Abstract
There is a critical need to quantify the role of soil mineral composition on organic carbon (C) stabilization in forest soils. Here, we address this need by studying a matrix of forest ecosystems and soil parent materials with the objective of quantifying controls on the physical partitioning and residence time of soil organic carbon. We sampled soil profiles across a climate gradient on the western slope of the California Sierra Nevada, focusing on three distinct forest ecosystems dominated by ponderosa pine, white fir, or red fir, on three igneous parent materials that included granite, andesite, and basalt. Results indicated that short-range order mineral phases were the dominant factors accounting for the variation in soil carbon content and residence time. The results further suggested an interaction between ecosystem fire regime and the degree of soil weathering on the partitioning, chemical composition, and residence time of C in density separated soil physical fractions. These results suggest a link between the degree of soil weathering and C storage capacity, with a greater divergence in storage capacity and residence time in the Inceptisols, Entisols, and Andisols of the white fir and red fir ecosystems relative to minimal variation in the highly weathered Ultisols and Alfisols of the ponderosa pine ecosystem.
Highlights
Understanding the fate and stabilization of organic carbon (C) in temperate forest soils is central to determining the role of terrestrial ecosystems in mitigating climate change, predicting effects of changing forest management and fire regimes, and quantifying local and regional terrestrial C budgets
General soil properties and taxonomic variation have been detailed in previous studies, with a brief summary here by ecosystem type and each parent material to provide context (Tables 1 and 2)
This pattern was most pronounced in the white fir ecosystem where the andesite-derived soils classified as Humic Haploxerands with an amorphic mineralogy class
Summary
Understanding the fate and stabilization of organic carbon (C) in temperate forest soils is central to determining the role of terrestrial ecosystems in mitigating climate change, predicting effects of changing forest management and fire regimes, and quantifying local and regional terrestrial C budgets. Temperate forests contain roughly 118 Pg of C, or approximately 15% of the total C in forested ecosystems globally [1]. We quantify how variation in soil parent material and soil mineral assemblage control the physical partitioning and stabilization of soil C across a range of regionally important, highly productive conifer ecosystems in the Sierra Nevada of California. These ecosystems play a significant and disproportionately large role in regional soil C budgets relative to their land area [4], highlighting the critical need to understand the mechanisms controlling soil C stabilization in these systems.
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