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sequestration in soils and biomass in both crop and livestock systems. Cropping systems practices include improved land and nba kobe bryant legends never die shirt fertiliser management, land restoration, biochar applications, breeding for larger root systems, and bridging yield gaps . Options for mitigation in livestock systems include better manure management, improved grazing land

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lacking, even though this topic is of considerable social importance. Available information is mostly on separate, individual impacts of either climate change or desertification. Responses to desertification are species-specific and mechanistic models are not yet able to accurately predict individual species responses to the many factors associated with desertification under changing climate. The suppression of the grass layer through the process of woody encroachment may lead to a decrease in carbon stocks within nba kobe bryant legends never die shirt this relatively small carbon pool . Conversely, increasing woody cover may lead to a decrease and even halt in surface fires and associated GHG emissions. In their analysis of drivers of fire in southern Africa, Archibald note that there is a potential threshold around canopy cover, above which surface grass fires are rare. Whilst there have been a number of studies on changes in carbon stocks due to desertification in North America, southern Africa and Australia, a global assessment of the net change in carbon stocks as well as fire and ruminant GHG emissions due to woody plant encroachment has not been done yet. Saline and sodic soils occur naturally in arid, semi-arid and dry subumid regions of the world. Climate change or hydrological change can cause soil salinisation by increasing the mineralised groundwater level.

However, secondary salinisation occurs when the concentration of dissolved salts in water and soil is increased by anthropogenic processes, mainly through poorly managed irrigation schemes. The threat of soil and groundwater salinisation induced by sea level rise and seawater intrusion are amplified by climate change Section … Areas for study include how to incentivise, regulate, and raise awareness of the co-benefits of healthy consumption patterns and climate change mitigation and adaptation; to improve access to healthy diets for vulnerable groups through food assistance programmes; and to implement policies and campaigns to reduce food loss and food waste. Knowledge gaps also exist on the role of different policies, and underlying uncertainties, to promote changes in food habits towards climate resilience and healthy diets. GHG emissions inventory techniques .Knowledge gaps include food consumption-based emissions at national scales, embedded emissions of food systems, comparison of GHG emissions per type of food systems , smallholder and large-scale commercial food systems, and GHG emissions from land-based aquaculture. An additional knowledge gap is the need for more socio-economic assessments of the potential of various integrated practices to deliver the mitigation potential estimated from a biophysical perspective. This needs to be effectively monitored, verified, and implemented, once barriers and incentives to adoption of the techniques, practices, and technologies are considered. Thus, future research needs fill the gaps on evaluation of climate actions in the food system. In summary, urban and peri-urban agriculture can contribute to improving urban food security, reducing GHG emissions, and adapting to climate change impacts . Food preference is an inherently cultural dimension that can ease or hinder transformations to food systems that contribute to climate change mitigation. Consumer choice and dietary preferences are guided by social, cultural, environmental, and traditional factors as well as economic growth. The food consumed by a given group conveys cultural significance about social hierarchy, social systems and human-environment relationships . Paustian developed a decision-tree for facilitating implementation of mitigation practices on cropland and described the features of key practices. They observed that most individual mitigation practices will have a small effect per unit of land, and hence they need to be combined and applied at large scales for their impact to be significant. Examples included aggregation of cropland practices and grazing land practices , grazing management, nutrient and fire management and species introduction that could increase net soil carbon stocks while reducing emissions of NO and CH. In this chapter, supply-side mitigation practices include land-use change and carbon

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