Mineral sequestration, the disposal of carbon dioxide in the form of benign solid carbonate, provides a permanent and safe method of carbon dioxide disposal of virtually unlimited capacity. The objective of this project is to to develop a combination iron oxide production and carbon sequestration plant that will use serpentine ores as the source of iron and dispose of its own CO2. By using the same ore processing steps for carbon sequestration and iron ore production we increase the value of the carbon sequestration process and consequently reduce the cost of sequestration with this added value.Particularly important for justifying the feasibility of a combined iron production and mineral carbonation process for the mitigation of CO 2 generated by the iron and steel industry is the identification of locations where this process may be implemented. This identification is dependent both on the physical and chemical characteristics of the deposits themselves, as well as the current land-ownership and use in their location and proximity to iron processing plants and/or large sources of CO 2 . In this project we identify the locations of deposits, estimate the volume of mineral available, and summarize known geochemical data on major deposits as described in the geological literature.In developing the chemical pathways for a hydrometallurgical process we will further the identification of potential solvents. Finally, we will create a standardized process through which to characterize serpentine deposits in terms of carbon disposal capacity and iron and steel production capacity. 3
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Executive SummaryHere we propose to develop a combination iron oxide production and carbon sequestration plant that will use serpentine ores as the source of iron and dispose of its own CO 2 --plus additional CO 2 from other sources --in the mineral tailings that are left after iron is separated. By using the same ore processing steps for carbon sequestration and iron ore production we increase the value of the carbon sequestration process and consequently reduce the cost of sequestration with this added value.1. Geographical information system (GIS) datasets describing surface geology were obtained for the majority of ultramafic-containing states and used to estimate surface area exposure of serpentinite and ultramafic resources. Regional and nationwide datasets filled in gaps where statewide data is not available. Various land use datasets were integrated to account for areas such as urban centers and designated wilderness to eliminate locations where it will not be politically feasible to operate a mineral sequestration plant. The east coast ultramafic resource surface area is approximately 1086.44 km 2 . After filters for land-use are applied, there are 976.10 km 2 suitable reserves. The west coast resources are much greater, at 8,730 km 2 and reducing to 6677 km 2 after land use is taken into account. With depths of at least 500 m available for economic mining and using the density of serpentine (2.55 g/cm 2 ), reserv...