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 |
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 |
Lake Almanor PLU |
1988-204 |
22 |
||||
23 Jan 1992 |
ASY |
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

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.

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).
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).
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.