scholarly journals Marine mammal observations report: marine mammal observations during a seismic survey 30 August-4 September 2017, Canada-Korea-USA research expedition in the Canadian Beaufort Sea

2018 ◽  
Author(s):  
R Reidy
1988 ◽  
Vol 83 (6) ◽  
pp. 2246-2254 ◽  
Author(s):  
Charles R. Greene ◽  
W. John Richardson

2013 ◽  
Vol 133 (5) ◽  
pp. 3398-3398 ◽  
Author(s):  
Marie-Noël R. Matthews ◽  
Alexander O. MacGillivray

Polar Record ◽  
1984 ◽  
Vol 22 (138) ◽  
pp. 271-280 ◽  
Author(s):  
Randall R. Reeves ◽  
Donald K. Ljungblad ◽  
Janet T. Clarke

AbstractSeismic survey activities in the western Beaufort Sea, involving ships and sound production, were monitored in autumn 1982 for their possible effects on migrating Bowhead whales Balaena mysticetus. The study, begun in 1981 by die Minerals Management Service of the US Department of the Interior, covered offshore waters between the Alaskan coast and 72°N. Distribution, behaviour and numbers of whales were recorded, and procedures were established for monitoring and controlling seismic activities in their presence.


2001 ◽  
Vol 110 (5) ◽  
pp. 2750-2750
Author(s):  
Charles R. Greene ◽  
William C. Burgess ◽  
W. John Richardson

2021 ◽  
Vol 8 ◽  
Author(s):  
Rebecca A. Dunlop ◽  
Janelle Braithwaite ◽  
Lars O. Mortensen ◽  
Catriona M. Harris

The Population Consequences of Disturbance (PCoD) model is a conceptual framework used to assess the potential for population-level consequences following exposure of animals to a disturbance activity or stressor. This framework is a four-step process, progressing from changes in individual behavior and/or physiology, to changes in individual health, then vital rates, and finally to population-level effects. Despite its simplicity, there are few complete PCoD models available for any marine mammal species due to a lack of data available to parameterize many of the steps. Here, we present an application of the PCoD framework for migrating humpback whales exposed to a simulated commercial seismic survey scenario. We approached the framework in two ways; first, progressing sequentially forwards through the steps and basing our assessment on lactating females. This cohort was considered to be the most vulnerable in terms of energetic costs of disturbance, and most likely to influence any change in population growth due to future breeding success. Field measurements of behavioral responses of migrating humpback whales to seismic air guns from a previous study were used to parameterize an agent-based model (ABM). This ABM was used to estimate the probability of response, where a response was defined as a change in the migratory movement of female-calf pairs, and the duration of any resulting delay in migration. We then estimated the energetic consequences of any delay in migration for the lactating females and created population growth models with which to assess any population-level effects. The results of the forwards approach suggested a low potential for population consequences of seismic surveys on migrating humpbacks. Working backwards through the framework, we investigated “worst case” scenarios that could potentially lead to a population-level effect. Here, we started with increasing calf mortality and assumed that an exposure time greater than 48 h would increase mortality risk. We determined the most likely context in which this exposure would occur (resting area) and then tested this context within an ABM. This backwards approach illustrates how the PCoD model can be used to make management decisions regarding animal populations and exposure to anthropogenic stressors.


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