4.7 Article

Seeing the forest for the fractions-Comparing soil organic matter fractionation methods using molecular features after forest stand conversion

Journal

GEODERMA
Volume 430, Issue -, Pages -

Publisher

ELSEVIER
DOI: 10.1016/j.geoderma.2022.116280

Keywords

Pyrolysis-GC/MS; Particulate organic matter (POM); Water-extractable organic matter (WEOM); Forest management; Soil carbon persistence

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By comparing the molecular composition and environmental significance of different soil organic matter (SOM) fractions, we found that only HA and BE fractions were successful in capturing the overall processes of soil carbon (C) dynamics. Different SOM fractions can be used complementary to each other to study the environmental and ecological effects of forest stand conversion on soil C dynamics.
The molecular composition of soil organic matter (SOM) contains key information on the persistence of soil carbon (C) in relation to changes in vegetation and environmental factors. Depending on the ecosystem, analytical method and specific objectives, many SOM fractions and numerous fractionation schemes have been proposed to study soil C. However, the molecular composition and environmental significance of those different SOM fractions have not yet been compared systematically. We use a reverse fit approach to fill this knowledge gap: i.e. we chose a study area with a well-known land history to assess which information is stored in the most frequently analysed SOM fractions. The Gaume forest (Belgium) is an ancient deciduous forest (>200 years) in which small stands were converted to Norway spruce (Picea abies) 40-50 years ago. Those stands are located along a lithological gradient in soil buffering capacity. We investigated the molecular composition of bulk mineral soil samples and five organic SOM fractions by pyrolysis gas chromatography/mass spectrometry (PyGC/MS). The SOM fractions included particulate OM (POM), water extractable OM (WEOM), and fractions obtained by alkaline extraction, including the traditionally used humic acid (HA) and fulvic acid (FA) and the total base extract from which they are obtained (BE). Our results indicate that pyrolysates of bulk mineral soil did not prove useful to reflect environmental changes after forest stand conversion. Principal Component Analysis indicated that within each organic fraction similar changes occurred when comparing soil depths, degree of SOM decomposition, litter inputs, and soil buffering capacity. However, only the HA and BE appeared successful in capturing all these processes: the degree of SOM decomposition was not expressed in pyrolysates from the POM, differences in litter input between forest stand types were not evidenced in the WEOM, and effects of buffering capacity were not demonstrated in the WEOM and FA fractions. Thus, the molecular composition of different SOM fractions can be used complementary to each other to study environmental and ecological effects of forest stand conversion on soil C dynamics.

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