During the process of urban expansion, the ongoing growth and concentration of populations and industries significantly alter the landscape ecological pattern (Salvati et al,
2018), profoundly impacting urban life, habitation, and production activities (Grimm et al.,
2008). The transformation of agricultural land into developed urban areas results in impervious surfaces such as roads, standalone commercial complexes, and densely populated residential zones, thereby transforming the original natural ecological landscape pattern (Tanner and Fuhlendorf,
2018; Wang et al.,
2019). This alteration in landscape configuration leads to spatial characteristics marked by high overall fragmentation and localized patchiness, which disrupts the integrity of urban ecosystems, affects biodiversity distribution, and influences travel behaviors among urban residents. Concurrently, the outward spread associated with urban expansion heightens both the frequency and intensity of natural disturbances while introducing new disruptions or prolonged pressures that inflict unprecedented damage on the landscape ecological patterns (Feng et al.,
2020), consequently altering nutrient cycling and energy flow within natural systems (Berling-Wolff and Wu,
2004; Lu et al.,
2023). Conversely, changes in landscape patterns can reflect significant transformations in the structure, processes, and functions of urban ecosystems. Such shifts may render heat waves, waterlogging events, and air pollution as potential threats to urban ecology (Gasper et al.,
2011; Gibb et al.,
2020), leading to increased ecological vulnerability while diminishing resilience within cities (Strohschon et al.,
2013; Pickett et al.,
2014). Nevertheless, research on the interplay between urban spatial expansion and changes in landscape ecological patterns has largely overlooked the differentiated impacts and responses induced by the new-type spatial development model. Most pertinent studies have quantified urban expansion within a spatiotemporal framework to ascertain the correlation between urban expansion and alterations in landscape ecological patterns (Jaeger and Schwick,
2014; Li et al.,
2015). The scope of these investigations ranges from individual cities to multiple cities and urban agglomerations. For instance, Darrel and Potere (
2010) conducted a comparative analysis of landscape pattern changes across 120 cities globally, while Ran et al. (
2023) examined landscape patterns and ecosystem health in 212 major Chinese cities. Nearly all findings indicate that metropolitan expansion and urban expansion lead to fragmentation, complexity, and heterogeneity in landscape patterns (Bosch et al.,
2020; Wu et al.,
2011). Methodologically, the impact of urbanization on landscape patterns is typically assessed quantitatively through indices of landscape patterning as well as Morphological Spatial Pattern Analysis (MSPA), with most indicators being integrated into spatiotemporal gradient analyses (Salvati,
2014; Zhang and Wang,
2023). Additionally, some studies incorporate nighttime lighting data to monitor shifts in urban landscapes and simulate economic activities within these areas (Li et al.,
2019). However, there remains a scarcity of comprehensive investigations into the evolution of landscape ecological patterns under varying models of urban expansion; thus, it is imperative to analyze their underlying driving mechanisms.