Au cours des 20 dernières années, les zones urbaines ont connu une croissance impressionnante. Actuellement, plus de 3,5 millions de personnes y vivent (environ la moitié de la population mondiale). Les pays en développement, en particulier, connaissent une évolution rapide avec un déclin des économies rurales au profit des économies urbaines (ONU-HABITAT, ICLEI et PNUE, 2009, p. 7). Si les pays en développement présentent des rythmes et une étendue d’urbanisation très variés, leur défi à relever tient à la difficulté de stabiliser une demande croissante en ressources énergétiques, de construire des ponts, d’assurer l’égalité et l’autonomisation, de diminuer la dégradation de l’environnement, de promouvoir la santé et les moyens de subsistance ainsi que d’élaborer de nouvelles orientations pour le développement (Droege, 2008, p. 1).
Abstract In recent years, global hunger has begun to rise, returning to levels from a decade ago. Climate change is a key driver behind these recent rises and is one of the leading causes of severe food crises. When coupled with population growth and land use change, future climate variability is predicted to have profound impacts on global food security. We examine future global impacts of climate variability, population, and land use change on food security to 2050, using the modeling framework FEEDME (Food Estimation and Export for Diet and Malnutrition Evaluation). The model uses national food balance sheets (FBS) to determine mean per capita calories, hence incorporating an assumption that minimum dietary energy requirements (MDER) remain constant. To account for climate variability, we use two Representative Concentration Pathway (RCP) scenarios from the Intergovernmental Panel on Climate Change (IPCC), alongside three Shared Socio‐economic Pathway (SSP) scenarios incorporating land use and population change within the model. Our results indicate that SSP scenarios have a larger impact on future food insecurity, in particular because of projected changes in population. Countries with a projected decrease in population growth had higher food security, while those with a projected rapid population growth tended to experience the worst impacts on food security. Although climate change scenarios had an effect on future crop yields, population growth appeared to be the dominant driver of change in undernourishment prevalence. Therefore, strategies to mitigate the consequences of projected population growth, including improved maternal health care, increasing equality of access to food at the national level, closing the yield gap, and changes in trade patterns, are essential to ensuring severe future food insecurity is avoided.
Abstract. A number of changes in agricultural land‐management show some potential as carbon mitigation options. However, research has focused on CO 2 ‐carbon mitigation and has largely ignored potential effects of land management change on trace gas fluxes. In this paper, we attempt for the first time, to assess the impact of these changes on fluxes of the important agricultural greenhouse gases, methane and nitrous oxide, in the UK. The estimates presented here are based on limited evidence and have a great (unquantifiable) uncertainty associated with them, but they show that the relative importance of trace gas fluxes varies enormously among the scenarlos. In some, such as the application of sewage sludge, woodland regeneration and bioenergy production scenarios, the inclusion of estimates for trace gas fluxes makes only a small (<10%) difference to the CO 2 ‐C mitigation potential. In the animal manure and agricultural extensification scenarios, including estimates of trace gas fluxes has a large impact, increasing the CO 2 ‐C mitigation potential by up to 50%. In the no‐till scenario, the carbon mitigation potential decreases significantly due to a sharp increase in N 2 O emissions under no‐till. When these land‐management options are combined for the whole agricultural land area of the UK, including trace gases has an impact on estimated mitigation potentials, and depending upon assumptions for the animal manure scenario, the total mitigation potential either decreases by about 10% or increases by about 30%, potentially shifting the mitigation potential of the scenario closer to the EU's 8% Kyoto target for reduction of CO 2 ‐carbon emissions (12.52 Tg C yr −1 for the UK).
In salt-affected soils, soil organic carbon levels are usually low as a result of poor plant growth; additionally, decomposition of soil organic matter may be decreased. Thus, the CO2 evolution from salt-affected soils is likely to be lower than that from non-saline soils. Carbon models such as Rothamsted Carbon (RothC) that are used to estimate global CO2 emission do not consider the effect of salinity on CO2 emission. Given the large extent of salt-affected soils (19 percent of 20.8 billion hectares of arable land on Earth), this may lead to overestimation of CO2 release. Two laboratory incubation experiments were conducted to assess the effect of soil texture on response of CO2 release to salinity and to calculate a rate modifier for salinity in soil carbon models and study soil carbon dynamics: a sandy loam (18.8% clay) and a sandy clay loam (22.5% clay) in one experiment and a loamy sand (6.3 % clay) and a clay loam (42 % clay) in another experiment. Sodium chloride (NaCl) was used to develop a range of salinities viz. EC1:5 1.0, 2.0, 3.0, 4.0 and 5.0 dS/m. The soils were amended with 2% wheat residues and CO2 emission was measured over 4 months. Cumulative CO2-C/g soil decreased with increased salinity. Cumulative CO2-C expressed as percent of the control soil (without salt addition) showed a lower impact of salinity on organic matter decomposition with increasing clay content. A decrease in particulate organic carbon (POC) associated with incubation was less in the higher saline soils whereas total organic carbon, humus-C and charcoal-C did not change over time and were not significantly affected by salinity. A significant exponential relationship was obtained between EC and the salt rate modifier, suggesting that a new salt rate modifier should be incorporated into RothC in order to accurately model CO2 emissions from salt-affected soils.
Abstract This article examines the architectural evolution of Barlborough Hall from its construction in 1583 to the present day, using a number of previously unpublished documents, mostly from the Locker-Lampson Collection. It also discusses a painting in the British Library which indicates that the house was once prefaced by ranges of forecourt buildings, and it outlines the various alterations made to the house and garden between 1696 and 1714, identifying the architect responsible for at least some of these changes as John Hallam. The most important source of new information is an album of drawings by Lindley, Woodhead & Hurst of 1815, which records the building in detail before further alterations completed in 1825. These drawings also permit reconstructions of the likely design and appearance of the original house. The relatively minor additions in the mid-nineteenth century and the alterations made to the building since it became a school in 1938 are also outlined.