7 μm mesh, 25 mm, Whatman GF/F) was attached between the syringe and the water inlet port. Water samples were purged with Helium 6.0. at a flow rate of 40 ml/min for 10 min (see more in Section 2.4.2, Selection of purging volume). Regular cleaning of the purging tube with deionized water, prevented salt crystal formation in the frit and purge efficiency reduction. During purging, the water samples were heated to a few degrees above room temperature using

a tube heating mantle connected to a temperature regulator (parts 5–6, Fig. 2). Gaseous VOCs extracted from the water sample were then trapped onto the sorbent material of the needle. Because of the temperature difference between the sampling air stream (30 °C) and the needle (room temperature 25 °C), some water vapor contained in the sampling air condensed in the NTD during sampling. Condensed water is a prerequisite of the NTD method. When the needle was

inserted into the hot injector (310 °C), the instantaneous find more transformation of trapped condensed water vapor into gas created high pressure within the needle (estimated > 50 bar) which served to drive the collected VOCs from the absorbent into the GC column. The 3-step procedure of the needle trap sampling is shown in Fig. 3. After sampling, both ends of the needle were sealed LY294002 with Teflon caps until subsequent analysis. The same NTD was used for up to 80 sample injections. To calibrate the system, deionized water was introduced into the glass tube without filtering. Using a gas-tight syringe, the VOC calibration gas mixture was introduced

(part 1, Fig. 2) into the He stream which then passed through the deionized water and afterwards through the needle trap device. Thereafter, the same procedure as with the seawater samples was followed. The desired concentration levels were obtained by appropriate dilution of the CHIR-99021 order multi-component mix gas standard with synthetic air. For a given volatile organic compound, the ideal purging time, and hence volume, will depend both on how easily it can be purged out of the water-phase and on how effectively it can be retained on the needle trap adsorbent. High volatile tracers need to be purged for a shorter time than the low volatile. If purging times are too long the amount of a selected compound will reduce as it is flushed from the needle trap. Purging volumes ranging from 50 to 700 ml were examined for all species. The contrasting behavior of isoprene and α-pinene is shown in Fig. 4, where the recorded peak areas (normalized to the higher value) are plotted against different purging volumes. Isoprene gave highest peak areas after 5 min of purging (200 ml) while α-pinene after 15 min (600 ml). Individual plots for all tracers are available in the supplementary data section. Calibrations (0.07–5 nM) performed at both short (100 ml) and long purging times (400 ml) exhibited linear relationships in both cases (r2 ≥ 0.96 for all tracers, see Table 1 in supplementary data).