Metadata Report for BODC Series Reference Number 1893027
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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Parameters |
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Definition of BOTTFLAG | |||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
BOTTFLAG | Definition |
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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.
AMT18 (JR20081003) pigment composition by HPLC analysis from CTD bottle samples
Data Acquisition and Analysis
Samples (1-3L) were vacuum filtered onto GF/F filters, flash frozen in liquid nitrogen and stored at -80°C on board ship. At PML, samples were stored in liquid nitrogen until analysis. Pigments were extracted from the sample filters into 2 mL 100% acetone using an ultrasonic probe (35 s; 50W). An internal standard was used (Trans-B-Apo-8'-carotenal) to correct for water content of filters. Extracts were centrifuged to remove filter and cell debris (5 min at 4000 rpm) and analysed by reversed phase HPLC, using a method based on Barlow et al. 1997. Analyses were performed using a Thermo Accela Series HPLC system with chilled autosampler (4°C) and photodiode array detector. The HPLC was calibrated using a suite of standards purchased from DHI (Denmark). Pigments were identified based on retention time and spectral match using photo-diode array.
Instrumentation Description
Thermo Accela Series HPLC system
BODC Data Processing Procedures
These data supersede data previously supplied to BODC without quality assurance (see the Data Quality Report section for more details). Data were submitted to BODC in Microsoft Excel spreadsheet format and saved to the archive with reference PML130050. The file was provided to BODC with date, latitude, longitude, station number and depth as metadata. Sample metadata were checked against information held in the database - there were no discrepancies.
The following parameters were provided in the file but only the parameters that were not derived from the summation of other parameters in the dataset were loaded into the database. The absent data value was recorded as the effective limit of detection (LOD). The effective limits of detection, calculated for a filter volume of 3L are given in the table below.
Originator's Parameter | Originator's description | Sum of | Effective LOD (µg/L) | Database load |
---|---|---|---|---|
[TChl a] | Total chlorophyll a | [Chlide a] + [DVChl a] + [Chl a] | - | No |
[TChl b] | Total chlorophyll b | [DVChl b] + [Chl b] | - | No |
[TChl c] | Total chlorophyll c | [Chl c12] + [Chl c3] | - | No |
[Caro] | Carotenes (beta-beta-Car + beta-epsilon-Car) | - | 0.001 | Yes |
[But fuco] | 19'-Butanoyloxyfucoxanthin | - | 0.001 | Yes |
[Hex fuco] | 19'-Hexanoyloxyfucoxanthin | - | 0.001 | Yes |
[Allo] | Alloxanthin | - | 0.001 | Yes |
[Diad] | Diadinoxanthin | - | 0.001 | Yes |
[Diato] | Diatoxanthin | - | 0.001 | Yes |
[Fuco] | Fucoxanthin | - | 0.001 | Yes |
[Perid] | Peridinin | - | 0.002 | Yes |
[Zea] | Zeaxanthin | - | 0.001 | Yes |
[Chl a] | Chlorophyll a | - | 0.003 | Yes |
[DVChl a] | Divinyl chlorophyll a | - | 0.002 | Yes |
[Chl b] + [DVChl b] | Chlorophyll b + Divinyl chlorophyll b | - | 0.003 | Yes |
[Chl c12] | chlorophyll c1 + chlorophyll c2 | - | 0.001 | Yes |
[Chl c3] | chlorophyll c3 | - | 0.001 | Yes |
[Lut] | lutein | - | 0.001 | Yes |
[Viola] + [Neo] | Violaxanthin + Neoxanthin | - | 0.001 | Yes |
[Gyr diester] | Gyroxanthin diester | - | 0.001 | Yes |
[TChl] | Total Chlorophyll | [TChl a] + [TChl b] + [TChl c] | - | No |
[PPC] | Photoprotective carotenoids | [Allo]+[Diad]+[Diato]+[Zea]+[Caro] | - | No |
[PSC] | Photosynthetic carotenoids | [But]+[Fuco]+[Hex fuco]+Perid] | - | No |
[PSP] | Photosynthetic pigments | [PSC]+[TChl] | - | No |
[TAcc] | Total accessory pigments | [PPC]+[PSC]+[TChl b]+[TChl c] | - | No |
[TPig] | Total pigments | [TAcc]+[TChl a] | - | No |
There were duplicate data provided for 3 samples (cast 78, depth 2 m; cast 82, depth 55 m; cast 100, depth 20 m) and the mean and standard deviation for these values were entered into the database for each sample.
Parameter codes defined in BODC parameter dictionary were assigned to the variables as shown in the table below. The data were provided in µg l-1 units that were converted to ng l-1 for all parameters but chlorophyll-a.
Data loaded into BODC's database without any further changes.
Originator's Parameter | Units | Description | BODC Parameter Code + SD Code | Units | Comments |
---|---|---|---|---|---|
[Chl a] | µg l-1 | Concentration of chlorophyll-a {chl-a} per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | CPHLHPP1 SDCLHPP1 | mg m-3 | n/a |
[Chl b + DVChl b] | µg l-1 | Concentration of chlorophyll-b+divinyl chlorophyll-b per unit volume of the water body [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | CBDVHPP1 CBDVSDP1 | ng l-1 | Unit conversion x1000 applied |
[DVChl a] | µg l-1 | Concentration of divinyl chlorophyll-a per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | DVCAHPP1 DVCASDP1 | ng l-1 | Unit conversion x1000 applied |
[Chl c12] | µg l-1 | Concentration of chlorophyll-c1c2 {chl-c1c2} per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | C1C2HPP1 C1C2SDP1 | ng l-1 | Unit conversion x1000 applied |
[Chl c3] | µg l-1 | Concentration of chlorophyll-c3 {chl-c3} per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | CLC3HPP1 CLC3SDP1 | ng l-1 | Unit conversion x1000 applied |
[Caro] | µg l-1 | Concentration of beta,epsilon-carotene+beta,beta-carotene {alpha-beta-carotene alpha+beta-carotene} per unit volume of the water body [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | ABCRHPP1 ABCRSDP1 | ng l-1 | Unit conversion x1000 applied |
[Perid] | µg l-1 | Concentration of peridinin per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | PERIHPP1 PERISDP1 | ng l-1 | Unit conversion x1000 applied |
[But fuco] | µg l-1 | Concentration of 19'-butanoyloxyfucoxanthin per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | BUTAHPP1 BUTASDP1 | ng l-1 | Unit conversion x1000 applied |
[Fuco] | µg l-1 | Concentration of fucoxanthin per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | FUCXHPP1 FUCXSDP1 | ng l-1 | Unit conversion x1000 applied |
[Hex fuco] | µg l-1 | Concentration of 19'-hexanoyloxyfucoxanthin per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | HEXOHPP1 HEXOSDP1 | ng l-1 | Unit conversion x1000 applied |
[Viola + Neo] | µg l-1 | Concentration of violaxanthin+neoxanthin per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | VINEHPP1 VINESDP1 | ng l-1 | Unit conversion x1000 applied |
[Diad] | µg l-1 | Concentration of diadinoxanthin per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | DIADHPP1 DIADSDP1 | ng l-1 | Unit conversion x1000 applied |
[Allo] | µg l-1 | Concentration of alloxanthin per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | ALLOHPP1 ALLOSDP1 | ng l-1 | Unit conversion x1000 applied |
[Diato] | µg l-1 | Concentration of diatoxanthin per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | DIATHPP1 DIATSDP1 | ng l-1 | Unit conversion x1000 applied |
[Zea] | µg l-1 | Concentration of zeaxanthin per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | ZEOXHPP1 ZEOXSDP1 | ng l-1 | Unit conversion x1000 applied |
[Lut] | µg l-1 | Concentration of lutein per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | LUTNHPP1 LUTNSDP1 | ng l-1 | Unit conversion x1000 applied |
[Gyr diester] | µg l-1 | Concentration of gyroxanthin diester per unit volume of the water column [particulate >GF/F phase] by filtration, acetone extraction and high performance liquid chromatography (HPLC) | GDHPLC01 GDIESDP1 | ng l-1 | Unit conversion x1000 applied |
Data Quality Report
Dataset originally obtained using inadequate quality assurance (QA) procedures (for an example of adequate QA procedures during pigment analysis, see Van Heukelem and Hooker (2011)). A series of duplicate samples spanning the chl-a concentration range observed in the dataset were analysed using a quality assured, validated HPLC method by an experienced pigment scientist. A comparison between the original and duplicate sample pigment concentrations was performed, and systematic errors for individual pigments identified. The AMT18 pigment dataset was corrected for the systematic errors identified. The same process was carried out for the AMT19 CTD bottle pigment dataset analysed at PML and theAMT19 surface pigment samples which were collected and later analysed independently by a validated pigment method in a NASA laboratory (Hornpoint). This enabled validation of the corrected PML dataset. The root mean square deviation of the two sample sets (PML and Hornpoint) was determined and normalized to the concentration range for each pigment. The average normalized root mean square deviation for the primary pigments was 7.9%. Notably, the highest NRMSD value for the primary pigments was observed for diatoxanthin, which was present at low concentration in all but one of the compared samples.
The precision for replicate filters (gives whole method precision, from filtering to analysis) was provided in a separate file and is available on request to BODC. The average coefficients of variation (CV%) were 7.02 and 14.74 for [TChl a] and [TPig], respectively.
Samples values provided with the effective LOD were flagged '<' for each parameter in the database.
Problem Report
This section is not relevant to this data set.
References Cited
Barlow R.G., Cummings D.G. and Gibb S.W., 1997. Improved resolution of mono- and divinyl chlorophylls a and b and zeaxanthin and lutein in phytoplankton extracts using reverse phase C8 HPLC. Marine Ecology Progress Series, 161 , 303-307.
Van Heukelem L. and Hooker S.B. 2011. The importance of a quality assurance plan for method validation and minimizing uncertainties in the HPLC analysis of phytoplankton pigments. In: Phytoplankton Pigments: Characterization, Chemotaxonomy and Applications in Oceanography, eds. Suzanne Roy, Carole A. Llewellyn, Einar Skarstad Egeland and Geir Johnsen. Cambridge University Press.
Project Information
Oceans 2025 Theme 10, Sustained Observation Activity 1: The Atlantic Meridional Transect (AMT)
The Atlantic Meridional Transect has been operational since 1995 and through the Oceans 2025 programme secures funding for a further five cruises during the period 2007-2012. The AMT programme began in 1995 utilising the passage of the RRS James Clark Ross between the UK and the Falkland Islands southwards in September and northwards in April each year. Prior to Oceans 2025 the AMT programme has completed 18 cruises following this transect in the Atlantic Ocean. This sustained observing system aims to provide basin-scale understanding of the distribution of planktonic communities, their nutrient turnover and biogenic export in the context of hydrographic and biogeochemical provinces of the North and South Atlantic Oceans.
The Atlantic Meridional Transect Programme is an open ocean in situ observing system that will:
- give early warning of any fundamental change in Atlantic ecosystem functionng
- improve forecasts of the future ocean state and associated socio-economic impacts
- provide a "contextual" logistical and scientific infrastructure for independently-funded national and international open ocean biogeochemical and ecological research.
The specific objectives are:
- To collect hydrographic, chemical, ecological and optical data on transects between the UK and the Falkland Islands
- To quantify the nature and causes of ecological and biogeochemical variability in planktonic ecosystems
- To assess the effects of variability in planktonic ecosystems on biogenic export and on air-sea exchange of radiatively active gases
The measurements taken and experiments carried out on the AMT cruises will be closely linked to Themes 2 and 5. The planned cruise track also allows for the AMT data to be used in providing spatial context to the Sustained Observation Activities at the Porcupine Abyssal Plain Ocean Observatory (SO2) and the Western Channel Observatory (SO10).
More detailed information on this Work Package is available at pages 6 - 9 of the official Oceans 2025 Theme 10 document: Oceans 2025 Theme 10
Weblink: http://www.oceans2025.org/
Data Activity or Cruise Information
Data Activity
Start Date (yyyy-mm-dd) | 2008-10-12 |
End Date (yyyy-mm-dd) | 2008-10-12 |
Organization Undertaking Activity | Plymouth Marine Laboratory |
Country of Organization | United Kingdom |
Originator's Data Activity Identifier | JR20081003_CTD_CTD020 |
Platform Category | lowered unmanned submersible |
BODC Sample Metadata Report for JR20081003_CTD_CTD020
Sample reference number | 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 |
---|---|---|---|---|---|---|---|---|---|
189243 | 1 | 1 | 306.80 | 307.80 | 304.90 | 20-litre Niskin | No problem reported | ||
189244 | 2 | 2 | 206.10 | 207.10 | 205.00 | 20-litre Niskin | No problem reported | ||
189245 | 3 | 3 | 142.30 | 143.30 | 141.80 | 20-litre Niskin | No problem reported | ||
189246 | 4 | 4 | 142.30 | 143.30 | 141.80 | 20-litre Niskin | No problem reported | ||
189247 | 5 | 5 | 142.30 | 143.30 | 141.80 | 20-litre Niskin | No problem reported | ||
189248 | 6 | 6 | 104.80 | 105.80 | 104.50 | 20-litre Niskin | No problem reported | ||
189249 | 7 | 7 | 99.70 | 100.70 | 99.50 | 20-litre Niskin | No problem reported | ||
189250 | 8 | 8 | 95.80 | 96.80 | 95.60 | 20-litre Niskin | No problem reported | ||
189251 | 9 | 9 | 95.80 | 96.80 | 95.60 | 20-litre Niskin | No problem reported | ||
189252 | 10 | 10 | 84.70 | 85.70 | 84.60 | 20-litre Niskin | No problem reported | ||
189253 | 11 | 11 | 73.70 | 74.70 | 73.70 | 20-litre Niskin | No problem reported | ||
189254 | 12 | 12 | 57.50 | 58.50 | 57.60 | 20-litre Niskin | No problem reported | ||
189255 | 13 | 13 | 43.40 | 44.40 | 43.60 | 20-litre Niskin | No problem reported | ||
189256 | 14 | 14 | 43.40 | 44.40 | 43.60 | 20-litre Niskin | No problem reported | ||
189257 | 15 | 15 | 43.30 | 44.30 | 43.50 | 20-litre Niskin | No problem reported | ||
189258 | 16 | 16 | 26.40 | 27.40 | 26.70 | 20-litre Niskin | No problem reported | ||
189259 | 17 | 17 | 26.50 | 27.50 | 26.80 | 20-litre Niskin | No problem reported | ||
189260 | 18 | 18 | 26.60 | 27.60 | 26.90 | 20-litre Niskin | No problem reported | ||
189261 | 19 | 19 | 15.40 | 16.40 | 15.80 | 20-litre Niskin | No problem reported | ||
189262 | 20 | 20 | 15.40 | 16.40 | 15.80 | 20-litre Niskin | No problem reported | ||
189263 | 21 | 21 | 6.30 | 7.30 | 6.80 | 20-litre Niskin | No problem reported | ||
189264 | 22 | 22 | 6.30 | 7.30 | 6.80 | 20-litre Niskin | No problem reported | ||
189265 | 23 | 23 | 6.30 | 7.30 | 6.80 | 20-litre Niskin | No problem reported | ||
189266 | 24 | 24 | 6.30 | 7.30 | 6.80 | 20-litre Niskin | 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 | JR20081003 (AMT18, JR218) |
Departure Date | 2008-10-03 |
Arrival Date | 2008-11-10 |
Principal Scientist(s) | E Malcolm S Woodward (Plymouth Marine Laboratory) |
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: JR20081003_CTD_CTD020
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 |
---|---|---|---|---|
1091743 | Water sample data | 2008-10-12 14:05:00 | 32.49001 N, 31.71019 W | RRS James Clark Ross JR20081003 (AMT18, JR218) |