Abstract

Adaptive management of marine protected areas (MPAs) requires developing methods to evaluate whether monitoring data indicate that they are performing as expected. Modeling the expected responses of targeted species to an MPA network, with a clear timeline for those expectations, can aid in the development of a monitoring program that efficiently evaluates expectations over appropriate time frames. Here, we describe the expected trajectories in abundance and biomass following MPA implementation for populations of 19 nearshore fishery species in California. To capture the process of filling in the age structure truncated by fishing, we used age‐structured population models with stochastic larval recruitment to predict responses to MPA implementation. We implemented both demographically open (high larval immigration) and closed (high self‐recruitment) populations to model the range of possible trajectories as they depend on recruitment dynamics. From these simulations, we quantified the time scales over which anticipated increases in abundance and biomass inside MPAs would become statistically detectable. Predicted population biomass responses range from little change, for species with low fishing rates, to increasing by a factor of nearly seven, for species with high fishing rates before MPA establishment. Increases in biomass following MPA implementation are usually greater in both magnitude and statistical detectability than increases in abundance. For most species, increases in abundance would not begin to become detectable for at least 10 years after implementation. Overall, these results inform potential indicator metrics (biomass), potential indicator species (those with a high fishing : natural mortality ratio), and time frame (>10 yr) for MPA monitoring assessment as part of the adaptive management process.

Highlights

  • Marine protected areas (MPAs) are locations in which fishing and other extractive activities are limited or prohibited, often with multiple objectives ranging from preservation of fishery resources to promoting ecosystem integrity (Leslie 2005, Edgar et al 2007, Klein et al 2008, Halpern et al 2010)

  • We focus on the length of time during which transient dynamics have the potential to dominate population responses, which informs management questions such as how long to monitor before expecting to see detectable marine protected areas (MPAs) effects and how much change in abundance or biomass we might expect from different species

  • To present the results of these analyses for our 19 modeled species, we show summary metrics across all species along with detailed trajectories for four example species expected to show a range of responses: (1) bocaccio, a species with low pre-MPA fishing mortality rates relative to natural mortality; (2) blue rockfish, a commonly fished rockfish with moderate pre-MPA fishing mortality rates; (3) China rockfish, a long-lived rockfish with moderate pre-MPA fishing mortality rates; (4) red sea urchin, a long-lived invertebrate with a high preMPA fishing mortality rate

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Summary

Introduction

Marine protected areas (MPAs) are locations in which fishing and other extractive activities are limited or prohibited, often with multiple objectives ranging from preservation of fishery resources to promoting ecosystem integrity (Leslie 2005, Edgar et al 2007, Klein et al 2008, Halpern et al 2010). One expects populations within MPAs to increase in abundance following MPA implementation. Disentangling the contributions of these drivers of population responses to MPAs is necessary for adaptive management to determine whether knowledge updates or management changes are necessary.

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