An improved knowledge of iron biogeochemistry is needed to better understand key controls on the functioning of high-nitrate low-chlorophyll (HNLC) oceanic regions. Iron budgets for HNLC waters have been constructed using data from disparate sources ranging from laboratory algal cultures to ocean physics. In summer 2003 we conducted FeCycle, a 10-day mesoscale tracer release in HNLC waters SE of New Zealand, and measured concurrently all sources (with the exception of aerosol deposition) to, sinks of iron from, and rates of iron recycling within, the surface mixed layer. A pelagic iron budget (timescale of days) indicated that oceanic supply terms (lateral advection and vertical diffusion) were relatively small compared to the main sink (downward particulate export). Remote sensing and terrestrial monitoring reveal 13 dust or wildfire events in Australia, prior to and during FeCycle, one of which may have deposited iron at the study location. However, iron deposition rates cannot be derived from such observations, illustrating the difficulties in closing iron budgets without quantification of episodic atmospheric supply. Despite the threefold uncertainties reported for rates of aerosol deposition (Duce et al., 1991), published atmospheric iron supply for the New Zealand region is ∼50-fold (i.e., 7- to 150-fold) greater than the oceanic iron supply measured in our budget, and thus was comparable (i.e., a third to threefold) to our estimates of downward export of particulate iron. During FeCycle, the fluxes due to short term (hours) biological iron uptake and regeneration were indicative of rapid recycling and were tenfold greater than for new iron (i.e. estimated atmospheric and measured oceanic supply), giving an “fe” ratio (uptake of new iron/uptake of new + regenerated iron) of 0.17 (i.e., a range of 0.06 to 0.51 due to uncertainties on aerosol iron supply), and an “Fe” ratio (biogenic Fe export/uptake of new + regenerated iron) of 0.09 (i.e., 0.03 to 0.24).
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 So far, many of our insights into iron biogeochemistry have come from shipboard and mesoscale iron perturbation experiments [Rue and Bruland, 1997; Bowie et al., 2001; Croot et al., 2001]. However, clearly there is now a need for an experimental approach that measures concurrently the pools and fluxes within the biogeochemical iron cycle without perturbing the HNLC condition. The tracer sulphur hexafluoride (SF6) provides an appropriate tool to conduct such an experiment, and has been used to explore the physics and chemistry of the unperturbed ocean during eddy studies [Law et al., 2001]. The use of the SF6 tracer, along with the timely advent of new approaches such as iron bioreporters [Mioni et al., 2003] and a trace metal clean wash to remove extracellularly bound iron from particles [Tovar-Sanchez et al., 2003], provide an appropriate “technological” platform for such a study.
 Our experiment, FeCycle, took place over 10 days in summer 2003 within an unperturbed (i.e., no iron addition) SF6 labeled patch of HNLC ocean SE of New Zealand. The aim of FeCycle was to obtain concurrent measurements of the key sources and sinks of new iron to the surface mixed layer, and also estimates of biological iron uptake and recycling within the SF6 labeled waters. This overview (1) provides a broader temporal and spatial context for the FeCycle study using remotely sensed atmospheric and oceanic observations and (2) summarizes and synthesizes the main findings of FeCycle. The latter rely on the construction of iron biogeochemical budgets on two timescales (hours, days) for the surface ocean from detailed studies in the FeCycle special section. They focus on: mixed layer and sinking particulate iron dynamics [Frew et al., 2005], iron bioavailability to heterotrophic bacteria [Mioni et al., 2005], iron acquisition mechanisms by plankton [Maldonado et al., 2005], algal iron dynamics [McKay et al., 2005], and the role of the microbial foodweb in iron recycling [Strzepek et al., 2005]. Other data are provided on upper ocean physics and chemistry from P. L. Croot et al. (The effects of physical forcing on iron chemistry and speciation during the FeCycle experiment in the South West Pacific, submitted to Marine Chemistry, 2005) (hereinafter referred to as Croot et al., submitted manuscript, 2005).
2. Study Site and Methods
 Prior to the FeCycle voyage we identified potential sites SE of New Zealand that had HNLC characteristics (Figure 1a). Site selection was refined to one (S. Mooring site, Figure 1a) as it had the most appropriate physical conditions (e.g., away from eddy activity) for a mesoscale tracer release. Site suitability was tested during a survey from 30 January to 1 February 2003, which comprised XBT releases interspersed with CTD casts to 1 km depth. Underway sampling from pumped seawater supply (5 m depth) provided maps of temperature, salinity (Seabird thermosalinograph), chlorophyll (Turner fluorometer), photosynthetic competence (Fv/Fm) [after Boyd and Abraham, 2001], dissolved nutrients [Frew et al., 2001] and dissolved iron (DFe) (using a clean tow-fish at 4 m depth after Bowie et al. ). The survey found an appropriate site at 178.72°E 46.24°S (auxiliary material table ts01 and Figure 1b), and the SF6 release commenced at 0200 local time (LT) on 2 February 2003.
 The tracer release into the surface mixed layer followed procedures of Law et al.  and took 12 hours to add SF6 over ∼49 km2 (Figure 2a and auxiliary material figure fs01) at a release depth of 7 m. No iron was added along with the SF6. Immediately following the tracer release, the areal extent of the labeled waters was assessed by underway mapping of the patch. Day 1 of FeCycle was nominally defined as 3 February 2003, and the 10-day study concluded on 12 February.
 During FeCycle we conducted several sampling strategies at the patch center (defined as the highest SF6 concentrations) including budget (on 4 days), depth-resolved (1 day) and diel sampling (2 days). FeCycle concluded with a detailed lateral transect of the patch. Each sampling period was interspersed with overnight mapping of the areal extent of the patch and concurrent sampling of lateral gradients in upper ocean properties. Water sampling on budget days took place at one depth (20 m) and shortly after local dawn when nighttime convective overturn would ensure a truly “mixed” layer for several hours [MacIntyre, 1998] before any solar heating influenced the structure of the upper ocean [McNeil and Farmer, 1995].
 All water was obtained using a trace-metal clean fish in conjunction with trace-metal clean polyethylene tubing and a Teflon pump [Hutchins et al., 1998] with a plastic pressure logger attached near the underwater intake. This system enabled all samples required for the budget to be obtained in <3 hours. Specific details of the sampling and analytical protocols for particulates, phytoplankton, iron chemistry and microbial components of this budget are presented by Frew et al. , Ellwood , McKay et al. , and Strzepek et al. , respectively.
 Other sampling during FeCycle included measuring particulate iron (PFe) flux exiting the upper ocean, and atmospheric iron deposition into the ocean. Export estimates were obtained by deploying two trace metal “clean” surface-tethered free-drifting sediment trap arrays for 7 days at 80 and 120 m depth [Frew et al., 2005]. Export flux was corrected for Fe contamination, using procedural blanks (20% or less of the PFe fluxes) taken from replicate sediment trap tubes [Frew et al., 2005]. On two occasions, dust was sampled using a filtration unit located on a mast (10 m above sea level) on the bow, on both the outward north-south leg (29/30 January from Wellington, 175°E 41°S) to the FeCycle site, and the return south-north leg (12/13 February). These >24-hour transit times were the only periods sufficient duration to sample aerosols in this relatively low dust deposition region [Jickells and Spokes, 2001]. For sampling details, see the auxiliary materials.
 Here we present two types of iron budgets: a long-term (i.e., days, focusing on sources of new iron and iron sinks) and a short-term budget (i.e., hours, based on biological iron uptake and recycling). In the latter we have expressed the pools and fluxes as mixed layer column integrals, even though in some cases data were available only from one depth, as they were sampled from a “truly” mixed layer. The short term budgets are “snapshots” in time and space (on days 2, 3, 4 and 7), and have been related to depth-resolved (day 6) and diel (days 5 and 9) sampling [McKay et al., 2005]. On several occasions, due to logistical issues, we have combined data within a daily budget that were obtained on different days during FeCycle; our rationale for this is the relative constancy from day to day in biological properties [Strzepek et al., 2005].
 The long term budget comprised four terms; three iron sources (two oceanic and one atmospheric) and one iron sink (downward PFe flux). Estimates of the oceanic terms (vertical diffusive and lateral advective iron supply) were obtained from the exchange between the SF6 labeled patch and both the surrounding and underlying waters (Figure 2 and auxiliary material figure fs01) and related to horizontal (Croot et al., submitted manuscript, 2005) and vertical gradients (Figure 3) in DFe.
3.1. Physical Evolution of the FeCycle Patch
 Initial mapping revealed that the patch was coherent, had an areal extent of ∼47 km2 (Figure 2a), and high SF6 concentrations (>300 fmol L−1, Figure 2b). The surface mixed layer depth, as indicated by a minimum in N2, the buoyancy frequency, was 40–50 m, although SF6 was initially restricted to 20 m by shallow isopycnals and deepened over days 1–3 to 40 m (Figure 2b). The subsequent development of vertical variation in the patch extent from day 5 (Figure 2b) restricted estimation of the vertical diffusivity (Kz) from SF6 profiles to days 1–4 only. This was achieved by fitting second-moment integrals to the SF6 distribution [Law et al., 2003] from 40 m, to obtain a Kz of 0.66 ± 0.11 cm2 s−1. This is comparable with estimates from other SF6 experiments, exceeding Kz estimates from the Southern Ocean, (0.11 ± 0.2 cm2 s−1 [Law et al., 2003]), and equatorial Pacific (0.25 cm2 s−1 [Law et al., 1998]), and intermediate between estimates from the North Atlantic (0.3 ± 0.2 cm2 s−1 [Kim et al., 2005]; 2.93 ± 0.42 cm2 s−1 [Law et al., 2001]). A Kz range of 0.05–3 cm2 s−1 was indirectly estimated from N2 for FeCycle after day 4 (Croot et al., submitted manuscript, 2005), from a tracer-derived Kz-N2 parameterization using data presented by Law et al. .
 From day 5, vertical variability in the patch extent developed in response to the formation of thermal structure and resultant shear in the mixed layer (Figure 2b). The patch developed into a filament of constant width (7 km) and exponentially increasing length (γ = 0.17 ± 0.03 d−1(n = 8, R = 0.90), as previously observed in other tracer experiments dominated by strain flow [Law et al., 2003]. As the patch evolved it increased in area by 0.17 d−1 to >400 on day 10, and thus may have impacted the iron biogeochemical budgets by both entraining surrounding waters which had slightly different biological signatures (Figure 1b), and altering the physical gradients in the upper ocean (Figure 2b). Changes in tracer layer depths (TLDs) were due to lateral shear events, associated with transient thermal structures within the seasonal mixed layer, whereas the lateral entrainment of water into the patch was mainly driven by shear, strain and rotation.
 The impact of lateral entrainment on the FeCycle study is evident from SeaWiFS chlorophyll time series (auxiliary material figure fs02). These data sets indicate that chlorophyll concentrations were typically HNLC (0.2–0.3 μg L−1) on both day 1 and 3 in the vicinity of the patch. However, after day 4, there were higher chlorophyll concentrations in the waters surrounding the patch (up to >1.0 μg chl L−1 on day 8) and also inside the patch. These elevated chlorophyll concentrations in the patch were due to either lateral entrainment of waters with higher chlorophyll concentrations or local in situ algal growth. Evidence from FeCycle supports the former mechanism, since there was no significant change in Fv/Fm (0.25) during our study [McKay et al., 2005]; Fv/Fm would have increased prior to any increase in chlorophyll concentrations [Boyd and Abraham, 2001]. Similarly, there was no increase in primary production rates (auxiliary material table ts01). Owing to the complex lateral mixing between the patch and the heterogeneous chlorophyll field evident in the surrounding waters (auxiliary material figures fs01 and fs02) entrainment of higher chlorophyll waters cannot be clearly demonstrated. However, application of the patch dilution rate (Croot et al., submitted manuscript, 2005) to the chlorophyll gradient between the patch center and waters outside confirms that lateral entrainment would account for a doubling of chlorophyll in the patch between day 3 and day 8–9, without the necessity for in situ algal growth.
 The initial biological and chemical properties of the patch (auxiliary material table ts01) indicate that it was HNLSiLC (high-nitrate low–silicic acid low-chlorophyll [Dugdale and Wilkerson, 1998]), rather than HNLC, as is expected in these waters during summer [Boyd, 2002b]. The FeCycle patch was dominated by picophytoplankton, and the algal community exhibited low values of Fv/Fm probably due to the picomolar DFe concentrations at this site (Figure 3), and as reported by Boyd et al. [1999, 2004b]. In general, there was no significant change in nutrient concentrations, phytoplankton composition, or Fv/Fm during FeCycle [McKay et al., 2005].
3.2. Short-Term Iron Budgets
 Four mixed layer budgets were constructed based on size fractions for pico- (0.2–2 μm), nano- (2–5 μm and 5–20 μm) and micro-plankton (>20 μm) after Sieburth et al. . For simplicity, we report only the mixed layer column integrated pool size (from size-fractionated PFe [Frew et al., 2005]), and the fluxes of iron into (biological uptake [McKay et al., 2005]) and out of (biological iron regeneration [Strzepek et al., 2005]) each pool. In each budget, several key trends are consistently observed (Figure 4 and auxiliary material figures fs03 to fs05): (1) the dominance of the bulk PFe pool by particles >20 μm, with a decreasing contribution to total PFe with decreasing size; (2) the greatest contribution to biological iron uptake by the <2-μm fraction, with a decrease in iron uptake generally observed with increasing size; (3) the biologically mediated iron regeneration was comparable for both the heterotrophic bacterial (0.2–0.8 μm) and algal (0.8–8 μm) fractions; (4) the rates of biological iron uptake and regeneration were of the same order; and (5) the pool turnover times for each size class (despite some gaps in each budget) were fastest for the <2-μm fraction (1–3 days based on Fe uptake), and increased with increasing size. Day-to-day variations in the PFe pool size were twofold or less for each size fraction [Frew et al., 2005]. Iron uptake rates for each pool generally showed less than twofold variations (Figure 4 and auxiliary material figures fs03 to fs05), and the results of both grazer-mediated iron regeneration experiments were in particularly close agreement [Strzepek et al., 2005]. In contrast, virally mediated iron regeneration rate estimates ranged from 0.4 to 28 pmol L−1 d−1 [Strzepek et al., 2005] and were not included within the daily budgets, where steady state was assumed.
 The trends observed in the short-term budgets can be related to the variability in environmental conditions over FeCycle. With the exception of chlorophyll concentrations, there were only small fluctuations in most of the biological and chemical properties with phytoplankton dominated by <2-μm cells (auxiliary material table ts01). There were twofold ranges in TLDs and incident PAR over the study (auxiliary material table ts02). The variations in TLDs reflected the dynamic nature of the upper 40 m within the seasonal mixed layer that occur over day-week timescales, as much smaller changes in the seasonal mixed layer depth were recorded (Figure 2 caption). Hence the underwater light climate (set by incident irradiance, light attenuance and mixed layer depth) varied little, resulting in less than twofold variations in column-integrated net primary production (auxiliary material table ts01) and iron uptake rates (auxiliary material table ts02). Thus the rates and pools measured during the short-term iron budgets are probably broadly representative of the entire study.
3.3. Long-Term Iron Budget
 All iron pools and long-term fluxes measured during FeCycle are presented in Table 1. Lateral advective iron supply was negligible during the 10-day study, and aerosol iron deposition, on the two occasions it was measured, was zero (i.e., identical to the filter blanks). The vertical diffusive supply term was small mainly due to weak vertical gradients in DFe across the pycnocline (0.66 nmol Fe m−4 (Figure 3); compared to 0.26 mmol NO3 m−4 [McKay et al., 2005]) as opposed to the low computed values of Kz. The sole loss term from the mixed layer was PFe export flux which was 15- to 30-fold greater than the total iron supply over FeCycle. Despite this apparent imbalance, there were no significant changes in the mixed layer PFe inventory [Frew et al., 2005]. The daily export flux represents around 1% of the PFe inventory in the mixed layer (Table 1), giving a turnover time of the PFe pool of 100 days. The PFe export term can be divided into biogenic (∼60%) and lithogenic (∼40%) (Table 1). There was no evidence of upwelling (based on density, SF6 and nutrient data sets) in the vicinity of our site. It appears that although we have measured all of the source and sink terms in the long-term budget there is a marked imbalance between iron supply and removal. Moreover, as most PFe supply will be lithogenic in origin, such as lateral advection or dust deposition [Jickells and Spokes, 2001], the budget is also not balanced with respect to biogenic PFe, since it represents 60% of PFe export.
Table 1. Summary of Iron Pools and Long-Term Iron Fluxes (and Standard Deviations) Measured During FeCyclea
Inventories of DFe (Figure 3) and PFe [Frew et al., 2005] for the surface mixed layer. The lateral exchange of DFe between the patch (surface mixed layer) and the surrounding waters was based on a Ky estimated from the strain rate of the SF6 labeled patch and DFe data from a lateral survey of the patch (Croot et al., submitted manuscript, 2005). The vertical diffusive supply was derived from the Fe gradient across the pycnocline (Figure 3) and a Kz from Law et al. . The lithogenic contribution was calculated from an Fe:Al crustal ratio (molar) of 0.18 (based on analysis of Australian dust samples [Frew et al., 2005]). Here nd denotes “no data.”
Pools, μmol m−2
4 ± 1
31 ± 7
Fluxes, nmol m−2d−1
Vertical advective Fe supply
15 ± 3
Lateral advective Fe supply
0 ± 2
Aerosol Fe deposition rate
Downward PFe flux
216 ± 27 to 548 ± 128
Downward lithogenic PFe flux
77 ± 7 to 196 ± 9
Downward biogenic PFe flux
139 ± 31 to 352 ± 123
3.4. Dust Activity Prior To and During FeCycle
 The supply of iron from dust deposition is often intermittent [Jickells and Spokes, 2001] and in the Australasian region is linked to dust storm activity [Middleton, 1984]. Between 1 January 2003 and 12 February 2003 there was evidence, from environmental monitoring stations in Australia [McTainsh, 1998], of 13 dust events in the arid and semi-arid regions of Australia (auxiliary material table ts03). Backward air mass trajectory analysis indicates that the provenance of hypothetical air parcels passing through the FeCycle site (FeCycle was from year days 34–43) was mainly marine from polar (year days 25, 26, 35–39) or subpolar (year days 26–43) regions south or west of this site (Figure 5). On year days 32 and 33, and 40 to 43, there was evidence of air that had previously transitted over subtropical waters passing through the FeCycle site. There were also several occasions (year days 27, 32–34, 38 and 40) when air from over the Australian subcontinent was subsequently transported in the vicinity of our site (Figure 5). Moreover, on year day 33 there was evidence of several dust storms in eastern Australia (auxiliary material table ts03), and on year day 37 and 38 of elevated aerosol concentrations to the east of New Zealand that extended over subpolar waters south of the FeCycle site (Figure 6). Both of our dust sampling measurements (year days 29/30 and 44/45) coincided with periods when the provenance of air was from the subpolar regions (Figure 5). It is therefore likely that they were not representative of rates of dust deposition during FeCycle (see Figure 6).
4.1. How Representative Was FeCycle?
 The study site was 45 km north of a site in subpolar waters in which both the biota [Bradford-Grieve et al., 1999], and physico-chemical properties of the upper ocean [Boyd et al., 2004a; Nodder et al., 2005] have been characterized throughout the annual cycle. A comparison of the initial conditions during FeCycle (auxiliary material table ts01) with those from this neighboring site [Boyd et al., 1999, 2004b] are favorable with low DFe concentrations, low Fv/Fm and a picophytoplankton-dominated community. During FeCycle, chlorophyll doubled in the SF6 labeled waters to 0.6 μg L−1 over 5 to 6 days [McKay et al., 2005]. There is evidence, from the regional chlorophyll climatology, of increased concentrations in late summer (Figure 1a). For the period 1997 to 2000, there is no compelling explanation for this trend, although Boyd et al. [2004b] put forward a putative mechanism involving episodic north-south transport of subtropical waters associated with the local bathymetry. Thus conditions during FeCycle are representative for summer in these HNLCLSi waters.
 Most of the iron inventories and flux data obtained for both the long- and short-term budgets have not previously been measured in the waters SE of New Zealand. Thus it is difficult to comment on how representative they were. However, it is possible to compare the magnitude of bulk fluxes (such as particulate organic carbon (POC) export flux) measured during FeCycle with other seasons for this site. Our estimate of downward POC export was comparable to fluxes (at a similar depth) in April 1996 [Nodder and Alexander, 1999] and January 2000 (S. Nodder, unpublished data, 2002). Furthermore, a comparison of trends in mass and POC export flux at 1.5 km depth from an annual time series indicate that export fluxes in February (i.e., the time period of FeCycle) are similar to those over spring and summer suggesting that our POC fluxes are representative of much of the annual cycle. Given the constancy of the downward mass and POC fluxes over most of the annual cycle [Nodder et al., 2005] it is likely that downward PFe fluxes will be similar over spring and summer, unless there are marked seasonal changes in the Fe:C ratios of settling particles.
 Other trends in FeCycle, such as the close coupling of algal growth and herbivory [Strzepek et al., 2005], the constancy of the HNLC condition, and the dominance of small algal cells [McKay et al., 2005] have been previously recorded [Bradford-Grieve et al., 1999; Boyd et al., 1999] suggesting that rapid iron recycling will characterize much of the annual cycle. Temporal trends in DFe profiles at this site indicate that they have a small seasonal amplitude, and weak gradients across the pycnocline (Figure 3). The characteristics of these profiles are similar to that reported in summer for subantarctic waters south of Australia by Sedwick et al. . However, when compared to trends in macronutrients [McKay et al., 2005] the gradients in DFe (0.66 nmol Fe m−4) and nitrate (0.26 mmol NO3 m−4) supply across the pycnocline during FeCycle yield a molar supply ratio of 2.5 × 10−6 (i.e., several orders of magnitude lower than planktonic Fe:N molar ratios [Martin et al., 1989]. It is not possible to predict how winter overturn will influence the vertical supply of DFe, although the small vertical DFe gradients over the upper 150 m suggest that vertical diffusive supply of iron will remain low over much of the annual cycle.
4.2. Iron Uptake and Recycling: Short-Term Iron Budgets
 Iron recycling through the microbial foodweb is reported to take place on a timescale of hours by both micro- [Barbeau and Moffett, 2000] and meso-zooplankton [Hutchins and Bruland, 1994]. Hence we conducted four daily budgets to measure the fluxes due to iron uptake and regeneration. Despite some missing terms, there are three main trends for each budget: first the >20 μm fraction consistently had the largest PFe pool (97 ± 3% of PFe was lithogenic [Frew et al., 2005]) but the smallest fluxes (iron uptake). In contrast, the 0.2- to 2-μm fraction had the largest fluxes and the smallest PFe pool (68 ± 6% of PFe was lithogenic). The biogenic pool comprised around 15% of total PFe pool, as estimated independently by Frew et al.  and Strzepek et al. . Strzepek et al. report that the <2-μm fraction made the largest contribution to this biogenic pool. PFe:POC molar ratios were ∼40 for FeCycle [Frew et al., 2005], but after correction for the lithogenic component, were 5–6, similar to those for HNLC Southern Ocean waters [Twining et al., 2004a, 2004b].
 Second, the uptake of iron in most of the size fractions during FeCycle was comparable to its rate of recycling for each budget day, indicative of active mobilization of a large proportion of the iron in each of the four size fractions. Bowie et al.  also reported this trend for the SOIREE mesoscale iron enrichment in the Southern Ocean, suggesting that regardless of the size of the iron inventory there is always rapid recycling. During FeCycle, both the herbivore and bacterivore-mediated rates of regeneration were similar and relatively constant (15–20 pmol L−1 d−1), whereas virally mediated iron regeneration ranged by 70-fold (0.4–28 pmol L−1 d−1) [Strzepek et al., 2005]. The grazer-mediated iron regeneration rates (33–44 pmol L−1 d−1) for FeCycle were comparable to those reported by Bowie et al.  (19 pmol L−1 d−1, SOIREE), but were fourfold higher than in the HNLC NE subarctic Pacific [Price and Morel, 1998].
 The third trend during FeCycle was of biogenic pool turnover times for each budget on the order of 1 day (i.e., hours) to weeks, with the fastest turnover times for the cells <2 μm. The PFe pool turnover times are faster (biogenic pool, hours to a few days) after correction for the lithogenic PFe component of the pool for each size class, whereas the lithogenic pools have much longer turnover times of weeks [Frew et al., 2005]. The fast turnover times of the biogenic PFe pools during each of the four budget days of FeCycle are comparable to those reported from both laboratory [Hutchins et al., 1995] and field studies [Tortell et al., 1999; Bowie et al., 2001].
 No previous biogeochemical study has constructed multiple iron budgets, based on repeat sampling over several days, and so no other comparisons are available. The consistency in the trends from the FeCycle short-term budgets is probably due to the relatively low fluctuations in environmental conditions that might influence iron biogeochemistry. Such conditions include solar forcing and its impact on photolysis and iron redox cycling [Barbeau and Moffett, 2000], photosynthesis [McNeil and Farmer, 1995], diel patterns in grazer dynamics [Fuhrman et al., 1985] and viral damage due to photolysis [Wilhelm et al., 1998]. During FeCycle, both daily incident irradiances (27 to 45 mol quanta m−2 d−1), and TLDs (25–45 m) ranged by less than twofold, compared with previous voyages in this region where fourfold variations in daily incident irradiances were recorded (P. W. Boyd, unpublished data, 2004).
 The balancing of biological iron uptake and regeneration within the “ferrous wheel” [Kirchman, 1996] in the mixed layer provides insights into questions raised by Strom et al. : What sets HNLC chlorophyll concentrations at ∼0.3 μg L−1, and how is the HNLC condition maintained? Strom et al. suggested that the constancy of the HNLC condition was related to prey switching, i.e., the plastic feeding abilities of microzooplankton that dominate HNLC waters. The tight coupling between iron supply and demand by the microbial foodweb, that is evident from FeCycle, points to a key role of iron in these waters in setting the HNLC condition. The balancing of iron uptake and supply within the “ferrous wheel” we observed raises a further issue: If more iron was supplied to the microbial foodweb, would the wheel spin faster or become larger?
4.3. Sources and Sinks for Iron: Long-Term Budget
 The long-term iron budget during FeCycle is characterized by a marked imbalance between the magnitude of iron sources and sinks, with downward PFe export being several orders of magnitude higher than all of the source terms. However, despite this imbalance, there was no change in the mixed layer PFe inventory [Frew et al., 2005], which suggests that we have underestimated the iron supply to the upper ocean. The ability to use the SF6 tracer to estimate the vertical diffusive and lateral advective iron terms in the budget suggests that both these supply terms are robust. The observed weak vertical DFe gradient at our site suggests that even stochastic events such as storms have little potential to vertically supply new iron. In contrast to the estimation of the oceanic iron supply terms, our two measurements of aerosol iron deposition took place on days when air mass trajectory analysis indicates that the provenance of the air near the FeCycle site was marine from the subpolar Southern Ocean. This observation and the indirect evidence, from satellite remote sensing of dust storm activity, indicates that we most likely underestimated aerosol iron supply. Although remotely sensed data provide insights into aerosol deposition prior to and during FeCycle, they cannot yield estimates of dust depositional fluxes during FeCycle.
4.4. Constraining Aerosol Iron Fluxes During FeCycle
 To compare the magnitude of the budget terms (for new and recycled iron) measured during FeCycle with that of aerosol iron flux we have cautiously applied published values for the latter. There are dust deposition rates for Australasia from both global data synthesis [Jickells and Spokes, 2001] and models [Jickells et al., 2005]. Although measured and modeled deposition rates (10 mg Fe m−2 yr−1) for the New Zealand region show relatively good agreement [Jickells et al., 2005], they are expressed as an annual rate to take into account the episodic and intermittent nature of dust supply (compare auxiliary Table ts03). Despite the episodic characteristics of dust deposition events, analysis of dust storm frequency in Australia between 1957 and 1982 by Middleton , and of the regional remote sensing (CZCS) aerosol archives by Stegmann and Tindale  both point to pronounced seasonality in dust storm activity over Australia. Spring and summer are characterized by up to threefold more dust storms than winter.
 Only one detailed study of dust deposition rates in the New Zealand region has taken place: during the SEAREX programme [Arimoto et al., 1990]. This 3-month time series study atop a 20-m tower at an isolated beach site on the North Island of New Zealand (that included concurrent radon measurements to assess the continental influences on the air sampled) provided daily dust deposition rates from Australia (and subsequent aerosol elemental analysis) in winter (June to August). A study of the main dust trajectory routes from Australia to New Zealand, in conjunction with dust core records, suggests that dust deposition rates to northern New Zealand are comparable with those to southern New Zealand [Hesse, 1994] where FeCycle took place. Wet and dry iron deposition rates for winter were 303 nmol Fe m−2 d−1 (mean, no statistics were provided) at this SEAREX site [Arimoto et al., 1990]. This iron deposition rate can be scaled for February, when FeCycle took place, using the monthly dust storm frequency index of Middleton . In winter the average dust storm activity was 34, compared with 85 storms for February, suggesting that the iron supply rate from dust deposition was ∼758 nmol Fe m−2 d−1 during FeCycle. This estimated deposition rate compares with 550 nmol Fe m−2 d−1 for the New Zealand region from the global synthesis of Jickells and Spokes  (derived by dividing their estimate of 0.2 mmol Fe m−2 yr−1 by 365). It is likely that there will be up to a threefold uncertainty (i.e., 183 to 1650 nmol Fe m−2 d−1) on this global depositional estimate [Duce et al., 1991]. All of these estimates are considerably higher than those measured during FeCycle.
4.5. Attempting a Pelagic Fe Biogeochemical Budget
 The inclusion of published aerosol iron deposition rates for our region along with the pools and fluxes measured during FeCycle enables the construction of pelagic iron budget (Figure 7). Despite the uncertainties in estimating aerosol iron fluxes over such short timescales (days) three trends are evident. First, iron supply from the atmosphere is the dominant iron supply term (i.e., 50-fold greater than the oceanic iron supply terms) to the FeCycle site. Second, the estimated rates of aerosol iron deposition are comparable to the downward PFe export observed for FeCycle (Figure 7) which are broadly representative of spring and summer (see section 4.1). Third, the magnitude of new iron supply from both atmospheric and oceanic sources is small relative to that for recycled iron in the mixed layer (Figure 7).
 Despite evidence that published regional estimates of aerosol iron flux are comparable to downward PFe export for FeCycle, major imbalances remain when the downward PFe export flux is divided into lithogenic and biogenic PFe (Figure 7). Regardless of how much PFe is supplied to the ocean from dust deposition, very little (<1%) will be biogenic, yet biogenic PFe comprised 60% of the downward PFe flux (Figure 3), but only <20% of the mixed layer PFe inventory [Frew et al., 2005].
Frew et al.  suggest that the most compelling mechanism to reconcile these imbalances in both lithogenic and biogenic PFe sources and sinks is the conversion of a large proportion of the deposited lithogenic PFe into biogenic PFe within the mixed layer. This mechanism relies on two factors: the long timescale (weeks) reported for mixed layer residence time of aerosol lithogenic PFe [Jickells, 1999; Croot et al., 2004; Frew et al., 2005], and recent evidence of mechanisms for microbes to access mineral iron via dissolution of iron hydroxides [Yoshida et al., 2002; Borer et al., 2005]. Such a pathway for the biota to access lithogenic PFe has implications for the debate regarding the solubility and bioavailability of aerosol iron [see Jickells and Spokes, 2001]. It appears that there are now two timescales of iron solubility: instantaneous (hours, driven by physico-chemical mechanisms) and sustained (weeks, driven by microbes and light climate [Borer et al., 2005]). The latter mechanism, by permitting sustained dissolution of aerosol iron on a timescale of weeks, may act as a buffer for iron supply to the upper ocean, to the episodic and intermittent nature of aerosol iron deposition.
4.6. New Versus Regenerated Iron: First Estimates of an “fe” Ratio
 At present, techniques to discriminate between new and regenerated iron, such as stable isotopic tracers, are not sufficiently sensitive to compare the relative magnitude of iron supply from these two distinct pools [Levasseur et al., 2004]. However, the fluxes of new and regenerated iron within the SF6 labeled FeCycle patch enable us to estimate an fe ratio (i.e., uptake of new iron/(uptake of new + regenerated iron)) indirectly. The dominant fluxes in our long timescale budget are particulate and based on “new iron,” whereas those in the short-term budget are associated with the biota and the dissolved phase, and are mainly based on “regenerated iron.” Biological iron uptake was measured during four 24-hour in situ incubations (Figure 7), and provides the term (new + regenerated iron uptake). From Figure 7 the new iron entering the mixed layer is approximately balanced by the PFe exiting the upper ocean each day. Thus, assuming steady state conditions, the new iron entering the upper ocean is 758 nmol m−2 d−1 (aerosol iron) and 15 nmol m−2 d−1 (vertical diffusive supply). However, the former term must be corrected for lithogenic iron leaving the mixed layer of 77 to 196 nmol m−2 d−1; this is regarded here as a throughput of lithogenic iron comprising 10 to 26% of aerosol iron. The upper bound for the biological uptake of new iron term is 666 nmol m−2 d−1 (15 + (758 − 77)). Thus the fe ratio for FeCycle is 0.17 (696/4055 nmol m−2 d−1). The e ratio [Murray et al., 1989] can also be derived for the FeCycle study, here defined as the “Fe” ratio of (biogenic PFe export/uptake of new + regenerated iron), and is 0.09 (352/4055 nmol m−2 d−1). Note that the fe ratio would be considerably underestimated if these calculations did not take into account the availability of a larger proportion of lithogenic Fe from dust deposition [Borer et al., 2005]. Previously, the availability of new iron from dust was scaled by a solubility factor ranging from 1 to 10% [Jickells and Spokes, 2001].
 An “fe” ratio of 0.17 and an “Fe” ratio of 0.09 for Fe limited HNLC waters south of New Zealand is comparable to the lower bound of f and e ratios for the N-limited oligotrophic waters of the subtropical and tropical ocean [Karl et al., 2003]. Although no f ratios are available for the FeCycle site, Varela and Harrison  report a mean f ratio of 0.21 for the HNLC waters of the NE subarctic Pacific. That the fe ratio is less than the f ratio for HNLC waters is consistent with the widespread iron limitation of the resident phytoplankton in these waters. As for the f ratio (see discussion in the work of Karl et al. ), the fe ratio will “scale positively” with elevated iron supply, such as from episodic events including dust storms. On the basis of the threefold uncertainties on dust supply rates [Duce et al., 1991] the fe ratio might range from 0.05 to 0.48 over the annual cycle.
 The low fe ratio estimated for FeCycle indicates that the fluxes (iron uptake and regeneration) associated with the “ferrous wheel” are almost tenfold greater than the fluxes of “new iron,” and are turning over rapidly (hours to days) compared with weeks for the “new iron” particulate phases. Fung et al.  attempted to model iron supply and demand for the upper ocean over annual timescales, and constructed DFe budgets including one for the HNLC NE subarctic Pacific. Fung et al. report that even in this relatively low dust deposition region, aerosol iron supply, rather than upwelling and vertical mixing, is the dominant source of new iron. This is consistent with our findings, and despite the rapid turnover times (hours) of this large regenerated iron pool in FeCycle, the year-round observed tight coupling of phytoplankton and micro-grazers suggest that it may be possible to extrapolate these rates into an annual iron budget. The results of FeCycle point to the need to develop, in parallel, a PFe budget, and to consider the transformations between the biogenic and lithogenic pools in detail.
4.7. FeCycle: Implications for Our Understanding of Iron Biogeochemistry
 1. FeCycle has provided the first estimates of the fe and Fe ratios for HNLC waters. As expected, both ratios are lower than f ratios for HNLC waters. As iron recycling is dominant, the biogeochemical cycling of iron in the upper ocean is dominated by the biota.
 2. PFe plays a more significant role in iron biogeochemistry than was previously thought, via a putative lithogenic to biogenic transformation pathway for PFe in which >50% of the lithogenic iron deposited from the atmosphere into the ocean is transformed to biogenic iron during its residence (weeks) in the surface mixed layer. There is a pressing need to construct PFe budgets for other oceanic regions (with high aerosol deposition rates).
 3. As the biogeochemical iron cycle is driven by both oceanic and atmospheric events, it is necessary to sample both on appropriate timescales in order to construct budgets. This is particularly difficult to do for the atmosphere which is characterized by intermittent and episodic supply.
 4. Improved understanding of iron biogeochemistry in the open ocean requires the development of new techniques such as: (1) the use of highly sensitive isotopic tracers of Fe fluxes; (2) methods to measure the bioavailability and uptake of actual and specific natural dissolved organic ligand-bound pools (these are needed to supersede existing iron radio-isotope approaches); and (3) long-term, event-resolved dust sampling (moorings).
 Thanks are owed to the officers and crew of the research vessel RV Tangaroa, and the personnel at NIWA vessel services. We are grateful to G. McTainsh for access to data from his dust environmental monitoring network. We acknowledge Orbimage and NASA for the availability of satellite images presented here (SeaWiFs and TOMS). This research was funded in part by the New Zealand PGSF Ocean Ecosystems project.