Geescroft Wilderness Carbon Chart
The accumulation of organic carbon in soil and tree biomass has been measured on two contrasting sites at Rothamsted that were fenced off in the 1880s and left to revert naturally to woodland. Geescroft, on acidic soil and Broadbalk Wilderness, on calcareous soil. Previously, both sites had been in arable cultivation for centuries.
The figure shows the accumulation of organic carbon in the soil, and tree root, litter and above-ground biomass in the Geescroft Wilderness, 1883-1999. This selected data is from work published in Poulton et al. (2003).
The Geescroft site was previously a long-term arable site, with natural regeneration of deciduous woodland following abandonment of arable cropping. It was originally part of an experimental field that grew beans (Vicia faba) from 1847-1878, with frequent breaks due to crop failure. This was followed by four years of bare fallowing 1879-1882. Clover was then grown 1883-1885, and last cultivated in spring 1883. In January 1886 the Wilderness area was fenced off and left uncultivated. Reversion is presumed to have started in spring 1883, after the last cultivation. The Wilderness covers part of the previous experiment on beans which included phosphorus treatments. Where possible, data has been given for soils taken from areas which had received no P fertilizer, although Jenkinson (1971) found no effect of P on the build up of organic C or N.
The acidic Geescroft Wilderness is now a deciduous wood dominated by oak (Quercus robur). In contrast, Broadbalk Wilderness is now dominated by ash (Fraxinus excelsior), with sycamore (Acer pseudoplatanus) and hawthorn (Craetagus monogyna).
The soil has been sampled to an equivalent depth of 69cm (see Poulton et al, 2003 for further details). Because the soil has become acidic, it is now covered by a permanent litter layer, in contrast to Broadbalk Wilderness, where each year's litter fall decomposes before the next arrives. This site has gained 2.00 t C ha-1 year over the 118 year period (0.38 t in litter and soil, plus an estimated 1.62 t in trees and their roots). Data on the accumulation of nitrogen is also available from the e-RA curators.
This dataset is available under a Creative Commons Attribution Licence (4.0).
YOU MUST CITE AS: Sarah Perryman (2015). Dataset: Geescroft wilderness accumulation of organic carbon Electronic Rothamsted Archive, Rothamsted Research 10.23637/KeyRefOAGEWoc
Please review our How to Credit Datasets guidance for more information.
Rothamsted relies on the integrity of users to ensure that datasets are used appropriately and Rothamsted Research receives suitable acknowledgment as being the originators of these data. Please review the Conditions of Use before downloading.
This dataset is derived from measurements made by the Analytical Chemistry Unit, Rothamsted Research, Harpenden. The data presented is mean data from selected plots and sections only. The complete data set, including the raw data used to derive the mean values, is available from the e-RA curators.
The Analytical Chemistry Unit follows the Joint Code of Practice (JCoPR) and participates in European Quality Assurance programmes. All performance is strictly monitored using certified external standards alongside in-house standard materials. Standards and check samples are monitored and recorded.
Site size Area: 1.3 ha
Soil detail Silty clay loam surface overlying clay-with-flints, over chalk at a depth of several metres. Topsoil (0-23cm) contains 20-25% clay, rising to 50-60% at depths of 1 metre. Stagnogleyic palaeo-argillic brown earth (Soil Survey of England and Wales classification). Aquic Paleudalf (USDA classification). Chromic Luvisol (FAO classification). Soil comparisons are made on an equivalent depth basis, to allow for changes in soil bulk density, see Poulton et al, 2003 for further details. The soil is now acid - the pH fell from 7.1 in 1883 to 4.4 in 1999. Geescroft never contained free CaCO3, although it occasionally received small amounts of chalk before the 1880s.
See key references in Related Documents for further information, particularly Poulton (1996).
For further information and assistance, please contact the e-RA curators, Sarah Perryman and Margaret Glendining using the e-RA email address: firstname.lastname@example.org