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February 5, 2026Ecology and Evolution2 citationsOpen Access

Diversity and Distribution Patterns of Invasive Alien Plant Species Along Dispersal Corridors in Parsa National Park, Central Nepal

SBShreehari BhattaraiBBBalram BhattaJGJeetendra Gautam

Key Points

  • This research aims to assess the diversity of invasive alien plant species (IAPS) across different dispersal corridors in Parsa National Park.
  • Sampled 156 plots (2 m × 5 m) along road verges, riversides, seasonal springs, fire lines, and trekking trails.
  • Analyzed the relationship between tree canopy openness and IAPS richness using statistical methods like one-way ANOVA.
  • Documented 10 IAPS species with varying distributions across different corridors.
  • Road verges and riversides were the most invaded, hosting 70% of the recorded species.
  • The walking trail had the lowest number of IAPS at 30%.
  • Chromolaena odorata was the most prevalent IAPS, followed by Mikania micrantha and Ageratum conyzoides.
  • Significant differences in IAPS richness across dispersal corridors (p < 0.001).
  • IAPS richness increased significantly with greater tree canopy openness (R = 0.8, p < 0.001).

Abstract

ABSTRACT Protected areas are vital for preserving native biodiversity, yet invasive alien plant species (IAPS) pose significant threats to their conservation. This study investigates how IAPS diversity varies across their dispersal corridors, such as road verges, riversides, seasonal springs, fire lines, and trekking trails, and examines the relationship between tree canopy openness and IAPS richness. We sampled 156 plots (2 m × 5 m) along these corridors in Parsa National Park (PNP), ensuring a minimum distance of 100 m between plots. Out of 10 IAPS recorded during the study, road verges and riversides were invaded by 70% of the recorded species, while the walking trail had the lowest number of IAPS (30%). The most prevalent IAPS was Chromolaena odorata , followed by Mikania micrantha and Ageratum conyzoides . One‐way ANOVA indicated significant differences in IAPS richness among dispersal corridors ( p < 0.001). Furthermore, IAPS richness increased with increasing tree canopy openness ( R = 0.8, p < 0.001). Given that road verges and riversides appeared to be the major dispersal corridors of IAPS in the context of PNP, it is imperative to prioritize these corridors for IAPS monitoring, early detection, eradication, and control. Such efforts can reduce the establishment probability of new IAPS and mitigate the impacts of the widespread IAPS on the native species and ecosystems.

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Cite This Study

Bhattarai et al. (2026) studied this question.

synapsesocial.com/papers/69843371f1d9ada3c1fb0885https://doi.org/10.1002/ece3.73046
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