Abstract

Post-calving surveys to estimate herd size of barren-ground caribou (Rangifer tarandus groenlandicus, R. t. granti, and R. t. caribou) have been used for caribou herds in Alaska, Yukon, Northwest Territories, Nunavut, and Québec/Labrador. The main field procedure uses relocation of collared caribou to locate aggregated groups of hundreds or thousands of caribou during times of high insect harassment that usually occur in July. These groups are then pho­tographed to obtain a count of the caribou in the aggregated groups. Often some caribou are missed, and the count of caribou may be a negatively biased estimate of total herd size, unless a high proportion of the herd is found and photographed. To address this, some previous studies have used the Lincoln-Petersen estimator, which estimates the proportion of the herd counted based on the percentage of available collared caribou found during the survey. However, this estimator assumes equal probabilities of all groups of caribou being found, regardless of group size and the numbers of collared caribou in the group. These assumptions may not be valid, as larger groups are more likely to be found than smaller groups, particularly if there are several collared caribou present. This may lead to estimates that are biased low, along with an estimate of variance that may also be biased low. A two phase estimator developed by Rivest et al., in 1998 became available in R statistical software in 2012. We analyzed 20 data sets from post-calving surveys in the NWT and NU carried out between 2000 and 2015 using the Rivest estimator to explore working characteristics of this estimator. We compared the Rivest estimates with Lincoln-Petersen estimates and total counts on each survey. We considered factors that influence precision of the Rivest estimator with a focus on sampling factors such as the proportion of collars found, the number of collars available, and natural factors such as the degree of aggregation of caribou in each survey (as indexed by the negative binomial dispersion parameter). In general, the Rivest estimator displayed acceptable preci­sion when high proportions of caribou groups with collars were detected and counted, collar numbers were sufficient, and aggregation was adequate. Notable exceptions occurred in years of lower aggregation which resulted in many small groups with 0 or few collared caribou, and in these cases herd estimates had large variances and low precision. Estimates from the Rivest estimator, Lincoln-Petersen estimator, and total counts converged when sampling effort was high, collar numbers relative to herd size were high, and caribou were well aggregated in a limited number of groups. In other cases, estimates of the Rivest estimator were generally higher than Lincoln-Petersen estimates, presumably due to negative bias with the Lincoln-Petersen estimator. We provide a set of working recommendations to optimize field sampling to ensure reliable estimates of herd size using post-calving methods.

Highlights

  • Post-calving surveys have been used to estimate population size of migratory caribou (Rangifer tarandus groenlandicus, R. t. granti, and R. t. caribou) herds in Alaska, Yukon, Northwest Territories, Nunavut and Québec/Labrador with the first survey in Alaska in 1961 (Davis et al, 1979; Valkenburg et al, 1985; Russell et al, 1996; Patterson et al, 2004; Harper, 2013; Adamczewski et al, 2017)

  • The main field procedure uses relocation of collared caribou to locate aggregated groups of hundreds or thousands of caribou during times of high insect harassment that usually occur in July

  • The main field procedure for this method is the use of collared caribou to locate aggregated groups of hundreds or thousands of caribou during times of high insect harassment that usually occur in July

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Summary

Introduction

Post-calving surveys have been used to estimate population size of migratory caribou (Rangifer tarandus groenlandicus, R. t. granti, and R. t. caribou) herds in Alaska, Yukon, Northwest Territories, Nunavut and Québec/Labrador with the first survey in Alaska in 1961 (Davis et al, 1979; Valkenburg et al, 1985; Russell et al, 1996; Patterson et al, 2004; Harper, 2013; Adamczewski et al, 2017). The main objective of field procedures is to photograph the aggregations of caribou found and thereby obtain a near-count of total herd size. The main challenge with this technique is that it is often difficult to locate all the aggregated groups and it is likely that some groups are missed; the total count of all photographed groups is an underestimate of total herd size by an unknown amount. The total count becomes an index and trend estimates will only be valid if it can be assumed that the total amount missed is the same each year (Anderson, 2001), or if the estimation of herd size reliably accounts for the proportion of the herd that was likely missed in each survey

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