Member State report / Art11 / 2014-2020 / D2 / Latvia / Baltic Sea
Report type | Member State report to Commission |
MSFD Article | Art. 11 Monitoring programmes (and Art. 17 updates) |
Report due | 2014-10-15; 2020-10-15 |
GES Descriptor | D2 Non-indigenous species |
Member State | Latvia |
Region/subregion | Baltic Sea |
Reported by | Latvian Institute of Aquatic Ecology |
Report date | 2014-12-05; 2021-06-09 |
Report access |
2014 data
2020 data
Monitoring programme | Monitoring programme name | MP_D2 |
||||||
---|---|---|---|---|---|---|---|---|
Reference existing programme | ||||||||
Marine Unit ID | ||||||||
Q4e - Programme ID | BAL-LV-2014 |
|||||||
Q4f - Programme description | ||||||||
Q5e - Natural variability |
|
|||||||
Q5d - Adequacy for assessment of GES | Q5d - Adequate data | N |
||||||
Q5d - Established methods | N |
|||||||
Q5d - Adequate understanding of GES | N |
|||||||
Q5d - Adequate capacity | N |
|||||||
Q5f - Description of programme for GES assessment | ||||||||
Q5g - Gap-filling date for GES assessment | After2020 |
|||||||
Q5h - Plans to implement monitoring for GES assessment | ||||||||
Q6a -Relevant targets | Q6a - Environmental target | Target 1 Target 6 |
||||||
Q6a - Associated indicator | ||||||||
Q6b - Adequacy for assessment of targets | Q6b_SuitableData | N |
||||||
Q6b_EstablishedMethods | N |
|||||||
Q6d_AdequateCapacity | N |
|||||||
Q6c - Target updating | ||||||||
Q6d - Description of programme for targets assessment | ||||||||
Q6e - Gap-filling date for targets assessment | After2020 |
|||||||
Q6f - Plans to implement monitoring for targets assessment | ||||||||
Q7a - Relevant activities |
|
|||||||
Q7b - Description of monitoring of activities | ||||||||
Q7c - Relevant measures | ||||||||
Q7e - Adequacy for assessment of measures | Q7d - Adequate data | |||||||
Q7d - Established methods | ||||||||
Q7d - Adequate understanding of GES | ||||||||
Q7d - Adequate capacity | ||||||||
Q7d - Addresses activities and pressures | ||||||||
Q7d - Addresses effectiveness of measures | ||||||||
Q7d - Description of monitoring for measures | ||||||||
Q7f - Gap-filling date for activities and measures | After2020 |
|||||||
Q8a - Links to existing Monitoring Programmes |
|
|||||||
Reference sub-programme | Sub-programme ID | |||||||
Sub-programme name | Pelagic habitats - community characteristics |
Plankton blooms (biomass, frequency) |
Seabed habitats - community characteristics |
Benthic species - abundance and/or biomass |
Seabed habitats - distribution and extent |
Non-indigenous species - abundance and/or biomass |
Non-indigenous species inputs - from specific sources |
|
Q4g - Sub-programmes | Sub-programme ID | |||||||
Sub-programme name | Pelagic habitats - community characteristics |
Plankton blooms (biomass, frequency) |
Seabed habitats - community characteristics |
Benthic species - abundance and/or biomass |
Seabed habitats - distribution and extent |
Non-indigenous species - abundance and/or biomass |
Non-indigenous species inputs - from specific sources |
|
Q4k - Monitoring purpose | ||||||||
Q4l - Links of monitoring programmes of other Directives and Conventions | ||||||||
Q5c - Features | Q5c - Habitats |
|
||||||
Q5c - Species list |
|
|||||||
Q5c - Physical/Chemical features | ||||||||
Q5c - Pressures |
|
|||||||
Q9a - Elements | ||||||||
Q5a - GES criteria | Relevant GES criteria |
|
||||||
Q5b - GES indicators | Relevant GES indicators |
|
||||||
Q9b - Parameters monitored (state/impact) | Species distribution | |||||||
Species population size | ||||||||
Species population characteristics | ||||||||
Species impacts | ||||||||
Habitat distribution | ||||||||
Habitat extent | ||||||||
Habitat condition (physical-chemical) | ||||||||
Habitat condition (biological) | ||||||||
Habitat impacts | ||||||||
Q9b - Parameters monitored (pressures) | Pressure input | |||||||
Pressure output | ||||||||
Q9b - Parameters monitored (activity) | Activity | |||||||
Q9b Parameters monitored (other) | Other | |||||||
Q41 Spatial scope | ||||||||
Q4j - Description of spatial scope | ||||||||
Marine Unit IDs |
|
|||||||
Q4h - Temporal scope | Start date- End date | - |
||||||
Q9h - Temporal resolution of sampling | ||||||||
Q9c - Monitoring method | ||||||||
Q9d - Description of alteration to method | ||||||||
Q9e - Quality assurance | ||||||||
Q9f - Quality control | ||||||||
Q9g - Spatial resolution of sampling | Q9g - Proportion of area covered % | |||||||
Q9g - No. of samples | ||||||||
Q9i - Description of sample representivity | ||||||||
Q10a - Scale for aggregation of data | ||||||||
Q10b - Other scale for aggregation of data | ||||||||
Q10c - Access to monitoring data | Q10c - Data type | |||||||
Q10c - Data access mechanism | ||||||||
Q10c - Data access rights | ||||||||
Q10c - INSPIRE standard | ||||||||
Q10c Date data are available | ||||||||
Q10c - Data update frequency | ||||||||
Q10d - Description of data access | ||||||||
Descriptor |
D2 |
||||||
---|---|---|---|---|---|---|---|
Monitoring strategy description |
1.The monitoring aims to detect input of new non-indigenous species. Accordingly, observations and sampling is carried out in port areas.
2. Two non-indigenous species, China mitten crab and round goby, are targeted by this sub-program. Wide spectrum of methods, including sampling and analyses of planktonic phase, collaboration with fishermen and public monitoring, are being utilized to chracterize distribution and abundance of these species. |
||||||
Coverage of GES criteria |
Adequate monitoring will be in place by 2024 |
||||||
Gaps and plans |
1. The monitoring aims to detect input of new non-indigenous species. Accordingly, observations and sampling is carried out in port areas.
2. To fully employ capacity of public monitoring dedicated application have been elaborated in 2020. |
||||||
Related targets |
|
||||||
Coverage of targets |
Adequate monitoring will be in place by 2024 |
||||||
Related measures |
|||||||
Coverage of measures |
|||||||
Related monitoring programmes |
|
||||||
Programme code |
LV-4.2.1. (D2C1) |
LV-4.2.2. (D2C2) |
|||||
Programme name |
Non-indigenous species inputs - from specific sources |
Non-indigenous species abundance and/or biomass (naturalized non-indigenous species) |
|||||
Update type |
New programme |
New programme |
|||||
Old programme codes |
|||||||
Programme description |
The purpose of the monitoring is to assess the ecological status of Baltic sea including one of the environmental status indicators occurrence of the non-indigenous species (NIS) and pathogens as well as changes of the ecological status, associated with the introduction of these invasive species and pathogens into the environment by the surveys of biological parameters and concern mobile and sessile species and human pathogens in water column and seabed habitats. NIS monitoring addresses all ecosystem components as NIS may belong to any trophic levels and affect the functioning of the system. Monitoring is performed at the source of NIS in ports to assess the influence the ballast waters of ships.
Corresponding HELCOM monitoring programme Non-Indigenous Species and
sub-programme Non-Indigenous Species with HELCOM core indicator Trends in arrival of new non-indigenous species which is linked to the monitoring undertaken in the sub-programme. HELCOM monitoring programme is not adapted for serving this indicator yet.
Monitoring of this sub-programme within HELCOM is partially coordinated. The monitoring of phytoplankton, zooplankton, macrophytes and benthic fauna undertaken as part of the HELCOM COMBINE Manual is coordinated and ongoing. Port monitoring has a coordinated and agreed protocol, bet the monitoring itself is not agreed at Baltic scale.
General monitoring of the state of the environment in ports is ongoing in Latvia, but measures to assess impacts of ship ballast waters according to the Ballast Water Convention in Latvia are still in the planning phase.
The survey and sampling of environmental parameters in Latvian ports is carried out in accordance with the HELCOM/OSPAR Port Survey Protocol, which is part of the Joint HELCOM/OSPAR Guidelines on Exceptions under the International Convention on the Control and Management of Ships' Ballast Water and Deposition, Regulations A-4 adopted by the Parties to HELCOM and OSPAR. adopted in 2013. |
The purpose of the monitoring is to assess the ecological status of Baltic sea including one of the environmental status indicators pressure caused by occurrence of the naturalized non-indigenous species (NIS) which significantly increase adverse effects on specific species groups or habitat types as well as changes of the ecological status, associated with the introduction of these invasive species into the environment.
Corresponding HELCOM monitoring programme Non-Indigenous Species and
sub-programme Non-Indigenous Species with HELCOM core indicator Trends in arrival of new non-indigenous species which is linked to the monitoring undertaken in the sub-programme. HELCOM monitoring programme is not adapted for serving this indicator yet. For this NIS (Chinese mitten crab) national programme is developed.
Different kinds of surveys are planned covering all stages of life observations of crabs in planktonic stage of development, collecting data from fishermen about by-caught individuals and public survey about found crabs.
The requirements for the marine waters of Latvia and the relationship of the specified environmental objectives with the qualitative characteristics characterizing the state of the marine environment are included in Regulation of the Cabinet of Ministers of Republic of Latvia No. 1071 of 23 November 2010, Requirements for the Assessment of the State of the Marine Environment, the Determination of Good Environmental State of the Sea and Development of Marine Environmental Goals.
Corresponding legislative acts of the Republic of Latvia concerning fisheries:
Fishery Law (adopted 12.04.1995.) and
Republic of Latvia Cabinet Regulation No. 296, adopted 2 May 2007 Regulations Regarding Commercial Fishing in Territorial Waters and Economic Zone Waters. |
|||||
Monitoring purpose |
|
|
|||||
Other policies and conventions |
|
|
|||||
Regional cooperation - coordinating body |
|
|
|||||
Regional cooperation - countries involved |
|||||||
Regional cooperation - implementation level |
Agreed data collection methods |
Agreed data collection methods |
|||||
Monitoring details |
Observations are made at fixed stations, the coordinates of which have been determined in advance in 3 largest ports of Latvia Liepāja, Ventspils and RD+ga. Frequency of sampling 3 times in 6 years twice in a year during spring and summer seasons, in a phytoplankton bloom maximum period. Methods according to the HELCOM/OSPAR Port Survey Protocol.
- Hydrobiological parameters determined:
- - Abundance, species composition and biomass of phytoplankton, zooplankton and zoobenthos organisms (details see in the sections LV-4.1.2., LV-4.1.3. and LV-4.1.4.);
- - mobile epifauna (sampling with pots (for crabs), by scraping from constructions and sedimentation plates)
- Physical and chemical parameters determined in the water column:
- - CTD probe (temperature, salinity, turbidity, dissolved oxygen), Secchi depth, chlorophyll a (details see in the sections LV-4.5.2., LV-4.5.4. and LV-4.5.5.);
- -Chemical parameters determined in the near-bottom layer (details see in the sections LV-4.5.4. and LV-4.5.5.:
temperature, salinity, oxygen saturation.
- Human pathogens:
Intestinal enterococci, Escherichia coli, Vibrio cholera (testing according to the EN ISO methods: 7899-1 or7899-2, 9308-1 or 9308-3, no standard method for Vibrio cholera yet)
- Ground type and fractions visual assessment during the sampling. |
3 national sub-programmes for monitoring of the Chinese mitten crab have been developed:
1) For monitoring of planktonic phase of development samples are collected with standard net construction with opening 57 cm and mesh size 100 microns. Observations are made at fixed stations, the coordinates of which have been determined in advance by sampling on certain depths. Frequency of sampling up to 9 times per year. Species composition, abundance and biomass is determined according to the HELCOM recommendations in COMBINE manual in Guidelines for monitoring of mesozooplankton. The method is suitable for qualitative (species composition) and quantitative (biomass) detection of zooplankton organisms in nature water samples.
2) For monitoring of adult Chinese mitten crabs abundance information about by-caught individuals in industrial coastal fishing is used. Information is collected from fishermen. Comparison of data about by-caught crabs in the form (CPUE or catch per unit effort) over seasons and coastal areas is made. Industrial fishing takes place regularly throughout the year, covering most of the coastal territory of Latvia and the information obtained will be spatially representative.
It is planned to use one coastal fishing company in each coastal parish of Latvia, by agreeing to register information on the duration of the fishing act, the fishing gear used and the Chinese mitten crabs caught in them during the whole fishing season.
In addition to this collection of biological crab samples are also planned in order to register their gender, maturity, morphological parameters (and genetic material). Biological analyses of crabs in the long term scale would help answer the question whether this species is able to adapt and reproduce successfully in Latvian marine waters.
3) Public monitoring of the distribution of these crabs in an internet site will be created, where the Latvian public can report on findings of Chinese mitten crab. The information reporting page defines the parameters to be reported (e.g. date, time, location coordinates, required images, etc.). LHEI, in cooperation with the DAP, will assess the quality of the reported data to be used for monitoring Chinese mitten crabs.
Data/samples for round goby are obtained from:
1) coastal commercial fishing trips and from coastal fishing logbooks,
2) coastal fish monitoring and
3) benthic fish surveys. |
|||||
Features |
Input of microbial pathogens
|
Newly introduced non-indigenous species
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Input or spread of non-indigenous species
|
||
Input of microbial pathogens
|
Newly introduced non-indigenous species
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Input or spread of non-indigenous species
|
|||
Input of microbial pathogens
|
Newly introduced non-indigenous species
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Input or spread of non-indigenous species
|
|||
Input of microbial pathogens
|
Newly introduced non-indigenous species
|
Chemical characteristics
|
Physical and hydrological characteristics
|
Input or spread of non-indigenous species
|
|||
Elements |
|
|
|
|
|
|
|
GES criteria |
D2C1 |
D2C1 |
NotRelevan |
NotRelevan |
D2C2 |
||
Parameters |
|
|
|
|
|
|
|
Parameter Other |
|||||||
Spatial scope |
|
|
|||||
Marine reporting units |
|
|
|||||
Temporal scope (start date - end date) |
2021-2026 |
2021-2026 |
|||||
Monitoring frequency |
Other |
Yearly |
|||||
Monitoring type |
|
|
|||||
Monitoring method |
|
|
|||||
Monitoring method other |
|||||||
Quality control |
QA procedures according to COMBINE Helsinki Commission Cooperative Monitoring in the Baltic Marine Environment manual of measurement protocols and Manual for Marine Monitoring in the COMBINE Programme of HELCOM. Part B. General Guidelines on Quality Assurance for Monitoring in the Baltic Sea" and in Guidelines for monitoring of specific parameters in this Manual (physical and chemical parameters as well as phytoplankton, zooplankton and zoobenthos).
For the fouling and epifauna procedures will be developed.
For human pathogens according to the ISO standard methods for testing used.
QC procedures: R - control charts based on agreed quality criterion, participation in ring-testing activities in line with HELCOM recommendations.
QC procedures: R - control charts based on agreed quality criterion, participation in ring-testing activities in line with HELCOM recommendations. |
Data holder is Latvian Institute of Aquatic Ecology (LIAE), Institute of Food Safety, Animal Health and Environment "BIOR" and Nature Conservation Agency of Latvia (NCA).
QA/QC on data (zooplankton) according to the Manual for Marine Monitoring in the COMBINE Programme of HELCOM. Part B. General Guidelines on Quality Assurance for Monitoring in the Baltic Sea and in Guidelines relating to the specific parameter in this Manual.
Data are available in LIAE and NCA. |
|||||
Data management |
Data holder is Latvian Institute of Aquatic Ecology (LIAE).
QC on data according to the Manual for Marine Monitoring in the COMBINE Programme of HELCOM. Part B. General Guidelines on Quality Assurance for Monitoring in the Baltic Sea . and guidelines
Data are available in LIAE. |
Data holder is Latvian Institute of Aquatic Ecology (LIAE) and Nature Conservation Agency of Latvia (NCA).
QC on data (zooplankton) according to the Manual for Marine Monitoring in the COMBINE Programme of HELCOM. Part B. General Guidelines on Quality Assurance for Monitoring in the Baltic Sea
Data are available in LIAE and NCA. |
|||||
Data access |
|||||||
Related indicator/name |
|
|
|||||
Contact |
Latvian Institute of Aquatic Ecology
e-mail: juris.aigars@lhei.lv |
Nature Conservation Agency of Latvia:
Latvian Institute of Aquatic Ecology:
e-mail: juris.aigars@lhei.lv |
|||||
References |
Guidelines for monitoring of mesozooplankton:
https://helcom.fi/media/publications/Guidelines-for-monitoring-of-mesozooplankton.pdf
Guidelines for Coastal Fish Monitoring Sampling Methods of HELCOM:
http://helcom.fi/Lists/Publications/Guidelines for Coastal fish Monitoring of HELCOM.pdf
and BIOR documentation:
https://www.bior.lv/sites/default/files/inline-files/Piekrastes_uzskaites_bentiska_uskaite_RJL.pdf |