Member State report / Art11 / 2020 / D1-F / Cyprus / Mediterranean: Aegean-Levantine 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 | D1 Fish |
| Member State | Cyprus |
| Region/subregion | Mediterranean: Aegean-Levantine Sea |
| Reported by | Department of Fisheries and Marine Research, Ministry of Agriculture, Rural Development and Environm |
| Report date | 2020-12-14 |
| Report access |
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Monitoring strategy description |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Cyprus has implemented the program code MALCY-D0143 in the geographical area of MAL-CY-MS. The monitoring program aims to investigate the abundance and geographical distribution and habitat identification of fish and cephalopods in maritime areas of Cyprus.
Under this program is the sub program MALCY-D0143-01 (fish and cephalopods monitoring program) and is listed as partially active in the maritime areas of Cyprus (GSA 25). The monitoring program is conducted yearly at the MEDITS sampling stations in water depths of 10 to 800 m. The methodology follows two sampling programs the MEDITS WG (2013) and the multi-force fishing (large pelagics ICTAT) then the data is transferred to the DFMS database. The monitoring program follows the MSFD criteria and indicators of species distribution (i.e. distributional range, pattern within latter where appropriate, and area covered by the species), population size (i.e. abundance and/or biomass), population condition (i.e. population demographic characteristics [body size or age class structure, sex ratio, fecundity rates, survival/mortality rates]), habitat condition (relative abundance and/or biomass), proportion of selected species at the top of the food web, and large fish. |
Coverage of GES criteria |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Gaps and plans |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Continuation of sampling for fish and cephalopods through Program MALCY-D0143 at the MEDITS sampling stations should be sufficient to re-establish GES for this biodiversity component. It is also recommended that the environmental authorities explore the option of utilizing environmental DNA (eDNA) to augment and enhance the results of the direct collection methodology that is currently in place (Thomsen and Willerslev, 2015). By using eDNA techniques correctly, it may be possible to monitor changes in biodiversity of those fish and cephalopod species that may be more cryptic (and therefore more difficult to monitor) within Cypriot territorial waters. Additionally, it may be possible to implement a more cost-effective sampling program that alternates yearly between an intensive field sampling effort and less intense eDNA sampling effort which relies on the collection and analysis of water samples. |
Related targets |
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Coverage of targets |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Adequate monitoring will be in place by 2024 |
Related measures |
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Coverage of measures |
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Related monitoring programmes |
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Programme code |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
D01 |
Programme name |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Biodiversity |
Update type |
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 |
Same programme as in 2014 |
Same programme as in 2014 |
Old programme codes |
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Programme description |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
The biodiversity monitoring programmes focuses on the distributions and abundances of birds, mammals, reptiles, fish and cephalopods (relating to Descriptor 1). The programmes capitalize in part on existing monitoring programmes. It addresses the MSFD biodiversity indicators as well as several of the indicators of Ecological Objective 01 adopted by the Contracting Parties of UNEP / MAP (2013) and aims to support the formal establishment of indicators and targets. The programmes also aim to generate a comprehensive assessment of marine species distribution and population size for all important species as well as potentially identify impacts and threats. The DFMR has implemented “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017)” to provide a current status of the environment prior to commencing activities in the oil and gas lease areas. Per these requirements, sediment samples are taken to assess the macrofaunal communities during Environmental Baseline Surveys (EBS) in the Economic Exclusion Zone (EEZ). The Cyprus fish and cephalopods monitoring programme focuses on state characteristics that describe the distributions, abundances, and demographic characteristics of demersal fish and cephalopods found in Cyprus waters. Moreover, shifts in these established indicators, e.g., population/age structure, may capture the effects of fishing (pressure). The programme uses data from the established Mediterranean International Trawling Survey (MedITS) to complement the three indicators and targets established in 2012 for fish, with additional ones for fish and cephalopods that will be formally established in 2018. The water column habitats monitoring programme addresses the state of the physicochemical conditions of the water column of Cyprus waters, and abundance and biomass of phytoplankton and zooplankton. Moreover, the programme assesses trends in their abundance and biomass with time, as groups with fast turnover times at the base of the food web. This programme establishes many baseline-level values against which the eutrophication (MALCY-D05) and hydrographical changes (MALCY-D07) monitoring programmes will assess their results. It addresses several MSFD biodiversity and food-web indicators of Ecological Objectives 05 and 07 adopted by the Contracting Parties of UNEP/MAP (2013). Marine & Environmental Research Lab Ltd. (2019). The seabed habitats monitoring programme focuses on the distribu |
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Monitoring details |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
The Game Fund Service methodology was used and consisted of monthly bird observations in each investigation area. The monitoring program followed the MSFD criteria and indicators of species distribution, distributional range, distributional pattern within the latter, population size, and population abundance and/or biomass; and UNEP/MAP (2013) criteria and indicators of distributional range, population abundance, and population density.
The physicochemical parameters of the water column include master-variables that control the productivity of the food web and the habitability of the water column. Establishing baseline values at suitable reference stations can already be achieved from existing data for coastal waters (UNEP/MAP, WFD, and Nitrates Directive monitoring) as well as territorial waters for some parameters. Expansion beyond the coastal zone will allow the firm establishment of baseline conditions for these master-variables that are only otherwise known from occasional research studies in the region. See also the “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). |
Features |
Surface-feeding birds
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Coastal/shelf cephalopods
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Demersal shelf fish
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Seals
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Turtles
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Coastal/shelf cephalopods
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Demersal shelf fish
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Turtles
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Surface-feeding birds
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Coastal/shelf cephalopods
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Demersal shelf fish
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Seals
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Turtles
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Turtles
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Coastal/shelf cephalopods
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Demersal shelf fish
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Other benthic habitats
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Other benthic habitats
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Other benthic habitats
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Chemical characteristics
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Chemical characteristics
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Chemical characteristics
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Physical and hydrological characteristics
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Physical and hydrological characteristics
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Physical and hydrological characteristics
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Elements |
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GES criteria |
D1C2 |
D1C2 |
D1C2 |
D1C2 |
D1C2 |
D1C3 |
D1C3 |
D1C3 |
D1C4 |
D1C4 |
D1C4 |
D1C4 |
D1C4 |
D1C4 |
D1C5 |
D1C5 |
D6C3 |
D6C4 |
D6C5 |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
NotRelevan |
Parameters |
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Parameter Other |
Population density within distributional range |
Relative abundance and / or biomass as appropriate |
Relative abundance and / or biomass as appropriate |
Relative abundance and / or biomass as appropriate |
Relative abundance and / or biomass as appropriate |
Population density within distributional range |
Relative abundance and / or biomass as appropriate |
Relative abundance and / or biomass as appropriate |
Species population characteristics (survival rate) |
Relative abundance and / or biomass as appropriate |
Relative abundance and / or biomass as appropriate |
Indirect effects of nutrient enrichment - Abundanc |
Habitat area |
Relative abundance and/or biomass |
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Spatial scope |
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Marine reporting units |
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Temporal scope (start date - end date) |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
2005-9999 |
Monitoring frequency |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
As needed |
Monitoring type |
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Monitoring method |
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Monitoring method other |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
D1. As described in the monitoring records of the Game Fund and fauna Service of the Republic of Cyprus and in the Terms of Reference document.
D1 Biodiversity - Mammals and Reptiles
The monitoring methods implemented in previous surveys in the region (eg. Ryan at al., 2014) and/or those recommended by a regional body, eg. ACCOBAMS (Agreement on the Conservation of cetaceans in the Black Sea Mediterranean Sea and Contigous Atlantic Area) are implemented. Mortality monitoring is conducted according to cetacean and turtle strandings programme procedures. See also “Guidelines for an Offshore Environmental Baseline Survey for Oil and Gas Exploration Activities in Cyprus (DFMR, 2017). For the marine turtles the monitoring follows the “Manual for the Conservation of Marine Turtles in the Mediterranean, (1995) UNEP(MAP/SPA) IUCN/CWS/Fish. Dept. MANRE (Cyprus)” and the “Addendum 1 – Conservation Practices, Manual for the Conservation of Marine Turtles in the Mediterranean (2008)”. The monitoring of Monachus monachus follows a national Protocol.
Biodiversity - Water columns |
Quality control |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Described in game fund and fauna Service monitoring records.
As described in recommended methodology.
QUASIMEME External validation system and internal lab quality control.
Biodiversity - Sea bed habitats: Monitoring Quality Control: as described in Antoniadis et al. (2020) |
Data management |
DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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DFMR database "THETIS".
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Data access |
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References |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |
Argyrou, M., Aplikioti, M., Marcou, M., & Stavrou, P. (2011). Πρόγραμμα παρακολούθησης παράκτιων υδάτων σύμφωνα με το Άρθρο 8 της Οδηγίας Πλαίσιο για τα Νερά (ΟΠΥ, 2000/60/ΕΚ) (p. 26). Nicosia, Cyprus: Department of Fisheries and Marine Research. Pergent G., 2007. Protocol for the setting up of
Posidonia meadows monitoring systems. « MedPosidonia » Programme / RAC/SPA - TOTAL Corporate Foundation for Biodiversity and the Sea; Memorandum of Understanding N°21/2007/RAC/SPA_MedPosidonia NautilusOkianos: 24p + Annexes. |