Member State report / Art11 / 2020 / D8 / Mediterranean
Report type | Member State report to Commission |
MSFD Article | Art. 11 Monitoring programmes (and Art. 17 updates) |
Report due | 2020-10-15 |
GES Descriptor | D8 Contaminants |
Region/subregion | Mediterranean |
Member state |
CY |
ES |
FR |
HR |
IT |
SI |
||||||||||||||||||||||||
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Report Access |
||||||||||||||||||||||||||||||
Descriptor |
D8 |
D8 |
D8 |
D8 |
D8 |
D8 |
||||||||||||||||||||||||
Monitoring strategy description |
Cyprus has implemented the program code MALCY-D08 in the geographical area of MAL-CY-MS to monitor pollutants in sediments and organisms (fish) and the investigation of pollution from accidental or illegal discharges. Under this program are the following sub programs. Sub program code MALCY-08-01 conducted yearly in the marine areas of Cyprus particularly the DFMR 2000/60/EC sampling stations. This sub program monitors pollutants in sediments. Sediment sampling is conducted using the CYS EN ISO 5667-19:2004, Water quality – Sampling - Part 19: Guidance on sampling in marine sediments, CYS EN ISO 5667-15:2009, Water quality – Sampling - Part 15: Guidance on the preservation and handling of sludge and sediment samples. Sediment samples (0 to 2 cm and 2 to 4 cm) are collected in triplicate at each sampling station using a Van Veen grab and placed into the appropriate sample container. The samples are analysed for nickel, lead, chromium, copper, cadmium, mercury, zinc polychlorinated biphenyls, polycyclic aromatic hydrocarbons at the State Chemical Laboratory following the methods outlined in DFMR (2020). The monitoring program follows the MSFD criteria and indicators of concentration of contaminants measured in the relevant matrix in a way that ensures comparability with the assessments under Directive 2000/60/EC, effects of contaminants, and occurrence, origin (if possible), extent of significant acute pollution events and their impact on biota physically affected; the UNEP/MAP (2013) criteria and indicators analysing concentration of key harmful contaminants in biota, sediment, or water, and occurrence, origin (if possible), extent of significant acute pollution events and their impact on biota physically affected. The DFMR (2020) report provided data from 2013 to 2019 for heavy metals and polycyclic aromatic hydrocarbons in sediments. Data was compared to the United States effects range low values and Italian standards due to no European or Regional standards being available. Only minimal polycyclic aromatic hydrocarbons were observed and mainly in 2017 with all being below the referenced standards. The majority of the nickel, lead, cadmium, chromium, and copper sediment concentrations exceeding the United States and Italian standards. The December 2019 GES Report stated Cyprus is in GES regarding metals in sediment due to the 2013 to 2016 data presented being within the targets (see Section 5.6.2) established. Sub program MALCY-08-02 is conducted yearly i |
El descriptor 8. Contaminación se evaluará mediante una estrategia de seguimiento con los siguientes objetivos:
•Proporcionar datos que permitan la evaluación del estado ambiental de la Demarcación Marina en comparación con el BEA, definido por la concentración de contaminantes que se encuentren ...
|
Le programme de surveillance « Contaminants » définit la surveillance nécessaire à l'évaluation permanente de l'état écologique des eaux marines et à la mise à jour périodique des objectifs environnementaux (OE) au titre du descripteur 8 « Contaminants ». Ce programme a pour objectif d'acquérir d...
|
Monitoring of contaminants, selected in accordance with the Directive 2000/60/EC, within coastal and territorial waters. Contaminant monitoring data provides an overview of chemical status of water bodies within coastal and territorial waters, as well as information on spatial and temporal changes, impacts and pressures. Monitoring strategy's main objectives are protection and improvement of quality of water bodies. Monitoring data will be used for the assessment of measures set to improve quality of water bodies, as well as development of policies to achieve and maintain good environmental status in marine waters, habitats and resources. |
La concentrazione di inquinanti nell’ambiente marino e i loro effetti vengono valutati tenendo in considerazione le disposizioni della Direttiva 2008/56/CE, così come richiesto dalla nuova Decisione 2017/848 del maggio 2017, ed anche le disposizioni pertinenti la Direttiva 2000/60/CE per le acque...
|
Strategija Monitoring koncentracij onesnaževal (D8) se navezuje na deskriptor kakovosti D8 Onesnaževala, ki naslavlja pritiske in vplive človekovih dejavnosti na morske vode z vidika vnosa onesnaževal v morsko okolje. Skladno s tem strategija Monitoring koncentracij onesnaževal (D8) naslavlja spr...
|
||||||||||||||||||||||||
Coverage of GES criteria |
Adequate monitoring will be in place by 2024 |
Adequate monitoring was in place in 2014 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring was in place in 2014 |
Adequate monitoring is in place by July 2020 |
Adequate monitoring was in place in 2014 |
||||||||||||||||||||||||
Gaps and plans |
Program D8 – Full GES coverage can be further achieved by collating seawater and sediment data already provided to the Cypriot environmental authorities by oil and gas operators into a central searchable data base. This database will allow for the calculation of baseline average (± standard deviation) concentration for each naturally occurring contaminant investigated. Future concentrations sampled after anthropogenic activity (i.e. drilling) can be compared against the baseline average in order to determine potential impacts resulting from that activity. |
Criterios D8C1 (primario) y D8C2 (secundario): la cobertura de ambos criterios se pretende cubrir a través de los programas de seguimiento CONT-1 y CONT-2, que abordan concentraciones de contaminantes en sedimento y biota, así como efectos de los contaminantes en ciertas especies, tanto en aguas ...
|
Principales perspectives du programme de surveillance « Contaminants » : - Conserver les dispositifs de surveillance opérationnels permettant l'acquisition de données de concentrations en contaminants chimiques dans le biote et les sédiments au niveau des zones côtières. - Poursuivre les réflexio...
|
D8C1: Selection of core set of contaminants, monitoring frequency and best matrices for monitoring. Thresholds and quantitative criteria for contaminant levels in sediments.
Selection of contaminants and relevant matrices for the extension of monitoring programs to open sea areas.
D8C2: Criteria and methodological standards regarding biological effects monitoring.
D8C3: An agreed definition of "significant acute pollution events" and relevant threshold values on the EU or the national level. |
T8.1 - Adequate monitoring was in place by 2014
T8.2 - Adequate monitoring is in place by July 2020 |
Presoja stanja morskega okolja je pokazala, da se v morskih vodah in na obali izvajajo številne dejavnosti, ki predstavljajo pritiske na stanje morskega okolja. Skupina ukrepov, relevantnih za deskriptor kakovosti onesnaženje morskega okolja z onesnaževali (D8), vključuje ukrepe za preprečevanje ...
|
||||||||||||||||||||||||
Related targets |
|
|
|
|
||||||||||||||||||||||||||
Coverage of targets |
Adequate monitoring was in place in 2014 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring was in place in 2014 |
Adequate monitoring is in place by July 2020 |
||||||||||||||||||||||||||
Related measures |
|
|
||||||||||||||||||||||||||||
Coverage of measures |
Adequate monitoring was in place in 2014 |
Adequate monitoring is in place by July 2020 |
||||||||||||||||||||||||||||
Related monitoring programmes |
|
|
|
|
|
|
||||||||||||||||||||||||
Programme code |
D08 |
ES-A-07_Hidrocarburos |
ES-A-21_Puertos |
ES-A-22_TransporteMaritimo |
ES-CONT-1_AguasCosteras |
ES-CONT-2_AguasAbiertas |
ES-CONT-4_ContaminacionAccidental |
ES-OA-B |
ES-PSBE-03_AporteContaminantes |
ES-PSBE-04_AporteBasuras |
FR-MWE-D8-01 |
FR-MWE-D8-02 |
FR-MWE-D8-03 |
FR-MWE-D8-04 |
FR-MWE-D8-05 |
FR-MWE-D8-06 |
MADHR-D08-06 |
MADHR-D08-07 |
MADHR-D08-08 |
MADIT-D8-01 |
MADIT-D8-02 |
MADIT-D8-03 |
MICIT-D8-01 |
MICIT-D8-02 |
MICIT-D8-03 |
MWEIT-D8-01 |
MWEIT-D8-02 |
MWEIT-D8-03 |
SI-D08-01 |
SI-D08-02 |
Programme name |
Contaminants (Cyprus contaminants monitoring programme) |
Extracción de petróleo y gas |
Infraestructuras portuarias |
Transporte marítimo |
Seguimiento contaminacion química en aguas costeras |
Seguimiento de la contaminación química marina en aguas abiertas |
Contaminación accidental |
Objetivos ambientales sobre vertidos al medio marino (B) |
Aporte de otras sustancias |
Aporte de basuras |
Contaminants chimiques dans les organismes marins |
Contaminants chimiques dans le milieu |
Effets des contaminants chez les organismes marins |
Apports fluviaux de contaminants |
Episodes de pollutions aiguës |
Partie activités, usages et politiques publiques |
Contaminant levels - in water/sediment |
Contaminant inputs - sea-based acute events, incl. oil spills |
Contaminant levels - in water/sediment |
Monitoraggio dei contaminanti chimici nei sedimenti – Adriatico |
Contaminanti chimici nel biota - Adriatico |
Effetti dei contaminanti chimici nel biota - Adriatico |
Monitoraggio dei contaminanti chimici nei sedimenti – Ionio |
Contaminanti chimici nel biota - Ionio |
Effetti dei contaminanti chimici nel biota - Ionio |
Monitoraggio dei contaminanti chimici nei sedimenti – Tirreno |
Contaminanti chimici nel biota - Tirreno |
Effetti dei contaminanti chimici nel biota - Tirreno |
Monitoring koncentracij onesnaževal |
Monitoring znatnega akutnega onesnaženja |
Update type |
Same programme as in 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
New programme |
Modified from 2014 |
New programme |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
Modified from 2014 |
New programme |
Same programme as in 2014 |
Same programme as in 2014 |
Modified from 2014 |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
New programme |
Modified from 2014 |
New programme |
Old programme codes |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||||||||||||||||
Programme description |
The Cyprus contaminants monitoring programme focuses on a pressure, contaminants, and evaluates their concentration in sediments and biota, as well as the frequency and magnitude of contaminant release through spills and illegal discharges. These components of the programme were decided jointly with other Mediterranean EU member-states . The programme capitalizes on the existing monitoring programme in the framework of MedPOL (UNEP/MAP) already measuring contaminants in biota, as well as sampling methodologies in the framework of WFD. This programme addresses in whole or in part the relevant indicators of Ecological Objective 09 adopted by the Contracting Parties of UNEP/MAP (2013).
Three sub-programmes are running under this programme :
1. Contaminants in sediments (MALCY-D08-01),
2. Contaminants in biota (MALCY-D08-02),
3. Spills and illegal discharges (MALCY-D08-03)
DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the offshore oil and gas lease areas. Per these requirements, sediment samples are taken to assess the chemical constituents including hydrocarbons, nutrients, metals, and radioactive compounds in the sediments within the lease areas during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). |
The extraction of oil and gas from the seabed is assessed, as well as the infrastructure needed both for the extraction, temporary storage of gas and for transport to land in order to assess the occupation of the seabed. Account is also taken of the various permits that may exist for exploration ...
|
An analysis is carried out of the main characteristics of ports with freight or passenger traffic as the main transport infrastructure with a direct link to the marine environment, both those managed by the State, through the port authorities, and those managed by the Autonomous Communities. The changes are identified and the gain or loss on land at sea is quantified.
|
Se evalúa la intensidad del transporte marítimo que tiene como origen o destino un puerto de las aguas marinas españolas y aquel que únicamente utiliza las aguas españolas para navegar por ellas. Asimismo, se consideran otras formas de navegación que no pueden ser estrictamente consideradas como ...
|
The CONT-1 programme focuses on monitoring pollution and its potential biological effects in the coastal marine area (up to 1 mile from the baseline). This area is the area most exposed to direct or diffuse pollution of terrestrial origin and therefore the most vulnerable.
The data generated thr...
|
The CONT-2 programme focuses on monitoring pollution and its potential biological effects on the deepest marine area (beyond the first mile from the baseline). This area is the least exposed area to direct pollution and is spatially complementary to the CONT-1 programme.
The data generated throu...
|
Accidental pollution may come from sources as diverse as incidents/accidents on ships, oil exploration and exploitation activities, port activities primarily loading and discharging oil or other polluting substances) or industrial activities carried out near the coast. Given the serious consequen...
|
Mediante la Resolución de 11 de junio de 2019 de la Secretaría de Estado de Medio Ambiente, se publicó el Acuerdo del Consejo de Ministros de 7 de junio de 2019, por el que se aprueban los objetivos ambientales del segundo ciclo de las estrategias marinas españolas. Estos objetivos ambientales se...
|
Se evalúa la variación espacio-temporal de los aportes de contaminantes, intencionada, al medio marino:
- De origen terrestre: ríos, vertidos directos desde tierra
- De origen marino: buques, plataformas, vertidos de material dragado, vertidos piscícolas.
- De origen aéreo: deposición atmosférica...
|
Se tratará de evaluar el aporte de basuras al medio marino teniendo en cuenta los siguientes aspectos:
• la presencia de macrobasuras en playas,
• los residuos recogidos en las instalaciones de recepción portuarias de los puertos de interés general, considerando las cantidades recogidas como cantidades de basuras que se ha evitado que lleguen al medio marino.
|
Les contaminants chimiques comme les métaux lourds ou les composés organochlorés s'accumulent dans les organismes vivants et peuvent se bioaccumuler le long de la chaîne alimentaire. Ainsi, les niveaux de concentrations en contaminants analysés dans le biote permettent de caractériser l'état de c...
|
Ce sous-programme complète la surveillance mise en œuvre dans le cadre du sous-programme 1 (Contaminants chimiques dans les organismes marins) en permettant l'acquisition de données sur la contamination dans le milieu. Les contaminants chimiques peuvent être transportés de différentes manières da...
|
La contamination chimique peut avoir des effets négatifs sur les organismes vivants, aussi bien au cours de leur développement que dans leurs fonctions physiologiques (e.g. reproduction, métabolisme). La sensibilité de certains organismes (e.g. nucelles) à des contaminants chimiques (e.g. tributy...
|
L'objectif de ce sous-programme est de caractériser les apports en contaminants chimiques des fleuves afin de mesurer les pressions auxquelles sont soumises les eaux côtières. Les apports fluviaux en contaminants dans les eaux côtières sont estimés à partir de méthodes de calculs couplant : (1) d...
|
L'objectif de ce sous-programme est de suivre les pollutions aiguës dues à des substances polluantes, notamment les hydrocarbures, et leurs effets néfastes sur la santé des espèces et l'état des habitats. La stratégie de surveillance de ce sous-programme pour le suivi des pollutions aiguës, ou po...
|
En France, la DCSMM est mise en œuvre conjointement avec la directive 2014/89/UE (établissant un cadre pour la planification de l'espace maritime) à travers les documents stratégiques de façade. Dans cette démarche, le document stratégique de façade contribue à améliorer la prise en compte récipr...
|
An on-going monitoring program for the assessment of the environmental status in Croatian coastal and territorial waters has been carried out in accordance to the requirements of the MSFD (2008/56/EZ) and WFD (2000/60/EC). The criteria proposed by the EU Commission decision (EU) 2017/848, has been applied for the assessment of environmental status in regard to Descriptor 8. Assessment of adverse effects of contaminants on species populations and biological communities has been based on monitoring of biological effects of contaminants on selected marine organisms (D8C2). |
There is not yet an agreed definition of "significant acute pollution events" on the EU or the national level. The elements for assessment are significant acute pollution events involving polluting substances, including crude oil and similar compounds. The spatial extent and duration of such events needs to be monitored. No threshold values have been set for the criteria D8C3 therefore, the criteria is not applied for the assessment of the status of the environment. |
An on-going monitoring program for the assessment of the environmental status in Croatian coastal and territorial waters has been carried out in accordance to the requirements of the MSFD (2008/56/EZ) and WFD (2000/60/EC). The criteria proposed by the EU Commission decision (EU) 2017/848, has been applied for the assessment of environmental status in regard to Descriptor 8. The concentrations of priority (hazardous) substances, specific pollutants and certain additional contaminants, for which the environmental quality standard is defined by the Directive 2008/105/EC, were monitored within coastal and territorial waters in relevant matrices (water, sediment and biota) (D8C1). The obtained results were compared to the set EQS values and the one-out-all-out principle was applied for determination of the status of the environment. |
L’obiettivo del programma è quello di verificare il raggiungimento del Target 8.1 e del GES 8.1 acquisendo i dati necessari a valutare gli elementi associati al criterio D8C1 (concentrazione dei contaminanti) primario della Decisione UE 2017/848. Il programma è finalizzato anche all’acquisizione ...
|
L’obiettivo del programma è quello di verificare il raggiungimento del Target 8.1 e del GES 8.1 acquisendo i dati necessari a valutare gli elementi associati al criterio D8C1 (concentrazione dei contaminanti) primario della Decisione UE 2017/848. Il programma è finalizzato anche all’acquisizione ...
|
L’obiettivo del programma è quello di verificare il raggiungimento del Target 8.2 (“Sono ridotte le lacune conoscitive sulla valutazione degli effetti biologici dovuti alla contaminazione chimica”) e del GES 8.2 (“Per ciascuna delle categorie di contaminanti regolamentate dalla legislazione perti...
|
L’obiettivo del programma è quello di verificare il raggiungimento del Target 8.1 e del GES 8.1 acquisendo i dati necessari a valutare gli elementi associati al criterio D8C1 (concentrazione dei contaminanti) primario della Decisione UE 2017/848. Il programma è finalizzato anche all’acquisizione ...
|
L’obiettivo del programma è quello di verificare il raggiungimento del Target 8.1 e del GES 8.1 acquisendo i dati necessari a valutare gli elementi associati al criterio D8C1 (concentrazione dei contaminanti) primario della Decisione UE 2017/848. Il programma è finalizzato anche all’acquisizione ...
|
L’obiettivo del programma è quello di verificare il raggiungimento del Target 8.2 (“Sono ridotte le lacune conoscitive sulla valutazione degli effetti biologici dovuti alla contaminazione chimica”) e del GES 8.2 (“Per ciascuna delle categorie di contaminanti regolamentate dalla legislazione perti...
|
L’obiettivo del programma è quello di verificare il raggiungimento del Target 8.1 e del GES 8.1 acquisendo i dati necessari a valutare gli elementi associati al criterio D8C1 (concentrazione dei contaminanti) primario della Decisione UE 2017/848. Il programma è finalizzato anche all’acquisizione ...
|
L’obiettivo del programma è quello di verificare il raggiungimento del Target 8.1 e del GES 8.1 acquisendo i dati necessari a valutare gli elementi associati al criterio D8C1 (concentrazione dei contaminanti) primario della Decisione UE 2017/848. Il programma è finalizzato anche all’acquisizione ...
|
L’obiettivo del programma è quello di verificare il raggiungimento del Target 8.2 (“Sono ridotte le lacune conoscitive sulla valutazione degli effetti biologici dovuti alla contaminazione chimica”) e del GES 8.2 (“Per ciascuna delle categorie di contaminanti regolamentate dalla legislazione perti...
|
Program Monitoring koncentracij onesnaževal se nanaša na spremljanje koncentracij onesnaževal v vodi, sedimentu in bioti – spremljanje stopnje pritiska v morskem okolju (angl. level of pressure in marine environment), posredno pa tudi na spremljanje vnosa onesnaževal iz zaledja, zraka ali dejavno...
|
Program Monitoring znatnega akutnega onesnaženja se nanaša na spremljanje pojava znatnih akutnih onesnaženj – spremljanje stopnje pritiska pri viru (angl. level of pressure at source). S programom Monitoring znatnega akutnega onesnaženja se zagotavlja tudi spremljanje učinkovitosti ukrepov v Načr...
|
Monitoring purpose |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Other policies and conventions |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||||||
Regional cooperation - coordinating body |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||||||||||||
Regional cooperation - countries involved |
||||||||||||||||||||||||||||||
Regional cooperation - implementation level |
Common monitoring strategy |
Coordinated data collection |
Coordinated data collection |
Common monitoring strategy |
Coordinated data collection |
Common monitoring strategy |
Joint data collection |
Joint data collection |
Joint data collection |
Agreed data collection methods |
Common monitoring strategy |
|||||||||||||||||||
Monitoring details |
⢠and annually for mussel pollution. 24
|
The sampling frequency will depend on the type of indicator to be analysed:
⢠annually or every two years for fish contamination
|
Elemento monitorato: D8C1 - All chemical characteristics e Concentration in sediment (total)
|
Elemento monitorato: D8C1 - All chemical characteristics, Concentration in biota (total), concentration in biota-muscle
|
Elemento monitorato: D8C2 - All chemical characteristics
Parametro monitorato: D8C2 - Other
|
Elemento monitorato: D8C1 - All chemical characteristics e Concentration in sediment (total)
|
Elemento monitorato: D8C1 - All chemical characteristics, Concentration in biota (total), concentration in biota-muscle
|
Elemento monitorato: D8C2 - All chemical characteristics
Parametro monitorato: D8C2 - Other |
Elemento monitorato: D8C1 - All chemical characteristics e Concentration in sediment (total) |
Elemento monitorato: D8C1 - All chemical characteristics, Concentration in biota (total), concentration in biota-muscle
|
Elemento monitorato: D8C2 - All chemical characteristics
Parametro monitorato: D8C2 - Other
|
Skladno s Sklepom Komisije (EU) 2017/848 se program Monitoring koncentracij onesnaževal nanaša na element meril Onesnaževala in merilo Koncentracije onesnaževal (D8C1). V okviru programa se spremlja pripadajoče elemente in parametre, ki predeljujejo stopnjo pritiska v morskem okolju in posredno tudi stopnjo pritiska pri viru.
|
Na podlagi določb ODMS in Sklepa Komisije (EU) 2017/848 se monitoring znatnih akutnih onesnaženj in z njimi povezanih onesnaževalnih snovi izvaja skladno z Direktivo Evropskega parlamenta in Sveta 2005/35/ES z dne 7. septembra 2005 o onesnaževanju morja z ladij in uvedbi kazni za kršitve.
|
|||||||||||||||||
Input or spread of non-indigenous species |
|
|||||||||||||||||||||||||||||
Disturbance of species (e.g. where they breed, rest and feed) due to human presence |
|
|
||||||||||||||||||||||||||||
Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) – diffuse sources, point sources, atmospheric deposition, acute events |
|
|
|
|
||||||||||||||||||||||||||
Input of litter (solid waste matter, including micro-sized litter) |
||||||||||||||||||||||||||||||
Eutrophication |
||||||||||||||||||||||||||||||
Contaminants - non UPBT substances |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|||||||||||||||
Contaminants - UPBT substances |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
||||||||||||||
Acute pollution events |
|
|
|
|||||||||||||||||||||||||||
Litter in the environment |
||||||||||||||||||||||||||||||
Micro-litter in the environment |
||||||||||||||||||||||||||||||
Litter and micro-litter in species |
||||||||||||||||||||||||||||||
Impulsive sound in water |
||||||||||||||||||||||||||||||
Continuous low frequency sound |
||||||||||||||||||||||||||||||
Extraction of oil and gas, including infrastructure |
||||||||||||||||||||||||||||||
Transport infrastructure |
||||||||||||||||||||||||||||||
Transport – shipping |
||||||||||||||||||||||||||||||
Adverse effects on species or habitats |
|
|
|
|
||||||||||||||||||||||||||
Spatial scope |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Marine reporting units |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Temporal scope (start date - end date) |
2016-9999 |
2014-9999 |
2014-9999 |
2014-9999 |
1991-9999 |
2006-9999 |
2013-9999 |
2020-2026 |
2011-9999 |
2020-9999 |
1974-9999 |
1993-9999 |
2009-9999 |
1971-9999 |
2000-9999 |
2021-9999 |
2021-2026 |
2021-2026 |
2021-2026 |
2021-2026 |
2021-2026 |
2021-2026 |
2021-2026 |
2021-2026 |
2021-2026 |
2021-2026 |
2021-2026 |
2021-2026 |
1999-9999 |
1977-9999 |
Monitoring frequency |
Yearly |
6-yearly |
6-yearly |
6-yearly |
Other |
Other |
As needed |
6-yearly |
6-yearly |
6-yearly |
3-yearly |
6-yearly |
Other |
Monthly |
Continually |
As needed |
Other |
As needed |
Other |
3-yearly |
Yearly |
3-yearly |
3-yearly |
Yearly |
3-yearly |
3-yearly |
Yearly |
3-yearly |
As needed |
As needed |
Monitoring type |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Monitoring method |
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
|
Monitoring method other |
The monitoring methods are described in Law et al. (2010). See also the DFMR has implemented Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
Se recopila y analiza la información publicada sobre las cantidades de hidrocarburos extraídos o inyectados, controladas en el marco de la política energética nacional y puesta a disposición del público a través de diferentes páginas web (www.cores.es, www.enagas.es). |
Se analiza la información generada por las distintas autoridades responsables en el marco de sus competencias, esto es: Puertos del Estado y las autoridades portuarias facilitan información relativa a las modificaciones de los puertos que conlleven la creación/modificación de infraestructuras portuarias o que den lugar a nuevas áreas del fondo marino selladas. En cuanto a las modificaciones de puertos autonómicos, estas se identifican haciendo uso de la comparativa de fotografías aéreas en distintos años procedentes del Plan Nacional de Ortofotografía Aérea. Para realizar este análisis se utilizan herramientas GIS. |
El análisis de la densidad de tráfico marítimo se realiza mediante el procesado de datos AIS facilitados por SASEMAR. Los datos de intensidad de tráfico marítimo en dispositivos de separación de tráfico marítimo los publica SASEMAR mientras que la información relativa a los puertos de interés general la publica Puertos del Estado. |
Salvamento Marítimo (SASEMAR, Dirección General de la Marina Mercante) registra información de las incidencias relativas a posibles episodios de contaminación en el mar, a través de su programa de vigilancia aérea y satelital y su sistema de información de emergencias, que alimenta la base de datos de la Agencia Europea de Seguridad Marítima (EMSA). Desde 2019, SASEMAR también alimenta el informe
anual de Vigilancia Aérea que publica el Acuerdo de Bonn, suministrando las contaminaciones registradas en la Zona del Golfo de Vizcaya incluida en el acuerdo.
En el marco de este programa de seguimiento se llevará a cabo un análisis de la información facilitada por Salvamento Marítimo, que previsiblemente incluirá la fecha y coordenadas geográficas del punto del accidente, el origen del vertido, así como su extensión y volumen.
De la base de datos de los posibles incidentes de contaminación en el medio marino, se seleccionarán aquellos episodios que hayan dado lugar a manchas contaminantes con una superficie mayor de 1 km2
y con origen conocido.
Esto permitirá descartar su acumulación o reiteración en determinadas zonas. En caso de que durante la vigencia de este programa de seguimiento se alcanzara algún consenso a nivel regional o europeo sobre la definición de evento significativo de contaminación aguda, este programa se adaptaría y se comenzarían a aplicar los términos
acordados.
Para los casos en que se produzca un episodio de contaminación aguda, el MITERD tiene previsto publicar una Guía de actuación ante fauna petroleada, en coordinación con las CCAA, en la cual se basará el seguimiento de los efectos adversos de estos episodios sobre especies marinas. |
Se recopilará la información entre las unidades administrativas competentes en cada uno de los indicadores asociadas a los objetivos. |
Para las demarcaciones noratlántica y sudatlántica, pertenecientes al Convenio OSPAR, la información de entradas de contaminantes (cadmio, mercurio, cobre, plomo, zinc, γ-hexaclorociclohexano y bifenilos policlorados) al mar por vertidos directos y aportes desde ríos se produce y compila siguiendo las instrucciones del Programa RID de OSPAR (OSPAR CEMP guidelines for coordinated monitoring for eutrophication, CAMP and RID (Agreement 2016-05), Revised in 2018).
Para el resto de demarcaciones y/o sustancias:
- los vertidos desde tierra y procedentes de la acuicultura se caracterizan en base a la información ofrecida por el Registro Estatal de Emisiones y Fuentes Contaminantes (Registro PRTR). No todas las instalaciones que realizan vertidos al mar están obligados a enviar información a este Registro, sino sólo aquellas que superan los umbrales que se especifican en el Real Decreto 508/2007, por el que se regula el suministro de información sobre emisiones del Reglamento E-PRTR y de las autorizaciones ambientales integradas, y sus modificaciones posteriores. La información que se ofrece no es, por tanto, exhaustiva, sino que tiene en cuenta las instalaciones más grandes. De este Registro, se seleccionan aquellos complejos que vierten al litoral, y se le asocian las cargas de contaminantes de las que han informado en el periodo de estudio. La definición de litoral es entendida en el mismo en sentido amplio, incluyendo también el dominio público marítimo-terrestre al que dan lugar las aguas de transición.
- Los aportes desde ríos se analizan con información facilitada por la Dirección General del Agua o las Comunidades Autónomas que recopila información sobre el volumen de vertido y las cargas totales aportadas de las siguientes sustancias: cadmio, mercurio, cobre, plomo, zinc, alfa-hexaclorociclohexano y bifenilos policlorados.
La información sobre los vertidos directos de radionucleidos la publica anualmente el Consejo de Seguridad Nuclear.
Las cargas vertidas al mar del material dragado las proporcionan los puertos y se notifica a los Convenios de OSPAR y Barcelona.
Para evaluar las deposiciones atmosféricas se emplean los datos del programa EMEP (Programa Concertado de Vigilancia y Evaluación del Transporte a Larga Distancia de los Contaminantes Atmosféricos en Europa). Este modela la deposición en el océano desde la atmósfera de algunos metales pesados: cadmio, mercurio y plomo. |
Respecto a las macrobasuras en playas, se utilizan los datos estacionales de basuras marinas de un transecto de 100 m procedentes del programa de seguimiento BM1. Se consideran los resultados considerando el “top X” (objetos más frecuentes) de las tipologías de objetos, entendido como el que representa el 80% de los objetos encontrados.
En el establecimiento de los orígenes de las macrobasuras en playas según los objetos más frecuentes (top X) se ha seguido lo indicado por el Convenio OSPAR, que, a través de su Grupo de Trabajo de Basuras Marinas (ICG-ML), tiene establecida una metodología consistente en la asignación de cada tipo de basura de los contemplados en el muestreo a cada uno de los 5 siguientes grupos de orígenes: pesca, transporte marítimo, turismo, instalaciones sanitarias y otros. En esta última categoría se incluyen aquellos objetos cuyo origen no pueda ser asignado a alguna de las anteriores categorías o aquellos que puedan corresponderse con más de una fuente. Además, se han redefinido las categorías establecidas por OSPAR para adecuarlas a las actividades listadas en el Cuadro 2b del Anexo III de la DMEM.
Los datos de basuras recogidas y del tráfico de buques en los puertos de interés general proceden de Puertos del Estado. |
Ce sous-programme repose sur des dispositifs de collecte (e.g. base de données, règlement, contrôle, étude d'impact, enquête, infrastructure de données...) permettant de fournir régulièrement un ou des jeux de données relatifs aux activités, aux usages ou aux politiques publiques. Les dispositifs de collecte utilisés fournissent des données sur les "Opérations de dragage par les ports maritimes ", la "Localisation et type des ports", la "Liste et localisation des ports de plaisance certifiés Ports Propres", les "zonages pluviaux annexés aux Plans Locaux d'Urbanisme", l' "état chimique des masses d'eau au titre de la Directive-cadre sur l'eau", et les "aires de carénage dans les ports de plaisance, zones de mouillages et chantiers nautiques privés". |
The contaminant effects being monitored: Acetylcholinesterase activity in mussels, Lysosomal membrane stability in mussels, Metallothioneins concentration in mussels, Stress on stress in mussels
DNA integrity - effect of genotoxic compounds, Neutral lipids - effect of organic pollutants, Water toxicity (Microtox®) and Sediment toxicity (Microtox®). The species used for the assessment of adverse effects of contaminants is Mytilus galloprovincialis. The tissues assessed include digestive gland, gills and the whole organism. Sediment and water toxicity is evaluated by an in vitro testing system using the bacterial strain Vibrio Fischeri.
Threshold values for adverse effects (including cumulative and synergistic effects) on the health of species and the condition of habitats, are set on the national level. |
Vessel Traffic Monitoring and Information System is going to collect all the necessary information on maritime traffic through different sensors, thus making possible to process, analyze, display in real time, store and replay all collected data, to share and distribute such information to the competent national and international authorities and institutions.
In the case of oil pollution accident the following indicators of the effects of pollution could be measured:
- Genotoxicity and toxicity of water samples
- Biological effects in mussels (“Mussel Watch” if necessary) |
Sampling procedure has been described in Marasovic I., Krstulovic, N., Leder, N., Loncar, G., Precali, R., Šolic, M., Loncar,.G., Beg- Paklar, G., Bojanic, N., Cvitkovic, I., Dadic, V., Despalatovic, M., Dulcic, J., Grbec, B., Kušpilic, G., Nincevic-Gladan, Ž., P. Tutman, Ujevic, I., Vrgoc, N., Vukadin, P., Žuljevic, A. Coastal cities water pollution control project, Part C1: Monitoring and Observation System for Ongoing Assessment of the Adriatic sea under the Adriatic sea Monitoring Programme, Phase II. Interim report (IR), December, 2013. (Ftp://baltazar.izor.hr) |
http://groupware.sinanet.isprambiente.it/strategia-marina/library/programmi-monitoraggio-ii-ciclo-2021-2026-21.05.2020/d8_nuovi_programmi_monitoraggio_2021-2026_21.05.2020 |
http://groupware.sinanet.isprambiente.it/strategia-marina/library/programmi-monitoraggio-ii-ciclo-2021-2026-21.05.2020/d8_nuovi_programmi_monitoraggio_2021-2026_21.05.2020 |
http://groupware.sinanet.isprambiente.it/strategia-marina/library/programmi-monitoraggio-ii-ciclo-2021-2026-21.05.2020/d8_nuovi_programmi_monitoraggio_2021-2026_21.05.2020 |
http://groupware.sinanet.isprambiente.it/strategia-marina/library/programmi-monitoraggio-ii-ciclo-2021-2026-21.05.2020/d8_nuovi_programmi_monitoraggio_2021-2026_21.05.2020 |
http://groupware.sinanet.isprambiente.it/strategia-marina/library/programmi-monitoraggio-ii-ciclo-2021-2026-21.05.2020/d8_nuovi_programmi_monitoraggio_2021-2026_21.05.2020 |
http://groupware.sinanet.isprambiente.it/strategia-marina/library/programmi-monitoraggio-ii-ciclo-2021-2026-21.05.2020/d8_nuovi_programmi_monitoraggio_2021-2026_21.05.2020 |
http://groupware.sinanet.isprambiente.it/strategia-marina/library/programmi-monitoraggio-ii-ciclo-2021-2026-21.05.2020/d8_nuovi_programmi_monitoraggio_2021-2026_21.05.2020 |
http://groupware.sinanet.isprambiente.it/strategia-marina/library/programmi-monitoraggio-ii-ciclo-2021-2026-21.05.2020/d8_nuovi_programmi_monitoraggio_2021-2026_21.05.2020 |
http://groupware.sinanet.isprambiente.it/strategia-marina/library/programmi-monitoraggio-ii-ciclo-2021-2026-21.05.2020/d8_nuovi_programmi_monitoraggio_2021-2026_21.05.2020 |
Program Monitoring koncentracij onesnaževal je del spremljanja kemijskega stanja površinskih voda, ki predstavlja obremenjenost površinskih voda s prednostnimi in prednostnimi nevarnimi snovmi, za katere so za Evropsko unijo (EU) postavljeni enotni okoljski standardi kakovosti, ter spremljanja ekološkega stanja površinskih voda, v okviru česar se spremljajo posebna onesnaževala, skladno z ODV. Meritve parametrov kemijskega stanja v vodi se izvajajo s pogostostjo enkrat mesečno 1x v obdobju NUV. Meritve parametrov kemijskega stanja v organizmih se izvajajo s pogostostjo vsaj na tri leta oz. glede na nacionalne strokovne podlage. Za spremljanje kemijskega stanja površinskih voda je na ravni EU 45 snovi ali skupin snovi zaradi njihove razširjene uporabe in zaradi ugotovljenih povišanih vsebnosti v površinskih vodah določenih kot prednostnih; enaindvajset od teh snovi je zaradi visoke obstojnosti, bioakumulacije in strupenosti določenih kot prednostnih nevarnih. Nekaj snovi je opredeljenih kot drugo onesnaževalo in tudi za te snovi so opredeljeni enotni EU okoljski standardi kakovosti, države članice pa morajo izvajati ukrepe z namenom, da dosežejo dobro kemijsko stanje. Na osnovi njihove najpogostejše uporabe se prednostne snovi delijo na fitofarmacevtska sredstva, biocide, ter na preostale nevarne snovi. Med slednje spadajo topila, tehnične kemikalije, ftalat ali DEHP, težke kovine, poliaromatski ogljikovodiki in dioksini. V monitoring so lahko vključena tista posebna onesnaževala (med njimi sintetična, nesintetična in druga posebna onesnaževala), ki se odvajajo v vodna telesa v pomembnih količinah, pri čemer je bil kriterij za pomembne količine oblikovan na podlagi Uredbe o emisiji snovi in toplote pri odvajanju odpadnih vod v vode in javno kanalizacijo (Ur. l. RS, št. 64/12, 64/14 in 98/15). Meritve posebnih onesnaževal v vodi se izvajajo s pogostostjo 4x letno, in sicer 1x v obdobju NUV. Metode vzorčenja vode za analize posebnih onesnaževal potekajo po enakih standardih, kot za spremljanje onesnaževal v okviru kemijskega stanja. |
Program Monitoring znatnega akutnega onesnaženja je del beleženja incidentnih onesnaženj na morju, ki se izvaja v okviru Nacionalnega programa varstva pred naravnimi in drugimi nesrečami, ki se izvaja na podlagi Resolucije o nacionalnem programu varstva pred naravnimi in drugimi nesrečami v letih od 2016 do 2022 (Uradni list RS, št. 75/16). V okviru programa se beležijo podatki o številu javljenih dogodkov na vodnih in priobalnih zemljiščih morja.
Podatki o številu zabeleženih javljenih onesnaženj na morju v Sloveniji se nahajajo na povezavi: http://kazalci.arso.gov.si/sl/content/onesnazevanje-z-ladij. |
|||||||
Quality control |
UNEP/MAP-IAEA PROFICIENCY TESTS AND INTERNAL QUALITY CONTROL |
Other quality checks: That applied by the competent authorities in the execution of the activity.
|
Other quality checks: That applied by the competent authorities in the execution of the activity.
|
Otros controles de calidad: El aplicado por la autoridad competente en la ejecución de la actividad o por la autoridad ejecutora durante el análisis de los datos.
|
⢠QUASIME-Quality Assurance of Information for Marine Environmental Monitoring in Europe
⢠BEQUALM Biological Effects Quality Assurance in Monitoring Programmes
⢠IAEA International Atomic Energy Agency intercomparison exercises
⢠UNEP/MED POL Biological Effects intercomparison exercises
...
|
⢠QUASIME-Quality Assurance of Information for Marine Environmental Monitoring in Europe
⢠BEQUALM Biological Effects Quality Assurance in Monitoring Programmes
⢠IAEA International Atomic Energy Agency intercomparison exercises
⢠UNEP/MED POL Biological Effects intercomparison exercises
...
|
That applied by the competent authority in the execution of the activity
|
Internal controls will be implemented to review documentation by the Responsible Authority (MITERD, through the Subdirectorate-General for the Protection of the Sea).
|
Other quality checks: That applied by the competent authority in the execution of the activity.
|
Other quality checks: That applied by the competent authority in the execution of the activity.
|
Prélèvements et acquisition des données dans le biote suivant les guides méthodologiques de surveillance issus de la convention de Barcelone. Bancarisation dans Quadrige : protocoles de validation et qualification des données.
|
Prélèvement et analyses des sédiments suivant les lignes directrices de la surveillance des contaminants dans les sédiments (Ospar, Accord 2002-16, révision 2018; et guides méthodologiques de surveillance issus de la convention de Barcelone). Bancarisation dans Quadrige : protocoles de validation et qualification des données.
|
Ce sous-programme de surveillance permet de suivre le potentiel toxique des sédimetns via la mise en œuvre du dispositif Remtox. Le dispositif Remtox repose sur un test analytique normalisé Afnor (AFNOR XP-T-90-382).
|
Les données sont contrôlées selon la méthode OSPAR (voir OSP-029) et les protocoles mis en œuvre dans le cadre de la directive cadre sur l'eau.
|
Pour chaque pollution constatée (par avion, bateau, ou imagerie satellite), les Centres régionaux opérationnels de surveillance et de sauvetage (CROSS) rédigent un rapport appelé POLREP. Ce rapport POLREP permet de connaitre la date, la position et l'étendue de la pollution, la force et la direct...
|
La méthodologie et le contrôle qualité est en cours de stabilisation pour ce nouveau sous-programme dédié aux suivis des activités, usages et politiques publiques des espaces maritimes et littoraux (données administratives). À terme, ce sous-programme a pour ambition d'intégrer des dispositifs ré...
|
Monitoring frequency:
Biota: 1 time per year
Sea water: 4 times per year
Sediment: 1 time per year
Laboratories are required to use validated methods. |
Laboratories are required to use validated methods. |
Monitoring frequency:
Coastal waters: Sea water (4 times per year every second year); Sediment (1 time in two years); Biota - shellfish (1 time per year); Biota - fish (1 time in two years)
Offshore waters: Sea water (3 times per year); Sediment (1 time per year); Biota - fish (1 time per year)
Laboratories are required to use validated methods. |
I dati di monitoraggio sono raccolti secondo standard informativi elaborati e condivisi con i soggetti attuatori che definiscono le informazioni da trasmettere in termini di formato (testo, numerico, data,…), valori ammissibili secondo liste predefinite (liste di contaminanti, specie, habitat, et...
|
I dati di monitoraggio sono raccolti secondo standard informativi elaborati e condivisi con i soggetti attuatori che definiscono le informazioni da trasmettere in termini di formato (testo, numerico, data,…), valori ammissibili secondo liste predefinite (liste di contaminanti, specie, habitat, et...
|
I dati di monitoraggio sono raccolti secondo standard informativi elaborati e condivisi con i soggetti attuatori che definiscono le informazioni da trasmettere in termini di formato (testo, numerico, data,…), valori ammissibili secondo liste predefinite (liste di contaminanti, specie, habitat, et...
|
I dati di monitoraggio sono raccolti secondo standard informativi elaborati e condivisi con i soggetti attuatori che definiscono le informazioni da trasmettere in termini di formato (testo, numerico, data,…), valori ammissibili secondo liste predefinite (liste di contaminanti, specie, habitat, et...
|
I dati di monitoraggio sono raccolti secondo standard informativi elaborati e condivisi con i soggetti attuatori che definiscono le informazioni da trasmettere in termini di formato (testo, numerico, data,…), valori ammissibili secondo liste predefinite (liste di contaminanti, specie, habitat, et...
|
I dati di monitoraggio sono raccolti secondo standard informativi elaborati e condivisi con i soggetti attuatori che definiscono le informazioni da trasmettere in termini di formato (testo, numerico, data,…), valori ammissibili secondo liste predefinite (liste di contaminanti, specie, habitat, et...
|
I dati di monitoraggio sono raccolti secondo standard informativi elaborati e condivisi con i soggetti attuatori che definiscono le informazioni da trasmettere in termini di formato (testo, numerico, data,…), valori ammissibili secondo liste predefinite (liste di contaminanti, specie, habitat, et...
|
I dati di monitoraggio sono raccolti secondo standard informativi elaborati e condivisi con i soggetti attuatori che definiscono le informazioni da trasmettere in termini di formato (testo, numerico, data,…), valori ammissibili secondo liste predefinite (liste di contaminanti, specie, habitat, et...
|
I dati di monitoraggio sono raccolti secondo standard informativi elaborati e condivisi con i soggetti attuatori che definiscono le informazioni da trasmettere in termini di formato (testo, numerico, data,…), valori ammissibili secondo liste predefinite (liste di contaminanti, specie, habitat, et...
|
Za analize vzorcev vode, sedimenta in živih organizmov se uporabljajo standardizirane analizne metode, ki so validirane in dokumentirane v skladu s standardom ISO/IEC 17025 in ustrezajo minimalnim izvedbenim merilom za analizne metode, definiranim v 16. členu Pravilnika o monitoringu stanja površinskih voda.
|
Podatek ni na voljo.
|
Data management |
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
|
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
|
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
|
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
|
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
|
Afin de référencer les dispositifs de collecte et de surveillance, les données répertoriées dans le cadre de la DCSMM sont intégrées dans les systèmes d'information de la DCSMM (en particulier le référencement des métadonnées). Elles sont également remises à disposition (sous réserve des droits d...
|
||||||||||||||||||||||||
Data access |
||||||||||||||||||||||||||||||
Related indicator/name |
|
|
|
|
|
|
|
|
||||||||||||||||||||||
Contact |
WESSEL Nathalie |
WESSEL Nathalie |
WESSEL Nathalie |
WESSEL Nathalie |
WESSEL Nathalie |
CHEVRIER Muriel |
||||||||||||||||||||||||
References |
Law, R., Hanke, G., Angelidis, M., Batty, J., Bignert, A., Dachs, J., … Vethaak, D. (2010).Marine Strategy Framework Directive – Task Group 8 Report Contaminants and pollution effects (p. 161). Luxembourg: Office for Official Publications of the European Communities. |
Podrobnejša vsebina metodologije za spremljanje koncentracij onesnaževal v okviru spremljanja stanja za oceno kemijskega in ekološkega stanja površinskih voda po ODV je navedena v Programu monitoringa kemijskega in ekološkega stanja voda za obdobje 2016 do 2021 (Dobnikar-Tehovnik s sod., 2017) in dostopna na spletnem naslovu:
https://www.arso.gov.si/vode/poro%C4%8Dila%20in%20publikacije/Program%202016%20do%202021_SPLET_kon%C4%8Dna.pdf
Način in obseg izvajanja monitoringa površinskih voda ureja Pravilnik o monitoringu stanja površinskih voda (Uradni list RS, 10/2009, 81/2011, 73/2016):
http://pisrs.si/Pis.web/pregledPredpisa?id=PRAV9315 |