“…Although such estimates should be considered as rather simplified, semi-qualitative approximations, the time depth variations obtained look rather plausible (see examples in Supplementary Material): the lower values are found in the deeper parts of upper layers, while in the surface layers the effects of extracellular excretion from spring and summer phytoplankton blooms, followed by sedimentation and lysis of degrading seston, could be recognized with a little imagination. The main result of this large-scale exercise, performed in every basin on thousands of measurements, is similar to deductions TP pool, 10 3 t P 9.5 ± 1.8 64.9 ± 14.7 462 ± 70 25.4 ± 6.1 10.4 ± 1.7 11.5 ± 2.2 10.8 ± 1.5 595 ± 88 TP input, 10 3 t P yr −1 3.4 ± 0.7 4.0 ± 0.7 24.2 ± 5.6 9.0 ± 2.2 3.9 ± 1.4 4.8 ± 3.0 2.5 ± 0.7 51.8 ± 12.5 TN:TP, mol:mol 94 ± 20 40 ± 7 17 ± 2 30 ± 7 33 ± 6 23 ± 4 23 ± 4 21 ± 3 TN in :TP in , mol:mol 41 ± 6 51 ± 6 52 ± 5 34 ± 10 64 ± 20 57 ± 28 83 ± 18 50 ± 6 DIN, 10 3 t N 124 ± 23 196 ± 58 620 ± 131 60 ± 24 30 ± 11 21 ± 6 27 ± 8 1,077 ± 210 DIP, 10 3 t P 2.6 ± 0.8 35.7 ± 13.6 348 ± 48 15.2 ± 3.9 3.9 ± 1.2 5.3 ± 1.5 5.4 ± 1.0 416 ± 62 DIN:DIP, mol:mol 119 ± 46 13 ± 3 4 ± 1 9 ± 3 19 ± 10 9 ± 3 11 ± 4 6 ± 1 Mean ± standard deviations from pools (1970-2016) and inputs (1970-2014) made from scarcer data (Hoikkala et al, 2015;Seidel et al, 2017): the share of the labile fraction of organic nitrogen (21-37%) increases toward the Baltic Entrance area and is significantly lower than that of phosphorus (35-67%).…”