Your new experience awaits. Try the new design now and help us make it even better

EDITORIAL article

Front. Ecol. Evol.

Sec. Conservation and Restoration Ecology

Volume 13 - 2025 | doi: 10.3389/fevo.2025.1687292

This article is part of the Research TopicEcosystem Condition Assessments: Progress towards a Global StandardView all 7 articles

Ecosystem Condition Assessments: Progress towards a Global Standard

Provisionally accepted
  • 1Department of Sustainable Agriculture, University of Patras, 2 G. Seferi St., 30131, Agrinio, Greece
  • 2Department of Ecology, School of Biology, Aristotle University, 54124, THESSALONIKI, Greece
  • 3Laboratory of Botany, Department of Biology, University of Patras, 26504, Rio, Greece

The final, formatted version of the article will be published soon.

1. Introduction Ecosystem services (ES), as diverse benefits that natural ecosystems provide to human societies, are the bedrock of human well-being and sustainable development (see e.g. Costanza et al., 1998, 2017; Hicks et al., 2015). However, the escalating pressures of global climate change, rapid urbanization, and intensified human activities have led to a discernible deterioration in ecosystem conditions worldwide, raising significant concerns among governments and the scientific community (Valencia Torres et al., 2021; Aryal et al., 2022). Understanding the complex spatiotemporal dynamics of these services (De Valck et al., 2023), identifying their key drivers, and anticipating future changes are therefore critical for developing effective environmental policies and management strategies (Xia et al., 2023). Recent research across diverse regions and ecosystems, from mainland and coastal China to East Africa forests, highlights the urgent need for comprehensive and data-driven assessment approaches, to support science-driven management and policy decisions for our natural capital. 2. Main considerations and management implications The spatial and temporal evolution of ES reveals nuanced trends, often reflecting the interplay between natural processes and human interventions. For instance, a study conducted in Wanjiang River Basin, indicated that vegetation productivity generally improved in the area, based on the Remote Sensing Ecological Index, with ecological restoration efforts contributing to this positive change; however, the variation trend of annual net primary productivity (NPP) showed a slight decrease, maintaining a basically unchanged overall level (Wang et al., 2024). A study for the Nanchang metropolitan area, revealed that various ES, e.g. carbon storage and habitat quality experienced declines, while soil conservation and water yield have an upward general trend, influenced significantly by the regional land use patterns (Zhang et al., 2024). Additionally, a study in the Yunnan-Guizhou Plateau, shows that ES significantly fluctuate, e.g., water yield initially declined but later increased, habitat quality and carbon storage showed a steady decline and soil conservation, continuously improved (Li et al., 2024). These diverse findings underscore the complexity of ecological responses to environmental changes, and the drivers of these changes are multifaceted, stemming from both natural and anthropogenic factors. Abiotic attributes like climate (precipitation, temperature, potential evaporation) and topography (elevation, slope), fundamental determinants of ES (Li et al., 2024; Zhang et al., 2024; Sun et al., 2025), affect differently ES distribution. For instance, precipitation is identified as a primary determinant of water resource generation (Li et al. 2025), the elevation and slope significantly restrict the spatiotemporal distribution of carbon storage (CS), habitat quality (HQ), and soil conservation (SC), while climate characteristics such as temperature, potential evapotranspiration, and precipitation primarily influence CS, HQ, SC , and water yield (see e.g. Sun et al., 2025; Zhang et al., 2024). However, anthropogenic factors, particularly land use changes, population density, and economic development (GDP), emerge as dominant forces shaping ecosystems and their functioning. Urbanization often leads to a reduction in high-value ecological areas such as cultivated land and forestland, replacing them with construction land. This conversion directly impacts ES; for example, increased construction land contributes to the loss of carbon storage and habitat quality (Sun et al., 2025), human-induced pressures like over-exploitation of forest resources, deforestation, increased demand for wood energy, and land use change are cited as major causes for loss in forested areas and decrease in ES (Osewe et al., 2024). Ιn urban centers, a significant negative correlation between NPP and population density is documented, illustrating the direct impact of human concentration on vegetation productivity; in rapidly urbanizing areas, rising population levels accelerate urbanization, leading to extensive conversion of arable land for construction purposes, which reduces vegetation cover and subsequently, carbon storage and habitat quality (Zhang et al., 2024). On the other hand, in areas with agricultural activities, a positive correlation between NPP and population density suggests that human activities, when managed sustainably, can contribute positively to ES (Wang et al., 2024). Understanding the complex interactions, trade-offs, and synergies among different ES is crucial for effective management. Research consistently shows a persistent negative correlation (trade-off) between WY and HQ or CS, often due to water regulation and the expansion of water bodies disturbing natural ecological environments. On the other hand, strong synergistic relationships are frequently documented between HQ, CS, and SC, with good HQ typically leading to higher biodiversity and enhanced CS (Li et al., 2025; Sun et al., 2025). The example from the Henan Province demonstrates that even if some trade-offs exist, the relation among five assessed ES (CS, HQ, SC, WC, WY) are predominantly synergistic, with trade-offs tending to transform into synergistic effects over time (Sun et al., 2025). Additionally, advanced modelling, remote sensing technologies, and earth observation data and products are revolutionizing ES assessments, prediction for future scenarios and natural capital accounting (Kokkoris et al. 2024). Models like ARIES (Villa et al., 2014), InVEST (Sharp et al., 2018), and PLUS (Liang et al., 2021), combined with machine learning algorithms, provide powerful tools for quantifying ES, simulating complex, future land use changes, and identifying the spatial heterogeneity of driving factors at a fine (operational) spatial scale, enabling more accurate forecasting (Zhang et al., 2024; Sun et al. 2025). Additionally, the integration of machine learning techniques enhances predictive accuracy, particularly for identifying nonlinear relationships and complex interactions within ecological data (see e.g. Zhang et al. 2024). Multi-scenario modelling offers vital insights for managers and policymakers into how land-use changes will affect ES under different socio-economic development pathways. Scenarios that are typically simulated are projections for business-as-usual, specific management (goal)-oriented, smart scenarios, eco-friendly (see e.g. Kokkoris et al. 2019). Results consistently show that scenarios prioritizing environmental protection lead to the most favourable outcomes for fostering synergies and enhancing overall ES performance (Li et al., 2025). For example, in the Yunnan-Guizhou Plateau, the ecological priority scenario demonstrated the best performance across all ES (Li et al., 2025). Similarly, in Henan Province, the ecological protection scenario effectively safeguards forest land and grassland, mitigating the degradation of CS, HQ, and WC (Sun et al., 2025). 3. Conclusion The collective findings emphasize the critical need for an integrated and adaptive approach to ecosystem management. Effective policy interventions, guided by data-driven assessments and multi-scenario predictions, are essential for mitigating ecological degradation and promoting sustainable development. This involves: (a) Strategic land use planning, to minimise the conversion of ecological land for urban expansion and agriculture in vulnerable areas; (b) Targeted conservation and restoration efforts, prioritizing forest conservation, reforestation, wetland protection, and biodiversity safeguarding in high-value ecological zones; (c) Balancing human activities with environmental protection, by managing population growth and urban sprawl to reduce ecological pressure, while incentivizing sustainable practices in agriculture and other sectors; (d) Refined assessment tools, i.e., continuing to develop and integrate advanced models and remote sensing technologies for more precise and localized understanding of ES dynamics and their drivers. While significant progress has been made, research gaps remain, particularly in refining model parameters to reflect local ecological realities, comprehensively analysing multifactor interactions, and incorporating higher-resolution data for more precise spatial analyses. Addressing these limitations will further enhance our capacity to manage complex ecological challenges and secure a sustainable future. The integration of EO data and products is also crucial to standardise methods and processes towards a global standard (Kokkoris et al. 2024), such as the System of Environmental-Economic Accounting—Ecosystem Accounting (SEEA EA) (United Nations et al. 2021). The path forward demands continuous innovation in research and a steadfast commitment from policymakers to translate scientific insights into actionable strategies for ecological protection and human well-being.

Keywords: Biodiversity, land use change, ecosystem management, ecosystem services, natural capital

Received: 17 Aug 2025; Accepted: 22 Aug 2025.

Copyright: © 2025 Kokkoris, Kallimanis and Dimopoulos. 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) or licensor 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: Ioannis P. Kokkoris, Department of Sustainable Agriculture, University of Patras, 2 G. Seferi St., 30131, Agrinio, Greece

Disclaimer: 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.