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Varying impacts of logging frequency on tree communities and carbon storage across evergreen and deciduous tropical forests in the Andaman Islands, India

Citation

Surendra, Akshay; Osuri, Anand; Ratnam, Jayashree (2021), Varying impacts of logging frequency on tree communities and carbon storage across evergreen and deciduous tropical forests in the Andaman Islands, India, Dryad, Dataset, https://doi.org/10.5061/dryad.1c59zw3rp

Abstract

The majority of Earth’s tropical forests have been selectively logged; some on repeated occasions. Selective logging is known to affect forest structure, composition and function in various ways, but how such effects vary with logging frequency and across forest types remains unclear. In the Andaman Archipelago in India, we examined adult and pole-sized trees in baseline (unlogged since 1990s), once-logged (logged between 2007 and 2014) and twice-logged (logged in early 1990s and between 2007 and 2014) evergreen and deciduous forests, and tested whether higher logging frequency was associated with lower canopy cover, tree density, tree diversity, aboveground carbon stocks and divergence in species composition, including increased relative abundances of deciduous species in these forests. While once-logged evergreen and deciduous forests were similar to their respective baselines for most attributes assessed, and twice-logged evergreen forests had 22–24% lower adult tree density and diversity, twice-logged deciduous forests had 17–50% lower canopy cover, pole density, adult species diversity and above-ground carbon stocks, and 12% higher deciduous fractions compared to the baselines. Collectively our results reveal lasting impacts of repeated selective logging, even at relative low intensity, on tree communities and carbon storage. These impacts can potentially be mitigated by reducing logging frequency and retaining unlogged patches in logged landscapes, but management must also incorporate heterogeneity in responses and recovery across different forest types. In the Andaman Islands, all forests may require more than 15–25 years between logging events, with deciduous forests potentially requiring more stringent extraction limits compared to evergreen forests.

Methods

See Methods section in the manuscript.

Plot type B corresponds to the innermost 10x10m plot, plot type A corresponds to the outer 50 x 10m plot and plot type C (not used in this manuscript) corresponds to large trees (>180cm DBH) and logging stumps enumerated in a 70x70m (0.49ha) plot circumambulating the two inner plots.

Usage Notes

All details are available in the ReadMe file (attached)

Funding

Sir Dorabji Tata Trust

Department of Atomic Energy, Government of India

Sir Dorabji Tata Trust