The concentration and elemental ratios of nitrogen (N), phosphorus (P) and silicate (Si) such as N:P:Si (typical nomenclature used in ecology) are known to strongly influence phytoplankton communities (Harris 1986). Redfield et al. (1963) proposed that growing phytoplankton take up nutrients from the water column in fixed proportions, namely C:N:P:Si ratios of 106:16:1:15. Deviations in nutrient concentrations from these proportions have been used as indicators of

the limitation of primary production in pelagic systems. However, the role of nutrient limitation and N:P ratios in structuring the phytoplankton communities has been suggested to vary considerably, both spatially and temporally, among different systems (Lagus et al. 2004). For example, Ibrutinib a C:N:P:Si ratio of 62:11:1:24 was proposed for the Southern Ocean by Jennings et al. (1984). Here, we observed N:P ratios between 0.3 and 107 with an annual average of 12.3 ± 1.5 which

was close to the 11 nominated for phytoplankton growth by Jennings et al. (1984). In addition, our winter to summer ratios (Table 1, Figure 4) were similar to the observed N:P spring MEK inhibitor ratio of 8.3 ± 5.4 in the Polar Frontal zone at 140°E (Lourey & Trull 2001) and at 64°S, 141°E (Takeda 1998). Like the N:P ratios, N:Si ratios were variable: this was expected, since they depend on the abundance of diatoms which can show both temporal and spatial variations. N:Si ratios were in the range of 0.01 to 1.52 with an annual average of 0.25 ± 0.02. This compares well with suggested values of 0.45 (Jennings et al. 1984). The values observed during spring (0.95) and

autumn (0.82) correspond to the expected ratio of 0.95 for planktonic diatoms (Brzezinski 1985) and match the blooming periods observed Tau-protein kinase for diatoms in this study. Furthermore, the Si:P ratios were highly variable between 5 and 171 with an annual average of 44.5 ± 3.25. Smayda (1990) suggested that changes in Si:P ratios would affect planktonic assemblages, with a possible shift from diatom to flagellate when a decline in Si:P ratios was observed. These ratios indicate that N was usually the limiting nutrient in the GSV, which is typical of marine systems (Hecky & Kilham 1988, Elser et al. 2007). All ratios were the highest in autumn with N:P ratios of 26.6 ± 4.5, N:Si ratios of 0.31 ± 0.03 and Si:P ratios of 71.3 ± 6.61 (Figure 4). Previous work showed that N:P ratios greater than 20–30 suggest P limitation (Dortch & Whitledge 1992, Justic et al. 1995), which should not happen in the GSV except in autumn when the ratio exceeds those values. In addition, since both N:Si and Si:P ratios showed that Si was in excess compared to N and P, the diatom-zooplankton-fish food web should not be compromised. Levels of Chl a revealed higher phytoplankton biomass during autumn ( Figure 3) which was significantly correlated to N:P (ρ= 0.309, p<0.05) and Si:P (ρ= 0.283, p<0.05) ratios. In their experiments, Lagus et al.