Abstract

Glaciers are receding at unprecedented rates in the alpine tropics, opening-up new areas for ecosystem assembly. However, little is known about the patterns/mechanisms of primary succession during the last stages of glacier retreat in tropical mountains. Our aim was to analyze soil development and vegetation assembly during primary succession, and the role of changing adaptive strategies and facilitative interactions on these processes at the forefront of the last Venezuelan glacier (Humboldt Peak, 4,940 m asl). We established a chronosequence of four sites where the glacier retreated between 1910 and 2009. We compared soil organic matter (SOM), nutrients and temperatures inside vs. outside biological soil crusts (BSCs) at each site, estimated the cover of lichen, bryophyte and vascular plant species present, and analyzed changes in their growth-form abundance and species/functional turnover. We also evaluated local spatial associations between lichens/bryophytes and the dominant ruderal vascular plant (the grassPoa petrosa). We found a progressive increase in SOM during the first century of succession, while BSCs only had a positive buffering effect on superficial soil temperatures. Early seral stages were dominated by lichens and bryophytes, while vascular plant cover remained low during the first six decades, and was almost exclusively represented by wind dispersed/pollinated grasses. There was a general increase in species richness along the chronosequence, but it declined in late succession for lichens. Lichen and bryophyte communities exhibited a higher species turnover than vascular plants, resulting in the loss of some pioneer specialists as succession progressed. Lichen and bryophyte species were positively associated with safe-sites for the colonization of the dominant ruderal grass, suggesting a possible facilitation effect. Our results indicate that lichens and bryophytes play a key role as pioneers in these high tropical alpine environments. The limited initial colonization of vascular plants and the progressive accumulation of species and growth-forms (i.e., direct succession) could be linked to a combination of severe environmental filtering during early seral stages and limitations for zoochoric seed dispersal and entomophilic/ornithophilic pollination. This could potentially result in a slow successional response of these ecosystems to accelerated glacier loss and climate change.

Highlights

  • The process of plant community structuring during succession can be interpreted as being the result of several interacting filters which determine: (a) the species that can reach a site; (b) the species that can tolerate conditions at the site; and (c) the species that are able to coexist at the site as a result of both positive and negative biotic interactions (Lortie et al, 2004)

  • Some generalizations have been proposed on the changing importance of these processes for vegetation dynamics, including the key role played by effective seed dispersal, local micro-site availability and autogenic habitat amelioration via facilitation during the first stages of primary succession (Walker and Chapin, 1987; del Moral and Wood, 1993; Jones and del Moral, 2009)

  • Based on the previous research on primary succession in temperate and tropical alpine regions, and considering the expected limitations for ecosystem development in glacier forefields of vanishing glaciers, we evaluated the following predictions: (1) the presence of biological soil crusts (BSCs) will be associated with an increase in soil organic matter and nutrients; (2) a progressive accumulation of species, more than species turnover, should characterize the dynamics of vascular plants under these extreme conditions, resulting in a successional increase in the richness of species and growth forms

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Summary

Introduction

The process of plant community structuring during succession can be interpreted as being the result of several interacting filters which determine: (a) the species that can reach a site (biogeographic/dispersal filters); (b) the species that can tolerate conditions at the site (adaptive/functional filters); and (c) the species that are able to coexist at the site as a result of both positive and negative biotic interactions (Lortie et al, 2004). Glacier retreat rates have accelerated in the last five decades (Zemp et al, 2019), while there is increasing evidence that alpine species distributions are shifting upward (Lenoir and Svenning, 2015). This offers a unique opportunity to study climate change impacts in high mountain environments and opens up important questions regarding the development of novel ecosystems and the ability of high elevation specialists to become established and to maintain viable populations in newly exposed areas (Cannone et al, 2008; Zimmer et al, 2018; Cuesta et al, 2019; Anthelme et al, 2021)

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