Metadata Report for BODC Series Reference Number 2283884
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
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.
Solid Phase Chemistry for cruise Charles Darwin CD92A
Document History
Converted from CDROM documentation.
Content of data series
| ALCNXMXT | Bulk sediment aluminium content |
| X-ray fluorescence on flux diluted fused bead | |
| Per cent | |
| BACNXTXT | Bulk sediment barium content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| BRCNXTXT | Bulk sediment bromine content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| CACNXMXT | Bulk sediment calcium content |
| X-ray fluorescence on flux diluted fused bead | |
| Per cent | |
| CECNXTXT | Bulk sediment cerium content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| CRCNXTXT | Bulk sediment chromium content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| CUCNS1XT | Loosely held bulk sediment copper content |
| AA assay of Chester et al. (1988) Stage 1 leachate (1M ammonium acetate at pH 7) | |
| Parts per million | |
| CUCNS2XT | Carbonate and surface associated bulk sediment copper content |
| AA assay of Chester et al. (1988) Stage 2 leachate (1M sodium acetate at pH 5) | |
| Parts per million | |
| CUCNS3XT | Easily reducible bulk sediment copper content |
| AA assay of Chester et al. Stage 3 leachate (1M Na acetate (pH5)/0.25M hydroxylamine hydrochloride) | |
| Parts per million | |
| CUCNS4XT | Moderately reducible bulk sediment copper content |
| AA assay of Chester et al. Stage 4 leachate (0.25M hydroxylamine hydrochloride/25pc acetic acid) | |
| Parts per million | |
| CUCNS5XT | Organic matter and sulphide associated bulk sediment Cu content |
| AA assay of Chester et al. (1988) Stage 5 leachate (H2O2/1M ammonium acetate (pH2)) | |
| Parts per million | |
| CUCNSTXT | Bulk sediment copper content |
| Sum of AA determinations on Chester et al. (1988) staged leachates | |
| Parts per million | |
| CUCNXTXT | Bulk sediment copper content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| FECNS2XT | Carbonate and surface associated bulk sediment iron content |
| AA assay of Chester et al. (1988) Stage 2 leachate (1M sodium acetate at pH 5 | |
| Per cent | |
| FECNS3XT | Easily reducible bulk sediment iron content |
| AA assay of Chester et al. Stage 3 leachate (1M Na acetate (pH5)/0.25M hydroxylamine hydrochloride) | |
| Per cent | |
| FECNS4XT | Moderately reducilble bulk sediment iron content |
| AA assay of Chester et al. Stage 4 leachate (0.25M hydroxylamine hydrochloride/25pc acetic acid) | |
| Per cent | |
| FECNS5XT | Organic matter and sulphide associated bulk sediment Fe content |
| AA assay of Chester et al. (1988) Stage 5 leachate (H2O2/1M ammonium acetate (pH2)) | |
| Per cent | |
| FECNSTXT | Bulk sediment iron content |
| Summation of AA determinations on Chester et al. (1988) staged leachates | |
| Per cent | |
| FECNXMXT | Bulk sediment total iron content |
| X-ray fluorescence on flux diluted fused bead | |
| Per cent | |
| IXCNXTXT | Bulk sediment iodine content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| KXCNXMXT | Bulk sediment potassium content |
| X-ray fluorescence on flux diluted fused bead | |
| Per cent | |
| LACNXTXT | Bulk sediment lanthanum content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| MGCNXMXT | Bulk sediment magnesium content |
| X-ray fluorescence on flux diluted fused bead | |
| Per cent | |
| MNCNS1XT | Loosely held bulk sediment manganese content |
| AA assay of Chester et al. (1988) Stage 1 leachate (1M Ammonium acetate at pH 7) | |
| Per cent | |
| MNCNS2XT | Carbonate and surface associated bulk sediment Mn content |
| AA assay of Chester et al. (1988) Stage 2 leachate (1M sodium acetate at pH 5 | |
| Per cent | |
| MNCNS3XT | Easily reducible bulk sediment manganese content |
| AA assay of Chester et al. Stage 3 leachate (1M Na acetate (pH5)/0.25M hydroxylamine hydrochloride) | |
| Per cent | |
| MNCNS4XT | Moderately reducible bulk sediment manganese content |
| AA assay of Chester et al. Stage 4 leachate (0.25M hydroxylamine hydrochloride/25pc acetic acid) | |
| Per cent | |
| MNCNS5XT | Organic matter and sulphide associated bulk sediment Mn content |
| AA assay of Chester et al. (1988) Stage 5 leachate (H2O2/1M ammonium acetate (pH2)) | |
| Per cent | |
| MNCNSTXT | Bulk sediment manganese content |
| Sum of AA determinations on Chester et al. (1988) staged leachates | |
| Per cent | |
| MNCNXMXT | Bulk sediment total manganese content |
| X-ray fluorescence on flux diluted fused bead | |
| Per cent | |
| MOCNXTXT | Bulk sediment molybdenum content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| NACNXMXT | Bulk sediment sodium content |
| X-ray fluorescence on flux diluted fused bead | |
| Per cent | |
| NBCNXTXT | Bulk sediment niobium content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| NDCNXTXT | Bulk sediment neodymium content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| NICNXTXT | Bulk sediment nickel content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| PBCNXTXT | Bulk sediment lead content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| PXCNXMXT | Bulk sediment phosphorus content |
| X-ray fluorescence on flux diluted fused bead | |
| Per cent | |
| RBCNXTXT | Bulk sediment rubidium content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| SCCNXTXT | Bulk sediment scandium content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| SICNXMXT | Bulk sediment silicon content |
| X-ray fluorescence on flux diluted fused bead | |
| Per cent | |
| SRCNXTXT | Bulk sediment strontium content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| THCNXTXT | Bulk sediment thorium content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| TICNXMXT | Bulk sediment titanium content |
| X-ray fluorescence on flux diluted fused bead | |
| Per cent | |
| TRISMBBS | Bulk sediment total reduced inorganic sulphur |
| Methylene blue colorimetry | |
| Milligrams per gram of dry sediment | |
| UXCNXTXT | Bulk sediment uranium content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| VXCNXTXT | Bulk sediment vanadium content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| YXCNXTXT | Bulk sediment yttrium content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| ZNCNXTXT | Bulk sediment zinc content |
| X-ray fluorescence on pressed powder | |
| Parts per million | |
| ZRCNXTXT | Bulk sediment zirconium content |
| X-ray fluorescence on pressed powder | |
| Parts per million |
Data Originator
Dr Graham Shimmield, CCMS Dunstaffnage Marine Laboratory, UK.
Sampling strategy and methodology
Samples were collected using a multicorer of standard design (Barnett et al., 1984), at four sites (S700, R1000, N1500, N2000). The cores were sliced into 0.5cm intervals for 10cm and 1cm for the remainder of the core (all cores were less than 30cm in length). Three replicate samples were collected from separate deployments of the multicorer at each site. Trace metal analysis was completed on cores from all four sites. Analysis for the major elements was not carried out on the core from site N2000.
Major elements
1g of dried sediment was accurately weighed into a platinum crucible and an ultra-pure lithium tetraborate flux, Spectroflux 105 (Johnson-Matthey Chemicals Ltd.) added in a ratio 5:1 (flux to sample). This was placed in a muffle furnace at 1100°C for 20 minutes. After cooling the slight weight loss was made up with the addition of Spetroflux 105. The mixture was reheated on a gas burner until the glass melted.
The molten liquid was poured onto a graphite mould contained inside a brass sleeve (on a hotplate at 220°C) and pressed with an aluminum plunger to produce a 45mm diameter glass disc approximately 1mm thick. After cooling, the discs were stored in a desiccator.
They were analysed for a series of major elements (Si, Al, Fe, Mg, Ca, Na, K, Ti, Mn and P) using a Phillips PW 1450 sequential automatic X-ray spectrometer.
Trace elements
3g of dried sediment was accurately weighed and placed in a stainless steel sleeve resting on a highly polished tungsten carbide disc. Both the sleeve and cylinder were enclosed within a larger stainless steel cylinder. A Perspex plunger was inserted into the sleeve and the powder was compacted into a semi-competent disc using hand pressure.
The Perspex plunger and sleeve were removed and sufficient boric acid to cover the sediment disc was added. A large stainless steel plunger was lowered onto the sample and placed under a hydraulic press where 10 tons of pressure was used to compress the sample.
This pressed powder disc with boric acid backing was analysed for a series of trace elements (Sc, Ba, V, La, Ce, Nd, Cr, Ni, Cu, Zn, Pb, Th, U, Rb, Sr, Y, Zr, Nb, Mo, I and Br) using a Phillips PW 1450 sequential automatic X-ray spectrometer.
Both major and trace elements were corrected for the presence of residual sea-salt.
References
Barnett P.R.O., Watson J. and Connelly D., 1984. A multiple corer for taking virtually undisturbed samples from shelf, bathyal and abyssal sediments. Oceanol. Acta, 7, 399-408.
Chester R., Thomas A., Lin F.J., Basaham A.S. and Jacinto G., 1988. The solid state speciation of copper in surface water particulates and oceanic sediments. Marine Chemistry 24, 261-292.
Cline J.D., 1969. Spectrophotometric determination of hydrogen sulfide in natural waters. Limnol. Oceanogr. 14, 454-458
Project Information
LOIS Shelf Edge Study (LOIS - SES)
Introduction
SES was a component of the NERC Land Ocean Interaction Study (LOIS) Community Research Programme that made intensive measurements from the shelf break in the region known as the Hebridean Slope from March 1995 to September 1996.
Scientific Rationale
SES was devoted to the study of interactions between the shelf seas and the open ocean. The specific objectives of the project were:
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To identify the time and space scales of ocean-shelf momentum transmission and to quantify the contributions to ocean-shelf water exchange by physical processes.
-
To estimate fluxes of water, heat and certain dissolved and suspended constituents across a section of the shelf edge with special emphasis on net carbon export from, and nutrient import to, the shelf.
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To incorporate process understanding into models and test these models by comparison with observations and provide a basis for estimation of fluxes integrated over time and the length of the shelf.
Fieldwork
The SES fieldwork was focussed on a box enclosing two sections across the shelf break at 56.4-56.5 °N and 56.6-56.7 °N. Moored instrument arrays were maintained throughout the experiment at stations with water depths ranging from 140 m to 1500 m, although there were heavy losses due to the intensive fishing activity in the area. The moorings included meteorological buoys, current meters, transmissometers, fluorometers, nutrient analysers (but these never returned any usable data), thermistor chains, colour sensors and sediment traps.
The moorings were serviced by research cruises at approximately three-monthly intervals. In addition to the mooring work this cruises undertook intensive CTD, water bottle and benthic surveys with cruise durations of up to 6 weeks (3 legs of approximately 2 weeks each).
Moored instrument activities associated with SES comprised current measurements in the North Channel in 1993 and the Tiree Passage from 1995-1996. These provided boundary conditions for SES modelling activities.
Additional data were provided through cruises undertaken by the Defence Evaluation and Research Agency (DERA) in a co-operative programme known as SESAME.
Data Activity or Cruise Information
Data Activity
| Start Date (yyyy-mm-dd) | 1995-12-11 |
| End Date (yyyy-mm-dd) | 1995-12-11 |
| Organization Undertaking Activity | Dunstaffnage Marine Laboratory (now Scottish Association for Marine Science) |
| Country of Organization | United Kingdom |
| Originator's Data Activity Identifier | CH123B_CTD_CTD63 |
| Platform Category | lowered unmanned submersible |
BODC Sample Metadata Report for CH123B_CTD_CTD63
| 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 |
|---|---|---|---|---|---|---|---|---|---|---|
| 79541 | 10.00 | 1008.80 | 1012.00 | 994.60 | Niskin bottle | No problem reported | ||||
| 79542 | 10.00 | 506.40 | 510.50 | 499.10 | Niskin bottle | No problem reported | ||||
| 79543 | 10.00 | 254.90 | 259.10 | 250.40 | Niskin bottle | No problem reported | ||||
| 79544 | 10.00 | 99.70 | 104.50 | 97.00 | Niskin bottle | No problem reported | ||||
| 79545 | 10.00 | 50.20 | 52.90 | 47.00 | Niskin bottle | No problem reported | ||||
| 79546 | 10.00 | 28.60 | 33.00 | 26.40 | Niskin bottle | No problem reported | ||||
| 79547 | 10.00 | 10.90 | 13.30 | 7.90 | 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 | CH123B |
| Departure Date | 1995-12-01 |
| Arrival Date | 1995-12-15 |
| Principal Scientist(s) | Ken Jones (Dunstaffnage Marine Laboratory) |
| Ship | RRS Challenger |
Complete Cruise Metadata Report is available here
Fixed Station Information
Fixed Station Information
| Station Name | LOIS (SES) Repeat Section R |
| Category | Offshore route/traverse |
LOIS (SES) Repeat Section R
Section R was one of four repeat sections sampled during the Land-Ocean Interaction Study (LOIS) Shelf Edge Study (SES) project between March 1995 and September 1996.
The CTD measurements collected at repeat section R, on the Hebridean Slope, lie within a box bounded by co-ordinates 56° 29.4' N, 9° 41.4' W at the southwest corner and 56° 32.4' N, 8° 55.8' W at the northeast corner.
Cruises occupying section R
| Cruise | Start Date | End Date |
|---|---|---|
| Charles Darwin 91B | 22/03/1995 | 02/04/1995 |
| Charles Darwin 93A | 07/05/1995 | 16/05/1995 |
| Charles Darwin 93B | 16/05/1995 | 30/05/1995 |
| Tydeman SESAME-1 | 10/08/1995 | 11/09/1995 |
| Challenger 121B | 18/08/1995 | 01/09/1995 |
| Challenger 121C | 01/09/1995 | 10/09/1995 |
| Challenger 123A | 15/11/1995 | 29/11/1995 |
| Challenger 123B | 01/12/1995 | 15/12/1995 |
| Challenger 124 | 08/01/1996 | 27/01/1996 |
| Challenger 125A | 31/01/1996 | 12/02/1996 |
| Challenger 125B | 13/02/1996 | 03/03/1996 |
| Challenger 126B | 27/04/1996 | 12/05/1996 |
| Challenger 128A | 10/07/1996 | 26/07/1996 |
| Challenger 128B | 26/07/1996 | 08/08/1996 |
Related Fixed Station activities are detailed in Appendix 2
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: CH123B_CTD_CTD63
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 |
|---|---|---|---|---|
| 2282229 | Water sample data | 1995-12-11 19:47:30 | 56.51582 N, 9.29567 W | RRS Challenger CH123B |
| 2288004 | Water sample data | 1995-12-11 19:47:30 | 56.51582 N, 9.29567 W | RRS Challenger CH123B |
| 2289530 | Water sample data | 1995-12-11 19:47:30 | 56.51582 N, 9.29567 W | RRS Challenger CH123B |
Appendix 2: LOIS (SES) Repeat Section R
Related series for this Fixed Station 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 |
|---|---|---|---|---|
| 847974 | CTD or STD cast | 1995-03-28 13:02:00 | 56.49 N, 9.01017 W | RRS Charles Darwin CD91B |
| 852859 | CTD or STD cast | 1995-05-11 20:39:00 | 56.51883 N, 9.2855 W | RRS Charles Darwin CD93A |
| 2249773 | Water sample data | 1995-05-11 21:05:30 | 56.51887 N, 9.28545 W | RRS Charles Darwin CD93A |
| 2252387 | Water sample data | 1995-05-11 21:05:30 | 56.51887 N, 9.28545 W | RRS Charles Darwin CD93A |
| 2256561 | Water sample data | 1995-05-11 21:05:30 | 56.51887 N, 9.28545 W | RRS Charles Darwin CD93A |
| 2257392 | Water sample data | 1995-05-11 21:05:30 | 56.51887 N, 9.28545 W | RRS Charles Darwin CD93A |
| 2259626 | Water sample data | 1995-05-11 21:05:30 | 56.51887 N, 9.28545 W | RRS Charles Darwin CD93A |
| 849213 | CTD or STD cast | 1995-05-20 08:35:00 | 56.50067 N, 8.93217 W | RRS Charles Darwin CD93B |
| 848639 | CTD or STD cast | 1995-05-20 09:53:00 | 56.50367 N, 8.99083 W | RRS Charles Darwin CD93B |
| 848640 | CTD or STD cast | 1995-05-20 11:09:00 | 56.506 N, 9.04 W | RRS Charles Darwin CD93B |
| 849225 | CTD or STD cast | 1995-05-20 13:02:00 | 56.505 N, 9.05933 W | RRS Charles Darwin CD93B |
| 848652 | CTD or STD cast | 1995-05-20 14:40:00 | 56.50783 N, 9.10683 W | RRS Charles Darwin CD93B |
| 848664 | CTD or STD cast | 1995-05-20 15:58:00 | 56.51533 N, 9.17183 W | RRS Charles Darwin CD93B |
| 849237 | CTD or STD cast | 1995-05-20 17:12:00 | 56.51317 N, 9.232 W | RRS Charles Darwin CD93B |
| 848676 | CTD or STD cast | 1995-05-20 18:38:00 | 56.516 N, 9.296 W | RRS Charles Darwin CD93B |
| 848688 | CTD or STD cast | 1995-05-20 20:54:00 | 56.53067 N, 9.48833 W | RRS Charles Darwin CD93B |
| 849249 | CTD or STD cast | 1995-05-20 23:04:00 | 56.538 N, 9.6765 W | RRS Charles Darwin CD93B |
| 848793 | CTD or STD cast | 1995-05-21 23:56:00 | 56.51983 N, 9.285 W | RRS Charles Darwin CD93B |
| 849286 | CTD or STD cast | 1995-05-22 02:23:00 | 56.51567 N, 9.28983 W | RRS Charles Darwin CD93B |
| 848800 | CTD or STD cast | 1995-05-22 04:04:00 | 56.51633 N, 9.2895 W | RRS Charles Darwin CD93B |
| 848812 | CTD or STD cast | 1995-05-22 06:11:00 | 56.51767 N, 9.29733 W | RRS Charles Darwin CD93B |
| 849342 | CTD or STD cast | 1995-05-22 08:44:00 | 56.51733 N, 9.2925 W | RRS Charles Darwin CD93B |
| 848824 | CTD or STD cast | 1995-05-22 10:35:00 | 56.51917 N, 9.29067 W | RRS Charles Darwin CD93B |
| 851217 | CTD or STD cast | 1995-08-22 14:52:00 | 56.50667 N, 9.05967 W | RRS Challenger CH121B |
| 1287421 | Water sample data | 1995-08-22 15:07:00 | 56.5066 N, 9.05972 W | RRS Challenger CH121B |
| 852128 | CTD or STD cast | 1995-09-03 20:42:00 | 56.49917 N, 8.93417 W | RRS Challenger CH121C |
| 851936 | CTD or STD cast | 1995-09-03 21:40:00 | 56.50483 N, 9.03733 W | RRS Challenger CH121C |
| 851948 | CTD or STD cast | 1995-09-03 22:18:00 | 56.50583 N, 9.06167 W | RRS Challenger CH121C |
| 851961 | CTD or STD cast | 1995-09-03 23:13:00 | 56.50967 N, 9.11833 W | RRS Challenger CH121C |
| 852141 | CTD or STD cast | 1995-09-04 00:07:00 | 56.51517 N, 9.18467 W | RRS Challenger CH121C |
| 851973 | CTD or STD cast | 1995-09-04 01:21:00 | 56.51867 N, 9.30033 W | RRS Challenger CH121C |
| 851997 | CTD or STD cast | 1995-09-04 20:42:00 | 56.519 N, 9.29967 W | RRS Challenger CH121C |
| 854830 | CTD or STD cast | 1995-11-27 01:51:00 | 56.51767 N, 9.2985 W | RRS Challenger CH123A |
| 2249484 | Water sample data | 1995-11-27 02:20:30 | 56.51759 N, 9.29842 W | RRS Challenger CH123A |
| 2249853 | Water sample data | 1995-11-27 02:20:30 | 56.51759 N, 9.29842 W | RRS Challenger CH123A |
| 2252781 | Water sample data | 1995-11-27 02:20:30 | 56.51759 N, 9.29842 W | RRS Challenger CH123A |
| 855685 | CTD or STD cast | 1995-12-07 05:34:00 | 56.52767 N, 9.288 W | RRS Challenger CH123B |
| 2281761 | Water sample data | 1995-12-07 06:14:30 | 56.52767 N, 9.28803 W | RRS Challenger CH123B |
| 2285553 | Water sample data | 1995-12-07 06:14:30 | 56.52767 N, 9.28803 W | RRS Challenger CH123B |
| 2287627 | Water sample data | 1995-12-07 06:14:30 | 56.52767 N, 9.28803 W | RRS Challenger CH123B |
| 855697 | CTD or STD cast | 1995-12-07 07:23:00 | 56.51767 N, 9.28667 W | RRS Challenger CH123B |
| 2281773 | Water sample data | 1995-12-07 07:56:00 | 56.51773 N, 9.28667 W | RRS Challenger CH123B |
| 2285565 | Water sample data | 1995-12-07 07:56:00 | 56.51773 N, 9.28667 W | RRS Challenger CH123B |
| 2287639 | Water sample data | 1995-12-07 07:56:00 | 56.51773 N, 9.28667 W | RRS Challenger CH123B |
| 855765 | CTD or STD cast | 1995-12-07 14:26:00 | 56.51717 N, 9.29483 W | RRS Challenger CH123B |
| 2281785 | Water sample data | 1995-12-07 14:33:00 | 56.51713 N, 9.29479 W | RRS Challenger CH123B |
| 2285577 | Water sample data | 1995-12-07 14:33:00 | 56.51713 N, 9.29479 W | RRS Challenger CH123B |
| 855704 | CTD or STD cast | 1995-12-07 15:19:00 | 56.51767 N, 9.177 W | RRS Challenger CH123B |
| 2281797 | Water sample data | 1995-12-07 15:41:00 | 56.51764 N, 9.17706 W | RRS Challenger CH123B |
| 2285589 | Water sample data | 1995-12-07 15:41:00 | 56.51764 N, 9.17706 W | RRS Challenger CH123B |
| 2287640 | Water sample data | 1995-12-07 15:41:00 | 56.51764 N, 9.17706 W | RRS Challenger CH123B |
| 855894 | CTD or STD cast | 1995-12-07 17:16:00 | 56.52783 N, 9.10217 W | RRS Challenger CH123B |
| 2281804 | Water sample data | 1995-12-07 17:37:00 | 56.52777 N, 9.10217 W | RRS Challenger CH123B |
| 2285590 | Water sample data | 1995-12-07 17:37:00 | 56.52777 N, 9.10217 W | RRS Challenger CH123B |
| 2287652 | Water sample data | 1995-12-07 17:37:00 | 56.52777 N, 9.10217 W | RRS Challenger CH123B |
| 854946 | CTD or STD cast | 1995-12-07 18:31:00 | 56.51017 N, 9.05117 W | RRS Challenger CH123B |
| 2281816 | Water sample data | 1995-12-07 18:46:00 | 56.51011 N, 9.05116 W | RRS Challenger CH123B |
| 2285608 | Water sample data | 1995-12-07 18:46:00 | 56.51011 N, 9.05116 W | RRS Challenger CH123B |
| 2287664 | Water sample data | 1995-12-07 18:46:00 | 56.51011 N, 9.05116 W | RRS Challenger CH123B |
| 855716 | CTD or STD cast | 1995-12-07 19:21:00 | 56.50633 N, 9.03967 W | RRS Challenger CH123B |
| 2281828 | Water sample data | 1995-12-07 19:32:00 | 56.50629 N, 9.03962 W | RRS Challenger CH123B |
| 2285621 | Water sample data | 1995-12-07 19:32:00 | 56.50629 N, 9.03962 W | RRS Challenger CH123B |
| 2287676 | Water sample data | 1995-12-07 19:32:00 | 56.50629 N, 9.03962 W | RRS Challenger CH123B |
| 855728 | CTD or STD cast | 1995-12-07 20:25:00 | 56.5045 N, 8.93233 W | RRS Challenger CH123B |
| 2281841 | Water sample data | 1995-12-07 20:32:30 | 56.50455 N, 8.93237 W | RRS Challenger CH123B |
| 2285633 | Water sample data | 1995-12-07 20:32:30 | 56.50455 N, 8.93237 W | RRS Challenger CH123B |
| 2287688 | Water sample data | 1995-12-07 20:32:30 | 56.50455 N, 8.93237 W | RRS Challenger CH123B |
| 855114 | CTD or STD cast | 1995-12-10 22:03:00 | 56.53 N, 9.66833 W | RRS Challenger CH123B |
| 2282162 | Water sample data | 1995-12-10 22:49:00 | 56.53001 N, 9.66836 W | RRS Challenger CH123B |
| 2285946 | Water sample data | 1995-12-10 22:49:00 | 56.53001 N, 9.66836 W | RRS Challenger CH123B |
| 2287965 | Water sample data | 1995-12-10 22:49:00 | 56.53001 N, 9.66836 W | RRS Challenger CH123B |
| 855925 | CTD or STD cast | 1995-12-11 16:28:00 | 56.51483 N, 9.296 W | RRS Challenger CH123B |
| 2282205 | Water sample data | 1995-12-11 16:59:30 | 56.51482 N, 9.29605 W | RRS Challenger CH123B |
| 2287989 | Water sample data | 1995-12-11 16:59:30 | 56.51482 N, 9.29605 W | RRS Challenger CH123B |
| 2289462 | Water sample data | 1995-12-11 16:59:30 | 56.51482 N, 9.29605 W | RRS Challenger CH123B |
| 855126 | CTD or STD cast | 1995-12-11 17:59:00 | 56.51533 N, 9.29383 W | RRS Challenger CH123B |
| 2282217 | Water sample data | 1995-12-11 18:27:00 | 56.51541 N, 9.29389 W | RRS Challenger CH123B |
| 2283872 | Water sample data | 1995-12-11 18:27:00 | 56.51541 N, 9.29389 W | RRS Challenger CH123B |
| 2287990 | Water sample data | 1995-12-11 18:27:00 | 56.51541 N, 9.29389 W | RRS Challenger CH123B |
| 2289529 | Water sample data | 1995-12-11 18:27:00 | 56.51541 N, 9.29389 W | RRS Challenger CH123B |
| 855882 | CTD or STD cast | 1995-12-11 19:17:00 | 56.51583 N, 9.29567 W | RRS Challenger CH123B |
| 2282229 | Water sample data | 1995-12-11 19:47:30 | 56.51582 N, 9.29567 W | RRS Challenger CH123B |
| 2288004 | Water sample data | 1995-12-11 19:47:30 | 56.51582 N, 9.29567 W | RRS Challenger CH123B |
| 2289530 | Water sample data | 1995-12-11 19:47:30 | 56.51582 N, 9.29567 W | RRS Challenger CH123B |
| 855507 | CTD or STD cast | 1995-12-11 21:06:00 | 56.5145 N, 9.304 W | RRS Challenger CH123B |
| 2280665 | Water sample data | 1995-12-11 21:39:00 | 56.5145 N, 9.30394 W | RRS Challenger CH123B |
| 2282230 | Water sample data | 1995-12-11 21:39:00 | 56.5145 N, 9.30394 W | RRS Challenger CH123B |
| 2288016 | Water sample data | 1995-12-11 21:39:00 | 56.5145 N, 9.30394 W | RRS Challenger CH123B |
| 856431 | CTD or STD cast | 1996-02-05 21:05:00 | 56.501 N, 8.9325 W | RRS Challenger CH125A |
| 856105 | CTD or STD cast | 1996-02-05 21:50:00 | 56.5035 N, 8.98833 W | RRS Challenger CH125A |
| 856117 | CTD or STD cast | 1996-02-05 22:34:00 | 56.50583 N, 9.041 W | RRS Challenger CH125A |
| 856418 | CTD or STD cast | 1996-02-07 03:28:00 | 56.51633 N, 9.30083 W | RRS Challenger CH125A |
| 856130 | CTD or STD cast | 1996-02-07 05:11:00 | 56.51833 N, 9.1805 W | RRS Challenger CH125A |
| 856142 | CTD or STD cast | 1996-02-07 06:22:00 | 56.5125 N, 9.11367 W | RRS Challenger CH125A |
| 856399 | CTD or STD cast | 1996-02-07 07:12:00 | 56.50283 N, 9.0575 W | RRS Challenger CH125A |
| 857852 | CTD or STD cast | 1996-02-22 05:28:00 | 56.49983 N, 8.92683 W | RRS Challenger CH125B |
| 1289581 | Water sample data | 1996-02-22 05:39:00 | 56.49986 N, 8.92676 W | RRS Challenger CH125B |
| 1699242 | Water sample data | 1996-02-22 05:39:00 | 56.49986 N, 8.92676 W | RRS Challenger CH125B |
| 1866889 | Water sample data | 1996-02-22 05:39:00 | 56.49986 N, 8.92676 W | RRS Challenger CH125B |
| 856953 | CTD or STD cast | 1996-02-22 06:42:00 | 56.50333 N, 9.042 W | RRS Challenger CH125B |
| 1289593 | Water sample data | 1996-02-22 06:56:00 | 56.50341 N, 9.04199 W | RRS Challenger CH125B |
| 1699254 | Water sample data | 1996-02-22 06:56:00 | 56.50341 N, 9.04199 W | RRS Challenger CH125B |
| 1866890 | Water sample data | 1996-02-22 06:56:00 | 56.50341 N, 9.04199 W | RRS Challenger CH125B |
| 857784 | CTD or STD cast | 1996-02-22 07:23:00 | 56.50633 N, 9.061 W | RRS Challenger CH125B |
| 1289600 | Water sample data | 1996-02-22 07:34:00 | 56.50639 N, 9.06092 W | RRS Challenger CH125B |
| 1699266 | Water sample data | 1996-02-22 07:34:00 | 56.50639 N, 9.06092 W | RRS Challenger CH125B |
| 1866908 | Water sample data | 1996-02-22 07:34:00 | 56.50639 N, 9.06092 W | RRS Challenger CH125B |
| 856965 | CTD or STD cast | 1996-02-22 08:18:00 | 56.512 N, 9.1215 W | RRS Challenger CH125B |
| 1289612 | Water sample data | 1996-02-22 08:33:00 | 56.51203 N, 9.12148 W | RRS Challenger CH125B |
| 1699278 | Water sample data | 1996-02-22 08:33:00 | 56.51203 N, 9.12148 W | RRS Challenger CH125B |
| 1866921 | Water sample data | 1996-02-22 08:33:00 | 56.51203 N, 9.12148 W | RRS Challenger CH125B |
| 856977 | CTD or STD cast | 1996-02-22 11:30:00 | 56.51483 N, 9.181 W | RRS Challenger CH125B |
| 1289624 | Water sample data | 1996-02-22 11:49:00 | 56.51491 N, 9.18092 W | RRS Challenger CH125B |
| 1699291 | Water sample data | 1996-02-22 11:49:00 | 56.51491 N, 9.18092 W | RRS Challenger CH125B |
| 1866933 | Water sample data | 1996-02-22 11:49:00 | 56.51491 N, 9.18092 W | RRS Challenger CH125B |
| 857502 | CTD or STD cast | 1996-02-22 13:27:00 | 56.5165 N, 9.302 W | RRS Challenger CH125B |
| 1289636 | Water sample data | 1996-02-22 13:58:00 | 56.51646 N, 9.30205 W | RRS Challenger CH125B |
| 1699309 | Water sample data | 1996-02-22 13:58:00 | 56.51646 N, 9.30205 W | RRS Challenger CH125B |
| 1866945 | Water sample data | 1996-02-22 13:58:00 | 56.51646 N, 9.30205 W | RRS Challenger CH125B |
| 858505 | CTD or STD cast | 1996-05-04 14:18:00 | 56.5325 N, 9.69267 W | RRS Challenger CH126B |
| 2253458 | Water sample data | 1996-05-04 14:50:00 | 56.53242 N, 9.69267 W | RRS Challenger CH126B |
| 2267706 | Water sample data | 1996-05-04 14:50:00 | 56.53242 N, 9.69267 W | RRS Challenger CH126B |
| 859926 | CTD or STD cast | 1996-05-04 16:34:00 | 56.52633 N, 9.49333 W | RRS Challenger CH126B |
| 2253471 | Water sample data | 1996-05-04 16:59:30 | 56.52634 N, 9.49326 W | RRS Challenger CH126B |
| 2267718 | Water sample data | 1996-05-04 16:59:30 | 56.52634 N, 9.49326 W | RRS Challenger CH126B |
| 859938 | CTD or STD cast | 1996-05-04 19:00:00 | 56.5165 N, 9.296 W | RRS Challenger CH126B |
| 2253483 | Water sample data | 1996-05-04 19:26:00 | 56.51645 N, 9.29595 W | RRS Challenger CH126B |
| 2267731 | Water sample data | 1996-05-04 19:26:00 | 56.51645 N, 9.29595 W | RRS Challenger CH126B |
| 859951 | CTD or STD cast | 1996-05-04 20:29:00 | 56.51683 N, 9.24267 W | RRS Challenger CH126B |
| 2253495 | Water sample data | 1996-05-04 20:54:30 | 56.51691 N, 9.24267 W | RRS Challenger CH126B |
| 2267743 | Water sample data | 1996-05-04 20:54:30 | 56.51691 N, 9.24267 W | RRS Challenger CH126B |
| 858517 | CTD or STD cast | 1996-05-04 22:10:00 | 56.515 N, 9.184 W | RRS Challenger CH126B |
| 2267755 | Water sample data | 1996-05-04 22:28:30 | 56.51499 N, 9.18403 W | RRS Challenger CH126B |
| 859963 | CTD or STD cast | 1996-05-04 23:38:00 | 56.51133 N, 9.11667 W | RRS Challenger CH126B |
| 2253502 | Water sample data | 1996-05-04 23:50:00 | 56.51138 N, 9.11667 W | RRS Challenger CH126B |
| 2267767 | Water sample data | 1996-05-04 23:50:00 | 56.51138 N, 9.11667 W | RRS Challenger CH126B |
| 859361 | CTD or STD cast | 1996-05-05 00:45:00 | 56.50767 N, 9.06683 W | RRS Challenger CH126B |
| 2267779 | Water sample data | 1996-05-05 00:56:00 | 56.50759 N, 9.06677 W | RRS Challenger CH126B |
| 859373 | CTD or STD cast | 1996-05-05 01:33:00 | 56.50383 N, 9.04017 W | RRS Challenger CH126B |
| 2253514 | Water sample data | 1996-05-05 01:40:00 | 56.50382 N, 9.0401 W | RRS Challenger CH126B |
| 2267780 | Water sample data | 1996-05-05 01:40:00 | 56.50382 N, 9.0401 W | RRS Challenger CH126B |
| 859385 | CTD or STD cast | 1996-05-05 02:19:00 | 56.50483 N, 8.991 W | RRS Challenger CH126B |
| 2267792 | Water sample data | 1996-05-05 02:25:00 | 56.50484 N, 8.99099 W | RRS Challenger CH126B |
| 859397 | CTD or STD cast | 1996-05-05 03:09:00 | 56.50133 N, 8.93333 W | RRS Challenger CH126B |
| 2267811 | Water sample data | 1996-05-05 03:13:30 | 56.50129 N, 8.93327 W | RRS Challenger CH126B |
| 859570 | CTD or STD cast | 1996-05-07 03:34:00 | 56.518 N, 9.29967 W | RRS Challenger CH126B |
| 2253711 | Water sample data | 1996-05-07 03:56:30 | 56.51804 N, 9.29974 W | RRS Challenger CH126B |
| 2268076 | Water sample data | 1996-05-07 03:56:30 | 56.51804 N, 9.29974 W | RRS Challenger CH126B |
| 859582 | CTD or STD cast | 1996-05-07 05:02:00 | 56.52 N, 9.29967 W | RRS Challenger CH126B |
| 2268088 | Water sample data | 1996-05-07 05:53:00 | 56.51996 N, 9.29959 W | RRS Challenger CH126B |
| 858799 | CTD or STD cast | 1996-05-07 10:48:00 | 56.51283 N, 9.2975 W | RRS Challenger CH126B |
| 2253723 | Water sample data | 1996-05-07 10:55:30 | 56.51282 N, 9.29752 W | RRS Challenger CH126B |
| 2268107 | Water sample data | 1996-05-07 10:55:30 | 56.51282 N, 9.29752 W | RRS Challenger CH126B |
| 860595 | CTD or STD cast | 1996-07-11 22:37:00 | 56.50183 N, 8.933 W | RRS Challenger CH128A |
| 1292460 | Water sample data | 1996-07-11 22:42:00 | 56.50187 N, 8.93308 W | RRS Challenger CH128A |
| 860177 | CTD or STD cast | 1996-07-11 23:32:00 | 56.50617 N, 9.04617 W | RRS Challenger CH128A |
| 1292552 | Water sample data | 1996-07-11 23:50:00 | 56.50611 N, 9.0461 W | RRS Challenger CH128A |
| 861027 | CTD or STD cast | 1996-07-12 00:25:00 | 56.50767 N, 9.0615 W | RRS Challenger CH128A |
| 1292668 | Water sample data | 1996-07-12 00:45:00 | 56.50771 N, 9.06142 W | RRS Challenger CH128A |
| 860602 | CTD or STD cast | 1996-07-12 01:44:00 | 56.512 N, 9.1135 W | RRS Challenger CH128A |
| 1292712 | Water sample data | 1996-07-12 02:00:00 | 56.512 N, 9.11353 W | RRS Challenger CH128A |
| 860189 | CTD or STD cast | 1996-07-12 03:24:00 | 56.5185 N, 9.29167 W | RRS Challenger CH128A |
| 1292030 | Water sample data | 1996-07-12 03:56:00 | 56.51842 N, 9.29173 W | RRS Challenger CH128A |
| 861297 | CTD or STD cast | 1996-07-28 18:33:00 | 56.51783 N, 9.3045 W | RRS Challenger CH128B |
| 2266229 | Water sample data | 1996-07-28 19:03:00 | 56.51789 N, 9.30445 W | RRS Challenger CH128B |
| 2271103 | Water sample data | 1996-07-28 19:03:00 | 56.51789 N, 9.30445 W | RRS Challenger CH128B |
| 861156 | CTD or STD cast | 1996-07-28 22:46:00 | 56.51817 N, 9.30833 W | RRS Challenger CH128B |
| 2266230 | Water sample data | 1996-07-28 23:26:30 | 56.51817 N, 9.30826 W | RRS Challenger CH128B |
| 2271115 | Water sample data | 1996-07-28 23:26:30 | 56.51817 N, 9.30826 W | RRS Challenger CH128B |
| 861304 | CTD or STD cast | 1996-07-29 00:29:00 | 56.52517 N, 9.3195 W | RRS Challenger CH128B |
| 2263127 | Water sample data | 1996-07-29 01:12:00 | 56.52524 N, 9.31953 W | RRS Challenger CH128B |
| 2266242 | Water sample data | 1996-07-29 01:12:00 | 56.52524 N, 9.31953 W | RRS Challenger CH128B |
| 2267442 | Water sample data | 1996-07-29 01:12:00 | 56.52524 N, 9.31953 W | RRS Challenger CH128B |
| 2267491 | Water sample data | 1996-07-29 01:12:00 | 56.52524 N, 9.31953 W | RRS Challenger CH128B |
| 2271127 | Water sample data | 1996-07-29 01:12:00 | 56.52524 N, 9.31953 W | RRS Challenger CH128B |


