Abstract

Abstract. Atmospheric deposition of iron (Fe) plays an important role in controlling oceanic primary productivity. However, the sources of Fe in the atmosphere are not well understood. In particular, the combustion sources of Fe and the subsequent deposition to the oceans have been accounted for in only few ocean biogeochemical models of the carbon cycle. Here we used a mass-balance method to estimate the emissions of Fe from the combustion of fossil fuels and biomass by accounting for the Fe contents in fuel and the partitioning of Fe during combustion. The emissions of Fe attached to aerosols from combustion sources were estimated by particle size, and their uncertainties were quantified by a Monte Carlo simulation. The emissions of Fe from mineral sources were estimated using the latest soil mineralogical database to date. As a result, the total Fe emissions from combustion averaged for 1960–2007 were estimated to be 5.3 Tg yr−1 (90% confidence of 2.3 to 12.1). Of these emissions, 1, 27 and 72% were emitted in particles < 1 μm (PM1), 1–10 μm (PM1-10), and > 10 μm (PM> 10), respectively, compared to a total Fe emission from mineral dust of 41.0 Tg yr−1 in a log-normal distribution with a mass median diameter of 2.5 μm and a geometric standard deviation of 2. For combustion sources, different temporal trends were found in fine and medium-to-coarse particles, with a notable increase in Fe emissions in PM1 since 2000 due to an increase in Fe emission from motor vehicles (from 0.008 to 0.0103 Tg yr−1 in 2000 and 2007, respectively). These emissions have been introduced in a global 3-D transport model run at a spatial resolution of 0.94° latitude by 1.28° longitude to evaluate our estimation of Fe emissions. The modelled Fe concentrations as monthly means were compared with the monthly (57 sites) or daily (768 sites) measured concentrations at a total of 825 sampling stations. The deviation between modelled and observed Fe concentrations attached to aerosols at the surface was within a factor of 2 at most sampling stations, and the deviation was within a factor of 1.5 at sampling stations dominated by combustion sources. We analysed the relative contribution of combustion sources to total Fe concentrations over different regions of the world. The new mineralogical database led to a modest improvement in the simulation relative to station data even in dust-dominated regions, but could provide useful information on the chemical forms of Fe in dust for coupling with ocean biota models. We estimated a total Fe deposition sink of 8.4 Tg yr−1 over global oceans, 7% of which originated from the combustion sources. Our central estimates of Fe emissions from fossil fuel combustion (mainly from coal) are generally higher than those in previous studies, although they are within the uncertainty range of our estimates. In particular, the higher than previously estimated Fe emission from coal combustion implies a larger atmospheric anthropogenic input of soluble Fe to the northern Atlantic and northern Pacific Oceans, which is expected to enhance the biological carbon pump in those regions.

Highlights

  • Sea-water dissolved iron (Fe) concentration is a primary factor that limits or co-limits the growth of phytoplankton in large regions of the global oceans (Martin et al, 1991; Moore et al, 2013)

  • The Fe concentrations attached to aerosols in surface air simulated for pixels of 0.94◦ latitude by 1.28◦ longitude were evaluated by 529 measurements obtained between 1990 to 2007

  • Similar to the distribution of annual mean Fe concentrations attached to aerosols in surface air (Fig. 6), the spatial distribution of Fe deposition was dominated by mineral sources

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Summary

Introduction

Sea-water dissolved iron (Fe) concentration is a primary factor that limits or co-limits the growth of phytoplankton in large regions of the global oceans (Martin et al, 1991; Moore et al, 2013). Observed concentrations of soluble Fe were not properly captured by the models simulating the atmospheric transport, chemical processing and deposition of Fe in aerosols (Hand et al, 2004; Luo et al, 2005; Fan et al, 2006), suggesting the existence of other sources. Nickovic et al (2012) developed a global data set to represent the mineral composition of soil in arid and semi-arid areas This mineralogical data set improved the agreement between simulated and measured concentrations of soluble Fe (Nickovic et al, 2013; Ito and Xu, 2014). Journet et al (2014) developed a new data set of soil mineralogy (including soil Fe content) covering most dust source regions of the world at a resolution of 0.5◦ × 0.5◦, with the aim to improve the modelling of the chemical forms of Fe in dust. The impact of the estimated combustion-related and mineral emissions of Fe on the model–data misfits at 825 stations measuring Fe concentration in surface aerosol and 30 stations measuring Fe deposition was investigated for different regions and stations

Emissions of Fe from combustion sources
Fe content in fuel
Partitioning of Fe in combustion
Spatial allocation of Fe emissions from combustion
Uncertainty of Fe emissions from combustion
Emissions of Fe from mineral sources
Modelling the atmospheric transport and deposition of Fe aerosols
Emissions of Fe from combustion
Spatial distributions of Fe emissions from combustion sources
Temporal trends of Fe emissions from combustion sources
Mineral sources of Fe
Comparison of Fe emissions with previous studies
Spatial distribution of Fe concentrations in surface air
Evaluation of Fe concentrations in surface air
Fe concentrations over the Atlantic Ocean
Role of the combustion sources
Effect of the new mineralogical database
Size distributions of Fe-containing particles
Global Fe deposition
Global atmospheric Fe budget
Influence of different Fe solubilities from different sources
Summary and conclusion
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