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                <gco:CharacterString>Parameter or Variable: Trace Metals (Cu, Cd) (calculated);
Units: nM;
Observation Category: laboratory analysis;
Sampling Instrument: Niskin-X bottle;
Sampling and Analyzing Method: Water samples were collected using Niskin-X with external spring and Teflon® coating. Seawater samples were filtered under a positive atmosphere in an ultra-clean laboratory using Nuclepore® polycarbonate filters (0.45 μm). Filters containing particulate material were stored at −8 °C until analysis. The filtered seawater was acidified to pH ~2 and dissolved Cu and Cd were pre-concentrated using Chelex-100 ion-exchange resin (Bio-Rad, Hercules, USA) following the methods of Bruland et al. (1979). Particulate Cu and Cd,  retained on filters, were digested in Teflon vessels via microwave-assisted acid digestion system (ETHOS TC, Milestone, Freemont, USA), using HNO3 and H2O2 (OmniTrace), following the methods of Quevauviller et al. (1993). The digests were evaporated at 80 °C and re-dissolved in 10 mL of 0.2% HNO3 for analysis. Both fractions were quantified by graphite furnace atomic absorption spectrophotometry (GF-AAS; AAnalyst 600, Perkin–Elmer, Shelton, USA.;
Data Quality Method: Accuracy and precision were verified using certified reference materials: CASS-5 (seawater, Canadian Research Council of Canada, Ottawa, Canada) and BCR 414 (plankton, Community Bureau of Reference, Geel, Belgium), with recoveries of 93–110% for Cud (n = 6) and 90–97% for Cup (n = 9) and a precision of 5–10%. Percent recovery for Cdd and Cdp were 93 ± 4% and 100 ± 10%, respectively.</gco:CharacterString>
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Units: cell/L;
Observation Category: laboratory analysis;
Sampling Instrument: dark bottles;
Sampling and Analyzing Method: Water samples for phytoplankton counts were transferred from Niskin-X samplers to dark HDPE bottles and fixed with 1mL of lugol-acetate to immobilize and preserve the cells.
Lingulaulax polyedra abundance was quantified following the Utermöhl method, using 50-mL sedimentation chambers and an CK-2 inverted microscope with phase contrast (Olympus, Shinjuku, Japan).;
Data Quality Method: Counts were done by transects in 365 fields, and the result was extrapolated to the total 730 fields in the sedimentation chamber.</gco:CharacterString>
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                <gco:CharacterString>Parameter or Variable: Nutrients (phosphate) (measured);
Units: µM;
Observation Category: laboratory analysis;
Sampling Instrument: Niskin bottle;
Sampling and Analyzing Method: 60 mL of water were directly transfered from the Niskin-X  sampler to a plastic siringe, filtered through GF/F filters (0.45 μm) previously ashed at  450 °C for 6 h.
Phosphate concentrations were determined using the ascorbic acid method described by Strickland and Parsons (1972).  A 12.5 mL sample of sea water was taken and 1.25 mL of mixed reagent was added. The reaction produced a blue color whose absorbance was measured at 885 nm using a Varian model Cary 50 UV–VIS spectrophotometer.;
Data Quality Method: Quality control included reagent blanks, duplicate samples, and calibration</gco:CharacterString>
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                <gco:CharacterString>Parameter or Variable: Physical oceanographic indices (CUTI) (calculated);
Units: m^3 s^-1 per 100 m of coastline;
Observation Category: model output;
Sampling Instrument: leverage  ocean models, satellite and in situ data to improve upon historically available upwelling indices for the U.S. W coast;
Sampling and Analyzing Method: CUTI values were averaged to daily resolution using arithmetic means.
Only dates corresponding to sampling periods were retained.
No interpolation or gap-filling was applied.
acox, M. G., Edwards, C. A., Hazen, E. L., &amp; Bograd, S. J. (2018).
Coastal Upwelling Revisited: Ekman, Bakun, and Improved Upwelling Indices
for the U.S. West Coast.
Journal of Geophysical Research: Oceans, 123, 7332–7350.
https://doi.org/10.1029/2018JC014187</gco:CharacterString>
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                <gco:CharacterString>Parameter or Variable: Atmospheric/reanalysis data (ERA5 surface variables) (calculated);
Units: ind speed at 10 m: m s^-1 Friction velocity (u*): m s^-1 Precipitation: mm;
Observation Category: model output;
Sampling Instrument: ERA5 reanalysis (ECMWF);
Sampling and Analyzing Method: ERA5 u10, v10 and total precipitation fields were extracted at the study site grid point.
2. Wind speed at 10 m was computed as sqrt(u10^2 + v10^2).
3. Wind stress was computed using a constant drag coefficient Cd = 1.3e-3 and air density rho_air = 1.225 kg m^-3.
4. Friction velocity (u*) was computed as u* = sqrt(tau / rho_water), using rho_water = 1025 kg m^-3.
5. Precipitation was converted from meters to millimeters.
6. The time series were subset to the period 2012-11-20 to 2013-01-04.
7. No temporal resampling, smoothing, or filtering was applied.
8. The resulting time series were exported to Excel format.
Hersbach, H., et al. (2020). The ERA5 global reanalysis. Quarterly Journal of the Royal Meteorological Society, 146, 1999–2049;
Data Quality Method: The data correspond directly to the original ERA5 products and were only mathematically derived (wind speed magnitude and friction velocity) and temporally subsetted. No interpolation or additional quality control procedures were applied.</gco:CharacterString>
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            <gco:CharacterString>NOAA National Centers for Environmental Information</gco:CharacterString>
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Why special entry for Niskin bottle but no entry for Nansen bottle?</gco:CharacterString>
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