Monitoring moose (Alces alces) populations is a key component of wildlife management in Alaska. In response to reports of recent difficulties implementing the existing techniques for monitoring moose, an interagency work group identified the monitoring techniques currently in use, characterized technique performance, and examined commonality and geographic patterns of problems encountered when applying techniques in the field. Field biologists engaged in monitoring moose in Alaska were emailed an online questionnaire designed to organize information about overall program satisfaction, population parameters monitored, techniques for estimating parameters, and current impediments to monitoring.
During 2007–2017, biologists failed to complete 42% of scheduled surveys to estimate abundance (n = 295 surveys, 42 respondents). Survey failure rates differed across ecoregions: failure rates were highest in the Kenai/Southcentral (57%), Eastern Interior (43%) and Coastal Subarctic (41%) ecoregions, but lower rates of survey failure were reported for Western Interior (20%) and Arctic Slope (15%) ecoregions of Alaska. Patterns of survey failure were similar for composition.
Lack of adequate snow cover and poor flying weather were the first and second most commonly cited reasons, respectively, for failure to complete scheduled surveys. Where surveys were successfully completed, estimates generally had less precision than desired, with only 50% of respondents achieving intended precision goals for abundance estimation. Biologists indicated a strong willingness to use a new method for monitoring moose if it 1) did not rely on complete snow cover, 2) was more accurate, 3) provided higher precision, 4) provided continuity with previous estimates, 5) could be used where inclement flying weather is frequent, 6) could be used in areas with dense vegetative cover, 7) was accompanied by technical assistance or a user manual, and 6) was similar in cost to existing methods. They indicated mild unwillingness to use a new method that 1) used ground observations, 2) required hunters to turn in specimens, 3) used helicopters for aerial observation, or 4) required more resources than current methods.
These results highlight the need to develop new survey and measurement techniques that can be conducted independently of problematic snow and weather conditions, or at least have far more flexibility in implementing survey protocols. Indeed, the problem of monitoring moose in areas with poor snow conditions is so challenging and pervasive that solutions may require a concentrated, cooperative effort among agencies, including practical feedback from field biologists. Precision of existing techniques may also be improved through better optimization of survey design, the integration of more historical population information in estimation, and perhaps by better clarifying precision requirements relative to program goals.