Abstract

This study presents practical and easy-to-implement approaches for determining appropriate, or “safe”, sample sizes for routinely conducted statistical surveys. Finite populations are considered holistically and independently of whether they are continuous, categorical, or dichotomous. It is proposed that in routinely conducted sampling surveys variance-ordered categories of populations should be the basis for calculating the safe sample size given that the variance within a target population is a primary factor in determining sample size a priori. Several theoretical and operational justifications are presented for this thesis. Dichotomous populations are often assumed to have higher variances than continuous populations when the latter have been standardized and have all values in the interval [0 1]. Herein, it is shown that this is not a valid assumption; a significant proportion of dichotomous populations have lower variances than continuous populations. Conversely, many continuous populations have variances that exceed the limits that are broadly assumed in literature for determining a safe sample size. Finite populations should thus be viewed holistically. A simple first step is to partition finite populations into just two categories: convex and concave. These two categories are relative to a flat population with a known variance as the threshold between them. This variance is used to determine a safe sample size for any continuous population with a flat or positive curvature, including approximately 20% of dichotomous populations. For all other populations the value of 0.25 is recommended for approximating the actual population variance as the primary parameter for sample size determination. The suggested approaches have been successfully implemented in fisheries statistical monitoring programmes but it is believed that they are equally applicable to other applications sectors.

Highlights

  • This study stems from the author’s experience in implementing sample-based data collection programmes in the fisheries sector

  • Based on the methodology and examples presented in this study, it would seem reasonable to suggest that in routinely conducted surveys, formula (5) remains a viable tool for safe sample size determination when it is used properly

  • It is worth noticing that the categorization of populations into convex and concave provides us with a quick way of determining safe sample size

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Summary

Introduction

This study stems from the author’s experience in implementing sample-based data collection programmes in the fisheries sector. In this case the target population is dichotomous and its proportion p is equivalent to the probability of a boat being active Another approach is to sample boats at random on a weekly basis and record the number of days fishing over the past week. The introductory information given above indicates that in routinely conducted fisheries surveys the target populations are of varying types: continuous for landings (comprising skewed, approximately normal, flat and U-shaped data) and dichotomous or categorical for boat activity. These populations are stratified by boat type and fishing method and by coastal zone, since the latter can affect the species composition and the quantities caught. It should be added here that in all cases the populations are finite and their respective size is known with good accuracy

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