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to Cefas at present. 

Once published, the data will be licensed under the Open Government Licence 
v3.0 (
`https://www.nationalarchives.gov.uk/doc/open-government-licence/version/3/`_
) – Please note the applicable attribution statement is as follows: ‘includes 
Crown copyright, Cefas 2025'


.. _`https://www.nationalarchives.gov.uk/doc/open-government-licence/version/3/`:
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-   CEND072023 – North Sea (Farnes Deep, Fulmar, &amp; Dogger Bank) – May 20-   th-    to June 10-   
    th-   , 2023.
-   CEND172023 – Celtic Sea – November 9-   th-    to November 28-   th-   , 2023.
-   CEND092024 – North Sea (Farnes Deep, Fulmar, &amp; Dogger Bank) - May 24-   th-    to June 9-   
    th-   , 2024.

This dataset was produced by work supported jointly by the Joint Nature Conservation Committee 
(JNCC) lead NC40 Offshore Marine Monitoring project funded by Department of Environment, Food, 
&amp; Rural Affairs (Defra) under its flagship marine Natural Capital and Ecosystem Assessment 
(mNCEA) programme and by the Defra funded Carbon Management Project (project number MRD333). 
Find out more about mNCEA at 
`https://www.gov.uk/government/publications/natural-capital-and-ecosystem-assessment-programme`_
.

At each station within a survey a NIOZ Box Corer was deployed collecting core up to a maximum 
sediment depth of 30cm. A surface scrape was taken from each core, and a metal cylinder was 
used to take 10cm diameter sub core which were sliced at 2cm intervals for CEND072023 and 
CEND172023, and 1cm for CEND092024. As soon as was reasonably practicable after delivery of 
sample they were freeze dried at -30 Deg C and then transferred to zip locked plastic bags and 
stored at -80 Deg C until analysis. The Porosity measurement is based on dry and wet sediment 
weights made pre and post freeze drying. The pore fluid is assumed to have a salinity of 35 
(Unitless). Sediment particles are assumed to be quartz or feldspar with a specific gravity of 
2.65 (Unitless).

Freeze dried samples were extracted in acetone (90%) overnight for 18 to 24hrs. 
Spectrophotometric analysis was performed by measuring Chlorophyll (uncorrected) absorption at 
665nm and compensated for background turbidity at 750nm. An estimate of chlorophyll (corrected) 
in the presence of phaeopigments was made by acidifying the samples and measuring absorbance at 
665 and 750nm. An estimation of phaeopigments concentration was inferred from the uncorrected 
and corrected chlorophyll measurements. The method is a modification of that described in: 
“Methods for the Examination of Waters and Associated Material - The Determination of 
Chlorophyll a in Aquatic Environments". London Her Majesty’s Stationery Office. 1980. A data 
point can potentially have multiple Quality Flags (QFlags) which will be semicolon separated. 
Definition of each QFlag can be found in the QFlag text file attached to this record.


.. _`https://www.gov.uk/government/publications/natural-capital-and-ecosystem-assessment-programme`:
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