Initial interest caught by the paper: The forgotten forests: Incorporating temperate peat-forming wet woodlands as nature-based solutions into policy and practice
“…there have been no rigorous wet woodland biodiversity studies across the range of taxonomic groups and wet woodland types in the UK. Thus, there are key knowledge gaps on the unique assemblages of wet woodlands, the environmental tolerances of wet woodland species, the role of microhabitats and microclimate on biodiversity now and under climate change, the importance of connectivity, and how the (eco)hydrological conditions at macro- and micro-scale influence biodiversity, above-ground productivity and carbon sequestration.”
Previous structural diversity measures have been found to miss important features of the wet woodland ecosystem such as canopy openings from tree fall.
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This was before the current focus and targets on carbon sequestration were developed (Milner et al, 2024)
Structural diversity mapping can help influence:
“How does the species’ composition of wet woodland compare to that of associated dry forest and non-forested wetland?”
“How will species assemblages of wet woodlands be affected by climate change?”
“How does the structural diversity of wet woodland compare to that of equivalent non-forested wetland or dry forest?”
Measures:
Volumetric capacity (occupied or unoccupied)
Physical arrangement
Identity/traits of biotic components (mainly sessile, though other biota also count)
Need to consider what technology is available and how much time is allocated for data collection. (eg. terrestrial LiDAR scanners)
Storch et al 2018 arrived at 11 measures for structural diversity, related to:
DBH (live and dead)
Diameter of downed deadwood
Stand height
Decay classes
Bark-diversity index
Flower/fructification diversity
Tree species richness
Wet woodland shows a higher structural diversity than either dry forest or non-forested wetland.
This paper analysed structural diversity of forested wetlands in Atlantic Canada, seeking a measure to distinguish firested wetland from upland forest. The results showed no siginificant difference.
1:
The physical features of wet woodland make it difficult for tree species to remain standing beyond a certain height.
This leads to frequent canopy openings, increased horizontal structure and prevalence of deadwood.
This creates a higher diversity of niches and thus higher structural diversity beyond that expected from dry forest or unforested wetlands.
2:
High temporal and spatial structural diversity due to changing water levels, premature tree fall and spatial variation in inundation lead to a diverse array of niches and thus higher structural diversity beyond that expected from dry forest or unforested wetlands.
3:
High species turnover due to poor growing conditions gives more opportunities for unique and rare species, including pioneer species, late-stage species and flood-tolerant species.