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Metadata Report for BODC Series Reference Number 2115763


Metadata Summary

Data Description

Data Category Water sample data
Instrument Type
NameCategories
Niskin bottle  discrete water samplers
SPX Bran+Luebbe colorimetric Autoanalyser 3  colorimeters; autoanalysers
Stand-alone pump  sieves and filters
Instrument Mounting lowered unmanned submersible
Originating Country United Kingdom
Originator Dr Helen Findlay
Originating Organization Plymouth Marine Laboratory
Processing Status banked
Online delivery of data Download available - Ocean Data View (ODV) format
Project(s) UKOARP_ThemeB
 

Data Identifiers

Originator's Identifier JC073_CTD_NUTS_3972:CTD45
BODC Series Reference 2115763
 

Time Co-ordinates(UT)

Start Time (yyyy-mm-dd hh:mm) 2012-06-06 09:41
End Time (yyyy-mm-dd hh:mm) -
Nominal Cycle Interval -
 

Spatial Co-ordinates

Latitude 55.48583 N ( 55° 29.1' N )
Longitude 15.80046 W ( 15° 48.0' W )
Positional Uncertainty 0.05 to 0.1 n.miles
Minimum Sensor or Sampling Depth 5.2 m
Maximum Sensor or Sampling Depth 606.3 m
Minimum Sensor or Sampling Height 157.7 m
Maximum Sensor or Sampling Height 758.8 m
Sea Floor Depth 764.0 m
Sea Floor Depth Source PEVENT
Sensor or Sampling Distribution Unspecified -
Sensor or Sampling Depth Datum Unspecified -
Sea Floor Depth Datum Instantaneous - Depth measured below water line or instantaneous water body surface
 

Parameters

BODC CODERankUnitsTitle
ADEPZZ011MetresDepth (spatial coordinate) relative to water surface in the water body
AMONAAD21Micromoles per litreConcentration of ammonium {NH4+ CAS 14798-03-9} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis
BOTTFLAG1Not applicableSampling process quality flag (BODC C22)
FIRSEQID1DimensionlessBottle firing sequence number
NTRAAA041Micromoles per litreConcentration of nitrate {NO3- CAS 14797-55-8} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis and correction for nitrite
NTRAAA051Micromoles per litreConcentration standard deviation of nitrate {NO3- CAS 14797-55-8} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis and correction for nitrite
NTRIAAD21Micromoles per litreConcentration of nitrite {NO2- CAS 14797-65-0} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis
PHOSAAD21Micromoles per litreConcentration of phosphate {PO43- CAS 14265-44-2} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis
ROSPOSID1DimensionlessBottle rosette position identifier
SAMPRFNM1DimensionlessSample reference number
SDAMAAD21Micromoles per litreConcentration standard deviation of ammonium {NH4+ CAS 14798-03-9} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis
SDNIAAD21Micromoles per litreConcentration standard deviation of nitrite {NO2- CAS 14797-65-0} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis
SDPHAAD21Micromoles per litreConcentration standard deviation of phosphate {PO43- CAS 14265-44-2} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis
SDSLAAD21Micromoles per litreConcentration standard deviation of silicate {SiO44- CAS 17181-37-2} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis
SLCAAAD21Micromoles per litreConcentration of silicate {SiO44- CAS 17181-37-2} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis

Definition of BOTTFLAG

BOTTFLAGDefinition
0The sampling event occurred without any incident being reported to BODC.
1The filter in an in-situ sampling pump physically ruptured during sample resulting in an unquantifiable loss of sampled material.
2Analytical evidence (e.g. surface water salinity measured on a sample collected at depth) indicates that the water sample has been contaminated by water from depths other than the depths of sampling.
3The feedback indicator on the deck unit reported that the bottle closure command had failed. General Oceanics deck units used on NERC vessels in the 80s and 90s were renowned for reporting misfires when the bottle had been closed. This flag is also suitable for when a trigger command is mistakenly sent to a bottle that has previously been fired.
4During the sampling deployment the bottle was fired in an order other than incrementing rosette position. Indicative of the potential for errors in the assignment of bottle firing depth, especially with General Oceanics rosettes.
5Water was reported to be escaping from the bottle as the rosette was being recovered.
6The bottle seals were observed to be incorrectly seated and the bottle was only part full of water on recovery.
7Either the bottle was found to contain no sample on recovery or there was no bottle fitted to the rosette position fired (but SBE35 record may exist).
8There is reason to doubt the accuracy of the sampling depth associated with the sample.
9The bottle air vent had not been closed prior to deployment giving rise to a risk of sample contamination through leakage.

Definition of Rank

  • Rank 1 is a one-dimensional parameter
  • Rank 2 is a two-dimensional parameter
  • Rank 0 is a one-dimensional parameter describing the second dimension of a two-dimensional parameter (e.g. bin depths for moored ADCP data)

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.

Niskin Bottle

The Niskin bottle is a device used by oceanographers to collect subsurface seawater samples. It is a plastic bottle with caps and rubber seals at each end and is deployed with the caps held open, allowing free-flushing of the bottle as it moves through the water column.

Standard Niskin

The standard version of the bottle includes a plastic-coated metal spring or elastic cord running through the interior of the bottle that joins the two caps, and the caps are held open against the spring by plastic lanyards. When the bottle reaches the desired depth the lanyards are released by a pressure-actuated switch, command signal or messenger weight and the caps are forced shut and sealed, trapping the seawater sample.

Lever Action Niskin

The Lever Action Niskin Bottle differs from the standard version, in that the caps are held open during deployment by externally mounted stainless steel springs rather than an internal spring or cord. Lever Action Niskins are recommended for applications where a completely clear sample chamber is critical or for use in deep cold water.

Clean Sampling

A modified version of the standard Niskin bottle has been developed for clean sampling. This is teflon-coated and uses a latex cord to close the caps rather than a metal spring. The clean version of the Levered Action Niskin bottle is also teflon-coated and uses epoxy covered springs in place of the stainless steel springs. These bottles are specifically designed to minimise metal contamination when sampling trace metals.

Deployment

Bottles may be deployed singly clamped to a wire or in groups of up to 48 on a rosette. Standard bottles and Lever Action bottles have a capacity between 1.7 and 30 L. Reversing thermometers may be attached to a spring-loaded disk that rotates through 180° on bottle closure.

Stand Alone Pump (SAP)

A submersible battery powered water pump that sucks water through various filters leaving the materials of interest on the filter for analysis. SAPs are deployed clamped to a hydrographic wire and may be used to sample at depths of up to 6000 m. A SAP can pump thousands of litres of water over a few hours.

Dissolved inorganic carbon, total alkalinity, inorganic nutrients and associated calculated carbonate system parameters from Niskin bottle samples collected during UKOA cruise JC073

Originator's Protocol for Data Acquisition and Analysis

Seawater was collected from Niskin bottles in 50 mL Borosilicate glass bottles with ground glass stoppers. The bottles were rinsed and filled according to Standard Operating Procedure 1 in Dickson et al. 2007. Duplicate samples were taken from the same Niskin bottle. Samples were then poisoned with 10 µL mercuric chloride and taken to the chemical laboratory where the samples were brought to room temperature (approximately 23°C). Samples were collected from depths throughout the water column at the following sites: Mingulay reef area 1 (and Banana reef), Logachev reef area, PICES site, and the Hebrides Terrace Seamount site. A total of 343 water column samples were collected and analysed for dissolved inorganic carbon and total alkalinity. All samples were analysed within 24 hours of collection.

Directly after collecting samples for DIC and total alkalinity, duplicate samples were collected from the Niskin bottles for nutrient analysis. From these samples, 50 mL was filtered into acid-cleaned, aged, 60 mL Nalgene bottles. The Nalgene bottles were then frozen and shipped back to land where analysis took place at Plymouth Marine Laboratory.

Inorganic Carbon
An Apollo SciTech AS-C3 Dissolved Inorganic Carbon (DIC) analyser was used to measure inorganic carbon. The analyser adds a strong acid to the sample causing all carbon species to be converted to CO2. This CO2 gas is purged from the water by pure nitrogen (N2) carrier gas which carries the CO2 through a drying system that includes a cooling system, reducing water vapour. The concentration of the dried CO2 gas is then measured using a LI-7000 CO2 analyser. CO2 was converted to DIC using a standard curve created from analysing known volumes of the Certified Reference Materials (Dickson, Batch 113 and Batch 109).

Total Alkalinity
Total alkalinity was measured by open-cell potentiometric titration (Dickson et al., 2007) using an Apollo SciTech AS-ALK2 total alkalinity titrator with replicate measurements made per sample. A calibration was conducted using Certified Reference Materials (Dickson, Batch 113 and Batch 109). The total alkalinity was then corrected with a calibration factor and also for the addition of mercuric chloride.

Inorganic Nutrients
A SPX Bran and Luebbe colorimetric Autoanalyser 3 was used to determine the concentration of the following inorganic nutrients: combined nitrate and nitrite, nitrite, phosphate and silicate. Nitrate concentrations were then calculated by subtracting the nitrite from the combined nitrate+nitrite concentration.

The remaining carbonate system parameters - including pHT, pCO2, Ωaragonite - were then calculated using DIC, total alkalinity, depth, temperature, salinity, silicate and phosphate according to Pierrot et al. (2006).

References

Dickson, A.G., Sabine, C.L. and Christian, J.R. (Eds.), 2007. Guide to Best Practices for Ocean CO2 Measurements. PICES Special Publication 3, 191 pp.

Findlay, H. S., Artioli, Y., Moreno Navas, J., Hennige, S. J., Wicks, L. C., Huvenne, V. A. I., Woodward, E. M. S. and Roberts, J. M., 2013. Tidal downwelling and implications for the carbon biogeochemistry of cold-water corals in relation to future ocean acidification and warming. Global Change Biology, 19: 2708-2719.

Pierrot D., Lewis E. and Wallace D.W.R., 2006. CO2sys DOS program developed for CO2 system calculations. ORNL/CDIAC-105. Carbon Dioxide Information Analysis Center, Oak Ridge National Laboratory, U.S. Department of Energy, Oak Ridge, Tennessee.

Instrumentation

The instrumentation used are as follows:

Manufacturer Model Parameters Measured
Apollo SciTech AS-C3 Dissolved Inorganic Carbon (DIC) analyser DIC
Apollo SciTech AS-ALK2 total alkalinity titrator Total Alkalinity
SPX Bran+Luebbe Colorimetric Autoanalyser 3 Combined nitrate and nitrite, nitrite, phosphate and silicate

BODC Data Processing Procedures

Data were submitted to BODC as a text file accompanied by a PDF document containing metadata which were subsequently archived by BODC. The data file contained water column profiles of dissolved inorganic carbon, total alkalinity, inorganic nutrients and the associated calculated carbonate system parameters from Niksin bottle and ROV samples. The Niskin bottle data are processed here with the ROV data available on request. The data also includes CTD parameters including salinity, oxygen, fluorescence and temperature but like the ROV data, have not been processed here. The data file included the following metadata: cruise, station number, date and time, latitude, longitude, depth and QC flag.

The data were reformatted and assigned BODC parameter codes which were in equivalent units to the original data so no unit conversions were applied. Measurement data were duplicated at each depth and so the two measurements were averaged and the standard deviation calculated. Data were loaded in BODC's samples database under Oracle Relational Database Management System using established BODC data banking procedures. Sample metadata were checked against information held in the database were no discrepancies were found.

The originator's parameters were mapped to BODC parameter codes as follows:

Originator's Parameter Unit Description BODC Parameter Code BODC Unit Comments
AT μmol kg^-1 Total alkalinity per unit mass of the water body MDMAP014 μmol kg^-1
CT μmol kg^-1 Concentration of total inorganic carbon {TCO2 CAS 7440-44-0} per unit mass of the water body [dissolved plus reactive particulate phase] TCO2MSXX μmol kg^-1
Nitrite μM Concentration of nitrite {NO2- CAS 14797-65-0} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis NTRIAAD2 μmol L^-1
Nitrate μM Concentration of nitrate {NO3- CAS 14797-55-8} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis and correction for nitrite NTRAAA04 μmol L^-1
Ammonium μM Concentration of ammonium {NH4+ CAS 14798-03-9} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis AMONAAD2 μmol L^-1
Silicate μM Concentration of silicate {SiO44- CAS 17181-37-2} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis SLCAAAD2 μmol L^-1
Phosphate μM Concentration of phosphate {PO43- CAS 14265-44-2} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis PHOSAAD2 μmol L^-1
Omega_A Saturation state of aragonite in the water body by computation ARGTWCAL Dimensionless
pCO2 μatm Partial pressure of carbon dioxide {CO2 CAS 124-38-9} {pCO2} in the water body by computation PCO2WCAL Microatmospheres
pH_tot pH units pH (total scale) {pH[T]} per unit mass of the water body by computation PHTLWCAL pH units
CO3 2- μmol kg^-1 Concentration of carbonate ions {CO3} per unit mass of the water body by computation CRBTWCAL μmol kg^-1
CO2* μmol kg^-1 Concentration of carbon (total inorganic) {TCO2} per unit mass of the water body by computation TCO2WCAL μmol kg^-1
HCO3 - μmol kg^-1 Concentration of bicarbonate ions {HCO3} per unit mass of the water body by computation BCRBWCAL μmol kg^-1
Omega_C Saturation state of calcite in the water body by computation CLCTWCAL Dimensionless
Total alkalinity standard deviation per unit mass of the water body MDMASD14 μmol kg^-1 Replicate samples averaged and standard deviation calculated by BODC.
Concentration standard deviation of total inorganic carbon {TCO2 CAS 7440-44-0} per unit mass of the water body [dissolved plus reactive particulate phase] TCO2MSSD μmol kg^-1 Replicate samples averaged and standard deviation calculated by BODC.
Concentration standard deviation of nitrite {NO2- CAS 14797-65-0} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis SDNIAAD2 μmol L^-1 Replicate samples averaged and standard deviation calculated by BODC.
Concentration standard deviation of nitrate {NO3- CAS 14797-55-8} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis and correction for nitrite NTRAAA05 μmol L^-1 Replicate samples averaged and standard deviation calculated by BODC.
Concentration standard deviation of ammonium {NH4+ CAS 14798-03-9} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis SDAMAAD2 μmol L^-1 Replicate samples averaged and standard deviation calculated by BODC.
Concentration standard deviation of silicate {SiO44- CAS 17181-37-2} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis SDSLAAD2 μmol L^-1 Replicate samples averaged and standard deviation calculated by BODC.
Concentration of phosphate {PO43- CAS 14265-44-2} per unit volume of the water body [dissolved plus reactive particulate <0.4/0.45um phase] by filtration and colorimetric autoanalysis SDPHAAD2 μmol L^-1 Replicate samples averaged and standard deviation calculated by BODC.
Saturation state standard deviation of aragonite in the water body by computation ARSDWCAL Dimensionless Replicate samples averaged and standard deviation calculated by BODC.
Partial pressure standard deviation of carbon dioxide {CO2 CAS 124-38-9} {pCO2} in the water body by computation PCSDWCAL Microatmospheres Replicate samples averaged and standard deviation calculated by BODC.
pH standard deviation (total scale) {pH[T]} per unit mass of the water body by computation PHTLSDWC pH units Replicate samples averaged and standard deviation calculated by BODC.
Concentration standard deviation of carbonate ions {CO3} per unit mass of the water body by computation CRSDWCAL μmol kg^-1 Replicate samples averaged and standard deviation calculated by BODC.
Concentration standard deviation of carbon (total inorganic) {TCO2} per unit mass of the water body by computation TCSDWCAL μmol kg^-1 Replicate samples averaged and standard deviation calculated by BODC.
Concentration standard deviation of bicarbonate ions {HCO3} per unit mass of the water body by computation BCSDWCAL μmol kg^-1 Replicate samples averaged and standard deviation calculated by BODC.
Saturation state standard deviation of calcite in the water body by computation CLSDWCAL Dimensionless Replicate samples averaged and standard deviation calculated by BODC.

Data Quality Report

The originator applied flags to all submitted data according to the following key: 1 = Good Quality; 4 = Questionable Quality; 8 = Bad Quality. During BODC processing the flags were removed if the flag was 1 and the flag was changed to L if the flag was 4. There were no instances were the flag 8 was applied.

If a value was flagged then this value was omitted when calculating the average at each depth and so the measurement would be the unflagged value within the pair. In these cases standard deviations were not calculated. In cases where both values at a depth were flagged L the average and standard deviation were calculated with the average flagged L. In a departure from standard practice, the means and standard deviations were calculated after the values had been rounded to the number of decimal places appropriate to the parameter, instead of before. This has resulted in a slight loss of precision.

The originator has no concerns over the quality of the data as the data is consistent with similar data in the wider literature and so no further flagging has been applied by BODC.


Project Information

UKOARP Theme B: Ocean acidification impacts on sea surface biology, biogeochemistry and climate

The overall aim of this theme is to obtain a quantitative understanding of the impact of ocean acidification (OA) on the surface ocean biology and ecosystem and on the role of the surface ocean within the overall Earth System.

The aims of the theme are:

  • To ascertain the impact of OA on planktonic organisms (in terms of physiological impacts, morphology, population abundances and community composition).
  • To quantify the impacts of OA on biogeochemical processes affecting the ocean carbon cycle (both directly and indirectly, such as via availability of bio-limiting nutrients).
  • To quantify the impacts of OA on the air-sea flux of climate active gases (DMS and N2O in particular).

The main consortium activities will consist of in-situ measurements on three dedicated cruises, as well as on-deck bioassay experiments probing the response of the in-situ community to elevated CO2. Most of the planned work will be carried out on the three cruises to locations with strong gradients in seawater carbon chemistry and pH; the Arctic Ocean, around the British Isles and the Southern Ocean.

Weblink: http://www.oceanacidification.org.uk/research_programme/surface_ocean.aspx


Data Activity or Cruise Information

Data Activity

Start Date (yyyy-mm-dd) 2012-06-06
End Date (yyyy-mm-dd) 2012-06-06
Organization Undertaking ActivityHeriot Watt University School of Life Sciences (now Heriot-Watt University Institute of Life and Earth Sciences)
Country of OrganizationUnited Kingdom
Originator's Data Activity IdentifierJC073_CTD_CTD45
Platform Categorylowered unmanned submersible

BODC Sample Metadata Report for JC073_CTD_CTD45

Sample reference number Nominal collection volume(l) Bottle rosette position Bottle firing sequence number Minimum pressure sampled (dbar) Maximum pressure sampled (dbar) Depth of sampling point (m) Bottle type Sample quality flag Bottle reference Comments
872681   10.00 7 7  606.00  607.30  606.70 Niskin bottle No problem reported    
872684   10.00 8 8  605.90  606.90  606.30 Niskin bottle No problem reported    
872687   10.00 9 9  606.30  606.90  606.60 Niskin bottle No problem reported    
872690   10.00 10 10  605.80  607.20  606.60 Niskin bottle No problem reported    
872693   10.00 11 11  505.00  505.50  505.20 Niskin bottle No problem reported    
872696   10.00 12 12  505.00  505.90  505.60 Niskin bottle No problem reported    
872699   10.00 13 13  404.60  405.30  404.90 Niskin bottle No problem reported    
872702   10.00 14 14  404.60  405.40  405.10 Niskin bottle No problem reported    
872705   10.00 15 15  102.40  103.50  102.80 Niskin bottle No problem reported    
872708   10.00 16 16  102.80  103.40  103.20 Niskin bottle No problem reported    
872711   10.00 17 17   51.40   51.80   51.50 Niskin bottle No problem reported    
872714   10.00 18 18   51.20   52.30   51.60 Niskin bottle No problem reported    
872717   10.00 19 19   26.80   27.70   27.30 Niskin bottle No problem reported    
872720   20 20   26.80   27.20   27.00 Stand-alone pump No problem reported   SAP in place of Niskin bottle on the CTD cast.
872723   21 21    4.90    5.60    5.20 Stand-alone pump No problem reported   SAP in place of Niskin bottle on the CTD cast.
872726   10.00 22 22    4.70    6.00    5.50 Niskin bottle No problem reported    
872978   10.00 1 1  606.50  606.70  606.60 Niskin bottle No problem reported    
872981   10.00 2 2  606.10  606.70  606.30 Niskin bottle No problem reported    
872984   10.00 3 3  606.40  607.10  606.80 Niskin bottle No problem reported    
872987   10.00 4 4  606.20  606.90  606.60 Niskin bottle No problem reported    
872990   10.00 5 5  606.10  607.10  606.70 Niskin bottle No problem reported    
872993   10.00 6 6  606.30  607.10  606.70 Niskin bottle No problem reported    

Please note:the supplied parameters may not have been sampled from all the bottle firings described in the table above. Cross-match the Sample Reference Number above against the SAMPRFNM value in the data file to identify the relevant metadata.

Related Data Activity activities are detailed in Appendix 1

Cruise

Cruise Name JC073
Departure Date 2012-05-18
Arrival Date 2012-06-15
Principal Scientist(s)John Murray Roberts (Heriot Watt University School of Life 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

Appendix 1: JC073_CTD_CTD45

Related series for this Data Activity are presented in the table below. Further information can be found by following the appropriate links.

If you are interested in these series, please be aware we offer a multiple file download service. Should your credentials be insufficient for automatic download, the service also offers a referral to our Enquiries Officer who may be able to negotiate access.

Series IdentifierData CategoryStart date/timeStart positionCruise
2114563Water sample data2012-06-06 09:41:4155.48583 N, 15.80046 WRRS James Cook JC073