(PDF) Figure 4: Beverton–Holt Spawning Stock Recruitment

Figure 4: Beverton–Holt Spawning Stock Recruitment Curves With Recruitment Capped at R0 (A) and Resulting Biomass Trajectories (B) From a Simple Population Model Using Different Steepness, H, Ranging From 0.35 to 0.95 and Time-Varying Mortality as in Fig. 2.

doi 10.7717/peerj.7308/fig-4

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Figure 3: Beverton–Holt Spawning Stock Recruitment Curves (A) and Resulting Biomass Trajectories (B) From a Simple Population Model Using Different Steepness, H, Ranging From 0.35 to 0.95 and Time-Varying Mortality as in Fig. 2.

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Figure 6: Hindcast Biomass Trajectory for the Myctophids Species Functional Group With Different Recruitment Steepness (H) and No Cap on Recruitment (A) and With Recruitment Capped at R0 (B).

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Figure 11: Biomass Ratio of Trophic Level 4 and Higher Over Trophic Level 3 From Chatham Rise Atlantis Model Simulations With Recruitment Steepness Set at 0.5 for Myctophids, No Cap on Recruitment (A), Recruitment Capped at R0 (B), and Three Catch Scenarios: (1) Zero Catch; (2) Status Quo Catch; (3) Half Catch, for the 2010–2016 Hindcast Period and 2016–2046 Projection Period.

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Figure 10: Biomass of Pelagic Fishes Over Biomass of All Age-Structured Species Groups From Chatham Rise Atlantis Model Simulations With Recruitment Steepness Set at 0.5 for Myctophids, No Cap on Recruitment (A), Recruitment Capped at R0 (B), and Three Catch Scenarios: (1) Zero Catch; (2) Status Quo Catch; (3) Half Catch, for the 2010–2016 Hindcast Period and 2016–2046 Projection Period.

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Figure 2: Time-Varying Mortality (M) Used for Simple Population Model.

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Figure 7: Kempton’s Q Calculated From Chatham Rise Atlantis Model Simulations With Recruitment Steepness Set at 0.5 for Myctophids, No Cap on Recruitment (A), Recruitment Capped at R0 (B), and Three Catch Scenarios: (1) Zero Catch; (2) Status Quo Catch; (3) Half Catch, for the 2010–2016 Hindcast Period and 2016–2046 Projection Period.

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A Parametrized Stock-Recruitment Relationship Derived From a Slow-Fast Population Dynamic Model

Mathematics and Computers in Simulation

Theoretical Computer Science

2018

English

Figure 1: Beverton–Holt SSR Curve With H = 0.4 (A, Blue Line) and H = 0.8 (B, Green Line), With B0 and R0 (Black Dot-Dashed Lines) and 20% B0 and R0.2 (Grey Dot-Dashed Lines).

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Using a Recruitment-Linked Multispecies Stock Assessment Model to Estimate Common Trends in Recruitment for US West Coast Groundfishes

Marine Ecology - Progress Series

English

Amanote Research

Figure 4: Beverton–Holt Spawning Stock Recruitment Curves With Recruitment Capped at R0 (A) and Resulting Biomass Trajectories (B) From a Simple Population Model Using Different Steepness, H, Ranging From 0.35 to 0.95 and Time-Varying Mortality as in Fig. 2.

doi 10.7717/peerj.7308/fig-4

Full Text

Abstract

Date

Authors

Publisher

Related search

Figure 3: Beverton–Holt Spawning Stock Recruitment Curves (A) and Resulting Biomass Trajectories (B) From a Simple Population Model Using Different Steepness, H, Ranging From 0.35 to 0.95 and Time-Varying Mortality as in Fig. 2.

Figure 6: Hindcast Biomass Trajectory for the Myctophids Species Functional Group With Different Recruitment Steepness (H) and No Cap on Recruitment (A) and With Recruitment Capped at R0 (B).

Figure 2: Time-Varying Mortality (M) Used for Simple Population Model.

A Parametrized Stock-Recruitment Relationship Derived From a Slow-Fast Population Dynamic Model

Figure 1: Beverton–Holt SSR Curve With H = 0.4 (A, Blue Line) and H = 0.8 (B, Green Line), With B0 and R0 (Black Dot-Dashed Lines) and 20% B0 and R0.2 (Grey Dot-Dashed Lines).

Using a Recruitment-Linked Multispecies Stock Assessment Model to Estimate Common Trends in Recruitment for US West Coast Groundfishes