Group size mediates effects of intraspecific competition and forest structure on productivity in a recovering social woodpecker population

Abstract

Conservation of endangered social wildlife in disturbance‐prone forests is challenging because direct and indirect effects of management strategies developed at the time of species’ listing when population density is low may change under high‐density conditions in locally recovered populations. Here, we used piecewise structural equation modeling to evaluate direct and indirect drivers of productivity in the federally endangered cooperatively breeding red‐cockaded woodpecker Dryobates borealis (RCW) on Savannah River Site, South Carolina, USA. We estimated direct and indirect relationships among group size, neighboring group sizes, fledgling production, density of cavity tree clusters occupied by RCWs, area satisfying threshold criteria of ≥22 stems ha−1 of pines ≥35.6 cm diameter at breast height (dbh), <1.4 m2 ha−1 basal area (BA) of hardwoods 7.6–22.9 cm dbh, and <6% hardwood canopy cover, and area treated with prescribed fire, and tested whether group size mediated indirect effects of area satisfying threshold criteria on fledgling production. Increases in area with ≥22 stems ha−1 of pines ≥35.6 cm dbh and <1.4 m2 ha−1 BA of hardwoods 7.6–22.9 cm dbh, and area treated with prescribed fire, but not area with <6% hardwood canopy cover, had direct positive effects on group size. Group size and area treated with prescribed fire, but not area satisfying threshold criteria, had direct positive effects on fledgling production. The direct effect of neighboring group sizes on fledgling production was negative and smaller relative to the direct positive effect of group size on fledgling production. Overall, our results indicate positive direct effects of group size on fledgling production outweighed negative direct effects of neighboring group sizes, and that group size mediated positive indirect effects of area satisfying structural threshold criteria on fledgling production. These findings indicate that ongoing forest management aimed to increase area with ≥22 pines ha−1 ≥35.6 cm dbh and <1.4 m2 ha−1 BA of hardwoods 7.6–22.9 cm dbh will promote large group sizes, which in turn improve fledgling production and offset costs of heightened competition with neighboring groups under high‐density conditions. Additionally, positive effects of area treated with prescribed fire on RCW group size and fledgling production indicate prescribed fire has unique contributions to woodpecker productivity, likely via direct effects on forest structure and potentially indirect effects on arthropod prey available to foraging RCWs. By simultaneously accounting for multiple drivers of productivity in social wildlife, our study contributes to the understanding of how increases in social wildlife population sizes can alter previously documented habitat‐fitness relationships.

Integrating forest structural diversity measurement into ecological research

“…FSD measurement has profound implications beyond research, extending into social, political, and economic spheres. Standardized FSD measurement could strengthen environmental policies and be used to assess progress toward achieving biodiversity, climate, and natural resource management goals (Jetz et al, 2019) and forest structure-wildlife fitness relationships to guide endangered species recovery (Garabedian et al, 2021). Increasing the availability, consistency, and utility of FSD measurements for compliance with forest carbon offset programs (e.g., California's forest carbon offset program) can further bolster the effectiveness of policy implementation and help scientifically informed, data-driven policy reforms.…”