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Final Technical Report: - Southwest Fisheries Science Center - NOAA

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isobath, and Beaufort sea state. Distance to the 2,000 m isobath was added to the list of<br />

predictors because sighting plots suggested that this variable could potentially improve model<br />

performance for some species (e.g., sperm whale, Physeter macrocephalus, and Baird’s beaked<br />

whale, Berardius bairdii) that are generally found only in slope or deep waters. This variable<br />

was coded to indicate whether the location was deeper (-) or shallower (+) than the 2,000 m<br />

isobath. Beaufort sea state affects the probability of detecting animals (Barlow et al. 2001), and<br />

the average observed sea state value on each segment was included as a continuous predictor<br />

variable in our models in order to account for sighting conditions.<br />

In addition to the variables used for the remotely-sensed models, the combined models<br />

included three potential predictors derived from data collected in situ: sea surface salinity, the<br />

natural logarithm of surface chlorophyll concentration, and mixed layer depth, measured as the<br />

depth at which the water temperature was 0.5C less than at the surface. Remotely sensed<br />

measures of SST and CV(SST) were used in the combined models because the remotely-sensed<br />

CV(SST) was found to be more effective at characterizing frontal regions than our in situ<br />

CV(SST) measures (Becker 2007), and SST measures performed similarly. The in situ data were<br />

derived in one of two ways. Salinity was sampled continuously along the transect and segmentspecific<br />

estimates were obtained by averaging values within 5 km of the mid-point of each<br />

transect segment included in the analysis. Chlorophyll and mixed layer depth were measured<br />

much less frequently, and a linear interpolation between nearby stations did not accurately<br />

capture values at the edges of the study area or when samples were sparse, causing 'bull’s eye'<br />

effects in estimated cetacean density. Therefore, the data were first contoured (see Section 3.2)<br />

to provide a 2-D surface of estimated chlorophyll and mixed-layer depth values, and segment<br />

mid-point values were extracted from the contour grid using the Surfer 8.0 (Golden Software,<br />

Inc) Residuals feature.<br />

Density Estimation<br />

Segment-specific density estimates were derived by incorporating the predicted values<br />

for encounter rate and group size into the standard line-transect equation (Buckland et al. 2001)<br />

as described by Becker (2007) and in Section 3.3.1. We relied on published values of detection<br />

probability (f(0) and g(0)) for each species as estimated from the same survey data used for<br />

model development (Barlow 2003). Published values for many species were stratified by group<br />

size and, for purposes of estimating densities, we incorporated weighted f(0) and g(0) values<br />

based on the number of small and large groups observed during the surveys (Becker 2007, Table<br />

4). All final model predictions were made using the average observed Beaufort sea state for<br />

conditions 0-5 during the SWFSC cruises. This is appropriate because it corresponds to the<br />

conditions for which the line-transect parameters f(0) and g(0) were estimated (Barlow 2003).<br />

For Dall’s porpoise and small beaked whales, published f(0) and g(0) values were available only<br />

for Beaufort conditions of 0-2. Model predictions for this species and guild were made using the<br />

average observed Beaufort sea state for conditions 0-2.<br />

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