Appendix 9
Evaluation of the vulnerability criteria for St. Lawrence beluga whale (
Delphinapterus leucas) to environmental stressors. Refer to table
4.22 for more details on criteria.
|
Environmental stressors
|
Frequency
|
Direct or indirect effects
|
Resistance
|
Recovery time
|
Effect of reproduction
|
Effect on the population
|
Status of the species
|
Resident species
|
|
Commercial anchorage sites
|
3
|
3
|
0
|
1
|
1
|
1
|
3
|
3
|
|
Hydrocarbons
|
1
|
3
|
2
|
2
|
2
|
3
|
3
|
3
|
|
Others
|
1
|
3
|
2
|
2
|
2
|
3
|
3
|
3
|
|
Unknown content
|
1
|
3
|
2
|
2
|
2
|
3
|
3
|
3
|
|
Dredging sites
|
2
|
2
|
0
|
1
|
0
|
3
|
3
|
3
|
|
Disposal sites
|
2
|
2
|
0
|
1
|
0
|
3
|
3
|
3
|
|
Planned capitalization dredging
|
1
|
2
|
0
|
1
|
0
|
3
|
3
|
3
|
|
Recorded shipwreck sites
|
0
|
0
|
0
|
0
|
0
|
0
|
3
|
3
|
|
Cargo
|
4
|
3
|
1
|
3
|
1
|
1
|
3
|
3
|
|
Containers
|
4
|
3
|
1
|
3
|
1
|
1
|
3
|
3
|
|
Dry bulk
|
4
|
3
|
1
|
3
|
1
|
1
|
3
|
3
|
|
Government / research
|
3
|
3
|
0
|
2
|
0
|
1
|
3
|
3
|
|
Marine mammals observation
|
3
|
3
|
0
|
2
|
1
|
1
|
3
|
3
|
|
Passenger / ferry / ro-ro
|
4
|
3
|
1
|
3
|
1
|
1
|
3
|
3
|
|
Pleasure vessels
|
3
|
3
|
1
|
3
|
1
|
1
|
3
|
3
|
|
Special ships
|
3
|
3
|
1
|
3
|
1
|
1
|
3
|
3
|
|
Tanker
|
4
|
3
|
1
|
3
|
1
|
1
|
3
|
3
|
|
Tugboat / port
|
3
|
3
|
1
|
3
|
1
|
1
|
3
|
3
|
|
Port shipping
|
4
|
3
|
1
|
3
|
1
|
1
|
3
|
3
|
|
Demersal, destructive, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
3
|
3
|
|
Demersal, non-destructive, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
3
|
3
|
|
Demersal, non-destructive, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
3
|
3
|
|
Pelagic, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
3
|
3
|
|
Pelagic, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
3
|
3
|
|
Commercial fisheries in fluvial sector
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Marine pollution
|
3
|
3
|
1
|
3
|
2
|
3
|
3
|
3
|
Evaluation of the vulnerability criteria for harbour porpoise (
Phocoena phocoena) to environmental stressors. Refer to table
4.22 for more details on criteria.
|
Environmental stressors
|
Frequency
|
Direct or indirect effects
|
Resistance
|
Recovery time
|
Effect of reproduction
|
Effect on the population
|
Status of the species
|
Resident species
|
|
Commercial anchorage sites
|
3
|
3
|
0
|
1
|
0
|
1
|
1
|
2
|
|
Hydrocarbons
|
1
|
3
|
2
|
2
|
2
|
1
|
1
|
2
|
|
Others
|
1
|
3
|
2
|
2
|
2
|
1
|
1
|
2
|
|
Unknown content
|
1
|
3
|
2
|
2
|
2
|
1
|
1
|
2
|
|
Dredging sites
|
2
|
2
|
0
|
1
|
0
|
1
|
1
|
2
|
|
Disposal sites
|
2
|
2
|
0
|
1
|
0
|
1
|
1
|
2
|
|
Planned capitalization dredging
|
1
|
2
|
0
|
1
|
0
|
1
|
1
|
2
|
|
Recorded shipwreck sites
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
2
|
|
Cargo
|
4
|
3
|
1
|
3
|
0
|
1
|
1
|
2
|
|
Containers
|
4
|
3
|
1
|
3
|
0
|
1
|
1
|
2
|
|
Dry bulk
|
4
|
3
|
1
|
3
|
0
|
1
|
1
|
2
|
|
Government / research
|
3
|
3
|
0
|
2
|
0
|
1
|
1
|
2
|
|
Marine mammals observation
|
3
|
3
|
0
|
2
|
0
|
1
|
1
|
2
|
|
Passenger / ferry / ro-ro
|
4
|
3
|
1
|
3
|
0
|
1
|
1
|
2
|
|
Pleasure vessels
|
3
|
3
|
1
|
3
|
0
|
1
|
1
|
2
|
|
Special ships
|
3
|
3
|
1
|
3
|
0
|
1
|
1
|
2
|
|
Tanker
|
4
|
3
|
1
|
3
|
0
|
1
|
1
|
2
|
|
Tugboat / port
|
3
|
3
|
1
|
3
|
0
|
1
|
1
|
2
|
|
Port shipping
|
4
|
3
|
1
|
3
|
0
|
1
|
1
|
2
|
|
Demersal, destructive, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
2
|
|
Demersal, non-destructive, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
2
|
|
Demersal, non-destructive, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
2
|
|
Pelagic, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
2
|
|
Pelagic, high-bycatch
|
3
|
4
|
1
|
2
|
0
|
1
|
1
|
2
|
|
Commercial fisheries in fluvial sector
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Marine pollution
|
3
|
3
|
1
|
3
|
2
|
3
|
1
|
2
|
Evaluation of the vulnerability criteria for minke whale (
Balaenoptera acutorostrata) to environmental stressors. Refer to table
4.22 for more details on criteria.
|
Environmental stressors
|
Frequency
|
Direct or indirect effects
|
Resistance
|
Recovery time
|
Effect of reproduction
|
Effect on the population
|
Status of the species
|
Resident species
|
|
Commercial anchorage sites
|
3
|
3
|
0
|
1
|
0
|
1
|
0
|
2
|
|
Hydrocarbons
|
1
|
3
|
2
|
2
|
2
|
2
|
0
|
2
|
|
Others
|
1
|
3
|
2
|
2
|
2
|
2
|
0
|
2
|
|
Unknown content
|
1
|
3
|
2
|
2
|
2
|
2
|
0
|
2
|
|
Dredging sites
|
2
|
2
|
0
|
1
|
0
|
1
|
0
|
2
|
|
Disposal sites
|
2
|
2
|
0
|
1
|
0
|
1
|
0
|
2
|
|
Planned capitalization dredging
|
1
|
2
|
0
|
1
|
0
|
1
|
0
|
2
|
|
Recorded shipwreck sites
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
2
|
|
Cargo
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
2
|
|
Containers
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
2
|
|
Dry bulk
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
2
|
|
Government / research
|
3
|
3
|
0
|
2
|
0
|
1
|
0
|
2
|
|
Marine mammals observation
|
3
|
3
|
0
|
2
|
0
|
1
|
0
|
2
|
|
Passenger / ferry / ro-ro
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
2
|
|
Pleasure vessels
|
3
|
3
|
1
|
3
|
0
|
1
|
0
|
2
|
|
Special ships
|
3
|
3
|
1
|
3
|
0
|
1
|
0
|
2
|
|
Tanker
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
2
|
|
Tugboat / port
|
3
|
3
|
1
|
3
|
0
|
1
|
0
|
2
|
|
Port shipping
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
2
|
|
Demersal, destructive, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
2
|
|
Demersal, non-destructive, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
2
|
|
Demersal, non-destructive, high-bycatch
|
3
|
4
|
1
|
2
|
0
|
1
|
0
|
2
|
|
Pelagic, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
2
|
|
Pelagic, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
2
|
|
Commercial fisheries in fluvial sector
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Marine pollution
|
3
|
3
|
1
|
3
|
2
|
3
|
0
|
2
|
Evaluation of the vulnerability criteria for harbor seal (
Phoca vitulina) to environmental stressors. Refer to table
4.22 for more details on criteria.
|
Environmental stressors
|
Frequency
|
Direct or indirect effects
|
Resistance
|
Recovery time
|
Effect of reproduction
|
Effect on the population
|
Status of the species
|
Resident species
|
|
Commercial anchorage sites
|
3
|
0
|
0
|
1
|
0
|
1
|
0
|
1
|
|
Hydrocarbons
|
1
|
3
|
2
|
2
|
2
|
1
|
0
|
1
|
|
Others
|
1
|
3
|
2
|
2
|
2
|
1
|
0
|
1
|
|
Unknown content
|
1
|
3
|
2
|
2
|
2
|
1
|
0
|
1
|
|
Dredging sites
|
2
|
2
|
0
|
1
|
0
|
1
|
0
|
1
|
|
Disposal sites
|
2
|
2
|
0
|
1
|
0
|
1
|
0
|
1
|
|
Planned capitalization dredging
|
1
|
2
|
0
|
1
|
0
|
1
|
0
|
1
|
|
Recorded shipwreck sites
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Cargo
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Containers
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Dry bulk
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Government / research
|
3
|
3
|
0
|
2
|
0
|
1
|
0
|
1
|
|
Marine mammals observation
|
3
|
3
|
0
|
2
|
0
|
1
|
0
|
1
|
|
Passenger / ferry / ro-ro
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Pleasure vessels
|
3
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Special ships
|
3
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Tanker
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Tugboat / port
|
3
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Port shipping
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Demersal, destructive, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Demersal, non-destructive, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Demersal, non-destructive, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Pelagic, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Pelagic, high-bycatch
|
3
|
4
|
1
|
2
|
0
|
1
|
0
|
1
|
|
Commercial fisheries in fluvial sector
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Marine pollution
|
3
|
3
|
1
|
3
|
2
|
3
|
0
|
1
|
Evaluation of the vulnerability criteria for harp seal (
Phoca groenlandica) to environmental stressors. Refer to table
4.22 for more details on criteria.
|
Environmental stressors
|
Frequency
|
Direct or indirect effects
|
Resistance
|
Recovery time
|
Effect of reproduction
|
Effect on the population
|
Status of the species
|
Resident species
|
|
Commercial anchorage sites
|
3
|
0
|
0
|
1
|
1
|
1
|
0
|
1
|
|
Hydrocarbons
|
1
|
3
|
2
|
2
|
2
|
1
|
0
|
1
|
|
Others
|
1
|
3
|
2
|
2
|
2
|
1
|
0
|
1
|
|
Unknown content
|
1
|
3
|
2
|
2
|
2
|
1
|
0
|
1
|
|
Dredging sites
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Disposal sites
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Planned capitalization dredging
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Recorded shipwreck sites
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Cargo
|
4
|
3
|
1
|
3
|
1
|
1
|
0
|
1
|
|
Containers
|
4
|
3
|
1
|
3
|
1
|
1
|
0
|
1
|
|
Dry bulk
|
4
|
3
|
1
|
3
|
1
|
1
|
0
|
1
|
|
Government / research
|
3
|
3
|
0
|
2
|
0
|
1
|
0
|
1
|
|
Marine mammals observation
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Passenger / ferry / ro-ro
|
4
|
3
|
1
|
3
|
1
|
1
|
0
|
1
|
|
Pleasure vessels
|
3
|
3
|
1
|
3
|
1
|
1
|
0
|
1
|
|
Special ships
|
3
|
3
|
1
|
3
|
1
|
1
|
0
|
1
|
|
Tanker
|
4
|
3
|
1
|
3
|
1
|
1
|
0
|
1
|
|
Tugboat / port
|
3
|
3
|
1
|
3
|
1
|
1
|
0
|
1
|
|
Port shipping
|
4
|
3
|
1
|
3
|
1
|
1
|
0
|
1
|
|
Demersal, destructive, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Demersal, non-destructive, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Demersal, non-destructive, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Pelagic, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Pelagic, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Commercial fisheries in fluvial sector
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Marine pollution
|
3
|
3
|
1
|
3
|
2
|
3
|
0
|
1
|
Evaluation of the vulnerability criteria for grey seal (
Halichoerus grypus) to environmental stressors. Refer to table
4.22 for more details on criteria.
|
Environmental stressors
|
Frequency
|
Direct or indirect effects
|
Resistance
|
Recovery time
|
Effect of reproduction
|
Effect on the population
|
Status of the species
|
Resident species
|
|
Commercial anchorage sites
|
3
|
0
|
0
|
1
|
0
|
1
|
0
|
1
|
|
Hydrocarbons
|
1
|
3
|
2
|
2
|
2
|
1
|
0
|
1
|
|
Others
|
1
|
3
|
2
|
2
|
2
|
1
|
0
|
1
|
|
Unknown content
|
1
|
3
|
2
|
2
|
2
|
1
|
0
|
1
|
|
Dredging sites
|
2
|
2
|
0
|
1
|
0
|
1
|
0
|
1
|
|
Disposal sites
|
2
|
2
|
0
|
1
|
0
|
1
|
0
|
1
|
|
Planned capitalization dredging
|
1
|
2
|
0
|
1
|
0
|
1
|
0
|
1
|
|
Recorded shipwreck sites
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Cargo
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Containers
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Dry bulk
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Government / research
|
3
|
3
|
0
|
2
|
0
|
1
|
0
|
1
|
|
Marine mammals observation
|
3
|
3
|
0
|
2
|
0
|
1
|
0
|
1
|
|
Passenger / ferry / ro-ro
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Pleasure vessels
|
3
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Special ships
|
3
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Tanker
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Tugboat / port
|
3
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Port shipping
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Demersal, destructive, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Demersal, non-destructive, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Demersal, non-destructive, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Pelagic, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Pelagic, high-bycatch
|
3
|
4
|
1
|
2
|
0
|
1
|
0
|
1
|
|
Commercial fisheries in fluvial sector
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Marine pollution
|
3
|
3
|
1
|
3
|
2
|
3
|
0
|
1
|
Evaluation of the vulnerability criteria for humpback whale (
Megaptera novaeangliae) to environmental stressors. Refer to table
4.22 for more details on criteria.
|
Environmental stressors
|
Frequency
|
Direct or indirect effects
|
Resistance
|
Recovery time
|
Effect of reproduction
|
Effect on the population
|
Status of the species
|
Resident species
|
|
Commercial anchorage sites
|
3
|
3
|
0
|
1
|
0
|
1
|
0
|
1
|
|
Hydrocarbons
|
1
|
3
|
2
|
2
|
2
|
2
|
0
|
1
|
|
Others
|
1
|
3
|
2
|
2
|
2
|
2
|
0
|
1
|
|
Unknown content
|
1
|
3
|
2
|
2
|
2
|
2
|
0
|
1
|
|
Dredging sites
|
2
|
2
|
0
|
1
|
0
|
1
|
0
|
1
|
|
Disposal sites
|
2
|
2
|
0
|
1
|
0
|
1
|
0
|
1
|
|
Planned capitalization dredging
|
1
|
2
|
0
|
1
|
0
|
1
|
0
|
1
|
|
Recorded shipwreck sites
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Cargo
|
4
|
4
|
1
|
3
|
0
|
2
|
0
|
1
|
|
Containers
|
4
|
4
|
1
|
3
|
0
|
2
|
0
|
1
|
|
Dry bulk
|
4
|
4
|
1
|
3
|
0
|
2
|
0
|
1
|
|
Government / research
|
3
|
3
|
0
|
2
|
0
|
1
|
0
|
1
|
|
Marine mammals observation
|
3
|
3
|
0
|
2
|
1
|
1
|
0
|
1
|
|
Passenger / ferry / ro-ro
|
4
|
4
|
1
|
3
|
0
|
2
|
0
|
1
|
|
Pleasure vessels
|
3
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Special ships
|
3
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Tanker
|
4
|
4
|
1
|
3
|
0
|
2
|
0
|
1
|
|
Tugboat / port
|
3
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Port shipping
|
4
|
3
|
1
|
3
|
0
|
1
|
0
|
1
|
|
Demersal, destructive, high-bycatch
|
0
|
0
|
0
|
1
|
0
|
0
|
0
|
1
|
|
Demersal, non-destructive, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Demersal, non-destructive, high-bycatch
|
3
|
4
|
1
|
2
|
0
|
1
|
0
|
1
|
|
Pelagic, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Pelagic, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
|
Commercial fisheries in fluvial sector
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Marine pollution
|
3
|
3
|
1
|
3
|
2
|
3
|
0
|
1
|
Evaluation of the vulnerability criteria for blue whale (
Balaenoptera musculus) to environmental stressors. Refer to table
4.22 for more details on criteria.
|
Environmental stressors
|
Frequency
|
Direct or indirect effects
|
Resistance
|
Recovery time
|
Effect of reproduction
|
Effect on the population
|
Status of the species
|
Resident species
|
|
Commercial anchorage sites
|
3
|
3
|
0
|
1
|
0
|
1
|
3
|
1
|
|
Hydrocarbons
|
1
|
3
|
2
|
2
|
2
|
2
|
3
|
1
|
|
Others
|
1
|
3
|
2
|
2
|
2
|
2
|
3
|
1
|
|
Unknown content
|
1
|
3
|
2
|
2
|
2
|
2
|
3
|
1
|
|
Dredging sites
|
2
|
2
|
0
|
1
|
0
|
1
|
3
|
1
|
|
Disposal sites
|
2
|
2
|
0
|
1
|
0
|
1
|
3
|
1
|
|
Planned capitalization dredging
|
1
|
2
|
0
|
1
|
0
|
1
|
3
|
1
|
|
Recorded shipwreck sites
|
0
|
0
|
0
|
0
|
0
|
0
|
3
|
1
|
|
Cargo
|
4
|
4
|
1
|
3
|
0
|
2
|
3
|
1
|
|
Containers
|
4
|
4
|
1
|
3
|
0
|
2
|
3
|
1
|
|
Dry bulk
|
4
|
4
|
1
|
3
|
0
|
2
|
3
|
1
|
|
Government / research
|
3
|
3
|
0
|
2
|
0
|
1
|
3
|
1
|
|
Marine mammals observation
|
3
|
3
|
0
|
2
|
1
|
1
|
3
|
1
|
|
Passenger / ferry / ro-ro
|
4
|
4
|
1
|
3
|
0
|
2
|
3
|
1
|
|
Pleasure vessels
|
3
|
3
|
1
|
3
|
0
|
1
|
3
|
1
|
|
Special ships
|
3
|
3
|
1
|
3
|
0
|
1
|
3
|
1
|
|
Tanker
|
4
|
4
|
1
|
3
|
0
|
2
|
3
|
1
|
|
Tugboat / port
|
3
|
3
|
1
|
3
|
0
|
1
|
3
|
1
|
|
Port shipping
|
4
|
3
|
1
|
3
|
0
|
1
|
3
|
1
|
|
Demersal, destructive, high-bycatch
|
0
|
0
|
0
|
1
|
0
|
0
|
3
|
1
|
|
Demersal, non-destructive, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
3
|
1
|
|
Demersal, non-destructive, high-bycatch
|
3
|
4
|
1
|
2
|
0
|
1
|
3
|
1
|
|
Pelagic, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
3
|
1
|
|
Pelagic, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
3
|
1
|
|
Commercial fisheries in fluvial sector
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Marine pollution
|
3
|
3
|
1
|
3
|
2
|
3
|
3
|
1
|
Evaluation of the vulnerability criteria for fin whale (
Balaenoptera physalus) to environmental stressors. Refer to table
4.22 for more details on criteria.
|
Environmental stressors
|
Frequency
|
Direct or indirect effects
|
Resistance
|
Recovery time
|
Effect of reproduction
|
Effect on the population
|
Status of the species
|
Resident species
|
|
Commercial anchorage sites
|
3
|
3
|
0
|
1
|
0
|
1
|
1
|
1
|
|
Hydrocarbons
|
1
|
3
|
2
|
2
|
2
|
2
|
1
|
1
|
|
Others
|
1
|
3
|
2
|
2
|
2
|
2
|
1
|
1
|
|
Unknown content
|
1
|
3
|
2
|
2
|
2
|
2
|
1
|
1
|
|
Dredging sites
|
2
|
2
|
0
|
1
|
0
|
1
|
1
|
1
|
|
Disposal sites
|
2
|
2
|
0
|
1
|
0
|
1
|
1
|
1
|
|
Planned capitalization dredging
|
1
|
2
|
0
|
1
|
0
|
1
|
1
|
1
|
|
Recorded shipwreck sites
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
1
|
|
Cargo
|
4
|
4
|
1
|
3
|
0
|
2
|
1
|
1
|
|
Containers
|
4
|
4
|
1
|
3
|
0
|
2
|
1
|
1
|
|
Dry bulk
|
4
|
4
|
1
|
3
|
0
|
2
|
1
|
1
|
|
Government / research
|
3
|
3
|
0
|
2
|
0
|
1
|
1
|
1
|
|
Marine mammals observation
|
3
|
3
|
0
|
2
|
1
|
1
|
1
|
1
|
|
Passenger / ferry / ro-ro
|
4
|
4
|
1
|
3
|
0
|
2
|
1
|
1
|
|
Pleasure vessels
|
3
|
3
|
1
|
3
|
0
|
1
|
1
|
1
|
|
Special ships
|
3
|
3
|
1
|
3
|
0
|
1
|
1
|
1
|
|
Tanker
|
4
|
4
|
1
|
3
|
0
|
2
|
1
|
1
|
|
Tugboat / port
|
3
|
3
|
1
|
3
|
0
|
1
|
1
|
1
|
|
Port shipping
|
4
|
3
|
1
|
3
|
0
|
1
|
1
|
1
|
|
Demersal, destructive, high-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
1
|
|
Demersal, non-destructive, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
1
|
|
Demersal, non-destructive, high-bycatch
|
3
|
4
|
1
|
2
|
0
|
1
|
1
|
1
|
|
Pelagic, low-bycatch
|
0
|
0
|
0
|
0
|
0
|
0
|
1
|
1
|
|
Pelagic, high-bycatch
|
0
|
0
|
0
|
1
|
0
|
0
|
1
|
1
|
|
Commercial fisheries in fluvial sector
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
0
|
|
Marine pollution
|
3
|
3
|
1
|
3
|
2
|
3
|
1
|
1
|