Abstract

Abstract. Since the start of the industrial revolution, human activities have caused a rapid increase in atmospheric carbon dioxide (CO2) concentrations, which have, in turn, had an impact on climate leading to global warming and ocean acidification. Various approaches have been proposed to reduce atmospheric CO2. The Martin (or iron) hypothesis suggests that ocean iron fertilization (OIF) could be an effective method for stimulating oceanic carbon sequestration through the biological pump in iron-limited, high-nutrient, low-chlorophyll (HNLC) regions. To test the Martin hypothesis, 13 artificial OIF (aOIF) experiments have been performed since 1990 in HNLC regions. These aOIF field experiments have demonstrated that primary production (PP) can be significantly enhanced by the artificial addition of iron. However, except in the Southern Ocean (SO) European Iron Fertilization Experiment (EIFEX), no significant change in the effectiveness of aOIF (i.e., the amount of iron-induced carbon export flux below the winter mixed layer depth, MLD) has been detected. These results, including possible side effects, have been debated amongst those who support and oppose aOIF experimentation, and many questions concerning the effectiveness of scientific aOIF, environmental side effects, and international aOIF law frameworks remain. In the context of increasing global and political concerns associated with climate change, it is valuable to examine the validity and usefulness of the aOIF experiments. Furthermore, it is logical to carry out such experiments because they allow one to study how plankton-based ecosystems work by providing insight into mechanisms operating in real time and under in situ conditions. To maximize the effectiveness of aOIF experiments under international aOIF regulations in the future, we therefore suggest a design that incorporates several components. (1) Experiments conducted in the center of an eddy structure when grazing pressure is low and silicate levels are high (e.g., in the SO south of the polar front during early summer). (2) Shipboard observations extending over a minimum of ∼40 days, with multiple iron injections (at least two or three iron infusions of ∼2000 kg with an interval of ∼10–15 days to fertilize a patch of 300 km2 and obtain a ∼2 nM concentration). (3) Tracing of the iron-fertilized patch using both physical (e.g., a drifting buoy) and biogeochemical (e.g., sulfur hexafluoride, photosynthetic quantum efficiency, and partial pressure of CO2) tracers. (4) Employment of neutrally buoyant sediment traps (NBST) and application of the water-column-derived thorium-234 (234Th) method at two depths (i.e., just below the in situ MLD and at the winter MLD), with autonomous profilers equipped with an underwater video profiler (UVP) and a transmissometer. (5) Monitoring of side effects on marine/ocean ecosystems, including production of climate-relevant gases (e.g., nitrous oxide, N2O; dimethyl sulfide, DMS; and halogenated volatile organic compounds, HVOCs), decline in oxygen inventory, and development of toxic algae blooms, with optical-sensor-equipped autonomous moored profilers and/or autonomous benthic vehicles. Lastly, we introduce the scientific aOIF experimental design guidelines for a future Korean Iron Fertilization Experiment in the Southern Ocean (KIFES).

Highlights

  • Since the start of the industrial revolution, human activities have caused a rapid increase in atmospheric carbon dioxide (CO2, a major greenhouse gas) from ∼ 280 ppm to ∼ 400 ppm, which has, in turn, led to global warming and ocean acidification, indicating that there is an urgent need to reduce global greenhouse gas emissions (IPCC, 2013) (Fig. 1)

  • In the equatorial Pacific (EP), initial surface partial pressure of CO2 values were 504.5 ± 33.5 μatm, which were much higher than those observed in the SO (355.6 ± 11.7 μatm) or the subarctic North Pacific (NP) (370.0 ± 16.3 μatm) (Table 3) (Steinberg et al, 1998). 2.2.2 Southern Ocean The initial physical conditions for the artificial OIF (aOIF) experiments in the SO (SOIREE, EisenEx, SOFeX-N, SOFeX-S, European Iron Fertilization Experiment (EIFEX), SAGE, and LOHAFEX) were very different from those found in the EP; mixed layer depth (MLD) were much deeper (57.9 ± 19.2 m)

  • 50 Drifting trap 100 Drifting trap 40 Drifting trap 100 Drifting trap a Export flux in EIFEX was digitized from the Supplement Fig. 5.1 of Smetacek et al (2012). b Export flux in LOHAFEX was digitized from the Fig. 4 of Martin et al (2013). c Export flux in LOHAFEX was digitized from the Fig. 6 of Martin et al (2013). d Export flux in SEEDS-1 was determined from the suspended particles. e Export flux in Subarctic Ecosystem Response to Iron Enrichment Study (SERIES) was digitized from the Fig. 2 of Boyd et al (2004)

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Summary

Introduction

Since the start of the industrial revolution, human activities have caused a rapid increase in atmospheric carbon dioxide (CO2, a major greenhouse gas) from ∼ 280 ppm (pre-industrial revolution) to ∼ 400 ppm (present day) (http: //www.esrl.noaa.gov/, last access: 6 September 2018), which has, in turn, led to global warming and ocean acidification, indicating that there is an urgent need to reduce global greenhouse gas emissions (IPCC, 2013) (Fig. 1). To test Martin’s hypothesis, six natural OIF (nOIF) and 13 artificial OIF (aOIF) experiments have been performed to date in the subtropical North Atlantic (NA), EP, subarctic NP, and SO (Blain et al, 2007, 2015; Boyd et al, 2007; Pollard et al, 2009; Strong et al, 2009; Smetacek et al, 2012; Martin et al, 2013) (Fig. 4a and Table 1) These OIF experiments demonstrated, for the SO, that PP could be significantly increased after iron addition (de Baar et al, 2005; Boyd et al, 2007). Added iron(II) Initial iron Target iron Tracer Patch size Duration Regional characteristics (kg) (day)

KEOPS-2c
Past: overview of previous aOIF experiments
Equatorial Pacific
Southern Ocean
IronEx-1
SOFeX-N
LOHAFEX
Subarctic North Pacific
Subtropical North Atlantic
SOFeX-S 7 EIFEX
Iron addition
Tracing iron-fertilized patch
Biogeochemical responses
50 Water-column 234Thd 100 Drifting trap 200 Water-column 234Th
Summary of the significant results from aOIF experiments
Export flux measurement methods
Considering environmental side effects
Regulation of aOIF: international law of the sea as it applies to aOIF
Future: designing future aOIF experiments
Year one plan
A plan for the future
Year three plan
Objective
Year five plan
Final remark
Findings
Summary
Full Text
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