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• Source-Resistance-Corridor Basic Framework for Identifying Restoration Areas. • Quantifying wetland ecosystem services to extract wetland ecological sources. • Provides solutions for identifying large-scale wetland restoration areas. • Focus on the relevance of wetlands and water systems. In recent years, wetland resources have been threatened by human activities such as mining, agriculture and construction land expansion, and problems such as shrinkage of wetland area and deterioration of water quality have emerged, impeding the exchange of materials between wetlands and reducing the ecological function of wetlands. Water systems are important channels for material exchange between wetland sources, and evaluating the ecological safety of wetland–water system ecological corridors can aid in efficiently delineating ecological restoration areas and identifying ecological problems. In this paper, the ecological safety of wetland–hydrological ecological corridors in the Han River Basin was evaluated, and ecological restoration areas were delineated by adopting the method of "identification of source areas - construction of resistance surfaces - extraction of wetland–hydrological ecological corridors" with the watershed as the research unit. The study identified wetland–hydrological ecological corridors with a total length of 7,589.77 km and delineated 31 sections of wetland–hydrological ecological corridors with a total length of 1,076 km; these corridors were located in the Hanzhong Canyon area, tributaries of the Danjiang River and Tangbai River, and tributaries of the main streams below Danjiangkou. Among them, 8 sections of the primary corridor account for 27 %, 14 sections of the secondary corridor account for 33 %, and 9 sections of the tertiary corridor account for 39 %. This study breaks administrative boundaries, emphasizes the correlation between wetlands and water bodies, highlights the integrity of ecosystems, and establishes a multidimensional systematic restoration methodology of "points, lines and surfaces", which provides guidelines for the long-term planning of ecological corridors of wetlands and water systems in large-scale regions. [ABSTRACT FROM AUTHOR]

• A watershed ESPs construction method integrating MCR model and circuit theory from the perspectives of ecosystem services and ecological sensitivity was proposed. • The ecological sensitivity weights of different regions were applied for constructing the ESPs of the YRB. • The distributions of ECs and EPPs presented spatial differences in the ecological environment of the YRB. • The proposal of optimizing ESPs can promote the ecological protection and high-quality development of the basin. Safeguarding ecological security is one of China's important development strategies. Identifying ecological security patterns (ESPs) is an effective way to collaboratively develop ecological and environmental security in different regions. Currently, studies on the construction of regional ESPs mainly focus on the innovation of ecosystem service functions, ignoring the differences in ecological sensitivities of different ecological environments on a large scale. In this paper, taking the Yellow River Basin (YRB) as an example, six important ecosystem service functions were selected to identify ecological sources (ESs), ecological sensitivity weights were set according to the ecological environment characteristics of different regions, and the ecological resistance surfaces (ERSs) were determined. And the ESPs of the YRB were further investigated based on the Minimum Cumulative Resistance (MCR) model and circuit theory. The research findings indicate:(1) We had identified 218 ESs on the YRB, covering an area of 387,165 km2, which was 19.36 % of the entire study area and highly concentrated in the upstream areas. There were 532 ecological corridors (ECs) identified with a total length of 39,015.95 km, with less distribution in the lower reaches of the YRB. There were 201 ecological pinch points (EPPs) mainly in forests and grasslands. (2) ERSs constructed with different sensitivities weights had a significant impact on the distribution of ECs and EPPs. There were significant variations in the ESPs of the YRB. The upstream areas were notably more secure than the middle and lower reaches, indicating an overall lower level of ecological security. (3) Different ecological sensitivity weights were adopted in different regions, which was more suitable for the construction of ESPs with regional environmental differences. This study provides a wise direction for coordinating the ecological protection and achieving high-quality development in the YRB. [ABSTRACT FROM AUTHOR]