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Lal. Carbon Footprints 2026, 5, 10                                                Page 5 of 20





               Soil C, the sum of SOC and soil inorganic carbon (SIC), is the heart of soil health. In turn, soil health is the
               source of critical ESs, including food, energy, water, moderation of climate, etc. Thus, the strong
               interconnectivity that depends on soil C dynamics is also called the Food-Energy-Water-Soil (FEWS) nexus.
               Indeed, soil health (as moderated by its C content) is the most basic natural resource that is at the center of
               the FEWS nexus. The FEWS nexus is moderated by the coupled cycling of carbon, water, and nutrients. This
               coupling is sensitive to land use and management of soil and its disruption by anthropogenic activities. Such
               disruption can lead to soil degradation, land desertification, and the creation of disservices because of
               alterations in planetary processes. It is also this disruption that is the cause of the accelerated soil erosion,
               water eutrophication, emission of GHGs, the drought-flood syndrome, and decline in food production along
               with reduction in its nutritional quality and safety. Thus, soil C content must be maintained in the root zone
               at an optimal level (1.5% to 2.5% by weight) for provisioning of ESs for humans and nature.


               SOIL CARBON POOL AND GLOBAL WARMING
               The terrestrial C pool has two components: (1) soil C and (2) the biomass C. Together, these two pools
               contain ~2,870 Pg C, comprising 2,250 Pg of soil to 1 m depth and 620 Pg of biomass C. The soil C pool
               comprises two components: SOC (1,500 Pg) and SIC (750 Pg). The soil C pool is ~78% (2,250 Pg C out of
               2,870 Pg C) of the total terrestrial pool. The soil C pool can be a source or sink of atmospheric CO 2
               depending on land use and management and other natural or anthropogenic factors. Thus, the aim of land
               use and soil management is not only to decrease the source of GHGs but also to increase the C storage
               capacity by re-carbonization of the terrestrial biosphere. Indeed, the interaction between soil and biotic pools
               is affected by land use change, soil degradation, and drastic soil disturbance (deforestation, war and
               explosives, plowing, irrigation and use of agro-chemicals).

               The ACC may create positive feedback by aggravating an increase in the atmospheric C pool, and negative
               feedback by creating new sinks of atmospheric CO . The ACC can increase global warming by accelerating
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               decomposition and altering the composition of SOM. However, credible and verifiable assessment of the
               exact magnitude of increase in global warming is a major challenge. Thus, available information is highly
               variable. For example, Ofiti et al.  observed that 4.5 years of soil warming created divergent responses in
                                           [13]
               sub-soil (> 20 cm depth) compared to those in the surface soil. Melillo et al.  reported that soil warming has
                                                                              [14]
               the potential to alter both pedologic (soil) and biotic (plant) processes which can affect C stock in the
               terrestrial ecosystems (soil and vegetation). Melillo et al. also observed that soil warming increases losses
               from soil C pool but increases C stock in woody tissue of trees, probably due to increase in N availability .
                                                                                                        [14]
               Global warming also leads to increase in soil respiration through its effect on autotrophic and heterotrophic
               respiration. Schindlbacher et al.  observed similar responses of soil warming to both types of respiration.
                                          [15]
               However, the autotrophic component had a distinct seasonal pattern and was the highest during summer.


               SOIL MANAGEMENT PRACTICES WHICH SEQUESTER CARBON
               Plow-based methods of seedbed preparation and indiscriminate use of agro-chemicals can aggravate
               emissions from agro-ecosystems by degradation of soil and environment. Indeed, soil of agroecosystems can
               be a source or sink of GHGs depending on land use and soil/crop/water management. When prone to
               accelerated erosion and other degradation processes, soil is a source of GHGs. When the amount of C in
               sediments is buried, it can be a sink. However, the net effect over the entire pathway (from upper reaches of
               the watershed to the burial aquatic site) can make the erosion process a major but unknown source of GHGs.
               Similarly, agro-inputs and farm operations are also a major source, especially plowing, use of nitrogenous
               fertilizers, input of pesticides, grain drying, etc. Despite their importance in aggravating ACC, the precise or
               credible magnitude of emissions from farm operations is not known. For example, an excessive use of
               chemical fertilizers may aggravate soil degradation and increase GHG emissions. Wu et al.  observed that
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