Metadata Report for BODC Series Reference Number 2282647
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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Data Identifiers |
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Time Co-ordinates(UT) |
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Spatial Co-ordinates | |||||||||||||||||||||||||||||||||||||
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Parameters |
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Definition of BOTTFLAG | |||||||||||||||||||||||||||||||||||||
| BOTTFLAG | Definition |
|---|---|
| 0 | The sampling event occurred without any incident being reported to BODC. |
| 1 | The filter in an in-situ sampling pump physically ruptured during sample resulting in an unquantifiable loss of sampled material. |
| 2 | Analytical 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. |
| 3 | The 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. |
| 4 | During 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. |
| 5 | Water was reported to be escaping from the bottle as the rosette was being recovered. |
| 6 | The bottle seals were observed to be incorrectly seated and the bottle was only part full of water on recovery. |
| 7 | Either 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). |
| 8 | There is reason to doubt the accuracy of the sampling depth associated with the sample. |
| 9 | The bottle air vent had not been closed prior to deployment giving rise to a risk of sample contamination through leakage. |
Definition of Rank |
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Problem Reports
No Problem Report Found in the Database
Data Access Policy
Open Data
These data have no specific confidentiality restrictions for users. However, users must acknowledge data sources as it is not ethical to publish data without proper attribution. Any publication or other output resulting from usage of the data should include an acknowledgment.
If the Information Provider does not provide a specific attribution statement, or if you are using Information from several Information Providers and multiple attributions are not practical in your product or application, you may consider using the following:
"Contains public sector information licensed under the Open Government Licence v1.0."
Narrative Documents
Metrohm 794 Basic Titrino Titrator
The Metrohm 794 Basic Titrino is an all-purpose titrator used for dynamic and monotonic determination of solution concentrations. Titration modes of the instrument are constant or depending on the titration curve variable dosing of the titration reagent and Endpoint-Titration. The operation modes include; Dynamic Equivalence-point Titration (DET), Monotonic Equivalence-point Titration (MET), Set Endpoint Titration (SET), pH Calibration (CAL), Measuring (MEAS) and Titration Procedure (TIP) which links various commands and methods to a titration procedure. All operating modes of the Titrino can be combined to perform extensive analytical sequences.
Ready-to-start methods for the most common applications are stored in the internal method memory for example; the determination of the hardness of drinking water, diazotation of sulfonamides and primary amines, and determination of the peroxid number of edible oil sand fats. The operator is free to modify and overwrite the methods or to create and store new titration sequences.
The instrument consists of an exchange unit with a small display, which can be connected to either a magnetic stirrer (728), propeller rod stirrer (802) or Ti stand (703 or 727). Data exchange with a PC is possible with the Metrodata VESUV Software and with Metrodata TiNet Software complete keypad remote control, data acquisition and evaluation via PC is enabled.
Further details can be found in the manufacturer's user manual.
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.
UKOA JR20120601 dissolved oxygen concentrations from CTD bottle samples and underway samples
Originator's Protocol for Data Acquisition and Analysis
Water samples were collected from a selected number of CTD casts for calibration of the CTD oxygen sensor. Seventeen CTDs were sampled for dissolved oxygen (DO) which were the first samples to be drawn from the Niskin bottles. Duplicate samples were collected from on average 6 depths. Seawater was collected directly into pre-calibrated glass bottles using a Tygon tube. Before the sample was drawn, the bottles were flushed with seawater for several seconds (for about 3 times the volume of the bottle) and the temperature of the water was recorded simultaneously using a handheld thermometer. The fixing reagents (manganese chloride and sodium hydroxide/sodium iodide solutions) were then added. Care was taken to avoid bubbles inside the sampling tube and sampling bottle. Samples were thoroughly mixed following the addition of the fixing reagents and were then kept in a dark plastic crate for 30 to 40 minutes to allow the precipitate to settle to <50% the volume of the bottle. Once the precipitate had settled all samples were thoroughly mixed for a second time in order to maximize the efficiency of the reaction.
Dissolved oxygen determinations were made using a Winkler O-Metrohm titration unit (794 DMS Titrino) with an amperometric system to determine the end point of the titration (Culberson and Huang, 1987). Chemical reagents were previously prepared at NOCS following the procedures described by Dickson (1994). Recommendations given by Dickson (1994), and by Holley and Hydes (1994) were adopted. In general, thiosulphate calibrations were carried out twice a week using a 1.667 mmol L-1 certified OSIL iodate standard, with the aid of a O-Metrohm 776 Dosimat unit. The thiosulphate solution was prepared at the beginning of the cruise by dissolving 50 g of sodium thiosulphate in 1L of MilliQ water. This solution was left to stabilize for 24 hours before the initial calibration, with a subsequent calibration 12 hours later to ensure the thiosulphate had stabilized.
References Cited
Culberson, C.H. and Huang, S. 1987. Automated amperometric oxygen titration. Deep Sea Research, 34, 875-880.
Dickson, A.G. 1994., Determination of dissolved oxygen in seawater by Winkler titration. Technical report, WOCE operations manual, WOCE report 68/91 Revision 1 November 1994.
Holley, S.E. and Hydes, D.J. 1994. Procedures for the determination of dissolved oxygen in seawater. Technical report, James Rennell Centre for Ocean Circulation.
Instrumentation Description
Metrohm 794 Basic Titrino Titrator
BODC Data Processing Procedures
Data were submitted in individual Excel spreadsheets for each CTD cast and archived under BODC's accession number DML120164. Sample metadata (Station, CTD cast, bottle number and depth) were checked against information held in the database. There were several discrepancies in the cast dates between the files and the database, but the data were loaded with the dates already in the database. Underway samples were provided with the same metadata as the CTD casts.
The concentration data were provided in micro-moles per litre. These units match the BODC parameter code units and a unit conversion was not applied. Where replicate measurements were provided the mean and standard deviation were calculated and loaded to the database. The standard deviation of oxygen fixation temperature was not loaded to the database. These data are available on request.
The data were reformatted and loaded in BODC's samples database under Oracle Relational Database Management System. Data were marked up with BODC parameter codes and loaded into the database.
A parameter mapping table is provided below;
| Originator's Parameter | Units | Description | BODC Parameter Code | Units | Comments |
|---|---|---|---|---|---|
| Fixing temp | degrees Celsius | Temperature of oxygen fixation | OXYTMP01 | degrees Celsius | n/a |
| Oxygen | µmol l-1 | Concentration of oxygen {O2} per unit volume of the water body [dissolved phase] by Winkler titration | DOXYWITX | µmol l-1 | n/a |
| - | - | Concentration standard deviation of oxygen {O2} per unit volume of the water body [dissolved phase] by Winkler titration | SDOXWITX | µmol l-1 | n/a |
Data Quality Report
The data from cast 10, depth 5 m and from cast 63, 30 m were flagged as suspect by the data originator. These samples have been marked as improbable in the database. No values were flagged by BODC.
Problem Report
Not relevant to this data set.
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) | 2012-06-08 |
| End Date (yyyy-mm-dd) | 2012-06-08 |
| Organization Undertaking Activity | Scottish Association for Marine Science |
| Country of Organization | United Kingdom |
| Originator's Data Activity Identifier | JR20120601_CTD_CTD017s |
| Platform Category | lowered unmanned submersible |
BODC Sample Metadata Report for JR20120601_CTD_CTD017s
| 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 |
|---|---|---|---|---|---|---|---|---|---|---|
| 757430 | 20.00 | 1 | 1 | 278.50 | 281.60 | 276.50 | Niskin bottle | No problem reported | ||
| 757433 | 20.00 | 2 | 2 | 279.00 | 281.00 | 276.40 | Niskin bottle | Bottle leak | ||
| 757436 | 20.00 | 3 | 3 | 151.00 | 151.60 | 149.10 | Niskin bottle | No problem reported | ||
| 757439 | 20.00 | 4 | 4 | 149.80 | 151.80 | 148.60 | Niskin bottle | No problem reported | ||
| 757442 | 20.00 | 5 | 5 | 100.60 | 102.00 | 99.60 | Niskin bottle | No problem reported | ||
| 757445 | 20.00 | 6 | 6 | 101.10 | 102.30 | 100.00 | Niskin bottle | No problem reported | ||
| 757448 | 20.00 | 7 | 7 | 80.90 | 81.40 | 79.60 | Niskin bottle | No problem reported | ||
| 757451 | 20.00 | 8 | 8 | 80.80 | 81.50 | 79.60 | Niskin bottle | No problem reported | ||
| 757454 | 20.00 | 9 | 9 | 60.40 | 61.70 | 59.70 | Niskin bottle | No problem reported | ||
| 757457 | 20.00 | 10 | 10 | 60.50 | 61.10 | 59.50 | Niskin bottle | Bottle leak | ||
| 757460 | 20.00 | 11 | 11 | 39.60 | 41.00 | 39.20 | Niskin bottle | No problem reported | ||
| 757463 | 20.00 | 12 | 12 | 39.70 | 41.80 | 39.60 | Niskin bottle | No problem reported | ||
| 757466 | 20.00 | 13 | 13 | 30.60 | 31.50 | 30.00 | Niskin bottle | No problem reported | ||
| 757469 | 20.00 | 14 | 14 | 30.60 | 31.00 | 29.80 | Niskin bottle | No problem reported | ||
| 757472 | 20.00 | 15 | 15 | 30.70 | 30.90 | 29.80 | Niskin bottle | No problem reported | ||
| 757475 | 20.00 | 16 | 16 | 30.20 | 31.10 | 29.60 | Niskin bottle | No problem reported | ||
| 757478 | 20.00 | 17 | 17 | 19.90 | 20.70 | 19.40 | Niskin bottle | No problem reported | ||
| 757481 | 20.00 | 18 | 18 | 20.00 | 20.70 | 19.40 | Niskin bottle | No problem reported | ||
| 757484 | 20.00 | 19 | 19 | 19.60 | 21.10 | 19.40 | Niskin bottle | No problem reported | ||
| 757487 | 20.00 | 20 | 20 | 20.40 | 20.90 | 19.70 | Niskin bottle | Bottle leak | ||
| 757490 | 20.00 | 21 | 21 | 6.90 | 7.60 | 6.40 | Niskin bottle | No problem reported | ||
| 757493 | 20.00 | 22 | 22 | 6.80 | 7.70 | 6.40 | Niskin bottle | No problem reported | ||
| 757496 | 20.00 | 23 | 23 | 7.00 | 7.90 | 6.60 | Niskin bottle | No problem reported | ||
| 757499 | 20.00 | 24 | 24 | 7.20 | 7.70 | 6.60 | 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 | JR20120601 (JR271) |
| Departure Date | 2012-06-01 |
| Arrival Date | 2012-07-02 |
| Principal Scientist(s) | Ray Leakey (Scottish Association for Marine Science) |
| Ship | RRS James Clark Ross |
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: JR20120601_CTD_CTD017s
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 Identifier | Data Category | Start date/time | Start position | Cruise |
|---|---|---|---|---|
| 2280930 | Water sample data | 2012-06-08 06:27:30 | 60.59422 N, 18.85645 W | RRS James Clark Ross JR20120601 (JR271) |
| 2282820 | Water sample data | 2012-06-08 06:27:30 | 60.59422 N, 18.85645 W | RRS James Clark Ross JR20120601 (JR271) |
| 2283976 | Water sample data | 2012-06-08 06:27:30 | 60.59422 N, 18.85645 W | RRS James Clark Ross JR20120601 (JR271) |
| 2284470 | Water sample data | 2012-06-08 06:27:30 | 60.59422 N, 18.85645 W | RRS James Clark Ross JR20120601 (JR271) |
| 2288575 | Water sample data | 2012-06-08 06:27:30 | 60.59422 N, 18.85645 W | RRS James Clark Ross JR20120601 (JR271) |
| 2289056 | Water sample data | 2012-06-08 06:27:30 | 60.59422 N, 18.85645 W | RRS James Clark Ross JR20120601 (JR271) |
| 1860218 | Water sample data | 2012-06-08 06:28:00 | 60.59422 N, 18.85645 W | RRS James Clark Ross JR20120601 (JR271) |


