Research Question

My research objective was to investigate the spatial scale and locations of surface feeding sites of humpback whales (Megaptera novaeangliae) in the Stellwagen Bank National Marine Sanctuary (SBNMS) in the southern Gulf of Maine, USA, and to investigate movement parameters of the whales.

 

Dataset

The existing data for this analysis stems from a long-term study investigating humpback whale behavior and ecology in the southern Gulf of Maine, USA, (for more details, see Friedlaender et al. 2009). Almost every summer since 2004, whales were equipped with non-invasive tags that recorded detailed information on the underwater movement of the whales or collected video-footage of the behavior of the tagged animal and associated whales. During daylight deployments that usually lasted for up to 8 hours, focal follows were conducted from a small boat following the tagged whale, during which detailed information on the behavior of the tagged whale at the water surface was collected. Because the tags did not contain a GPS, range and bearing information on the whale were also collected at least once when the whale was observed at the surface in between consecutive dives, usually resulting in the collection of one location point every 3-5 min (temporal extent: 117-260 min), with a spatial resolution of tens or hundreds of meters (less when the whale is foraging, more when it is traveling) (extent: 103-104 m). Continuous GPS locations of the boat were automatically collected. Based on the time stamps of the range/bearing data and the boat GPS data, the GPS locations collected at or close to the time the range and bearing data was collected were identified and together this data was used to calculate the locations of the whale.

 

Hypotheses

  • Surface feeding areas (FPT radius) are larger than mean length of prey schools (139 m, Hazen et al. 2009)
  • Size of surface feeding areas (FPT radius) positively correlated with group size (larger groups search larger area)
  • Positive correlation between FPT (at FPT radius) and depth and slope (prey habitat preference)
  • No autocorrelation in FPT
  • No autocorrelation of absolute turning angles on spatial scale of surface feeding sites (unpredictable foraging movement)

 

Approaches

  • Scan focal follow data for deployments during which surface feeding was major behavior
  • For these deployments, use R package adehabitatLT (Calegne 2011) to implement first-passage time (FPT) metric
    • Based on the location points of an animal and the time spend at/between these points, FPT radius identifies the spatial scale on which foraging effort along an animal’s path is concentrated (Fauchald & Tveraa 2003)
    • The time spent within this radius of each location point is called FPT. Location points with high FPT identify important foraging areas along the animal’s path (Bailey & Thompson 2006)
  • Compare FPT radius for each deployment to the group size during the deployment
  • Map color-coded FPT (at FPT radius) for each deployment onto bathymetry and slope raster layer in ArcMap
  • Extract depth and slope values for each location point
  • Connect the location points for each deployment with lines to show path of the animal
  • Buffer each location point by the value of the FPT radius for the respective deployment
  • Dissolve buffer for better visibility of the range of foraging effort around the location points and relative to underlying depth and slope rasters
  • Perform linear regression of FPT against depth/slope for each deployment and calculate r2 value
  • Calculate autocorrelation in turning angles and first-passage time using Moran’s I coefficient of autocorrelation in the pgirmess R-package

 

Results

Three deployments (188a, 188b_f, 195b) were identified for which suitable location data existed and that contained a large amount of surface feeding. Because deployment 188b_f originally also contained a large amount of traveling, here, only the part of the path with surface feeding activity was included in the analysis. Table 1 summarizes the results of the analyses.

 

Table 1: FPT radius, group size and correlation coefficient r2 for the regression of FPT against depth and slope are shown for each of the three deployments.

final_results

  • There does not seem to be a fixed spatial scale of surface feeding as the values of FPT radius range between 90 and 347 m.
  • It is difficult to investigate a potential relationship between FPT radius and group size as the foraging groups were very dynamic with changes in group size throughout the deployments. However, the smallest FPT radius was calculated for the only group that consisted of group size 1 for some part of the deployment, and the largest FPT radius was observed for the group that had the largest group size during some part of the deployment.
  • Significant relationships between FPT and depth or slope were found for two of the three deployments. For deployment 188a, depth explained 17.2 % of the variability in FPT (p=0.001). For deployment 188b_f, depth explained 14.2 % (p<0.001) and slope 29.2 % (p<0.001) of the variability in FPT (Figures 1-3)
  • Autocorrelation in FPT was found for all three deployments at scales greater than the FPT radius for each deployment (Figure 4)
  • Autocorrelation in absolute turning angles was found for two of three deployments at spatial scales much greater than FPT radius.

 

Figures 1-3: Whale paths, FPT and FPT radius mapped on slope chart of SBNMS (USGS/SBNMS). Whale locations for each deployment (circles) are color-coded to represent high/low FPT (red/green) at FPT radius (purple buffer) and connected with lines to show temporal sequence of locations. From top to bottom: 188a, 188b_f, 195b.

final_188a_track

final_188b_track

final_195b_track

 

Figure 4: Moran’s I autocorrelation coefficient calculating FPT autocorrelation plotted against lag distance for all deployments. Vertical lines represent FPT radius for each deployment. Red circles indicate significant autocorrelation in FPT.

final_AC fpt

 

 

Discussion and Significance

The three deployments investigated here showed a wide range of spatial scales of surface feeding. However, there is some indication that this variability could at least in part be explained by the differences in group size between the three groups, with larger groups having a greater spatial scale of surface feeding. The spatial scale of surface feeding is somewhat consistent with the mean size of prey schools. Bathymetry and bathymetric relief seem to have some influence on the locations of concentrated search effort (FPT). This is obvious from both the correlation coefficients of FPT and depth/slope as well as from the map. However, the results of this analysis are obscured by the autocorrelation in FPT. Since the deployments are opportunistic observations, no absence data was analyzed here and the sample size is small, it is unclear whether non-feeding whales also concentrate their activity on similar locations within SBNMS and whether surface feeding also occurs over other parts of SBNMS with different ranges of depth/slope. The spatial scale of autocorrelation in FPT (451-596 m) is more similar between the three whales than the spatial scale of foraging effort. This could suggest the existence of a prey searching mechanism that is similar for all three whales and works on a scale larger than the foraging mechanism captured by the FPT analysis.

A better understanding of the foraging mechanisms of the whales can help to improve management decisions aimed at mitigating ship strike and entanglement risks in the SBNMS.

 

Learning outcomes

  • Working with spatial data in R
  • Implementing FPT metric
  • Calculating spatial autocorrelation
  • Extracting raster values in ArcMap

 

 References

Bailey, H. & Thompson P. (2006). “Quantitative Analysis of Bottlenose Dolphin Movement Patterns and Their Relationship with Foraging: Movement Patterns and Foraging.” Journal of Animal Ecology 75 (2): 456–65.

Calenge, C. (2011). “Analysis of Animal Movements in R: The adehabitatLT Package.” Saint Benoist, Auffargis, France: Office Nationale de La Chasse. http://cran.gis-lab.info/web/packages/adehabitatLT/vignettes/adehabitatLT.pdf.

Fauchald, P. & Tveraa T. (2003). “Using First-Passage Time in the Analysis of Area-Restricted Search and Habitat Selection.” Ecology 84 (2): 282–88.

Friedlaender, A. S., Hazen, E. L., Nowacek, D. P., Halpin, P. N., Ware, C., Weinrich, M. T., Hurst, T., Wiley, D. (2009). Diel changes in humpback whale Megaptera novaeangliae feeding behavior in response to sand lance Ammodytes spp. behavior and distribution. Marine Ecology Progress Series 395: 91–100.

Hazen E.L., Friedlaender A.S., Thompson M.A., Ware C.R., Weinrich M.T., Halpin P.N., Wiley D.N. (2009). “Fine-Scale prey aggregations and foraging ecology of humpback whales Megaptera Novaeangliae.” Marine Ecology Progress Series 395: 75–89.

 

Jennifer Allen and Michael Thompson calculated and provided the whale locations based on boat GPS and range and bearing data. Thank you!

In my last blog post, I analyzed spatial autocorrelation in the whale movement parameters swimming speed and turning angles between consecutive segments of the whale’s trajectory for a single whale. In this update, I am expanding on this analysis by analyzing over a range of distances the spatial autocorrelation in swimming speed and turning angles in the trajectories of three foraging whales in the Stellwagen Bank National Marine Sanctuary. Positive autocorrelation in either parameter would mean that, when comparing two trajectory segments, the values for this parameter are similar between the two segments, and negative autocorrelation would mean that they are not similar. A correlogram shows the values of the autocorrelation coefficient for a range of distances between the trajectory segments. Here, I am presenting results from the analysis of the whale trajectories using the R CRAN adehabitatLT package (Calenge 2011).

The correlogram below shows the Moran’s I autocorrelation coefficient for the swimming speeds of three whales. Two whales show significant autocorrelation in swimming speed over short distances (<1000 m) (p<0.05, indicated by red circles). This means that during segments of the whale’s trajectories that are within 1000 m of each other, the whales maintained similar speeds. This is not surprising because generally it does not seem likely that the whales would abruptly change their swimming speed over such short distances.

AC speed

After converting the turning angles to radians, the analysis of autocorrelation in turning angles (Moran’s I) revealed that the turning angles of only one trajectory were significantly positively autocorrelated at distances of 1000 and 2000 m (p<0.05, indicated by red circles).

AC angles

 

 

Next, I used the R CRAN package adehabitatLT (Calenge 2011) to calculate first-passage time (Fauchald & Tveraa 2003) as metric for the search effort along each whale’s trajectory, and used linear regression to relate first-passage time to the environmental variables water depth and seafloor slope. The image below shows the three trajectories (in turquoise: 195b, purple: 188b_f, red: 188a) on a slope chart of the Stellwagen Bank National Marine Sanctuary area (USGS/NOAA).

slope_traj

 

 

Basend on the description by Fauchald & Tveraa (2003), for each trajectory, first-passage time quantifys the spatial scale of the animal’s foraging effort. The values of first-passage time at this spatial scale distinguish areas with high foraging effort (long first-passage time) from areas with low foraging effort (short first-passage time). The color-coded figure below shows first-passage time for whale 188b_f relative to seafloor slope (red: long first-passage time, green: short first-passage time).

slope_fpt

Simple linear regression revealed that depth explained 17.2% of the variance in first-passage time for the trajectory of whale 188a (p=0.001). Separately, depth and slope explained 14.2 and 29.2 %, respectively, of the variance in first-passage time for the trajectory of whale 188b_f (each p<0.0005) (see figures below). For the trajectory of whale 195b, neither depth nor slope were significant predictors of first-passage time (each p>0.2).

regressionSome authors (see Calenge 2011 for details) have suggested the analysis of autocorrelation of movement parameters of an animal’s trajectory following the standardization of the segment lengths. I will investigate this method in a follow-up analysis. Furthermore, I will re-analyze autocorrelation in turning angles using the absolute values of the turning angles instead of radians to facilitate the interpretation of the results.

 

Literature cited:

Calenge, C. 2011. “Analysis of Animal Movements in R: The adehabitatLT Package.” Saint Benoist, Auffargis, France: Office Nationale de La Chasse. http://cran.gis-lab.info/web/packages/adehabitatLT/vignettes/adehabitatLT.pdf.

Fauchald, P. & T. Tveraa. 2003. “Using First-Passage Time in the Analysis of Area-Restricted Search and Habitat Selection.” Ecology 84 (2): 282–88.

The goal of this exercise was to investigate spatial autocorrelation in the movement parameters of a foraging humpback whale. I used location points of sightings of the whale at the water surface between consecutive dives to infer the path of the whale (Friedlaender et al., 2009). To facilitate the analysis, I assumed linear travel of the whale below the surface between consecutive surfacings. I projected the location points and used the adehabitatLT package in R CRAN (Calenge, 2011) to plot the location points of the whale as well as the linear travel segments between these points (see graph below).trajectorymn06_188a

The blue triangle indicates the first, the red square the last observation of the whale at the surface.

Using projected data, the adehabitatLT package calculates the distance traveled by the whale between consecutive observations, the turning angle between consecutive linear segments of the whale’s path as well as the duration between the observations. Using the distance and duration data I calculated the swimming speed of the whale.

Then I calculated the spatial autocorrelation in swimming speed and turning angles using Moran’s I for the entire path, and also for a small section of the path which I assumed to be a foraging area of the whale (cluster of points southeast of the blue triangle). In this small area, the whale spent a comparatively large amount of its time and swam shorter distances between consecutive surfacings, possibly indicating foraging activity.

A small p-value in one of the parameters would provide convincing evidence for the hypothesis that the movement of the whale is autocorrelated in the respective parameter, i.e. that neighboring locations have more similar values than locations that are further apart.

The results from the current analysis (see table below) provide moderate evidence for spatial autocorrelation in swimming speed for the analysis of the entire path, indicating that the whale swam slower in certain parts of its path and faster in other parts (Calenge 2011). However there was no evidence to suggest that travel speed in the small foraging area was autocorrelated. This could be explained by the fact that in the foraging area, the whale swam at a constant, slow speed to the probability of prey detection or encounter (Benhamou, 1992). When leaving this foraging area, the whale is likely to increase its speed, resulting in separate areas of the whale’s path with lower and higher swimming speeds, which would explain the autocorrelation in swimming speed observed for the entire path.

 

Entire path Foraging area
Speed Angle Speed Angle
p-value 0.017 0.841 0.702 0.651

 

 

Benhamou, S. (1992). Efficiency of area-concentrated searching behaviour in a continuous patchy environment. Journal of Theoretical Biology – J THEOR BIOL, 159(1), 67–81. http://doi.org/10.1016/S0022-5193(05)80768-4

Calenge, C. (2011). Analysis of Animal Movements in R: the adehabitatLT Package. Saint Benoist, Auffargis, France: Office Nationale de La Chasse. Retrieved from http://cran.gis-lab.info/web/packages/adehabitatLT/vignettes/adehabitatLT.pdf

Friedlaender, A. S., Hazen, E. L., Nowacek, D. P., Halpin, P. N., Ware, C., Weinrich, M. T., Hurst, T., Wiley, D. (2009). Diel changes in humpback whale Megaptera novaeangliae feeding behavior in response to sand lance Ammodytes spp. behavior and distribution. Marine Ecology Progress Series, 395, 91–100. http://doi.org/10.3354/meps08003

 

 

My research objective is to investigate two spatial aspects of humpback whale (Megaptera novaeangliae) surface feeding in and around the Stellwagen Bank National Marine Sanctuary in the southern Gulf of Maine, USA. Specifically, I aim to:

  • Quantify the spatial scale of this behavior.
  • Investigate whether this behavior is more frequently observed in certain areas of the study region.

Most studies investigating the spatial scale of humpback whale movement have focused on large spatial and temporal scales, using 1-2 location points per day over the course of several days or weeks during which the animals traveled hundreds or thousands of kilometers (Dalla Rosa et al. 2008; Heide-Jorgensen and Laidre 2007; Kennedy et al. 2013). In contrast, the proposed study aims at investigating the detailed movement of these whales on the temporal and spatial scales of daily bouts of foraging events. Analyzing such fine-scale foraging movement patterns can contribute to our knowledge of how marine predators search for patchily distributed resources (Levin 1992; Pinaud and Weimerskirch 2005).

The existing data for this analysis stems from a long-term study investigating humpback whale behavior and ecology in the southern Gulf of Maine, USA, (for more details, see Friedlaender et al. 2009). Almost every summer since 2004, whales were equipped with non-invasive tags that recorded detailed information on the underwater movement of the whales or collected video-footage of the behavior of the tagged animal and associated whales. During daylight deployments that usually lasted for up to 8 hours, focal follows were conducted from a small boat following the tagged whale, during which detailed information on the behavior of the tagged whale at the water surface was collected. Because the tags did not contain a GPS, range and bearing information on the whale were also collected at least once when the whale was observed at the surface in between consecutive dives, usually resulting in the collection of one location point every 3-5 min. Continuous GPS locations of the boat were automatically collected. Based on the time stamps of the range/bearing data and the boat GPS data, the GPS location collected at or close to the time the range and bearing data was collected, were identified and together this data was used to calculate the location of the whale.

The analysis proposed here will use the whale behavioral observation data to identify focal follows during which surface feeding was observed. The location data of these focal follows will be used for the following analysis. For each focal follow of a surface feeding whale, I will use the R package adehabitat (Calenge 2011) to implement first-passage time analysis to calculate the spatial scale of surface feeding, and to identify areas of intense foraging effort. The following description of the method is based on Fauchald & Tveraa (2003). First-passage time is a metric used to quantify search effort along an animal movement path. Around each location point, a circle of a given radius is created, and the amount of time the animal spent within the area of the circle is measured. The measurement is then repeated for each location point of the animal’s path with successively increasing circle radii. Increasing the radii will increase the amount of time the animal spent within the circle, but the increase in time will be greater in areas of intense search effort compared to areas through which the animal was simply traveling. The radius at which the variance in first-passage time between the different location points is greatest represents the spatial scale of foraging effort. I intend to statistically test for differences in the spatial scales of surface feeding between individuals and as a function of group size. At the radius representing the spatial scale of foraging, those circles with the longest first-passage times identify areas where foraging effort is concentrated (Bailey & Thompson 2006). Comparing the locations of intense foraging effort between individuals, areas within the study region can be identified that represent suitable foraging habitat (Bailey & Thompson 2006). The expected outcome of this part of the analysis is a map of the study region displaying locations of suitable foraging habitat based on first-passage time calculation.

I expect to find that different individuals have a similar spatial scale of surface feeding, as I anticipate that the spatial scale of foraging is correlated with spatial metrics of prey schools (Benoit-Bird et al. 2013). Because the spatial scale of search effort is likely to be larger than the spatial scale of the prey patches themselves, I expect the spatial scale of foraging for all individuals to be larger than the average prey school length in the area, which is ca. 139 m (Hazen et al. 2009). I expect to find a positive correlation between the spatial scale of surface feeding and group size because I anticipate that larger groups will cover a wider area during their search. I expect to see a concentration of surface feeding locations in the western part of the sanctuary region as this has been found to be an important feeding area in a previous study using a subset of the data I am planning on analyzing here (Hazen et al. 2009). This is due to the substrate type, topography and oceanographic conditions in this area which serve to attract and aggregate prey (Hazen et al. 2009).

I currently have basic knowledge of ArcMap and R and no experience with Python or Modelbuilder.

 

Literature cited:

Bailey, H. & P. Thompson. 2006. “Quantitative Analysis of Bottlenose Dolphin Movement Patterns and Their Relationship with Foraging: Movement Patterns and Foraging.” Journal of Animal Ecology 75 (2): 456–65. doi:10.1111/j.1365-2656.2006.01066.x.

Benoit-Bird, K.J., B.C. Battaile, C.A. Nordstrom, and A.W. Trites. 2013. “Foraging Behavior of Northern Fur Seals Closely Matches the Hierarchical Patch Scales of Prey.” Marine Ecology Progress Series 479 (April): 283–302. doi:10.3354/meps10209.

Calenge, C. 2011. “Analysis of Animal Movements in R: The adehabitatLT Package.” Saint Benoist, Auffargis, France: Office Nationale de La Chasse. http://cran.gis-lab.info/web/packages/adehabitatLT/vignettes/adehabitatLT.pdf.

Dalla Rosa, L., E. R. Secchi, Y. G. Maia, A. N. Zerbini, and M. P. Heide-Jørgensen. 2008. “Movements of Satellite-Monitored Humpback Whales on Their Feeding Ground along the Antarctic Peninsula.” Polar Biology 31 (7): 771–81. doi:10.1007/s00300-008-0415-2.

Fauchald, P. & T. Tveraa. 2003. “Using First-Passage Time in the Analysis of Area-Restricted Search and Habitat Selection.” Ecology 84 (2): 282–88.

Friedlaender, A.S., E.L. Hazen, D.P. Nowacek, P.N. Halpin, C. Ware, M.T. Weinrich, T. Hurst, and D. Wiley. 2009. “Diel Changes in Humpback Whale Megaptera Novaeangliae Feeding Behavior in Response to Sand Lance Ammodytes Spp. Behavior and Distribution.” Marine Ecology Progress Series 395 (December): 91–100. doi:10.3354/meps08003.

Hazen, E.L., A.S. Friedlaender, M.A. Thompson, C.R. Ware, M.T. Weinrich, P.N. Halpin, and D.N. Wiley. 2009. “Fine-Scale Prey Aggregations and Foraging Ecology of Humpback Whales Megaptera Novaeangliae.” Marine Ecology Progress Series 395 (December): 75–89. doi:10.3354/meps08108.

Heide-Jorgensen, M. P., and K. L. Laidre. 2007. “Autumn Space-Use Patterns of Humpback Whales (Megaptera Novaeangliae) in West Greenland.” Journal of Cetacean Research and Management 9 (2): 121.

Kennedy, A.S., A.N. Zerbini, O.V. Vásquez, N. Gandilhon, P.J. Clapham, and O. Adam. 2013. “Local and Migratory Movements of Humpback Whales (Megaptera Novaeangliae) Satellite-Tracked in the North Atlantic Ocean.” Canadian Journal of Zoology 92 (1): 9–18. doi:10.1139/cjz-2013-0161.

Levin, S.A. 1992. “The Problem of Pattern and Scale in Ecology: The Robert H. MacArthur Award Lecture.” Ecology 73 (6): 1943. doi:10.2307/1941447.

Pinaud, D.D. & H. Weimerskirch. 2005. “Scale-Dependent Habitat Use in a Long-Ranging Central Place Predator.” Journal of Animal Ecology 74 (5): 852–63. doi:10.1111/j.1365-2656.2005.00984.x.