Member State report / Art8 / 2018 / D5 / Portugal / NE Atlantic: Macaronesia

Report type Member State report to Commission
MSFD Article Art. 8 Initial assessment (and Art. 17 updates)
Report due 2018-10-15
GES Descriptor D5 Eutrophication
Member State Portugal
Region/subregion NE Atlantic: Macaronesia
Reported by DGRM
Report date 2021-03-03
Report access ART8_GES_PT_setembro2020.xml

Azores Subdivision (AMA-PT-SD-AZO)

GES component
D5
D5
D5
D5
D5
D5
D5
D5
Feature
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Element
Nutrients (integrated)
Chlorophyll-a
Cyanobacterial bloom index: Cyanobacterial biomass+cyanobacteria surface accumulations
Photic limit
Dissolved oxygen
Benthic habitats - opportunistic macroalgae
Benthic habitats - macrophyte communities
Benthic habitats - macrobenthic communities
Element code
FI_Nutrients
EEA_3164-01-0
Combined_E
EEA_3111-01-1
EEA_3132-01-2
QE1-2-1
QE1-2-2
QE1-3
Element code source
Species (D1) http://www.marinespecies.org/
Link to other vocabulary or code lists that may be relevant
Undefined
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Element 2
Element 2 code
Element 2 code source
Element source
MS in (sub)region
MS in (sub)region
MS in (sub)region
MS in (sub)region
MS in (sub)region
MS in (sub)region
MS in (sub)region
MS in (sub)region
Criterion
D5C1
D5C2
D5C3
D5C4
D5C5
D5C6
D5C7
D5C8
Parameter
Concentration in water
Concentration in water
Extent
Transparency in water
Concentration in water
Extent
Parameter other
Threshold value upper
Threshold value lower
Threshold qualitative
Qualitative assessment
Qualitative assessment
Qualitative assessment
Qualitative assessment
Qualitative assessment
Qualitative assessment
Threshold value source
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Not applicable
Threshold value source other
Value achieved upper
Value achieved lower
Value unit
Value unit other
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend
Stable
Stable
Stable
Stable
Stable
Stable
Parameter achieved
Yes
Yes
Yes
Yes
Yes
Yes
Description parameter
Underground flows in most of the islands are higher than surface run-off, accounting for 53.2 % of the total on the island of Flores, 55.0 % in Santa Maria, 67.9 % in São Miguel, 75.7 % in Terceira and 85.6 % in São Jorge. and 89.7 % in Graciosa
Higher values of chlorophyll are recorded for the northern area of the Exclusive Economic Zone surrounding the EEZ of the Azores together with the adjacent area of the extended continental shelf claimed by Portugal, i.e. between 28° and 40° N, 17° and 41° W, whereas variability has been higher in the areas plus the south of this area. At the same time, higher chlorophyll values were observed in the areas associated with the islands. For average net primary productivity estimates (NPP), determined between 2003-2013, they were 464.3 ± 142.2 mg/2-1. The highest concentrations were recorded in May (704 ± 64 mg/2.day-1) and minors in December (307 ± 15 mg/2.day-1). For particulate matter average monthly average organic carbon estimates, determined from 2003-2013, these ranged from about 42.1 ± 2.9 mg.m-3 in September and 73.8 ± 6.4 mg.m-3 in April, having been the minimum of 37.43 and maximum 86,61 ± 11.19 mg.m-3, whereas the annual average was around 57.75 ± 11.19 mg.m-3. As regards particulate carbon, but for the inorganic component (particulate inorganic carbon), the average values determined between 2003 and 2013 varied between 0.00013 and 0.00049 mol.m-3, with an average of 0.00021 ± 0.0008 mol.m-3. [reference to: Please see attached written report]
On the island of São Miguel, for a total of 38 samples, 22 were positive for the occurrence of PSts. 7 absorption values were thus detected above the legal threshold for two starfish species (Ophidiaster ophidianus and Marthasterias glacialis) followed by molluscs belonging to the species Stronita haemasoma and Patella gomesii. Although there are no harmful algal blooms with a significant environmental impact, there has been a one-off occurrence reported for the island of São Jorge. These writers referred to the first expression of the toxic inado-ice-cream in the Azores in which high concentrations of more than 1,3 x 107 cells were recorded in September 2013 in the Fajã de Santo Christ lagoon and the island of São Jorge. Orange browned colours, with consequent fish mortality (Mugil cephalus) and bivalves (Ruditapes decussatus), derived from the occurrence of high levels of shellfish poison that exceeded 30 times acceptable levels for these toxic substances, which also led to four poisoning. The increase in phosphate levels has increased the abundance of the Prorocentrum dinofolice, which demonstrates storage and mobilisation capacity for phosphate while the capacity to store macronutrients was verified in diatoms of the genus Chaetoceros. Although the increase in the nitrogen level has promoted the abundance of inofolicice and diatoms, it has not been significant, which may indicate that phosphorus (together with trace metals), rather than nitrogen, is the limiting nutrient factor. In the island of São Miguel, and in particular in São Roque, two strains of cyanobacteria, in particular Synehatystis sp. and Chroococccales, were isolated from the species of sponges Polypotent agglutinans and Tedania Ignis, respectively. Although the two strains have already been demonstrated to be embryotoxic, on the contrary no change in the larval length has been observed, which will allow the inference that their toxic effect is only felt in the early embryonic stages of the sea urchins. [further details and related bibliographic references are available in the written report]
On the islands of São Miguel, Santa Maria and Terceira, it was observed that the depth values of the euphotic zone varied between 30 and 130 m, 20 m and 105 m and 53 m and 130 m respectively. In addition, values for the euphotic area of 33 m and 4 m respectively were recorded for the Islands of the Triangle (Faial, Pico and São Jorge) and for the island of Corvo. Active radiation from photosynthesis with basic values for the photic zone of approximately 70 m depth and the dysphotic limit is approximately 150 m deep. Bio-erosion, primarily a light availability function for the phototrophic bodies of phototrophic and for herbivorous grazing livestock, is 10 times higher in the more illuminated area of the photic zone. Specifically, for the southern part of the Canal Faial, the superficial irradiance varied between 809 and 2611 ?mol phtons m ? 2 s ? 1 and between 419 and 1797 ?mol phtons m ? 2 s ? 1, respectively, above and immediately below the water surface
In the Azores, dissolved oxygen concentrations in seawater show a variation of approximately 5 to 6 ml/l (surface) to < 4 ml/l in the deep water areas, with, on the surface, a tendency to increase and decrease respectively to the north and south and south-east of the Azores. Winter and spring seasons, which account for higher productivity periods, do not, however, show the maximum values for dissolved oxygen
In the Azores, there are sites without registration of opportunistic species and the maximum figure for the average proportion of these species was 0.38 for the island of Santa Maria. 4 species of opportunistic macroalgae have been identified: Chaetomorpha pachynema, Ulva Compressa, Ulva intestinal insalis and Ulva rida (Wallenstein, Neto, et al., 2013). However, there was an increase in this value with a further 6 species, namely, Ulva compressa, Porphyra sp. Arctocarpus fasciatus, Ectocarpus siliculosus, minimum and Chaetomorpha pha aerea for the island of São Miguel. In fact, opportunistic green algae are known to be responsive to nutrient enrichment and are more sensitive to changes in water quality than other opportunistic species, with the species of the genera Ulva, Chaetomorpha or Cladhora are in fact the most commonly used species in the outcrops, although the species of the genera Ceramium, Ecoccarpus and Porphyra can reach proportions. In addition, results have shown that for a total of 43 macroalgal taxa recorded and in which Pico Island has the highest number of opportunistic taxa (4), in a ratio of 58 %, which is in line with previous studies. [further details and related bibliographic references are available in the written report]
Related indicator
Criteria status
Good
Good
Good
Good
Good
Good
Not assessed
Not assessed
Description criteria
The Azores vary widely and seasonally in oceanographic conditions. Given the high exposure of the coasts of the Azores islands resulting from their oceanic position associated with high seas and a strong wave, as well as the great distance between them, the oligotrophic nature of marine water bodies, the low population density of the Azores and the low degree of industrialisation, it will be accepted that the inflow of nutrients into the coastal areas is negligible. However, in specific areas such as ports, marinas, and bays, a higher risk of eutrophication with explosive development of algae with toxic potential is expected. In parallel, the bodies of coastal water present a good State Excellent according to the WFD assessment, while the need to reduce nutrient discharge to prevent pollution of inland water bodies and, consequently, the coastal environment. [reference to: Please see attached written report]
The concentrations of the sea chlorophyll are not particularly high in the Region of the Azores, with these low values, together with other chemical parameters, one of the indicators confirming the marine oligotrophic nature of the Azores-Madeira region. However, it is recognised that the annual climatological pattern of chlorophyll distribution is significantly similar to the nutrient standard, which implies that the supply of nutrients during the winter controls the annual pattern at the level of chlorophyll concentration. In fact, the average chlorophyll concentration is higher during spring, in the Azores Central Group, with the Eastern Group having the lowest productivity (also for the winter period), which could suggest that local biological and nutritional enrichment is highly dependent on the islands? interaction with the oceanographic characteristics inherent in the Gulf Stream. At the same time, a localised area has been identified between the central and eastern groups with a different pattern of variability when compared to neighbouring areas, and that there is less variation of chlorophyll a. the nutrient enrichment originates in the Gulf Stream and that during the winter conflushed onto the Archipelago of the chlorophyll origin water bodies. The authors therefore propose that the Azores Central Group should be regarded as an area where the west and east of the North Atlantic are brought together, and that it is also necessary to consider the inclusion of atmospheric carbon absorption processes due to the amount of primary production taking place there. [reference to: Please see attached written report]
Not qualitatively or quantitatively assessed as they require further studies on the subject, including monitoring of the occurrence and patterns of evolution of the various toxic substances which have been identified in the meantime. However, some important aspects regarding algal blooms and the emergence of toxins associated with algal blooms are mentioned in the element status and parameters. [further details and related bibliographic references are available in the written report]
The Azores being a oligotrophic region that is open in an open ocean area, the light is not a limiting factor and the occurrence of most nutrients is expected at the surface level by a dynamic process, such as an oceanic filament or a redemolition. However, the depth of the euphotic area is smaller in the autumn, unlike in the spring and summer, as cloud coverage is larger in the autumn months. [further details and related bibliographic references are available in the written report]
In the Azores region, although there is a clear link between the depth and the oxygen (dissolved oxygen, apparent use of oxygen and oxygen saturation) and the nutritional parameters (nitrates, phosphates and silicates), some distinct spatial patterns have been observed, which appear to show some independence from the depth of water. [further details and related bibliographic references are available in the written report]
There is, in the Azorean coastal areas in general, an ecological quality that can be considered as Good and/or Eled. Furthermore, according to all water bodies analysed, they meet the environmental requirements established by the WFD, where most of them are of high quality. [reference to: Please see attached written report]
Not applicable to the Azores. [further details and related bibliographic references are available in the written report]
In the Azores, the inter-tidal communities have a smaller variety of invertebrates associated with them compared to other regions of the Atlantic, which is probably due to the lesser extent of their inter-tidal biotopes resulting from very high wave power and high wave power. However, despite the secondary and optional character of this criterion, a very rough characterisation of the diversity of benthic macrofauna was presented in the Azores, highlighting some of the most relevant aspects. [further details and related bibliographic references are available in the written report]
Element status
Good
Good
Good
Good
Good
Good
Not assessed
Not assessed
Description element
As a result of agricultural fertiliser application on grassland, nitrogen leaching is an environmental pressure factor that negatively affects water quality in the Azores. Groundwater discharges, usually characterised by a higher concentration of nutrients, are an important element of the ocean?s chemical flows and thus result in a decrease in the quality of coastal waters. Pollution of the Azorean surface water and groundwater, resulting from agricultural activity, may be a significant concern. There are less good situations, such as those reported by the DRA and relating to various situations of discharges of waste water into the water lines, as well as contamination with fertilisers and pesticides from livestock farming. However, there are important factors, such as the hydrodynamism or the low population density of the islands that reduce the occurrence of nutrient concentrations that are too high in coastal areas to a large extent. [further details and related bibliographic references are available in the written report]
The same increase is due to the rapid cooling of the ocean associated with the passage of storms and the resulting conds-to-water phenomena of the mixing of water bodies as well as the input of nutrients from the deeper areas of the thermoclina and the transport of phytoplanktonic cells from the maximum length of chlorophyll for the surface areas of the water column. [further details and related bibliographic references are available in the written report]
There is little information about phytoplankton, although there is some knowledge about algal blooms in other parts of the world, with the most common sources of nutrients corresponding to the domestic effluents, the run-off of intensive farming activity as well as the food industry?s effluents. Experimental studies carried out also on samples taken off the island of Terceira have shown that an increase in phytoplankton biomass caused by an increase in nutrient levels is often dominated by diatoms, inofolinecreams or algae tree species. Shellfish paralytic shellfish toxins (PSTs) correspond to a type of toxins that are produced by various types of micro-algae and global distribution cyanobacteria. The fruits of the genera Alexandrium, Gymnodinium and Pyrorogram are those who produce these substances most of them with the majority of the poisonings associated with explosive events in these organisms. Along the island of Terceira, during the period between the end of the autumn and the winter, an abundance of cocolittics was increased as a result of the proliferation of the species eutrophic Emilania huxleyi and Gephyrocapsa ericsonii, although the highest abundance of those species was recorded during spring and winter, especially due to these two species. The same study also showed that the increase of colitolithromycin species is related to the increase in nutrient concentrations, such as phosphates, nitrates and silicates, as well as to the relative low temperatures of the ocean surface water or the mixing of the surface area of the water column. In the hydro-thermal source located off the island of Faial, the occurrence of individuals of green algae from the genera Euogontia sp. and Phaeophila sp., as well as of cyanobacterial endpoints Hyella sp. and the species Mastigocholeus testarum, have been recorded, which are characteristic organisms of the pioneering communities of microerosion
In the eiphic area (15 m), the development of a 40 registered biocenosis biocenosis in the euphotic zone has been observed after a year of exposure, but there has been a reduction in icnodiversity from the depth of 15 m due to a limitation on light availability associated with a gradual reduction of microophytic bodies of phototrophic as well as of consumer species. In addition, a number of different bioceneses have also been reported in the growing euphotic area (60 m) and in the deep-hotic area (150 m), with 46 and 41 recorded, respectively, with a general decline of icnodiversity with depth. Bathymetry patterns have been shown by the greater abundance of clophage between euphotic and dysphotic areas, while at depths ahotic occurred only chemotrophic organisms, where peak biodiversity peaks have been reported in the deep euphotic area, ranging from 15 to 60 m deep. [further details and related bibliographic references are available in the written report]
(2) 550-1 500 m: Variation between 75 and 96 %
Not applicable to the Azores. [further details and related bibliographic references are available in the written report]
Not assessed. [further details and related bibliographic references are available in the written report]
Integration rule type parameter
Other
Other
Other
Other
Other
Other
Other
Other
Integration rule description parameter
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
Integration rule type criteria
Other
Other
Other
Other
Other
Other
Other
Other
Integration rule description criteria
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
Qualitative evaluation: No integration rules applied
GES extent threshold
GES extent achieved
GES extent unit
GES achieved
GES achieved
GES achieved
GES achieved
GES achieved
GES achieved
GES achieved
GES achieved
GES achieved
Description overall status
For the assessment of Descriptor D5, the sources of information were based on the technical literature published and made available by the various official bodies as well as on scientific literature directly or indirectly related to the subject of coastal eutrophication in the Azores archipelago and described in the written report. In addition, it is important to highlight the important link of the MSFD with the WFD, as described by the European Commission and thus many of the significant content of the literature consulted is also based on the same assumptions established by the WFD. According to the qualitative analysis carried out on the most relevant scientific studies available to the Azores, despite a number of very one-off occurrences, it is proposed that GES should be considered overall. [further details and related bibliographic references are available in the written report]
For the assessment of Descriptor D5, the sources of information were based on the technical literature published and made available by the various official bodies as well as on scientific literature directly or indirectly related to the subject of coastal eutrophication in the Azores archipelago and described in the written report. In addition, it is important to highlight the important link of the MSFD with the WFD, as described by the European Commission and thus many of the significant content of the literature consulted is also based on the same assumptions established by the WFD. According to the qualitative analysis carried out on the most relevant scientific studies available to the Azores, despite a number of very one-off occurrences, it is proposed that GES should be considered overall. [further details and related bibliographic references are available in the written report]
For the assessment of Descriptor D5, the sources of information were based on the technical literature published and made available by the various official bodies as well as on scientific literature directly or indirectly related to the subject of coastal eutrophication in the Azores archipelago and described in the written report. In addition, it is important to highlight the important link of the MSFD with the WFD, as described by the European Commission and thus many of the significant content of the literature consulted is also based on the same assumptions established by the WFD. According to the qualitative analysis carried out on the most relevant scientific studies available to the Azores, despite a number of very one-off occurrences, it is proposed that GES should be considered overall. [further details and related bibliographic references are available in the written report]
For the assessment of Descriptor D5, the sources of information were based on the technical literature published and made available by the various official bodies as well as on scientific literature directly or indirectly related to the subject of coastal eutrophication in the Azores archipelago and described in the written report. In addition, it is important to highlight the important link of the MSFD with the WFD, as described by the European Commission and thus many of the significant content of the literature consulted is also based on the same assumptions established by the WFD. According to the qualitative analysis carried out on the most relevant scientific studies available to the Azores, despite a number of very one-off occurrences, it is proposed that GES should be considered overall. [further details and related bibliographic references are available in the written report]
For the assessment of Descriptor D5, the sources of information were based on the technical literature published and made available by the various official bodies as well as on scientific literature directly or indirectly related to the subject of coastal eutrophication in the Azores archipelago and described in the written report. In addition, it is important to highlight the important link of the MSFD with the WFD, as described by the European Commission and thus many of the significant content of the literature consulted is also based on the same assumptions established by the WFD. According to the qualitative analysis carried out on the most relevant scientific studies available to the Azores, despite a number of very one-off occurrences, it is proposed that GES should be considered overall. [further details and related bibliographic references are available in the written report]
For the assessment of Descriptor D5, the sources of information were based on the technical literature published and made available by the various official bodies as well as on scientific literature directly or indirectly related to the subject of coastal eutrophication in the Azores archipelago and described in the written report. In addition, it is important to highlight the important link of the MSFD with the WFD, as described by the European Commission and thus many of the significant content of the literature consulted is also based on the same assumptions established by the WFD. According to the qualitative analysis carried out on the most relevant scientific studies available to the Azores, despite a number of very one-off occurrences, it is proposed that GES should be considered overall. [further details and related bibliographic references are available in the written report]
For the assessment of Descriptor D5, the sources of information were based on the technical literature published and made available by the various official bodies as well as on scientific literature directly or indirectly related to the subject of coastal eutrophication in the Azores archipelago and described in the written report. In addition, it is important to highlight the important link of the MSFD with the WFD, as described by the European Commission and thus many of the significant content of the literature consulted is also based on the same assumptions established by the WFD. According to the qualitative analysis carried out on the most relevant scientific studies available to the Azores, despite a number of very one-off occurrences, it is proposed that GES should be considered overall. [further details and related bibliographic references are available in the written report]
For the assessment of Descriptor D5, the sources of information were based on the technical literature published and made available by the various official bodies as well as on scientific literature directly or indirectly related to the subject of coastal eutrophication in the Azores archipelago and described in the written report. In addition, it is important to highlight the important link of the MSFD with the WFD, as described by the European Commission and thus many of the significant content of the literature consulted is also based on the same assumptions established by the WFD. According to the qualitative analysis carried out on the most relevant scientific studies available to the Azores, despite a number of very one-off occurrences, it is proposed that GES should be considered overall. [further details and related bibliographic references are available in the written report]
Assessments period
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
2012-2018
Related pressures
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Input of organic matter - diffuse sources and point sources
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Input of organic matter - diffuse sources and point sources
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Input of organic matter - diffuse sources and point sources
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Input of organic matter - diffuse sources and point sources
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Input of organic matter - diffuse sources and point sources
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Input of organic matter - diffuse sources and point sources
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Input of organic matter - diffuse sources and point sources
  • Input of nutrients - diffuse sources, point sources, atmospheric deposition
  • Input of organic matter - diffuse sources and point sources
Related targets
  • D5-AZO-M1
  • D5-AZO-M2
  • D5-AZO-M3
  • D5-AZO-M4
  • D5-AZO-M1
  • D5-AZO-M2
  • D5-AZO-M3
  • D5-AZO-M4
  • D5-AZO-M1
  • D5-AZO-M2
  • D5-AZO-M3
  • D5-AZO-M4
  • D5-AZO-M1
  • D5-AZO-M2
  • D5-AZO-M3
  • D5-AZO-M4
  • D5-AZO-M1
  • D5-AZO-M2
  • D5-AZO-M3
  • D5-AZO-M4
  • D5-AZO-M1
  • D5-AZO-M2
  • D5-AZO-M3
  • D5-AZO-M4
  • D5-AZO-M1
  • D5-AZO-M2
  • D5-AZO-M3
  • D5-AZO-M4
  • D5-AZO-M1
  • D5-AZO-M2
  • D5-AZO-M3
  • D5-AZO-M4

Madeira subdivision (AMA-PT-SD-MAD)

GES component
D5
D5
D5
D5
Feature
Eutrophication
Eutrophication
Eutrophication
Eutrophication
Element
Nutrients (integrated)
Chlorophyll-a
Transparency
Dissolved oxygen
Element code
FI_Nutrients
EEA_3164-01-0
QE3-1-1
EEA_3132-01-2
Element code source
Undefined
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Eutrophication (D5)(EQRs) http://dd.eionet.europa.eu/vocabulary/wise/ObservedPropertyBiologyEQR/view
Eutrophication (D5) and contaminants (D8-D9) http://dd.eionet.europa.eu/vocabulary/wise/ObservedProperty/view
Element 2
Element 2 code
Element 2 code source
Element source
MS in (sub)region
MS in (sub)region
MS in (sub)region
MS in (sub)region
Criterion
D5C1
D5C2
D5C4
D5C5
Parameter
Concentration in water
Concentration in water
Transparency in water
Concentration in water
Parameter other
Threshold value upper
10.0
5.0
2.0
6.0
Threshold value lower
Threshold qualitative
Threshold value source
Water Framework Directive (2000/60/EC)
Waste Framework Directive (2008/98/EC)
National
Water Framework Directive (2000/60/EC)
Threshold value source other
Value achieved upper
12.03
5.871
35.0
7.3
Value achieved lower
1.6
9.0
5.9
Value unit
micromole per litre
microgram per litre
metre
milligram per litre
Value unit other
Proportion threshold value
Proportion value achieved
Proportion threshold value unit
Trend
Unknown
Unknown
Not relevant
Unknown
Parameter achieved
Yes
Yes, based on low risk
Yes
Yes, based on low risk
Description parameter
Oxygen values are on average close to the saturation values and do not vary significantly
Related indicator
  • AMA-PT-MAD_Nutrients
  • AMA-PT-MAD_Chla
  • AMA-PT_MAD_TRA
  • AMA-PT-MAD_DO
Criteria status
Good
Good, based on low risk
Good
Good
Description criteria
Element status
Good
Good
Good
Good
Description element
Integration rule type parameter
Integration rule description parameter
Integration rule type criteria
Integration rule description criteria
GES extent threshold
GES extent achieved
100.00
100.00
100.00
100.00
GES extent unit
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
Proportion of area in good status
GES achieved
GES achieved
GES achieved
GES achieved
GES achieved
Description overall status
Existing scientific knowledge and data do not allow the use of high levels of reference and limit values. However, this assessment of the GES of D5, the Autonomous Region of Madeira (RAM) does not fully follow Commission Decision (EU) 2017/848. The thresholds do not apply to the subdivision of Madeira because no limit values have been set for Madeira, i.e. only limit values have been set for mainland Portugal on the basis of the ecological characteristics, effect of coastal contact and salinity regime of continental marine waters. It is essential that a description be made for the subdivision of Madeira for the next MSFD cycle, and appropriate limit values are defined. This evaluation follows the same delimitation used in the assessment of the initial status of the waters of the subdivision of Madeira (SRA, 2014), which follows the steps described by OSPAR (2005). Despite very limited information on the distribution of nutrients and organic matter, the origin of which generally concerns area A1, there is no record of human activities justifying the non-natural variation of those parameters or which could induce biodiversity losses or the degradation of benthic communities.
Existing scientific knowledge and data do not allow the use of high levels of reference and limit values. However, this assessment of the GES of D5, the Autonomous Region of Madeira (RAM) does not fully follow Commission Decision (EU) 2017/848. The thresholds do not apply to the subdivision of Madeira because no limit values have been set for Madeira, i.e. only limit values have been set for mainland Portugal on the basis of the ecological characteristics, effect of coastal contact and salinity regime of continental marine waters. It is essential that a description be made for the subdivision of Madeira for the next MSFD cycle, and appropriate limit values are defined. This evaluation follows the same delimitation used in the assessment of the initial status of the waters of the subdivision of Madeira (SRA, 2014), which follows the steps described by OSPAR (2005). Despite very limited information on the distribution of nutrients and organic matter, the origin of which generally concerns area A1, there is no record of human activities justifying the non-natural variation of those parameters or which could induce biodiversity losses or the degradation of benthic communities.
Existing scientific knowledge and data do not allow the use of high levels of reference and limit values. However, this assessment of the GES of D5, the Autonomous Region of Madeira (RAM) does not fully follow Commission Decision (EU) 2017/848. The thresholds do not apply to the subdivision of Madeira because no limit values have been set for Madeira, i.e. only limit values have been set for mainland Portugal on the basis of the ecological characteristics, effect of coastal contact and salinity regime of continental marine waters. It is essential that a description be made for the subdivision of Madeira for the next MSFD cycle, and appropriate limit values are defined. This evaluation follows the same delimitation used in the assessment of the initial status of the waters of the subdivision of Madeira (SRA, 2014), which follows the steps described by OSPAR (2005). Despite very limited information on the distribution of nutrients and organic matter, the origin of which generally concerns area A1, there is no record of human activities justifying the non-natural variation of those parameters or which could induce biodiversity losses or the degradation of benthic communities.
Existing scientific knowledge and data do not allow the use of high levels of reference and limit values. However, this assessment of the GES of D5, the Autonomous Region of Madeira (RAM) does not fully follow Commission Decision (EU) 2017/848. The thresholds do not apply to the subdivision of Madeira because no limit values have been set for Madeira, i.e. only limit values have been set for mainland Portugal on the basis of the ecological characteristics, effect of coastal contact and salinity regime of continental marine waters. It is essential that a description be made for the subdivision of Madeira for the next MSFD cycle, and appropriate limit values are defined. This evaluation follows the same delimitation used in the assessment of the initial status of the waters of the subdivision of Madeira (SRA, 2014), which follows the steps described by OSPAR (2005). Despite very limited information on the distribution of nutrients and organic matter, the origin of which generally concerns area A1, there is no record of human activities justifying the non-natural variation of those parameters or which could induce biodiversity losses or the degradation of benthic communities.
Assessments period
2014-2018
2014-2018
2014-2018
2014-2018
Related pressures
  • All pressures related to inputs of substances, litter and energy
  • All pressures related to inputs of substances, litter and energy
  • All pressures related to inputs of substances, litter and energy
  • All pressures related to inputs of substances, litter and energy
Related targets