10 11 Soils as carbon sinks or sources: from mid-Wales to the Arctic Soils as carbon sinks or sources: from mid-Wales to the Arctic Soils as carbon sinks or sources: from mid-Wales to the Arctic > Alan Jones, John Scullion and Dylan Gwynn-Jones With so much attention currently paid to rising levels of atmospheric CO2, we would be forgiven in thinking that this was the greatest part of the climate change story. However, soil carbon represents the ‘hidden half’ of the global carbon (C) balance and this is often overlooked by popular imagination. Soil represents a major global store of carbon, holding approximately twice the quantity of carbon than is present in the atmosphere and three times that of terrestrial vegetation. The potential for soil to either store or emit carbon depending on the prevailing conditions, and its immense relative size, means that soil management for carbon worldwide is a pressing concern in our response to global climate change. When land management is changed markedly or environmental conditions are perturbed, soil carbon stocks can respond relatively rapidly as the soil-atmosphere system equilibrates to the new circumstances. A recent example of this is the rapid erosion of peat-rich moorland and associated release of dissolved organic carbon observed in some upland areas of the UK (Freeman et al., 2004). Determining exactly how soils respond to such external changes is imperative if we are to optimally manage carbon stocks in the future. Environmental factors such as soil temperature and biological activity are also important for carbon stability (Hartley and Ineson, 2008). In parts of the UK where the climate is cooler and wetter, soil carbon accumulates naturally. This is especially true for soils with impeded drainage, and some mire ecosystems in Wales represent very large long-term carbon stores. However, such areas are also subject to short-term climatic variability and so the medium-term impacts of climate change are very uncertain. In these and many other ecological communities, the future stability of carbon stocks is very much open to question. Rising atmospheric CO2 concentrations will in the future have indirect effects on the carbon dynamics and stability of soils via impacts on vegetation and litter (Freeman et al., 2004). There is significant international interest on how this will impact soils that have successfully accumulated carbon in the past and whether they will have the capacity to continue to sequester carbon under elevated concentrations of CO2. The Arctic biome holds enormous carbon stocks in its soil, representing one third of the global soil C store. With a rapidly warming climate in this region and future elevated concentrations of CO2, will this stock in the future represent a net sink or emitter of CO2? To address these issues, IBERS scientists are now synthesising work on soil carbon from a series of experiments, ranging in location from Wales to Arctic Sweden. Project teams led by Drs John Scullion and Dylan Gwynn-Jones have received funding from the Welsh European Funding Office (WEFO) under the Convergence Programme and from the Natural Environment Research Council (NERC), respectively, to investigate the dynamics of carbon cycling and sequestration in soils. 1. Carbon soil sequestration: land changes and amendments (SEREN Project) > John Scullion, Gareth Griffth, Dylan Gwynn-Jones, Mike Humphreys, Iain Donnison and Kerrie Farrar The SEREN project started in spring 2011 and involves collaboration between Aberystwyth, Bangor and Cardiff universities. Aberystwyth and Bangor research in SEREN focuses on the potential for soil carbon sequestration and retention under a range of land use scenarios. The IBERS team will investigate the soil carbon impacts of different restoration strategies on land degraded by mining or industry, the effects of novel cropping and soil amendments, and the opportunities for plant breeding to improve carbon sequestration. 12 13 Soils as carbon sinks or sources: from mid-Wales to the Arctic Soils as carbon sinks or sources: from mid-Wales to the Arctic Bioenergy crops as carbon sequesters A key focus of research in Wales has been to investigate ways to optimise levels of soil carbon sequestration. Bioenergy crops have received much media attention of late due to their perceived negative impacts on food security but such crops can provide an excellent potential strategy for combating rising atmospheric CO2 levels. Figure 1. Reclaimed soils on opencast mining land: a potential future target area for enhanced soil carbon accumulation. Carbon sequestration in restored soils Degraded soils in Wales on land disturbed by activities such as mining (Fig. 1) have depleted organic carbon levels (Scullion and Malik, 2001) and offer significant opportunities for carbon sequestration through their rehabilitation and re-vegetation. The value of this approach in terms of carbon gain will be governed by the initial condition of the soils, the efficacy of the techniques used and the range of plant species employed (see Fig. 2). The purpose of the SEREN carbon soil sequestration project is to test a variety of rehabilitation approaches for carbon sequestration and evaluate their wider applicability in real world conditions. 15 IBERS scientists have already developed a range of biomass crops at the Plas Gogerddan campus. The SEREN project makes use of existing replicated field experiments investigating Miscanthus, willow, switchgrass and reed canary grass for their bioenergy cropping potential. It also makes the assumption that biofuel crops of the future will often be grown on more marginal or reclaimed land, hence experimental sites are located on several different soil types. This provides a unique opportunity to investigate how many soil factors, including fertility, texture and moisture levels, affect below-ground carbon allocation in such systems. Carbon sequestration using Biochar SEREN is also considering the potential role of biochar, a fine grained, organic charcoal produced by pyrolysis of agricultural plant biomass, including that derived from biofuel production. When used as a soil amendment, biochar has the potential to make a direct contribution to stable soil carbon stores, thereby enhancing carbon sequestration (Laird, 2008). There are further benefits to be gained that may lead to this technology being even more widely accepted, since biochar can also have positive effects on crop performance. Descriptions of the field and glasshouse experiments underway at IBERS to investigate these benefits can be found in the paper by Hodgson, Bevan and Farrar in this issue (see p17). Novel grass hybrids There is much interest in the prospect of genetically engineering crops to obtain favourable yields and benefits for the environment. Many of these effects may also be obtained by conventional breeding of novel hybrids which combine the favourable traits of two species. One such IBERS breeding programme has developed a ryegrass x fescue hybrid, known as Festulolium (see Humphreys paper in this issue.). With a greater efficiency of resource use than conventional cultivars, Festulolium is potentially resilient to climate change, and has added advantages of enhancing soil stabilisation and reducing the soil’s greenhouse gas emissions. to reduce the carbon footprint of grassland agriculture. SEREN research will evaluate existing Festulolium cultivars by comparing root growth and turnover during three consecutive growing seasons, in conjunction with a second trial to compare the relative productivity of these grasses as forage. The carbon sequestration potential of each cultivar will be quantified, together with appraisals of their suitability as a practical component of grassland agriculture in Wales. If a successful hybrid is developed and grown widely, it would therefore not only benefit productivity but, most importantly, would also allow grassland agriculture to play a part in offsetting greenhouse gas emissions. 2. Securing Arctic soil carbon stocks in an elevated CO2 world > Dylan Gwynn-Jones, Alan Jones, John Scullion The Arctic project also started in the spring of 2011 but builds on nearly two decades of research investment in this area. Sub-Arctic heath communities in Northern Sweden (68oN)were first exposed to elevated CO2 levels in 1993, with the aim of investigating how plants, ecological communities and carbon stocks would respond in the year 2050. The experiment continues to the present day (Fig. 4) and represents one of the longest running experiments of its kind in the world. Experiments are based at the Abisko Scientific Research station which is an international hub for climate change research. By generating cultivars of fescue-ryegrass hybrids (Fig. 3) that also maximise below-ground carbon storage, scientists at IBERS will determine the potential of plant breeding Anaerobic digestion aids carbon sequestration Given the heavy reliance on livestock production in Wales, inroads can be made locally in the sustainable management of livestock waste products and their potential utility in aiding carbon sequestration through soil application. 5 h’ ig ‘H yr ’ ’ 21 21 yr ‘Lo w h ig r ‘h 9y ‘lo w 9y r lan ed rb Un di stu ’ 0 d % Soil organic matter 10 Fast growing bioenergy crops such as Miscanthus, willow, switchgrass and reed canary grass not only substitute for non-renewable fossil fuel sources, thereby lowering carbon emissions, but have the added benefit that some of their carbon content can also be sequestered to the soil as root biomass. In the case of Miscanthus, between 0.5 and 1.5 tonnes of carbon may be sequestered below-ground per hectare annually (Hansen et al., 2003). Until recently, the focus of research on biomass fuel crops has been on enhancing their above-ground productivity and structural characteristics as fuels. There is now increasing interest in their wider impacts (Fernando et al., 2010), including their below-ground characteristics and the impacts of their cropping techniques on soil carbon stores (Garten and Wullschleger, 1999). receiving mineral fertilisers or conventionally managed slurries/ manures to those treated with anaerobic digestates. Figure 2. Percentage soil organic matter (as loss on ignition (LOI)) data (Scullion and Malik, 2001), comparing undisturbed land and restored opencast mine soils. Restored soils were subject to high and low intensity fertilisation treatments over 9 and 21 years. In a 2010 report, Defra highlighted the important contribution that anaerobic digestion (AD) can make to mitigating climate change, firstly by reducing greenhouse gas emissions from manure and secondly as a source of renewable energy. In addition to this, however, anaerobic digestates may also be useful as alternative land amendments to mineral fertilisers. Using the extensive glasshouse and field trials facilities at IBERS, SEREN will compare soil organic carbon allocation in grasslands Figure 3. Lolium multiflorum and Lolium perenne x Festuca.mairei and Festuca glaucescens –Festulolium hybrids produced by IBERS. Figure 4. Elevated CO2 fumigation experiment in Abisko (Sweden) based on a Vaccinium empetrum forest heath. 14 15 Soils as carbon sinks or sources: from mid-Wales to the Arctic Soils as carbon sinks or sources: from mid-Wales to the Arctic The vast majority of experiments that have exposed plant communities to elevated CO2 levels have seen a stimulation of above-ground growth during the first seasons of exposure. However, following this early stimulation, such growth benefits are not maintained and communities are believed to acclimatise to the new CO2 conditions. A major limitation with such research has been the limited longevity of previous experiments, with most typically maintained for just 3-5 years. With already nearly two decades of observations at Abisko, however, we are able to look beyond the initial acclimation and investigate the relative dynamics of aboveground growth to below-ground processes, studying how elevated CO2 has affected the long-term carbon dynamics and stocks in the system (Fig. 5). Elevated CO 2 Respired CO 2 some insight into how these wider communities might respond to predicted atmospheric composition in the year 2050 and allow us to interrogate their carbon stability and dynamics thoroughly. During summer 2011, the research team will investigate above-ground photosynthetic activity at both species and community level. We will also look at CO2 fluxes from the soil and at plant respiration levels. despite it often being overlooked. Research carried out over the next few years will inform future policies and practice, with potentially global implications. By developing these methods, IBERS scientists are clearly leading the way towards progressive new approaches to address the problems raised by climate change. During 2012, the work will focus on quantifying biomass production and harvesting carbon from all components of the community, including more detailed studies of the important soil microbial ecosystem. The soil’s organic matter will be separated into its constituent fractions, enabling, for the first time in this habitat, assessments of the relative rates of organic matter breakdown under elevated CO2 conditions, and also allowing the relative size of the organic pool to be quantified. This last aspect will be especially important as soil organic matter forms the main store of soil carbon. Data SEREN is part funded by the European Regional Development Fund and undertaken in conjunction with Cardiff University, the British Geological Survey, Bangor University and WDS Environmental. Litter C Root C store Root exudades & root material Acknowledgement The Arctic research is supported by NERC grant 10334 and is undertaken in collaboration with Dr Nick Ostle at CEH Lancaster, Prof. Terry Callaghan of Abisko Scientific Research Station and Prof. John Lee of Sheffield University. References DEFRA (2010). Accelerating the Uptake of Anaerobic Digestion in England: an Implementation Plan. http://archive.defra.gov.uk/environment/waste/ad/documents/ implementation-plan2010.pdf Freeman, C., Fenner, N., Ostle, N.J., Kang, H., Dowrick, D.J., Reynolds, B., Lock, M. A., Sleep, D., Hughes, S. and Hudson, J. (2004). Export of dissolved organic carbon from peatlands under elevated carbon dioxide levels. Nature 430, 195-197. Hartley, I. P. and Ineson, P. (2008). Substrate quality and the temperature sensitivity of soil organic matter decomposition. Soil Biology and Biochemistry 40, 1567-1574. Scullion, J. and Malik, A. (2001). The influence of land use and earthworm activity on organic matter dynamics in soils restored after opencast coal mining. In: Rees, R. M., Ball, B. C., Campbell, C. D. and Watson, C. A. (Eds). Sustainable management of soil organic matter. Wallingford, UK, CABI Publishing, pp. 377-385. Hansen, E.M., Christensen, B.T., Jensen, L.S. and Kristensen, K. (2003). Carbon sequestration in soil beneath long-term Miscanthus plantations as determined by 13C abundance. Biomass and Bioenergy 26, 97-105. Fernando, A.L., Duarte, M.P., Almeida, J., Boleo, S. and Mendes, B. (2010). Environmental impact assessment of energy crops cultivation in Europe. Biofuels Bioproducts & Biorefining 4, 594-604. Recalcitrant Organic Matter Garten, C.T. and Wullschleger, S.D. (1999). Soil carbon inventories under a bioenergy crop (switchgrass): measurement limitations. Journal of Environmental Quality 28, 1359–1365. Microbial biomass C Laird, D.A. (2008). The charcoal vision: a win–win–win scenario for simultaneously producing bioenergy, permanently sequestering carbon, while improving soil and water quality. Agronomy Journal 100, 178-181. Soil Organic Matter Fractions Dissolved organic carbon Figure 5. A simplified conceptual model of elevated carbon flows in Arctic heath. A very important question for the future will be whether plants in natural communities photosynthesise more carbon at elevated CO2. If they do, is the additional carbon metabolised expressed as increased above-ground growth, or is the extra carbon stored below-ground, or is it released back into the atmosphere via the soil? The fact that the additional CO2 added at Abisko over the past 20 years has a specific δ13C carbon isotope signal will be of great assistance in tracing where the elevated CO2 has gone, as it will remain detectable in leaves, roots, soil, microbes and the surrounding atmosphere. The heath community being studied is found as part of a typical sub-arctic birch forest (Fig. 6), a type of ecosystem which covers vast areas of Northern Europe. The findings from this research will therefore allow Figure 6. Sub-Arctic birch forest – a characteristic plant community of large areas of northern Europe. from these analyses will then be accessible for modelling land-based changes in sub-Arctic carbon dynamics in the future. Given the large land areas covered by the type of plant communities being studied at Abisko, the importance of this biome for carbon sequestration and its relative sensitivity to a wide range of environmental changes, this information will be of global significance. Conclusion These combined IBERS research programmes demonstrate how management of soil carbon can become a versatile tool in our strategies to adapt to rising atmospheric CO2 levels,
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