Seaside centipede lichen (Heterodermia sitchensis) COSEWIC assessment and status report: chapter 7

Population Sizes and Trends

Search effort

From 2001 to 2004, Parks Canada supported a considerable search effort for H. sitchensis. A total of 30 person days of search time has been dedicated to this species each summer, with a total of 60 days devoted to Pacific Rim National Park and 30 each to Gwaii Haanas (South Moresby Island) and northern Vancouver Island. To these more recent search efforts can be added several earlier field studies concentrated in coastal B.C., especially those of Dr. Irwin Brodo in the Queen Charlotte Islands in 2000 (I.M. Brodo, pers. comm.). See Appendix 1. Other search efforts within the known range of H. sitchensis are summarized in Table 2 and mapped in Figure 3.

Table 2.  Significant macrolichen collections within the potential Canadian (and American) range of Heterodermia sitchensis
Map numbers 1, 65 and 105 are labelled in Figure 3
Map # Location Year visited Collector # lichen specimens collected
1 Haida Gwaii (Queen Charlotte Islands) 1967-2000 E. Brodo
5500
2 Alice Lake 1969-1970 K. Ohlsson
66
3 Squamish River 1969-1970 K. Ohlsson
24
4 Black Tusk 1969-1970 K. Ohlsson
50
5 Black Tusk 1969-1970 K. Ohlsson
45
6 Black Tusk 1969-1970 K. Ohlsson
25
7 Alta Lake 1969-1970 K. Ohlsson
38
8 Pemberton 1969-1970 K. Ohlsson
27
9 Alice Lake 1969-1970 K. Ohlsson
40
10 Sechelt 1969-1970 K. Ohlsson
82
11 Port Mellon 1969-1970 K. Ohlsson
19
12 Wilson Creek 1969-1970 K. Ohlsson
22
13 Walt Lake 1969-1970 K. Ohlsson
88
14 Frank Island and Cox Bay 1969-1970 K. Ohlsson
110
15 Kennedy Lake 1969-1970 K. Ohlsson
30
16 Kennedy Lake 1969-1970 K. Ohlsson
16
17 Cox Bay 1969-1970 K. Ohlsson
17
18 Goldstream Park 1969-1970 K. Ohlsson
11
19 Mt. Cain 1969-1970 K. Ohlsson
141
20 Schoen Lake 1969-1970 K. Ohlsson
44
21 Marble River 1969-1970 K. Ohlsson
38
22 Beaver Harbour 1969-1970 K. Ohlsson
69
23 Coal Harbour 1969-1970 K. Ohlsson
35
24 Holberg 1969-1970 K. Ohlsson
30
25 Port McNeil 1969-1970 K. Ohlsson
83
26 Buttle Lake 1969-1970 K. Ohlsson
73
27 Mt. Becher 1969-1970 K. Ohlsson
84
28 Forbidden Plateau 1969-1970 K. Ohlsson
14
29 Young Creek 1969-1970 K. Ohlsson
45
30 Mosher Creek 1969-1970 K. Ohlsson
44
31 Bella Coola 1969-1970 K. Ohlsson
33
32 Thorsen River 1969-1970 K. Ohlsson
31
33 Crayden Bay 1969-1970 K. Ohlsson
50
34 Kwatna Inlet 1969-1970 K. Ohlsson
8
35 Restoration Bay 1969-1970 K. Ohlsson
9
36 Namu 1969-1970 K. Ohlsson
40
37 Atnarko River 1969-1970 K. Ohlsson
42
38 Burnt River 1969-1970 K. Ohlsson
49
39 Mt. Walker 1969-1970 K. Ohlsson
28
40 Bella Coola River 1969-1970 K. Ohlsson
28
41 Four Mile Mountain 1969-1970 K. Ohlsson
43
42 Bella Coola Valley Summit 1969-1970 K. Ohlsson
19
43 Anahim Lake 1969-1970 K. Ohlsson
35
44 Furlong Bay 1969-1970 K. Ohlsson
15
45 Robinson Lake 1969-1970 K. Ohlsson
25
46 Hartley Inlet 1969-1970 K. Ohlsson
22
47 Kishkosh Inlet 1969-1970 K. Ohlsson
23
48 Port Ashton 1969-1970 K. Ohlsson
23
49 Emsley Pt 1969-1970 K. Ohlsson
4
50 Mt. Attree 1969-1970 K. Ohlsson
49
51 Furlong Bay 1969-1970 K. Ohlsson
31
52 Williams Creek 1969-1970 K. Ohlsson
35
53 Minette Bay 1969-1970 K. Ohlsson
39
54 Kitimat River 1969-1970 K. Ohlsson
26
55 Bornite Mountain 1969-1970 K. Ohlsson
43
56 Mt. Claque 1969-1970 K. Ohlsson
35
57 Bornite Mountain 1969-1970 K. Ohlsson
42
58 Mannix Creek 1969-1970 K. Ohlsson
29
59 Dorreen 1969-1970 K. Ohlsson
26
60 New Hazelton 1969-1970 K. Ohlsson
18
61 Buckley River 1969-1970 K. Ohlsson
41
62 Nine Mile Mt. 1969-1970 K. Ohlsson
25
63 Nine Mile Mt. 1969-1970 K. Ohlsson
43
64 Seeley Lake 1969-1970 K. Ohlsson
28
65 Gulf Islands & SE Vancouver Island 1974-1981 W. Noble
5500
66 Burns Bog 1982 T. Goward
30
67 Dyea, Alaska 1982 T. Goward
50
68 Taku River 1982 T. Goward
165
69 Pacific Rim National Park 1982-1983 T. Goward
1500
70 Port Alberni 1983 T. Goward
15
71 Sooke 1984 T. Goward
85
72 Gates Lake 1984 T. Goward
120
73 Vancouver 1986 T. Goward
110
74 Upper Campbell Lake, Vancouver Island 1991 T. Goward
3
75 China Beach and s. Vancouver Isl. 1991 T. Goward
11
76 Carmanah Valley and area 1991 T. Goward
120
77 Bamfield 1991 T. Goward
46
78 Port Alberni 1991 T. Goward
64
79 Sayward Area 1991 T. Goward
125
80 Kispiox Valley 1991 T. Goward
128
81 Terrace 1991 T. Goward
240
82 Skeena (w. of Terrace) 1991 T. Goward
76
83 Prince Rupert 1991 T. Goward
100
84 South Hazelton area 1991 T. Goward
38
85 Kitimat 1991 T. Goward
48
86 Kitlope 1991 T. Goward
114
87 Sooke 1991 T. Goward
56
88 Cathedral Grove - Port Alberni 1991 T. Goward
130
89 Tofino 1991 T. Goward
75
90 Cultus Lake - Chilliwack Lake 1991 T. Goward
145
91 Mt. Baker (WA, USA) 1992 T. Goward
17
92 Lower Fraser Valley 1992 T. Goward
1
93 Kispiox 1992 T. Goward
150
94 Haines Triangle - Tatshenshini R 1992 T. Goward
700
95 Chilliwack Lake 1992 T. Goward
63
96 Kispiox 1994 T. Goward
10
97 Kispiox 1995 T. Goward
290
98 Meziadin Lake 1995 T. Goward
90
99 Bell-Irving 1995 T. Goward
60
100 Hazelton 1995 T. Goward
17
101 Mount Cain 1996 T. Goward
475
102 KispioxValley 1996 T. Goward
82
103 Pacific Rim National Park, Vancouver Island 2001 T. Goward
175
104 Pacific Rim National Park, Vancouver Island 2002 T. Goward
155
105 South Morseby (Gwaii Haanas N. P.) 2003 T. Goward/T. Tønsberg
720
106 Queen Charlotte Strait 2004 K. Wright
200
107 Kyuquot Sound, Vancouver Island 2004 K. Wright
200
  Total number of speciments collected:    
20446

Abundance

Two hundred and twenty-seven thalli of H. sitchensis in twelve localities have been recorded to date, including two localities that no longer support this species. Sixty-five percent of these thalli, however, were noted at only three of the existing localities (Table 3).

Table 3. Localities of Heterodermia sitchensis, their history of documentation and potential threats
Detailed locality information is given in Appendix 1
Locality First record abundance
(No. of thalli)
Last record abundance
(No. of thalli)
Ownership
Threats
Canada, British Columbia, Vancouver Island, Schooner Cove (Type locality) 30 March 1983
12 (min.)
16 June 2002
4 (1 thallus dying)
National Parkland (Pacific Rim National Park Reserve)
Disturbance by recreationists
Canada, British Columbia, Vancouver Island, Ucluth Peninsula 3 April 1983
4 (min.)
3 April 1983
N/A
Private land; unprotected
Colony extirpated by 1991 by logging for a housing development
Canada, British Columbia, Vancouver Island, Quisitis Point 17 July 2001
6
17 July 2001
N/A
National Parkland (Pacific Rim National Park Reserve)
Disturbance by recreationists
Canada, British Columbia, Vancouver Island, Florencia Island 24 July 2001
56
11 June 2002
27
National Parkland (Pacific Rim National Park Reserve)
Disturbance by recreationists
Canada, British Columbia, Vancouver Island, Ucluth Peninsula 18 July 2001
2
18 July 2001
N/A
Private land
Logging
Canada, British Columbia, Vancouver Island, Benson Island 20 June 2002
1
20 June 2002
N/A
National Parkland
(Pacific Rim National Park Reserve)
Disturbance by recreationists
Canada, British Columbia, Vancouver Island, Dicebox Island 21 July 2001
1
21 July 2001
N/A
National Parkland
(Pacific Rim National Park Reserve)
Disturbance by recreationists
Canada, British Columbia, Vancouver Island, Wouwer Island 21 July 2001
44
18 June 2002
12 (not a complete count)
National Parkland
(Pacific Rim National Park Reserve)
Disturbance by recreationists
Canada, British Columbia, Clayoquot Sound, Vancouver Island, Lawrence Island July 2001
1 (not a complete count)
12 June 2002
21
Crown Land
Logging
Canada, British Columbia, Vancouver Island, Folger Island 19 June 2002
18
19 June 2002
N/A
Crown Land
Logging
Canada, British Columbia,  Vancouver Island, vicinity of Kyuquot 26 June 2004
14 (8 on fallen branch)
26 June 2004
N/A
Crown Land
Logging & Disturbance by recreationists
Canada, British Columbia, Vancouver Island, a second location in the vicinity of Kyuquot 26 June 2004
48
26 June 2004
N/A
Crown Land
Logging & Disturbance by recreationists
United States of America, Oregon, Tillamook Co.,  Cape Lookout 11 September 2000 10 June 2001
5-10 (T. Tønsberg, pers. comm.)
State Park
Disturbance by recreationists (heavy use) & changes in environmental conditions

Fluctuations and trends

What little is known about population trends in H. sitchensis is based on observations made at two localities. The first of these is the holotype locality at Schooner Cove where in 1983 a single Sitka spruce branch bore at least a dozen thalli. When this same branch was re-examined twenty years later, in 2002, it was found to support only a single, rather moribund thallus of H. sitchensis. Also lacking on this branch was Physcia tenella, which had been reported two decades earlier (Goward 1984). The fact that both H. sitchensis and P. tenella are nitrophiles could suggest that their decline here is related to a gradual decline in nutrient status. In 1983 the host branch was apparently situated within the nutrient column of a bird perch no longer in use 20 years later. According to this scenario, potential host branches for H. sitchensis are likely to be available to this species for a short time only, depending on the spatial configuration of nutrient supply, suitable substrate (slow-growing Sitka spruce twigs), and diaspore availability.

One of the most productive sites for H. sitchensis is a stretch of shoreline on WouwerIsland in the Broken Group Islands. Here, in 2001, a dozen thalli were noted among the lower branches of a stunted Sitka spruce tree exposed to northwest winds. When the same tree was visited in 2002, only eight thalli were found, one of which was apparently healthy, the others dead. A careful survey of the upper canopy revealed an additional twelve thalli, of which only four were alive. The high incidence of dead thalli points to a die-back event during the winter of 2001/2002. In fact, such a die-back had been predicted by Barry Campbell (pers. comm.), on the basis of exceptionally strong northwest winds in April of 2002. The branches of the host tree appear to have been repeatedly drenched with salt water, as suggested by the greenish algal layer covering the basal portions of the lichens. Epiphytic mosses, too, had been partly smothered by algae. Damage in the upper canopy was less extensive than in the lower canopy. Discoloured lichen thalli were noted in many other localities in 2002, especially in sites exposed to northwest winds.

Rescue effect

At the present time, H. sitchensis is an almost exclusively Canadian species, with only a single, presumably relictual population known from the United States. Because of this, diaspores originating from points south of the border are extremely unlikely to remedy future population losses in Canada.

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