AI Article Synopsis

  • The study examines the cycling of iodine isotopes in forest ecosystems, revealing a compartment model with both labile and non-labile iodine pools.
  • The model indicates that soil acts as a primary sink for atmospheric iodine, with minimal long-term influence from tree vegetation, and shows equilibrium in iodine cycling occurring after approximately 5000 years.
  • Key processes like volatilisation significantly affect iodine storage and residence time in soil, necessitating improved estimates for factors like dry deposition to enhance predictions of iodine cycling in terrestrial environments.

Article Abstract

Differences in the source and behaviour of I compared to I isotopes have been described for a variety of surface environments, but little is known about the cycling rates of each isotope in terrestrial ecosystems. We developed a compartment model of the iodine cycle in a forest ecosystem, with a labile and non-labile pool to simplify the complex fate of iodine in the forest floor and soil. Simulations were performed using atmospheric I and I inputs for sites differing in climate, vegetation, and soil. In general, considering dry deposition in addition to wet deposition improved model simulations. Model results support the view that soil is the sink for atmospheric iodine deposited in forest ecosystems, while tree vegetation has little influence on long-term iodine budgets. Modelling also showed that iodine cycling reaches equilibrium after a period of about 5000 years, mainly due to a gradual incorporation of iodine into the bulk stabilised soil organic matter. At steady state, this pool of non-labile iodine in soil can retain about 20% of total deposition with a mean residence time of 900 years, while the labile iodine pool is renewed after 90 years. The proportions of modern anthropogenic I in each modelled pool reflect those of stable I at least several decades after input to the forest; this result explains why isotopic disequilibrium is common in field data analysis. Volatilisation plays a central role in regulating iodine storage in soil and, therefore, its residence time, while drainage is a minor export pathway, except at some calcareous sites. Dynamic modelling has been particularly helpful for gaining insight into the long-term response of iodine partitioning to continuous, single or even varying deposition. Our modelling study suggested that better estimates of dry deposition of atmospheric iodine, weathering of parent rock, and volatilisation of the deposited iodine from soil and vegetation will be required for reliable predictions of iodine cycling in specific forests, because these processes remain insufficiently explored.

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Source
http://dx.doi.org/10.1016/j.scitotenv.2022.154901DOI Listing

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