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CK RESEARCH AND MANAGEMENT
1966
UNITED STATES DEPARTMENT OF THE INTERIOR
FISH AND WILDLIFE SERVICE
BUREAU OF SPORT FISHERIES AND WILDLIFE
Special Scientific Report-Wildlife No. 101
UNITED STATES DEPARTMENT OF THE INTERIOR, STEWART L. UDALL, Secretary Stanley A. Cain, Assistant Secretmy for Fish and Wildlife and Parks
Fish and Wildlife Service, Clarence F. Pautzke, Commissioner Bureau of Sport Fisheries and Wildlife, John S. Gottschalk, Director
WOODCOCK RESEARCH AND MANAGEMENT, 1966
Compiled by William H. Goudy
Migratory Bird Populations Station Division of Wildlife Research
Drawings by Lata R, Goudy
Special Scientific Report — Wildlife No. Washington, D, C. • April 1967
101
CONTENTS
ABSTRACT iv
INTRODUCTION 1
THE 1966 STATUS OF AMERICAN WOODCOCK AND RECENT POPULATION TRENDS , by William H. Goudy 3
RELATION BETWEEN MALE COURTSHIP ACTIVITIES AND NESTING OF
AMERICAN WOODCOCK, by Aelred D. Geis 13
TRENDS IN THE CONTINENTAL WOODCOCK HARVEST,
by William H. Goudy 15
TRENDS IN WOODCOCK HARVESTS AND HUNTER INTEREST IN MAINE,
by J. William Peppard 20
resume' OF 1965 's WOODCOCK HUNTING SURVEY IN PENNSYLVANIA,
by Stephen A. Liscinsky 22
TENNESSEE'S WOODCOCK INVESTIGATIONS,
by Eugene Legler , Jr » 24
A SUMMARY OF WOODCOCK HEN AND CHICK BANDING IN MICHIGAN,
by George A. Ammann 26
WOODCOCK SUMMER BANDING OPERATIONS AT THE MOOSEHORN
NATIONAL WILDLIFE REFUGE, by Eldon R. Clark 28
WOODCOCK BANDING STUDIES IN WEST VIRGINIA'S CANAAN VALLEY, by Robert C. Kletzly and Joe Rief fenberger 31
WOODCOCK NIGHT- LIGHTING TECHNIQUES AND EQUIPMENT,
by Joe Rief fenberger and Robert C. Kletzly 33
WOODCOCK BRIEFS FROM HERE 'N THERE,
by William H. Goudy • 36
REFERENCES 39
111
ABSTRACT
Surveys designed to determine the population status of American woodcock indicate little change in recent continental breeding populations, but a continuing decline in production. The annual harvest of this species, meanwhile, continues to soar with an apparent upsurge in hunters' awareness of the woodcock's sporting qualities. Research activities continue to uncover information related to the reliability of singing- ground surveys while banding operations in Louisiana, Maine, Michigan, and West Virginia testify to the feasibility of expanding this very important program throughout North America. West Virginia has contributed significantly to this program through its improvement of the night- lighting technique which was developed in association with their primary objective of evaluating the importance of hunting as a mortality factor. Woodcock bandings and recoveries from the Moosehorn National Wildlife Refuge are being examined to determine more about the characteristics of this lightly harvested population and to better understand their use of various habitat types.
IV
WOODCOCK RESEARCH AND MANAGEMENT, 1966
The secretive, sombre-colored American woodcock (Philohela minor Gmelin) is one of our finest game birds as well as being a special attraction to non-hunters. The nesting female serves as an excellent model for photographers, while the male's spectacular courtship antics provide many hours of refreshing observation on warm, spring evenings. The woodcock provides most of its recreation from early September to the end of January as its darting shadow challenges both the novice and the experienced hunter. To many of the latter, woodcock are a favorite game bird even though most hunters consider them as an incidental (but welcome) addition to their primary bag of ruffed grouse, bobwhite quail, pheasants, or rabbits. Its habitat and flushing character- istics usually cause many rounds of ammunition to be expended before a daily bag of five birds has been obtained. Thus, the American woodcock must be considered as having economic as well as esthetic value.
This report summarizes recent activities concerned with woodcock research and management programs and plans throughout North America. We sincerely thank those who have contributed to this publication. Although special appreciation is expressed to the authors of the articles appearing on the following pages, sincere gratitude is also extended to those who take the time each spring to conduct singing-ground surveys in both the United States and Canada.
-1-
Figure l.--West Virginia Game Biologist Robert C. Kletzly
releasing a newly banded woodcock which was captured in a mist net (photo courtesy West Virginia Department of Natural Resources Hal Dillon photographer).
THE 1966 STATUS OF AMERICAN WOODCOCK AND RECENT POPULATION TRENDS
William H. Goudy
Research Biologist
Migratory Bird Populations Station
Laurel, Maryland
Two major surveys are conducted in eastern North America each year to obtain information concerning the population status of American woodcock. A singing-ground survey, conducted each spring in most States and Provinces where woodcock nest, provides an index to the size of the breeding population. During the hunting season, the wing-collection survey is conducted to obtain an index of reproductive success and to appraise changes in the geographic distribution and size of the harvest. The wing-collection survey also provides information necessary in establishing effective regulations.
This report summarizes results of recent woodcock singing- ground and wing-collection surveys.
SINGING -GROUND SURVEY
Breeding Population Index - Singing- ground counts have been conducted annually throughout much of North America's primary woodcock nesting range since 1953. These surveys are conducted primarily to determine changes in the spring breeding popula- tion. Techniques and methods employed in this survey have been thoroughly discussed in previous Special Scientific Reports (Robbins 1960; Martin 1961, 1962, 1963, and 1964; and Goudy and Martin 1966).
An index to the 1966 population was obtained from 188 com- parable survey routes conducted in 18 States and 2 Provinces. Results from this survey indicated a "singing" male population very similar to 1965 's (table 1). A comparison of recent
woodcock breeding population indexes obtained from comparable singing-ground survey routes, between adjacent years, is presented in table 2. When these values are combined and adjusted to the 1965 index (as the base year), a gradually increasing breeding population is suggested (fig. 2-A).
WING- COLLECTION SURVEY
Productivity Index - Reproductive success is usually meas- ured by the ratio of immature birds to adult females in the fall bag. Woodcock can be aged and sexed by examining their wing feathers; therefore, a wing-collection survey was initiated in 1959 to determine breeding success and to evaluate changes in annual productivity.
Prior to each hunting season, woodcock wing-collection envelopes are mailed to hunters who sent in wings during the previous season. A sample of "duck stamp" purchasers, who indicated in the Waterfowl Kill Survey that they also hunted woodcock, have been asked to participate in the Woodcock Wing- Collection Survey since 1965. By combining the information received from these two sources , we attempt to obtain wings from all 32 States that provide woodcock hunting opportunities. The Canadian Wildlife Service also distributes envelopes to some of their hunters that pursue this fine game bird. The response of hunters during past hunting seasons has been out- standing and they have contributed an average of over 12,000 wings annually (table 3). Last year (1965-66 hunting season), 11,947 woodcock wings were received at the Migratory Bird Populations Station from 1,001 cooperating hunters (table 4).
The number of immatures per adult female has varied con- siderably among States and Provinces (table 5), and within these harvest areas, between years (Goudy and Martin 1966). This variation was probably caused by differences in hunting season dates, varying weather conditions, and extreme fire conditions which restricted hunting seasons. Nevertheless, during the first 6 years of this survey, age ratios in the North American kill did not vary more than 4 percent from an adjusted weighted mean of
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1.63 immature birds per adult female. However, age ratios from woodcock shot during the 1965 hunting season decreased almost 9 percent from those obtained in 1964 (table 6). Since age ratios derived from a wing-collection survey can be seriously affected by such things as differential vulnerability and migration, it is quite possible that no real change occurred in 1965 's wood- cock production. It should also be noted, though, that this is the fourth consecutive year that this survey has indicated a lower ratio of immatures in the fall bag (fig. 2-B).
■6-
Table 1. --Woodcock breeding population indexes as indicated by singing-ground surveys
in 1965 and 1966
State or Province
Total number of routes conducted
1965 1966
Number
of
comparable
routes
Number of
woodcock heard
per comparable
route
1965
1966
Percent change in woodcock heard per route from 1965
EASTERN REGION
Connecticut |
13 |
12 |
9 |
3,67 |
3.22 |
Delaware |
1 |
4 |
1 |
5.00 |
5.00 |
Maine |
42 |
43 |
32 |
9.00 |
8.63 |
Maryland |
3 |
26 |
2 |
6.50 |
3.30 |
Massachusetts |
8 |
8 |
6 |
8.67 |
7.50 |
New Brunswick |
6 |
9 |
2 |
11.00 |
7.50 |
New Hampshire |
13 |
13 |
3 |
3.33 |
3.33 |
New Jersey |
5 |
5 |
3 |
6.00 |
6.67 |
New York |
36 |
29 |
18 |
6.89 |
6.72 |
North Carolina |
13 |
0 |
0 |
-- |
-- |
Nova Scotia |
23 |
30 |
12 |
8.00 |
8.00 |
Pennsylvania |
26 |
23 |
14 |
7.29 |
7.86 |
Prince Edward Is. |
3 |
3 |
0 |
-- |
-- |
Vermont |
5 |
5 |
4 |
5.75 |
9.50 |
REGIONAL TOTS. & WEIGHTED AVG.*
197
210
106
7.43
7.61
+2.47.
WESTERN REGION
Illinois |
5 |
5 |
2 |
3.50 |
4.50 |
Indiana |
10 |
14 |
2 |
12.00 |
13.00 |
Iowa |
10 |
13 |
4 |
1.50 |
3.50 |
Kentucky |
10 |
0 |
0 |
-- |
-- |
Michigan |
121 |
135 |
17 |
4.71 |
5.59 |
Minnesota |
23 |
14 |
9 |
5.00 |
3.67 |
Ohio |
10 |
8 |
7 |
4.29 |
4.00 |
Ontario |
2 |
0 |
0 |
-- |
-- |
West Virginia |
62 |
51 |
30 |
0.83 |
0.80 |
Wisconsin |
16 |
16 |
11 |
5.00 |
5.09 |
REGIONAL TOTS. & WEIGHTED AVG.* |
256 |
82 |
3.82 |
3.80 |
-0.5% |
NORTH AMERICAN TOTS, & WEIGHTED AVG.* ^^^ |
466 |
188 |
6.01 |
6.11 |
+1.7% |
* Weighted indexes are obtained by multiplying woodcock heard per comparable route with a factor based on land area represented by at least 10 routes or where one comparable route represented 2,100 square miles or less.
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Table 3. --Total number of wings received from the last three woodcock
wing-collection surveys
State or Province of harvest
Hunting Season
1963 |
1964 |
1965 |
0 |
0 |
6 |
422 |
419 |
539 |
0 |
0 |
17 |
0 |
0 |
5 |
0 |
0 |
2 |
61 |
56 |
35 |
3 |
0 |
2 |
372 |
188 |
137 |
1,802 |
2,852 |
2,116 |
14 |
3 |
30 |
514 |
566 |
454 |
1,796 |
1,684 |
1,184 |
545 |
431 |
237 |
0 |
0 |
5 |
1 |
2 |
3 |
1,065 |
660 |
446 |
370 |
693 |
745 |
778 |
795 |
823 |
874 |
1,654 |
1,602 |
0 |
0 |
19 |
75 |
184 |
154 |
159 |
241 |
214 |
837 |
1,053 |
669 |
750 |
1,430 |
847 |
459 |
251 |
93 |
66 |
59 |
41 |
0 |
0 |
8 |
0 |
0 |
5 |
0 |
0 |
2 |
99 |
311 |
310 |
0 |
3 |
3 |
140 |
315 |
381 |
1,443 |
1,202 |
803 |
0 |
6 |
10 |
Arkansas
Connecticut
Florida
Georgia
Illinois
Indiana
Kentucky
Louisiana
Maine
Maryland
Massachusetts
Michigan
Minnesota
Mississippi
Missouri
New Brunswick
New Hampshire
New Jersey
New York
North Carolina
Nova Scotia
Ohio
Ontario
Pennsylvania
Quebec
Rhode Island
South Carolina
Tennessee
Texas
Vermont
Virginia
West Virginia
Wisconsin
Unknown Areas
TOTAL WINGS HARVEST AREAS
12,645 (23)
15,058 (23)
11,947 (33)
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■12-
RELA.TION BETWEEN MALE COURTSHIP ACTIVITIES AND NESTING OF AMERICAN WOODCOCK
Aelred D. Geis Assistant Director Migratory Bird Populations Station Laurel, Maryland
Counts made on the annual breeding population survey of woodcock depend on the conspicuous behavior of males in their "courtship performance. " Male singing-ground activities begin prior to and during northern migration each spring and continue beyond the nesting period. Studies by Blankenship (1957), Goudy (1960), and Duke (1966) indicate that the time of nesting depends on whether the spring season is early or late, which also supports Mendall and Aldous ' (1943) view that hatching dates are directly correlated with weather conditions. It is necessary to time the singing-ground survey so that it starts after migrants have left an area in order to obtain an unbiased measure of the resident woodcock population.
Recently, there has been concern about the accuracy of the singing-ground survey in the southern portions of the woodcock's breeding range. Some States have even discontinued their coop- eration in the survey since they have felt the Bureau's suggested "time interval" for conducting singing-ground routes was too late to hear breeding males perform. The basis for this decision was the observation that many young birds were known to have hatched before the prescribed survey period. Some biologists have assumed that this presents a problem because experience with other species has demonstrated that male courtship performances either cease or are much reduced following the nesting period.
In Maryland, spring migration is judged to be complete by April 10, and the survey is conducted between this date and April 30. During the spring of 1966, a study area in the Piedmont Section near Clarksville, Maryland, was visited repeat- edly to observe the duration of the courtship performance and its relation to associated nesting activities» On this area,
•13-
four to five males were regularly observed engaging in court- ship activities through May 26, almost a month after the end of the singing-ground survey period. The "spring season" was late in 1966, probably causing an abnormally prolonged court- ship period. On May 7th, two different woodcock broods were found which were already capable of flight and appeared nearly full grown. This means the chicks had to have hatched about April 20th, at least 35 days prior to the cessation of "singing' male activity. This indicates that the woodcock breeding pop- ulation survey provides an index to the number of "singing" males long after the nesting period has been completed.
-14-
TRENDS IN THE CONTINENTAL WOODCOCK HARVEST
William H. Goudy
Research Biologist
Migratory Bird Populations Station
Laurel, Maryland
Analysis of various Bureau, State, and Provincial kill surveys indicates that more than a million woodcock were har- vested in North America during the 1965 hunting season compared to an estimated kill of 300,000 eleven years ago. While the bulk of the U.S. harvest still occurs in the Northeastern and Lake States, the kill of woodcock in the Southeastern and Gulf States is also increasing. Following this discussion are sep- arate reports of harvest trends and hunter interest in Maine, Pennsylvania, and Tennessee.
Hunter Success Index - A systematic method of appraising trends in the woodcock harvest has been attempted by determining the average number of wings returned by identical cooperators participating in the wing-collection survey for 2 consecutive years (table 7). Despite variations in woodcock shooting success among States each year, there was little change in the cooperator's average daily bag in 1963 and 1964 (Goudy and Martin 1966); but in 1965, their daily kill decreased almost 9 percent. The aver- age number of wings submitted per season by these same cooperators, meanwhile, was larger in 1964 than in 1963 and resulted from more trips afield (Goudy and Martin 1966). In 1965, it appears as if the 4 percent decrease in total number of wings received from comparable hunters may have been due to woodcock not being as available in some areas as they were during the previous fall. A drop in daily and seasonal success by comparable hunters could be due to an increase in hunting pressure as well as a decrease in woodcock availability. However, since the woodcock kill by these hunters is relatively constant, the continuing "spiral" in the continental woodcock harvest has to be due pri- marily to an increase in the number of hunters participating in this form of recreation.
■15-
Waterfowl Questionnaire Index - Beginning in 1964, the Bureau's Waterfowl Kill Survey (a mail questionnaire to a sample of "duck stamp" purchasers) has included a question regarding the hunting of other migratory birds including woodcock. Analysis of 1964 and 1965 data has provided some insight into the annual magnitude and distribution of the woodcock harvest in the States that do not have kill surveys or do not request woodcock hunting information from their small-game hunters. It should be remembered that these data are based on information obtained from waterfowl hunters. The magnitude of woodcock hunt- ing by non-duck stamp purchasers is not known in most States; therefore, these statistics provide only an indication to the hunting recreation provided by these migratory upland game birds. Listed below is the mean kill of woodcock in 1964 and 1965 by active adult "duck stamp" purchasers:
Michigan
Louisiana
Wisconsin
New York
Pennsylvania
Maine
Massachusetts
Ohio
Connecticut
68,000 50,000 49,000 35,000 23,000 22,000 21,000 13,000 12,000
New Jersey |
= |
11,000 |
Minnesota |
= |
8,000 |
New Hampshire |
= |
8,000 |
North Carolina |
= |
6,000 |
South Carolina |
= |
6,000 |
Texas |
= |
5,000 |
Mississippi |
= |
5,000 |
16 Others |
= |
38,000 |
TOTAL |
= |
380,000 |
There are several significant items to discuss in reference to the above table. First, on the basis of reliable State-conducted kill surveys, this waterfowl-woodcock index may be a fairly good indicator of the relative woodcock harvest among States. For instance, Michigan ranks first in the annual total woodcock har- vest with a mean kill of about 165,000 during the 1964 and 1965 seasons. Wisconsin and New York also are high in this survey and their own mail questionnaires in recent years have indicated annual harvests of over 100,000. The big surprise in this sur- vey is the high ranking Louisiana obtained. This suggests they are harvesting a minimum of 50,000 birds annually which makes them a very important harvest area as well as being "the" wintering concentration site for woodcock.
■16-
A "crude" estimate of the total U.S. woodcock harvest can be obtained by expanding these data on the basis of known wood- cock kill and/or number of woodcock hunters in States that have reliable kill surveys. This expansion suggests that about 425,000 U.S. hunters harvested somewhere in the neighborhood of 900,000 woodcock during the 1965 hunting season (fig. 3). It is not our intent to imply that we are satisfied with this tech- nique or the results obtained. However, until a sampling frame is available that will permit contacting a representative sample of woodc»ck hunters (such as the "duck stamp" provides for waterfov/1 hunters), estimates of total woodcock harvest and number of hunters will continue to be quite unreliable. The information ir figure 3 is presented primarily to stress the increasing recreational opportunity woodcock are now affording in contrast with their popularity a decade ago. It is unfor- tunate that inadequate kill statistics make it inappropriate to present this information in greater detail.
-17-
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-18-
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^ |
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||
HARVEST |
HUNTERS |
||
^ |
360,000 |
160 |
,000 |
•fi*j>:i*. |
340,000 |
140 |
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200,000 |
125 |
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Figure 3.--1965 woodcock harvest and hunter interest by regions of the United States as indicated by State kill surveys and water- fowl hunter questionnaires.
-19-
TRENDS IN WOODCOCK HARVESTS AND HUNTER INTEREST IN MAINE
J. William Peppard
Regional Game Biologist
Department of Inland Fisheries and Game
Orono, Maine
A gradual increase in the number of woodcock hunters has resulted in a higher harvest of woodcock in Maine during recent years. Field investigations and our Game Kill Questionnaire confirm this. As may be seen in table 8, the woodcock harvest has increased from less than 11,000 in 1951 to almost 47,000 during the 1965 season. Since 1960, estimates of both the number of hunters and the annual kill have been calculated from mail questionnaires. Both estimates have increased quite constantly during recent years. Also, the survey has undoubtedly been more consistent from 1960 until the
present time because the same person John D. Gill
has been responsible for its operation. Gill also reports that, during these years, estimated numbers of deer and waterfowl hunters have not shown this increase in hunting effort.
■20-
Table 8. --Woodcock kill and hunter participation in Maine
Hunting |
NUMBER OF HUNTERS |
Estimated |
||
Season |
Resident |
Non-Resident |
Total |
Total Kill |
1951 |
Unknown |
Unknown |
Unknown |
10,900 |
1952 |
19,100 |
|||
1953 |
25,000 |
|||
1954 |
20,000 |
|||
1955 |
23,000 |
|||
1956 |
22,000 |
|||
1957 |
21,000 |
|||
1958 |
18,000 |
|||
1959 |
28,500 |
|||
1960 |
8,200 |
930 |
9,130 |
33,300 |
1961 |
7,200 |
1,100 |
8,300 |
32,100 |
1962 |
8,090 |
1,120 |
9,210 |
38,100 |
1963 |
8,100 |
825 |
8,925 |
31,000* |
1964 |
9,200 |
1,200 |
10,400 |
43,800 |
1965 |
9,270 |
1,200 |
10,470 |
46,700 |
* Even though bag limits and season length were increased, forest fire hazards restricted hunting in many primary harvest areas during 10 days in late October.
-21-
resume' OF 1965 's WOODCOCK HUNTING SURVEY IN PENNSYLVANIA
Stephen A. Liscinsky Biologist Pennsylvania Game Commission State College, Pennsylvania
In 1964, the Pennsylvania Game Commission initiated a pilot study of grouse and woodcock hunting. This investigation was designed to provide information that would serve as a basis for measuring annual changes in shooting opportunities. The results of . this initial survey were sufficiently rewarding to warrant continuation of the study.
Just prior to the 1965 small game season, 320 individuals who hunted grouse or woodcock were contacted by questionnaire. Approximately 60 percent of them responded by submitting a detailed report of their trips afield. This account constitutes an analysis of these records.
After the first few days of the woodcock season (which opened in mid-October, the same day as grouse season) most of the "cooperators" switched their efforts to hunting grouse. Nevertheless, a compilation of the reports shows that consider- able time was exerted in hunting primarily for woodcock.
During 816 hours of hunting, 1,417 woodcock were flushed, 768 were shot at, and 421 killed. This constitutes 1.73 flushes per hour, 54 percent shot at, and 55 percent of the birds shot at were bagged.
Note, — This article was condensed from an article published in the September 1966 issue of the Pennsylvania Game News.
■22-
Flushing rates varied from place to place and as the season progressed. Flushes per hour, by region were: Central - 2.42, Northeast - 1.41, and Northwest - 1.20. The Statewide flush- ing rates by weeks of the season (first to fourth), were: 1.88, 1.88, 1.60, and 1. 18.
Despite their playing "second fiddle" to the wild turkey and ring-necked pheasant in Pennsylvania, woodcock and grouse continue to afford the rugged individualist many hours of enjoyable recreation.
•23-
TENNESSEE'S WOODCOCK INVESTIGATIONS - 1966
Eugene Legler, Jr. Leader, Wildlife Investigations Project Game and Fish Commission Nashville, Tennessee
In an effort to aid in the Bureau of Sport Fisheries and Wildlife's Woodcock Productivity Study, Tennessee quail hunters were asked to submit wings from any woodcock they might shoot during the 1966 hunting season. Hie hunters contacted were participating in the Commission's annual quail wing-collection survey and they responded by submitting a total of 4,835 quail and 57 woodcock wings. Sixteen wings were obtained from other sources resulting in 73 woodcock wings from 35 different Tennessee hunters. Age and sex categories determined from these wings follow:
Adult Adult Immature Immature Age Total Male Female Male Female Unknown Wings
22 16 15 12 8 73
The resulting productivity index ratio of 1.69 immatures per adult female is quite realistic even though the sample size is small. Last year's (1965) continental unweighted mean age ratio, from almost 12,000 woodcock wings examined by the Bureau, was 1.60.
Distribution of the woodcock kill in this sample shows that none was obtained from the far eastern or western counties. More than half were shot in the middle counties; with the plateau counties of Cumberland and Bledsoe also ranking high.
The 1966-67 woodcock season in Tennessee ran from November 21 through January 9, and 75 percent of the wings submitted were obtained during the first 7 days of the season. Only four cooperators shot woodcock on more than one day, and even though the average season harvest was just over 2 birds per hunter, one hunter achieved the daily bag limit of 5.
■24-
Although woodcock are not considered important game birds in Tennessee, it is quite likely that about 10,000 are har- vested annually by hunters primarily in pursuit of rabbits, quail, and ruffed grouse.
■25-
A SUMMARY OF WOODCOCK HEN AND CHICK BANDING IN MICHIGAN
George A. Ammann Game Ornithologist Department of Conservation Lansing, Michigan
Woodcock hens and chicks are being banded in Michigan to assist in determining whether there are homogeneous population units within the breeding range of this species (fig. 4). Ihe primary objectives of this program are to determine harvest rates of woodcock produced in Michigan and to relate these production areas with their related harvest areas.
The capture of woodcock hens and their chicks also pro- vides extremely valuable supplemental information on nest and brood densities, habitat preferences, hatching dates, brood size, movements, and dispersal.
Non-technical help has been solicited to band woodcock the past two springs. Although relatively few woodcock have been banded to date, judging from the enthusiasm shown, the program shows great promise. A total of 270 woodcock (24 adult hens and 246 chicks) was banded during 1965 and 1966 compared to an average of 43 during each of the previous 4 springs. The most successful, individual banders for the past 2 years have been:
Andy Ammann 73
Tom Prawdzik 58
Walt Palmer 33
Frank Kargol 31
Al McLain 22
Jack & Bill Wicksall 12
Al Schrader 10
Art Fleetwood 9
Charlie Cook 7
5 Others 15
■26-
Figure 4. --Michigan Game Biologist Dr. G. A. Amraann securing band on a woodcock chick (photo courtesy Michigan Department of Conservation — Oscar Warbach photo- grapher.
■27-
WOODCOCK SUMMER BANDING OPERATIONS AT THE MOOSEHORN NATIONAL WILDLIFE REFUGE, MAINE
Eldon R. Clark Wildlife Management Biologist Moosehorn National Wildlife Refuge Calais, Maine
In 1962, Bureau Biologist Fant Martin demonstrated that significant numbers of woodcock could be caught and banded at Moosehorn National Wildlife Refuge during the summer months using mist nets, spot-lights, and ground traps (Martin and Clark 1964). The success of this experimental phase led to the initiation of an intensive trapping and banding program in the summer of 1963 which has continued through the summers of 1964, 1965, and 1966.
Recoveries from woodcock bandings provide answers to questions on mortality rates, distribution and magnitude of the harvest, effects of regulations on recovery rates, and the like. For this study, it was also decided to see whether catch data could be used to indicate annual changes in reproductive success; to estimate the summer population on the Refuge; to evaluate summer use of various habitat types ; and to determine summer movements and home range. In addition, we continually evaluate the three woodcock capturing techniques to increase their efficiency. The following paragraphs summarize the woodcock catch during the past 4 years and briefly discuss some of the factors responsible.
The number of woodcock handled in 1966 was close to that of 1964 and 1965, the most productive years of the study. Following is a summary of the catch during the 4 years :
Year |
New Birds |
Returns |
Repeats |
Tots |
il Birds Handled |
1963 |
518 |
26 |
185 |
729 |
|
1964 |
450 |
33 |
252 |
735 |
|
1965 |
285 |
50 |
241 |
576 |
|
1966 |
434 |
34 |
255 |
723 |
|
TOTAL |
1,687 |
143 |
933 |
2,763 |
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Ground trapping success has held up well (fig. 5). The number of woodcock captured in traps increased in 1966 as it has each year. However, trapping was continued, on a reduced scale, to a later date than in 1964 and 1965.
Mist-netting success improved over 1965, but was lower than in 1963 and 1964 (fig. 6). September rainfall was near normal and usage of night-feeding areas increased.
While there were very few nights when conditions were favorable for night-lighting in 1966, catches on those nights were substantially greater than in 1965. Following is a summary of captures by the three methods over the 4-year period :
Year |
Trapping |
Netting |
Lighting |
Total |
1963 |
277 |
314 |
138 |
729 |
1964 |
362 |
209 |
164 |
735 |
1965 |
378 |
141 |
57 |
576 |
1966 |
395 |
183 |
145 |
723 |
TOTAL
1,412
847
504
2,763
All data from the 4 years of banding have been recorded on IBM punch cards at the Migratory Bird Populations Station. These data have been transferred to tape and the cards moved to the University of Maine computer center for tabulating and analysis. Migratory Bird Populations Station biologists will assist in analyses of population dynamics phases and a series of reports will be published beginning in 1967.
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Figure 5. --Netting is attached to top of woodcock ground trap
by Student Assistant Patrick Corr and Refuge Biologist Eldon Clark. Wire leads (foreground) extends to another cell of trap. At most trap sites on the Moosehorn National Wildlife Refuge, cover was much heavier (photo by Moosehorn National Wildlife Refuge).
;;s'^<«.tv:
Figure 6. --Students examine a woodcock's wing to determine its sex and age during mist-netting operation. Student assistant Kenneth Lewis (right) will record data (photo by Moosehorn National Wildlife Refuge).
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WOODCOCK BANDING STUDIES IN WEST VIRGINIA'S CANAAN VALLEY
Robert C. Kletzly and Joe Rief fenberger
Game Biologists
West Virginia Department of Natural Resources
Davis, West Virginia
During the past 2 years, the authors have been engaged in a woodcock banding program in Canaan Valley, Tucker County, West Virginia (fig. 1). The primary purpose of this program has been to develop effective methods of capturing woodcock so that effects of hunting mortality on the local Canaan Valley woodcock population can be measured. Three hundred and ninety-eight woodcock have been banded (496 handled) during this period through the use of mist nets, ground traps, and night-lighting techniques. Following is a summary of the catch during the past 2 years :
Total Year New Birds Returns Repeats Birds Handled
1965 101 0 4 105
1966 297 8 86 391
TOTAL 398 8 90 496
Considerable effort has been made to locate woodcock con- centrations in both diurnal and nocturnal covers. When a site has been found one or more of the three capture techniques is
Note. — This article is a contribution of Federal Aid in Wildlife Restoration Program, West Virginia Project W-37-R.
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used. Success of the various techniques varies with the habi- tat and climatic conditions present- Following is a summary of captures by the three methods for the past 2 years :
Year
1965 1966
TOTAL
Trapping
19 106
125
Netting
84 60
144
Lighting
2 225
227
Total Birds Handled
105 391
496
It is quite apparent that success is also dependent upon the experience of the investigators. In 1967, more emphasis will be placed on capturing "singing" males and the associated early summer residents of the Valley.
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WOODCOCK NIGHT- LIGHTING TECHNIQUES AND EQUIPMENT
Joe Rieffenberger and Robert C Kletzly Game Biologists West Virginia Department of Natural Resources Davis, West Virginia
During the summer of 1966, the authors were engaged in a woodcock banding study in the Canaan Valley of West Virginia. Night-lighting techniques presently used in Maine (Clark 1966) and Louisiana (Glasgow 1958) proved to be fruitless in this area because the headlamps were too dim to locate and/or "down" flushed woodcock.
The search for a better source of light culminated in the use of a Honda motorcycle battery. A 12-volt, wet-cell battery, weighing about 7 pounds, was rigged with a shoulder strap, an on-off switch, 3 feet of lamp cord, and a sealed beam spotlamp. Since this was a wet-cell battery, the air vent tube was looped to lessen the danger of acid spillage. The battery shown in figure 7 was used a total of 146 hours with daily trickle recharging. Weight and cost of the lamp were minimized by attaching a handle of heavy, insulated copper wire directly to the sealed beam unit, the back of which was painted black.
The net (fig. 7) is a little over 3 feet in diameter. One-inch mesh netting covers this with a bag depth of 4 inches (the object is to pin the bird to the ground). The 6-foot handle has a wooden, finger- fitting grip taped about 1 foot from the end. This allows the operator to tell which way the net is facing without having to take his eyes off the quarry. The hoop and handle are painted a dull black and the netting is dyed a dark color to reduce light reflection.
Note. — This article is a contribution of Federal Aid in Wildlife Restoration Program, West Virginia Project W-37-R.
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While walking across a woodcock feeding field (usually a pasture), the operator casts the light back and forth, cover- ing a distance of about 20 yards ahead and to both sides. This distance is increased in heavily grazed sites and reduced to a few feet in areas with heavier ground cover.
After locating (spotting) a woodcock, the approach is made directly and quietly. Care must be taken not to flush additional, unobserved woodcock during the approach as their flight may alarm the individual being pursued. The hand holding the light is extended to prevent illumination of the operator's feet. The net is held vertically during the approach. When close enough, the net is slowly lowered to about belt height and then dropped. Quick action is necessary to pin the bird by hand and prevent injury.
Often a woodcock is flushed without having been seen beforehand. When this occurs, the spotlight is immediately directed at the bird. If the bird circles, the spotter must be careful not to flash the light on any part of himself or the net while tracking it. Silence is "golden" at this time. When the bird is "knocked down," the approach is made as previously described.
During the summer and fall of 1966, a total of 363 manhours of effort resulted in the banding of 177 woodcock, the capture of 6 from previous season's activities, and 42 repeats of prior 1966 captures. An additional 7 birds were killed, mostly by swinging the net instead of letting it drop on the bird by gravity (6 of these mortalities occurred in the first 83 captures while the technique was still being mastered). In addition to these 225 woodcock, 31 snipe and 1 mourning dove were captured with this method.
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Fig. 7. --Night-lighting equipment used for capturing woodcock in West Virginia (photo by Edelene Wood).
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WOODCOCK BRIEFS FROM HERE 'N THERE
William H. Goudy Research Biologist Migratory Bird Populations Station Laurel, Maryland
Woodcock Singing-Ground Study Initiated in Massachusetts - The Massachusetts Cooperative Wildlife Research Unit will con- duct a woodcock singing-ground study during the spring of 1967. The study was conceived by Dr. William G. Sheldon and is designed to determine the incidence of breeding male turnover and replace- ment on singing grounds. Results of this graduate student research project should clarify population dynamics of the male segment of breeding woodcock populations and thereby provide information on the number of males represented by one occupied singing ground.
Randomization of the Woodcock Singing-Ground Survey Most routes used in the annual singing-ground survey since 1953 have been established in areas where woodcock were known to be present. Such routes have been altered and/or replaced from time to time as the habitat changed. Since routes are not uniformly distributed in all types of habitat, counts are not representative of woodcock population densities in the various States and Provinces. Furthermore, they may not properly reflect changes in relative numbers of breeding birds from one year to the next (Martin 1962, 1963, and 1964).
This spring (1967), randomly-distributed routes will be conducted in Michigan, West Virginia, Maryland, Delaware, and Pennsylvania. It is hoped that other States and Provinces throughout the woodcock's breeding range will have established randomly-selected routes before 1968. Such surveys would per- mit a statistically sound, annual assessment of relative densities and fluctuations in the continental population of breeding woodcock.
•36-
Woodcock Banding Study Completed in Michigan - Recoveries of banded woodcock provide information on population character- istics that cannot be obtained in any other way. During the past year, a Bureau-sponsored study to develop effective methods of trapping woodcock prior to the hunting season was completed in northern Michigan. Michigan State University graduate student Larry Gregg, with one field assistant, banded over 400 woodcock during his two summers of applied study. This is not only a very creditable accomplishment but also proved the feasibility of establishing a summer banding program in northern Michigan. His investigations indicate that minor habitat manipulations may attract and thereby concentrate woodcock into sites where they can be readily captured.
Woodcock Hunting Mortality Research in West Virginia - One of the most important phases of the woodcock research program dur- ing 1966 was the continuation of a population dynamics study by the West Virginia Department of Natural Resources in cooperation with the Bureau. Preliminary results indicate that mortality associated with hunting was approximately 25 percent in the Canaan Valley study area. These data also suggest that there may be differential vulnerability by age and/or sex associated with relatively intense hunting pressure. The size of the Canaan Valley's woodcock population was calculated using kill estimates from bag checks and kill rate estimates from band recoveries. These calculations placed the study area's woodcock population in 1965 and 1966 at about 1,500 resident birds.
Initial Woodcock Seminar Held in Minnesota - A woodcock seminar sponsored jointly by the University of Minnesota and the Bureau of Sport Fisheries and Wildlife was held at the Long Lake Conservation Center near McGregor, Minnesota, during October 1966. Twenty- five participants representing Canadian Provincial, Federal and State agencies, private conservation organizations and univer- sities, and several interested individuals gave the meeting a broad base.
The objectives of the seminar were three- fold:
1. To review the American Woodcock Research and Management Jgrogram report prepared in January 1966.
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2. To further develop the research project reconmenda- tions contained in the above report.
3. To explore in more detail the problems of funding woodcock research and management proposals at the National, State, and university level.
Minutes of this meeting may be obtained by writing to the Section of Migratory Upland Game Bird Studies, Migratory Bird Populations Station, Laurel, Maryland 20810.
Woodcock Seminar Planned for 1968
The second seminar
on American woodcock research and management activities is tentatively scheduled for January 1968 in Louisiana. The exact location(s) and dates have not yet been established but should be announced in September. It is planned that much of this seminar will be devoted to night banding operations and field investigations of primary woodcock wintering habitat. The sponsors (Louisiana Wild Life and Fisheries Commission, Louisiana State University, and the Bureau of Sport Fisheries and Wildlife) will forward invitations to representatives of Provincial, Federal, and State agencies, private conservation organizations, and universities. Interested individuals should contact the sponsoring organizations for further information.
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REFERENCES
BLA.NKENSHIP, L. H.
1957. Investigations of the American woodcock in Michigan. Michigan Conservation Department, Game Division, Lansing. Report 2123. 217p.
CLARK, E. R.
1966. Woodcock capture techniques and population studies at Moosehorn National Wildlife Refuge. Proceedings of the N. E. Section of the Wildlife
Society, Boston, Massachusetts January 16-19, 1966.
8p.
DUKE, G. E.
1966. Reliability of censuses of sinj^ing male woodcocks. Journal of Wildlife Management. Vol. 30, No. 4, P-697-707.
GLASGOW, L. L.
1958. Contributions to the knowledge of the American woodcock Philohela minor (Gmelin), on the wintering range in Louisiana. Unpublished Ph.D. Thesis, Agriculture and Mechanical College of Texas. 159p.
GOUDY, W. H.
1960. Factors affecting woodcock spring population indexes in southern Michigan. Michigan Conservation Department, Game Division, Lansing. Report 2281. 44p.
and F. W. MARTIN.
1966. Woodcock status report, 1965. Bureau of Sport
Fisheries and Wildlife, Special Scientific Report
Wildlife No. 92. 43p.
MARTIN, F. W.
1961. Woodcock status report, 1961. Bureau of Sport
Fisheries and Wildlife, Special Scientific Report
Wildlife No. 58. 29p.
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REFERENCES--Continued
1962. Woodcock status report, 1962. Bureau of Sport
Fisheries and Wildlife, Special Scientific Report
Wildlife No. 69. 36p.
1963. Woodcock status report, 1963. Bureau of Sport
Fisheries and Wildlife, Special Scientific Report
Wildlife No. 76. 43p.
1964. Woodcock status report, 1964. Bureau of Sport
Fisheries and Wildlife, Special Scientific Report
Wildlife No. 88. 43p.
and E. R. CIARK.
1964. Summer bandings of woodcock, 1962-1963. Administrative Report No. 43. Migratory Bird Populations Station, U.S. Department of the Interior. 9p.
MENDALL, H. L., and C. M. ALDOUS.
1943. The ecology and management of the American woodcock. Maine Cooperative Wildlife Research Unit, Orono. 201p.
ROBBINS, C. S.
1960. Woodcock status report, 1960. Bureau of Sport
Fisheries and Wildlife, Special Scientific Report
Wildlife No. 50. 26p.
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ft U S GOVERNMENT PRINTING OFFICE 1967 O — 265-487
The Department of the Interior, created in 1849, is a Department of Conservation, concerned with management, conservation, and develop- ment of the Nation's water, wildlife, fish, mineral, forest, and park and recreational resources. It has major responsibilities also for Indian and Territorial affairs.
As America's principal conservation agency, the Department works to assure that nonrenewable resources are developed and used wisely, that park and recreational resources are conserved for the future, and that renewable resources make their full contribution to the progress, pros- perity, and security of the United States, now and in the future.
UNITED STATES
DEPARTMENT OF THE INTERIOR
FISH AND WILDLIFE SERVICE
BUREAU OF SPORT FISHERIES AND WILDLIFE
WASHINGTON. D. C. 20240
POSTAGE AND FEES PAID .S. DEPARTMENT OF THE INTERIOR