Contributors | Affiliation | Role |
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Acevedo-Gutierrez, Alejandro | Western Washington University (WWU) | Lead Principal Investigator |
Bromaghin, Jeffrey F | United States Geological Survey (USGS) | Co-Principal Investigator |
Jeffries, Steven J | Washington Department of Fish and Wildlife | Co-Principal Investigator |
Kennish, John M | University of Alaska, Anchorage (UAA) | Co-Principal Investigator |
Lance, Monique M | Washington Department of Fish and Wildlife | Co-Principal Investigator |
Levin, Philip S. | National Marine Fisheries Service (NMFS) | Co-Principal Investigator |
Rauch, Shannon | Woods Hole Oceanographic Institution (WHOI BCO-DMO) | BCO-DMO Data Manager |
Number of seals counted during several aerial surveys of the Salish Sea during July and August of 2008. Data are also available from 2007 surveys.
Related publications: (Both available from Alejandro Acevedo's lab website.)
Howard, S. 2009. Seasonal energy budgets to model energy use and prey consumption in harbor seals (Phoca vitulina) in the San Juan Islands, WA. MSc thesis, Department of Biology, Western Washington University, Bellingham, WA.
Hardee, S. 2008. Movements and home ranges of harbor seals (Phoca vitulina) in the Georgia Basin: implications for marine reservinland waters of the Pacific Northwest. MSc thesis, Department of Biology, Western Washington University, Bellingham, WA.
Following protocol from Jeffries et al. (2003), with collaboration from the Washington Department of Fish and Wildlife, surveys were flown in a Cessna 185 at 200 to 300 m, moving at 90 kt, on two or three consecutive days during moderately low tides. Flights were made over the region moving with the tide, to cover the entire area within +/- 2 h from low tide. Visual counts were taken on sites with < 25 seals and digital photographs and visual counts were taken concurrently at sites with > 25 animals, using a Nikon D100 with a 200 mm lens. The time was documented on the survey log for all haul-out counts, haul-out estimates and photographs. Surveys were conducted under permit 782-1702 awarded to the Washington Department of Fish and Wildlife by the Office of Protected Resources.
Selection of flight times was not only dependent on tidal conditions but also on time of day. If one chooses tidal heights that are extremely low, there is a risk that the survey underestimates the number of seals in the region because normal haul-out sites may be inaccessible (Jeffries, pers. comm.). Additionally, fog may become problematic for flying if the tide window, especially in August, is too early in the morning. These factors were taken into account when selecting the survey dates.
Tide times on dates of aerial surveys are as follows:
Date Tide Station Tide Time Tide Height (ft)
07/17/08 Port Townsend 10:12 -1.7
07/18/08 Port Townsend 10:49 -1.8
07/18/08 Seattle 11:48 -1.6
07/31/08 Port Townsend 09:44 -2.6
07/31/08 Seattle 10:39 -2.9
08/01/08 Port Townsend 10:32 -2.4
08/14/08 Port Townsend 09:14 -0.9
08/15/08 Port Townsend 09:52 -1.0
References:
Jeffries SJ, Huber HR, Calambokidis J, Laake J (2003) Trends and status of harbor seals in Washington State: 1978-1999. Journal of Wildlife Management 67:208-219. Available online from Washington Department of Fish and Wildlife.
Huber HR, Jeffries SJ, Brown RF, DeLong RL, Van Blaricom G (2001) Correcting aerial survey counts of harbor seals (Phoca vitulina richardsi) in Washington and Oregon. Marine Mammal Science 17:276-293. DOI: 10.1111/j.1748-7692.2001.tb01271.x
The estimation of seal population size based on haul-out counts requires a correction factor to account for seals in the water at the time of the survey (Huber et al. 2001, Jeffries et al. 2003), however, correction factors have NOT been applied to these data.
BCO-DMO made the following edits to the dataset:
- Blanks and 'NA' were replaced with 'nd' to indicate 'no data';
- Parameter names were modified to conform with BCO-DMO conventions;
- day, month, and year were separated from original date column;
- Abbreviated species names were replaced with the full species names;
- Corrected typos in the year column from '2009' to '2008';
- lat and lon were added based on the site_code (2007 site_codes are the same locations as 2008).
File |
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seal_counts_2008.csv (Comma Separated Values (.csv), 53.87 KB) MD5:72535028c0ca4c0387d01ae142a587f0 Primary data file for dataset ID 3707 |
Parameter | Description | Units |
date | Month, day, and year in mmddyy format (local time). | mmddyy |
month | 2-digit month of year, local time. | mm (01 to 12) |
day | 2-digit day of month, local time. | dd (01 to 31) |
year | 4-digit year (local time). | YYYY |
site_code | Numeric identifier for the sampling site. | unitless |
lat | Latitude; North = positive. (Added by BCO-DMO; assumes site_codes used in 2008 are the same locations as 2007.) | decimal degrees |
lon | Longitude; West = negative. (Added by BCO-DMO; assumes site_codes used in 2008 are the same locations as 2007.) | decimal degrees |
time_local | Local time when the survey occurred, in hours and minutes, 24-hour clock. | HH:MM |
species | Name of the species: | text |
est_total | Estimated total number of seals. | unitless |
est_pups | Estimated number of pups. | unitless |
count_total | Total number seals, corrected using photos if available. | unitless |
count_pups | Number of pups, corrected using photos if available. | unitless |
photo | TRUE = photo was taken; FALSE = no photo was taken. | unitless |
photo_no | The photograph identification number, if a photo was taken. | unitless |
count_type | 1 = hauled out; 2 = in the water. | unitless |
count_q_flag | Count quality flag: | unitless |
comment | Remarks/comments about the observation. | text |
Dataset-specific Instrument Name | Camera |
Generic Instrument Name | Camera |
Dataset-specific Description | Photos were taken using a Nikon D100 with a 200 mm lens. |
Generic Instrument Description | All types of photographic equipment including stills, video, film and digital systems. |
Website | |
Platform | Cessna-185 |
Start Date | 2008-07-17 |
End Date | 2008-08-15 |
Description | With collaboration from the Washington Department of Fish and Wildlife, aerial surveys of harbor seals were flown in a Cessna 185 at 200 to 300 m. Six flights were made between 07/17/2008 and 08/15/2008 in support of the project "Responses of Seals and Sea Lions to Increased Rockfish Density". |
From NSF proposal:
This project is a collaborative study of the responses of harbor seals and other mammalian predators to changes in prey density in Puget Sound. The general study approach will involve multi-year field estimates to observe the responses of predators to rockfish density in protected areas, candidate marine reserves, and unprotected sites.
The collaborating investigators will estimate 1) rockfish density using visual and mark and recapture techniques; 2) predator abundance using aerials surveys and dedicated land observations; and 3) predator food consumption using scat to describe diet, tagging of harbor seals to describe individual foraging sites, and population-based and individual bioenergetics models to describe consumption of rockfish. The investigators will also take into account confounding factors that might explain predator behavior, such as environmental variables and alternative prey, by creating a GIS database from available information from the area. The different field observations and database estimates are explicitly linked through a common hypothesis and coordinated methodologies, and their results will be integrated into a model describing the impact of predation on rockfish populations. The responses of top predators to changes in prey density and their impact on fish populations of interest are unknown. This study will evaluate the effectiveness of MPAs as fish refugia, offer a framework for the management and conservation of marine resources, and provide an exciting opportunity for students to participate in ecological and conservation research.
Hypotheses:
1) Harbor seals and other pinniped species show aggregative responses to changes in prey density. Hence, their abundance will increase with fish density.
2) Harbor seals and other pinniped species show Type 2 or 3 functional responses to changes in prey density. Thus, their consumption rate of a particular prey type follows an asymptotic or sigmoidal curve relative to the prey’s density, respectively.
3) Predation by harbor seals and other pinniped species is sufficiently intense that it impedes recovery of depleted fish populations.
Objectives:
1) Quantify the number of harbor seals and other pinniped species in relation to rockfish density and other environmental (confounding) factors.
2) Estimate the consumption rate of harbor seals and other pinniped species in relation to rockfish density and other prey species.
3) Correlatively estimate the influence of predation by harbor seals and other pinniped species on survivorship and population size of rockfish.
Publications resulting from this NSF award:
Bjorland, R. H., Pearson, S. F, Jeffries, S. J, Lance, M. M., Acevedo- Gutiérrez, A. & Ward, E. J. 2015. Stable isotope mixing models elucidate sex and size effects on the diet of a generalist marine predator. Marine Ecology Progress Series 526: 213-225. DOI: 10.3354/meps11230
Bromaghin, J. F., Lance, M. M., Elliott, E. W., Jeffries, S. J., Acevedo-Gutierrez, A. & Kennish, J. M. 2013. New insights into the diets of harbor seals in the Salish Sea of western North America revealed by quantitative fatty acid signature analysis. Fishery Bulletin 111: 13-26. DOI: 10.7755/FB.111.1.2
Buzzell, B.1, Lance, M. & Acevedo-Gutiérrez, A. 2014. Spatial and temporal variation in river otter (Lontra canadensis) diet and predation on rockfish (Genus Sebastes) in the San Juan Islands, Washington. Aquatic Mammals 40: 150- 161. DOI: 10.1578/AM.40.2.2014.150
Howard, S., Lance, M., Jeffries, S. & Acevedo-Gutierrez, A. 2013. Fish consumption by harbor seals (Phoca vitulina) in the San Juan Islands, WA. Fishery Bulletin 111: 27-41. DOI: 10.7755/FB.111.1.3
Lance, M. M., Chang, W.-Y., Jeffries, S. J., Pearson, S. F. & Acevedo-Gutierrez, A. 2012. Harbor seal diet in northern Puget Sound: implications for the recovery of depressed fish stocks. Marine Ecology Progress Series 464:257-271. DOI:10.3354/meps09880
Luxa, K. & Acevedo-Gutierrez, A. 2013. Food habits of harbor seals (Phoca vitulina) in two estuaries in the central Salish Sea. Aquatic Mammals 39: 10- 22. DOI: 10.1578/AM.39.1.2013.10
Peterson, S., Lance, M. M., Jeffries, S. J. & Acevedo-Gutierrez, A. 2012. Long distance movements and disjunct spatial use of harbor seals (Phoca vitulina) in the inland waters of the Pacific Northwest. PLoS ONE 7: e39046. DOI: 10.1371/journal.pone.0039046
Thomas, AC; Lance, MM; Jeffries, SJ; Miner, BG; Acevedo-Gutierrez, A. 2011. Harbor seal foraging response to a seasonal resource pulse, spawning Pacific herring. Marine Ecology-Progress Series, v.441. p. 225. DOI: 10.3354/meps09370
Ward, EJ; Levin, PS; Lance, MM; Jeffries, SJ; Acevedo-Gutierrez, A. 2012. Integrating diet and movement data to identify hot spots of predation risk and areas of conservation concern for endangered species. Conservation Letters, v.5, p. 37. DOI: 10.1111/j.1755-263X.2011.00210.x
Wilson, K.2, Lance, M., Jeffries, S. & Acevedo-Gutiérrez, A. 2014. Fine-scale variability in harbor seal foraging behavior. PLoS ONE 9: e92838. DOI: 10.1371/journal.pone.0092838.
Funding Source | Award |
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NSF Division of Ocean Sciences (NSF OCE) |