The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Sprattus sprattus because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet. Salmo salar was also not assessed for D3C1 and D3C3 due to a lack of sufficient data.

The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet.

The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet.

The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet.

The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet.

The criterion D3C3 was not assessed for Clupea harengus membras because: 1) as short-lived species, their population status is not primarily indicated by changes in age and size structure; 2) age and size data are already included in population models for fishing mortality (D3C1) and spawning biomass (D3C2) assessments; and 3) threshold values have not been established yet.