Abstract. Afforestation is a strategy to sequester atmospheric
carbon in the terrestrial system and to enhance ecosystem services.
Iceland's large areas of formerly vegetated and now degraded ecosystems
therefore have a high potential to act as carbon sinks. Consequently, the
ecological restoration of these landscape systems is part of climate
mitigation programmes supported by the Icelandic government. The aim of this
study was to explore the change in the soil organic carbon (SOC) pools and
to estimate the SOC sequestration potential during the re-establishment of
birch forest on severely degraded land. Differently aged afforested mountain
birch sites (15, 20, 25 and 50 years) were compared to sites of severely
degraded land, naturally growing remnants of mountain birch woodland and
grasslands which were re-vegetated using fertilizer and grass seeds 50 years
ago. The soil was sampled to estimate the SOC stocks and for physical
fractionation to characterize the quality of the SOC. The results of our
study show that the severely degraded soils can potentially sequester an
additional 20 t C ha−1 (0–30 cm) to reach the SOC stock of naturally
growing birch woodlands. After 50 years of birch growth, the SOC stock is
significantly lower than that of a naturally growing birch woodland,
suggesting that afforested stands could sequester additional SOC beyond 50
years of growth. The SOC fractionation revealed that at all the tested sites
most of the carbon was stored in the <63 µm fraction.
However, after 50 years of birch growth on severely degraded soils the
particulate organic matter (POM) fraction was significantly enriched most
(+12 t POM-C ha−1) in the top 30 cm. The study also found a doubling
of the dissolved organic carbon (DOC) concentration after 50 years of birch
growth. Therefore and due to the absence of any increase in the tested
mineral-associated SOC fractions, we assume that the afforestation process
evokes a carbon deposition in the labile SOC pools. Consequently, parts of
this plant-derived, labile SOC may be partly released into the atmosphere
during the process of stabilization with the mineral soil phases in the
future. Our results are limited in their scope since the selected sites do
not fully reflect the heterogeneity of landscape evolution and the range of
soil degradation conditions. As an alternative, we suggest using repeated
plot measurements instead of space-for-time substitution approaches for
testing C changes in severely degraded volcanic soils. Our findings clearly
show that detailed measurements on the SOC quality are needed to estimate
the SOC sequestration potential of restoration activities on severely
degraded volcanic soils, rather than only measuring SOC concentration and
SOC stocks.