Abstract

In fisheries monitoring, catch is assumed to be a product of fishing intensity, catchability, and availability, where availability is defined as the number or biomass of fish present and catchability refers to the relationship between catch rate and the true population. Ecological monitoring programs use catch per unit of effort (CPUE) to standardize catch and monitor changes in fish populations; however, CPUE is proportional to the portion of the population that is vulnerable to the type of gear used in sampling, which is not necessarily the entire population. Programs often deal with this problem by assuming that catchability is constant, but if catchability is not constant, it is not possible to separate the effects of catchability and population size using monitoring data alone. This study uses individual-based simulation to separate the effects of changing environmental conditions on catchability and availability in environmental monitoring data. The simulation combines a module for sampling conditions with a module for individual fish behavior to estimate the proportion of available fish that would escape from the sample. The method is applied to the case study of the well monitored fish species Delta Smelt (Hypomesus transpacificus) in the San Francisco Estuary, where it has been hypothesized that changing water clarity may affect catchability for long-term monitoring studies. Results of this study indicate that given constraints on Delta Smelt swimming ability, it is unlikely that the apparent declines in Delta Smelt abundance are the result of changing water clarity affecting catchability.

Highlights

  • For fisheries stock assessments, catch is assumed to be a product of fishing intensity, catchability, and availability, where availability is defined as the number or biomass of fish present at a site and catchability refers to the relationship between the rate at which fish are caught and the true population size (Ricker 1975)

  • This paper describes an individual-based simulation study that aims to separate the effects of changing environmental conditions on catchability and availability in environmental monitoring data

  • As Delta Smelt have become rarer, interest has grown in evaluating the programs such as the Fall Midwater Trawl (FMWT) that are used to monitor their abundance as well as the factors that determine their distribution in the estuary

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Summary

Introduction

Catch is assumed to be a product of fishing intensity, catchability, and availability, where availability is defined as the number or biomass of fish present at a site and catchability refers to the relationship between the rate at which fish are caught and the true population size (Ricker 1975). Ecological monitoring programs use catch per unit of effort (CPUE) as a way to monitor changes in fish. VOLUME 19 ISSUE 3, ARTICLE 6 populations and communities; CPUE is proportional to the portion of the population that is vulnerable to the type of gear that is used in sampling, which is not necessarily the entire population (Maunder et al 2006). Ecological monitoring programs typically assume that the relationship between catch and biomass or population size is constant, i.e., that catchability is constant. By making this assumption, monitoring programs can compare abundance of organisms relative to abundance in other locations or points in time without having to estimate the proportion of the population that is vulnerable to sampling gear. The goal is to standardize catch so that the non-vulnerable portion of the population cancels out of the equation

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