Global Hotspots and Trends of Ecological Network Research (1991–2024): Insights from Bibliometric Analysis
Abstract
1. Introduction
2. Mini-Review of EN Research
3. Data and Methods
3.1. Data Collection
3.2. Methods
4. Results
4.1. Analysis of Publication Output
- Incubation stage (1991–2009). This period was characterized by limited output, with 122 articles published. Contributions involved 350 authors from 176 institutions across 18 WOSCC subject categories. This stage reflects an emerging field focused on establishing foundational concepts and methodologies.
- Development stage (2010–2021). This period witnessed a significant increase in activity, with 943 articles published—approximately 7.7 times the output of the incubation stage. The number of contributing authors grew to 3332, affiliated with 1299 institutions, and disciplinary coverage expanded to 34 subject categories. This surge indicates rapid growth, diversification, and increasing interdisciplinary engagement.
- Rapid development stage (2022–2024). By September 2024, 741 publications had been recorded in this period, involving 3074 authors and 1120 institutions. The number of subject categories stabilized at 34. The accelerated growth during this period can be attributed to (i) heightened global emphasis on ecological security and sustainable development, particularly within the framework of the United Nations Sustainable Development Goals, driving academic interest in EN and ESP applications, and (ii) expanded coverage and publication efficiency in the WOSCC, including the rise in open-access journals, which increased the visibility and volume of EN-related literature [52].
4.2. Analysis of Research Hotspots
- Ecological protection and biodiversity conservation. Anchored by “conservation” (376 occurrences, betweenness centrality 0.26) and “biodiversity” (266, 0.17), this hotspot emerged around 2002 and remains central to EN research. Studies focus on EN’s role in supporting species migration corridors [59] and mitigating habitat fragmentation [25]. Its persistence underscores the ongoing challenge of sustaining biodiversity amid increasing landscape pressures.
- Ecosystem service assessment and spatial optimization. Defined by “ecosystem service” (notable frequency post-2013) and “land use”, this hotspot examines the impacts of land use change on regulating and provisioning services [5,8]. Research emphasizes spatial optimization to enhance service delivery but faces challenges in standardizing valuation methods and balancing trade-offs in human-modified landscapes.
- Multi-scale landscape structure evolution. Focused on “landscape” and “pattern”, this hotspot investigates the interplay between multi-scale landscape configurations and ecological processes [61]. It provides a topological framework for optimizing ESPs, linking spatial patterns to ecological functionality.
4.3. Analysis of Research Themes
- Cluster #0: Ecological Network Analysis (2012–2024, 27 keywords). This theme focuses on landscape-scale spatial structures and ecological processes, utilizing graph theory and circuit theory to model node–corridor topologies and least-cost paths. It examines how landscape configurations influence species dispersal, gene flow, and ecological functions. Recent advancements include the MCR model and ecological node optimization strategies. For example, Yu et al. [65] refined the MCR model using energy flow principles to optimize ecological node layouts in Dengkou County, Inner Mongolia, increasing network connectivity robustness from 0.73 to 1.00. Similarly, Zhao et al. [66] applied the DPSIR (Drivers–Pressures–State–Impacts–Response) framework to evaluate ecological network resilience across 35 Chinese cities, revealing higher resilience in coastal cities compared to inland regions.
- Cluster #1: Ecological Network (2002–2022, 18 keywords). This cluster emphasizes the conceptual development, construction, and evaluation of EN, prioritizing biodiversity conservation and ecosystem service provision. It addresses challenges such as habitat fragmentation and ecological source identification. EN frameworks support regional conservation planning. For instance, Saura et al. [67,68] introduced the Probability of Connectivity (PC) index to quantify habitat connectivity in landscape planning. Kong et al. [24] optimized the greenspace network in Jinan City, China, using least-cost paths and gravity models. However, subjectivity in ecological source identification remains a challenge. Peng et al. [8] addressed this by integrating ecosystem service assessments to identify ecological sources in Yunnan Province.
- Cluster #2: Graph Theory (2007–2022, 16 keywords). This cluster employs graph theory to analyze landscape and functional connectivity, identifying critical nodes and corridors essential for an EN. Graph-based approaches represent the EN as nodes and edges, and enhance the understanding of EN dynamics. Saura et al. [60] advanced stepping-stone theory, demonstrating the critical role of small and medium-sized habitat patches in facilitating long-distance dispersal. Rayfield et al. [69] developed a network metric classification framework, distinguishing path-specific flux and path redundancy. However, graph theory’s oversight of nonlinear ecological processes and computational complexity may limit its adoption in management practices. Ayram et al. [70] advocated for the development of user-friendly software, for example, Guidos Toolbox (current version: 3.3, available at https://forest.jrc.ec.europa.eu/, accessed on 15 May 2025).
- Cluster #3: Landscape Pattern (2012–2024, 16 keywords). This theme investigates the formation, evolution, and ecological impacts of landscape patterns. Landscape pattern research quantifies spatial heterogeneity to reveal ecological process drivers. Cui et al. [40] applied the MSPA and least-cost distance methods to construct a greenspace ecological network in Tongzhou District, Beijing, reducing landscape fragmentation through optimized corridors. Kang et al. [71] identified better ESPs in the Jiaodong Peninsula using multi-scenario simulations. Shi et al. [72] employed structural equation modeling to analyze landscape heterogeneity in the Yellow River Basin’s agro-pastoral zone, identifying grazing and agriculture as primary drivers of spatial patterns.
- Cluster #4: Green Infrastructure (2006–2023, 15 keywords). Green infrastructure integrates natural and anthropogenic systems to enhance ecological services and human well-being. This cluster focuses on designing and managing green infrastructure to mitigate environmental stressors, such as climate change and urbanization. For example, Cunha et al. [30] constructed Portugal’s national EN through multi-level ecological assessments, covering 67% of the country’s area, but only 25% was protected, revealing significant conservation gaps. Wu et al. [73] developed a source–sink-theory-based green infrastructure framework for Wu’an County, a resource-based city, highlighting ecological corridors’ role in enhancing resilience.
- Cluster #5: Forest Management (2003–2024, 15 keywords). This theme targets sustainable forest ecosystem management, leveraging ESP and circuit theory to optimize spatial patterns. It navigates trade-offs between conservation and resource utilization. For example, Saura et al. [59] assessed European forest connectivity from 1990 to 2000 using the Equivalent Connected Area index. Emer et al. [74] studied seed dispersal networks in the Atlantic Forest, underscoring the critical role of small birds and plants in fragmented landscapes. Fu et al. [5] optimized ecological sources on the Loess Plateau via hotspot analysis, proposing a “two-axis, four-core, six-belt, eight-zone” framework that enhanced internal connectivity.
- Cluster #6: Circuit Theory (2003–2024, 14 keywords). Circuit theory simulates ecological flows by quantifying landscape resistance and currents. This cluster applies circuit theory to model EN structure and resilience against disturbances. For example, Wang et al. [75] validated the resilience of EN for Nanchang City through scenario simulations. An et al. [28] optimized an EN for tropical southwest China by incorporating stepping stones. Dai et al. [76] constructed an EN for the Poyang Lake urban agglomeration to mitigate industrial impacts.
- Cluster #7: Minimum Cumulative Resistance (2017–2024, 14 keywords). The MCR model identifies corridors and nodes by quantifying ecological resistance. This theme centers on the MCR model, usually integrated with MSPA, to assess ecosystem integrity in EN planning. For example, Nie et al. [77] constructed an EN in Anji County using MCR and network analysis. Xu et al. [78] optimized EN in the Pingshuo open-pit mining area using landscape ecological risk assessments and MCR.
- Cluster #8: PLUS Model (2000–2024, 12 keywords). The low S value of this cluster reflects thematic heterogeneity due to its interdisciplinary scope. The PLUS (Patch-generating Land Use Simulation) model optimizes land use planning by coupling EN and multi-scenario simulations. For example, Peng et al. [8] combined circuit theory and the PLUS model to identify ecological corridors in Yunnan Province. Lin et al. [79] integrated landscape ecological risk assessments with the PLUS model in Guiyang City to predict 2030 risk changes, validating the ecological priority scenario’s superior protection efficacy. Nie et al. [80] simulated 2034 land use scenarios in Anji County using the ESP-MS-PLUS model.
- Cluster #9: Ecological Corridors (2012–2023, 12 keywords). Ecological corridors facilitate species movement and ecosystem connectivity. This theme prioritized the planning, construction and preservation of ecological corridors to support biodiversity and ecological flows. For instance, Li et al. [81] optimized an ESP in a northern mining area using a multi-process MCR model, constructing a “three-horizontal, two-vertical, two-ring” corridor pattern. Wang et al. [82] identified ecological corridors and nodes to enhance landscape connectivity. Wei et al. [83] extracted ecological corridors in the Ebinur Lake Basin to construct a “four-zone, two-belt” ecological pattern.
- Cluster #10 Urban Ecology (2014–2023, 12 keywords). Urban ecology addresses ecological challenges from urbanization through network design. This cluster explores multi-scale ENs in urban environments. For example, Shi et al. [84] proposed a landscape-based resource assessment method in Shenzhen City, prioritizing ecological core areas. Ran et al. [85] integrated ecosystem service supply–demand perspectives to identify ecological demand corridors in central Yunnan’s urban agglomeration. Chen et al. [86] identified ecological sources and corridors in Tianjin City to propose targeted restoration strategies.
- Cluster #11: Ecological Security Pattern (2006–2022, nine keywords). This theme focuses on the construction, assessment, and conservation of ESP. It emphasizes biodiversity conservation, ecosystem service maintenance, and ecological restoration, with key concepts including nestedness, landscape connectivity, and biodiversity maintenance. For example, Peng et al. [36] employed ant colony algorithms and kernel density estimation to identify ecological sources and corridors in Beijing. Wang et al. [61] reconstructed Gansu Prefecture’s ESP to develop a continuous ecological barrier system. Fu et al. [5] constructed an ESP in the Loess Plateau to optimize the ecological source area.
4.4. Analysis of Research Directions
- EN theoretical research
- 2.
- EN construction methodology
- 3.
- EN and ecosystem services
4.5. Analysis of Research Frontier Evolution
- Stage I: Theoretical foundation (1991–2009). This initial stage established the conceptual foundations of EN research, characterized by keywords such as conservation (burst strength: 34.69; burst duration: 2002–2015), habitat fragmentation (23.29, 2007–2018), and ecological network (17.40, 2003–2012). The research focused on elucidating the mechanisms underpinning EN design and their effectiveness in mitigating habitat fragmentation while supporting ecosystem services. Theoretical frameworks, including island biogeography and landscape connectivity, provided the intellectual scaffolding for understanding spatial configurations and ecological processes during this period.
- Stage II: Technological transition (2010–2021). The second stage marked a shift toward quantitative and analytical rigor, with prominent keywords including biodiversity (20.38; 2011–2019), graph theory (18.74; 2011–2018), and climate change (15.63; 2010–2016). Research transitioned from descriptive to predictive approaches, leveraging graph theory to quantify the structural properties of ENs, such as node connectivity and network robustness. The integration of climate change as a research focus prompted the development of dynamic models to capture ecological processes under changing environmental conditions. This period represented a methodological advancement, enhancing the precision and predictive power of EN studies through computational and statistical tools.
- Stage III: Technological integration (2022–2024). The current phase reflects an interdisciplinary synthesis, driven by keywords such as circuit theory (20.19; 2023–2024), ecological security pattern (10.60; 2022–2024), and construction (6.86; 2023–2024). The research emphasizes the design, restoration, and risk assessment of corridor systems to enhance ecological security. Circuit theory, combined with remote sensing, geographic information systems, and machine learning, enables the development of multi-scale simulations of ecological flows and the precise identification of connective corridors. This stage integrates a pattern–process–service–risk framework, fostering data-driven, intelligent decision-making for resilient landscape planning and management.
5. Conclusions and Outlook
5.1. Conclusions
5.2. Outlook
- Advancing ecosystem service quantification and integration. Ecosystem services are fundamental to the functionality of ENs, yet their quantitative assessment remains underexplored in many EN frameworks. Future research should prioritize the development and application of standardized, spatially explicit models to evaluate the contributions of ENs to provisioning (e.g., food and water supply), regulating (e.g., flood control and carbon sequestration), supporting (e.g., nutrient cycling and habitat provision), and cultural (e.g., recreational and aesthetic value) services. By integrating tools such as InVEST (Integrated Valuation of Ecosystem Services and Tradeoffs) and circuit-theory-based resistance models, researchers can map ecosystem service flows across ENs. Such efforts will provide a rigorous scientific foundation for prioritizing ecological protection and restoration initiatives, ensuring alignment with regional conservation goals and global frameworks such as the UN Sustainable Development Goals.
- Enhancing climate change adaptation and resilience. Climate change poses significant threats to EN integrity through increased frequency of extreme weather events, shifting species distributions, and altered ecological processes. Future research must deepen the understanding of ENs’ adaptive capacity by modeling their responses to climate-induced stressors, such as drought, flooding, and habitat fragmentation. This involves integrating dynamic climate models with EN simulations to predict changes in connectivity and ecosystem functionality under various climate scenarios (e.g., RCP 4.5 and 8.5). For example, circuit-theory- and graph-based approaches can be used to identify climate-resilient corridors that facilitate species migration and gene flow in fragmented landscapes. Additionally, research should explore nature-based solutions, such as green infrastructure enhancements, to bolster EN resilience against climate impacts. These insights will inform adaptive management strategies, enabling policymakers to design ENs that maintain ecological stability, and support biodiversity conservation amidst climatic uncertainties.
- Strengthening socioeconomic integration for sustainable development. The interplay between ENs and socioeconomic systems is critical for achieving sustainable development, particularly in rapidly urbanizing regions. Future research should focus on elucidating how ENs can optimize ecological spatial configurations to balance conservation objectives with socioeconomic demands, such as agricultural productivity and urban expansion. Special attention should be given to stakeholder engagement and participatory planning to ensure that EN designs reflect local socioeconomic priorities. These efforts will enhance the applicability of ENs in supporting regional sustainable development and fostering resilient human–nature interactions.
- Leveraging interdisciplinary collaboration and technological innovation. The complexity of EN research necessitates interdisciplinary collaboration and the adoption of cutting-edge technologies to advance dynamic monitoring, simulation, and optimization. Future studies should harness emerging tools, such as big data analytics, artificial intelligence, and unmanned aerial vehicles, to enhance the precision of EN research. Furthermore, fostering collaboration across disciplines will drive the development of user-friendly software platforms, for example, Guidos Toolbox or Conefor Sensinode (current version: 2.6, available at http://conefor.org/gisextensions.html, accessed on 15 May 2025) that bridge the gap between research and management. These advancements will facilitate data-driven, intelligent decision-making, enabling the design of adaptive and resilient ENs.
5.3. Limitations
- Selection of data source. The study exclusively utilized the WOSCC as its data source. To investigate the implications of database selection, we compared publication outputs between the WOSCC and Scopus (Figure 5). The analysis revealed notable differences in publication volume, largely due to Scopus’s broader indexing of scholarly content compared to the WOSCC’s more selective inclusion of high-impact, rigorously peer-reviewed publications. Some researchers argue that larger publication volumes do not necessarily enhance the robustness of bibliometric analyses [88], while others advocate for integrating multiple databases to achieve a more comprehensive assessment [15]. Although both databases offer important scientific merits, further systematic comparisons are required to determine their optimal use—either individually or in combination—for specific research objectives.
- Reliance on a single data source. The study exclusively utilized the WOSCC as its data source. While the WOSCC is an authoritative database for bibliometric analyses due to its rigorous indexing standards, there are still limitations in its nature. First, the WOSCC exhibits regional bias to some extent, with publications from regions such as Africa and Asia being underrepresented [89]. This may skew the global geographical distribution of EN research, potentially marginalizing contributions from non-English-speaking countries. Second, the WOSCC’s focus on English-language publications excludes substantial non-English literature available in databases such as Scopus, Google Scholar, or the China National Knowledge Infrastructure (CNKI) [90]. The non-English literature also provides unique insights into localized ecological issues and application-oriented research.
- Challenges in keyword semantics and retrieval consistency. The quantitative nature of bibliometric analysis is sensitive to semantic variations in keywords. The same terms may carry different meanings across disciplines, languages, or regional contexts, leading to incomplete or inconsistent retrieval results. Such semantic heterogeneity can obscure the accurate identification of research hotspots, especially in interdisciplinary or cross-cultural studies. To address this, future studies could adopt advanced retrieval strategies, such as synonym expansion, and natural language processing (NLP) techniques.
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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No. | Subject Category | Journal | Country | Institution |
---|---|---|---|---|
1 | Environmental Sciences (772) | Ecological Indicators (190) | China (902) | Chinese Academy of Sciences (154) |
2 | Ecology (692) | Sustainability (126) | USA (244) | Beijing Normal University (144) |
3 | Biodiversity Conservation (395) | Landscape Ecology (91) | UK (148) | Peking University (39) |
4 | Environmental Studies (318) | Journal of Cleaner Production (69) | Italy (110) | Beijing Forestry University (34) |
5 | Green Sustainable Science Technology (169) | Ecological Modelling (56) | Germany (98) | China University of Geosciences (25) |
6 | Physical Geography (154) | Science of the Total Environment (51) | Canada (92) | Wuhan University (25) |
7 | Multidisciplinary Geosciences (121) | Landscape and Urban Planning (48) | France (91) | Swedish University of Agricultural Sciences (24) |
8 | Environmental Engineering (111) | Biological Conservation (43) | Spain (77) | University of Regina (24) |
9 | Urban Studies (102) | Journal of Environmental Management (39) | Netherlands (69) | Towson University (24) |
10 | Geography (86) | Remote Sensing (37) | Australia (58) | Universidade de São Paulo (23) |
No. | Author | Publication Volume | Publication Date | Country | Current Institution |
---|---|---|---|---|---|
1 | Michael J. Samways | 19 | 2010–2023 | South Africa | Stellenbosch University |
2 | Qiang Yu | 18 | 2017–2024 | China | Beijing Forestry University |
3 | Santiago Saura | 15 | 2007–2019 | Spain | Universidad Politécnica de Madrid |
4 | James S. Pryke | 15 | 2010–2023 | South Africa | Stellenbosch University |
5 | Céline Clauzel | 13 | 2012–2024 | France | Université Paris 1 Panthéon-Sorbonne |
6 | Jian Peng | 12 | 2017–2024 | China | Peking University |
7 | Jiansheng Wu | 11 | 2015–2022 | China | Peking University |
8 | Kevin Watts | 11 | 2009–2018 | UK | Forest Research of the Forestry Commission |
9 | Jianquan Dong | 9 | 2019–2024 | China | Peking University |
10 | Marie-Josée Fortin | 9 | 2011–2021 | Canada | University of Toronto |
Cluster ID | Cluster size | Silhouette | From | To | Duration | Avg. Year | Activeness | Research Theme |
---|---|---|---|---|---|---|---|---|
0 | 27 | 0.912 | 2012 | 2024 | 13 | 2019 | Active | Ecological Network Analysis |
1 | 18 | 0.949 | 2002 | 2022 | 21 | 2013 | Active | Ecological Network |
2 | 16 | 0.900 | 2007 | 2022 | 16 | 2016 | Active | Graph Theory |
3 | 16 | 0.942 | 2012 | 2024 | 13 | 2020 | Active | Landscape Pattern |
4 | 15 | 1.000 | 2006 | 2023 | 18 | 2018 | Active | Green Infrastructure |
5 | 15 | 0.851 | 2003 | 2024 | 22 | 2017 | Active | Forest Management |
6 | 14 | 0.965 | 2003 | 2024 | 22 | 2013 | Active | Circuit Theory |
7 | 14 | 0.919 | 2017 | 2024 | 8 | 2021 | Active | Minimum Cumulative Resistance |
8 | 12 | 0.270 | 2000 | 2024 | 25 | 2015 | Active | PLUS Model |
9 | 12 | 0.982 | 2012 | 2023 | 12 | 2019 | Active | Ecological Corridors |
10 | 12 | 0.879 | 2014 | 2023 | 10 | 2020 | Active | Urban Ecology |
11 | 9 | 0.974 | 2006 | 2022 | 17 | 2015 | Active | Ecological Security Pattern |
Keywords | Year | Strength | Begin | End |
---|---|---|---|---|
conservation | 2002 | 34.69 | 2002 | 2015 |
ecological network | 2003 | 17.40 | 2003 | 2012 |
dispersal | 2003 | 15.05 | 2003 | 2017 |
population | 2003 | 9.19 | 2003 | 2016 |
habitat fragmentation | 2007 | 23.29 | 2007 | 2018 |
landscape connectivity | 2007 | 14.50 | 2007 | 2017 |
corridor | 2007 | 7.44 | 2007 | 2013 |
climate change | 2010 | 15.63 | 2010 | 2016 |
biodiversity | 2006 | 20.38 | 2011 | 2019 |
graph theory | 2011 | 18.74 | 2011 | 2018 |
diversity | 2006 | 9.87 | 2011 | 2016 |
ecosystem | 2012 | 10.47 | 2012 | 2019 |
biodiversity conservation | 2012 | 8.10 | 2012 | 2019 |
network analysis | 2012 | 6.90 | 2012 | 2018 |
functional connectivity | 2014 | 7.10 | 2014 | 2016 |
forest | 2016 | 9.03 | 2016 | 2020 |
ecological security pattern | 2019 | 10.60 | 2022 | 2024 |
circuit theory | 2020 | 20.19 | 2023 | 2024 |
construction | 2021 | 6.86 | 2023 | 2024 |
risk | 2021 | 5.58 | 2023 | 2024 |
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Wang, J.; Tang, H.; Guo, W.; Yu, W.; Luo, Y. Global Hotspots and Trends of Ecological Network Research (1991–2024): Insights from Bibliometric Analysis. Sustainability 2025, 17, 4716. https://doi.org/10.3390/su17104716
Wang J, Tang H, Guo W, Yu W, Luo Y. Global Hotspots and Trends of Ecological Network Research (1991–2024): Insights from Bibliometric Analysis. Sustainability. 2025; 17(10):4716. https://doi.org/10.3390/su17104716
Chicago/Turabian StyleWang, Jingxian, Hui Tang, Wei Guo, Wendong Yu, and Yunjian Luo. 2025. "Global Hotspots and Trends of Ecological Network Research (1991–2024): Insights from Bibliometric Analysis" Sustainability 17, no. 10: 4716. https://doi.org/10.3390/su17104716
APA StyleWang, J., Tang, H., Guo, W., Yu, W., & Luo, Y. (2025). Global Hotspots and Trends of Ecological Network Research (1991–2024): Insights from Bibliometric Analysis. Sustainability, 17(10), 4716. https://doi.org/10.3390/su17104716