Seeing the forest for the fractions Comparing soil organic matter fractionation methods using molecular features after forest stand conversion
| Authors |
|
|---|---|
| Publication date | 02-2023 |
| Journal | Geoderma |
| Article number | 116280 |
| Volume | Issue number | 430 | 116280 |
| Pages (from-to) | 430 |
| Number of pages | 11 |
| Organisations |
|
| Abstract |
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 (Py-GC/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.
|
| Document type | Article |
| Note | With supplementary file. |
| Language | English |
| Published at | https://doi.org/10.1016/j.geoderma.2022.116280 |
| Downloads |
1-s2.0-S0016706122005870-main
(Final published version)
|
| Supplementary materials | |
| Permalink to this page | |
