The 2019 assessment of CSEMP contaminant and biological effects data includes an assessment of the status and trends of EROD activity in fish at monitoring stations around the UK. Assessments are made for a large number of time series, each of EROD activity in males or females of a single species at a single monitoring station. This document synthesises the results of the individual time series to assess the status and trends of EROD activity at the biogeographic regional level.
The regional assessment only considers coastal and offshore stations and excludes estuarine stations. The results are therefore based on the monitoring data collected within the waters assessed under the Marine Strategy Framework Directive.For simplicity, the term ‘region’ is used throughout to describe biogeographic regions. MSFD sub-regions are always referred to as such.
The following sections:
A time series of EROD activities is assessed for status if:
The conditions are more stringent for trends. Specifically, a time series is assessed for trends if:
Note that all trend assessments for individual time series and most status assessments are based on the fit of a parametric model. This is important because only the parametric results are passed into the regional assessments in the following sections. As it turns out, none of the EROD time series were assessed for status using a non-parametric test.
The first tab below shows all the monitoring stations where there are individual time series assessments of trend or status for EROD. The purple circles are stations where there is a trend assessment and the light blue cirles are stations where there is only a status assessment, The areas delineated by the thinner black lines are the biogeographic regions; those delineated by the thicker black lines are the MSFD sub-regions.
The next set of tabs show the trend and status assessments for EROD. The colours have the following meaning:
And the shapes have the following meaning:
The final set of tabs give:
Number of time series with upwards, downwards or no trend by biogeographic region and MSFD sub-region
MSFD sub-region | biogeographic region | status | EROD |
---|---|---|---|
Greater North Sea | Northern North Sea | upward trend | 0 |
no trend | 8 | ||
downward trend | 4 | ||
Southern North Sea | upward trend | 0 | |
no trend | 9 | ||
downward trend | 1 | ||
E Channel | upward trend | 0 | |
no trend | 4 | ||
downward trend | 0 | ||
total | upward trend | 0 | |
no trend | 21 | ||
downward trend | 5 | ||
Celtic Seas | Minches & W Scotland | upward trend | 0 |
no trend | 2 | ||
downward trend | 0 | ||
Irish Sea | upward trend | 0 | |
no trend | 12 | ||
downward trend | 10 | ||
W Channel & Celtic Sea | upward trend | 0 | |
no trend | 4 | ||
downward trend | 2 | ||
total | upward trend | 0 | |
no trend | 18 | ||
downward trend | 12 |
Proportion of time series with upwards, downwards or no trend by biogeographic region and MSFD sub-region
MSFD sub-region | biogeographic region | status | EROD |
---|---|---|---|
Greater North Sea | Northern North Sea | upward trend | 0 |
no trend | 67 | ||
downward trend | 33 | ||
Southern North Sea | upward trend | 0 | |
no trend | 90 | ||
downward trend | 10 | ||
E Channel | upward trend | 0 | |
no trend | 100 | ||
downward trend | 0 | ||
total | upward trend | 0 | |
no trend | 81 | ||
downward trend | 19 | ||
Celtic Seas | Minches & W Scotland | upward trend | 0 |
no trend | 100 | ||
downward trend | 0 | ||
Irish Sea | upward trend | 0 | |
no trend | 55 | ||
downward trend | 45 | ||
W Channel & Celtic Sea | upward trend | 0 | |
no trend | 67 | ||
downward trend | 33 | ||
total | upward trend | 0 | |
no trend | 60 | ||
downward trend | 40 |
Number of time series with each status by biogeographic region and MSFD sub-region
MSFD sub-region | biogeographic region | status | EROD |
---|---|---|---|
Greater North Sea | Northern North Sea | blue | 8 |
orange | 9 | ||
Southern North Sea | blue | 5 | |
orange | 5 | ||
E Channel | blue | 4 | |
orange | 0 | ||
total | blue | 17 | |
orange | 14 | ||
Celtic Seas | Minches & W Scotland | blue | 2 |
orange | 0 | ||
Irish Sea | blue | 15 | |
orange | 6 | ||
W Channel & Celtic Sea | blue | 4 | |
orange | 2 | ||
total | blue | 21 | |
orange | 8 |
Proportion of time series with each status by biogeographic region and MSFD sub-region
MSFD sub-region | biogeographic region | status | EROD |
---|---|---|---|
Greater North Sea | Northern North Sea | blue | 47 |
orange | 53 | ||
Southern North Sea | blue | 50 | |
orange | 50 | ||
E Channel | blue | 100 | |
orange | 0 | ||
total | blue | 55 | |
orange | 45 | ||
Celtic Seas | Minches & W Scotland | blue | 100 |
orange | 0 | ||
Irish Sea | blue | 71 | |
orange | 29 | ||
W Channel & Celtic Sea | blue | 67 | |
orange | 33 | ||
total | blue | 72 | |
orange | 28 |
Tabulating the number of time series with each status category by region provides a quick summary of the individual time series results. However, it does not provide an objective regional assessment of status. Similarly, tabulating the number of time series with an upward or downward trend does not provide an objective regional assessment of trend. This section describes how the individual time series results can by synthesised in a meta-analysis to assess both status and trend at the regional level.
For a regional trend assessment, the trend in each time series is summarised by the estimated change in log activity over the last twenty years (or shorter if the time series doesn’t extend that far back). Regional trends are then estimated by fitting the following linear mixed model by restricted maximum likelihood:
The fixed model means that a trend is estimated for each region. The random model has three terms:
The meta-analysis is restricted to time series from monitoring stations that are classified as ‘representative’. ‘Baseline’ stations (those with near pristine conditions or only subject to very diffuse inputs) are omitted because any trends there will likely be caused by different processes to those at representative stations. Similarly ‘impacted’ stations (those close to a point source) are omitted because trends there will likely reflect changes due to the point source, and will be ‘unrepresentative’ at the regional level.
The meta-analysis is further restricted to regions with at least three trend stations with good geographic spread. Three stations is considered the minimum required to provide some sort of evidence base at the regional level.
For a regional status assessment, the status of each time series is summarised by the difference between the estimated mean log activity in the final monitoring year and the log assessment concentration. This ensures that status is always measured on the same scale, even though the assessment concentration might vary between species. Essentially the same linear mixed model as for trends is then fitted:
where status estimation variation is the variation in the status estimates from the individual time series analysis, assumed known and fixed.
There are no restrictions on the time series used in the status meta-analysis based on the classification of the monitoring station; time series from baseline, representative and impacted stations are all included.
Again, the meta-analysis is restricted to regions with at least three status stations with good geographic spread.
The results of both the trend and status regional assessments are back-transformed for presentation. The estimated regional trend is then interpreted as the percentage yearly change in activity and the estimated regional status as the ratio of the mean regional activity to the assessment concentration. To illustrate the latter, a value of 1 indicates that the mean regional activity is equal to the assessment concentration; a value of 0.5 indicates that it is half the assessment concentration, and a value of 2 indicates that it is twice the assessment concentration.
This section provides more detail on the number and geographic spread of the time series available for the meta-analyses. The map shows the stations with parametric trend and status assessments having excluded trend assessments at baseline and impacted stations. The purple circles are stations where there is a trend assessment and the light blue cirles are stations where there is only a status assessment,
The following regions have an insufficient number or time series or spread of stations and are excluded from the regional assessment:
The first 2 tabs show:
The symbols in all these plots have the following interpretation:
The final tab shows the estimates of the regional trend in EROD.
This table shows the estimates of the regional trend:
biogeographic region | trend | se | lower | upper | % yearly change | %yc lower | %yc upper |
---|---|---|---|---|---|---|---|
Northern North Sea | -6.79 | 2.68 | -12.05 | -1.54 | -6.57 | -11.35 | -1.52 |
Southern North Sea | -6.75 | 3.31 | -13.24 | -0.25 | -6.52 | -12.40 | -0.25 |
Irish Sea | -9.52 | 2.30 | -14.04 | -5.01 | -9.08 | -13.10 | -4.89 |
W Channel & Celtic Sea | 0.55 | 4.22 | -7.72 | 8.82 | 0.55 | -7.43 | 9.22 |
The first 2 tabs show:
The symbols in all the plots have the following interpretation:
The final tab shows the estimates of the regional status in EROD.
This table shows the estimates of the regional status:
biogeographic region | status | se | upper | concentration | conc upper |
---|---|---|---|---|---|
Northern North Sea | -0.97 | 0.36 | -0.39 | 0.38 | 0.68 |
Southern North Sea | -0.83 | 0.56 | 0.09 | 0.44 | 1.09 |
Irish Sea | -0.88 | 0.34 | -0.32 | 0.41 | 0.73 |
W Channel & Celtic Sea | -1.13 | 0.71 | 0.04 | 0.32 | 1.04 |