Abstract

There is concern that accelerating sea‐level rise will exceed the vertical growth capacity of coastal‐wetland substrates in many regions by the end of this century. Vertical vulnerability estimates rely on measurements of accretion and/or surface‐elevation‐change derived from soil cores and/or surface elevation tables (SETs). To date there has not been a broad examination of whether the multiple timescales represented by the processes of accretion and elevation change are equally well‐suited for quantifying the trajectories of wetland vertical change in coming decades and centuries. To examine the potential for timescale bias in assessments of vertical change, we compared rates of accretion and surface elevation change using data derived from a review of the literature. In the first approach, average rates of elevation change were compared with timescale‐averaged accretion rates from six regions around the world where sub‐decadal, decadal, centennial, and millennial timescales were represented. Second, to isolate spatial variability, temporal comparisons were made for regionally unique environmental categories within each region. Last, comparisons were made of records from sites where SET‐MH stations and radiometric measurements were co‐located in close proximity. We find that rates vary significantly as a function of measurement timescale and that the pattern and magnitude of variation between timescales are location‐specific. Failure to identify and account for temporal variability in rates will produce biased assessments of the vertical change capacity of coastal wetlands. Robust vulnerability assessments should combine accretion rates from multiple timescales with the longest available SET record to provide long‐term context for ongoing monitoring observations and projections.

Highlights

  • (Woodroffe 1990; Reed 2002; Alongi 2015; Kirwan et al 2016)

  • The vertical growth of coastal wetland substrates occurs through dynamic feedbacks related to the production/supply and retention/preservation of organic matter and mineral sediments relative to the accommodation space created by rising water level (Kirwan and Megonigal 2013; Krauss et al 2014; Woodroffe et al 2016)

  • Vertical change in coastal wetlands found for decadal accretion in N Aust. (n 5 5), and centennial accretion in NW Med. (n 5 6) and S Aust. (n 5 2)

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Summary

Introduction

(Woodroffe 1990; Reed 2002; Alongi 2015; Kirwan et al 2016). there is growing concern that these wetlands will not be able to keep pace with projected rates of accelerated SLR in the current century (Ellison and Stoddart 1991; Cahoon et al 2006; FitzGerald et al 2008; Lovelock et al 2015; Sasmito et al 2016). The vertical growth of coastal wetland substrates occurs through dynamic feedbacks related to the production/supply and retention/preservation of organic matter and mineral sediments relative to the accommodation space created by rising water level (Kirwan and Megonigal 2013; Krauss et al 2014; Woodroffe et al 2016). The physical process of decreasing the volume occupied by a given unit of soil mass. A decrease in the soil volume as a function of such processes as drying (loss of water volume), decomposition of organic matter (loss of soil mass), or rearrangement and increase of packing density of mineral particles. A continuum of processes that include the physical degradation of material as well as biological and chemical transformation of complex compounds into simpler ones that in turn may be removed from the soil in a gaseous or dissolved state

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