Abstract

Peatlands represent an important component of the global carbon cycle, storing 180–621 Gt of carbon (C). Small-scale spatial variations in elevation, frequently referred to as microtopography, influence ecological processes associated with the peatland C cycle, including Sphagnum photosynthesis and methane flux. Microtopography can be characterized with measures of topographic variability and by using conceptual classes (microforms) linked to function: most commonly hummocks and hollows. However, the criteria used to define these conceptual classes are often poorly described, if at all, and vary between studies. Such inconsistencies compel development of explicit quantitative methods to classify microforms. Furthermore, gradient-based characterizations that describe spatial variability without the use of microforms are lacking in the literature. Therefore, the objectives of this study were to (1) calculate peatland microtopographical elevation gradients and measures of spatial variability, (2) develop three microform classification methods intended for specific purposes, and (3) evaluate and contrast classification methods. Our results suggest that at spatial scales much larger than microforms, elevation distributions are unimodal and are well approximated with parametric probability density functions. Results from classifications were variable between methods and years and exhibited significant differences in mean hollow areal coverages of a raised ombrotrophic bog. Our results suggest that the conceptualization and classification of microforms can significantly influence microtopographic structural metrics. The three explicit methods for microform classification described here may be used and built upon for future applications.

Highlights

  • Northern peatlands are an important component of the global carbon (C) cycle (Yu and others 2010, 2011), typically storing C at rates in the range of 20–30 g C m-2 y-1 (Yu and others 2011)

  • We provide four measures of microtopography in SPRUCE plots that are based on elevation distributions, spatial variability, and surface roughness of peatland microtopography

  • To address the need for explicit microform classification schemes, we developed quantitative methods to classify microforms for three purposes that differ in their conceptualize of microforms (a) the Functional_Classification classifies microforms based on how the structure of microtopography interacts with ecological drivers to determine ecological function; (b) the ELM_Classification is designed to generate microtopographic parameters that are most consistent with the conceptualization of microtopography in a land surface model, ELM_SPRUCE; and (c) the Scaling_Classification is constructed to classify microforms in a manner consistent with the subjective placement of instrumentation in the field, and meant to be used to make spatial extrapolations

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Summary

Introduction

Northern peatlands are an important component of the global carbon (C) cycle (Yu and others 2010, 2011), typically storing C at rates in the range of 20–30 g C m-2 y-1 (Yu and others 2011). The hummock–hollow complex dominates the microtopography of many peatlands and plays a major role in several ecological, hydrologic, and biogeochemical processes including C dynamics. These include: an influence on greenhouse gas emissions (Bubier and others 2003; Hirano and others 2009; Moore and others 2011), rates of decomposition (Johnson and Damman 1991), peat accumulation (Chaudhary and others 2018), plant community (Andrus and others 1983; Chaudhary and others 2018; Harris and Baird 2018; Arsenault and others 2019; Malhotra and others 2016), plant productivity (Moore 1989), water chemistry (Arsenault and others 2019), and nutrient availability (Chapin and others 1979; Damman 1978). The primary biophysical driver of these differences is changes in peat water and oxygen content, which are associated with water table depth

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