Table

Trumpeter Swan – Accepted

     

1. 08 Nov 1935

Bailey Creek LAS

1984-189

10,30

see McLean 1937

   

2. 01 Jan–09 Mar 1962

ASY

Abbotts Lagoon MRN

1984-193

10,14

Fig. 10, ph.

     

3. 13–22 Jan 1973

ASY

Carrizo Plain SLO

1980-179

7

Fig. 11, ph., Schram 1973, Roberson (1980)

     

4. 01 Jan–17 Feb 1975

ASY

El Monte LA

1980-131

6

     

and 13–15 Mar 1975

ASY

Covina LA

     

5-8. 27 Nov 1977

4 AHY

Mono Lake MNO

1978-002

4

     

9. 24 Feb 1979

ASY

Tule Lake LAK

1979-016

5

     

10. 23 Dec 1984

AHY

Tule Lake NWR SIS

1985-028

12

green-collared bird

     

11. 23 Dec 1984

AHY

Tule Lake NWR MOD

1985-196

12

     

12-15. 02 Dec 1985–14 Mar 1986

4 AHY

Smith R. bottoms DN

1986-001

11

     

16-17. 01 Feb 1986

2 ASY

King I. SJ

1986-340

12

     

18-20. 30 Dec 1986

3

Butte Sink SUT

1987-018

14

     

21-22. 18 Jan 1987

2 ASY

Tule Lake NWR SIS

1987-078

12

     

23. 26 Dec 1987

ASY

vic. Stockton SJ

1988-060

13

     

24-26. 12 Feb 1988

3 ASY

Lower Klamath NWR SIS

1988-295

13

     

27-28. 02–03 Jan 1989

2 SY

Honey Lake Wildlife Area LAS

1989-079

13

     

29. 10 Feb 1989

 

Nelson BUT

1989-052

15

red-collared bird from NW Territories

   

30-31. 30 Nov 1991

2 AHY

Lower Klamath NWR SIS

1991-210

18

ph.

     

32-34. 28 Feb 1992

3

Sierra Valley PLU

1992-091

18

     

35-36. 27 Nov 1993

2

Tule Lake NWR SIS

1994-003

19

sketch in Erickson & Terrill (1996)

     

37. 03 Feb 1994

ASY

~7.5 mi. nne Marysville YUB

1998-077

24

ph.

     

38. 17 Dec 1995

AHY

Rindge Tract SJ

1998-215

24

     

39. 04 Jan 1996

ASY

vic. Grimes COL

1996-037

23

one of two reported

     

40. 02 Jan–27 Feb 1999

ASY male

Pleasant Vly. Res./Tinnemaha Res. INY

1999-020

25

ph., green-collared bird from ne Idaho

     

41-43. 22 Jan 1999

3

Staten Island SJ

1999-049

25,28

     

44. 19 Dec 1999

AHY

Smith R. bottoms DN

1999-212

25

     

45-46. 14 Dec 2000

2 AHY

vic. Marysville YUB

2000-158

27

     

47. 05 Jan 2001

ASY

vic. Nelson BUT

2001-020

27

     

48-49. 26 Jan 2001

2 ASY

vic. Alturas MOD

2001-036

27

     

50-51. 18 Dec 2001

2

Marysville YUB

2002-055

29

     

52. 30 Dec 2001

AHY

Tule Lake NWR SIS

2002-060

27

     

53-54. 26–27 Dec 2002

2 AHY

Tule Lake NWR SIS

2003-022

28

ph.

     

55-57. 08 Feb–07 Mar 2003

3 ASY

Modoc NWR MOD

2003-026

29

ph.

     

58. 11 Mar 2003

SY

Modoc NWR MOD

2003-043

29

     

59. 12 Mar 2003

SY

Lower Klamath NWR SIS

2003-044

29

     
          

Trumpeter Swan – Not accepted, identification not established

     

? Jan 1957

 

Wards Lake LAS

1984-109

14

   

01–13 Jan 1963

 

Abbotts Lagoon MRN

1992-097

16

   

21 Jan 1963

 

Empire Track, Stockton SJ

1984-190

10

   

early Feb–25 Mar 1967

 

Pescadero SM

1989-082

14

ph.

   

31 Dec 1967–14 Jan 1968

5

vic. Santa Rosa SON

1977-041

5

     

29 Dec 1968

3

Año Nuevo State Reserve SM

1984-191

10

     

02 Mar 1969

 

s Humboldt Bay HUM

1984-192

10

   

17 Nov 1974

3

Santa Clara R. mouth VEN

1988-198

15

ph.

     

15 Jul 1975

 

Shingletown SHA

1986-194

14

   

11 Nov 1978

 

Lake Merced SF

1978-125

6

   

04 Feb 1979

 

Lower Klamath NWR SIS

1986-195

12

   

Trumpeter Swan – Not accepted, identification not established (continued)

     

02 Jan 1982

 

Chico BUT

1982-002

9

   

05 Dec 1983

 

Antelope Valley LA

1990-047

14

   

06 Jan 1984

20

Clear Lake NWR MOD

1987-068

12

     

15 Dec 1984

 

Diaz Lake INY

1985-029

12

   

21 Mar 1986

 

Colusa NWR COL

1987-070

14

   

20–25 Jan 1988

 

Modesto STA

1988-208

13,15

ph., AB 42:314, SBMNH 4059 (skeleton of Tundra Swan)

   

18 Mar–02 Apr 1988

 

Sierra Valley PLU

1988-111

16

video

   

29 Dec 1988

 

Lake Almanor PLU

1989-200

15

   

20 Jan 1989

 

Venice I. SJ

1989-053

16

   

23 Dec 1989

 

~5 mi. s Talmage MEN

1990-060

15

ph.

   

01 Jan 1991

2

n Stockton SJ

1991-059

16

     

02–06 Jan 1991

5

Arcata bottoms HUM

1991-058

17

Fig. 12, ph., Heindel & Patten (1996)

     

28 Apr 1991

 

Goose Lake MOD

1992-020

17

   

24 Dec 1991

 

Tule Lake NWR MOD

1992-218

17

   

18 Jan 1992

 

Lower Klamath NWR SIS

1992-104

18

   

07 Feb 1993

3

Modoc NWR MOD

1997-199

22

     

15 Feb 1993

3

Lake Almanor PLU

1993-068

21

     

10 Dec 1994

2

Lake Mendocino MEN

1998-128

23

     

07 Feb 1995

 

vic. Grimes COL

1995-022

22

   

04 Jan 1996

 

vic. Grimes COL

1996-037

23

see table entry 39

   

14 Feb 1998

 

Lower Klamath NWR SIS

1998-194

24

   

15 Feb 1998

 

Ash Creek Wildlife Area LAS

1998-195

24

   

16 Nov 1998

 

Cosumnes R. Preserve SAC

1998-227

24

   

16 Dec 1998

 

vic. Marysville YUB

1998-228

24

   

19 Dec 1998

 

Bobelaine Sanctuary SUT

1999-019

25

   

29 Dec 1998

5

Trinity Center TRI

1999-023

24

     

24 Jan 1999

 

Cosumnes R. Preserve SAC

1999-085

25

   

08 Mar 1999

8

Modoc NWR MOD

1999-084

25

     

22 Jan 2001

4

Yuba City SUT

2001-021

27

     
          

Trumpeter Swan – Not accepted, establishment of introduced population questionable (identification established)

     

02 Feb 1987

2 ASY

Lower Klamath NWR SIS

1987-153

22

     

01 Jan–15 Feb 1988

TY male

Lake Almanor PLU

1988-204

22

     

23 Jan 1992

ASY male

Tecopa INY

1992-206

22

ph.

     

24–27 Dec 1992

3 HY

Independence INY

1993-065

22

ph.

     

and 05 Apr 1993

3 SY

Klondike Lake INY

   

see records not submitted

 

30 Nov–26 Dec 1993

2

Modoc NWR MOD

1994-004

21,22

     

22–23 Dec 1998

AHY

vic. Roseville PLA

1998-230

24

     
          

Trumpeter Swan – Not submitted

     

various 19th-century records

locations unspecified

2004-601

14

see Grinnell & Miller (1944)

     

22 Dec 1893

 

Buena Vista Lake KER

2004-600

14

   

29 Dec 1963

2

Pt. Reyes MRN

 

14

AFN 18:321

   

14–20 Jan 1968

2

Limantour Estero MRN

   

AFN 22:473

 

08 Feb–14 Mar 1969

5

vic. Santa Rosa SON

   

AFN 23:515

 

Jan/Feb 1979

>1?

Lower Klamath NWR SIS/MOD

   

AB 33:309

 

04 Jan 1992

 

Goose Lake MOD

   

AB 46:311

winter 1992/1993

18

SIS to YOL

   

AB 47:296, color-marked transplants

 

22–31 Jan 1993

3 SY

Tinnemaha Res. INY

   

AB 47:300, see record 1993-065 under “Not accepted, establishment of introduced population questionable (identification established)”

 

14–16 Dec 2000

 

Lake Combie PLA

   

NAB 55:224

10 Jan 2002

 

Cosumnes R. Preserve SAC

   

Central Valley Bird Club Bull. 5:26

03–04 Jan 2003

 

Staten I. SJ

   

Central Valley Bird Club Bull. 6:37

20 Jan 2003

 

vic. Blythe RIV

   

NAB 57:256, from managed population

 

Figures

Image3409.TIF

Figure 9. Distribution of 59 Trumpeter Swans accepted through 2003. Most records are from the interior, and very few are from the state’s southern half.

 

Image3354.JPG

Figure 10. The first Trumpeter Swan photographed in California—an adult at Abbotts Lagoon, Marin County, on 4 January 1962—showed several characteristic marks, including an “unpinched” black loral area with no yellow spot, feathering that formed a nearly straight border between eye and gape, and a large bill with the culmen only slightly curved (1984-193; Grace M. Miller).

 

Image3456.TIF

Figure 11. In direct comparison to an adult Tundra Swan (right), note the much larger size and more extensively black face of California’s third Trumpeter Swan (left), an adult photographed on 22 January 1973 on the Carrizo Plain, San Luis Obispo County (1980-179; Brad Schram).

 

Image3508.TIF

Figure 12. After a lengthy review, Committee members were unable to reach a consensus concerning the identification of this family group of swans present from 2 to 6 January 1991 in the Arcata bottoms of Humboldt County. Many reviewers ultimately concluded that the birds may have been Tundra Swans (1991-058; Michael Hughes).

 

 

Trumpeter Swan

TRUMPETER SWAN Cygnus buccinator Richardson, 1832

Accepted: 59 (37%)

Treated in Appendix H: yes

Not accepted: 103

CBRC review: all records

Not submitted/reviewed: 37+

Color image: none

This swan breeds in Alaska and western Canada and at scattered sites in the interior West. After being extirpated from much of its former range in Canada and the interior United States, this species has been re-introduced to historic breeding locations and established in some new ones eastward to the eastern Great Lakes. These conservation measures have enjoyed generally high rates of success (e.g., Mitchell 1994), and the wintering population in western Washington has increased greatly over the past two decades. Marked birds from managed populations have been recorded in places as distant as Texas, Mississippi, Chihuahua (Mitchell 1994), and recently California (see below). An unmarked yearling found in Massachusetts in March 2004 (NAB 58:340) presumably originated in one of the more easterly managed populations. Birds recorded in Arizona and New Mexico during recent years are of questionable origin.

Grinnell and Miller (1944) discussed many early reports from California, but no specimens were preserved, so the CBRC cannot verify any of these early reports. The first record with acceptable documentation refers to a bird observed closely and heard on 8 November 1935 at Bailey Creek Meadow between Grasshopper Valley and Termo, Lassen County (McLean 1937). The first modern record to be physically documented (photographed, in this case) involves an adult present 1 January–9 March 1962 at Abbotts Lagoon in Marin County (Figure 10). All acceptable records fall between 8 November and 15 March, and most are from midwinter.

The Trumpeter Swan is one of relatively few species for which the Committee has accepted fewer than half of the submitted records. Identification problems are considerable and perhaps still underappreciated, especially for first-year birds that have not developed the diagnostic feather patterns around the eye and bill (e.g., see Figure 12, Patten and Heindel 1994). Trumpeter Swans may be more numerous in California than is suggested by the number of accepted records, but misidentifications remain all too frequent. Many reports pertain to lone, silent birds, which do not allow direct comparisons of size, structure, and voice with known Tundra Swans. Only with extensive field experience can one fully understand the variations in size and appearance exhibited by Trumpeter and Tundra Swans (e.g., McEneaney 2005 reviewed rare color variants in the former species) or the range of their vocal repertoires.

Complicating matters further, California has hosted a number of Trumpeter Swans that were transplanted by wildlife managers or that originated from introduced populations. For example, breeding programs have been initiated in both Oregon (mainly at Summer Lake) and Washington (e.g., at Turnbull NWR, where past attempts to establish a population failed; Wahl et al. 2005), even though the species never bred in these states historically (Feltner et al. 1989, Marshall et al. 2003). Collared birds dispersing from these places, and from southern Idaho, have reached California, including southerly records from Santa Barbara and Los Angeles Counties in December 2004 (NAB 59:323; after the cutoff date for this book). On 6 March 2005 the Los Angeles County bird was photographed at Lake Havasu in San Bernardino County (NAB 59:49, CBRC unpubl. data). The CBRC has not accepted such records as involving naturally occurring vagrants. See also Appendix H.