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Additional metadata information concerning NIVA FerryBox systems

1. Method description for measured variables

Sensors were equipped on an underway flow-through system (FerryBox) on ships of opportunity. Clean seawater inlets were custom installed at ∼5 m depth and directly pumped to a sensor package.

Seawater Temperature (unit: 'degree_Celsius' )

A SeaBird digital oceanographic thermometer (SBE38) was installed at the FerryBox inlet, in addition to a SeaBird SBE45 thermosalinograph in the FerryBox cabinet. The temperature sensors were periodically checked and calibrated using a traceable reference thermometer.

AutoQC tests applied: Water flow test, GPS quality test, Frozen test, Range test, Spike test

Seawater Salinity (unit: 'PSU' )

A SeaBird thermosalinograph (SBE45) was installed in the FerryBox cabinet. The salinity sensor was periodically checked and calibrated using discrete salinity samples measured using a laboratory salinometer (Portasal).

AutoQC tests applied: Water flow test, GPS quality test, Frozen test, Range test, Spike test

Seawater Oxygen Saturation (unit: ‘%’)

Measured with oxygen optode (Aanderaa optode 4835), which was periodically checked and calibrated with discrete samples analyzed using Winkler titration.

AutoQC tests applied: Water flow test, GPS quality test, Frozen test, Range test

Chlorophyll a fluorescence (mg/m3)

A Turner Designs C3 submersible sensor configured with chlorophyll a, coloured dissolved organic matter (CDOM), and turbidity sensors; excitation 465 nm, emission 696 nm; calibrated using algal cultures, and periodically validated with Turner Designs solid secondary standards and Chl-a samples analysed via methanol extraction and spectrophotometry.

AutoQC tests applied: Water flow test, GPS quality test, Frozen test, Range test

Coloured dissolved organic matter fluorescence (fDOM) (mg/m3)

A Turner Designs C3 submersible sensor configured with chlorophyll a, coloured dissolved organic matter (CDOM), and turbidity sensors; excitation 325 nm, emission 470 nm; calibrated using quinine sulfate and periodically validated using Turner Designs solid secondary standards.

AutoQC tests applied: Water flow test, GPS quality test, Frozen test

Turbidity (Formazin Nephelometric Unit, FNU)

A Turner Designs C3 submersible sensor configured with chlorophyll a, coloured dissolved organic matter (CDOM), and turbidity sensors; excitation and emission at 850 nm; calibrated using formazin calibration solutions and periodically validated with a custom-made solid standard (NIVA).

AutoQC tests applied: Water flow test, GPS quality test, Frozen test

2. Calibration procedure

Chlorophyll-a fluorescence (chl-a): Chl-a fluorescence is calibrated using phytoplankton from culture within a range of 0 - 20 µg/L. NIVA uses a common algae from the monitoring area, e.g. Skeletonema spp. The calibration is performed in dark conditions using filtered seawater as a blank followed by adding a known concentration of the phytoplankton culture. Filtered chl-a samples are taken for each added concentration of algae culture and analyzed spectrophotometrically (reference). The raw counts from the sensor are used with the chl-a concentration to generate a linear calibration equation.

cDOM fluorescence (fDOM): fDOM is calibrated using freshly prepared quinine sulphate (QS) standards from a stock solution of 7040 mg/m3 in 0.05 M sulfuric acid in the concentration range 0-200 mg/m3 QS. Calibration is done in dark conditions. Blank is measured with both ultrapure water (Milli-Q) and 0.05 M sulfuric acid, followed by adding known concentrations of QS. The different concentrations of QS are compared to the raw counts from the sensor to generate a linear calibration equation.

Turbidity: Turbidity is calibrated using formazin in dark conditions within a range of 0 - 40 FNU. Milli-Q water is used as a blank, followed by adding formazin from low to high concentration. For each concentration of formazin, the sample is also measured with a reference turbidimeter (Hach). The results from the turbidimeter are compared with the raw counts from the sensor to generate a linear calibration equation.

3. Quality control procedure

Quality control procedures follow established protocols [1, 2].

The following tests have been implemented in [1, 2] for the real-time quality control: 

  1. Water flow test It checks if water pump operates and if the difference between temperature measured in the cabinet and at inlet is within acceptable range. 

  2. GPS quality test Bounded variance test and range test are applied to boat velocity calculated using finite difference and longitude and latitude measurements and including earth curvature. 

  3. Frozen test It checks if 4 consecutive values before the tested value are equal. 

  4. Range test It checks that data is within a specified range of values. Accepts time range and geographic range. The latter is based on minimum and maximum latitudes and longitudes values. 

  5. Spike test Tests the difference between sequential measurements as defined in [2]. 

Outcomes of the above tests, per parameter, per timestamp are combined into the final quality control flag. The result is passed if at least one test passed, and no tests failed. The result is failed if at least one test failed. Tests 1 and 2 are mandatory for all parameters. Tests 3-5 are by default applied but also configurable in [2]. 

References:

[1] EuroGOOS Data Management, Exchange, and Quality Working Group (2015). Real Time Quality Control of biogeochemical measurements. https://eurogoos.eu/download/RTQC_BGC_recommendations_v2.5.pdf

[2] Copernicus Marine in situ TAC BGC quality control group (2022). Real time quality control of biogeochemical measurements within Copernicus Marine in situ TAC. https://doi.org/10.13155/75704

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