Abstract

Harvesting alters demography and life histories of exploited populations, and there is mounting evidence that rapid phenotypic changes at the individual level can occur when harvest is intensive. Therefore, recreational fishing is expected to induce both ecological and rapid evolutionary changes in fish populations and consequently requires rigorous management. However, little is known about the coupled demographic and evolutionary consequences of alternative harvest regulations in managed freshwater fisheries. We used a structurally realistic individual‐based model and implemented an eco‐genetic approach that accounts for microevolution, phenotypic plasticity, adaptive behavior, density‐dependent processes, and cryptic mortality sources (illegal harvest and hooking mortality after catch and release). We explored the consequences of a range of harvest regulations, involving different combinations of exploitation intensity and minimum and maximum‐length limits, on the eco‐evolutionary trajectories of a freshwater fish stock. Our 100‐year simulations of size‐selective harvest through recreational fishing produced negative demographic and structural changes in the simulated population, but also plastic and evolutionary responses that compensated for such changes and prevented population collapse even under intense fishing pressure and liberal harvest regulations. Fishing‐induced demographic and evolutionary changes were driven by the harvest regime, and the strength of responses increased with increasing exploitation intensity and decreasing restriction in length limits. Cryptic mortality strongly amplified the impacts of harvest and might be exerting a selective pressure that opposes that of size‐selective harvest. “Slot” limits on harvestable length had overall positive effects but lower than expected ability to buffer harvest impacts. Harvest regulations strongly shape the eco‐evolutionary dynamics of exploited fish stocks and thus should be considered in setting management policies. Our findings suggest that plastic and evolutionary responses buffer the demographic impacts of fishing, but intense fishing pressure and liberal harvest regulations may lead to an unstructured, juvenescent population that would put the sustainability of the stock at risk. Our study also indicates that high rates of cryptic mortality may make harvest regulations based on harvest slot limits ineffective.

Highlights

  • Contemporary evolution is driven by several anthropogenic pressures that often operate on the same traits and impose new adaptive challenges to populations (Sullivan, Bird, & Perry, 2017)

  • Our findings suggest that plastic and evolutionary responses buffer the demographic impacts of fishing, but intense fishing pressure and liberal harvest regulations may lead to an unstructured, juvenescent population that would put the sustainability of the stock at risk

  • Our study indicates that high rates of cryptic mortality may make harvest regulations based on harvest slot limits ineffective

Read more

Summary

| INTRODUCTION

Contemporary evolution is driven by several anthropogenic pressures that often operate on the same traits and impose new adaptive challenges to populations (Sullivan, Bird, & Perry, 2017). Experimental, and empirical studies have assessed the evolutionary consequences of intensive, size-­ selective fishing on physiological, behavioral, and life history traits and the resulting effects for population dynamics and fishery yields (e.g., Dunlop, Heino, & Dieckmann, 2009; Edeline et al, 2007; Heino, 1998; Piou, Taylor, Papaïx, & Prévost, 2015). We added a fishing module to the eco-­genetic individual-­based model inSTREAM-­Gen (Ayllón et al, 2016) to explore the effects of harvest under different management strategies that use different types of length-­based harvest regulations (MLL vs HSs) that vary in their restrictiveness and intensity of exploitation, on the eco-­evolutionary trajectory of the population and the sustainability of the recreational fish stock. | 9602 differ across regulation scenarios, being (a) stronger with increasing exploitation intensity and decreasing minimum-­length limit and (b) buffered by implementing a maximum-­length limit (MaxLL), the buffering effect increasing as the maximum harvestable length is decreased

| MATERIALS AND METHODS
Findings
| DISCUSSION
Full Text
Paper version not known

Talk to us

Join us for a 30 min session where you can share your feedback and ask us any queries you have

Schedule a call

Disclaimer: All third-party content on this website/platform is and will remain the property of their respective owners and is provided on "as is" basis without any warranties, express or implied. Use of third-party content does not indicate any affiliation, sponsorship with or endorsement by them. Any references to third-party content is to identify the corresponding services and shall be considered fair use under The CopyrightLaw.