Abstract

Temperate conifer forests in the Colorado Front Range are fire-adapted ecosystems where wildland fires leave a legacy in the form of char and charcoal. Long-term soil charcoal C (CC) pools result from the combined effects of wildland fires, aboveground biomass characteristics and soil transfer mechanisms. We measured CC pools in surface soils (0–10 cm) at mid-slope positions on east facing aspects in five continuous foothills shrubland and conifer forest types. We found a significant statistical effect of vegetation type on CC pools along this ecological gradient, but not a linear pattern increasing with elevation gain. There is a weak bimodal pattern of CC gain with elevation between foothills shrublands (1.2 mg CC ha−1) and the lower montane, ponderosa pine (1.5 mg CC ha−1) and Douglas-fir (1.5 mg CC ha−1) forest types prior to a mid-elevation decline in upper montane lodgepole pine forests (1.2 mg CC ha−1) before increasing again in the spruce/subalpine fir forests (1.5 mg CC ha−1). We propose that CC forms and accumulates via unique ecological conditions such as fire regime. The range of soil CC amounts and ratios of CC to total SOC are comparable to but lower than other regional estimates.

Highlights

  • Temperate conifer forests and foothills shrublands in the Colorado Front Range of the RockyMountains are fire-adapted ecosystems where wildland fires leave a legacy of black C (BC) on the landscape

  • The general pattern is foothill shrublands dominated by mountain mahogany (Cercocarpus montanus) at the lowest elevations which transitions to open montane forests dominated by ponderosa pine (Pinus ponderosa var. scopulorum) on warm, dry sites and Rocky Mountain

  • We accept the general hypothesis that soil organic C (SOC) and charcoal C (CC) vary by vegetation type, but we can make specific vegetation type comparisons for SOC only

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Summary

Introduction

Temperate conifer forests and foothills shrublands in the Colorado Front Range of the Rocky. Mountains are fire-adapted ecosystems where wildland fires leave a legacy of black C (BC) on the landscape. Black C is a generalized term applied to thermally-altered vegetation. The term charcoal C (CC) is used to define the BC fraction that is resistant to a weak nitric acid (HNO3)/hydrogen peroxide (H2O2) digest. Charcoal accumulates in soils through various transfer mechanisms and is retained potentially from centuries to millennia [3]. Fire-derived charcoal is an integrated component in temperate conifer forest soils, linked to increased total soil organic C (SOC) pools [4] and inorganic nitrogen (N) availability [5,6]

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