D. Sleep

Export of dissolved organic carbon from peatlands under elevated carbon dioxide levels

Peatlands represent a vast store of global carbon. Observations of rapidly rising dissolved organic carbon concentrations in rivers draining peatlands have created concerns that those stores are beginning to destabilize. Three main factors have been put forward as potential causal mechanisms, but it appears that two alternatives—warming and increased river discharge—cannot offer satisfactory explanations. Here we show that the third proposed mechanism, namely shifting trends in the proportion of annual rainfall arriving in summer, is similarly unable to account for the trend. Instead we infer that a previously unrecognized mechanism—carbon dioxide mediated stimulation of primary productivity—is responsible. Under elevated carbon dioxide levels, the proportion of dissolved organic carbon derived from recently assimilated carbon dioxide was ten times higher than that of the control cases. Concentrations of dissolved organic carbon appear far more sensitive to environmental drivers that affect net primary productivity than those affecting decomposition alone.

Carbon assimilation and turnover in grassland vegetation using anin situ13CO2 pulse labelling system

A mobile laboratory was developed to administer a controlled flow of (13)C labelled CO(2) at ambient concentrations ( approximately 350 ppm) in the field. The stable isotope delivery (SID) system consists of an isotope-mixing unit with flow control to a series of 12 independent labelling chambers. In-line CPU controlled infrared gas analysers allow automated measurement of chamber CO(2) concentrations and gas flow management. A preliminary experiment was established on an upland pasture located at the NERC Soil Biodiversity experimental site, Sourhope, UK, in August 1999. The objective of this investigation was to determine the magnitude of pulse-derived C incorporation into a typical upland plant community. To achieve this, the SID system was deployed to pulse-label vegetation with CO(2) enriched with (13)C (50 atom %) at ambient concentrations ( approximately 350 ppm) on two consecutive days in August 1999. Samples of headspace CO(2), shoot and root were taken on four occasions over a period of 28 days after (13)C labelling. These materials were then prepared for (13)C/(12)C ratio determination by continuous-flow/combustion/isotope ratio mass spectrometry (CF-C-IRMS). Results showed that pulse derived CO(2)-C was assimilated at a rate of 128 +/- 32 microg g shoot-C hour(-1). Dynamic samplings showed that pulse-derived (13)C concentrations in the labelled plant tissues declined by 77.4 +/- 6% after 48 hours. The rapid decline in (13)C concentrations in plant matter was the result of C loss from the plant in the form of respired CO(2) and root exudates, and dilution by subsequent unlabelled C assimilates. This novel system offers considerable potential for in situ tracer investigations.

Active microbial RNA turnover in a grassland soil estimated using a 13CO2 spike

Rhizosphere microbes are critical to the initial transfer and transformation of root carbon inputs to the soil but our understanding of the activity of these organisms remains constrained by their limited culturability. In this study we combined isotopic 13C tracer and molecular approaches to measure the incorporation of recently assimilated plant C into soil microbial RNA and DNA pools as a means to determine the turnover of the ‘active’ rhizosphere community. This required the development of a method for the extraction, purification and preparation of small-sample soil DNA and RNA (<5 μg C) for isotope analysis. Soil, plant and respired CO2 samples were collected from a 13CO2 pulse-chase experiment at intervals for 20 days post-labelling. The peak of 13C release in soil/root respired CO2 came between 5 and 48 h after 13CO2 pulse-labelling and was followed by a secondary peak of soil heterotroph 13C respiration after 136 h. Results showed that both soil DNA and RNA rapidly incorporated recent photosynthate with greatest 13C found in the ‘active’ microbial RNA fraction reflecting higher rates of microbial RNA turnover. The dilution rate of the pulse derived 13C in RNA-C was used to estimate a microbial RNA turnover of approximately 20% day−1 with a 15–20 day residence time for photosynthate derived 13C in the RNA pool. The findings of this work confirm the rapid transfer of photosynthate C inputs through soil microorganisms to the atmosphere as CO2 and the potential of the biomolecular-isotope tracer approach in soil C research.

Earthworms of a land restoration site treated with paper mill sludge

Land restoration at a former landfill site, Bidston Moss, NW England, has involved heavy applications of paper mill sludge (PMS), a byproduct of paper recycling. The development of earthworm communities at the site has been assisted by earthworm inoculation. Initially low numbers of epigeic species were present, but as the restoration has progressed since 1996 a substantial number, biomass and diversity of earthworms has become established, including a variety of ecological types. In some areas there is substantial surface casting. Cast colour indicates selective consumption of PMS, and δ13C ratios suggest that PMS is a major nutrient source for earthworms. Although concentrations of copper in the PMS are higher than those typical for soils, concentrations in earthworm tissue are relatively low. Low availability of copper will reflect the high content of organic matter and clay, and relatively high pH, of the PMS.

Impact of water table depth on forest soil methane turnover in laboratory soil cores deduced from natural abundance and tracer 13C stable isotope experiments

We investigated turnover of methane (CH4) in soils from a poorly drained UK forest. In situ, this forest exhibited a negligible soil–atmosphere CH4 flux, whereas adjacent grassland plots were sources of CH4. We hypothesised that the forest plots exhibited reduced anaerobic CH4 production through water-table draw down. Consequently, we exposed soil cores from under oak to high and low water-table conditions in the laboratory. Methane fluxes increased significantly in the high water-table (1925±1702 μg CH4 m−2 h−1) compared to the low one (−3.5±6.8 μg CH4 m−2 h−1). Natural abundance δ13C values of CH4 showed a strong depletion in high water-table cores (−56.7±2.9 ‰) compared to methane in ambient air (−46.0 ‰) indicative of methanogenic processes. The δ13C values of CH4 from low water-table cores (δ13C−46.8±0.2 ‰) was similar to ambient air and suggested little alteration of headspace CH4 by the soil microbial community. In order to assess the CH4 oxidizing activity of the two treatments conclusively, a 13CH4 spike was added to the cores and 13CO2 production was measured as the by-product of CH4 oxidation. 13CH4 oxidation rates were 57.5 (±12.7) and 0.5 (±0.1) μg CH4 m−2 h−1 for high and low water-tables, respectively. These data show that the lower water-table hydrology treatment impacted methanogenic processes without stimulating methanotrophy.