Deciphering interactions between climate, carbon, biodiversity and livelihoods in East African mountains Rob Marchant, Claudia Capitani, Philip Platts, Dereje Denu, Mathew Mathayo Mpanda, Dickens Odeny, Peter Omeny, Tadesse Woldemariam Gole, Joyce Ininda, Faith Karanja, Ensermu Kelessa, Chris Oludhe, Geoffrey Mwchala, Geroge Ogutu, Philip Omondi, Amos Majule, Marion Pfeifer and Fergus Sinclair During the last four decades, cumulative CO2 emissions from forest loss and other land use changes have increased by 45%, with commensurate impacts on global climate and biodiversity, as well as more localised impacts on ecosystem goods and services such as hydrological functioning, soil conservation and forest products. Half of the African population, and most priority sites for conservation, are concentrated in mountain and coastal regions. Research on the interactions between mountain biodiversity, carbon storage and local livelihoods under environmental change is, therefore, crucial. It is challenging to understand how and why climates are changing at local scales, and how climate models can be used to provide useful information for a range of stakeholders (national level policy developers through to households), particularly in mountain areas where environmental gradients are steep and where large and local scale drivers interact to greatly influence climate variability, and associated uncertainty in projections. Addressing the lack of high-resolution, regionally-focused climate projections for Africa, we constructed ‘AFRICLIM’ climate ensembles from a range of global climate models, spatially downscaled by regional climate centres (CORDEX initiative), and then by bias-correction against high-resolution baselines. Comparing historical runs with remotely-sensed and in situ weather records across East Africa revealed that unimodal rainfall patterns are better captured than the bi-modal rainfall regimes of the equatorial sub-region. These uncertainties notwithstanding, spatially downscaled projections for the CHIESA transects indicate that by mid-century, mean annual temperatures could be 1.8–2.4°C warmer in the Taita Hills, 1.9–2.6°C warmer in Mount Kilimanjaro, and 2.3–3.0°C warmer in the Jimma Highlands. Mean annual rainfall is projected to increase in Taita but to remain similar for Kilimanjaro and Jimma, but with high model uncertainty (Figure 1). The projections indicate an increase in climatic extremes, seasonally and annually, compounded by increased uncertainty around the timing of these events. In participatory scenario analysis, local stakeholders in Taita envisaged solutions for possible changes in rainfall and temperature, mainly targeting improved water retention and usage. These farmers are most concerned by increasing variability and unpredictability of climatic events, as opposed to steady changes in these parameters. The spatial distributions of tree biomass, soil organic carbon and soil nutrients, plant, bird and butterfly diversity were studied across ~150 1-ha plots: 29 in Jimma, 75 in Kilimanjaro and 48 in Taita. The plots span a range of land use / land cover types, including natural or degraded forest, semi-managed coffee forest (SMCF), mixed agroforestry systems, woodland, pasture, low-intensity cropland, and plantation. Carbon assessments highlight the importance of 1 agroforestry systems for climate change mitigation, in both the above- and below-ground carbon pools. For example, trees in Jimma Highland’s SMCFs store 62±25 (mean±SE) AGC t.ha-1, compared with 82±32 t.ha-1 in adjacent natural forests (Figure 2). Other land use types, such as woodland, pasture and cropland, store significantly less carbon. Diversity among all growth forms of plant is highest in SMCFs, partly due to degradation in the natural forests. Butterfly diversity is highest in the natural forests, especially among habitat specialists. Similarly in Taita, bird and butterfly diversity among habitat specialists is highest in the forests, while overall diversity, driven by generalist species, is highest in the agroforest and low-intensity cropland systems. Future loss of trees from these landscapes can, however, be expected to impact negatively on biodiversity and, particularly in Kilimanjaro, has been linked with reductions in soil fertility. To ensure future safeguarding of biodiversity, carbon storage, and other ecosystem services, we suggest that traditional coffee farmers be supported during times of yield loss or failure in the market price of coffee, to lower the risk of conversion to cropland. Tree planting is encouraged as part of an integrated management system, to increase carbon storage and to improve soil fertility, as well as to facilitate pest control and pollination services. Increased tree cover has the additional benefit of regulating hydrological flows, and reducing air temperatures locally and regionally, helping to mitigate some of the projected impacts of climate change. Surveying over 500 sites across East African biomes, we document a predictable relationship between vegetation canopy structure and its impact on local land surface temperature - a beneath the canopy cooling effect, whereby dense vegetation may reduce microclimatic in the understory by several degrees Celsius, compared to open lands. Indeed, it remains unclear to what extent locally perceived changes in recent climate are a function of broad-scale processes (e.g. global warming) as opposed to local and regional changes in land use. Participatory scenario analysis in Taita found that local stakeholders, on the one hand, acknowledged the negative effects of deforestation in water catchment areas, and the need for increased forest cover; on the other hand, they could not envisage alternative economic activities to farming, which is expected to expand in line with local population increase. Reconciling these apparently opposing trajectories is a major challenge for conservation of the forest resource that underpins local food security, environmental regulation and connects with global issues of climate regulation. 2 Figure 1. Changes in rainfall as predicted by one regional model compared to satellite-derive rainfall. While coastal Eastern Africa is predicted to get broadly wetter, the Ethiopian Highlands are predicted to have a reduction in annual rainfall and also experience significant changes in the seasonal distribution of this rainfall (right). Platts PJ, Omeny PA, Marchant R (2015). AFRICLIM: high-resolution climate projections for ecological applications in Africa. African Journal of Ecology 53, 103-108. Figure 2. Left: Distribution of vegetation plots (1 ha) along a 23.6 km transect in the Jimma Highlands, southwest Ethiopia, part of the Eastern Afromontane Biodiversity Hotspot. Right: Aboveground live carbon storage across land use / land covers types. Traditionally managed coffee forests retain 75% of carbon, compared with natural forests. Plant and animal diversity is high is both systems compared to other land use types. Plantations store the most carbon, but the trees are harvested at maturity and the stands retain minimal biodiversity. 3
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