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Metadata Report for BODC Series Reference Number 2262148


Metadata Summary

Data Description

Data Category Water sample data
Instrument Type
NameCategories
Niskin bottle  discrete water samplers
Instrument Mounting lowered unmanned submersible
Originating Country United Kingdom
Originator Unknown
Originating Organization Research Vessel Services (now National Marine Facilities Sea Systems)
Processing Status banked
Online delivery of data Download available - Ocean Data View (ODV) format
Project(s) LOIS River-Atmosphere-Coast Study (RACS)
 

Data Identifiers

Originator's Identifier CH115A_CTD_TPSL_1:CP26
BODC Series Reference 2262148
 

Time Co-ordinates(UT)

Start Time (yyyy-mm-dd hh:mm) 1994-10-07 15:34
End Time (yyyy-mm-dd hh:mm) -
Nominal Cycle Interval -
 

Spatial Co-ordinates

Latitude 53.97397 N ( 53° 58.4' N )
Longitude 0.42017 E ( 0° 25.2' E )
Positional Uncertainty 0.05 to 0.1 n.miles
Minimum Sensor or Sampling Depth 49.9 m
Maximum Sensor or Sampling Depth 49.9 m
Minimum Sensor or Sampling Height 4.0 m
Maximum Sensor or Sampling Height 4.0 m
Sea Floor Depth 53.9 m
Sea Floor Depth Source PEVENT
Sensor or Sampling Distribution Fixed common depth - All sensors are grouped effectively at the same depth which is effectively fixed for the duration of the series
Sensor or Sampling Depth Datum Instantaneous - Depth measured below water line or instantaneous water body surface
Sea Floor Depth Datum Unspecified -
 

Parameters

BODC CODERankUnitsTitle
ADEPZZ011MetresDepth (spatial coordinate) relative to water surface in the water body
BOTTFLAG1Not applicableSampling process quality flag (BODC C22)
PSALBSTX1DimensionlessPractical salinity of the water body by bench salinometer and computation using UNESCO 1983 algorithm
SAMPRFNM1DimensionlessSample reference number
TEMPRTNX1Degrees CelsiusTemperature of the water body by reversing thermometer

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

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.

Hydrography for cruises by RRS Challenger.

Document History

Converted from CDROM documentation.

Content of data series

CLXXIETX Dissolved chloride
Ion-selective electrode (unfiltered water)
Micromoles/litre
PSALBSTX Bench salinometer practical salinity
Salinometer
Practical Salinity Units
PSALPR01 Practical salinity (unspecified probe type)
Unspecified conductivity probe
Practical Salinity Units
PSALSG01 Practical salinity (thermosalinograph)
Thermosalinograph conductivity measurement
Practical Salinity Units
PSALST01 Practical salinity (CTD)
CTD conductivity measurement
Practical Salinity Units
SIGTPR01 Sigma-theta (CTD data)
Computed from CTD data using UNESCO functions POTEMP and SVAN
Practical Salinity Units
TEMPPR01 Sea temperature (unspecified)
Unspecified temperature probe
Degrees centigrade
TEMPRTNX Reversing thermometer sea temperature
Reversing thermometer
Degrees centigrade
TEMPSG01 Sea temperature (thermosalinograph)
Thermosalinograph measurement
Degrees centigrade
TEMPST01 Sea temperature (CTD/STD)
CTD or STD measurement
Degrees centigrade
TOKGPR01 µM to µmoles/litre conversion (CTD)
Computed from sigma-theta derived from CTD data
Dimensionless

Data Originator

Research Vessel Services

Sampling strategy and methodology

RRS Challenger cruises CH99, CH108A, CH108B, CH108C, CH115A, CH115B, CH115C, CH117A0, CH117A, CH117B, CH118A, CH118B, CH118C, CH119A, CH119B and CH119C.

Temperature measurements are made using SIS digital reversing thermometers. Two or three instruments were mounted together in a reversing cage to provide duplicate data and an indication of occasions when the cage has failed to reverse cleanly. Each thermometer was periodically calibrated at the RVS laboratory facility and a correction, in the form of a third order polynomial, determined. These corrections were routinely applied. Data in the database are the averages of the readings from all thermometers in the cage after fliers (such as caused by the reading being written down incorrectly) have been eliminated.

Salinity samples were taken in medicine bottles. After rinsing, the bottle was filled up to the shoulder, carefully dried off and then sealed with a plastic stopper under the cap. Salinities were determined by taking triplicate readings on a Guildline Autosal bench salinometer as soon as the samples had come to laboratory temperature (generally 24-36 hours after sampling). The instrument was standardised against OSI standard seawater.

References

Balls, P.B. and Laslett, R., 1991. A simple estuarine water sampler suitable for trace metals and other constituents. Estuarine Coastal and Shelf Science 33, 623-629.


Project Information

LOIS River-Atmosphere-Coast Study (LOIS - RACS)

Introduction

The Land-Ocean Interaction Study (LOIS) was a NERC research programme designed to study processes in the coastal zone. The Rivers, Atmosphere and Coasts Study (RACS) was a major component of LOIS that looked at land-sea interactions in the coastal zone and the major exchanges (physical, chemical and biological) between rivers and estuaries and the atmosphere. The study focused on the east coast of the UK from the Wash to the Tweed.

RACS included several sub-components

  • BIOTA - A study of salt marshes of the Humber and Wash
  • RACS (A) - An atmospheric chemistry study looking at air mass changes from the Wash into East Anglia
  • RACS (C) - A study of the estuaries, coasts and coastal waters between Great Yarmouth and Berwick upon Tweed.
    1. The coastal oceangraphic survey
    2. The Humber estuarine study
    3. The Tweed estuarine study
    4. The Holderness experiment
  • RACS (R) - A study of rivers that drain into the North Sea

RACS (A) was coordinated by the University of East Anglia and RACS (C) by the Plymouth Marine Laboratory.

RACS (A)

The bulk of the RACS (A) data set was collected during two field campaigns in the winter (October/November) of 1994 and the summer (May/June) of 1995. During these campaigns data were collected continuously from the University of East Anglia Atmospheric Observatory at Weybourne on the north Norfolk coast. An instrumented vessel was stationed offshore to provide a second sampling site to allow changes in a given air mass to be monitored. The Imperial College Jetstream research aircraft made one flight during each campaign to provide a link between the two surface stations. The Jetstream made four additional flights in 1996 and 1997.

RACS (C)

The coastal oceanographic survey

The coastal oceanographic data set was collected during a series of 17 RRS Challenger cruise legs. Most cruises covered two survey grids. One from Great Yarmouth to the Humber designed around the distribution of the sandbanks and a second simple zig-zag grid from the Humber to Berwick on Tweed. A large number of anchor stations, usually over one or two tidal cycles, were worked in the area of the Humber mouth or the Holderness coast.

The Humber estuarine study

The Humber estuarine data set was collected during a series of 33 campaigns on the Environment Agency vessels Sea Vigil and Water Guardian in the Humber, Trent and Ouse river systems at approximately monthly intervals between June 1993 and December 1996. Each campaign consisted of two or three one-day cruises. The tracks covered the estuary from the tidal limits of both Trent and Ouse to Spurn Point. Instrumental and sample data are available from a series of fixed stations that were sampled during every campaign.

The Tweed estuarine study

The Tweed estuarine data set was collected during a series of 13 campaigns using RV Tamaris in association with a rigid inflatable vessel at approximately monthly intervals between July 1996 and July 1997. Each campaign covered the tidal reaches of the River Tweed.

The Holderness experiment

The Holderness Experiment was designed to monitor the process of sediment transport along the Holderness coastline. It consisted of three moored instrument deployments during the winters of 1993-1994, 1994-1995 and 1995-1996. Mooring platforms were deployed at eight stations along two lines off the Holderness coast. A northerly and a southerly line of four stations each were used (N1 - N4 and S1 to S4) with the lowest numbers being inshore. Both lines were approximately perpendicular to the coast, although the S4 station lay to the south of the S line, off Spurn Head.


Data Activity or Cruise Information

Data Activity

Start Date (yyyy-mm-dd) 1994-10-07
End Date (yyyy-mm-dd) 1994-10-07
Organization Undertaking ActivityProudman Oceanographic Laboratory (now National Oceanography Centre, Liverpool)
Country of OrganizationUnited Kingdom
Originator's Data Activity IdentifierCH115A_CTD_CP26
Platform Categorylowered unmanned submersible

BODC Sample Metadata Report for CH115A_CTD_CP26

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
364721   10.00       50.90   51.10   49.90 Niskin bottle No problem reported    
364843   10.00        1.30    2.80    1.40 General Oceanics GO-FLO water sampler No problem reported    
364844   10.00        4.60    6.10    4.60 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 CH115A
Departure Date 1994-10-04
Arrival Date 1994-10-17
Principal Scientist(s)David Prandle (Proudman Oceanographic Laboratory)
Ship RRS Challenger

Complete Cruise Metadata Report is available here


Fixed Station Information

Fixed Station Information

Station NameHolderness Site N4
CategoryCoastal location
Latitude53° 58.80' N
Longitude0° 25.20' E
Water depth below MSL54.0 m

LOIS RACS (Holderness Experiment) Mooring Site N4

The site was occupied for phase 1 of the Holderness Experiment between October 1994 and late January 1995 by a POL Monitoring Platform (PMP) seabed mooring. The PMP mooring included an ADCP (zero data return), a transmissometer and a pressure gauge programmed to sample at high frequency in burst mode, which allowed the derivation of 1-D wave spectra. Basic wave statistics (Hs and Tz) have been computed.

The data returned were as follows:

Instrument Start End
Pressure 07 oct 1994 11 nov 1994
Pressure 12 nov 1994 27 jan 1995
Transmissometer 07 oct 1994 11 nov 1994
Transmissometer 12 nov 1994 26 dec 1994

This station was not occupied for the second (1995-1996) phase of the project. The mean sea level water depth at the station was 54m and magnetic variation at the time of the deployments was 4 degrees west.

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: CH115A_CTD_CP26

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
2255810Water sample data1994-10-07 15:34:3053.97397 N, 0.42017 ERRS Challenger CH115A
1712400Water sample data1994-10-07 15:35:0053.97397 N, 0.42017 ERRS Challenger CH115A

Appendix 2: Holderness Site N4

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 IdentifierData CategoryStart date/timeStart positionCruise
833063CTD or STD cast1994-10-07 14:04:0053.9755 N, 0.4125 ERRS Challenger CH115A
2255809Water sample data1994-10-07 14:06:3053.97549 N, 0.41243 ERRS Challenger CH115A
2262136Water sample data1994-10-07 14:06:3053.97549 N, 0.41243 ERRS Challenger CH115A
833075CTD or STD cast1994-10-07 14:41:0053.96283 N, 0.40683 ERRS Challenger CH115A
834515CTD or STD cast1994-10-07 15:31:0053.974 N, 0.42017 ERRS Challenger CH115A
2255810Water sample data1994-10-07 15:34:3053.97397 N, 0.42017 ERRS Challenger CH115A
833087CTD or STD cast1994-10-07 16:30:0053.97333 N, 0.41583 ERRS Challenger CH115A
833099CTD or STD cast1994-10-07 16:59:0053.972 N, 0.41783 ERRS Challenger CH115A
2250670Water sample data1994-10-07 17:02:3053.97201 N, 0.4178 ERRS Challenger CH115A
2255822Water sample data1994-10-07 17:02:3053.97201 N, 0.4178 ERRS Challenger CH115A
2262161Water sample data1994-10-07 17:02:3053.97201 N, 0.4178 ERRS Challenger CH115A
834527CTD or STD cast1994-10-07 17:31:0053.97367 N, 0.4175 ERRS Challenger CH115A
833106CTD or STD cast1994-10-07 18:01:0053.9735 N, 0.41933 ERRS Challenger CH115A
2250694Water sample data1994-10-07 18:04:3053.97355 N, 0.41937 ERRS Challenger CH115A
2255846Water sample data1994-10-07 18:04:3053.97355 N, 0.41937 ERRS Challenger CH115A
2262185Water sample data1994-10-07 18:04:3053.97355 N, 0.41937 ERRS Challenger CH115A
833118CTD or STD cast1994-10-07 18:31:0053.97333 N, 0.41867 ERRS Challenger CH115A
2255858Water sample data1994-10-07 18:34:0053.97331 N, 0.41872 ERRS Challenger CH115A
2262197Water sample data1994-10-07 18:34:0053.97331 N, 0.41872 ERRS Challenger CH115A
577801Transmittance/attenuance, turbidity, or SPM conc.1994-10-07 19:46:0053.9752 N, 0.4212 ERRS Challenger CH115A
833131CTD or STD cast1994-10-07 20:32:0053.98417 N, 0.42417 ERRS Challenger CH115A
2250701Water sample data1994-10-07 20:37:0053.9842 N, 0.4242 ERRS Challenger CH115A
2255871Water sample data1994-10-07 20:37:0053.9842 N, 0.4242 ERRS Challenger CH115A
2262204Water sample data1994-10-07 20:37:0053.9842 N, 0.4242 ERRS Challenger CH115A
426314Waves (1D spectra)1994-10-07 20:50:3753.9752 N, 0.4212 ERRS Challenger CH115A
834539CTD or STD cast1994-10-07 21:02:0053.984 N, 0.41983 ERRS Challenger CH115A
833143CTD or STD cast1994-10-07 21:31:0053.98717 N, 0.41917 ERRS Challenger CH115A
2250713Water sample data1994-10-07 21:35:0053.98718 N, 0.41909 ERRS Challenger CH115A
2255883Water sample data1994-10-07 21:35:0053.98718 N, 0.41909 ERRS Challenger CH115A
2262216Water sample data1994-10-07 21:35:0053.98718 N, 0.41909 ERRS Challenger CH115A
833155CTD or STD cast1994-10-07 22:00:0053.98633 N, 0.41667 ERRS Challenger CH115A
834540CTD or STD cast1994-10-07 22:30:0053.98667 N, 0.41833 ERRS Challenger CH115A
2250725Water sample data1994-10-07 22:35:0053.98669 N, 0.41841 ERRS Challenger CH115A
2255895Water sample data1994-10-07 22:35:0053.98669 N, 0.41841 ERRS Challenger CH115A
2262228Water sample data1994-10-07 22:35:0053.98669 N, 0.41841 ERRS Challenger CH115A
834853CTD or STD cast1994-10-07 23:03:0053.98683 N, 0.41833 ERRS Challenger CH115A
833929CTD or STD cast1994-10-07 23:33:0053.98883 N, 0.41517 ERRS Challenger CH115A
2250737Water sample data1994-10-07 23:35:0053.98888 N, 0.41512 ERRS Challenger CH115A
2255902Water sample data1994-10-07 23:35:0053.98888 N, 0.41512 ERRS Challenger CH115A
2262241Water sample data1994-10-07 23:35:0053.98888 N, 0.41512 ERRS Challenger CH115A
833930CTD or STD cast1994-10-08 00:02:0053.98867 N, 0.41233 ERRS Challenger CH115A
833942CTD or STD cast1994-10-08 00:32:0053.987 N, 0.413 ERRS Challenger CH115A
2250749Water sample data1994-10-08 00:35:0053.98707 N, 0.41293 ERRS Challenger CH115A
2255914Water sample data1994-10-08 00:35:0053.98707 N, 0.41293 ERRS Challenger CH115A
2262253Water sample data1994-10-08 00:35:0053.98707 N, 0.41293 ERRS Challenger CH115A
834865CTD or STD cast1994-10-08 01:03:0053.98267 N, 0.413 ERRS Challenger CH115A
833954CTD or STD cast1994-10-08 01:31:0053.98283 N, 0.4095 ERRS Challenger CH115A
2250750Water sample data1994-10-08 01:35:0053.98285 N, 0.40942 ERRS Challenger CH115A
2255926Water sample data1994-10-08 01:35:0053.98285 N, 0.40942 ERRS Challenger CH115A
2262265Water sample data1994-10-08 01:35:0053.98285 N, 0.40942 ERRS Challenger CH115A
833966CTD or STD cast1994-10-08 02:01:0053.98733 N, 0.41433 ERRS Challenger CH115A
834877CTD or STD cast1994-10-08 02:32:0053.9825 N, 0.41567 ERRS Challenger CH115A
2250762Water sample data1994-10-08 02:35:0053.98253 N, 0.41573 ERRS Challenger CH115A
2255938Water sample data1994-10-08 02:35:0053.98253 N, 0.41573 ERRS Challenger CH115A
2262277Water sample data1994-10-08 02:35:0053.98253 N, 0.41573 ERRS Challenger CH115A
833978CTD or STD cast1994-10-08 03:03:0053.98433 N, 0.41717 ERRS Challenger CH115A
833991CTD or STD cast1994-10-08 03:32:0053.96517 N, 0.41783 ERRS Challenger CH115A
2250774Water sample data1994-10-08 03:34:0053.9652 N, 0.41791 ERRS Challenger CH115A
2255951Water sample data1994-10-08 03:34:0053.9652 N, 0.41791 ERRS Challenger CH115A
2262289Water sample data1994-10-08 03:34:0053.9652 N, 0.41791 ERRS Challenger CH115A
834005CTD or STD cast1994-10-08 04:01:0053.95733 N, 0.42183 ERRS Challenger CH115A
2250786Water sample data1994-10-08 04:05:0053.95726 N, 0.42176 ERRS Challenger CH115A
2255963Water sample data1994-10-08 04:05:0053.95726 N, 0.42176 ERRS Challenger CH115A
2262290Water sample data1994-10-08 04:05:0053.95726 N, 0.42176 ERRS Challenger CH115A
834889CTD or STD cast1994-10-08 05:01:0053.96533 N, 0.42067 ERRS Challenger CH115A
2255975Water sample data1994-10-08 05:03:3053.96537 N, 0.42073 ERRS Challenger CH115A
2262308Water sample data1994-10-08 05:03:3053.96537 N, 0.42073 ERRS Challenger CH115A
834017CTD or STD cast1994-10-08 05:31:0053.9605 N, 0.4245 ERRS Challenger CH115A
577813Transmittance/attenuance, turbidity, or SPM conc.1994-11-12 13:48:0053.9752 N, 0.4212 ERRS Challenger CH115C
426326Waves (1D spectra)1994-11-12 14:50:1553.9752 N, 0.4212 ERRS Challenger CH115C