Member State report / Art8-2024 / 2024 / D4 / Spain / Mediterranean: Western Mediterranean Sea
| Report type | Member State report to Commission |
| MSFD Article | Art8 |
| Report due | 2024-10-15 |
| GES Descriptor | D4 Food webs/D1 Ecosystems |
| Member State | Spain |
| Region/subregion | Mediterranean: Western Mediterranean Sea |
| Report date | 2026-03-24 07:53:11 |
Demarcación marina del Estrecho y Alborán (MWE-ES-SD-ESAL)
Regional assessment area |
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Component MRUs |
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GES component |
D4
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D4
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D4
|
D4
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D4
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D4
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D4
|
D4
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D4
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D4
|
D4
|
D4
|
D4
|
D4
|
D4
|
D4
|
D4
|
D4
|
D4
|
D4
|
D4
|
D4
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D4
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D4
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D4
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D4
|
D4
|
D4
|
D4
|
D4
|
D4
|
D4
|
Feature |
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Oceanic/deep-sea ecosystem
|
Shelf ecosystem
|
Oceanic/deep-sea ecosystem
|
Shelf ecosystem
|
Element |
All consumers |
All consumers |
Sub-apex demersal predators |
Sub-apex demersal predators |
top predators |
top predators |
All consumers |
All consumers |
Sub-apex demersal predators |
Sub-apex demersal predators |
top predators |
top predators |
All consumers |
Sub-apex demersal predators |
top predators |
All consumers |
Sub-apex demersal predators |
top predators |
All consumers |
Sub-apex demersal predators |
top predators |
All consumers |
Sub-apex demersal predators |
top predators |
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Element extent |
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Trend element |
Deteriorating |
Improving |
Stable |
Improving |
Improving |
Stable |
Stable |
Improving |
Improving |
Stable |
Deteriorating |
Stable |
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Element 2 |
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Average trophic level of marine consumers
|
Average trophic level of marine consumers
|
Average trophic level of marine consumers
|
Average trophic level of marine consumers
|
Average trophic level of marine consumers
|
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Trophic heterogeneity
|
Trophic heterogeneity
|
Trophic heterogeneity
|
Trophic heterogeneity
|
Trophic heterogeneity
|
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Element source |
OSPAR |
National |
OSPAR |
National |
OSPAR |
National |
OSPAR |
National |
OSPAR |
National |
OSPAR |
National |
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Criterion |
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C2
|
D4C2
|
D4C2
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D4C2
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D4C2
|
D4C2
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D4C2
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D4C2
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D4C3
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D4C3
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D4C4
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D4C4
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Parameter |
Other
|
Other
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Other
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Other
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Other
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Other
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Other
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Other
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Other
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Other
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Other
|
Other
|
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Threshold value upper |
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Threshold value lower |
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Threshold value operator |
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Threshold qualitative |
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Threshold value source |
Not applicable
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Not applicable
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Not applicable
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Not applicable
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Not applicable
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Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
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Value achieved upper |
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Value achieved lower |
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Value unit |
Other
|
Other
|
Other
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Other
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Other
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Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
Other
|
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Proportion threshold value |
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Proportion value achieved |
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Proportion threshold value unit |
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Trend parameter |
Deteriorating |
Stable |
Improving |
Stable |
Improving |
Deteriorating |
Improving |
Improving |
Stable |
Improving |
Stable |
Stable |
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Parameter achieved |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
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Description parameter |
RT-MTL indicator shows a significant downward trend for all community. This negative trend indicates that over the last two decades the benthic-demersal communities have experienced a decrease in the average trophic level. |
The indicator shows a significant decreasing trend. The negative result indicates that over the last two decades the benthic-demersal communities have experienced a slight decrease in the average trophic level. |
The indicator shows a significant increasing trend. This positive trend indicates that over the last two decades the benthic-demersal communities have experienced a slight improvement in the average trophic level. |
RT-MTL indicator obtains a non-significant result showing a stability of its mean trophic level. This lack of significant trend is interpreted as a sign of the resilience of the benthic-demersal communities throughout the historical series. |
RT-MTL shows a significant increasing trend indicating that mesopredators in shelf communities experienced an slight improvement in average trophic level over the last two decades. |
RT-MTL shows a significant decreasing trend indicating that apex predators in shelf communities experienced a decline in average trophic level over the last two decades. |
The indicator shows a significant recovery in slope areas when the whole community is considered in the analysis. |
Regarding the temporal trends of the slope for the scenario that considers all the meso and apical predators, RT-HT indicator shows a general increasing trend and recovery of trophic richness. |
The indicator for the apical predators in the slope area shows stability in the trophic richness patterns, with a non-significant increasing trend. |
If all community is considered, a recovery of this index can be seen in the shelf stratum, the indicator RT-HT shows a significant increasing trend with a high level of significance,indicating a general improvement of communities in deep waters. |
Mesopredators and apex predators show a moderate regression of the structural heterogeneity of the ecosystem, although it does not reach significant values. |
At the global level, the trend of the indicator RT-HT on the shelf shows patterns of loss of trophic richness, since the beginning of the historical series in 2001, although the results of the slope are not significant. |
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Related indicator |
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Criteria status |
Unknown |
Unknown |
Unknown |
Unknown |
Not assessed |
Not assessed |
Unknown |
Unknown |
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Description criteria |
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Element status |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
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Description element |
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Source assessment feature |
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Reporting method feature |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Trend feature |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Integration rule type parameter |
Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Integration rule description parameter |
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Integration rule type criteria |
Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
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Not relevant
|
Integration rule description criteria |
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GES extent threshold |
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GES extent achieved |
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GES extent unit |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
GES achieved |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Description overall status |
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Assessments period |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
Related pressures |
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Related targets |
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Test TV |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
Test results |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
False |
False |
False |
False |
Demarcación marina levantino-balear (MWE-ES-SD-LEV)
Regional assessment area |
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Component MRUs |
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GES component |
D4
|
D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
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D4
|
D4
|
D4
|
Feature |
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Oceanic/deep-sea ecosystem
|
Shelf ecosystem
|
Oceanic/deep-sea ecosystem
|
Oceanic/deep-sea ecosystem
|
Shelf ecosystem
|
Shelf ecosystem
|
Element |
All consumers |
All consumers |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
Sub-apex demersal predators |
Sub-apex demersal predators |
top predators |
top predators |
All consumers |
All consumers |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
Sub-apex demersal predators |
Sub-apex demersal predators |
top predators |
top predators |
All consumers |
All consumers |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
Sub-apex demersal predators |
top predators |
All consumers |
All consumers |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
Sub-apex demersal predators |
top predators |
All consumers |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
Sub-apex demersal predators |
top predators |
All consumers |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
All trophic guilds |
Sub-apex demersal predators |
top predators |
All trophic guilds |
All trophic guilds |
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Element extent |
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Trend element |
Stable |
Improving |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Improving |
Stable |
Stable |
Stable |
Stable |
Improving |
Stable |
Improving |
Deteriorating |
Improving |
Stable |
Stable |
Stable |
Stable |
Stable |
Stable |
Improving |
Stable |
Stable |
Stable |
Stable |
Improving |
Improving |
Improving |
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Element 2 |
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Biomass of IUCN-endangered species in the community |
Biomass of commercial species
|
Finn's mean Path Length
|
IUCN-endangered species in the catch
|
Kempton's biodiversity index
|
Mean transfer efficiency
|
Mean trophic level of the catch
|
Mean trophic level of the community
|
Psust
|
System omnivory index
|
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Biomass of IUCN-endangered species in the community |
Biomass of commercial species
|
Finn's mean Path Length
|
IUCN-endangered species in the catch
|
Kempton's biodiversity index
|
Mean transfer efficiency
|
Mean trophic level of the catch
|
Mean trophic level of the community
|
Psust
|
System omnivory index
|
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Average trophic level of marine consumers
|
Average trophic level of marine consumers
|
Finn's mean Path Length
|
IUCN-endangered species in the catch
|
Kempton's biodiversity index
|
Mean trophic level of the catch
|
Mean trophic level of the community
|
System omnivory index
|
Average trophic level of marine consumers
|
Average trophic level of marine consumers
|
Average trophic level of marine consumers
|
Average trophic level of marine consumers
|
Finn's mean Path Length
|
IUCN-endangered species in the catch
|
Kempton's biodiversity index
|
Mean trophic level of the catch
|
Mean trophic level of the community
|
System omnivory index
|
Average trophic level of marine consumers
|
Average trophic level of marine consumers
|
Trophic heterogeneity
|
Biomass of IUCN-endangered species in the community |
Biomass of IUCN-endangered species in the community |
Finn's mean Path Length
|
Kempton's biodiversity index
|
Mean trophic level of the catch
|
Mean trophic level of the community
|
Psust
|
System omnivory index
|
Trophic heterogeneity
|
Trophic heterogeneity
|
Trophic heterogeneity
|
Biomass of IUCN-endangered species in the community |
Biomass of IUCN-endangered species in the community |
Finn's mean Path Length
|
Kempton's biodiversity index
|
Mean trophic level of the catch
|
Mean trophic level of the community
|
Psust
|
System omnivory index
|
Trophic heterogeneity
|
Trophic heterogeneity
|
Psust
|
Psust
|
||||||||
Element source |
OSPAR |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
OSPAR |
National |
OSPAR |
National |
OSPAR |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
National |
OSPAR |
National |
OSPAR |
National |
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Criterion |
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C1
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C2
|
D4C3
|
D4C3
|
D4C4
|
D4C4
|
D4C4
|
D4C4
|
||||||||||||||||||||||||||||||||
Parameter |
Other
|
Other
|
Trophic interaction
|
Biomass
|
Kempton
|
Trophic level
|
Trophic level
|
Biodiversity
|
Other
|
Other
|
Other
|
Other
|
Trophic interaction
|
Biomass
|
Kempton
|
Trophic level
|
Trophic level
|
Biodiversity
|
Other
|
Other
|
Other
|
Biomass
|
Biomass
|
Trophic interaction
|
Kempton
|
Trophic level
|
Trophic level
|
Probability
|
Biodiversity
|
Other
|
Other
|
Other
|
Biomass
|
Biomass
|
Trophic interaction
|
Kempton
|
Trophic level
|
Trophic level
|
Probability
|
Biodiversity
|
Other
|
Other
|
Probability
|
Probability
|
||||||||||||||||||||||||||||||||||||||||
Threshold value upper |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value lower |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value operator |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold qualitative |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Threshold value source |
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
Not applicable
|
||||||||||||||||||||||||||||||||||||||||
Value achieved upper |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Value achieved lower |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Value unit |
percentage
|
Other
|
nr
|
percentage
|
Adimensional
|
Adimensional
|
Adimensional
|
Adimensional
|
Other
|
Other
|
percentage
|
Other
|
nr
|
percentage
|
Adimensional
|
Adimensional
|
Adimensional
|
Adimensional
|
Other
|
Other
|
Other
|
t/km2
|
t/km2
|
nr
|
Adimensional
|
Adimensional
|
Adimensional
|
percentage
|
Adimensional
|
Other
|
Other
|
Other
|
t/km2
|
t/km2
|
nr
|
Adimensional
|
Adimensional
|
Adimensional
|
percentage
|
Adimensional
|
Other
|
Other
|
percentage
|
percentage
|
||||||||||||||||||||||||||||||||||||||||
Proportion threshold value |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Proportion value achieved |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Proportion threshold value unit |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Trend parameter |
Stable |
Stable |
Stable |
Stable |
Stable |
Improving |
Stable |
Stable |
Stable |
Stable |
Stable |
Deteriorating |
Stable |
Stable |
Stable |
Improving |
Stable |
Stable |
Stable |
Improving |
Improving |
Stable |
Stable |
Stable |
Stable |
Improving |
Stable |
Stable |
Stable |
Improving |
Improving |
Improving |
Stable |
Stable |
Stable |
Stable |
Improving |
Stable |
Stable |
Stable |
Improving |
Improving |
Stable |
Stable |
||||||||||||||||||||||||||||||||||||||||
Parameter achieved |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
||||||||||||||||||||||||||||||||||||||||
Description parameter |
The RT-mTE shows signs of stability over time.
|
RT-MTL indicator obtains a non-significant result showing a stability of its mean trophic level. This lack of significant trend is interpreted as a sign of the resilience of the benthic-demersal communities throughout the historical series. |
The RT-PL shows signs of stability over time.
|
The RT-IUCN species C shows a non-significant decreasing trend over the analysed time period. |
The RT-Kempton's Q shows a non-significant increasing trend over the analysed time period. |
The RT-mTLc index displays a significant increasing trend, suggesting a gradual recovery of the ecosystem's trophic structure over the analysed time period. |
The RT-mTLco shows a non-significant decreasing trend over the time period analysed. |
The RT-SOI shows a non-significant decreasing trend over the time period analysed. |
RT-MTL indicator obtains a non-significant result showing a stability of its mean trophic level. This lack of significant trend is interpreted as a sign of the resilience of the benthic-demersal communities throughout the historical series. |
RT-MTL indicator obtains a non-significant result showing a stability of its mean trophic level. This lack of significant trend is interpreted as a sign of the resilience of the benthic-demersal communities throughout the historical series. |
The RT-mTE shows signs of stability over time.
|
RT-MTL indicator shows a significant downward trend for all community. This negative trend indicates that over the last two decades the benthic-demersal communities have experienced a decrease in the average trophic level. |
The RT-PL shows signs of stability over time.
|
The RT-IUCN species C shows a non-significant decreasing trend over the analysed time period. |
The RT-Kempton's Q shows a non-significant increasing trend over the analysed time period. |
The RT-mTLc indicator displays a significant increasing trend, suggesting a gradual recovery of the ecosystem's trophic structure over the analysed time period. |
The RT-mTLco shows a non-significant decreasing trend over the time period analysed. |
The RT-SOI shows a non-significant decreasing trend over the analysed time period. |
RT-MTL indicator obtains a non-significant result showing a stability of its mean trophic level. This lack of significant trend is interpreted as a sign of the resilience of the benthic-demersal communities throughout the historical series. |
The indicator shows a significant increasing trend. This positive trend indicates that over the last two decades the benthic-demersal communities have experienced a slight improvement in the average trophic level. |
The indicator shows a significant recovery in slope areas when the whole community is considered in the analysis. |
The RT-Commercial B shows a non-significant decreasing trend over the analysed time period. |
The RT-IUCN species B shows a non-significant decreasing trend over the analysed time period. |
The RT-PL shows signs of stability over time.
|
The RT-Kempton's Q shows a non-significant increasing trend over the analysed time period. |
The RT-mTLc index displays a significant increasing trend, suggesting a gradual recovery of the ecosystem's trophic structure over the analysed time period. |
The RT-mTLco shows a non-significant decreasing trend over the time period analysed. |
The RT-Psust exhibits a significant increase during the initial part of the time series, but shows a non-significant trend over the rest of the time period analysed. |
The RT-SOI shows a non-significant decreasing trend over the time period analysed. |
Regarding the temporal trends of the slope for the scenario that considers all the meso and apical predators, RT-HT indicator shows a general increasing trend and recovery of trophic richness. |
The indicator for the apical predators in the slope area shows a significant increasing trend. This positive trend indicates that over the last two decades the benthic-demersal communities have experienced a slight improvement in the average trophic level. |
If all community is considered, a recovery of this index can be seen in the shelf stratum, the indicator RT-HT shows a significant increasing trend with a high level of significance,indicating a general improvement of communities in deep waters. |
The RT-Commercial B shows a non-significant decreasing trend over the analysed time period. |
The RT-IUCN species B shows a non-significant decreasing trend over the the analysed time period. |
The RT-PL shows signs of stability over time.
|
The RT-Kempton's Q shows a non-significant increasing trend over the analysed time period. |
The RT-mTLc indicator displays a significant increasing trend, suggesting a gradual recovery of the ecosystem's trophic structure over the analysed time period. |
The RT-mTLco shows a non-significant decreasing trend over the time period analysed. |
The RT-Psust exhibits a significant increase during the initial part of the time series, but shows a non-significant trend over the rest of the time period. |
The RT-SOI shows a non-significant decreasing trend over the analysed time period. |
Mesopredators and apex predators show a a recovery of this index can be seen in the shelf stratum, the indicator RT-HT shows a significant increasing trend with a high level of significance,indicating a general improvement of communities in deep waters. |
Apex predators show a a recovery of this index can be seen in the shelf stratum, the indicator RT-HT shows a significant increasing trend with a high level of significance,indicating a general improvement of communities in deep waters. |
The RT-Psust exhibits a significant increase during the initial part of the time series, but shows a non-significant trend over the rest of the time period analysed. |
The RT-Psust exhibits a significant increase during the initial part of the time series, but shows a non-significant trend over the rest of the time period. |
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Related indicator |
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Criteria status |
Unknown |
Unknown |
Unknown |
Unknown |
Not assessed |
Not assessed |
Unknown |
Unknown |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Description criteria |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Element status |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
||||||||||||||||||||||||||||||||||||||||||||||||||||
Description element |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Source assessment feature |
|
|
|
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|
|
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|
|
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|
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|
|
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|
|
|
|
|
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|
|
|
|
|
|
Reporting method feature |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Type D |
Trend feature |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Integration rule type parameter |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description parameter |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Integration rule type criteria |
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Not relevant
|
Integration rule description criteria |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
GES extent threshold |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
GES extent achieved |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
GES extent unit |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
Not relevant |
GES achieved |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Unknown |
Description overall status |
||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||||
Assessments period |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
2001-2022 |
Related pressures |
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Related targets |
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Test TV |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
NA |
Test results |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
Correct |
False |
False |
False |
Correct |
False |
Correct |