Metadata Report for BODC Series Reference Number 2111909
Metadata Summary
Problem Reports
Data Access Policy
Narrative Documents
Project Information
Data Activity or Cruise Information
Fixed Station Information
BODC Quality Flags
SeaDataNet Quality Flags
Metadata Summary
Data Description |
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Time Co-ordinates(UT) |
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Parameters |
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Problem Reports
No Problem Report Found in the Database
Data Access Policy
Open Data supplied by Natural Environment Research Council (NERC)
You must always use the following attribution statement to acknowledge the source of the information: "Contains data supplied by Natural Environment Research Council."
Narrative Documents
SPX Bran+Luebbe Autoanalyser 3
The instrument uses continuous flow analysis (CFA) with a continuous stream of material divided by air bubbles into discrete segments in which chemical reactions occur. The continuous stream of liquid samples and reagents are combined and transported in tubing and mixing coils. The tubing passes the samples from one apparatus to the other with each apparatus performing different functions, such as distillation, dialysis, extraction, ion exchange, heating, incubation, and subsequent recording of a signal.
An essential principle of the system is the introduction of air bubbles. The air bubbles segment each sample into discrete packets and act as a barrier between packets to prevent cross contamination as they travel down the length of the tubing. The air bubbles also assist mixing by creating turbulent flow (bolus flow), and provide operators with a quick and easy check of the flow characteristics of the liquid.
Samples and standards are treated in an exactly identical manner as they travel the length of the tubing, eliminating the necessity of a steady state signal, however, since the presence of bubbles create an almost square wave profile, bringing the system to steady state does not significantly decrease throughput and is desirable in that steady state signals (chemical equilibrium) are more accurate and reproducible.
The autoanalyzer can consist of different modules including a sampler, pump, mixing coils, optional sample treatments (dialysis, distillation, heating, etc), a detector, and data generator. Most continuous flow analyzers depend on color reactions using a flow through colorimeter, however other methods have been developed that use ISE, flame photometry, ICAP, fluorometry, and so forth.
More details can be found in the manufacturer's introduction to autoanalysers andinstrument description.
Clean pumped sea water supply
The system comprises a precision echosounder (PES) fish attached to a clean, reinforced tube (typically composed of braided polyvinyl chloride (PVC)). The fish is designed to be towed alongside a moving ship at a depth of one to three metres and water is drawn through the system by a clean pump. The tube usually leads to a clean laboratory on board the vessel, inside which samples are drawn for analysis. The system is typically used for continuous, underway, clean sampling (e.g., trace metal studies) of near surface waters.
Underway Towed Fish Sampling - dissolved organic phosphorous (DOP) for GEOTRACES Cruise JC150
Responsible investigator
Dr Claire Mahaffey
email: claire.mahaffey@liverpool.ac.uk
University of Liverpool Department of Earth, Ocean and Ecological Sciences
4 Brownlow Street
Liverpool, Merseyside
United Kingdom
L69 3GP
Laboratory of analysis:
University of Southampton
Acquisition description:
Sampling methodology
High-resolution underway surface samples were collected using a 'towfish' which was deployed off the starboard side of the ship. Surface seawater was pumped into the trace metal clean laboratory using a Teflon diaphragm pump (Almatec A-15) connected by acid-washed braided PVC tubing to a towed 'fish' positioned at approximately 2-3 m. Underway samples were collected every 2 hours along the transect between stations. In all, 130 towed fish time point samples were taken along the transect. Unfiltered seawater samples were collected under trace metal clean conditions for determination of DOP concentrations from the underway fish sampling. Samples were collected in 125 mL HDPE bottles (acid washed, Fisher Scientific) and stored at -20°C for later analysis in the laboratory.
Analytical methodology
Total dissolved phosphorus (TDP) was determined using the high temperature acid persulfate technique as described in Lomas et al (2010) with the following modifications. Standards were prepared in P-free artificial seawater using potassium monobasic phosphate (KHPO4, Sigma Aldrich). Samples and standards were autoclaved (121°C, 40 min) in 40 mL aliquots in tightly sealed 50 mL glass Pyrex bottles with Teflon lined screw caps after addition of 5 mL potassium persulfate solution (64 g/L). Following oxidation samples were left to cool overnight and then precipitated using the MAGIC technique (Karl and Tien 1992) by addition of 5 mL 1M NaOH solution (Sigma Aldrich). Following centrifugation (1000 x g, 60 min), the supernatant was discarded and the sample/standard pellet were completely dissolved in 40 mL 0.1 M HCl (Trace metal grade, Sigma Aldrich). Analytical blanks were determined as described in Lomas et al (2010).
Total dissolved phosphorus were determined in triplicate as dissolved inorganic phosphorus (DIP) concentrations after persulfate oxidation of the samples by the molybdenum blue method (Murphy and Riley, 1962) using a Bran and Leubbe QuAAtro 5-channel autoanalyser (DIP detection limit 50 nM). Dissolved organic phosphorus (DOP) has been taken as the difference between TDP and DIP determined prior to persulfate oxidation (i.e. DOP = TDP - DIP; DOP detection limit 40 nM). In this case, DIP values were taken from the phosphate data of Malcolm Woodward, PML, obtained during the cruise.
References Cited
Karl, D. M., Tien, G. (1992) MAGIC: A sensitive and precise method for measuring dissolved phosphorus in aquatic environments, Limnology and Oceanography, 37, doi: 10.4319/lo.1992.37.1.0105.
Lomas, M. W., Burke, A. L., Lomas, D. A., Bell, D. W., Shen, C., Dyhrman, S. T., and Ammerman, J. W.(2010) Sargasso Sea phosphorus biogeochemistry: an important role for dissolved organic phosphorus (DOP), Biogeosciences, 7, 695-710, https://doi.org/10.5194/bg-7-695-2010
Murphy, J and Riley, J.P.. (1962) A Modified Single Solution Method for the Dermination of Phosphate in Natural Waters. Anal. Chim. Acta. 26. 678-681.
BODC Data Processing Procedures
Data received were loaded into the BODC database using established BODC data banking procedures. A parameter mapping table is provided below:
Originator's Variable | Originator's Units | BODC Parameter Code | BODC Unit | Comments |
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DOP | nM | ORGPDSZZ | umol/l | Conversion of /1000 applied |
Project Information
Zinc, iron and phosphorous co-limitation in the Ocean: ZIPLOc
ZIPLOc is an 3 year project that aims to measure how zinc and phosphorous control biological activity in the North Atlantic subtropical gyre using novel measurement techniques. The observations made will be further explored using the latest modelling techniques over decadal timescales and in other basins.
The research aims to make an improvement in our overall understanding of how subtropical gyre ecosystems respond to ongoing climate change.
The project is led by the University of Liverpool, Earth, Ocean and Ecological Sciences and is a collaboration with the University of Southampton, School of Ocean and Earth Science. The project received funding from the Natural Environmental Research Council and runs between January 2017 and February 2020.
Data Activity or Cruise Information
Cruise
Cruise Name | JC150 (GApr08, ZIPLOC) |
Departure Date | 2017-06-25 |
Arrival Date | 2017-08-12 |
Principal Scientist(s) | Claire Mahaffey (University of Liverpool Department of Earth, Ocean and Ecological Sciences) |
Ship | RRS James Cook |
Complete Cruise Metadata Report is available here
Fixed Station Information
No Fixed Station Information held for the Series
BODC Quality Control Flags
The following single character qualifying flags may be associated with one or more individual parameters with a data cycle:
Flag | Description |
---|---|
Blank | Unqualified |
< | Below detection limit |
> | In excess of quoted value |
A | Taxonomic flag for affinis (aff.) |
B | Beginning of CTD Down/Up Cast |
C | Taxonomic flag for confer (cf.) |
D | Thermometric depth |
E | End of CTD Down/Up Cast |
G | Non-taxonomic biological characteristic uncertainty |
H | Extrapolated value |
I | Taxonomic flag for single species (sp.) |
K | Improbable value - unknown quality control source |
L | Improbable value - originator's quality control |
M | Improbable value - BODC quality control |
N | Null value |
O | Improbable value - user quality control |
P | Trace/calm |
Q | Indeterminate |
R | Replacement value |
S | Estimated value |
T | Interpolated value |
U | Uncalibrated |
W | Control value |
X | Excessive difference |
SeaDataNet Quality Control Flags
The following single character qualifying flags may be associated with one or more individual parameters with a data cycle:
Flag | Description |
---|---|
0 | no quality control |
1 | good value |
2 | probably good value |
3 | probably bad value |
4 | bad value |
5 | changed value |
6 | value below detection |
7 | value in excess |
8 | interpolated value |
9 | missing value |
A | value phenomenon uncertain |
B | nominal value |
Q | value below limit of quantification |