MS/Art11/2020/D8/Estonia/Baltic Sea

Member State report / Art11 / 2020 / D8 / Estonia / Baltic Sea

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
Member State	Estonia
Region/subregion	Baltic Sea
Reported by	Estonian Environment Agency
Report date	2020-11-11
Report access	ART11_Programmes_Merge_EE_v5.xml msfd-ART11_Strategies_ea.xml

Simplified table

Descriptor	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8	D8
Monitoring strategy description	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.	The aim of the monitoring strategy “SD8 – Contaminants” is to collect data on levels of contaminants and their impact on the marine environment in the Estonian waters. Based on the gathered data, the human-induced pressures in the marine environment are assessed. The levels of contaminants are analysed in water, sediments or biota whereas the matrix depends on the substance. Priority substances, listed in EQS directive 2013/39 are monitored in coastal waters and metals, PCBs, TBT, PFOS, HBCDD, PBDE, PAH, DEHP, HCH and pesticides on offshore areas (from Baltic herring). The monitoring programmes involved are: “Inputs of nutrients and contaminants – land-based sources”, “Contaminant levels – in water”, “Contaminant levels – in sediments”, “Contaminant levels – in species”, “Radioactive substances”, “Oil spills”. The impact onto biota is assessed using data collected within the monitoring programmes “Birds – mortality due to oil pollution” and “Abundance of waterbirds in the breeding season”. Information on the uses and human activities, potentially causing contamination of the environment and on pollution loads, is collected in the programme “Marine and coastal activities”.
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Gaps and plans	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.	There is a need to analyse the structure of the national hydrochemical monitoring programme of rivers, including its spatial and temporal scope, in order to ensure sufficient data for reliable assessment of contaminants load from land-based sources. There is no information about the input and load of synthetic substances. The monitoring frequency of concentration of contaminants in the coastal area does not provide sufficient data that could be used for the HELCOM assessments based on core indicators (at least 3 times per 6-year period needed). Open-sea area monitoring of contaminants in biota is carried out using fish species, while zoobenthos is the preferred matrix for some substances. There is no monitoring of contaminants in water and sediments in open-sea areas. There is also a need to monitor secondary pollution, including getting data of developments, dredging and dumping works into a public database. Monitoring of the biological effects of hazardous substances has been carried out as pilot projects, i.e information for the development of D8C2 assessment indicators has been collected. An indicator "Proportion of oiled birds" has been developed for the assessment of the impact and specific pressure of oil pollutants to the status of species and habitats (or the impact of significant acute pollution events on species health and habitat status, GES criterion D8C4), but has not been applied in the D8 assessment yet. Baltic Sea-specific threshold values for contaminants in sediments need to be developed.
Related targets	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23	BALEE-T31 BALEE-T32 BALEE-T33 BALEE-T35 Target 23
Coverage of targets	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020
Related measures	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'	BALEE-M010 - 'Management of direct discharges of storm water to minimise the load of nutrients, contaminants and litter' BALEE-M011 - 'Enhancing the capability of marine pollution control to respond to emergencies and environmental pollution at sea' BALEE-M012 - 'Managing environmental risks accompanying bunkering at sea' Not specified - 'Limiting emissions of hazardous substances' Not specified - 'Water management plans - revision of environmental permit conditions, additional monitoring of compliance with the legislative requirements and with the conditions of permit for the special use of water, complying with the set requirements, Training of wastewater treatment plant operators'
Coverage of measures	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020	Adequate monitoring is in place by July 2020
Related monitoring programmes	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides	BALEE-D00-40_MarineAndCoastalActivities BALEE-D0104-2_BirdsBreeding BALEE-D0508-22_NutContLandSource BALEE-D08-30_ContaminantSediment BALEE-D08-31_ContaminantWater BALEE-D08-34_OilPollution BALEE-D08-35_BirdsWashedAshore BALEE-D0809-29_ContaminantBiota BALEE-D0809-33_Radionuclides
Programme code	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D00-40_MarineAndCoastalActivities	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0104-2_BirdsBreeding	BALEE-D0508-22_NutContLandSource	BALEE-D0508-22_NutContLandSource	BALEE-D08-30_ContaminantSediment	BALEE-D08-30_ContaminantSediment	BALEE-D08-31_ContaminantWater	BALEE-D08-31_ContaminantWater	BALEE-D08-34_OilPollution	BALEE-D08-35_BirdsWashedAshore	BALEE-D08-35_BirdsWashedAshore	BALEE-D08-35_BirdsWashedAshore	BALEE-D0809-29_ContaminantBiota	BALEE-D0809-29_ContaminantBiota	BALEE-D0809-29_ContaminantBiota	BALEE-D0809-29_ContaminantBiota	BALEE-D0809-33_Radionuclides
Programme name	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Marine and coastal activities	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Abundance of water birds in the breeding season	Inputs of nutrients and contaminants – land-based sources	Inputs of nutrients and contaminants – land-based sources	Contaminant levels – in sediment	Contaminant levels – in sediment	Contaminant levels – in water	Contaminant levels – in water	Oil spills	Birds – mortality due to oil pollution (birds washed ashore)	Birds – mortality due to oil pollution (birds washed ashore)	Birds – mortality due to oil pollution (birds washed ashore)	Contaminant levels – in species	Contaminant levels – in species	Contaminant levels – in species	Contaminant levels – in species	Radioactive substances
Update type	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Same programme as in 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014	Modified from 2014
Old programme codes	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities	BALEE-D00-39_CoastalOffshoreActivities																								BALEE-D08-30_ContaminantSediment	BALEE-D08-30_ContaminantSediment	BALEE-D08-31_ContaminantWater	BALEE-D08-31_ContaminantWater	BALEE-D08-33_OilPollution	BALEE-D08-34_BirdsWashedAshore	BALEE-D08-34_BirdsWashedAshore	BALEE-D08-34_BirdsWashedAshore	BALEE-D0809-29_ContaminantBiota	BALEE-D0809-29_ContaminantBiota	BALEE-D0809-29_ContaminantBiota	BALEE-D0809-29_ContaminantBiota	BALEE-D0809-32_Radionuclides
Programme description	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the monitoring programme is to collect data on human activities that directly or indirectly impact the marine environment. The monitored human activities are those listed in the MSFD Annex III Table 2b (2017/845/EC) and relevant for point (c) of Article 8(1), and Articles 10 and 13. The following activities are covered: Coastal defence and flood protection; Offshore structures (other than for oil/gas/renewables); Restructuring of seabed morphology, including dredging and depositing of materials; Extraction of minerals; Extraction of oil and gas, including infrastructure; Extraction of water; Renewable energy generation (wind, wave and tidal power), including infrastructure; Transmission of electricity and communications (cables); Fish harvesting (professional, recreational); Fish and shellfish processing; Marine plant harvesting; Hunting and collecting for other purposes; Aquaculture — marine, including infrastructure; Transport infrastructure; Transport — shipping; Waste treatment and disposal; Tourism and leisure infrastructure; Tourism and leisure activities; Military operations and Research, survey and educational activities. Data are gathered at least once during a six-year assessment period, but in some cases also annually. The system of such data collection activities is still under development. The programme corresponds to the following monitoring programmes in the indicative list: Activities extracting living resources (fisheries including recreational, marine plant harvesting, hunting and collecting); Activities extracting non-living resources (sand, gravel, dredging); Activities producing food (aquaculture); Activities with permanent infrastructures (e.g. renewable energy, oil & gas, ports) or structural changes (e.g. coastal defences); Sea-based mobile activities (shipping, boating); Coastal human activities (e.g. tourism, recreational sports, ecotourism). The programme is the further development of the programme presented in 2014. The code of the programme also changed.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor the abundance of waterbirds in Estonian coastal areas during the breeding season. It provides data to monitoring strategy “SD1.1 – Biological diversity – Birds” and “SD8 – Contaminants”. The programme is related to GES Descriptor D1, Criterion D1C2 and potentially D1C3 and D1C4, as well as GES Descriptor D4, Criteria D4C2 and D4C4 and Descriptor D8, Criterion D8C2. Monitoring is conducted yearly on small islands (island groups) where the full number of nests and species are registered. White-tailed eagle breeding success is monitored to assess the impact of contaminants. The monitoring area of the white-tailed eagle relevant to marine status assessment covers the area up to 20 km landward from the seashore. The programme data collection is regionally coordinated via HELCOM. Data are annually reported to the national environmental monitoring database KESE (annually by 1 March). The programme corresponds to following monitoring programmes in the indicative list: Mobile species – distribution, abundance and/or biomass; Mobile species – health status; Mobile species – population characteristics.	The aim of the programme is to monitor and estimate the load of nutrients and contaminants from the land-based sources via rivers and direct discharges. It provides data to monitoring strategies “SD5 – Eutrophication” and “SD8 - Contaminants”. The programme is related to anthropogenic pressure “Input of nutrients” and “Inputs of other substances” (MSFD Annex III). Monitoring is conducted yearly. The program is regionally coordinated via HELCOM and the HELCOM PLC guidelines are followed. The programme corresponds to the following monitoring programmes in the indicative list: Nutrient inputs - land-based sources; Contaminant inputs - land-based sources.	The aim of the programme is to monitor and estimate the load of nutrients and contaminants from the land-based sources via rivers and direct discharges. It provides data to monitoring strategies “SD5 – Eutrophication” and “SD8 - Contaminants”. The programme is related to anthropogenic pressure “Input of nutrients” and “Inputs of other substances” (MSFD Annex III). Monitoring is conducted yearly. The program is regionally coordinated via HELCOM and the HELCOM PLC guidelines are followed. The programme corresponds to the following monitoring programmes in the indicative list: Nutrient inputs - land-based sources; Contaminant inputs - land-based sources.	The aim of the programme is to monitor the concentrations of contaminants in sediments. It provides data to monitoring strategy “SD8 – Contaminants” and is related to GES Descriptor D8, Criterion D8C1. The pressure levels in the environment are assessed for the Estonian waters, both the coastal and the off-shore areas (territorial waters, HELCOM division). Sediment samples are analysed for the following harmful substances: PAHs, PBDEs and BDE209, DEHPs, HCHs, phenols, metals (Hg, Cd, Ni, Pb, Zn, Cu, Ba, Cr, As, Sn), TBT, pesticides, chlorobenzenes, PFOS, dioxins and dl-PCBs, HBCDDs, hydrocarbons (C10-C40). The programme data collection is regionally coordinated via HELCOM, but data are delivered separately by each country. HELCOM guidelines are followed as well as EU-WFD guidelines on sediment sampling for chemical status assessment. The data are yearly reported to the environmental monitoring database KESE (by 1 March) and the HELCOM ICES database (by 1 September). The programme has been modified since 2014: the list of monitoring substances and monitoring sites was updated. The programme corresponds to the following monitoring programmes in the indicative list: Contaminant levels - in water/sediment.	The aim of the programme is to monitor the concentrations of contaminants in sediments. It provides data to monitoring strategy “SD8 – Contaminants” and is related to GES Descriptor D8, Criterion D8C1. The pressure levels in the environment are assessed for the Estonian waters, both the coastal and the off-shore areas (territorial waters, HELCOM division). Sediment samples are analysed for the following harmful substances: PAHs, PBDEs and BDE209, DEHPs, HCHs, phenols, metals (Hg, Cd, Ni, Pb, Zn, Cu, Ba, Cr, As, Sn), TBT, pesticides, chlorobenzenes, PFOS, dioxins and dl-PCBs, HBCDDs, hydrocarbons (C10-C40). The programme data collection is regionally coordinated via HELCOM, but data are delivered separately by each country. HELCOM guidelines are followed as well as EU-WFD guidelines on sediment sampling for chemical status assessment. The data are yearly reported to the environmental monitoring database KESE (by 1 March) and the HELCOM ICES database (by 1 September). The programme has been modified since 2014: the list of monitoring substances and monitoring sites was updated. The programme corresponds to the following monitoring programmes in the indicative list: Contaminant levels - in water/sediment.	The aim of the programme is to monitor the concentrations of contaminants in water. It provides data to monitoring strategy “SD8 – Contaminants” and is related to GES Descriptor D8, Criterion D8C1. The pressure levels in the environment are assessed for the Estonian waters, both the coastal and the off-shore areas (territorial waters, HELCOM sub-divisions). Water samples are analysed for the harmful substances: DEHPs, phenols, metals (Hg, Cd, Ni, Pb, Zn, Cu, Ba, Cr, As, Sn), TBT, pesticides, PFOS, PFAS, hydrocarbons (C10-C40). The program data collection is regionally coordinated via HELCOM (data delivered separately by each country), and the HELCOM guidelines and requirements of WFD and its daughter directives are followed. The data are yearly reported to the environmental monitoring database KESE (by 1 March) and the HELCOM ICES database (by 1 September). The programme has been modified since 2014: the list of monitoring substances was updated. The programme corresponds to the following monitoring programmes in the indicative list: Contaminant levels - in water/sediment	The aim of the programme is to monitor the concentrations of contaminants in water. It provides data to monitoring strategy “SD8 – Contaminants” and is related to GES Descriptor D8, Criterion D8C1. The pressure levels in the environment are assessed for the Estonian waters, both the coastal and the off-shore areas (territorial waters, HELCOM sub-divisions). Water samples are analysed for the harmful substances: DEHPs, phenols, metals (Hg, Cd, Ni, Pb, Zn, Cu, Ba, Cr, As, Sn), TBT, pesticides, PFOS, PFAS, hydrocarbons (C10-C40). The program data collection is regionally coordinated via HELCOM (data delivered separately by each country), and the HELCOM guidelines and requirements of WFD and its daughter directives are followed. The data are yearly reported to the environmental monitoring database KESE (by 1 March) and the HELCOM ICES database (by 1 September). The programme has been modified since 2014: the list of monitoring substances was updated. The programme corresponds to the following monitoring programmes in the indicative list: Contaminant levels - in water/sediment	The aim of the programme is to detect oil spills in the Estonian marine waters. It provides data to monitoring strategy “SD8 – Contaminants” and is related to GES Descriptor D8, Criterion D8C3 (and D8C1). Data are gathered by regular aerial surveillance flights and remote sensing. The extent, duration and volume of oil spills are estimated. The program is regionally coordinated and the HELCOM Response manual (Ch. 7: CO-OPERATION ON AERIAL SURVEILLANCE OVER THE BALTIC SEA AREA) is followed. Data are yearly reported to HELCOM. The programme corresponds to the following monitoring programmes in the indicative list: Contaminant inputs – acute pollution events, incl. oil spills. The programme is essentially the same as in 2014, only the code was changed.	The aim of the programme is to assess the impact of oil pollution on water birds. It provides data to monitoring strategy “SD8 – Contaminants” and is related to GES Descriptor D8, Criteria D8C2 and D8C4, and potentially provides data for monitoring strategy „SD1.1 – Biological diversity – Birds“. Data are gathered to assess the impact of human-induced pressures. Monitoring is conducted twice a year (spring and autumn) by counting dead birds washed ashore along the selected monitoring sites (on beaches). The species and their contamination by oil are recorded, and data are reported as the number of dead birds per 1 km of coastline. The monitoring program is regionally not coordinated yet. Data are yearly reported to the national environmental monitoring database KESE (by 1 March). The programme corresponds to the following monitoring programmes in the indicative list: Mobile species – mortality/injury rates from other human activities. The programme is essentially the same as in 2014, only the code was changed.	The aim of the programme is to assess the impact of oil pollution on water birds. It provides data to monitoring strategy “SD8 – Contaminants” and is related to GES Descriptor D8, Criteria D8C2 and D8C4, and potentially provides data for monitoring strategy „SD1.1 – Biological diversity – Birds“. Data are gathered to assess the impact of human-induced pressures. Monitoring is conducted twice a year (spring and autumn) by counting dead birds washed ashore along the selected monitoring sites (on beaches). The species and their contamination by oil are recorded, and data are reported as the number of dead birds per 1 km of coastline. The monitoring program is regionally not coordinated yet. Data are yearly reported to the national environmental monitoring database KESE (by 1 March). The programme corresponds to the following monitoring programmes in the indicative list: Mobile species – mortality/injury rates from other human activities. The programme is essentially the same as in 2014, only the code was changed.	The aim of the programme is to assess the impact of oil pollution on water birds. It provides data to monitoring strategy “SD8 – Contaminants” and is related to GES Descriptor D8, Criteria D8C2 and D8C4, and potentially provides data for monitoring strategy „SD1.1 – Biological diversity – Birds“. Data are gathered to assess the impact of human-induced pressures. Monitoring is conducted twice a year (spring and autumn) by counting dead birds washed ashore along the selected monitoring sites (on beaches). The species and their contamination by oil are recorded, and data are reported as the number of dead birds per 1 km of coastline. The monitoring program is regionally not coordinated yet. Data are yearly reported to the national environmental monitoring database KESE (by 1 March). The programme corresponds to the following monitoring programmes in the indicative list: Mobile species – mortality/injury rates from other human activities. The programme is essentially the same as in 2014, only the code was changed.	The aim of the programme is to monitor the concentrations of contaminants in biota. It provides data to monitoring strategy “SD8 – Contaminants” and is related to GES Descriptor D8, Criterion D8C1. The pressure levels in the environment and the contamination of the species are assessed for the Estonian waters, both the coastal and the off-shore areas (HELCOM sub-divisions). Fish samples (perch in coastal waters and herring in open sea areas, either muscle or liver, depending on the substance) are analysed for the following harmful substances: PAHs, PBDEs and BDE209, DEHPs, HCHs, phenols, metals (Hg, Cd, Ni, Pb, Zn, Cu, Ba, Cr, As, Sn), TBT, pesticides, chlorobenzenes, PFOS, dioxins and dl-PCBs, HBCDDs, hydrocarbons (C10-C40). PAHs in coastal waters are monitored from Mytilus trossulus Gould. The programme is regionally coordinated via HELCOM, but also by EU WFD chemical monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March), HELCOM ICES database (by 1 September) and European Environment Agency Eionet database. The programme corresponds to the following monitoring programmes in the indicative list: Contaminant levels - in species, including seafood. The programme has been modified since 2014: the list of monitoring substances was updated and sampling is performed from different matrixes. Food safety monitoring is no longer a part of the programme: the new separate programme was created (Contaminant level - in seafood).	The aim of the programme is to monitor the concentrations of contaminants in biota. It provides data to monitoring strategy “SD8 – Contaminants” and is related to GES Descriptor D8, Criterion D8C1. The pressure levels in the environment and the contamination of the species are assessed for the Estonian waters, both the coastal and the off-shore areas (HELCOM sub-divisions). Fish samples (perch in coastal waters and herring in open sea areas, either muscle or liver, depending on the substance) are analysed for the following harmful substances: PAHs, PBDEs and BDE209, DEHPs, HCHs, phenols, metals (Hg, Cd, Ni, Pb, Zn, Cu, Ba, Cr, As, Sn), TBT, pesticides, chlorobenzenes, PFOS, dioxins and dl-PCBs, HBCDDs, hydrocarbons (C10-C40). PAHs in coastal waters are monitored from Mytilus trossulus Gould. The programme is regionally coordinated via HELCOM, but also by EU WFD chemical monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March), HELCOM ICES database (by 1 September) and European Environment Agency Eionet database. The programme corresponds to the following monitoring programmes in the indicative list: Contaminant levels - in species, including seafood. The programme has been modified since 2014: the list of monitoring substances was updated and sampling is performed from different matrixes. Food safety monitoring is no longer a part of the programme: the new separate programme was created (Contaminant level - in seafood).	The aim of the programme is to monitor the concentrations of contaminants in biota. It provides data to monitoring strategy “SD8 – Contaminants” and is related to GES Descriptor D8, Criterion D8C1. The pressure levels in the environment and the contamination of the species are assessed for the Estonian waters, both the coastal and the off-shore areas (HELCOM sub-divisions). Fish samples (perch in coastal waters and herring in open sea areas, either muscle or liver, depending on the substance) are analysed for the following harmful substances: PAHs, PBDEs and BDE209, DEHPs, HCHs, phenols, metals (Hg, Cd, Ni, Pb, Zn, Cu, Ba, Cr, As, Sn), TBT, pesticides, chlorobenzenes, PFOS, dioxins and dl-PCBs, HBCDDs, hydrocarbons (C10-C40). PAHs in coastal waters are monitored from Mytilus trossulus Gould. The programme is regionally coordinated via HELCOM, but also by EU WFD chemical monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March), HELCOM ICES database (by 1 September) and European Environment Agency Eionet database. The programme corresponds to the following monitoring programmes in the indicative list: Contaminant levels - in species, including seafood. The programme has been modified since 2014: the list of monitoring substances was updated and sampling is performed from different matrixes. Food safety monitoring is no longer a part of the programme: the new separate programme was created (Contaminant level - in seafood).	The aim of the programme is to monitor the concentrations of contaminants in biota. It provides data to monitoring strategy “SD8 – Contaminants” and is related to GES Descriptor D8, Criterion D8C1. The pressure levels in the environment and the contamination of the species are assessed for the Estonian waters, both the coastal and the off-shore areas (HELCOM sub-divisions). Fish samples (perch in coastal waters and herring in open sea areas, either muscle or liver, depending on the substance) are analysed for the following harmful substances: PAHs, PBDEs and BDE209, DEHPs, HCHs, phenols, metals (Hg, Cd, Ni, Pb, Zn, Cu, Ba, Cr, As, Sn), TBT, pesticides, chlorobenzenes, PFOS, dioxins and dl-PCBs, HBCDDs, hydrocarbons (C10-C40). PAHs in coastal waters are monitored from Mytilus trossulus Gould. The programme is regionally coordinated via HELCOM, but also by EU WFD chemical monitoring guidelines. The data are yearly reported to the environmental monitoring database KESE (by 1 March), HELCOM ICES database (by 1 September) and European Environment Agency Eionet database. The programme corresponds to the following monitoring programmes in the indicative list: Contaminant levels - in species, including seafood. The programme has been modified since 2014: the list of monitoring substances was updated and sampling is performed from different matrixes. Food safety monitoring is no longer a part of the programme: the new separate programme was created (Contaminant level - in seafood).	The aim of the programme is to monitor the concentrations of radioactive substances in the marine environment. It provides data to monitoring strategy “SD8 – Contaminants” and is related to GES Descriptor D8, Criterion D8C1. The pressure levels and status are assessed for the Estonian waters in the Gulf of Finland as agreed in HELCOM MORS. Monitoring is conducted yearly, and the samples collected from water, sediments and biota are analysed for Cs-137 and K-40 concentrations. The program data collection is regionally coordinated via HELCOM (data delivered separately by each country) and the HELCOM guidelines are followed. Data are yearly reported to the national environmental monitoring database KESE (by 1 March) and ICES (HELCOM Combine). The programme corresponds to the following monitoring programmes in the indicative list: Contaminant levels - in water/sediment; Contaminant levels - in species, including seafood. The programme is essentially the same as in 2014, only the code was changed.
Monitoring purpose	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures at source Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Environmental state and impacts Pressures in the marine environment	Effectiveness of measures Pressures at source	Effectiveness of measures Pressures at source	Effectiveness of measures Environmental state and impacts Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Pressures in the marine environment	Effectiveness of measures Human activities causing the pressures Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Pressures in the marine environment	Effectiveness of measures Environmental state and impacts Pressures in the marine environment	Pressures in the marine environment
Other policies and conventions	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Bathing Water Directive Birds Directive Convention on Long-Range Transboundary Air Pollution Data Collection Framework Multi-Annual Plan (Common Fisheries Policy) Habitats Directive IMO-BWM Maritime Spatial Planning Directive Minamata Convention on Mercury Monitoring programme targeting at national legislation National Emission Ceilings Directive Nitrates Directive Stockholm Convention on persistent organic pollutions (POPs) Urban Waste Water Treatment Directive Water Framework Directive	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Birds Directive Habitats Directive Monitoring programme targeting at national legislation	Minamata Convention on Mercury Monitoring programme targeting at national legislation Nitrates Directive Urban Waste Water Treatment Directive Water Framework Directive	Minamata Convention on Mercury Monitoring programme targeting at national legislation Nitrates Directive Urban Waste Water Treatment Directive Water Framework Directive	HELCOM Monitoring programmes Minamata Convention on Mercury Monitoring programme targeting at national legislation Water Framework Directive	HELCOM Monitoring programmes Minamata Convention on Mercury Monitoring programme targeting at national legislation Water Framework Directive	HELCOM Monitoring programmes Minamata Convention on Mercury Monitoring programme targeting at national legislation Water Framework Directive	HELCOM Monitoring programmes Minamata Convention on Mercury Monitoring programme targeting at national legislation Water Framework Directive	HELCOM Monitoring programmes IMO-OPRC-H International Convention for the Prevention of Pollution from Ships International Convention on Oil Pollution Preparedness, Response and Co-operation	Birds Directive	Birds Directive	Birds Directive	HELCOM Monitoring programmes Minamata Convention on Mercury Monitoring programme targeting at national legislation Water Framework Directive	HELCOM Monitoring programmes Minamata Convention on Mercury Monitoring programme targeting at national legislation Water Framework Directive	HELCOM Monitoring programmes Minamata Convention on Mercury Monitoring programme targeting at national legislation Water Framework Directive	HELCOM Monitoring programmes Minamata Convention on Mercury Monitoring programme targeting at national legislation Water Framework Directive	HELCOM Monitoring programmes
Regional cooperation - coordinating body																								HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM	HELCOM				HELCOM	HELCOM	HELCOM	HELCOM	HELCOM
Regional cooperation - countries involved																																																			EE,FI,LT,LV,SE
Regional cooperation - implementation level																								Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection				Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection	Coordinated data collection
Monitoring details																								Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. All breeding species on the island are registered. The indexes for the assessment of the abundance trend by species are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity their nesting sites are monitored and the number of occupied nests and fledglings are registered. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously. Other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years. Breeding birds monitoring is mainly being conducted in frames of the national monitoring programme. Updated and detailed information on the monitoring plan according to the national monitoring programme is available at https://www.keskkonnaagentuur.ee/eesmargid-tegevused/keskkonnaseire/seireankeedid.	Based on the data from hydrometric stations, the discharges of the monitored rivers are determined. The flows of rivers and areas that not covered by the monitoring are estimated using the corresponding transfer coefficients and model (ESTMODEL). In frames of hydrochemical monitoring of watercourses, the contents of nutrients and hazardous substances in water are determined at designated monitoring stations. The pollution loads are assessed by the Estonian Environment Agency according to the methodology agreed within the HELCOM cooperation (PLC-Water Guidelines; https://helcom.fi/action-areas/monitoring-and-assessment/monitoring-guidelines/plc-water-guidelines/). The hydrochemical sampling is performed yearly, 4-12 times a year; river flows are measured continuously. The data are used for assessment of achievement of environmental targets (targets 16 and 23) on the basis of associated indicators.	Based on the data from hydrometric stations, the discharges of the monitored rivers are determined. The flows of rivers and areas that not covered by the monitoring are estimated using the corresponding transfer coefficients and model (ESTMODEL). In frames of hydrochemical monitoring of watercourses, the contents of nutrients and hazardous substances in water are determined at designated monitoring stations. The pollution loads are assessed by the Estonian Environment Agency according to the methodology agreed within the HELCOM cooperation (PLC-Water Guidelines; https://helcom.fi/action-areas/monitoring-and-assessment/monitoring-guidelines/plc-water-guidelines/). The hydrochemical sampling is performed yearly, 4-12 times a year; river flows are measured continuously. The data are used for assessment of achievement of environmental targets (targets 16 and 23) on the basis of associated indicators.	According to the national environmental monitoring programme, coastal water sediment samples are taken from clayey sediments (more than 20% of sediments with siltstone or clay fraction particles d <0.63 μm) from the upper sediment layer of the accumulation areas (depth 0-3-5 cm, maximum 10 cm for older pollution). Minimum of three subsamples are collected for the pooled sample. Samples, with a total volume of at least 1 litre, are mixed, sieved to remove stones and other unnecessary particles. In the laboratory, the concentrations of hazardous substances (µg/kg dry weight) and supplementary parameters as total organic carbon (TOC) concentration are determined. The HELCOM sediment sampling methodology may be used for sampling and contaminants' trend analysis in the territorial sea area. The monitoring is carried at designated sites out in rotation. The monitoring data are also gathered from the environmental impact assessment projects and environmental permits when the corresponding requirement is listed.	According to the national environmental monitoring programme, coastal water sediment samples are taken from clayey sediments (more than 20% of sediments with siltstone or clay fraction particles d <0.63 μm) from the upper sediment layer of the accumulation areas (depth 0-3-5 cm, maximum 10 cm for older pollution). Minimum of three subsamples are collected for the pooled sample. Samples, with a total volume of at least 1 litre, are mixed, sieved to remove stones and other unnecessary particles. In the laboratory, the concentrations of hazardous substances (µg/kg dry weight) and supplementary parameters as total organic carbon (TOC) concentration are determined. The HELCOM sediment sampling methodology may be used for sampling and contaminants' trend analysis in the territorial sea area. The monitoring is carried at designated sites out in rotation. The monitoring data are also gathered from the environmental impact assessment projects and environmental permits when the corresponding requirement is listed.	The samples for analyses of contaminant levels in water are collected from coastal and territorial waters in frames of the national monitoring programme. The monitoring considers WFD requirements. Total organic carbon and water hardness are also measured for supplementary background information. The monitoring is conducted annually in rotation at designated sites - 3 times in the 6-year period at certain sites, 1-4 times during the ice-free period. The monitoring data are also gathered from companies' environmental permits, according to monitoring and frequency requirements listed.	The samples for analyses of contaminant levels in water are collected from coastal and territorial waters in frames of the national monitoring programme. The monitoring considers WFD requirements. Total organic carbon and water hardness are also measured for supplementary background information. The monitoring is conducted annually in rotation at designated sites - 3 times in the 6-year period at certain sites, 1-4 times during the ice-free period. The monitoring data are also gathered from companies' environmental permits, according to monitoring and frequency requirements listed.	Oil pollution is monitored by the Estonian Police and Border Guard Board. The remote observation is performed either by satellite or aerial surveys (ordered and patrol flights), which provides the detection of pollution. The satellite images also contain additional information about the possible level of pollution alert. Three alert levels – green, yellow and red – are distinguished depending on pollution seriousness. When pollution is detected, an aircraft or ship is sent to assess the situation. There are also regular flights conducted 2-3 times a week on certain routes. In case of flight monitoring during daylight hours, the extent and volume of pollution shall be determined visually by the operator in accordance with HELCOM methods. In the dark time, the radar device provides information on the extent of the pollution. To detect oil pollution, satellite images are ordered and patrol flights are organized in the Estonian sea area. Patrols are coordinated with Finland by a Memorandum of Understanding (MoU), under which the Gulf of Finland is covered by patrols even if one of the parties is unable to do so at some reason. The rest of the Estonian sea area is covered only by Estonian patrol flights.	The monitoring is carried out twice a year in four designated areas: in spring, usually in April and May, when migratory waterbirds have not left yet, and in autumn, usually in late October or early November, when the autumn migration of birds is ending. In some monitoring areas additional winter and spring observations have also been conducted at the initiative of observers. The number of dead birds is characterized by the density (number of individuals/km). At certain monitoring area, all dead birds or their remains washed ashore are counted. Residues that are difficult to determine are collected with reference material for later determination. In addition, dead seals found during the observations are recorded. The main parameters obtained as a result of monitoring are the density of dead waterbirds (individuals/ km) and the proportion of oil-stained waterbirds of all found waterbirds (%). The monitoring is carried out in frames of the national environmental monitoring programme (Wildlife diversity and landscape monitoring subprogramme, monitoring activity Birds washed ashore).	The monitoring is carried out twice a year in four designated areas: in spring, usually in April and May, when migratory waterbirds have not left yet, and in autumn, usually in late October or early November, when the autumn migration of birds is ending. In some monitoring areas additional winter and spring observations have also been conducted at the initiative of observers. The number of dead birds is characterized by the density (number of individuals/km). At certain monitoring area, all dead birds or their remains washed ashore are counted. Residues that are difficult to determine are collected with reference material for later determination. In addition, dead seals found during the observations are recorded. The main parameters obtained as a result of monitoring are the density of dead waterbirds (individuals/ km) and the proportion of oil-stained waterbirds of all found waterbirds (%). The monitoring is carried out in frames of the national environmental monitoring programme (Wildlife diversity and landscape monitoring subprogramme, monitoring activity Birds washed ashore).	The monitoring is carried out twice a year in four designated areas: in spring, usually in April and May, when migratory waterbirds have not left yet, and in autumn, usually in late October or early November, when the autumn migration of birds is ending. In some monitoring areas additional winter and spring observations have also been conducted at the initiative of observers. The number of dead birds is characterized by the density (number of individuals/km). At certain monitoring area, all dead birds or their remains washed ashore are counted. Residues that are difficult to determine are collected with reference material for later determination. In addition, dead seals found during the observations are recorded. The main parameters obtained as a result of monitoring are the density of dead waterbirds (individuals/ km) and the proportion of oil-stained waterbirds of all found waterbirds (%). The monitoring is carried out in frames of the national environmental monitoring programme (Wildlife diversity and landscape monitoring subprogramme, monitoring activity Birds washed ashore).	Sampling material (fish) is collected from commercial trawling and scientific fish monitoring and the biological analyse is performed (length, weight, age, sex and gonadal maturity). For chemical analyses as uniform as possible in age, size, sex and sexual maturity specimens are chosen. Chemical analyses should be performed in 3-5 replicates for each chemical class, therefore pooled fish samples are used to make up a sample large enough to provide sufficient material for analysis. The target species for monitoring of contaminants in biota are perch (Perca fluviatilis) in coastal waters and herring (Clupea harengus) in territorial waters and off-shore areas. Samples are taken from female 10-15 perch specimens caught in July-September and female 12-15 herring specimens caught in August-September. Depending on substances that will be analysed, both liver samples (metals, excl. Hg) and muscle tissue (dorso-lateral muscle) samples are made. Although fish is predominantly used for monitoring, PAHs (excl anthracene, naphthalene, fluoranthene) should be determined separately from molluscs - Mytilus trossulus Gould, soft body is used for sample. Pooled sample should be made to provide sufficient material for analysis, which makes ca 100 specimens per sample. Adult specimens (70-90% of the maximum size) are collected. If there are not enough mussels in the coastal water body to collect a representative sample, or if sampling proves to be too expensive, the molluscs samples are replaced by fish samples and analyses are performed from fish muscle tissue. Monitoring is carried out in frames of national marine monitoring - hazardous substances, which contributes to WFD RBMP and programme of measures. In addition, the data on contaminants concentration and impact in biota are gathered from different project-based studies that are ordered by the Ministry of the Environment.	Sampling material (fish) is collected from commercial trawling and scientific fish monitoring and the biological analyse is performed (length, weight, age, sex and gonadal maturity). For chemical analyses as uniform as possible in age, size, sex and sexual maturity specimens are chosen. Chemical analyses should be performed in 3-5 replicates for each chemical class, therefore pooled fish samples are used to make up a sample large enough to provide sufficient material for analysis. The target species for monitoring of contaminants in biota are perch (Perca fluviatilis) in coastal waters and herring (Clupea harengus) in territorial waters and off-shore areas. Samples are taken from female 10-15 perch specimens caught in July-September and female 12-15 herring specimens caught in August-September. Depending on substances that will be analysed, both liver samples (metals, excl. Hg) and muscle tissue (dorso-lateral muscle) samples are made. Although fish is predominantly used for monitoring, PAHs (excl anthracene, naphthalene, fluoranthene) should be determined separately from molluscs - Mytilus trossulus Gould, soft body is used for sample. Pooled sample should be made to provide sufficient material for analysis, which makes ca 100 specimens per sample. Adult specimens (70-90% of the maximum size) are collected. If there are not enough mussels in the coastal water body to collect a representative sample, or if sampling proves to be too expensive, the molluscs samples are replaced by fish samples and analyses are performed from fish muscle tissue. Monitoring is carried out in frames of national marine monitoring - hazardous substances, which contributes to WFD RBMP and programme of measures. In addition, the data on contaminants concentration and impact in biota are gathered from different project-based studies that are ordered by the Ministry of the Environment.	Sampling material (fish) is collected from commercial trawling and scientific fish monitoring and the biological analyse is performed (length, weight, age, sex and gonadal maturity). For chemical analyses as uniform as possible in age, size, sex and sexual maturity specimens are chosen. Chemical analyses should be performed in 3-5 replicates for each chemical class, therefore pooled fish samples are used to make up a sample large enough to provide sufficient material for analysis. The target species for monitoring of contaminants in biota are perch (Perca fluviatilis) in coastal waters and herring (Clupea harengus) in territorial waters and off-shore areas. Samples are taken from female 10-15 perch specimens caught in July-September and female 12-15 herring specimens caught in August-September. Depending on substances that will be analysed, both liver samples (metals, excl. Hg) and muscle tissue (dorso-lateral muscle) samples are made. Although fish is predominantly used for monitoring, PAHs (excl anthracene, naphthalene, fluoranthene) should be determined separately from molluscs - Mytilus trossulus Gould, soft body is used for sample. Pooled sample should be made to provide sufficient material for analysis, which makes ca 100 specimens per sample. Adult specimens (70-90% of the maximum size) are collected. If there are not enough mussels in the coastal water body to collect a representative sample, or if sampling proves to be too expensive, the molluscs samples are replaced by fish samples and analyses are performed from fish muscle tissue. Monitoring is carried out in frames of national marine monitoring - hazardous substances, which contributes to WFD RBMP and programme of measures. In addition, the data on contaminants concentration and impact in biota are gathered from different project-based studies that are ordered by the Ministry of the Environment.	Sampling material (fish) is collected from commercial trawling and scientific fish monitoring and the biological analyse is performed (length, weight, age, sex and gonadal maturity). For chemical analyses as uniform as possible in age, size, sex and sexual maturity specimens are chosen. Chemical analyses should be performed in 3-5 replicates for each chemical class, therefore pooled fish samples are used to make up a sample large enough to provide sufficient material for analysis. The target species for monitoring of contaminants in biota are perch (Perca fluviatilis) in coastal waters and herring (Clupea harengus) in territorial waters and off-shore areas. Samples are taken from female 10-15 perch specimens caught in July-September and female 12-15 herring specimens caught in August-September. Depending on substances that will be analysed, both liver samples (metals, excl. Hg) and muscle tissue (dorso-lateral muscle) samples are made. Although fish is predominantly used for monitoring, PAHs (excl anthracene, naphthalene, fluoranthene) should be determined separately from molluscs - Mytilus trossulus Gould, soft body is used for sample. Pooled sample should be made to provide sufficient material for analysis, which makes ca 100 specimens per sample. Adult specimens (70-90% of the maximum size) are collected. If there are not enough mussels in the coastal water body to collect a representative sample, or if sampling proves to be too expensive, the molluscs samples are replaced by fish samples and analyses are performed from fish muscle tissue. Monitoring is carried out in frames of national marine monitoring - hazardous substances, which contributes to WFD RBMP and programme of measures. In addition, the data on contaminants concentration and impact in biota are gathered from different project-based studies that are ordered by the Ministry of the Environment.	Radioactive substances monitoring is carried out by the Environmental Board in the frame of national environmental monitoring programme (radiation monitoring sub-programme). Monitoring in seawater, biota (fish, bladderwrack) and sediments is carried out every year at designated sites and areas in the Gulf of Finland, and long-term data series are already available. Water samples and sediment samples are collected during off-shore monitoring cruises, benthic samples are collected separately and fish samples are obtained from professional fishermen (commercial fishing). The collection and analysis of samples are guided by the HELCOM MORS guidelines and the radiation monitoring sub-programme of the national environmental monitoring programme. Water samples from the Baltic Sea are collected from five stationary stations agreed in the framework of the HELCOM marine monitoring programme. The concentration of Cs-137 and K-40 in the surface water samples of the Gulf of Finland is determined by gamma spectrometry.
Features	Aquaculture – marine, including infrastructure	Fish and shellfish harvesting (professional, recreational)	Hunting and collecting for other purposes	Marine plant harvesting	Extraction of minerals (rock, metal ores, gravel, sand, shell)	Extraction of oil and gas, including infrastructure	Extraction of water	Military operations (subject to Article 2(2))	Transmission of electricity and communications (cables)	Renewable energy generation (wind, wave and tidal power), including infrastructure	Research, survey and educational activities	Coastal defence and flood protection	Offshore structures (other than for oil/gas/renewables)	Restructuring of seabed morphology, including dredging and depositing of materials	Tourism and leisure activities	Tourism and leisure infrastructure	Transport infrastructure	Transport – shipping	Waste treatment and disposal	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)	Input of nutrients – diffuse sources, point sources, atmospheric deposition	Input of anthropogenic sound (impulsive, continuous)	Benthic-feeding birds	Grazing birds	Pelagic-feeding birds	Surface-feeding birds	Wading birds	Benthic-feeding birds	Grazing birds	Pelagic-feeding birds	Surface-feeding birds	Surface-feeding birds	Wading birds	Benthic-feeding birds	Grazing birds	Pelagic-feeding birds	Surface-feeding birds	Surface-feeding birds	Wading birds	Coastal ecosystems	Coastal ecosystems	Coastal ecosystems	Adverse effects on species or habitats	Input of nutrients – diffuse sources, point sources, atmospheric deposition	Input of other substances (e.g. synthetic substances, non-synthetic substances, radionuclides) – diffuse sources, point sources, atmospheric deposition, acute events	Contaminants - non UPBT substances	Contaminants - UPBT substances	Contaminants - non UPBT substances	Contaminants - UPBT substances	Acute pollution events	Input of litter (solid waste matter, including micro-sized litter)	Acute pollution events	Adverse effects on species or habitats	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - non UPBT substances	Contaminants - UPBT substances	Contaminants - non UPBT substances
Elements	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Not Applicable	Aythya ferina Aythya fuligula Melanitta fusca Somateria mollissima	Anser anser Branta leucopsis Cygnus olor Fulica atra	Mergus merganser Mergus serrator Phalacrocorax carbo Podiceps cristatus	Haliaeetus albicilla Hydrocoloeus minutus Hydroprogne caspia Larus argentatus Larus canus Larus fuscus graellsii Larus fuscus intermedius Larus marinus Larus ridibundus Sterna albifrons Sterna hirundo Sterna paradisaea Sterna sandvicensis	Arenaria interpres Calidris alpina Charadrius hiaticula Haematopus ostralegus Recurvirostra avosetta Tadorna tadorna	Aythya ferina Aythya fuligula Melanitta fusca Somateria mollissima	Anser anser Branta leucopsis Cygnus olor Fulica atra	Mergus merganser Mergus serrator Phalacrocorax carbo Podiceps cristatus	Haliaeetus albicilla	Hydrocoloeus minutus Hydroprogne caspia Larus argentatus Larus canus Larus fuscus graellsii Larus fuscus intermedius Larus marinus Larus ridibundus Sterna albifrons Sterna hirundo Sterna paradisaea Sterna sandvicensis	Arenaria interpres Calidris alpina Charadrius hiaticula Haematopus ostralegus Recurvirostra avosetta Tadorna tadorna	Aythya ferina Aythya fuligula Melanitta fusca Somateria mollissima	Anser anser Branta leucopsis Cygnus olor Fulica atra	Mergus merganser Mergus serrator Phalacrocorax carbo Podiceps cristatus	Haliaeetus albicilla	Hydrocoloeus minutus Hydroprogne caspia Larus argentatus Larus canus Larus fuscus graellsii Larus fuscus intermedius Larus marinus Larus ridibundus Sterna albifrons Sterna hirundo Sterna paradisaea Sterna sandvicensis	Arenaria interpres Calidris alpina Charadrius hiaticula Haematopus ostralegus Recurvirostra avosetta Tadorna tadorna	Apex predators	Apex predators	Apex predators	Haliaeetus albicilla	Not Applicable	Not Applicable	2,3-dimethyl-phenol 2,6-Dimethyl phenol 2-methyl-phenol 3,4-dimethyl-phenol 3,5-Dimethyl phenol Alachlor Anthracene Arsenic and its compounds Atrazine Barium Brominated diphenylethers (congener numbers 28, 47, 66, 85, 99, 100, 153, 154, and 183) Cadmium and its compounds Chlorfenvinphos Chloroalkanes C10-13 Chlorpyrifos Chromium and its compounds Copper and its compounds DDT, p,p' Di(2-ethylhexyl)phthalate (DEHP) Diuron Endosulfan Fluoranthene Hexachlorocyclohexane (α-, β-, γ-HCH) Isoproturon Lead and its compounds Naphthalene Nickel and its compounds Nonylphenol Octylphenol Pentachlorophenol Petroleum hydrocarbons Phenol Resorcinol Simazine Tin and its compounds Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p') Total cyclodiene pesticides (aldrin + dieldrin + endrin + isodrin) Trichlorobenzenes (all isomers) Trifluralin Zinc and its compounds m-/p-Cresol	Hexabromocyclododecanes (HBCDD) Mercury and its compounds Perfluorooctane sulfonic acid (PFOS) and its derivatives Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene) Tributyltin-cation	1,2-Dichloroethane 2,3-dimethyl-phenol 2,6-Dimethyl phenol 2-methyl-phenol 3,4-dimethyl-phenol 3,5-Dimethyl phenol Alachlor Arsenic and its compounds Atrazine Barium Benzene Cadmium and its compounds Chlorfenvinphos Chlorpyrifos Chromium and its compounds Copper and its compounds DDT, p,p' Di(2-ethylhexyl)phthalate (DEHP) Dichloromethane Diuron Endosulfan Hexachlorobenzene Isoproturon Lead and its compounds Meta xylene + para xylene Nickel and its compounds Nonylphenol Octylphenol Pentachlorobenzene Pentachlorophenol Petroleum hydrocarbons Phenol Resorcinol Simazine Tin and its compounds Toluene Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p') Total cyclodiene pesticides (aldrin + dieldrin + endrin + isodrin) Trichlorobenzenes (all isomers) Trichloromethane Trifluralin Zinc and its compounds m-/p-Cresol o-Xylene	Mercury and its compounds Perfluorooctane sulfonic acid (PFOS) and its derivatives Tributyltin-cation	Not Applicable	Not Applicable	Not Applicable	Not Applicable	2,3-dimethyl-phenol 2,6-Dimethyl phenol 2-methyl-phenol 3,4-dimethyl-phenol 3,5-Dimethyl phenol Alachlor Anthracene Atrazine Brominated diphenylethers (congener numbers 28, 47, 66, 85, 99, 100, 153, 154, and 183) Chlorfenvinphos Chlorpyrifos DDT, p,p' Di(2-ethylhexyl)phthalate (DEHP) Diuron Endosulfan Fluoranthene Hexachlorocyclohexane (α-, β-, γ-HCH) Isoproturon Naphthalene Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) Nonylphenol Octylphenol Pentachlorobenzene Pentachlorophenol Phenol Resorcinol Simazine Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p') Total cyclodiene pesticides (aldrin + dieldrin + endrin + isodrin) Trifluralin m-/p-Cresol	Arsenic and its compounds Barium Chromium and its compounds	Cadmium and its compounds Copper and its compounds Lead and its compounds Nickel and its compounds Tin and its compounds Zinc and its compounds	Dioxins and dioxin-like compounds (7 PCDDs + 10 PCDFs + 12 PCB-DLs) Hexabromocyclododecanes (HBCDD) Mercury and its compounds Perfluorooctane sulfonic acid (PFOS) and its derivatives Total PAHs (Benzo(a)pyrene, Benzo(b)fluoranthene, Benzo(k)fluoranthene, Benzo(ghi)perylene, Indeno(1,2,3-cd)pyrene) Tributyltin-cation	Cesium-137 K-40
GES criteria	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	NotRelevan	D1C2	D1C2	D1C2	D1C2	D1C2	D1C3	D1C3	D1C3	D1C3	D1C3	D1C3	D1C4	D1C4	D1C4	D1C4	D1C4	D1C4	D4C1	D4C2	D4C4	D8C2	D5C1	D8C1	D8C1	D8C1	D8C1	D8C1	D8C3	D10C4	D8C3	D8C4	D8C1	D8C1	D8C1	D8C1	D8C1
Parameters	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	AMO-WC Amount on coastline Amount on seabed Other	Other	Level of sound Other	Abundance (number of individuals)	Abundance (number of individuals)	Abundance (number of individuals)	Abundance (number of individuals)	Abundance (number of individuals)	Breeding success	Breeding success	Breeding success	Breeding success Brood size	Breeding success	Breeding success	Distribution (pattern) Distribution (range)	Distribution (pattern) Distribution (range)	Distribution (pattern) Distribution (range)	Distribution (pattern)	Distribution (pattern) Distribution (range)	Distribution (pattern) Distribution (range)	Other	Abundance (number of individuals) Other	Other	Other	Concentration in water Other	Concentration in water Other	Concentration in sediment (total)	Concentration in sediment (total)	Concentration in water	Concentration in water	Extent Other	Other	Other	Other	Concentration in biota – muscle Other	Concentration in biota – liver Other	Concentration in biota – liver Other	Concentration in biota – muscle Other	Concentration in biota (total) Concentration in sediment (total) Concentration in water
Parameter Other	Production (tonnes); Area; Nutrient load	Catch; By-catch	Number of individuals hunted by species (waterbird	Amount (kg); Area	Mining volume; Mining area; Area pressure index	Pipe length (area); Area pressure index	Volume	Number of explosions; Number of trainings; Trainin	Cable length (area); Area pressure index	Area; Area pressure index	Volume of costs on marine researches; Number of re	Length of defence structure; Coastline pressure in	Area of structure; Area pressure index	Soil volume; Extent; Area pressure index	Number of vacationists; Number of visits; People's	Number of marinas per coastline; Length of beach	Area; Volume (goods and passengers); Number of loa	Number of ships (incl. number of ships complying w	Areas of dumping sites and volume of dumped materi	Pollution load (tonnes/year) - Hg, Cd, Cu, Pb, Zn,	Amount in sediments; Litter type and material	Pollution load (tonnes/year) - N, P, BHT5	Number of disturbance days - Impulsive underwater																		Species composition	Distribution (pattern); Distribution (range)	Breeding success	Productivity; Brood size; Breeding success	Water level; Temperature; Freshwater input rates f	Load of contaminant					Amount on water surface	Number of individuals, which are adversely affecte	Presence	Abundance (number of dead individuals, ind/km); Ag	Concentration in biota – muscle - Perca fluviatili	Concentration in biota – muscle - Perca fluviatili	Concentration in biota – liver - Perca fluviatilis	Concentration in biota – muscle - Perca fluviatili
Spatial scope	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD)	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) EEZ (or similar) Territorial waters	Coastal waters (WFD) Territorial waters
Marine reporting units	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB BAL-EE-GF BAL-EE-GR BAL-EE-NBP	BAL-EE-AA BAL-EE-EGB-OFFSHORE BAL-EE-GF-OFFSHORE BAL-EE-GR-OFFSHORE BAL-EE-NBP-OFFSHORE BAL-EGB-EE-EEEE_11 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-NBP-EE-EEEE_10	BAL-EE-AA BAL-EE-EGB-OFFSHORE BAL-EE-GF-OFFSHORE BAL-EE-GR-OFFSHORE BAL-EE-NBP-OFFSHORE BAL-EGB-EE-EEEE_11 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-NBP-EE-EEEE_10	BAL-EE-AA BAL-EE-EGB-OFFSHORE BAL-EE-GF-OFFSHORE BAL-EE-GR-OFFSHORE BAL-EE-NBP-OFFSHORE BAL-EGB-EE-EEEE_11 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-NBP-EE-EEEE_10	BAL-EE-AA BAL-EE-EGB-OFFSHORE BAL-EE-GF-OFFSHORE BAL-EE-GR-OFFSHORE BAL-EE-NBP-OFFSHORE BAL-EGB-EE-EEEE_11 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-NBP-EE-EEEE_10	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-EE-AA	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GF-EE-ICES_SD_32 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GF-EE-ICES_SD_32 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GF-EE-ICES_SD_32 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EGB-EE-EEEE_11 BAL-EGB-EE-ICES_SD_28-2 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_02 BAL-GF-EE-EEEE_03 BAL-GF-EE-EEEE_05 BAL-GF-EE-EEEE_06 BAL-GF-EE-ICES_SD_32 BAL-GR-EE-EEEE_07 BAL-GR-EE-EEEE_08 BAL-GR-EE-EEEE_09 BAL-GR-EE-EEEE_13 BAL-GR-EE-EEEE_14 BAL-GR-EE-EEEE_16 BAL-GR-EE-EEEE_17 BAL-GR-EE-EEEE_18 BAL-GR-EE-EEEE_19 BAL-GR-EE-ICES_SD_28-1 BAL-NBP-EE-EEEE_10	BAL-AS-EE-ICES_SD_29 BAL-EE-AA BAL-EE-GF-OFFSHORE BAL-EE-NBP-OFFSHORE BAL-EGB-EE-ICES_SD_28-2 BAL-GF-EE-EEEE_01 BAL-GF-EE-EEEE_06 BAL-GF-EE-ICES_SD_32 BAL-GR-EE-ICES_SD_28-1
Temporal scope (start date - end date)	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	2015-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1957-9999	1924-9999	1924-9999	2014-9999	2014-9999	2010-9999	2010-9999	2000-9999	1992-9999	1992-9999	1992-9999	1994-9999	1994-9999	1994-9999	1994-9999	1997-9999
Monitoring frequency	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Other	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Yearly	Other	Other	Yearly	Yearly	Yearly	Yearly	Continually	Other	Other	Other	Yearly	Yearly	Yearly	Yearly	Yearly
Monitoring type	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Administrative data collection	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	Visual observation	In-situ sampling land/beach Numerical modelling	In-situ sampling land/beach Numerical modelling	In-situ sampling coastal In-situ sampling offshore	In-situ sampling coastal In-situ sampling offshore	In-situ sampling coastal In-situ sampling offshore	In-situ sampling coastal In-situ sampling offshore	Remote satellite imagery Remote surveillance	Visual observation	Visual observation	Visual observation	In-situ sampling coastal In-situ sampling offshore	In-situ sampling coastal In-situ sampling offshore	In-situ sampling coastal In-situ sampling offshore	In-situ sampling coastal In-situ sampling offshore	In-situ sampling coastal In-situ sampling offshore
Monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	OSPAR CEMP Guidelines for Monitoring and Assessment of loud, low and mid-frequency impulsive sound sources in the OSPAR Maritime Region Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	Other monitoring method	HELCOM Guidelines for the annual and periodical compilation and reporting of waterborne pollution inputs to the Baltic Sea (PLC-Water) Other monitoring method	HELCOM Guidelines for the annual and periodical compilation and reporting of waterborne pollution inputs to the Baltic Sea (PLC-Water) Other monitoring method	HELCOM Guideline for the determination of heavy metals in sediment HELCOM Guidelines for determination of PAH in sediment HELCOM Guidelines for determination of chlorinated hydrocarbons in sediment Other monitoring method WFD Guidance document n.° 25 - Chemical Monitoring of Sediment and Biota	HELCOM Guideline for the determination of heavy metals in sediment HELCOM Guidelines for determination of PAH in sediment HELCOM Guidelines for determination of chlorinated hydrocarbons in sediment Other monitoring method WFD Guidance document n.° 25 - Chemical Monitoring of Sediment and Biota	HELCOM Guideline on the determination of perfluoroalkylated substances (PFAS) in seawater HELCOM Guidelines for determination of POPs in seawater Other monitoring method WFD Guidance document n.° 19 - Monitoring under the Water Framework Directive (surface water chemical monitoring)	HELCOM Guideline on the determination of perfluoroalkylated substances (PFAS) in seawater HELCOM Guidelines for determination of POPs in seawater Other monitoring method WFD Guidance document n.° 19 - Monitoring under the Water Framework Directive (surface water chemical monitoring)	HELCOM Manual on co-operation in response to marine pollution	Other monitoring method	Other monitoring method	Other monitoring method	WFD Guidance document n.° 25 - Chemical Monitoring of Sediment and Biota WFD Guidance document n.° 32 - Biota Monitoring	WFD Guidance document n.° 25 - Chemical Monitoring of Sediment and Biota WFD Guidance document n.° 32 - Biota Monitoring	WFD Guidance document n.° 25 - Chemical Monitoring of Sediment and Biota WFD Guidance document n.° 32 - Biota Monitoring	WFD Guidance document n.° 25 - Chemical Monitoring of Sediment and Biota WFD Guidance document n.° 32 - Biota Monitoring	HELCOM Guidelines for monitoring of radioactive substances Other monitoring method
Monitoring method other	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	There is no separate monitoring for the programme, the administrative data collection is performed and based on information from databases, maps, plans, environmental permits and their reporting and controls, etc. Estonian maritime spatial plan. The frequency of monitoring depends on activity: from annually to once per the 6-year period.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	The monitoring is based on the method and proposals described by A. Leito in "Väikeste meresaarte haudelindude (merelindude) seire senine kogemus ning ettepanekud ühtse riikliku seireprogrammi rakendamiseks Eestis" ("Experience of monitoring of breeding birds on small maritime islands and proposals for the implementation of the common national monitoring programme in Estonia") in 2008. Monitoring is carried out on selected small islands (island groups) and nesting sites of white-tailed eagle (on land up to 20 km from seashore). Breeding pairs, as well as a monitoring-year nest and/or pair or single bird, are used as counting units. The number of breeding species on the island Is counted. The indexes for the assessment of the abundance trend are based on whole gathered data from small islands. For assessment of white-tailed eagle productivity, the nesting sites are monitored and the number of occupied nests and fledglings are fixed. The nests are usually being controlled in late May-early July. The productivity is counted as the mean number of fledglings per occupied nest. The monitoring on small islands is carried out every year on sites with continuous monitoring and where cormorant, Sandwich tern and Caspian tern colonies are monitored continuously, other sites are monitored in rotation – at least once per 6-year period. The monitoring of white-tailed eagle nesting sites is done in rotation, and all nests are controlled at least once every 3 years.	WMO no 168, national regulations	WMO no 168, national regulations	Commission Directive 2009/90/EC (technical specifications for chemical analysis and monitoring of water status)	Commission Directive 2009/90/EC (technical specifications for chemical analysis and monitoring of water status)	Commission Directive 2009/90/EC (technical specifications for chemical analysis and monitoring of water status); national regulation nr 35 of the minister of the environment.	Commission Directive 2009/90/EC (technical specifications for chemical analysis and monitoring of water status); national regulation nr 35 of the minister of the environment.		National (https://www.keskkonnaagentuur.ee/sites/default/files/seiretoo_ankeet_randa_uhutud_linnud_2020.docx; https://kese.envir.ee/kese/downloadReportFile.action?fileUid=12394806&monitoringWorkUid=1207453) and HELCOM/ICES JWGBird Group agreed methods (the monitoring time is not agreed).	National (https://www.keskkonnaagentuur.ee/sites/default/files/seiretoo_ankeet_randa_uhutud_linnud_2020.docx; https://kese.envir.ee/kese/downloadReportFile.action?fileUid=12394806&monitoringWorkUid=1207453) and HELCOM/ICES JWGBird Group agreed methods (the monitoring time is not agreed).	National (https://www.keskkonnaagentuur.ee/sites/default/files/seiretoo_ankeet_randa_uhutud_linnud_2020.docx; https://kese.envir.ee/kese/downloadReportFile.action?fileUid=12394806&monitoringWorkUid=1207453) and HELCOM/ICES JWGBird Group agreed methods (the monitoring time is not agreed).					2000/473/Euratom: Commission recommendation of 8 June 2000 on the application of Article 36 of the Euratom Treaty concerning the monitoring of the levels of radioactivity in the environment for the purpose of assessing the exposure of the population as a whole.
Quality control	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	Data quality control systems of relevant data sources.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	National, ie observations are carried out by professional observers and quality control is performed when entering data into databases.	The quality is assured by following the HELCOM PLC guidelines, standards EVS-EN ISO 11905-1, EVS-EN ISO 11732, EVS-EN ISO 13395, ISO 15681-2, EN ISO/IEC-17025 and accreditation of experts and persons by whom the monitoring is performed.	The quality is assured by following the HELCOM PLC guidelines, standards EVS-EN ISO 11905-1, EVS-EN ISO 11732, EVS-EN ISO 13395, ISO 15681-2, EN ISO/IEC-17025 and accreditation of experts and persons by whom the monitoring is performed.	The quality is assured by filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025, following the guidance documents, national regulations' requirements and standards EVS-EN 25667 (EVS-EN 25667-1 and EVS-EN 25667-2), EVS-EN ISO 5667-12, EVS-EN ISO 5667-15, EVS-EN ISO 5667-19. When the data are being uploaded to the database, QA/QC controls are performed.	The quality is assured by filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025, following the guidance documents, national regulations' requirements and standards EVS-EN 25667 (EVS-EN 25667-1 and EVS-EN 25667-2), EVS-EN ISO 5667-12, EVS-EN ISO 5667-15, EVS-EN ISO 5667-19. When the data are being uploaded to the database, QA/QC controls are performed.	The quality is assured by filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025, following the guidance documents, national regulations' requirements and standards EVS-EN 25667 (EVS-EN 25667-1 and EVS-EN 25667-2), EVS-EN ISO 5667 (parts 3, 4, 9, 10, 11, 13 and 15). When the data are being uploaded to the database, QA/QC controls are performed.	The quality is assured by filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025, following the guidance documents, national regulations' requirements and standards EVS-EN 25667 (EVS-EN 25667-1 and EVS-EN 25667-2), EVS-EN ISO 5667 (parts 3, 4, 9, 10, 11, 13 and 15). When the data are being uploaded to the database, QA/QC controls are performed.	The quality is ensured by following the HELCOM RESPONSE guidance materials.	The observations are conducted by professional observers and data quality control is performed while submitting into the database. Also HELCOM/ICES JWGBirg Group agreed method is used.	The observations are conducted by professional observers and data quality control is performed while submitting into the database. Also HELCOM/ICES JWGBirg Group agreed method is used.	The observations are conducted by professional observers and data quality control is performed while submitting into the database. Also HELCOM/ICES JWGBirg Group agreed method is used.	The quality is assured by filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025 and following the guidance documents and national regulations' requirements. Supplementary data analysed (biological data, lipid wight etc.) provides data normalisation.	The quality is assured by filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025 and following the guidance documents and national regulations' requirements. Supplementary data analysed (biological data, lipid wight etc.) provides data normalisation.	The quality is assured by filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025 and following the guidance documents and national regulations' requirements. Supplementary data analysed (biological data, lipid wight etc.) provides data normalisation.	The quality is assured by filling of general requirements for the competence of testing and calibration laboratories according to ISO/IEC 17025 and following the guidance documents and national regulations' requirements. Supplementary data analysed (biological data, lipid wight etc.) provides data normalisation.	The quality is ensured by following the HELCOM recommendation 26/3 and HELCOM monitoring guidance. EU member states have implemented a common methodology for environmental radiation monitoring, which is described in the European Commission's recommendation 2000/473/Euratom. In addition, the quality is assured by the accreditation of experts and persons by whom the monitoring is performed and database, QA/QC requirements.
Data management	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	The data are compiled from different databases of different institutions. The compilation and collection of data are coordinated by the Marine Environment Department of the Ministry of the Environment.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	Data are annually reported to the national environmental monitoring database KESE (by 1 March). Data collection into the regional database for assessment purposes is coordinated by the HELCOM/ICES JWGBird Group.	The hydrochemical data are yearly reported to the national environmental monitoring database KESE. The hydrological data are uploaded quarterly to the database WISKI. Water-borne pollution loads are reported to HELCOM PLC database annually.	The hydrochemical data are yearly reported to the national environmental monitoring database KESE. The hydrological data are uploaded quarterly to the database WISKI. Water-borne pollution loads are reported to HELCOM PLC database annually.	The data are yearly reported to the national environmental monitoring database KESE (by 1 March), ICES (HELCOM). The data gathered from environmental permits are stored at database KOTKAS.	The data are yearly reported to the national environmental monitoring database KESE (by 1 March), ICES (HELCOM). The data gathered from environmental permits are stored at database KOTKAS.	The data are yearly reported to the national environmental monitoring database KESE and ICES (HELCOM). The data gathered from environmental permits are stored at database KOTKAS.	The data are yearly reported to the national environmental monitoring database KESE and ICES (HELCOM). The data gathered from environmental permits are stored at database KOTKAS.	The data are stored at Joint Rescue Coordination Centre - JRCC Tallinn.	Data and reports are yearly submitted to the national environmental monitoring database KESE.	Data and reports are yearly submitted to the national environmental monitoring database KESE.	Data and reports are yearly submitted to the national environmental monitoring database KESE.	Data are yearly reported to the national environmental monitoring database KESE (by 1 March), ICES (HELCOM Combine) and Eionet.	Data are yearly reported to the national environmental monitoring database KESE (by 1 March), ICES (HELCOM Combine) and Eionet.	Data are yearly reported to the national environmental monitoring database KESE (by 1 March), ICES (HELCOM Combine) and Eionet.	Data are yearly reported to the national environmental monitoring database KESE (by 1 March), ICES (HELCOM Combine) and Eionet.	The data collected during the monitoring are stored at the Environmental Board but also submitted to the national monitoring database KESE. Monitoring data are reported to the HELCOM Combine database as well (and to the Helcom MORS working group).
Data 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egevused/kalandus/harrastuspuuk/statistika-ja-uuringud,https://www.envir.ee/et/kalanduse-uuringud-ja-aruanded,https://www.etis.ee/,https://www.keskkonnaagentuur.ee/et/kuttimine,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/jahindus/operatiivsed-kuttimisandmed,https://www.marinetraffic.com/en/ais/,https://www.sadamaregister.ee/,https://www.terviseamet.ee/et/keskkonnatervis/ettevotjale-ja-kohalikule-omavalitsusele/supluskohad-ja-ujulad/suplusvee-profiilid,https://xgis.maaamet.ee/xgis2/page/app/maainfo,https://xgis.maaamet.ee/xgis2/page/app/merekaart	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	http://www.ilmateenistus.ee/siseveed/ajaloolised-vaatlusandmed/vooluhulgad/,https://kese.envir.ee	http://www.ilmateenistus.ee/siseveed/ajaloolised-vaatlusandmed/vooluhulgad/,https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	http://maps.helcom.fi/website/mapservice/	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee	https://kese.envir.ee,https://www.keskkonnaamet.ee/et/eesmargid-tegevused/kiirgus/aruanded-ja-uuringud
Related indicator/name																								Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity	Abundance of waterbirds in the breeding season White tailed eagle productivity			-cd)pyrene 1' 2 3 3 3'‐tetramethylbutyl)‐phenol) 3-dimethyl-phenol 4-dimethyl-phenol 5-Dimethyl phenol 6-Dimethyl phenol 2,3-dimethyl-phenol 2,6-Dimethyl phenol 2-methyl-phenol (O-Cresol) 3,4-dimethyl-phenol 3,5-Dimethyl phenol Alachlor Anthracene Arsenic and its compounds Atrazine Barium Benzo(a)pyrene Benzo(b)fluoranthene Benzo(g,h,i)perylene Benzo(k)fluoranthene Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154) Cadmium and its compounds Chlorfenvinphos Chloroalkanes C10-13 Chlorpyrifos Chromium and its compounds Copper and its compounds DDT, p,p' Di(2-ethylhexyl)phthalate (DEHP) Diuron Endosulfan Fluoranthene Hexachlorocyclohexane Indeno(1,2,3,-cd)pyrene Isoproturon Lead and its compounds Mercury and its compounds Naphthalene Nickel and its compounds Nonylphenol Octylphenol (4‐(1,1',3,3'‐tetramethylbutyl)‐phenol) Pentachlorophenol Petroleum hydrocarbons (C10-C40) Phenol Resorcinol Simazine Tin and its compounds Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p') Total cyclodiene pesticides (aldrin + dieldrin + endrin + isodrin) Tributyltin-cation Trichlorobenzenes (all isomers) Trifluralin Zinc and its compounds m-/p-Cresol BALEED8C1.65 BALEED8C1.66 h i)perylene p' p' + DDD, p p' + DDE, p p' + DDT, o p')	-cd)pyrene 1' 2 3 3 3'‐tetramethylbutyl)‐phenol) 3-dimethyl-phenol 4-dimethyl-phenol 5-Dimethyl phenol 6-Dimethyl phenol 2,3-dimethyl-phenol 2,6-Dimethyl phenol 2-methyl-phenol (O-Cresol) 3,4-dimethyl-phenol 3,5-Dimethyl phenol Alachlor Anthracene Arsenic and its compounds Atrazine Barium Benzo(a)pyrene Benzo(b)fluoranthene Benzo(g,h,i)perylene Benzo(k)fluoranthene Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154) Cadmium and its compounds Chlorfenvinphos Chloroalkanes C10-13 Chlorpyrifos Chromium and its compounds Copper and its compounds DDT, p,p' Di(2-ethylhexyl)phthalate (DEHP) Diuron Endosulfan Fluoranthene Hexachlorocyclohexane Indeno(1,2,3,-cd)pyrene Isoproturon Lead and its compounds Mercury and its compounds Naphthalene Nickel and its compounds Nonylphenol Octylphenol (4‐(1,1',3,3'‐tetramethylbutyl)‐phenol) Pentachlorophenol Petroleum hydrocarbons (C10-C40) Phenol Resorcinol Simazine Tin and its compounds Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p') Total cyclodiene pesticides (aldrin + dieldrin + endrin + isodrin) Tributyltin-cation Trichlorobenzenes (all isomers) Trifluralin Zinc and its compounds m-/p-Cresol BALEED8C1.65 BALEED8C1.66 h i)perylene p' p' + DDD, p p' + DDE, p p' + DDT, o p')	1' 2-Dichloroethane 3 3'‐tetramethylbutyl)‐phenol) 3-dimethyl-phenol 4-dimethyl-phenol 5-Dimethyl phenol 6-Dimethyl phenol 1,2-Dichloroethane 2,3-dimethyl-phenol 2,6-Dimethyl phenol 2-methyl-phenol (O-Cresol) 3,4-dimethyl-phenol 3,5-Dimethyl phenol Alachlor Arsenic and its compounds Atrazine Barium Benzene Cadmium and its compounds Chlorfenvinphos Chlorpyrifos Chromium and its compounds Copper and its compounds DDT, p,p' Di(2-ethylhexyl)phthalate (DEHP) Dichloromethane Diuron Endosulfan Hexachlorobenzene Isoproturon Lead and its compounds Mercury and its compounds Meta xylene + para xylene Nickel and its compounds Nonylphenol Octylphenol (4‐(1,1',3,3'‐tetramethylbutyl)‐phenol) Pentachlorobenzene Pentachlorophenol Petroleum hydrocarbons (C10-C40) Phenol Resorcinol Simazine Tin and its compounds Toluene Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p') Total cyclodiene pesticides (aldrin + dieldrin + endrin + isodrin) Tributyltin-cation Trichlorobenzenes (all isomers) Trichloromethane Trifluralin Zinc and its compounds m-/p-Cresol o-Xylene BALEED8C1.66 p' p' + DDD, p p' + DDE, p p' + DDT, o p')	1' 2-Dichloroethane 3 3'‐tetramethylbutyl)‐phenol) 3-dimethyl-phenol 4-dimethyl-phenol 5-Dimethyl phenol 6-Dimethyl phenol 1,2-Dichloroethane 2,3-dimethyl-phenol 2,6-Dimethyl phenol 2-methyl-phenol (O-Cresol) 3,4-dimethyl-phenol 3,5-Dimethyl phenol Alachlor Arsenic and its compounds Atrazine Barium Benzene Cadmium and its compounds Chlorfenvinphos Chlorpyrifos Chromium and its compounds Copper and its compounds DDT, p,p' Di(2-ethylhexyl)phthalate (DEHP) Dichloromethane Diuron Endosulfan Hexachlorobenzene Isoproturon Lead and its compounds Mercury and its compounds Meta xylene + para xylene Nickel and its compounds Nonylphenol Octylphenol (4‐(1,1',3,3'‐tetramethylbutyl)‐phenol) Pentachlorobenzene Pentachlorophenol Petroleum hydrocarbons (C10-C40) Phenol Resorcinol Simazine Tin and its compounds Toluene Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p') Total cyclodiene pesticides (aldrin + dieldrin + endrin + isodrin) Tributyltin-cation Trichlorobenzenes (all isomers) Trichloromethane Trifluralin Zinc and its compounds m-/p-Cresol o-Xylene BALEED8C1.66 p' p' + DDD, p p' + DDE, p p' + DDT, o p')					-cd)pyrene 1' 2 3 3 3'‐tetramethylbutyl)‐phenol) 3-dimethyl-phenol 4-dimethyl-phenol 5-Dimethyl phenol 6-Dimethyl phenol 2,3-dimethyl-phenol 2,6-Dimethyl phenol 2-methyl-phenol (O-Cresol) 3,4-dimethyl-phenol 3,5-Dimethyl phenol Alachlor Anthracene Arsenic and its compounds Atrazine Barium Benzo(a)pyrene Benzo(b)fluoranthene Benzo(g,h,i)perylene Benzo(k)fluoranthene Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154) Cadmium and its compounds Chlorfenvinphos Chlorpyrifos Chromium and its compounds Copper and its compounds DDT, p,p' Di(2-ethylhexyl)phthalate (DEHP) Diuron Endosulfan Fluoranthene Hexachlorocyclohexane Indeno(1,2,3,-cd)pyrene Isoproturon Lead and its compounds Mercury and its compounds Naphthalene Nickel and its compounds Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) Nonylphenol Octylphenol (4‐(1,1',3,3'‐tetramethylbutyl)‐phenol) Pentachlorobenzene Pentachlorophenol Phenol Resorcinol Simazine Tin and its compounds Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p') Total cyclodiene pesticides (aldrin + dieldrin + endrin + isodrin) Tributyltin-cation Trifluralin Zinc and its compounds m-/p-Cresol BALEED8C1.64 BALEED8C1.65 BALEED8C1.66 h i)perylene p' p' + DDD, p p' + DDE, p p' + DDT, o p')	-cd)pyrene 1' 2 3 3 3'‐tetramethylbutyl)‐phenol) 3-dimethyl-phenol 4-dimethyl-phenol 5-Dimethyl phenol 6-Dimethyl phenol 2,3-dimethyl-phenol 2,6-Dimethyl phenol 2-methyl-phenol (O-Cresol) 3,4-dimethyl-phenol 3,5-Dimethyl phenol Alachlor Anthracene Arsenic and its compounds Atrazine Barium Benzo(a)pyrene Benzo(b)fluoranthene Benzo(g,h,i)perylene Benzo(k)fluoranthene Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154) Cadmium and its compounds Chlorfenvinphos Chlorpyrifos Chromium and its compounds Copper and its compounds DDT, p,p' Di(2-ethylhexyl)phthalate (DEHP) Diuron Endosulfan Fluoranthene Hexachlorocyclohexane Indeno(1,2,3,-cd)pyrene Isoproturon Lead and its compounds Mercury and its compounds Naphthalene Nickel and its compounds Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) Nonylphenol Octylphenol (4‐(1,1',3,3'‐tetramethylbutyl)‐phenol) Pentachlorobenzene Pentachlorophenol Phenol Resorcinol Simazine Tin and its compounds Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p') Total cyclodiene pesticides (aldrin + dieldrin + endrin + isodrin) Tributyltin-cation Trifluralin Zinc and its compounds m-/p-Cresol BALEED8C1.64 BALEED8C1.65 BALEED8C1.66 h i)perylene p' p' + DDD, p p' + DDE, p p' + DDT, o p')	-cd)pyrene 1' 2 3 3 3'‐tetramethylbutyl)‐phenol) 3-dimethyl-phenol 4-dimethyl-phenol 5-Dimethyl phenol 6-Dimethyl phenol 2,3-dimethyl-phenol 2,6-Dimethyl phenol 2-methyl-phenol (O-Cresol) 3,4-dimethyl-phenol 3,5-Dimethyl phenol Alachlor Anthracene Arsenic and its compounds Atrazine Barium Benzo(a)pyrene Benzo(b)fluoranthene Benzo(g,h,i)perylene Benzo(k)fluoranthene Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154) Cadmium and its compounds Chlorfenvinphos Chlorpyrifos Chromium and its compounds Copper and its compounds DDT, p,p' Di(2-ethylhexyl)phthalate (DEHP) Diuron Endosulfan Fluoranthene Hexachlorocyclohexane Indeno(1,2,3,-cd)pyrene Isoproturon Lead and its compounds Mercury and its compounds Naphthalene Nickel and its compounds Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) Nonylphenol Octylphenol (4‐(1,1',3,3'‐tetramethylbutyl)‐phenol) Pentachlorobenzene Pentachlorophenol Phenol Resorcinol Simazine Tin and its compounds Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p') Total cyclodiene pesticides (aldrin + dieldrin + endrin + isodrin) Tributyltin-cation Trifluralin Zinc and its compounds m-/p-Cresol BALEED8C1.64 BALEED8C1.65 BALEED8C1.66 h i)perylene p' p' + DDD, p p' + DDE, p p' + DDT, o p')	-cd)pyrene 1' 2 3 3 3'‐tetramethylbutyl)‐phenol) 3-dimethyl-phenol 4-dimethyl-phenol 5-Dimethyl phenol 6-Dimethyl phenol 2,3-dimethyl-phenol 2,6-Dimethyl phenol 2-methyl-phenol (O-Cresol) 3,4-dimethyl-phenol 3,5-Dimethyl phenol Alachlor Anthracene Arsenic and its compounds Atrazine Barium Benzo(a)pyrene Benzo(b)fluoranthene Benzo(g,h,i)perylene Benzo(k)fluoranthene Brominated diphenylethers (congener numbers 28, 47, 99, 100, 153 and 154) Cadmium and its compounds Chlorfenvinphos Chlorpyrifos Chromium and its compounds Copper and its compounds DDT, p,p' Di(2-ethylhexyl)phthalate (DEHP) Diuron Endosulfan Fluoranthene Hexachlorocyclohexane Indeno(1,2,3,-cd)pyrene Isoproturon Lead and its compounds Mercury and its compounds Naphthalene Nickel and its compounds Non-dioxin like PCB (sum of 6 PCB: 28, 52, 101, 138, 153 and 180) Nonylphenol Octylphenol (4‐(1,1',3,3'‐tetramethylbutyl)‐phenol) Pentachlorobenzene Pentachlorophenol Phenol Resorcinol Simazine Tin and its compounds Total DDT (DDT, p,p' + DDT, o,p' + DDE, p,p' + DDD, p,p') Total cyclodiene pesticides (aldrin + dieldrin + endrin + isodrin) Tributyltin-cation Trifluralin Zinc and its compounds m-/p-Cresol BALEED8C1.64 BALEED8C1.65 BALEED8C1.66 h i)perylene p' p' + DDD, p p' + DDE, p p' + DDT, o p')	Cesium-137
Contact																								Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Meelis Leivits, Estonian Environment Agency, meelis.leivits@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Maritime security centre (Joint Rescue Coordination Centre - JRCC Tallinn): jrcc@politsei.ee.	Estonian Environment Agency: Piret Kiristaja, piret.kiristaja@envir.ee; Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee.	Estonian Environment Agency: Piret Kiristaja, piret.kiristaja@envir.ee; Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee.	Estonian Environment Agency: Piret Kiristaja, piret.kiristaja@envir.ee; Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee.	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee	Environmental Board: Monika Lepasson: monika.lepasson@keskkonnaamet.ee; Estonian Environment Agency: Anastasiia Kovtun-Kante, anastasiia.kovtun-kante@envir.ee; Arthur Kivi, arthur.kivi@envir.ee
References	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).	The monitoring programme is approved by the minister of the environment and available at https://www.envir.ee/et/eesmargid-tegevused/merekeskkonna-kaitse/merestrateegia (https://www.envir.ee/sites/default/files/mereala_seireprogramm_2021_2026.pdf) (in Estonian).