Iron is the fourth most abundant element in the Earth’s crust (following oxygen, silicon, and aluminum), and therefore, iron is a major constituent of all soils and sediments. During rock weathering at the Earth’s surface, iron forms secondary minerals with very small particle sizes and sometimes weak crystallinity. Since the element iron can be oxidized or reduced, it is also of fundamental importance in natural environments which are periodically anaerobic due to high water contents or flooding. Such environments include wetlands, river floodplains, estuaries, tidal flats, irrigated rice paddy soils, groundwater aquifers, and lake or marine shelf sediments. In recent decades, it has been established that biogeochemical redox processes can directly or indirectly lead to a complete recrystallization and/or transformation of iron minerals, which has important implications for understanding modern and past biogeochemical cycles of carbon, phosphorus, nitrogen, sulfur, and essential or potentially toxic trace elements. In these element cycles, iron minerals are important as sorbents and/or host phases for other elements, as electron acceptors or donors in biogeochemical redox reactions, and as catalysts of surface reactions with inorganic or organic compounds. Recently, the importance of poorly-crystalline iron oxyhydroxide minerals for organic carbon stabilization in soils and sediments has been recognized and is now receiving much attention because of its possible impact on global climate and soil fertility. In addition to natural environments, iron mineral transformation processes also play important roles in engineered systems (e.g. wastewater treatment, groundwater remediation, geological storage of nuclear waste), corrosion sciences, archaeology and cultural heritage sciences, and research on paleoclimate and the evolution of early Earth and Mars. Previous to the IRMIDYN project, iron mineral recrystallization and transformation processes and their influence on other element cycles had mostly been studied in strongly simplified laboratory systems. In-situ studies in soils and sediments were lacking because it is very challenging to detect poorly-crystalline minerals in small quantities in a soil matrix containing many other more crystalline minerals. Therefore, we developed new experimental approaches to study iron mineral transformations in-situ in soils and sediments in the field, making use of 57Fe as a stable isotope tracer combined with 57Fe Mössbauer spectroscopy providing information of Fe redox states and mineral structure. This new approach was tested in the lab and applied in field studies in the German Wadden Sea, rice paddy soils in Thailand, and organic-rich wetland soils in Iceland. These studies resulted in novel insights in iron mineral transformation processes in soils and sediments and consequences for nutrient and contaminant behavior. Our project including the new experimental approach developed was explained in a short documentary film available here:
https://www.youtube.com/watch?v=XFWnumTda5s(s’ouvre dans une nouvelle fenêtre).