Elsevier

Ecological Informatics

Volume 5, Issue 4, July 2010, Pages 273-280
Ecological Informatics

Estimation of fish and wildlife disease prevalence from imperfect diagnostic tests on pooled samples with varying pool sizes

https://doi.org/10.1016/j.ecoinf.2010.04.003Get rights and content

Abstract

Methods of estimating disease or parasite prevalence in free-ranging and some captive fish and wildlife populations are frequently lacking in precision due to limited numbers of observations and different assay procedures. Recently statistical methods and software programs have been developed to use Bayesian and other methods to obtain estimates of disease prevalence from diagnostic tests in which sensitivity and/or specificity is not perfect (imperfect) and with sampling schemes using pooled samples. However, these published methods and software programs that consider pooled data sampling have generally considered the case of one uniform pool size for all samples. We present a method for estimating disease prevalence from imperfect diagnostic tests with pooled data collected from a variety of pool sizes. We use a Bayesian approach and obtain a sample from the posterior distribution of prevalence, sensitivity, and specificity, using an MCMC sampling algorithm implemented in the WINBUGS statistical package. We illustrate the use of these methods with three examples and perform efficiency calculations to investigate the performance of these estimators relative to maximum likelihood estimators that assume perfect diagnostic tests. Our results illustrate that the estimates produced from these methods adjust for imperfect tests, and are often more efficient than estimates assuming perfect tests, except in some situations when there is not much prior information on diagnostic test sensitivity and specificity.

Introduction

Estimation of disease or parasite prevalence in wild, free-ranging or captive animal populations is crucial for effective risk analysis, prediction and management. Exotic or endemic diseases or parasites can be transferred among populations and considerable uncertainty often exists regarding findings and interpretations (Daszak and Cunningham, 2000, Krkošek et al., 2004, Bruno, 2004, Moffitt et al., 2004, Murray et al., 2009, O'Brien et al., 2009a). Managers of animal health must consider the disease dynamics and risks to target animal populations in the context of commerce and other human activities, and spatial analysis tools and assessment of uncertainty are needed in disease prediction models (Clough et al., 2003, Haine et al., 2004, Murray and Peeler, 2005, Jennelle et al., 2007). The data needed for management of these risks often come from a variety of sources and may be collected using different sampling protocols, tools, and methods for assessment. Additionally, the data typically come from diagnostic tests in which sensitivity and/or specificity are not perfect (Cannon, 2001, Williams and Moffitt, 2003, Kalis et al., 2004, Branscum et al., 2005, O'Brien et al., 2009b). Studies of free-ranging fish and wildlife populations pose additional challenges for regulatory and management entities, as the science of pathogen identification and methods for screening are relatively new, and difficulties exist in opportunities for consistent sampling. To improve both the sensitivity and specificity of testing procedures, new tools are used as they are developed (USFWS and AFS-FHS, 2003, Diggles et al., 2003, Hogge et al., 2004, López-Vázquez et al., 2006). Many animal disease prevalence monitoring processes use pooled samples for efficient and economical detection of disease (Wells et al., 2003, Bruno, 2004, Jordan, 2005, Muñoz-Zanzi et al., 2006). For all these reasons, the data used to monitor disease status in wild or free-ranging fish or other wildlife populations can be heterogeneous, and samples can be unpooled or pooled with varying pool sizes.

Statistical methods have been reported and software developed to consider imperfect tests for prevalence estimation from a wide variety of sampling plans (Mendoza-Blanco et al., 1996, Cowling et al., 1999, Hanson et al., 2003, Humphry et al., 2004), but these methods consider only a common pool size. Estimation of disease prevalence from pooled samples with common pool sizes has been evaluated both by maximum likelihood-based approaches that assume perfect sensitivity and specificity (Williams and Moffitt, 2001), and with Bayesian approaches that reflect imperfect sensitivity and specificity (Williams and Moffitt, 2003).

Recent studies and evaluations of salmon and other animal populations have utilized a variety of statistical tools, especially Bayesian methods, to consider the outcome of diagnostic tests for pathogens for which there is no true gold standard (Branscum et al., 2005, Gari et al., 2008, Nérette et al., 2008). It is important in all these exercises to provide guidance for understanding disease prevalence under the wide variety of circumstances that observations are made on both captive and free-ranging populations.

The objectives of this paper are to: 1) provide statistical methods to estimate and examine disease prevalence in fish and wildlife populations with data from imperfect diagnostic tests and varying pool sizes; 2) using three data sets, compare prevalence estimates obtained with Bayesian methods and imperfect sensitivity and specificity with estimates calculated with maximum likelihood methods that assume perfect sensitivity and specificity of diagnostic tests, and 3) conduct two efficiency studies to compare the mean-squared error of the Bayesian and maximum likelihood methods for a range of prevalence, sensitivity, and specificity values as well as for different pooled sample structures.

Section snippets

Model and notation

Suppose that a pooled sample of ri fish is obtained, and the probability that an individual fish is positive for the disease of interest is π. Let the sensitivity and specificity of the diagnostic test be η and λ, respectively. Then a pooled sample will be observed to be positive if either it is truly positive and correctly detected, or if it is truly negative and incorrectly declared positive. Adding these two probabilities, we obtain the probability of observing a positive pooled sample asP+|r

Prevalence estimates from data sets

The first two data sets are used to illustrate how Bayesian posterior intervals compare to the likelihood-based intervals (from inverting the likelihood ratio test, discussed in Williams and Moffitt, 2001) that assume perfect tests, for a range of different prior distributions of sensitivity and specificity. The third data set illustrates some advantages of the Bayesian approach for a longitudinal data set. Fig. 1 shows the 95% Bayes posterior intervals for the Truckee River data for several

Prevalence estimates

The first two examples from the M. cerebralis data illustrate routine Bayesian analyses of prevalence that incorporate properties of the diagnostic tests. The third example in which we tested change over time and allowed sensitivity and specificity to change over time illustrated the flexibility of these analyses to address questions that would be quite difficult to address in a traditional frequentist approach. All three examples demonstrate the uncertainty in interpreting results using

Acknowledgments

We are grateful to the staff of the Eagle Fish Health Laboratory, Idaho Department of Fish and Game for access to their data and insight into factors affecting wild fish populations. This is contribution 1051 of the University of Idaho Forestry, Wildlife and Range Resources Experiment Station, Moscow, Idaho, and resulted from previous work supported by a grant to C. Moffitt by the Department of Agriculture, Western Regional Aquaculture Center. We thank D. Nalle, C. Brown and M. Wiest and

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