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2002 Fall Banding Report for Rocky Point Bird Observatory

 

 

by David Woodward


 

 

TABLE OF CONTENTS

 

 Introduction

Methods

Results

Discussion

Acknowledgments

Literature Cited

 References

Tables 1 and 2

Tables 3 and 4

Tables 5, 6, 7, and 8

 Tables 9, 10, and 11

Appendix I

Appendix II

 

 


 

INTRODUCTION

 

Rocky Point Bird Observatory is a banding station located at the extreme southern tip of Vancouver Island. It is used to monitor the migration route of passerines (as well as raptors and seabirds to a lesser extent). This is done through banding, recaptures, and visual and auditory observations. The dominant passerines migrating through this area that were banded were Ruby-crowned Kinglets, Pacific-slope Flycatchers, Wilson’s Warblers, Winter Wrens and Song Sparrows.

The purpose of this research was to get an idea of the passerines migrating through the southwestern tip of Vancouver Island. Although scientific in nature, it does not give a complete summary of all bird migration. This research needs to be conducted and monitored over many years in order to get an accurate picture. This is the ninth year in existence. Also, to get an understanding of migration patterns, this data should be shared with other banding stations across North America.

This paper, however, concentrates on this particular station. Banding totals are examined as well as the efficiency of the nets. In particular, the reasons why some nets might be more productive and why banding totals were high this year. It is a summary of certain aspects of the 2002 banding season. For more information on Banding Totals and especially on Estimated Totals and Census figures see the RPBO website.


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METHODS

 

Research Site

The research was conducted from 20 July- 21 October, 2002. Days lost due to blasting by the Department of National Defence (DND) were from 8 October-11 October. The research site was located in rural Metchosin on the Department of National Defence’s Rocky Point Ammunition Depot, on the southwestern tip of Vancouver Island. The area monitored covered 9 km2. The area covered consisted of open meadows, old growth forest including Douglas and Grand Fir, endangered Garry Oaks and riparian habitat.

Nets and Equipment

There were thirteen mist nets in all, five of which were in the open meadow area and the remaining eight in the forest. The type of mist nets used were 70 denier/2-ply, 2.6 x 12 meters, made of nylon, with 30 mm mesh and 4 shelves. For banding purposes, banding pliers, rulers for measurements, and standardized scales for weighing were used. Birds, once caught in nets, were extracted and placed in cotton bags.

Standardized Procedure

Banding, recapture data, census and estimated totals were done daily, weather permitting. Banding and recaptures started with net openings, half an hour before sunrise. Net closing was six hours after net opening. Another hour was permitted to do observations. Therefore, a total of seven hours was spent in the field. Also, one hour after sunrise census was taken. This count area was within the monitoring area, and an individual who could identify birds conducted the count by sight and sound. The census-taker had one hour and twenty minutes to walk the census route and then report all sightings. At the end of each seven-hour day, estimated total (Ets), were tallied. They included all banded birds during the six-hour standardized banding period, the census count and all observations encountered during the seven-hour count period.

Personnel, Duties and Techniques

The research crew consisted of the bander-in-charge, volunteer staff and other volunteers. The bander-in-charge was responsible for banding the birds, teaching and supervising volunteers, opening and closing nets and administering tasks to the volunteers. Banding criteria was based on identifying the species, sex, age, wing chord, fat deposit and weight. This was done with the aid of the official bird-banding guide for North America written by Peter Pyle.

Ageing was done by using a combination of skulling and plumage techniques. Sexing was done using cloacal protrusions (CP) for males and brood patches (BP) for females. Both techniques, however, could only be used on adult birds. Plumage criteria for ageing and sexing could be used on hatch year (HY) and after hatch year (AHY) birds. For more information, see Pyle, 1997.

Where recaptures were concerned, all banding procedures were done with the exception of putting on a band. Volunteers were responsible for extracting birds from nets (after being supervised by the bander-in-charge), census, observations, acting as scribes and maintaining the net lanes. On days of heavy rain and/or high winds the station was not in operation.


 

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RESULTS

 

Banding Totals

In total, 3153 individuals were banded including 56 species (Appendix1). The most frequent banded species was the Ruby-crowned Kinglet (466), followed by the Pacific-slope Flycatcher (271) and Wilson's Warbler (231). These three species have been at or near the top for the past nine years of banding at Rocky Point (Table1). They accounted for 30.7% of the total birds banded in 2002. The top ten birds banded accounted for 63.5% of the total.

Banding totals were higher this year compared to the eight previous years (Table2). However, 1995 and 1996 had the highest banded species totals with 62 species recorded. It is important to note that this was the first year that thirteen nets were used on a daily basis. The two highest banding days were 17/09 with 101 and 26/09 with 100 (Appendix2).

Age and Sex

The age and sex of the top ten species banded are tabulated in Tables 3 & 4, respectively. Hatch year birds dominated (1629) compared to 302 after hatch year, one second year and 69 unknown age. Hatch years, therefore, accounted for 81.4% of the total top ten birds. Out of the 2001 top ten birds banded, 1140, or 57.0% were of unknown sex. Winter Wrens and Lincoln’s Sparrows were not sexed at all. Pacific-slope Flycatchers and Song Sparrows were only able to be sexed (all females) on seven occasions (Table4).

 

Coverage

Banding days accounted for 87 days out of a potential of 94. Four days were lost due to DND blasting near the site and three days were lost due to excessive rain. This comes to 92.6% banding day coverage. Days lost due to rain were 02 September, 16 September and 03 October. Days lost due to DND blasting were 8 October to 11 October.

Since thirteen nets were used daily, net coverage was the highest this year than any other year (Table5). Net hours this year came to 6509.5, out of a potential of 7332 hours if all thirteen nets had been open for the full six hours of the 94-day banding period. Due to weather (wind and/or rain), however, all or some of the nets may have been closed during the six-hour banding period. Also, since banding only occurred on 87 of the 94 potential banding days, each net had a potential of being open for 522 hours during the banding season. Nets1 and 2 were closed the most often. They both accounted for 428 and 428.5 hours respectively. Nets6, 9 and 10 were kept open the most often (517 hours). Table8 gives a detailed account of all the net hours.

The most productive net was net4 with 382 banded followed by net7 with 366 banded birds from that net (Table7). The additional nets (nets11-13) caught 820 of the total birds banded (Table6). This accounts for 26% of the total birds banded. Birds per net hour this year were 0.48 for nets1-13 and 0.53 for nets11-13. Tables 5 & 6 show how they compare to previous years.

Recaptures

In total 608 birds were recaptured. Song Sparrows (98) and Chestnut-backed Chickadee (90) being the most frequent (Table11). Two Wilson’s Warblers banded in 1998 at RPBO were recaptured.

Rarities

There were three new species added to the RPBO sightings list, including Cattle Egret, Marbled Godwit and Rusty Blackbird (Table9). Also, there were two new species added to the RPBO banding list, including Blue-grey Gnatcatcher and Northern Parula (Table10).


 

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DISCUSSION

 

Banding Totals

Banding totals were higher this year than previous years in part due to the fact that nets11-13 were open for the entire season. Very high Ruby-crowned Kinglet and Pacific-slope Flycatcher numbers also helped boost banding totals. However, Winter Wren and Orange-crowned Warbler numbers were relatively low compared to previous years. Because of this, it is hard to tell whether numbers were higher for other reasons. Good weather conditions play a certain role. For instance, more birds land when migrating at night when there is a weather disturbance during the night. However, weather conditions this year were very good. It was a very dry season, which could mean that large numbers of birds did not land. Only three full days were lost due to rain. Good breeding years for certain key species such as Ruby-crowned Kinglets and Pacific-slope Flycatchers could increase numbers but this type of insight would need co-operation with other biologists.

Banding totals increased from mid-September onward. This can be misleading, however, when looking at peak migration patterns. Certain species peak at different times. For example, Ruby-crowned Kinglets were banded late in the season from late September to late October. They definitely helped increase banding totals late in the season. Wilson Warblers and Pacific-slope Flycatchers were caught mostly in August and early September. These latter species are known to breed in the area so breeding birds could have helped increase banding totals. Ruby-crowned Kinglets are not known to breed in the immediate area but when they come through late in the season they often constitute most of the birds banded on any given day. Without Ruby-crowned Kinglets, banding in October would be very slow.

Net Coverage

Good coverage can be misleading. While nets hours were extremely high this year compared to previous years, birds per net/hour were not. If there are not as many birds in the area, leaving more nets open will not necessarily mean a higher proportion of birds. It seems that since birds/net hour were low this year, that weather could have played a factor in the total birds caught. In 2001,for instance, if there were thirteen nets open for the full season numbers could have been higher than 2002 due to the fact that birds/net hour were considerably higher. Nets11-13 also were not as efficient as 2001 and 2000. Birds/net hour were considerably higher in both previous years. This could suggest that other factors (other than the total of nets) are involved in total birds banded. The right weather conditions for birds to descend and productive breeding success being two possible considerations. Keeping thirteen nets open for the entire season in the years to come will give a better indication of banding totals.

Some nets were more productive than others. For instance, net8 was very poor. Nets4 and 7 were relatively productive. It could be that the latter nets were more hidden or that the vegetation contained more insects for forage. Nets that are well hidden usually catch more birds and it seems that in this case it was true. Although there were a lot of birds in the vicinity of net8 it was not very well hidden. Nets1 and 2 were very close to nets3 and 4 but not as productive. The previous were in the grassland area. The latter, however, were surrounded by tall bushes and trees as well as grassland. This could suggest that not only are the nets more hidden but also the area may contain a higher diversity of bird species. This seemed to be the case as nets3 and 4 caught high numbers of Sparrows and Warblers while nets1 and 2 caught mostly Sparrows and Goldfinches. Nets1 and 2, however, were often closed due to high westerly winds. This would have a negative impact on their banded totals.

Nets surrounded by a higher diversity of plants might enable birds to find more to forage on (insects, berries and seeds), hide from predators as well as not see nets since the vegetation makes the nets less visible. Various heights of vegetation around nets should also catch birds that forage at different levels. MacArthur (1958) found that five Warbler species occupied feeding niches in firs and spruces that were considerably distinct. Birds that occupy different foraging niches might get caught in different panels thereby increasing the number of birds that get caught. The fact that there is high vegetation surrounding nets and that the nets are well hidden does not in itself mean that they will be productive. Nets5 and 10 were well hidden by tall vegetation but did not catch a significantly higher amount of birds. Birds around these nets such Chestnut-backed Chickadees would often fly over. However, net10 was productive at catching Winter Wrens since they move about at low levels in dense brush.

Sex and Age

Most birds that were caught turned out to be hatch year birds. Skulling in the fall is a big help in determining their age. Pacific-slope Flycatchers were not reliably aged, as their skulls did not always match their plumage criteria. For instance, a bird that was skulled as a hatch year did not necessarily have plumage that would indicate a hatch year especially early in the season. Later in the season, hatch year skulls did match hatch year plumage on a more regular basis.

Species that do not show sexual dimorphism cannot be reliably sexed. These include the Sparrows, Flycatchers and Wrens. Since breeding birds were caught, some adults could be sexed by brood patch or cloacal protrusion. These were limited to breeding birds early in the season. Pacific-slope Flycatcher and Song Sparrows were two such species that were suspected of breeding in the area and were sexed using these methods.

Recaptures

Song Sparrows are suspected of breeding in the area. To confirm this some adults had been found with brood patches. This might help explain their high recapture rate. Wilson’s Warblers and Common Yellowthroats are also suspected breeders. Some hatch years that were caught had barely reached the fledgling stage. The two Wilson’s Warblers caught in 1998 could also help confirm breeding status. Backed-backed Chickadees might use the area to breed and forage year round. Ruby-crowned Kinglets were so numerous this year that recaptures seemed inevitable.

Rarities

Two new species banded this year at RPBO were the Blue-grey Gnatcatcher and the Northern Parula. The previous breeds historically as far north as southern Oregon (National Geographic, third edition). The latter’s breeding range extends as far west as eastern Manitoba (National Geographic, third edition). They were definitely out of their historical range. The Marbled Godwit was seen early in the season on the mudflats and it hung around for several days. The Cattle Egret was a flyover.

 

Summary

Excellent coverage and additional nets made this the most productive banding season yet. However, because of the lack of weather disturbances it was not the most efficient in terms of birds caught per net. Banding totals should increase in the years to come with thirteen nets open and improved weather conditions. Ruby-crowned Kinglets were exceptionally high this year. Pacific-slope Flycatchers and Wilson’s Warblers were a distant second.


 

 

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ACKNOWLEDGMENTS

I wish to thank the following volunteers for their contribution to the banding season:

Gabriel David, June Pretzer, Robert Hadley, Michael Dyson, Ed Pellizzon, Jen Rock, Ted Ardley, Jeremy Gatton, Jessica Murray, Laurie Savard, Erin Burrell, Nathan Debruin, Rob Gowan, Camela Smith, Naira Johnstone, Kim West, Christy Morrissey, Nathan West, Brent Beach, Sue Ennis, Ann Duncan, Michael Clinchy, Joanne MacDonald, John Cooper, Susanne Maidment, Al Storey, Andy Stewart, Claudia Steinacker, Cyril Schonbachler, David Kelly, Kristi Millner, Ginette Heppelle, Rick Toochin, George Clulow, Brian Self, Carlo Giavanello, Owain Mckibbin, Rene Mckibbin, Chris Sanders, Don Eastman, Guy Monty, Eric Higgs, Andrew MacDonald and Dale Jensen.

I would especially like to thank the volunteer staff who run the banding station year-round. Without their tireless support, on and off the field, the season would have been a lot more gruelling. They are as follows:

President… David Allinson

Vice-President… Colleen O’Brien

Treasurer… Thomas Gillespie

Secretary… Denise Gubersky

Rod Mitchell

Ann Nightingale

Paul Levesque

Rick Schortinghuis

Michael Porter

Suzanne Beauschesne

Marilyn Lambert

Lastly, I would like to Jukka Jantunen who was the bander-in-charge for the last ten days of banding.


 

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LITERATURE CITED

 

Derbyshire, D. 2000. A report on Migration Monitoring at Rocky Point: Fall 2000. Rocky Point Bird Observatory, Metchosin, British Columbia.

Gibson, G.C. 2001. A report on Migration Monitoring at Rocky Point: Fall 2001. Rocky Point Bird Observatory, Metchosin, British Columbia.

Pyle, P. 1997. Identification Guide to North American Birds. Part1. Slate Creek Press, Bolinas, California.


REFERENCES

 

MacArthur, R.H. (1958). Population ecology of some warblers of northeastern coniferous forests. Ecology 39. 599-619.

National Geographic. 1999. Field Guide to the Birds of North America. Third Edition. Published by National Geographic Society.


 

TABLES

 

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Table 1. Top ten species banded in 2002 compared to years 1994-2001.

Species

2002

2001

2000

1999

1998

1997

1996

1995

1994

Pacific-sloped Flycatcher

271

187

228

228

209

91

54

79

52

Winter Wren

177

204

265

61

135

102

106

64

75

Golden-crowned Kinglet

117

94

81

57

53

37

25

10

26

Ruby-crowned Kinglet

466

186

295

199

156

159

232

79

70

Orange-crowned Warbler

150

220

125

185

117

109

82

67

66

Yellow Warbler

114

109

139

106

57

101

38

45

44

Wilson's Warbler

231

225

177

257

153

53

37

58

70

Song Sparrow

168

109

120

71

101

114

63

79

134

Lincoln's Sparrow

148

102

171

154

160

138

120

124

151

American Goldfinch

159

146

45

68

107

46

39

42

90

Totals

2001

1582

1646

1386

1248

950

796

647

778

 

Table 2. Total birds banded and species totals from 1994-2002

 

2002

2001

2000

1999

1998

1997

1996

1995

1994

Total banded

3153

2576

2723

2255

2127

1818

1571

1260

1547

Total species

56

54

57

61

59

52

62

62

60

*2002 total of 13 nets
*2000-2001 nets 11-13 used only on odd days
*1994-1999 total of 10 nets


 

 

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Table 3. The ages of the top ten species banded.

Species

HY

AHY

U

SY
Pacific-slope Flycatcher

212

43

16
Winter Wren

143

27

7
Golden-crowned Kinglet

99

15

3
Ruby-crowned Kinglet

385

55

26
Orange-Crowned Warbler

101

44

5
Yellow Warbler

80

34
Wilson's Warbler

213

12

6
Song Sparrow

149

16

3
Lincoln's Sparrow

122

24

2
American Goldfinch

125

32

1

1
Total

1629

302

69

1

 

Table 4. The sexes of the top ten species banded.

Species

M

F

U
Pacific-slope Flycatcher

5

266
Winter Wren

177
Golden-crowned Kinglet

64

22

31
Ruby-crowned Kinglet

178

81

207
Orange-crowned Warbler

43

45

62
Yellow Warbler

43

38

33
Wilson's Warbler

116

88

27
Song Sparrow

2

166
Lincoln's Sparrow

148
American Goldfinch

86

50

23
Total

530

331

1140


 

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Table 5. Coverage effort from 1999-2002.

Year

Coverage period

Days

Banded

Net hours

Birds/net hour

2002

20/07-21/10

87

3153

6509.5

0.48

2001

23/07-7/10

75

2576

4296

0.6

2000

21/07-21/10

90

2724

5113

0.53

1999

23/07-23/10

87

2255

4493

0.48
*1999 ten mist nets used
*2000-2001 ten mist nets and three additional mist nets used on odd days
*2002 thirteen mist nets used

 

Table 6. Capture rate for nets 11-13 (additional nets).

 

Year

Banded

Net hours

Birds/net hour

2002

820

1536.5

0.53

2001

394

560

0.7

2000

620

692

0.89
 

Table 7. Productivity of all thirteen nets.

 

Table 8. Net hours per net

Net

Banded

% of total

Net

Hours

1

160

5.1

1

428.5

2

225

7.1

2

428

3

354

11.2

3

513.5

4

382

12.1

4

513.5

5

115

3.6

5

516.5

6

204

6.5

6

517

7

366

11.6

7

511

8

60

1.9

8

511

9

288

9.2

9

517

10

173

5.5

10

517

11

295

9.4

11

506.5

12

219

7

12

515

13

306

9.7

13

515
Total

3147

99.9
Total

6509.5
*percentage based on 3147 banded


 

 

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Table 9. Non-banded Rarities

Table 10. Banded Rarities

Yellow-billed loon Northern Pygmy Owl
Sooty Shearwater Dusky Flycatcher
Fork-tailed Storm Petrel Blue-gray Gnatcatcher (RPBO first)
Cattle Egret (RPBO first) Northern Parula (RPBO first)
Broad-winged Hawk Black-headed Grosbeak
Rough-legged Hawk Swamp Sparrow
Golden Eagle White-throated Sparrow
Whimbrel
Marbled Godwit (RPBO first)
Ruddy Turnstone
Red Knot
Pomarine Jaeger
Parasitic Jaeger
Franklin's Gull
Little Gull
Black-legged Kittiwake
Tufted Puffin
Barn Owl
Black Swift
Red-breasted Sapsucker
Lewis's Woodpecker
Bank Swallow
Nashville Warbler
Northern Waterthrush
Western Palm Warbler
Yellow-headed Blackbird
Rusty Blackbird (new RPBO sp.)

 

Table 11. Top 5 recaptured species.

Species

#
Chestnut-backed Chickadee

90
Ruby-crowned Kinglet

54
Common Yellowthroat

55
Wilson's Warbler

50
Song Sparrow

98


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Appendix 1 Total birds banded

Species
Numbers banded
Sharp-shinned Hawk

10
Northern Pygmy Owl

1
Northern Saw-whet Owl

1
Downy Woodpecker

1
Red-shafted Flicker

2
Traill's Flycatcher

47
Hammond's Flycatcher

23
Dusky Flycatcher

1
Pacific-sloped Flycatcher

271
Hutton's Vireo

4
Warbling Vireo

11
Steller's Jay

8
Violet-green Swallow

4
Northern Rough-winged Swallow

2
Chestnut-backed Chickadee

93
Bushtit

45
Red-breasted Nuthatch

4
Brown Creeper

9
Bewick's Wren

34
House Wren

11
Winter Wren

177
Marsh Wren

8
Golden-crowned Kinglet

117
Ruby-crowned Kinglet

466
Blue-gray Gnatcatcher

1
Swainson's Thrush

62
Hermit Thrush

53
American Robin

15
Cedar Waxwing

7
Orange-crowned Warbler

150
Northern Parula

1
Yellow Warbler

114
Yellow-rumped Warbler

31
Black-throated Grey Warbler

4
Townsend's Warbler

2
MacGillivray's Warbler

48
Common Yellowthroat

74
Wilson's Warbler

231
Black-headed Grosbeak

1
Spotted Towhee

88
Chipping Sparrow

14
Savannah's Sparrow

74
Fox Sparrow

95
Song Sparrow

168
Lincoln's Sparrow

148
Swamp Sparrow

1
White-throated Sparrow

1
White-crowned Sparrow

96
Golden-crowned Sparrow

66
Oregon Junco

63
Red-winged Blackbird

8
Brown-headed Cowbird

7
Purple Finch

6
House Finch

6
Pine Siskin

9
American Goldfinch

159
Total individuals

3153
Total Species

56


 

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Appendix 2 Captures per day.

Date

Banded
       
20-Jul

28
31-Aug

17
19-Oct

17
21-Jul

29
1-Sep

7
20-Oct

14
22-Jul

31
3-Sep

32
21-Oct

18
23-Jul

37
4-Sep

23
Total banded=3156
24-Jul

38
5-Sep

51
Total days banding=87
25-Jul

24
6-Sep

61
Average/day=36
26-Jul

45
7-Sep

67
27-Jul

27
8-Sep

17
28-Jul

27
9-Sep

11
29-Jul

11
10-Sep

8
30-Jul

33
11-Sep

59
31-Jul

31
12-Sep

37
1-Aug

48
13-Sep

27
2-Aug

30
14-Sep

20
3-Aug

35
15-Sep

16
4-Aug

21
17-Sep

101
5-Aug

27
18-Sep

80
6-Aug

57
19-Sep

26
7-Aug

36
20-Sep

50
8-Aug

26
21-Sep

50
9-Aug

22
22-Sep

39
10-Aug

25
23-Sep

54
11-Aug

20
24-Sep

51
12-Aug

24
25-Sep

44
13-Aug

8
26-Sep

100
14-Aug

14
27-Sep

58
15-Aug

11
28-Sep

60
16-Aug

14
29-Sep

74
17-Aug

14
30-Sep

66
18-Aug

26
1-Oct

70
19-Aug

19
2-Oct

66
20-Aug

50
4-Oct

85
21-Aug

33
5-Oct

69
22-Aug

38
6-Oct

44
23-Aug

24
7-Oct

40
24-Aug

39
12-Oct

37
25-Aug

30
13-Oct

24
26-Aug

17
14-Oct

26
27-Aug

33
15-Oct

28
28-Aug

17
16-Oct

29
29-Aug

27
17-Oct

48
30-Aug

46
18-Oct

40

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1514

Copyright 2006, Rocky Point Bird Observatory.