AMNWR 2019/06 SURVEYS OF LEDGE-NESTING SEABIRDS AT SELECTED SITES IN THE NORTHERN BERING SEA AND EASTERN CHUKCHI SEA, JULY-AUGUST 2018 Donald E. Dragoo, Marianne Aplin, Aaron Christ, Heather M. Renner, Nora A. Rojek, Jeffrey C. Williams, and Kara Zwickey Key Words: Alaska, Bering Sea, black-legged kittiwake, Bluff, Cape Lewis, Cape Lisburne, Cape Thompson, Chamisso Island, Chukchi Sea, common murre, Kotzebue Sound, Norton Sound, pelagic cormorant, Phalacrocorax pelagicus, populations, productivity, Rissa tridactyla, seabirds, Sledge Island, thick-billed murre, Topkok Head, Uria aalge, Uria lomvia, wildlife U.S. Fish and Wildlife Service Alaska Maritime National Wildlife Refuge 95 Sterling Hwy, Suite 1 Homer, Alaska, USA 99603-7472 September 2019 Cite as: Dragoo, D. E., M. Aplin, A. Christ, H. M. Renner, N. A. Rojek, J. C. Williams, and K. Zwickey. 2019. Surveys of ledge-nesting seabirds at selected sites in the northern Bering Sea and eastern Chukchi Sea, July-August 2018. U.S. Fish and Wildl. Serv. Rep., AMNWR 2019/06. Homer, Alaska.
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AMNWR 2019/06 SURVEYS OF LEDGE-NESTING SEABIRDS AT SELECTED SITES IN THE NORTHERN BERING SEA
AND EASTERN CHUKCHI SEA, JULY-AUGUST 2018
Donald E. Dragoo, Marianne Aplin, Aaron Christ, Heather M. Renner, Nora A. Rojek, Jeffrey C. Williams, and Kara Zwickey
U.S. Fish and Wildlife Service Alaska Maritime National Wildlife Refuge
95 Sterling Hwy, Suite 1 Homer, Alaska, USA 99603-7472
September 2019
Cite as: Dragoo, D. E., M. Aplin, A. Christ, H. M. Renner, N. A. Rojek, J. C. Williams, and K. Zwickey.
2019. Surveys of ledge-nesting seabirds at selected sites in the northern Bering Sea and eastern Chukchi Sea, July-August 2018. U.S. Fish and Wildl. Serv. Rep., AMNWR 2019/06. Homer, Alaska.
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TABLE OF CONTENTS Page
INTRODUCTION ........................................................................................................................................... 1 STUDY AREA ............................................................................................................................................... 1 METHODS ................................................................................................................................................... 2 Cruise itinerary ........................................................................................................................................ 3 INTERESTING OBSERVATIONS ................................................................................................................ 4 ACKNOWLEDGEMENTS ............................................................................................................................. 6 REFERENCES .............................................................................................................................................. 6 MAPS ........................................................................................................................................................... 8 FIGURES AND TABLES ............................................................................................................................. 10 Land-based index plots ........................................................................................................................ 11 Common and thick-billed murres ................................................................................................... 11 Black-legged kittiwakes .................................................................................................................. 20 Black-legged kittiwake nests .......................................................................................................... 29 Boat-based index plots ......................................................................................................................... 32 Common and thick-billed murres ................................................................................................... 32 Black-legged kittiwakes .................................................................................................................. 36 Black-legged kittiwake nests .......................................................................................................... 40 Locations of index plots ........................................................................................................................ 44 Cape Thompson ............................................................................................................................. 44 Cape Lisburne ................................................................................................................................ 45
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INTRODUCTION The eastern Chukchi Sea supports two large seabird nesting colonies, at capes Lisburne and Thompson. Both of these colonies are part of the Chukchi Sea Unit of the Alaska Maritime National Wildlife Refuge (AMNWR). Research of the seabird communities in this area was first conducted in 1959-1961 as part of the environmental assessment of the Cape Thompson area for Project Chariot, a U.S. Atomic Energy Commission proposal to use nuclear devices to create a harbor in the lower Ogoturuk Creek valley (Swartz 1966). Seabird data have been collected regularly at Cape Lisburne and sporadically at other Chukchi colonies since, sometimes with long intervals between visits. In 2018, the AMNWR vessel R/V Tiglax voyaged through the northern Bering Sea and, for the first time in 30 years, into the eastern Chukchi Sea (Figure 1). The purpose of the cruise was to conduct biological monitoring at Cape Thompson and, if possible, other Refuge sites in the area (Figure 2). We also wanted to assess the condition of Cape Thompson seabird monitoring plots, some of which were originally established in 1959, to determine if present-day counts would be comparable to those from the past. No refuge crew had been to Cape Thompson since 1995. STUDY AREA Cape Thompson: The Cape Thompson seabird colonies are situated in the Cape Thompson Subunit, Chukchi Sea Unit of the AMNWR at about 68⁰08’ N, 166º21’ W, approximately 40 km southeast of Point Hope, Alaska. The seabird nesting area comprises five large cliff faces (Colonies 1-5). Swartz (1966) estimated that the Cape Thompson colonies contained about 420,000 birds total (~393,000 common and thick-billed murres, and ~30,000 black-legged kittiwakes). Cape Lisburne: The Cape Lisburne seabird colony is located in the Ann Stevens-Cape Lisburne Subunit, Chukchi Sea Unit of the AMNWR at about 68º52’ N, 166º05’ W, approximately 62 km northeast of Point Hope, Alaska. Nesting habitat consists of about 7 km of precipitous, nearly continuous 15-200 m-high sedimentary limestone and shale sea-cliffs that begin about 1 km south of Kay Creek and end approximately 1 km west of the Cape Lisburne U. S. Air Force Long Range Radar Site (LRRS) runway (Roseneau et al. 2000). Currently, the seabird colony is estimated to number about 400,000-500,000 murres (comprising about 25-30% common murres and 70-75% thick-billed murres), 20,000-30,000 black-legged kittiwakes, and a total of a few thousand pelagic cormorants (Phalacrocorax pelagicus), glaucous gulls (Larus hyperboreus), black guillemots (Cepphus grylle), parakeet auklets (Aethia psittacula), and horned and tufted puffins (Fratercula corniculata and F. cirrhata, respectively; Roseneau 2010 and Dragoo et al. 2017). Cape Lewis: Cape Lewis is in the Chukchi Sea Unit of the AMNWR, approximately 46 km northeast of Point Hope, Alaska, at about 68°43’ N, 166°11’ W.
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Chamisso Island area: Chamisso and Puffin islands and the adjacent sea stacks are located in the Chukchi Sea Unit of the AMNWR, approximately 85 km southeast of Kotzebue, Alaska, at about 66°13’ N, 161°50’ W. The Chamisso Islands group is one of the oldest refuges in the system and was one of the first designated wilderness areas in the U. S. It was established as the Chamisso Island National Wildlife Refuge (NWR) by President William Howard Taft in 1912, designated as wilderness in 1975, and incorporated into AMNWR at its creation in 1980. The Chamisso Island group is estimated to contain more than 60% of the breeding seabirds in Kotzebue Sound (Nelson and Sowls 1985). Norton Sound: Norton Sound is located in the Bering Sea Unit of the AMNWR, at about 64° N, 164° W, near Nome, Alaska. There is a large seabird colony at Bluff that was studied periodically between 1975 and 2012. METHODS Personnel: The U. S. Fish and Wildlife Service crew consisted of Marianne Aplin, Aaron Christ, Don Dragoo, Heather Renner, Nora Rojek, Jeff Williams, and Kara Zwickey. R/V Tiglax crew: John Faris, Dan Puterbaugh, Eric Nelson, Andy Velsko, Marin Lee, and Morgan Stewart. Data Collection and Analysis: The methods used to collect and analyze seabird-related data followed the procedures described in Fadely et al. (1989), Roseneau et al. (2000), and Alaska Maritime National Wildlife Refuge (2018) with the following exceptions:
• Murre productivity was assessed by recording the number of birds that were either standing (obviously with no egg or chick), or in an incubating or brooding posture (indicating the possibility of the presence of an egg or chick). The total number of birds in incubating and brooding posture was then divided by the total number of birds whose posture was recorded to produce an estimate of the maximum productivity. It should be noted, however, that this is the maximum potential productivity and it’s likely that the actual value was lower since some of the murres exhibiting incubating or brooding postures may not have had young.
• Kittiwake productivity was estimated by recording the number of nests that obviously were empty, the number of eggs or chicks present in nests, and the number of nests on which an adult kittiwake was sitting. Sitting birds prevented a determination of whether their nests contained eggs or chicks. The total number of birds with eggs or chicks plus the number of birds sitting was divided by the total number of nests whose status was recorded to produce an estimate of the maximum productivity. It should be noted, however, that this is the maximum potential productivity and it’s likely that the actual value was lower since some of the nests with sitting birds may not have contained young.
• The land-based plots that we refer to as “Swartz index plots” were originally set up beginning in 1959 (e.g., Table 4). The boat-based plots at Colony 4 also date from the Swartz era (e.g., Table 19). The other set of land-based index plots (e.g., Table 1) were established in 1988 (Fadely et al. 1989).
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• The entirety of Cape Thompson Colonies 1, 2, 3, 4, and 5 were photographed from a skiff. All of the cliffs comprising the Cape Lisburne boat-based population plots also were photographed in 2018. Cape Thompson land-based plots at Colonies 3, 4, and 5 were photographed and counted, as were the boat-based plots at Colony 4. Photographs of the plots, including those that were not counted in 2018, are archived at AMNWR offices.
Counts made from photographs: Counts of adult birds and nests on photographs for Capes Thompson and Lisburne plots were completed by using the computer program GIMP™ 2.10.10. We created a new GIMP file for each plot. Photos were chosen based on clarity and whether they contained the entire plot. The image file for a plot was imported to a base layer in GIMP. Plot boundaries from historical photographs were drawn on a second layer. Next, different dot colors and layers were assigned to three categories, murres, black-legged kittiwakes, and black-legged kittiwake nests. A dot composed of 25 pixels was placed over each bird or nest within the boundary area of each plot. After the plot was completed, the total number of pixels (counted by software) for each category was divided by 25 to obtain the number of dots, each dot representing a bird or nest. R/V Tiglax Cruise itinerary: 30 July: Departed Nome just before midnight heading for Cape Thompson. 31 July: Enroute to Cape Thompson, via King and Little Diomede islands, and Fairway Rock. Crossed the Arctic Circle. 1 August: Arrived in the Cape Thompson area. Began photographing the five colonies from skiffs. We also completed a boat-based population count of plots at Colony 4. 2 August: Finished photographing seabird colonies from the skiffs. Visited Project Chariot site to assess condition of the landing strip. Completed a boat-based count of Colony 4 plots. 3 August: Located observation points and counted birds on land-based plots in Colony 4 and Colony 5. We also conducted counts of land-based plots at Colony 3. 4 August: Conducted a count of land-based plots at Colonies 4 and 5. Also documented productivity of murres and kittiwakes. Cruised to Cape Lisburne overnight. 5 August: Photographed all of the plots at Cape Lisburne from skiffs. Attempted to count birds on boat-based plots but the seas were too choppy to complete the count. Photographed and did a rough count of birds at Cape Lewis. Began cruising to Kotzebue Sound and the Chamisso Island group overnight. 6 August: Enroute to Kotzebue Sound. 7 August: Went ashore at Chamisso Island and attempted to circumnavigate the island in the skiffs, to no avail due to rough seas. Began the return cruise to Nome. 8 August: Enroute to Nome. Arrived at Sledge Island in the evening and skiffed to and around the island. 9 August: Skiff surveys of Bluff and Topkok Head in Norton Sound. Returned to Nome in the evening.
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INTERESTING OBSERVATIONS Cape Thompson:
• A quick check of murre productivity in the Cape Thompson area revealed that very few murres appeared to have eggs or chicks in 2018. Out of more than a thousand murres checked for productivity, only about 2.4% were in incubating or brooding postures. All of the birds that were observed to be in brooding posture (indicating that they had a chick) during two observation days were common murres, suggesting that common murres had higher productivity than thick-billed murres in the Cape Thompson area in 2018.
• Murre numbers were down in 2018 on both the common and Swartz land-based plots. Kittiwake numbers were similar to the past on both common and Swartz land-based plots.
• Murre numbers were lower in 2018 on boat-based population plots than in previous count years. Black-legged kittiwake adult and nest numbers were within the range of values from previous count years.
• Murre species composition was evaluated on seven Colony 5 plots on 5 August. We found that approximately 96% of the murres occupying the plots on that day were thick-billed murres. The average ratio of thick-billed murres to common murres reported in past years was about 44% thick-billed murres to 56% common murres.
• During a quick check of black-legged kittiwake productivity in the Cape Thompson area, an estimate of the maximum reproductive potential was calculated to be about 0.54 chicks fledged/nest. This is similar to the average productivity reported for Cape Thompson kittiwakes from past monitoring efforts (Dragoo et al. 2001). We were a bit early in the breeding season to be able to see large chicks in the nests.
• The beach from which the Colony 3 land-based population plots are counted was eroded to the point where observers would have had to stand out in the water to view the plots from the distance and angle at which the plot photographs had been taken in the past. We established a new Colony 3 plot (3-2D) that can be viewed from the current beach.
• Some of the observation points for the land-based population plots at Colonies 4 and 5 have eroded compared to the plot photographs that were taken in 1988. In one case (observation point 5-1) observers noted that the observation point had “moved <10 feet inland due to erosion” (Table 3). Observers believed that, although some of the areas within the plot boundaries of the old photographs were not visible from the new observation point, the 2018 counts were comparable with those from the past, especially for the Swartz plots.
• We visited the Project Chariot site to assess the condition of the airstrip and found that it appears to be in adequate condition to allow for use by the type of small aircraft that was used in past Cape Thompson camp deployments.
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Cape Lisburne:
• During a quick check of black-legged kittiwake productivity in the Cape Lisburne area, an estimate of the maximum reproductive potential was calculated to be about 0.67 chicks fledged/nest. This is slightly higher than the average productivity reported for Cape Lisburne kittiwakes from past monitoring efforts (Dragoo et al. 2018). We were a bit early in the breeding season to be able to see large chicks in the nests.
• The 2018 marine mammal monitoring crew at Cape Lisburne (Sasha Ertl and Brian O’Donnell, dnaEnvironmental Inc.) made the following observations: “NO young murre, puffin or cormorant observed. NO alcids ever observed carrying fish. Relatively few hatch-year Kittiwakes seen; however, Sasha Ertl observed many young Kittiwakes on ledges and in the water on September 30th.”
• Sasha Ertl also stated in an e-mail (dated 25 September 2018): “Brian and I have been discussing the fact that neither of us saw any alcid chicks this year. I know that’s both not good news and not unique-to-Lisburne news. We are both hoping we just missed it, but I took a bunch of pics of the cliffs to look for young and didn’t see any. We also were waiting for the dad/chick murres, and never saw that either. Did see young kittiwakes and glaucous gulls though. And lots of adult alcids in the cliffs. And like I reported before, there are huge groups of gulls out on the water, even still! They must be on bait balls? So I don’t understand the lack of alcid chicks.”
Cape Lewis:
• We estimated that there was a minimum of 20,790 murres at Cape Lewis (counted by 10s and 100s), similar to the 25,000 reported in 1977 (Sowls et al. 1978).
• Observers noted that there appeared to be little or no murre or kittiwake productivity at Cape Lewis in 2018.
• The pinnacles at Cape Lewis are reminiscent of those in the Bryce Canyon area of Utah. Chamisso Island area:
• Rough seas prevented formal surveys but we did note that there were no murres occupying a small colony on Chamisso Island, an area that typically contains upwards of one hundred murres (Dragoo and Slater 2015).
• We made a brief inspection of Puffin Island, but high seas and strong winds prevented any counts. Many hundreds (possibly thousands) of murres were at least attending the cliffs there.
Norton Sound:
• During a quick check of black-legged kittiwake productivity at Sledge Island, an estimate of the maximum reproductive potential was calculated to be about 0.29 chicks fledged/nest. Pelagic cormorants appeared to be doing fairly well at Sledge Island, whereas murres apparently failed to produce young there.
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• A circumnavigation survey of birds at Sledge Island found 976 murres (species combined), 1,934
black-legged kittiwakes, and 277 pelagic cormorants. Our murre counts were similar to those from 1984 (Byrd 1984), but much lower than 1976 counts (Sowls et al. 1978). The 2018 counts of black-legged kittiwakes was similar to the 1976 count, but almost twice the number counted in 1984. Pelagic cormorant numbers appear to be increasing at Sledge Island but the number of nests was down in 2018 compared to 1984 (11 nests in 2018 vs 100 nests in 1984).
• During a quick check of black-legged kittiwake productivity in the Bluff area, an estimate of the
maximum reproductive potential was calculated to be about 0.29 chicks fledged/nest. This is below the average productivity reported for Bluff kittiwakes from past monitoring efforts (Dragoo et al. 2011).
• A quick check of murre productivity at Bluff revealed that only about 13% of birds appeared to be in incubating or brooding posture. Just one chick was observed.
• Large numbers of murres flushed every time we approached the cliffs at Bluff in the skiff.
• Topkok Head contained mostly pelagic cormorants and glaucous gulls, with dozens of pigeon guillemots, and a few horned and tufted puffins. Many of the pelagic cormorant nests contained large chicks (often more than three chicks/nest). Numerous cormorant chicks were near, or past, fledging age.
• A golden eagle nest was observed at Topkok head.
ACKNOWLEDGEMENTS We would like to thank the crew of the R/V Tiglax for getting us there and back safely and well fed. Frances Murphy was always ready to provide a “Ride ‘em cowboy” for us during our many lumpy skiff rides. National Park Service in Nome provided bunkhouse space. We thank the estate of Wilfred W. Lane, Sr. for access to their allotment at the Chariot site. We also thank Melissa Petschauer for spending the hours necessary to count birds and nests on the 2018 Cape Thompson population plot photographs, and Arthur Kettle for helping get Melissa set up and able to do the photo counts. Finally, we would like to express our gratitude to the staff of the Alaska Maritime National Wildlife Refuge for their continued help and support. Cover photo of “Puddles” the blue goose was taken by Aaron Christ. REFERENCES Alaska Maritime National Wildlife Refuge. 2018. Standardized protocols for annual seabird monitoring
camps at Aiktak, Buldir, Chowiet, St. George, St. Lazaria and St. Paul islands, Cape Lisburne, and select intermittent sites in the Alaska Maritime National Wildlife Refuge in 2018. U.S. Fish and Wildl. Serv. Report AMNWR 2018/04. Homer, Alaska.
Byrd, G. V. 1984. Observations of flora and fauna in the Bering Sea Unit Alaska Maritime NWR in July 1984. U.S. Fish and Wildl. Serv. Report AMNWR 1984/02. Homer, Alaska.
Dragoo, D. E., G. V. Byrd, and D. B. Irons. 2001. Breeding status, population trends and diets of seabirds in Alaska, 2000. U.S. Fish and Wildl. Serv. Report AMNWR 2001/07. Homer, Alaska.
Dragoo, D. E., G. V. Byrd, and D. B. Irons. 2011. Breeding status, population trends and diets of seabirds in Alaska, 2008. U.S. Fish and Wildl. Serv. Report AMNWR 2011/07. Homer, Alaska.
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Dragoo, D. E., and L. Slater. 2015. Biological monitoring at the Chamisso Island group, Alaska in 2014. U.S. Fish and Wildl. Serv. Report AMNWR 2015/04. Homer, Alaska.
Dragoo, D. E., G. Thomson, and M. D. Romano. 2017. Biological monitoring at Cape Lisburne, Alaska in 2017. U. S. Fish and Wildl. Serv. Report AMNWR 2017/15. Homer, Alaska.
Dragoo, D. E., H. M. Renner, and R. S. A. Kaler. 2018. Breeding status and population trends of seabirds in Alaska, 2017. U.S. Fish and Wildl. Serv. Report AMNWR 2018/02. Homer, Alaska.
Ertl, S., and B. O’Donnell, dnaEnvironmental Inc. Personal Communication, 2018. Anchorage, Alaska. Fadely, B. S., J. F. Piatt, S. A. Hatch, and D. G. Roseneau. 1989. Populations, productivity, and feeding
habits of seabirds at Cape Thompson, Alaska. Minerals Mgmt. Serv., OCS Study MMS 89-0014. Nelson, J. W., and A. L. Sowls. 1985. Breeding seabird survey of Chamisso Island and southern Kotzebue
Sound, 8-20 August 1981. U. S. Fish and Wildl. Serv. Report. Anchorage, Alaska (AMNWR 1985/17).
Nishimoto, M., and V. M. Mendenhall. 1994. Cape Thompson. Chap. 6, pp. 94-109 in Mendenhall, V. M. (ed.). Monitoring of populations and productivity of seabirds at St. Matthew Island, Bluff, Little Diomede Island, and Cape Thompson, Alaska, 1991. Minerals Mgmt. Serv., OCS Study MMS 93-0067.
Roseneau, D. G., M. F. Chance, P. F. Chance, and G. V. Byrd. 2000. Monitoring seabird populations in areas of oil and gas development on the Alaskan continental shelf: Cape Lisburne and Cape Thompson seabird studies, 1995-1997. Final report by the Alaska Maritime National Wildlife Refuge, Homer, Alaska to the U.S. Geological Survey Biological Resources Division, Western Regional Office, Seattle WA (USGS Study USGS/BRD/CR-1999-0002 and OCS Study 99-0011). U. S. Fish and Wildl. Serv. Report AMNWR 2000/09. Homer, Alaska.
Roseneau, D. G. 2010. Monitoring murres and kittiwakes at Cape Lisburne, Alaska, 1976-2009. AMNWR monitoring poster prepared 23 February 2010, AMNWR, Homer, Alaska.
Sharp. B. E., 1993. Populations and productivity of seabirds at Cape Thompson in 1990. Pp. 94-139 in Mendenhall, V. M. (ed.). Monitoring populations and productivity of seabirds at Cape Peirce, Bluff, and Cape Thompson, Alaska, 1990. Minerals Mgmt. Serv., OCS Study MMS 92-0047.
Sowls, A. L., S. A. Hatch, and C. J. Lensink. 1978. Catalog of Alaskan seabird colonies. FWSLOBS-78/78. USFWS Biol. Serv. Prog. Anchorage, Alaska.
Springer, A. M., and D. G. Roseneau. 1978. Ecological studies of colonial seabirds at Cape Thompson and Cape Lisburne, Alaska. U. S. Dept. Commer., NOAA OCSEAP, Annual Rept., Vol. 2, pp. 839-960.
Springer, A. M., D. G. Roseneau, E. C. Murphy, and M. I. Springer. 1979. Ecological studies of colonial seabirds at Cape Thompson and Cape Lisburne, Alaska. U.S. Dept. Commer., NOAA OCSEAP, Annual Rept., Vol. 2, pp 517-574.
Swartz, G. 1966. Sea-cliff birds. Pp. 611-678 in N. J. Wilimovsky and J. N. Wolfe (eds.). Environment of the Cape Thompson region, Alaska. U.S. Atomic Energy Commission, Oak Ridge, TN.
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Figure 1. Map of 2018 northern Bering and eastern Chukchi seas cruise (green line is northbound route, red line is southbound).
Point Hope
Kotzebue
Diomedes
Nome
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Figure 2. Map of 2018 Study locations.
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FIGURES AND TABLES
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Figure 3. Mean numbers of murres (species combined) counted on land-based index plots (4-1A, 4-1B, 4-2C, 4-3D, and 4-4E) on Colony 4 at Cape Thompson, Alaska. No counts were conducted in 1989, 1992-1994, or 1996-2017.
0
200
400
600
800
1000
1200
1400
1600
1800
88 90 92 94 96 98 00 02 04 06 08 10 12 14 16 18
Mea
n nu
mbe
r of m
urre
s
Year
12
Table 1. Numbers of murres (species combined) counted on land-based index plots (4-1A, 4-1B, 4-2C, 4-3D, and 4-4E) on Colony 4 at Cape Thompson, Alaska. No counts were conducted in 1989, 1992-1994, or 1996-2017.
SD 235 86 142 109 322 First count 11 Jul 9 Jul 15 Jul 22 Jul 3 Aug Last count 15 Aug 1 Aug 8 Aug 15 Aug 4 Aug
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Figure 4. Mean numbers of murres (species combined) counted on land-based index plots (5-1A, 5-1B, 5-1C, 5-1D, 5-2E, 5-2F, 5-2G, and 5-3H) on Colony 5 at Cape Thompson, Alaska. No counts were conducted in 1989, 1992-1994, or 1996-2017.
0
500
1000
1500
2000
2500
3000
88 90 92 94 96 98 00 02 04 06 08 10 12 14 16 18
Mea
n nu
mbe
r of m
urre
s
Year
14
Table 2. Numbers of murres (species combined) counted on land-based index plots (5-1A, 5-1B, 5-1C, 5-1D, 5-2E, 5-2F, 5-2G, and 5-3H) on Colony 5 at Cape Thompson, Alaska. No counts were conducted in 1989, 1992-1994, or 1996-2017.
SD 244 202 322 211 942 First count 25 Jul 22 Jul 15 Jul 22 Jul 3 Aug Last count 15 Aug 9 Aug 4 Aug 15 Aug 4 Aug
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Table 3. Numbers of murres (species combined) counted on land-based index plots at Cape Thompson, Alaska in 2018.
Date 3-Aug 4-Aug Plot 2018 2018 Notes (Notes in italics are quoted from field notebooks and/or summary data sheets.)
3-1A 3 NCa Plot couldn't be counted from the location at which the previous photos were taken (1988) due to beach erosion. 3-2B 115 NC Plot couldn't be counted from the location at which the previous photos were taken (1988) due to beach erosion. 3-2C 35 NC Plot couldn't be counted from the location at which the previous photos were taken (1988) due to beach erosion. 3-2D 120 NC New plot established in 2018. 4-1A 192 244 4-1B 134 193 4-2C 199 292 4-3D 150 322 “Rebar marker at lower end of tall grass patch” 4-4E 275 355 5-1A 13 22 “Obs. point moved <10 feet inland due to coastal erosion.” "Potential for missing birds on far left edge." 5-1B 137 269 “Obs. point moved <10 feet inland due to coastal erosion.” "Has lost some cliff but can see fine." 5-1C 27 96 “Obs. point moved <10 feet inland due to coastal erosion.” "Lower and right portion not visible." 5-1D 64 455 “Obs. point moved <10 feet inland due to coastal erosion.” "Right-hand portion of Fadely's plot not visible." 5-2E 125 419 5-2F 136 341 5-2F' 55 107 5-2G 112 181 5-3H 2 79 5-3H' 0 34 5-4I 145 304 5-5J 452 807 "Swartz L." 5-6K 119 385 "Swartz M." (Swartz Plot M includes Fadely Plot 5-6K plus Plot 5-K’). 5-6K' 89 138 "Swartz M." (Swartz Plot M includes Fadely Plot 5-6K plus Plot 5-K’). 5-7L 68 NC 5-7L' 35 NC 5-8-M NC 920 5-8N 81 500 5-8N' 0 140
a NC = Plot not counted.
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Figure 5. Numbers of murres (species combined) counted on land-based Swartz index plots 5G, 5L, 5M, 5N, 5O, 5P, and 5Q at Cape Thompson, Alaska. No counts were conducted in 1961-1978, 1980, 1981, 1983-1989, 1992-1994, or 1996-2017. Error bars represent one standard deviation.
0
3,000
6,000
9,000
12,000
15,000
18,000
21,000
60 64 68 72 76 80 84 88 92 96 00 04 08 12 16
Mea
n nu
mbe
r of m
urre
s
Year
17
Table 4. Numbers of murres (species combined) counted on land-based Swartz index plots 5G, 5L, 5M, 5N, 5O, 5P, and 5Q at Cape Thompson, Alaska. No counts were conducted in 1961-1978, 1980, 1981, 1983-1989, 1992-1994, or 1996-2017.
Table 6. Numbers of murres (species combined) counted from photographs of land-based plots at Cape Thompson, Alaska. Photographs were taken on 3 August 2018.
Plot Birds Notes
4-1A 258 4-1B 142 4-2C 154 4-3D 304 4-4E 446 5-1A 26 5-1B 81 5-1C 21 5-1D 70 5-2E 167 Photo quite far, zooming in a lot creates blurry image. 5-2F 194 Photo quite far, zooming in a lot creates blurry image. 5-2G 144 Photo quite far, zooming in a lot creates blurry image. 5-3H 3 5-4I 98 5-5J 441
Swartz 5-Q 95 Swartz 5-G 462 Photo did not include all of the plot, blurry Swartz 5-N 335 Swartz 5-O 328 Swartz 5-P 571
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Table 7. Numbers of murres (species combined) counted manually and from photographs of land-based plots at Cape Thompson, Alaska in 2018. Photographs were taken and counts were conducted on the same day (3 August 2018). Manual counts were made within 10 minutes of the time when the photographs were taken.
Plot Manual Count Mean on 3 Aug. (Birds) Photo Count (Birds)
Figure 6. Mean numbers of black-legged kittiwakes counted on land-based index plots (4-1A, 4-1B, 4-2C, 4-3D, and 4-4E) on Colony 4 at Cape Thompson, Alaska. No counts were conducted in 1989, 1992-1994, or 1996-2017.
0
100
200
300
400
500
600
700
800
88 90 92 94 96 98 00 02 04 06 08 10 12 14 16 18
Mea
n nu
mbe
r of k
ittiw
akes
Year
21
Table 8. Numbers of black-legged kittiwakes counted on land-based index plots (4-1A, 4-1B, 4-2C, 4-3D, and 4-4E) on Colony 4 at Cape Thompson, Alaska. No counts were conducted in 1989, 1992-1994, or 1996-2017.
SD 52 44 82 109 11 First count 11 Jul 9 Jul 15 Jul 22 Jul 3 Aug Last count 8 Aug 6 Aug 8 Aug 15 Aug 4 Aug
22
Figure 7. Mean numbers of black-legged kittiwakes counted on land-based index plots (5-1A, 5-1B, 5-1C, 5-2F, and 5-2G) on Colony 5 at Cape Thompson, Alaska. No counts were conducted in 1989, 1992-1994, or 1996-2017.
0
50
100
150
200
250
300
350
400
88 90 92 94 96 98 00 02 04 06 08 10 12 14 16 18
Mea
n nu
mbe
r of k
ittiw
akes
Year
23
Table 9. Numbers of black-legged kittiwakes counted on land-based index plots (5-1A, 5-1B, 5-1C, 5-2F, and 5-2G) on Colony 5 at Cape Thompson, Alaska. No counts were conducted in 1989, 1992-1994, or 1996-2017.
SD 17 12 36 52 8 First count 11 Jul 22 Jul 15 Jul 22 Jul 3 Aug Last count 8 Aug 9 Aug 12 Aug 15 Aug 4 Aug
24
Table 10. Numbers of black-legged kittiwakes counted on land-based index plots at Cape Thompson, Alaska in 2018.
Date 3-Aug 4-Aug Plot 2018 2018 Notes (Notes in italics are quoted from the summary data sheets.)
3-1A 1 NCa Plot couldn't be counted from the location at which the previous photos were taken (1988) due to beach erosion. 3-2B 48 NC Plot couldn't be counted from the location at which the previous photos were taken (1988) due to beach erosion. 3-2C 20 NC Plot couldn't be counted from the location at which the previous photos were taken (1988) due to beach erosion. 3-2D 51 NC New plot established in 2018. 4-1A 122 82 4-1B 44 66 4-2C 246 252 4-3D 86 82 “Rebar marker at lower end of tall grass patch” 4-4E 256 256 5-1A 12 14 "Potential for missing birds on far left edge." 5-1B 132 140 "Has lost some cliff but can see fine." 5-1C 16 19 "Lower and right portion not visible." 5-1D 1 2 "Right-hand portion of Fadely's plot not visible." 5-2E 2 3 5-2F 2 2 5-2F' 0 0 5-2G 99 98 5-3H 0 0 5-3H' 0 0 5-4I 4 5 5-5J 57 68 "Swartz L." 5-6K 1 2 "Swartz M." (Swartz Plot M includes Fadely Plot 5-6K plus Plot 5-K’). 5-6K' 0 0 "Swartz M." (Swartz Plot M includes Fadely Plot 5-6K plus Plot 5-K’). 5-7L 10 NC 5-7L' 12 NC 5-8-M NC 82 5-8N 23 38 Swartz Q. 5-8N' 2 2 Swartz Q.
a NC = Plot not counted.
25
Figure 8. Numbers of black-legged kittiwakes counted on land-based Swartz index plots 5G, 5L, 5M, 5N, 5P, and 5Q at Cape Thompson, Alaska. No counts were conducted in 1980-1989, 1992-1994, or 1996-2017. Error bars represent one standard deviation.
Table 11. Numbers of black-legged kittiwakes counted on land-based Swartz index plots 5G, 5L, 5M, 5N, 5P, and 5Q at Cape Thompson, Alaska. No counts were conducted in 1961-1978, 1980, 1981, 1983-1989, 1992-1994, or 1996-2017.
Table 13. Numbers of black-legged kittiwakes counted from photographs of land-based plots at Cape Thompson, Alaska. Photographs were taken on 3 August 2018.
Plot Birds Notes
4-1A 112
4-1B 40
4-2C 318
4-3D 98
4-4E 237
5-1A 33
5-1B 86
5-1C 11
5-1D 1
5-2E 1 Photo quite far, zooming in a lot creates blurry image.
5-2F 3 Photo quite far, zooming in a lot creates blurry image.
5-2G 132 Photo quite far, zooming in a lot creates blurry image.
5-3H 0
5-4I 4
5-5J 66
Swartz 5-M 1
5-6K 3 Slightly blurry
5-7L 24
5-8M 86 Blurry
Swartz 5-Q 33
Swartz 5-G 52 Photo did not include all of the plot, blurry
Swartz 5-N 79
Swartz 5-O 13
Swartz 5-P 199
28
Table 14. Numbers of black-legged kittiwakes counted manually and from photographs of land-based plots at Cape Thompson, Alaska in 2018. Photographs were taken and counts were conducted on the same day (3 August 2018). Manual counts were made within 10 minutes of the time when the photographs were taken.
Plot Manual Count Mean on 3 Aug. (Birds) Photo Count (Birds)
Table 15. Numbers of black-legged kittiwake nests counted on land-based index plots at Cape Thompson, Alaska in 2018.
Date 3-Aug 4-Aug Maximum Plot 2018 2018 Count Notes (Notes in italics are quoted from the summary data sheets.)
3-1A 2 NCa 2 Plot couldn't be counted from the location at which the previous photos were taken (1988) due to beach erosion. 3-2B 27 NC 27 Plot couldn't be counted from the location at which the previous photos were taken (1988) due to beach erosion. 3-2C 18 NC 18 Plot couldn't be counted from the location at which the previous photos were taken (1988) due to beach erosion. 3-2D 43 NC 43 New plot established in 2018. 4-1A 49 45 49 4-1B 46 18 46 4-2C 104 119 119 4-3D 33 42 42 “Rebar marker at lower end of tall grass patch” 4-4E 135 160 160 5-1A 6 6 6 "Potential for missing birds on far left edge." 5-1B 51 63 63 "Has lost some cliff but can see fine." 5-1C 14 12 14 "Lower and right portion not visible." 5-1D 1 1 1 "Right-hand portion of Fadely's plot not visible." 5-2E 1 1 1 5-2F 2 1 2 5-2F' 0 0 0 5-2G 67 55 67 5-3H 0 0 0 5-3H' 0 0 0 5-4I 2 3 3 5-5J 36 48 48 "Swartz L." 5-6K 1 1 1 "Swartz M." (Swartz Plot M includes Fadely Plot 5-6K plus Plot 5-K’). 5-6K' 0 0 0 "Swartz M." (Swartz Plot M includes Fadely Plot 5-6K plus Plot 5-K’). 5-7L 9 NC 9 5-7L' 7 NC 7 5-8-M NC 43 43 5-8N 21 25 25 Swartz Q. 5-8N' 2 2 2 Swartz Q.
a NC = Plot not counted.
30
Table 16. Numbers of black-legged kittiwake nests counted on land-based Swartz index plots at Cape Thompson, Alaska in 2018.
Table 17. Numbers of black-legged kittiwake nests counted from photographs of land-based plots at Cape Thompson, Alaska. Photographs were taken on 3 August 2018.
Plot Nests Notes
4-1A 46
4-1B 16
4-2C 118
4-3D 38
4-4E 161
5-1A 17
5-1B 52
5-1C 8
5-1D 1
5-2E 0 Photo quite far, zooming in a lot creates blurry image.
5-2F 1 Photo quite far, zooming in a lot creates blurry image.
5-2G 58 Photo quite far, zooming in a lot creates blurry image.
5-3H 0
5-4I 3
5-5J 49
Swartz 5-M 0
5-6K 2 Slightly blurry
5-7L 19
5-8M 67 Blurry
Swartz 5-Q 27
Swartz 5-G 35 Photo did not include all of the plot, blurry
Swartz 5-N 69
Swartz 5-O 12
Swartz 5-P 102
31
Table 18. Numbers of black-legged kittiwake nests counted manually and from photographs of land-based plots at Cape Thompson, Alaska in 2018. Photographs were taken and counts were conducted on the same day (3 August 2018). Manual counts were made within 10 minutes of the time when the photographs were taken.
Plot Manual Count Mean on 3 Aug. (Nests) Photo Count (Nests)
Figure 9. Numbers of murres (species combined) counted on boat-based index plots at Colony 4, Cape Thompson, Alaska. No counts were conducted in 1962-1975, 1978, 1980-1981, 1983-1987, 1989, 1991-1994, or 1996-2017. Error bars represent one standard deviation.
0
1000
2000
3000
4000
5000
6000
7000
8000
9000
60 64 68 72 76 80 84 88 92 96 00 04 08 12 16
Mea
n nu
mbe
r of m
urre
s
Year
33
Table 19. Numbers of murres (species combined) counted on boat-based index plots at Colony 4, Cape Thompson, Alaska. No counts were conducted in 1962-1975, 1978, 1980-1981, 1983-1987, 1989, 1991-1994, or 1996-2017.
Mean = 6027 Mean = 5453 Mean = 4993 Mean = 6142 Mean = 3257 SDd = 1019 SD = 824 SD = 747 SD = 900 SD = 1557
a Data are from Roseneau et al. 2000; Table 28. b NC = Plot not counted. c Plot 4K was not included in the replicate total, having not been counted in 1961. dSD = Standard deviation.
34
Table 20. Numbers of murres (species combined) counted from photographs of boat-based plots at Colony 4, Cape Thompson, Alaska. Photographs were taken on 1 August 2018.
Plot Birds Notes
4-4R 94 Zooming in creates blurry image, difficult to get accurate count 4-4Q 249 Zooming in creates blurry image, difficult to get accurate count 4-4P 299 Zooming in creates blurry image, difficult to get accurate count 4-4N 159 Zooming in creates blurry image, difficult to get accurate count 4-4M 160 Zooming in creates blurry image, difficult to get accurate count 4-4O 43 Zooming in creates blurry image, difficult to get accurate count 4-4L 57 Zooming in creates blurry image, difficult to get accurate count 4-4K 49 Zooming in creates blurry image, difficult to get accurate count 4-4J 241 Zooming in creates blurry image, difficult to get accurate count 4-4H 142 Zooming in creates blurry image, difficult to get accurate count 4-4I 9 Zooming in creates blurry image, difficult to get accurate count 4-4F 144 Zooming in creates blurry image, difficult to get accurate count 4-4G 423 Zooming in creates blurry image, difficult to get accurate count 4-4E 445 Zooming in creates blurry image, difficult to get accurate count 4-4C 344 Zooming in creates blurry image, difficult to get accurate count 4-4B 233 Zooming in creates blurry image, difficult to get accurate count 4-4A 42 Zooming in creates blurry image, difficult to get accurate count
35
Table 21. Numbers of murres (species combined) counted manually and from photographs of boat-based index plots at Colony 4, Cape Thompson, Alaska. Photographs were taken and counts were conducted on the same day (1 August 2018).
a Plots 4-4F and 4-4G were combined during the 2018 murre count. b Plots 4-4D and 4-4E were combined during the 2018 count. Plot 4-4D eroded
to the point that it is essentially gone.
36
Figure 10. Numbers of black-legged kittiwakes counted on boat-based index plots at Colony 4, Cape Thompson, Alaska. No counts were conducted in 1961-1975, 1980-1981, 1983-1987, 1989, 1991-1994, or 1996-2017. Error bars represent one standard deviation.
0
1000
2000
3000
4000
5000
6000
7000
60 64 68 72 76 80 84 88 92 96 00 04 08 12 16
Mea
n nu
mbe
r of k
ittiw
akes
Year
37
Table 22. Numbers of black-legged kittiwakes counted on boat-based index plots at Colony 4, Cape Thompson, Alaska. No counts were conducted in 1961-1975, 1980-1981, 1983-1987, 1989, 1991-1994, or 1996-2017.
a Data are from Roseneau et al. 2000; Table 23. b Plots 4F and 4G combined. c Plots 4A and 4B combined. d Plots 4D and 4E combined. e Plots 4J, 4K, 4L, and 4O combined. f NC = Plot not counted. g Plots 4M, 4N, 4P, and 4R combined. h Plot 4Q was not included in the replicate total, having not been counted in 1977. I SD= Standard deviation.
38
Table 23. Numbers of black-legged kittiwakes counted from photographs of boat-based plots at Colony 4, Cape Thompson, Alaska. Photographs were taken on 1 August 2018.
Plot Birds Notes
4-4R 51 Zooming in creates blurry image, difficult to get accurate count
4-4Q 122 Zooming in creates blurry image, difficult to get accurate count
4-4P 195 Zooming in creates blurry image, difficult to get accurate count
4-4N 263 Zooming in creates blurry image, difficult to get accurate count
4-4M 129 Zooming in creates blurry image, difficult to get accurate count
4-4O 66 Zooming in creates blurry image, difficult to get accurate count
4-4L 231 Zooming in creates blurry image, difficult to get accurate count
4-4K 173 Zooming in creates blurry image, difficult to get accurate count
4-4J 165 Zooming in creates blurry image, difficult to get accurate count
4-4H 147 Zooming in creates blurry image, difficult to get accurate count
4-4I 307 Zooming in creates blurry image, difficult to get accurate count
4-4F 272 Zooming in creates blurry image, difficult to get accurate count
4-4G 620 Zooming in creates blurry image, difficult to get accurate count
4-4E 651 Zooming in creates blurry image, difficult to get accurate count
4-4C 422 Zooming in creates blurry image, difficult to get accurate count
4-4B 688 Zooming in creates blurry image, difficult to get accurate count
4-4A 264 Zooming in creates blurry image, difficult to get accurate count
39
Table 24. Numbers of black-legged kittiwakes counted manually and from photographs of boat-based index plots at Colony 4, Cape Thompson, Alaska. Photographs were taken and counts were conducted on the same day (1 August 2018).
a Plots 4-4D and 4-4E were combined during the 2018 count. Plot 4-4D eroded to the point that it is essentially gone.
40
Figure 11. Numbers of black-legged kittiwake nests counted on boat-based index plots at Colony 4, Cape Thompson, Alaska (maximum nest count was used in 2018). No counts were conducted in 1962-1977, 1980-1981, 1983-1987, or 1989-2017.
0
500
1000
1500
2000
2500
3000
3500
61 65 69 73 77 81 85 89 93 97 01 05 09 13 17
Num
ber o
f kitt
iwak
e ne
sts
Year
41
Table 25. Numbers of black-legged kittiwake nests counted on boat-based index plots at Colony 4, Cape Thompson, Alaska. No counts were conducted in 1961-1975, 1980-1981, 1983-1987, 1989, 1991-1994, or 1996-2017.
a Data are from Fadely et al. 1989; Table G.55. b Data are from Fadely et al. 1989; Table G.58. c Data are from Fadely et al. 1989; Table G.59. d Data are from Fadely et al. 1989; Table G.60. e Data are from Fadely et al. 1989; Table G.61. f 2018 maximum nest count was used for comparisons.
42
Table 26. Numbers of black-legged kittiwake nests counted from photographs of boat-based plots at Colony 4, Cape Thompson, Alaska. Photographs were taken on 1 August 2018.
Plot Nests Notes
4-4R 31 Zooming in creates blurry image, difficult to get accurate count
4-4Q 65 Zooming in creates blurry image, difficult to get accurate count
4-4P 116 Zooming in creates blurry image, difficult to get accurate count
4-4N 131 Zooming in creates blurry image, difficult to get accurate count
4-4M 63 Zooming in creates blurry image, difficult to get accurate count
4-4O 39 Zooming in creates blurry image, difficult to get accurate count
4-4L 133 Zooming in creates blurry image, difficult to get accurate count
4-4K 123 Zooming in creates blurry image, difficult to get accurate count
4-4J 99 Zooming in creates blurry image, difficult to get accurate count
4-4H 67 Zooming in creates blurry image, difficult to get accurate count
4-4I 140 Zooming in creates blurry image, difficult to get accurate count
4-4F 141 Zooming in creates blurry image, difficult to get accurate count
4-4G 244 Zooming in creates blurry image, difficult to get accurate count
4-4E 313 Zooming in creates blurry image, difficult to get accurate count
4-4C 208 Zooming in creates blurry image, difficult to get accurate count
4-4B 365 Zooming in creates blurry image, difficult to get accurate count
4-4A 126 Zooming in creates blurry image, difficult to get accurate count
43
Table 27. Numbers of black-legged kittiwake nests counted manually and from photographs of boat-based index plots at Colony 4, Cape Thompson, Alaska. Photographs were taken and counts were conducted on the same day (1 August 2018).
a Plots 4-4D and 4-4E were combined during the 2018 count. Plot 4-4D eroded to the point that it is essentially gone.
44
Table 28. Locations (latitude, longitude) of endpoints of seabird colonies at Cape Thompson, Alaska (WGS 84).
Colony Eastern end point Western end point
1 68.09861⁰ N, -165.80456⁰ W 68.10235⁰ N, -165.81784⁰ W 2 68.10577⁰ N, -165.85312⁰ W 68.11750⁰ N, -165.90397⁰ W 3 68.12993⁰ N, -165.94596⁰ W 68.13758⁰ N, -165.97140⁰ W 4 68.14081⁰ N, -165.97536⁰ W 68.14553⁰ N, -165.98247⁰ W 5 68.14553⁰ N, -165.98247⁰ W 68.15807⁰ N, -165.99591⁰ W
Table 29. Locations (latitude, longitude) of observation points for land-based plots at Cape Thompson, Alaska (WGS 84).
Observation Post
Location
Plots counted from the Observation Post
4-1 68.14209⁰ N, -165.97695⁰ W 4-1A, 4-1B 4-2 68.14236⁰ N, -165.97765⁰ W 4-2C 4-3 68.14283⁰ N, -165.97987⁰ W 4-3D 4-4 68.14417⁰ N, -165.98093⁰ W 4-4E 5-1a 68.14596⁰ N, -165.97874⁰ W 5-1A, 5-1B, 5-1C, 5-1D 5-2 68.14710⁰ N, -165.97940⁰ W 5-2E, 5-2F, 5-2F’, 5-2G 5-3 68.14773⁰ N, -165.98012⁰ W 5-3H, 5-3H’, Swartz 5G 5-4 68.14809⁰ N, -165.98093⁰ W 5-4I 5-5 68.14850⁰ N, -165.98062⁰ W 5-5J, Swartz 5L (same plot as 5-5J) 5-6 68.14877⁰ N, -165.98047⁰ W 5-6K, 5-6K’, Swartz 5-M (same plot as 5-6K plus 5-6K’), Swartz 5N, Swartz 5O, Swartz 5P
Swartz 5-6 68.14771⁰ N, -165.97983⁰ W Swartz 5-M. Plots 5-6K + 5-6K’ but counted from a slightly different observation point. 5-7 68.14919⁰ N, -165.98030⁰ W 5-7L, 5-7L’ 5-8 68.14962⁰ N, -165.98111⁰ W 5-8M, 5-8N, 5-8N’, Swartz 5Q (same plot as 5-8N plus 5-8N’)
a See notes in Table 3 regarding ability to see plots from this observation post.
45
Table 30. Locations (latitude, longitude) of midpoints of boat-based plots at Cape Lisburne, Alaska (WGS 84).
Plot Location
11 68.85045⁰N, -166.21787⁰W 12 68.85059⁰ N, -166.21812⁰ W 25 68.86113⁰ N, -166.22567⁰ W 26 68.86136⁰ N, -166.22604⁰ W 30 68.86294⁰ N, -16622900⁰ W 32 68.86434⁰ N, -16622962⁰ W 65 68.88303⁰ N, -166.20009⁰ W 66 68.88224⁰ N, -166.19514⁰ W 70 68.88099⁰ N, -166.18708⁰ W 72 68.88080⁰ N, -166.18464⁰ W
72/73a 68.88063⁰ N, -166.18069⁰ W 74 68.88040⁰ N, -166.17708⁰ W