting goals, such as the tension between agricultural expansion for food security and the imperative to protect natural habitats, highlights a deficit in policy coherence (Chahar et al., 2016). This gap is compounded by a disconnect between public perception which tends to equate sustainable development with conservation and a policy discourse that still largely interprets it as conventional economic growth (Clémençon, 2021). Furthermore, fragmented, sectoral approaches that address biodiversity and climate change as separate issues ignore the fundamental and interdependent nature of these two global crises (Kearney, 2022); (Time to integrate global climate change and biodiversity science-policy agendas, 2021).
This review aimed to critically analyze the existing literature to diagnose the structural weaknesses of the current “coexistence” approach and to propose a conceptual framework for a transition toward mutualism. By synthesizing evidence from various policy, economic, and scientific sectors, this review examined the barriers that perpetuate the disconnect between conservation and development agendas. The central argument advanced is that to holistically achieve the SDGs, a fundamental paradigm shift is required from mere coexistence to a mutualistic relationship. Within this framework, biodiversity is no longer viewed as a constraint or a burden but as a prerequisite and an active driver that generates reciprocal benefits with development objectives. In essence, investing in ecosystem health will inherently strengthen the achievement of socio-economic targets, and vice versa.
To construct this argument, the article first provides an in-depth analysis of the limitations of the “coexistence” model. It then elaborates on the concept of “mutualism” as a superior alternative paradigm capable of creating synergies between conservation and other development sectors, such as agriculture (Mamabolo et al., 2020). Finally, the article outlines strategic pathways to facilitate this transition, focusing on three key pillars: coherent policy integration, mobilization of public support, and an integrated research agenda.
The central argument advanced is that to holistically achieve the SDGs, a fundamental paradigm shift is required from mere coexistence to a mutualistic relationship. While previous reviews have cataloged the barriers to mainstreaming biodiversity, this paper offers a novel conceptual contribution by proposing ‘mutualism’ as an operational framework. We argue that this paradigm shift is not just a semantic change but a necessary strategic pivot to unlock powerful synergies previously constrained by a ‘coexistence’ mindset. This review synthesizes evidence from policy, economic, and scientific sectors to construct this argument, ultimately outlining strategic pathways to facilitate this critical transition.
REVIEW
Conceptual Framework: From Coexistence to Mutualism
The central argument of this review hinges on the critical distinction between two paradigms for integrating biodiversity and development: coexistence and mutualism. Coexistence, in the context of the Sustainable Development Goals (SDGs), describes a state where different entities, such as human communities and wildlife, exist together with interactions managed primarily to minimize conflict ((Gao & Clark, 2023); (Petitpierre-Sauvain, 2008). This approach often frames biodiversity and development as separate domains that must be carefully balanced to prevent negative interference. In contrast, mutualism proposes a more deeply integrated relationship, drawing from its ecological origins to describe interactions that produce net positive benefits for all parties involved (Fox et al., 2020). Applied to the SDGs, a mutualistic framework actively seeks to create systems where environmental protection and socio-economic progress are not merely compatible but mutually reinforcing, shifting the goal from avoiding harm to actively creating synergistic value (Lydgate, 2012).
The imperative to transition from coexistence to mutualism is rooted in the indivisible and interconnected nature of the SDGs themselves. While coexistence can prevent conflict, it is insufficient to drive the transformative progress required. A mutualistic framework is superior because it fosters synergistic benefits that are essential for accelerating progress across the interconnected goals (Fenner, 2022); (The added value of partnerships in implementing the UN sustainable development goals, 2024). By leveraging the strengths of multiple stakeholders, it spurs innovation and creates positive feedback loops where advancing one goal supports another (Sharma & Sharma, 2024). A coexistence model, however, often leads to fragmented efforts and untapped potential (McGowan et al., 2019);(Basheer et al., 2025).
Furthermore, a mutualistic approach inherently demands integrated strategies that minimize the trade-offs often seen between competing objectives, such as economic growth and ecosystem protection (Fader et al., 2018); (Assessing the land resource–food price nexus of the Sustainable Development Goals, 2016). It forces a holistic perspective that redesigns systems to align these goals. This approach also promotes the deep, multi-stakeholder cooperation needed to tackle complex global challenges by creating shared benefits, which provides a powerful incentive for long-term commitment (Kloke-Lesch, 2021); (King, 2025).
Current Status of Biodiversity Integration in the SDGs
An analysis of biodiversity mainstreaming within the Sustainable Development Goals (SDGs) to date reveals a complex picture, marked by commendable progress alongside persistent gaps. At the planning level, biodiversity is explicitly recognized as fundamental to achieving various SDGs, particularly those related to poverty eradication, food security, and environmental sustainability (Lucas et al., 2014); (Ament et al., 2019). This recognition is institutionalized through SDG 14 (Life Below Water) and SDG 15 (Life on Land), which directly target conservation and sustainable use (Khan & Shehzad, 2025);(Lernborg & Atallah, 2025). Furthermore, the Kunming-Montreal Global Biodiversity Framework reinforces this through its 23 targets for 2030, especially Target 14, which mandates that parties ensure biodiversity values are fully integrated into policies and regulations at all levels of government. At the implementation level, various innovative models have demonstrated the potential for synergy, such as Integrated Conservation and Development Projects (ICDPs), Nature-Based Solutions (NBS), and regenerative agriculture practices, all of which link conservation with socio-economic development (Ernoul & Mesleard, 2008);(E et al., 2020);(Himshikha et al., 2024). In financing, mechanisms like Payment for Ecosystem Services (PES) have been identified as effective tools, although these efforts are still hampered by a significant funding gap to reverse biodiversity loss (Lernborg & Atallah, 2025); (Wei et al., 2021).
However, despite these efforts, the current state of integration more closely reflects a paradigm of coexistence rather than true mutualism. Significant gaps remain, hindering the realization of a mutually beneficial relationship. Key challenges include insufficiently robust policy frameworks, inadequate biodiversity monitoring indicators at the country level, and a limited diversity of funding channels (Ogwu et al., 2025); (Dickens et al., 2020); (Wei et al., 2021). The disconnect between public perception, which favors conservation, and policy implementation, which often prioritizes other goals, also presents a major barrier (Clémençon, 2021). These gaps are not merely technical issues but are symptomatic of deeper, interconnected, fundamental barriers.
To transition toward a mutualistic relationship, it is crucial to understand the barriers that perpetuate the status quo. The literature identifies several key categories. Policy and institutional barriers such as imperfect regulations, conflicting policies, and a lack of inter-agency cooperation directly explain why on-the-ground implementation is often ineffective and fragmented (Wang et al., 2022); (Domenech et al., 2019); (Davis et al., 2022); (Szymańska et al., 2023). Financially, the aforementioned funding gap is exacerbated by weak economic incentives and a lack of sustainable financial support to foster mutualistic practices (Domenech et al., 2019); (Andrei et al., 2019).
Perhaps the most fundamental are the social and environmental barriers. Cultural resistance to cooperation often rooted in historical contexts along with power asymmetries and the risk of exploitation in partnerships, creates a climate of distrust that impedes genuine collaboration (Andrei et al., 2019); (Powell & Maoz, 2014); (Egger & Hibbett, 2004); (When cheating turns into a stabilizing mechanism of plant–pollinator communities, 2023). Furthermore, environmental conditions themselves, such as resource availability and climate variability, can affect the stability of mutualistic relationships (Grman et al., 2012); (Dunkley et al., 2020). Thus, the journey from coexistence to mutualism demands a systemic approach that not only focuses on individual projects but also strategically dismantles these interconnected policy, institutional, financial, and social barriers.
Mechanisms and Strategies Toward Mutualism
Transitioning from a paradigm of coexistence to one of mutualism requires the application of policy instruments and practical approaches that actively create synergies between biodiversity conservation and development objectives. A review of the literature identifies several promising pathways, which are supported by lessons learned from various case studies around the world. This section outlines these instruments and distills critical lessons from both the successes and failures of their implementation.
The literature highlights several key instruments as effective in fostering mutualistic relationships. Nature-based Solutions (NbS) are recognized for their significant potential to simultaneously address climate, biodiversity, and disaster risk challenges. Although their implementation faces constraints such as a lack of expertise and stakeholder conflicts, studies demonstrate that NbS like forest landscape restoration can yield significant positive economic impacts, particularly in water flow regulation (Scolobig et al., 2025); (Restrepo et al., 2024). Overcoming these barriers requires legally binding policy instruments, mobilization of public and private finance, and enhanced capacity building (Scolobig et al., 2025).
Another effective instrument is Payments for Ecosystem Services (PES), which establishes a direct mutualistic link by integrating the economic valuation of ecosystem services into land-use planning. By providing direct financial incentives, PES transforms stakeholders from passive residents into active partners in conservation, creating a relationship where maintaining and enhancing ecosystem services generates tangible economic benefits (Restrepo et al., 2024).
More broadly, the development and updating of National Biodiversity Strategies and Action Plans (NBSAPs) now serve as the primary policy mechanism for countries to translate GBF targets including those focused on mutualism into national action. Furthermore, the literature emphasizes the importance of Policy Mixes the combination of various instruments such as taxes, tradable permits, and command-and-control regulations.
This approach has proven more effective at addressing multiple market failures and enhancing policy synergy, fostering a comprehensive governance structure that supports mutualistic outcomes (Persson, 2006);(Ji et al., 2022);(Dalhammar et al., 2018). Market-based instruments like carbon pricing also effectively promote eco-innovation, though they often require supplementation with stringent controls to drive more radical change (Sánchez & Deza 2015).
The real-world application of these mutualistic approaches provides valuable lessons. Successful case studies reveal common key factors in the finance realm, innovations such as ‘biodiversity credits’ and nature-linked green bonds are being explored as ways to scale up private sector investment. These instruments are designed to create a mutualistic link where financial returns are directly tied to verifiable ecological outcomes, aligning with the goal of increasing transparency and accountability in biodiversity finance.
For instance, successful cross-border cooperation between Cieszyn (Poland) and Cesky Tesin (Czech Republic) was driven by clear goals, diverse stakeholder involvement, and guaranteed mutual benefits (Kurowska-Pysz et al., 2018). Similarly, successful Public-Private Partnerships (PPPs) in developing countries and a university- city partnership in Malmö, Sweden, underscore the importance of strategic alignment, transparent and participatory governance, and mutual learning processes (Tanveer et al., 2025); (Stauffacher et al., 2008).
Conversely, cases of failure offer critical insights. One international alliance failed due to a high dependency on single-project success and the difficulty for small companies to lead independently, highlighting structural challenges for smaller actors (Hollins, 2006). Another example of a lack of mutualism in a production relationship between Finland and Somalia showed that without an equitable distribution of benefits and production capacity, such relationships become unsustainable (Fox et al., 2020).
From these cases, several universal lessons can be drawn. First, inclusivity and stakeholder engagement are fundamental prerequisites; all parties must have ownership and derive benefits. Second, success hinges on clear objectives and strategic alignment from the outset. Third, transparent and collaborative governance is crucial for building trust and ensuring accountability. Finally, a mutualistic approach must consciously address power and capacity imbalances, especially in international collaborations, to ensure equitable and sustainable relationships. Therefore, the application of appropriate policy instruments must be accompanied by careful and adaptive partnership design based on these lessons.
Navigating Synergies and Trade-offs within the SDG Framework
The shift from a paradigm of coexistence to one of mutualism demands a nuanced understanding of how biodiversity conservation efforts interact with the broader Sustainable Development Goals (SDGs). These interactions manifest as both mutually reinforcing synergies and conflict-laden trade-offs. This section reviews the most significant synergies, analyzes the primary areas of conflict, and outlines strategies for their management based on findings from the extant literature.
Biodiversity conservation efforts demonstrate powerful synergies with the achievement of several key SDGs. Most prominently, this is visible with SDG 2 (Zero Hunger), where ecosystem services such as pollination, natural pest control, and soil fertility all of which are underpinned by biodiversity are crucial for enhancing agricultural productivity and resilience (Yang et al., 2020);(Makwinja et al., 2022);(Hu et al., 2022). Ecosystem restoration programs have also been shown to synergistically advance SDG 2 (Yao et al., 2021). An equally strong synergy exists with SDG 6 (Clean Water and Sanitation), as healthy ecosystems act as natural water filters and protect watersheds, which is essential for maintaining water quality and availability (Yang et al., 2020); (Yao et al., 2021); (E et al., 2020). Furthermore, conservation is a core component of SDG 13 (Climate Action), given that biodiversity-rich ecosystems like forests and wetlands are vital for carbon sequestration and climate regulation (Yang et al., 2020); (Hu et al., 2022); (E et al., 2020). The synergies also extend to goals such as SDG 1 (No Poverty), where ecosystem services support local livelihoods through fisheries, forestry, and tourism, thereby offering pathways for poverty alleviation (Yang et al., 2020); (Sustainable protected areas: synergies between biodiversity conservation and socioeconomic development, 2022); (Integrating ecology and poverty reduction: Ecological dimensions, 2012).
Despite these powerful synergies, conflicts between conservation and development objectives are unavoidable. The most acute trade-offs often emerge at the nexus of economic development and conservation. Agricultural expansion to meet food demands and the extraction of natural resources like oil, gas, and minerals frequently occur in areas of high biodiversity, creating direct conflicts (Grigg, 2007);(Chahar et al., 2016). Similarly, infrastructure development, including urbanization and port expansion, leads to habitat fragmentation and loss (Chahar et al., 2016); (Rajvanshi et al., 2009). Conflicts are also common within protected area management, where divergent stakeholder interests can impede the simultaneous achievement of social and environmental goals (Fisher et al., 2023).
The literature suggests several strategies to navigate these complex trade-offs. First, inclusive stakeholder engagement is critical for minimizing conflict and ensuring equitable outcomes, even if it is resource-intensive (Fisher et al., 2023); (Broussard et al., 2023). Second, analytical tools like Multi-Criteria Decision Analysis (MCDA) can help formally and transparently assess trade-offs between ecological and socio-economic goals (Drechsler, 2004). Third, the economic valuation of ecosystem services can build a compelling financial case for conservation, particularly for the finance sector (Grigg, 2007). Fourth, policy coherence between global biodiversity regimes and national policies, supported by a strong science-policy interface, is essential (Kedia & Anand, 2021). Finally, adaptive management approaches that embrace flexibility and a broader ethical-cultural discourse on the value of biodiversity can help manage uncertainty and align public perception with policy objectives (The emergence of biodiversity conflicts from biodiversity impacts: characteristics and management strategies, 2010); (Clémençon, 2021). By employing these strategies, it is possible to balance competing demands and steer interactions away from mere coexistence and toward genuine mutualism.
The shift from a paradigm of coexistence to one of mutualism demands a nuanced understanding of how biodiversity conservation efforts interact with the broader Sustainable Development Goals (SDGs). These interactions manifest as both mutually reinforcing synergies and conflict-laden trade-offs. On one hand, conservation efforts demonstrate powerful synergies with key goals, including SDG 2 (Zero Hunger), SDG 6 (Clean Water and Sanitation), and SDG 13 (Climate Action), where healthy ecosystems provide foundational services. Conversely, the most acute trade-offs often emerge at the nexus of conservation and economic development objectives, such as those outlined in SDG 8 (Decent Work and Economic Growth) and SDG 9 (Industry, Innovation, and Infrastructure). Navigating this complex landscape thus requires strategic management to mitigate negative impacts and foster mutually beneficial outcomes. The following Table 1 synthesizes these key interactions, illustrating the primary synergies, most common trade-offs, and proposed mutualistic management strategies for select, representative SDGs.
| Relevant SDG |
Primary synergy with biodiversityconservation |
Primary trade-off with biodiversity conservation | Mutualistic management and mitigation strategy |
|---|---|---|---|
| SDG 1 (No Poverty) | Ecosystem services support local livelihoods through fisheries, forestry, and tourism, providing pathways for poverty alleviation. |
Access restrictions to resources in protected areas can adversely affect r e sour ce-de pende nt communities. |
Implement inclusive stakeholder engagement and establish equitable benefit-sharing schemes. |
| SDG 2 (Zero Hunger) | Ecosystem services such as pollination, natural pest control, and soil fertility are crucial for enhancing agricultural productivity and resilience | Agricultural expansion to achieve food security objectives often leads to habitat loss and deforestation in areas of high biodiversity. | Adopt regenerative agriculture and agroforestry practices; integrate the economic valuation of ecosystem services into land use planning. |
| SDG 6 (Clean Water and Sanitation) | Healthy ecosystems function as natural water purifiers and protect water catchments, which is essential for maintaining water quality and availability. | The development of water infrastructure, such as dams, can alter river flows and degrade aquatic habitats. | Employ Nature-based Solutions (NbS) for water management; utilize Multi- Criteria Decision Analysis (MCDA) to assess trade-offs. |
|
SDG 8 (Decent Work and Economic Growth) and SDG 9 (Industry, Innovation and Infrastructure) |
Ecotourism and other nature-based industries create novel economic opportunities. | Infrastructure development (e.g., urbanization, ports) and resource extraction (e.g., mining, oil, gas) result in habitat fragmentation and loss. | Enforce stringent biodiversity offset policies; utilize integrated spatial planning; ensure early and inclusive stakeholder engagement to minimize conflicts. |
| SDG 13 (Climate Action) | Carbon-rich ecosystems, such as forests and wetlands, are vital for carbon sequestration and enhancing resilience to climate impacts. | Certain energy solutions, such as large-scale bioenergy production, may compete for land with natural habitats. | Integrate NbS into National Climate Action Plans and align Nationally Determined Contributions(NDCs) with National Biodiversity Strategies and Action Plans (NBSAPs). |
CONCLUSION
This review concludes that the prevailing coexistence paradigm for mainstreaming biodiversity is insufficient to achieve the 2030 Agenda, making a fundamental shift toward mutualism an urgent necessity. The current separation of conservation and development perpetuates policy incoherence and unresolved trade-offs, undermining long-term ecological and social well-being. While progress is evident through innovative models like Nature-based Solutions and Payments for Ecosystem Services, their impact is constrained by deep-seated financial, institutional, and social barriers. To overcome these obstacles and harness the powerful synergies between biodiversity and key SDGs, a systemic approach is required, centered on integrated policy mixes, inclusive governance, and equitable partnerships that actively generate shared value. Ultimately, embedding this mutualistic ethos into all development planning is not merely an ecological ideal but a pragmatic and essential strategy for building resilient, equitable societies and realizing a future where human prosperity and a thriving biosphere are understood to be inseparably linked.
Policy Implications and Future Directions
The transition toward mutualism requires concrete actions. For policymakers, this review highlights the need to move beyond fragmented, single-issue regulations toward integrated policy mixes that reward the generation of reciprocal benefits. This includes designing financial mechanisms like PES and green bonds that not only fund conservation but also create measurable value for development actors. Furthermore, establishing transparent and inclusive governance platforms is essential to manage trade-offs and build the trust necessary for multi-stakeholder partnerships to succeed.
For future research, several gaps need to be addressed. First, there is a pressing need for robust, standardized metrics to quantify ‘mutualism’ in practice—how can we measure the reciprocal benefits between development projects and ecosystem health? Second, more longitudinal case studies are required to track the socio-economic and ecological outcomes of projects that explicitly adopt a mutualistic framework. Finally, research should explore the cultural and social barriers to mutualism, such as power imbalances and historical distrust, and identify strategies to foster a collaborative ethos essential for sustainable development. Addressing these research questions will be vital to operationalize the mutualistic paradigm and accelerate progress toward the 2030 Agenda.
References
- A multi‐methods approach for assessing how conserving biodiversity interacts with other sustainable development goals in Nepal. Sustain Dev. 2023; 31(5):3239-3253.
- Ament J.M., Collen B., Carbone C., Mace G.M., Freeman R.. Compatibility between agendas for improving human development and wildlife conservation outside protected areas: insights from 20 years of data. People Nat. 2019; 1(3):305-316. DOI
- Andrei J., Ion R., Chivu L., Pop R.-E., Marin A.. Investigations on farmers’ willingness to associate and join in environmental responsible short supply chain in Romania. Appl Ecol Environ Res. 2019; 17(2):1617-1639. DOI
- Azizi D., Biermann F., Kim R.E.. Policy integration for sustainable development through multilateral environmental agreements: An empirical analysis, 2007-2016. Glob Govern. 2019; 25(3):445-475. DOI
- Basheer N., Ahmed V., Bahroun Z., Al-Othman A., Al-Marzouqi A., Al-Ohaly A.-H.. Sustainability assessment in higher education institutions: exploring indicators, stakeholder perceptions, and implementation challenges. Discov Sustain. 2025; 6(252)DOI
- Broussard A., Dahdouh-Guebas F., Hugé J.. Diversity of perspectives in biodiversity conservation: A case study of port land use in Antwerp and Rotterdam. J Environ Manage. 2023; 341(117937)DOI
- Chahar S.S., Kumar D., Singh A.K.. Biodiversity conservation and sustainable development: Are we doing enough? A review. Biochem Cell Arch. 2016; 16(Suppl 1):317-322.
- Clémençon R.. Is sustainable development bad for global biodiversity conservation? Glob Sustain 4:e16. 2021. DOI
- Dalhammar C., Luth Richter J., Machacek E.. Cambridge University Press: Cambridge (UK; 2018. DOI
- Davis E.J., Huber-Stearns H., Caggiano M., McAvoy D., Cheng A.S., Deak A., Evans A.. Managed wildfire: A strategy facilitated by civil society partnerships and interagency cooperation. Soc Nat Resour. 2022; 35(8):975-993. DOI
- Dickens C., McCartney M., Tickner D., Harrison I.J., Pacheco P., Ndhlovu B.. Evaluating the global state of ecosystems and natural resources: Within and beyond the SDGs. Sustainability. 2020; 12(18)DOI
- Domenech T., Bleischwitz R., Doranova A., Panayotopoulos D., Roman L.. Mapping industrial symbiosis development in Europe: Typologies of networks, characteristics, performance and contribution to the circular economy. Resour Conserv Recycl. 2019; 141:76-98. DOI
- Drechsler M.. Model-based conservation decision aiding in the presence of goal conflicts and uncertainty. Biodivers Conserv. 2004; 13(1):141-164.
- When cheating turns into a stabilizing mechanism of plant–pollinator communities. PLoS Biol. 2023; 21(12)DOI
- Dunkley K., Ward A.J.W., Perkins S.E., Cable J.. To clean or not to clean: Cleaning mutualism breakdown in a tidal environment. Ecol Evol. 2020; 10(6):3043-3054. DOI
- Egger K.N., Hibbett D.S.. The evolutionary implications of exploitation in mycorrhizas 1. 2004. Publisher Full Text
- Ernoul L., Mesleard F.. Adaptive management of an estuarine integrated conservation and development project in Morocco. Environ Conserv. 2008; 35(4):279-280. DOI
- Fader M., Cranmer C., Lawford R., Engel-Cox J.. Toward an understanding of synergies and trade-offs between water, energy, and food SDG targets. Front Environ Sci. 2018; 6(112)DOI
- Fenner R.. Springer: Cham (CH; 2022. DOI
- Fisher J., Allen S., Woomer A., Crawford A.. Protected areas under pressure: An online survey of protected area managers regarding social and environmental conservation target attainment and stakeholder conflicts. World Dev Sustain. 2023; 3(100084)DOI
- Fox S., Mubarak Y., Adam A.. Ecological analyses of social sustainability for international production with fixed and moveable technologies. Sustainability. 2020; 12(20)DOI
- Frank A.S.K., Schäffler L.. Identifying key knowledge gaps to better protect biodiversity and simultaneously secure livelihoods in a priority conservation area. Sustainability. 2019; 11(20)DOI
- Gao Y., Clark S.G.. An interdisciplinary conception of human-wildlife coexistence. J Nat Conserv. 2023; 73(126370)DOI
- Sustainable protected areas: synergies between biodiversity conservation and socioeconomic development. People Nat. 2022; 4:893-903. DOI
- E Gómez Martín, R Giordano, A Pagano, Keur PM Máñez Costa. Using a system thinking approach to assess the contribution of nature based solutions to sustainable development goals. Sci Total Environ. 2020; 738(139693)DOI
- Grigg A.. Greenleaf Publishing: Sheffield (UK; 2007.
- Grman E., Robinson T.M., Klausmeier C.A.. Ecological specialization and trade affect the outcome of negotiations in mutualism. Am Nat. 2012; 179(5):567-581. DOI
- Himshikha Sharma T., T Kaur, A Singh, A Mohapatra, N Saikia. Springer: Singapore (SG; 2024. DOI
- Hollins W.J.. When everything seems right and it still goes wrong: A case study. DS 36: Proceedings of DESIGN 2006, the 9th International Design Conference. 2006;847-854. Publisher Full Text
- Hu S., Yang Y., Li A., Liu K., Mi C., Shi R.. Integrating ecosystem services into assessments of sustainable development goals: A case study of the Beijing-Tianjin-Hebei Region, China. Front Environ Sci. 2022; 10(897792)DOI
- Springer: New York (US; 2012. DOI
- Ji X., Wu G., Lin J., Zhang J., Su P.. Reconsider policy allocation strategies: A review of environmental policy instruments and application of the CGE model. J Environ Manage. 2022; 323(116176)DOI
- Kearney M.. Astonishingly hyperconnected. Issues Sci Technol. 2022; 38(2):77-80.
- Kedia S., Anand M.. Global biodiversity regime complex and sustainable development goals: Implications for India. Asian Biotechnol Dev Rev. 2021; 23(2):57-87.
- Khan K.I., Shehzad A.. Investing in nature: A bibliometric analysis of biodiversity finance and its contribution to SDGs 14 and 15. Sustain Dev. 2025; 33(4):5436-5457. DOI
- King N.A.S.. The role of district commissioners in managing sustainable development in Tanzania. OIDA Int J Sustain Dev. 2025; 18(1):67-72.
- Kloke-Lesch A..In: Chaturvedi S., Janus H., Klingebiel S., Li X., AdM Souza, Sidiropoulos E., Wehrmann D.. The Palgrave handbook of development cooperation for achieving the 2030 Agenda. Palgrave Macmillan: Palgrave Macmillan; 2021. DOI
- Kuc-Czarnecka M., Markowicz I., Sompolska-Rzechuła A.. SDGs implementation, their synergies, and trade-offs in EU countries: Sensitivity analysis-based approach. Ecol Indic. 2023; 146(109888)DOI
- Kurowska-Pysz J., Castanho R.A., Loures L.. Sustainable planning of cross-border cooperation: a strategy for alliances in border cities. Sustainability. 2018; 10(5)DOI
- The added value of partnerships in implementing the UN sustainable development goals. J Clean Prod. 2024; 438(140794)DOI
- Lernborg C.M., Atallah M..In: W Leal Filho, AM Azul, LL Brandli, PG Özuyar, T Wall. Routledge handbook of the UN sustainable development goals research and policy. Routledge: Routledge; 2025.
- Lucas P.L., Kok M.T.J., Nilsson M., Alkemade R.. Integrating biodiversity and ecosystem services in the post-2015 development agenda: Goal structure, target areas and means of implementation. Sustainability. 2014; 6(1):193-216. DOI
- Lydgate E.. Sustainable development in the WTO: from mutual supportiveness to balancing Brighton. 2012. Publisher Full Text
- Makwinja R., Mengistou S., Kaunda E., Alamirew T.. Managing ecosystem services demand under a changing catchment: A case study of Lake Malombe Catchment, Malawi. GeoJournal. 2022; 87(5):5305-5325. DOI
- Mamabolo E., Makwela M.M., Tsilo T.J.. Achieving sustainability and biodiversity conservation in agriculture: Importance, challenges and prospects. Eur J Sustain Dev. 2020; 9(3):616-628. DOI
- McGowan P.J.K., Stewart G.B., Long G., Grainger M.J.. An imperfect vision of indivisibility in the Sustainable Development Goals. Nat Sustain. 2019; 2(1):43-45. DOI
- Assessing the land resource–food price nexus of the Sustainable Development Goals. Sci Adv. 2016; 2(9)DOI
- Ogwu M.C., El Malahi S., Izah S.C..In: Ogwu M.C., Chibueze Izah S.. Evaluating environmental processes and technologies. Springer: Springer; 2025. DOI
- A Pereira Santos, X Vence. Environmental policy instruments and eco-innovation: An overview of recent studies. Innovar. 2015; 25(58):65-80. DOI
- Persson Å.. Characterizing the policy instrument mixes for municipal waste in Sweden and England. Eur Environ. 2006; 16(4):222-236. DOI
- Petitpierre-Sauvain A..In: Wüger D., Cottier T.. Genetic engineering and the world trade system: World Trade Forum. Cambridge University Press: Cambridge University Press; 2008:175-192.
- Time to integrate global climate change and biodiversity science-policy agendas. J Appl Ecol. 2021; 58:2384-2393. DOI
- Powell B.M., Maoz I.. Barriers to conflict resolution in landscapes of asymmetric conflict: Current issues and future directions. Dyn Asymmetric Conflict. 2014; 7(2–3):226-235. DOI
- Rajvanshi A., Mathur V.B., Slootweg R., Kolhoff A..In: Slootweg R., Rajvanshi A., Mathur V.B., Kolhoff A.. Biodiversity in environmental assessment: Enhancing ecosystem services for human well-being. Cambridge University Press: Cambridge University Press; 2009:255-286.
- Restrepo J.D., Bottaro G., Barci L., Beltrán L.M., Londoño-Behaine M., Masiero M.. Assessing the impacts of nature-based solutions on ecosystem services: A water-energy-food-ecosystems nexus approach in the Nima River sub-basin (Colombia. Forests. 2024; 15(11)DOI
- Scolobig A., Martin J., Linnerooth-Bayer J., Aguilera Rodriguez J.J., Fresolone-Caparrós A..In: Pan H., Kalantari Z., Ferreira C., Cong C.. Nature-based solutions in supporting sustainable development goals. Elsevier: Elsevier; 2025:129-151. DOI
- Sharma S., Sharma P.. Temporal depth & directionality: Competitive advantage for sustainable family enterprises. Eur J Fam Bus. 2024; 14(1):5-18. DOI
- Stauffacher M., Flüeler T., Krütli P., Scholz R.W.. Analytic and dynamic approach to collaboration: A transdisciplinary case study on sustainable landscape development in a Swiss Prealpine region. Syst Pract Action Res. 2008; 21(5):409-422. DOI
- Szymańska E.J., Rysz M., Utnik-Banaś K.. Cooperation of fruit farms with the institutional environment toward sustainable development. Sustainability. 2023; 15(8)DOI
- Tanveer U., Hoang T.G., Ishaq S., Khalid R.U.. Public-private partnerships as catalysts for digital transformation and circular economy: Insights from developing countries. Technol Forecast Soc Change. 2025; 219(124270)DOI
- Thool V..In: Fontaine-Skronski K., Thool V., Eschborn N.. Does the UN model still work? Challenges and prospects for the future of multilateralism. Brill: Brill; 2023. Publisher Full Text
- Wang S., Zhang Z., Wang Z., Liu G.. Exploring the multidimensional factors and emergence mechanisms of industrial symbiotic relationships based on machine learning. J Clean Prod. 2022; 381(135169)DOI
- Wei W., Shen X., Liu Y.. Toward developing a new funding mechanism to support post-2020 biodiversity conservation. Biodivers Sci. 2021; 29(2):259-268. DOI
- Yang S., Zhao W., Liu Y., Cherubini F., Fu B., Pereira P.. Prioritizing sustainable development goals and linking them to ecosystem services: A global expert’s knowledge evaluation. Geogr Sustain. 2020; 1(4):321-330. DOI
- Yao Y., Fu B., Liu Y., Wang Y., Song S.. The contribution of ecosystem restoration to sustainable development goals in Asian drylands: A literature review. Land Degrad Dev. 2021; 32(16):4472-4483. DOI
- The emergence of biodiversity conflicts from biodiversity impacts: characteristics and management strategies. Biodivers Conserv. 2010; 19(14):3973-3990. DOI
Adhikari B, Urbach D, Chettri N, Sharma E, Breu T, Geschke J, …, Prescott GW. 2023. A multi‐methods approach for assessing how conserving biodiversity interacts with other sustainable development goals in Nepal. Sustain Dev 31(5):3239-3253. DOI: https://doi.org/10.1002/sd.2582
Ament JM, Collen B, Carbone C, Mace GM, Freeman R. 2019. Compatibility between agendas for improving human development and wildlife conservation outside protected areas: insights from 20 years of data. People Nat 1(3):305–316. DOI: 10.1002/pan3.10041 DOI: https://doi.org/10.1002/pan3.10041
Andrei J, Ion R, Chivu L, Pop R-E, Marin A. 2019. Investigations on farmers’ willingness to associate and join in environmental responsible short supply chain in Romania. Appl Ecol Environ Res 17(2):1617–1639. DOI: 10.15666/aeer/1702_16171639 DOI: https://doi.org/10.15666/aeer/1702_16171639
Azizi D, Biermann F, Kim RE. 2019. Policy integration for sustainable development through multilateral environmental agreements: An empirical analysis, 2007-2016. Glob Govern 25(3):445-475. DOI: 10.1163/19426720-02503005 DOI: https://doi.org/10.1163/19426720-02503005
Basheer N, Ahmed V, Bahroun Z, Al-Othman A, Al-Marzouqi A, Al-Ohaly A-H. 2025. Sustainability assessment in higher education institutions: exploring indicators, stakeholder perceptions, and implementation challenges. Discov Sustain 6:252. DOI: 10.1007/s43621-025-01116-w DOI: https://doi.org/10.1007/s43621-025-01116-w
Broussard A, Dahdouh-Guebas F, Hugé J. 2023. Diversity of perspectives in biodiversity conservation: A case study of port land use in Antwerp and Rotterdam. J Environ Manage 341:117937. DOI: 10.1016/j.jenvman.2023.117937 DOI: https://doi.org/10.1016/j.jenvman.2023.117937
Chahar SS, Kumar D, Singh AK. 2016. Biodiversity conservation and sustainable development: Are we doing enough? A review. Biochem Cell Arch 16(Suppl 1):317–322.
Clémençon R. 2021. Is sustainable development bad for global biodiversity conservation? Glob Sustain 4:e16. DOI: 10.1017/sus.2021.14 DOI: https://doi.org/10.1017/sus.2021.14
Dalhammar C, Luth Richter J, Machacek E. 2018. Energy efficiency regulations, market and behavioural failures and standardization. In: Maitre-Ekern E, Dalhammar C, Bugge HC (Editors), Preventing environmental damage from products: an analysis of the policy and regulatory framework in Europe. Cambridge (UK): Cambridge University Press. p. 176-228. DOI: 10.1017/9781108500128.008 DOI: https://doi.org/10.1017/9781108500128.008
Davis EJ, Huber-Stearns H, Caggiano M, McAvoy D, Cheng AS, Deak A, Evans A. 2022. Managed wildfire: A strategy facilitated by civil society partnerships and interagency cooperation. Soc Nat Resour 35(8):975-993. DOI: 10.1080/08941920.2022.2092803 DOI: https://doi.org/10.1080/08941920.2022.2092803
Dickens C, McCartney M, Tickner D, Harrison IJ, Pacheco P, Ndhlovu B. 2020. Evaluating the global state of ecosystems and natural resources: Within and beyond the SDGs. Sustainability 12(18):7381. DOI: 10.3390/su12187381 DOI: https://doi.org/10.3390/su12187381
Domenech T, Bleischwitz R, Doranova A, Panayotopoulos D, Roman L. 2019. Mapping industrial symbiosis development in Europe: Typologies of networks, characteristics, performance and contribution to the circular economy. Resour Conserv Recycl 141:76–98. DOI: 10.1016/j.resconrec.2018.09.016. DOI: https://doi.org/10.1016/j.resconrec.2018.09.016
Drechsler M. 2004. Model-based conservation decision aiding in the presence of goal conflicts and uncertainty. Biodivers Conserv 13(1):141–164. DOI: https://doi.org/10.1023/B:BIOC.0000004316.91025.8c
Duchenne F, Aubert S, Barreto E, Brenes E, Maglianesi MA, Santander T, …, Graham CH. 2023. When cheating turns into a stabilizing mechanism of plant–pollinator communities. PLoS Biol 21(12):e3002434. DOI: 10.1371/journal.pbio.3002434 DOI: https://doi.org/10.1371/journal.pbio.3002434
Dunkley K, Ward AJW, Perkins SE, Cable J. 2020. To clean or not to clean: Cleaning mutualism breakdown in a tidal environment. Ecol Evol 10(6):3043–3054. DOI: 10.1002/ece3.6120 DOI: https://doi.org/10.1002/ece3.6120
Egger KN, Hibbett DS. 2004. The evolutionary implications of exploitation in mycorrhizas 1. [Internet]. [cited 2025 Aug 14]. Available from: https://commons.clarku.edu/ faculty_biology/280
Ernoul L, Mesleard F. 2008. Adaptive management of an estuarine integrated conservation and development project in Morocco. Environ Conserv 35(4):279–280. DOI: 10.1017/s0376892908005158 DOI: https://doi.org/10.1017/S0376892908005158
Fader M, Cranmer C, Lawford R, Engel-Cox J. 2018. Toward an understanding of synergies and trade-offs between water, energy, and food SDG targets. Front Environ Sci 6:112. DOI: 10.3389/fenvs.2018.00112 DOI: https://doi.org/10.3389/fenvs.2018.00112
Fenner R. 2022. Common themes, accelerating progress and beyond 2030. In: Rajapakse J (Editor), Safe water and sanitation for a healthier world. Cham (CH): Springer. DOI: 10.1007/978-3-030-94020-1_12 DOI: https://doi.org/10.1007/978-3-030-94020-1_12
Fisher J, Allen S, Woomer A, Crawford A. 2023. Protected areas under pressure: An online survey of protected area managers regarding social and environmental conservation target attainment and stakeholder conflicts. World Dev Sustain 3:100084. DOI: 10.1016/j.wds.2023.100084 DOI: https://doi.org/10.1016/j.wds.2023.100084
Fox S, Mubarak Y, Adam A. 2020. Ecological analyses of social sustainability for international production with fixed and moveable technologies. Sustainability 12(20):8476. DOI: 10.3390/su12208476 DOI: https://doi.org/10.3390/su12208476
Frank ASK, Schäffler L. 2019. Identifying key knowledge gaps to better protect biodiversity and simultaneously secure livelihoods in a priority conservation area. Sustainability 11(20):5695. DOI: 10.3390/su11205695 DOI: https://doi.org/10.3390/su11205695
Gao Y, Clark SG. 2023. An interdisciplinary conception of human-wildlife coexistence. J Nat Conserv 73:126370. DOI: 10.1016/j.jnc.2023.126370 DOI: https://doi.org/10.1016/j.jnc.2023.126370
Gatiso TT, Kulik L, Bachmann M, Bonn A, Bösch L, Freytag A, , …, Kühl HS. 2022. Sustainable protected areas: synergies between biodiversity conservation and socioeconomic development. People Nat 4:893–903. DOI: 10.1002/pan3.10326 DOI: https://doi.org/10.1002/pan3.10326
Gómez Martín E, Giordano R, Pagano A, van der Keur P, Máñez Costa M. 2020. Using a system thinking approach to assess the contribution of nature based solutions to sustainable development goals. Sci Total Environ 738:139693. DOI: 10.1016/j.scitotenv.2020.139693 DOI: https://doi.org/10.1016/j.scitotenv.2020.139693
Grigg A. 2007. Biodiversity and the extractive industry: innovative practices and remaining challenges. In: Addison J (Editor), The business of biodiversity: The new imperative for corporate responsibility. Sheffield (UK): Greenleaf Publishing. p. 83–91.
Grman E, Robinson TM, Klausmeier CA. 2012. Ecological specialization and trade affect the outcome of negotiations in mutualism. Am Nat 179(5):567–581. DOI: 10.1086/665006 DOI: https://doi.org/10.1086/665006
Himshikha, Sharma T, Kaur T, Singh A, Mohapatra A, Saikia N. 2024. Regenerative agriculture and sustainable development goals. In: Kumar S, Meena RS, Sheoran P, Jhariya MK (Editors), Regenerative agriculture for sustainable food systems. Singapore (SG): Springer. DOI: 10.1007/978-981-97-6691-8_5 DOI: https://doi.org/10.1007/978-981-97-6691-8_5
Hollins WJ. 2006. When everything seems right and it still goes wrong: A case study. In: Marjanovic D (Editor), DS 36: Proceedings of DESIGN 2006, the 9th International Design Conference. Glasgow (UK): The Design Society. p. 847–854. Available from: https://www.designsociety.org/publication/19083/when_everything_seems_right_and_it_still_goes_wrong_–_a_case_study.
Hu S, Yang Y, Li A, Liu K, Mi C, Shi R. 2022. Integrating ecosystem services into assessments of sustainable development goals: A case study of the Beijing-Tianjin-Hebei Region, China. Front Environ Sci 10:897792. DOI: 10.3389/fenvs.2022.897792 DOI: https://doi.org/10.3389/fenvs.2022.897792
Ingram JC, DeClerck F, Rumbaitis del Rio C (Editors). 2012. Integrating ecology and poverty reduction: Ecological dimensions. New York (US): Springer. DOI: 10.1007/978-1-4419-0633-5 DOI: https://doi.org/10.1007/978-1-4419-0633-5
Ji X, Wu G, Lin J, Zhang J, Su P. 2022. Reconsider policy allocation strategies: A review of environmental policy instruments and application of the CGE model. J Environ Manage 323:116176. DOI: 10.1016/j.jenvman.2022.116176 DOI: https://doi.org/10.1016/j.jenvman.2022.116176
Kearney M. 2022. Astonishingly hyperconnected. Issues Sci Technol 38(2):77–80.
Kedia S, Anand M. 2021. Global biodiversity regime complex and sustainable development goals: Implications for India. Asian Biotechnol Dev Rev 23(2):57–87.
Khan KI, Shehzad A. 2025. Investing in nature: A bibliometric analysis of biodiversity finance and its contribution to SDGs 14 and 15. Sustain Dev 33(4):5436–5457. DOI: 10.1002/sd.3416 DOI: https://doi.org/10.1002/sd.3416
King NAS. 2025. The role of district commissioners in managing sustainable development in Tanzania. OIDA Int J Sustain Dev 18(1):67–72.
Kloke-Lesch A. 2021. The untapped functions of international cooperation in the age of sustainable development. In: Chaturvedi S, Janus H, Klingebiel S, Li X, e Souza AdM, Sidiropoulos E, Wehrmann D (Editors), The Palgrave handbook of development cooperation for achieving the 2030 Agenda. Cham (CH): Palgrave Macmillan. DOI: 10.1007/978-3-030-57938-8_7 DOI: https://doi.org/10.1007/978-3-030-57938-8_7
Kuc-Czarnecka M, Markowicz I, Sompolska-Rzechuła A. 2023. SDGs implementation, their synergies, and trade-offs in EU countries: Sensitivity analysis-based approach. Ecol Indic 146:109888. DOI: 10.1016/j.ecolind.2023.109888 DOI: https://doi.org/10.1016/j.ecolind.2023.109888
Kurowska-Pysz J, Castanho RA, Loures L. 2018. Sustainable planning of cross-border cooperation: a strategy for alliances in border cities. Sustainability 10(5):1416. DOI: 10.3390/su10051416 DOI: https://doi.org/10.3390/su10051416
Leal Filho W, Dibbern T, Pimenta Dinis MA, Coggo Cristofoletti E, Mbah MF, Mishra A, …, Aina YA. 2024. The added value of partnerships in implementing the UN sustainable development goals. J Clean Prod 438:140794. DOI: 10.1016/j.jclepro.2024.140794 DOI: https://doi.org/10.1016/j.jclepro.2024.140794
Lernborg CM, Atallah M. 2025. The role of payment for ecosystem services in achieving the sustainable development goals: lessons for biodiversity in the Democratic Republic of the Congo. In: Leal Filho W, Azul AM, Brandli LL, Özuyar PG, Wall T (Editors), Routledge handbook of the UN sustainable development goals research and policy. Abingdon (UK): Routledge. DOI: https://doi.org/10.4324/9781003285472-31
Lucas PL, Kok MTJ, Nilsson M, Alkemade R. 2014. Integrating biodiversity and ecosystem services in the post-2015 development agenda: Goal structure, target areas and means of implementation. Sustainability 6(1):193-216. DOI: 10.3390/su6010193 DOI: https://doi.org/10.3390/su6010193
Lydgate E. 2012. Sustainable development in the WTO: from mutual supportiveness to balancing Brighton (UK): University of Sussex. [Internet]. [cited 2025 Aug 14]. Available from: https://hdl.handle.net/10779/uos.23398436.v1
Makwinja R, Mengistou S, Kaunda E, Alamirew T. 2022. Managing ecosystem services demand under a changing catchment: A case study of Lake Malombe Catchment, Malawi. GeoJournal 87(5):5305–5325. DOI: 10.1007/s10708-022-10575-x DOI: https://doi.org/10.1007/s10708-022-10575-x
Mamabolo E, Makwela MM, Tsilo TJ. 2020. Achieving sustainability and biodiversity conservation in agriculture: Importance, challenges and prospects. Eur J Sustain Dev 9(3):616-628. DOI: 10.14207/ejsd.2020.v9n3p616 DOI: https://doi.org/10.14207/ejsd.2020.v9n3p616
McGowan PJK, Stewart GB, Long G, Grainger MJ. 2019. An imperfect vision of indivisibility in the Sustainable Development Goals. Nat Sustain 2(1):43–45. DOI: 10.1038/s41893-018-0219-5 DOI: https://doi.org/10.1038/s41893-018-0190-1
Obersteiner M, Walsh B, Frank S, Havlík P, Cantele M, Liu J, …, van Vuuren D. 2016. Assessing the land resource–food price nexus of the Sustainable Development Goals. Sci Adv 2(9):e1501499. DOI: 10.1126/sciadv.1501499 DOI: https://doi.org/10.1126/sciadv.1501499
Ogwu MC, El Malahi S, Izah SC. 2025. Policy and regulatory frameworks for sustainable environmental practices. In: Ogwu MC, Chibueze Izah S (Editors), Evaluating environmental processes and technologies. Cham (CH): Springer. DOI: 10.1007/978-3-031-85327-2_16 DOI: https://doi.org/10.1007/978-3-031-85327-2
Pereira Santos A, Vence X. 2015. Environmental policy instruments and eco-innovation: An overview of recent studies. Innovar 25(58):65–80. DOI: 10.15446/innovar.v25n58.52426 DOI: https://doi.org/10.15446/innovar.v25n58.52426
Persson Å. 2006. Characterizing the policy instrument mixes for municipal waste in Sweden and England. Eur Environ 16(4):222-236. DOI: 10.1002/eet.419 DOI: https://doi.org/10.1002/eet.419
Petitpierre-Sauvain A. 2008. Coexistence and liability: Implications for international trade drawn from the Swiss example. In: Wüger D, Cottier T (Editors), Genetic engineering and the world trade system: World Trade Forum. Cambridge (UK): Cambridge University Press. p. 175–192. DOI: https://doi.org/10.1017/CBO9780511494581.008
Pettorelli N, Graham NAJ, Seddon N, da Cunha Bustamante M, Lowton MJ, Sutherland WJ, …, Barlow J. 2021. Time to integrate global climate change and biodiversity science-policy agendas. J Appl Ecol 58:2384–2393. DOI: 10.1111/1365-2664.13985 DOI: https://doi.org/10.1111/1365-2664.13985
Powell BM, Maoz I. 2014. Barriers to conflict resolution in landscapes of asymmetric conflict: Current issues and future directions. Dyn Asymmetric Conflict 7(2–3):226–235. DOI: 10.1080/17467586.2014.980283 DOI: https://doi.org/10.1080/17467586.2014.980283
Rajvanshi A, Mathur VB, Slootweg R, Kolhoff A. 2009. Reconciling conservation and development: the role of biodiversity offsets. In: Slootweg R, Rajvanshi A, Mathur VB, Kolhoff A (Editors), Biodiversity in environmental assessment: Enhancing ecosystem services for human well-being. Cambridge (UK): Cambridge University Press. p. 255-286. DOI: https://doi.org/10.1017/CBO9781139195775.013
Restrepo JD, Bottaro G, Barci L, Beltrán LM, Londoño-Behaine M, Masiero M. 2024. Assessing the impacts of nature-based solutions on ecosystem services: A water-energy-food-ecosystems nexus approach in the Nima River sub-basin (Colombia). Forests 15(11):1852. DOI: 10.3390/f15111852 DOI: https://doi.org/10.3390/f15111852
Scolobig A, Martin J, Linnerooth-Bayer J, Aguilera Rodriguez JJ, Fresolone-Caparrós A. 2025. Policy, finance, and capacity-building innovations for scaling nature-based solutions. In: Pan H, Kalantari Z, Ferreira C, Cong C (Editors), Nature-based solutions in supporting sustainable development goals. Amsterdam (NL): Elsevier. p. 129-151. DOI: 10.1016/B978-0-443-21782-1.00002-6 DOI: https://doi.org/10.1016/B978-0-443-21782-1.00002-6
Sharma S, Sharma P. 2024. Temporal depth & directionality: Competitive advantage for sustainable family enterprises. Eur J Fam Bus 14(1):5–18. DOI: 10.24310/ejfb.14.1.2024.18462 DOI: https://doi.org/10.24310/ejfb.14.1.2024.18462
Stauffacher M, Flüeler T, Krütli P, Scholz RW. 2008. Analytic and dynamic approach to collaboration: A transdisciplinary case study on sustainable landscape development in a Swiss Prealpine region. Syst Pract Action Res 21(5):409–422. DOI: 10.1007/s11213-008-9107-7 DOI: https://doi.org/10.1007/s11213-008-9107-7
Szymańska EJ, Rysz M, Utnik-Banaś K. 2023. Cooperation of fruit farms with the institutional environment toward sustainable development. Sustainability 15(8):6576. DOI: 10.3390/su15086576 DOI: https://doi.org/10.3390/su15086576
Tanveer U, Hoang TG, Ishaq S, Khalid RU. 2025. Public-private partnerships as catalysts for digital transformation and circular economy: Insights from developing countries. Technol Forecast Soc Change 219:124270. DOI: 10.1016/j.techfore.2025.124270 DOI: https://doi.org/10.1016/j.techfore.2025.124270
Thool V. 2023. Biodiversity loss under the lens of multilateralism: An environmental governance and international law perspective. In: Fontaine-Skronski K, Thool V, Eschborn N (Editors), Does the UN model still work? Challenges and prospects for the future of multilateralism. Leiden (NL): Brill. Available from: https://ssrn.com/abstract=4623490 DOI: https://doi.org/10.1163/9789004516489_013
Wang S, Zhang Z, Wang Z, Liu G. 2022. Exploring the multidimensional factors and emergence mechanisms of industrial symbiotic relationships based on machine learning. J Clean Prod 381:135169. DOI: 10.1016/j.jclepro.2022.135169 DOI: https://doi.org/10.1016/j.jclepro.2022.135169
Wei W, Shen X, Liu Y. 2021. Toward developing a new funding mechanism to support post-2020 biodiversity conservation. Biodivers Sci 29(2):259–268. DOI: 10.17520/biods.2020353 DOI: https://doi.org/10.17520/biods.2020415
Yang S, Zhao W, Liu Y, Cherubini F, Fu B, Pereira P. 2020. Prioritizing sustainable development goals and linking them to ecosystem services: A global expert’s knowledge evaluation. Geogr Sustain 1(4):321–330. DOI: 10.1016/j.geosus.2020.09.004 DOI: https://doi.org/10.1016/j.geosus.2020.09.004
Yao Y, Fu B, Liu Y, Wang Y, Song S. 2021. The contribution of ecosystem restoration to sustainable development goals in Asian drylands: A literature review. Land Degrad Dev 32(16):4472–4483. DOI: 10.1002/ldr.4065 DOI: https://doi.org/10.1002/ldr.4065
Young JC, Marzano M, White RM, McCracken DI, Redpath SM, Carss DN, …, Watt AD. 2010. The emergence of biodiversity conflicts from biodiversity impacts: characteristics and management strategies. Biodivers Conserv 19(14):3973-3990. DOI: 10.1007/s10531-010-9941-7 DOI: https://doi.org/10.1007/s10531-010-9941-7
Copyright (c) 2025 Ari Budi Suryawinata, Mariel Tania Darmayani, Listyani Suhargo

This work is licensed under a Creative Commons Attribution-NonCommercial-NoDerivatives 4.0 International License.
Authors who publish with this journal agree with the following terms:
- Authors retain copyright and grant the journal right of first publication, with the work 1 year after publication simultaneously licensed under a Creative Commons attribution-noncommerical-noderivates 4.0 International License that allows others to share, copy and redistribute the work in any medium or format, but only where the use is for non-commercial purposes and an acknowledgement of the work's authorship and initial publication in this journal is mentioned.
- Authors are able to enter into separate, additional contractual arrangements for the non-exclusive distribution of the journal's published version of the work (e.g., post it to an institutional repository or publish it in a book), with an acknowledgement of its initial publication in this journal.
- Authors are permitted and encouraged to post their work online (e.g., in institutional repositories or on their website) prior to and during the submission process, as it can lead to productive exchanges, as well as earlier and greater citation of published work (See The Effect of Open Access).




