Reprinted with permission:
RH : Recorded Alarm calls for goose dispersal
Efficacy of Recorded Alarm and Alert Calls for Canada Goose Dispersal
LUKE A. STRENG , Marysville OH 43040, USA
PHILIP C. WHITFORD, Capital University Biology Department, Columbus, OH
43209, USA
Abstract: Effectiveness of replay of alarm and alert calls at
dispersing giant Canada geese, Branta canadensis maxima, was tested on
10.0 hectares of grass seed and herbicide treatment test growth plots which
experienced daily usage by 2-400 resident geese/goslings. Tests 5 June- 25 July
2001 used 2 modified Bird X-Peller systems provided by Bird-X Inc, 300 N.
Elizabeth, Chicago IL 60607, which played naturally recorded alarm and alert
calls of the species daily at randomized 5-10 minute intervals dawn to dusk.
Geese were flightless via molt of primaries, and many goslings (< 3 weeks of
age) were present when call playback was initiated. Initial response to call
playback was complete absence of geese from 15-16 hec for 4 days. Geese could
not escape the playback, and habituation appeared after roughly 1350 call
repetitions compressed over 5-7 days. Geese continued to avoid the most exposed
test plots at significant levels three weeks after the call units were turned
off. Initial response suggests these units should show efficacy at dispersing
flighted geese at sites where they can readily escape the audible range of the
Bird-X-Pellers.
INTRODUCTION
The Giant Canada Goose, Branta canadensis maxima, population has
skyrocketed in the past 20 years. Once thought extinct, they have rapidly
repopulated much of their historic range and expanded into new areas via
translocation programs of the 1970’s and 1980’s, becoming a nuisance in many
areas of the United States, Canada and New Zealand. Giant Canada geese are
commonly found in areas having mowed grass associated with a body of water, thus
providing both foraging sites and safety (Conover 1991). Given a feeding
preference for short, highly fertilized grass of high nutritional content it is
clear why giant Canada geese have infiltrated suburban and city environs with
their many lakes and ponds, business parks, golf courses, parks and homes all of
which fertilize and mow heavily for aesthetic reasons.
Homeowners, corporations, golf courses and farmers have sought ways to deter
geese from inhabiting their property. Golf courses have used Border Collies,
firecrackers, guns (blanks), decoys, balloons, wires, and general harassment
(Conover 1991). Farmers have tried propane exploders, scare flags, shell
crackers, and hunters, all of which have proven unsuccessful at keeping geese
from crops in the long term (Conover 1991). Rapid habituation to lasers used for
dispersal on confined geese was recently reported (Blackwell, et al 2002). Tests
of early audio systems in agricultural fields deterred geese in some areas,
while no effect was seen in others, and geese habituated to propane exploders as
well (Conover 1991). Reports indicate repeated presentation of taped distress
calls to geese led to decline in response (Aubin 1990) or failure to respond (Aquilera
1991), and goose return once playback terminated (Mott and Timbrook 1988).
Geese have species-specific alert and alarm calls. Alert calls warn of danger
at a distance (Boudreau 1968). Giant Canada goose alert calls, phonetically “Hrr-urr-uh,”
used call forms H and I, in frequency ranges from 450cps, base frequency, to
1450 cps for 1st harmonics and 0.3 - 0.64 sec in duration varying with sex, age,
and intensity of the alert reaction (Whitford 1987). Alert calls may reflect two
levels of intensity: mild apprehension, with no need for immediate response, at
intervals of >5 sec between successive calls; and, a more imperative warning
of perceived impending danger < 0.3 sec between multiple calls commonly
leading to “orderly mass movement” of geese from the area (Whitford 1987,
1998). Low intensity alert calls cause nearby geese to raise their heads, extend
the neck vertically and look in the direction the caller faces, “an alert
posture,” as it is described by Balham (1954) and modified by Klopman (1958).
If danger is not imminent, and calls cease, geese often resume eating (Whitford
1987).
“Alarm calls,” one of the least used calls of the species, are comprised
of a mixed series of call forms. All Canada geese present normally take flight,
if possible, or seek the relative safety of water when alarm calls are given (Whitford
1987). Alarm calls used 0.20 – 0.23 sec duration “A” calls at 0.55 sec
intervals mixed with “J” calls of 0.37 sec duration and 0.42 sec intervals
for males, and female “E” calls of 0.1 - 0.13 sec duration and
undeterminable interval in the only series sonographed (Whitford 1987).
Most avian species have auditory discrimination ability to as little as 20 Hz
at 2 kHz (Dooling 1982). While alarm and alert calls are given at frequency
ranges preferentially responded to by their own species, auditory discrimination
may permit geese to identify specific calls as being from one individual, or
recorded source. Thus, they may learn to ignore it (habituate) or respond to it
based on past experience, using call form, frequency, duration and interval as
discrimination parameters and dominance status of callers (Whitford 1987).
This study was designed to test efficacy of Canada goose alert and alarm
calls described above for goose dispersal using a timer controlled,
microchip-based audio system for playback. We focused on defining: 1) how
discriminating and long lasting was the memory of Giant Canada geese for
specific alert and alarm calls; 2) how quickly habituation occurred to repeated
exposure of free ranging flightless geese to call playback while in preferred
environments and unable to leave the audible range of the playback units due to
gosling brooding requirements; and, 3) how long habituation lasts if the call
source is removed and reintroduced at a later time.
STUDY AREA AND METHODS
Alarm and alert calls were played back using two “Super Bird X-Peller”
audio systems (Super Bird X-Pellers supplied by Bird-X, Inc., of Chicago, IL.,
and specially modified to playback 12 sec sequences of random alarm and/or alert
calls recorded on microchips within the unit.) Calls were played by both units
at 5-10 minute intervals using random time functions built into the units and
with call playback from dawn to dusk by use photovoltaic control cells. Giant
Canada Goose alarm and alert calls used were recorded under natural conditions
by the author.
To test habituation response in the field we sought isolated, preferred giant
Canada goose habitat, with ponds, well-fertilized grass, and minimal
disturbance. The area found was a corporate site of 300+ hec, but we must honor
the request of the sponsoring company in that we not disclose their name and
precise location. Located in Central Ohio, the site had three ponds of .2 - .5
hec adjacent to 10.0 hec of grass test growth plots comprised of varied species
which were heavily fertilized and cut weekly to the short length that geese
prefer. The remainder of the property was lawns with widely scattered trees kept
in park-like condition around the office complexes. Protected from hunting and
disturbance, geese had resided there for 20 years with little fear of humans.
While tolerant of the geese, the corporation that owned the site found they
confused research by continually eating grasses of test growth plots, adding
their own ”special brand” of fertilizer, and altering species composition of
test plots via selective feeding activities. We hoped to reduce some of these
negative effects by using alarm call playback to deter geese from feeding on the
test plots.
Primary test areas consisted of three 3.3 hec test growth plots each seeded
with different species of grasses; bent grass (Poacene agrostis);
Kentucky bluegrass (Poa pretensis); and a ryegrass (Lolium sp)/crab
grass (Digitaria sp) mixture. Test plots formed adjacent rectangles in an
east west line with a 0.4 hec pond 50 meters to the west of the bent grass plot
and a 0.2 hec pond and adjoining practice putting green (much loved by geese for
feeding) some 40 m south of the central bluegrass plot. From late March to early
June, before playback began, background data on time of use and goose numbers on
each plot was gathered using 2 hour split block format from 06:00 to 18:00 EST.
Each block was sampled once per week during this period and weather data,
temperature and rough categories of cloud cover (clear, partially cloudy,
overcast) and wind strength (calm, moderate, strong) were recorded to permit
evaluation whether they influenced goose use of test plots. Goose numbers/plot
were counted every five minutes. Sums of all geese present per hour were
recorded. Background data collection continued until 1 week after all known
nests had hatched. It provided baseline data and insight into feeding, resting
and daily post-nesting/brooding movement of geese on this site.
Post-nesting timing of this experiment was intentionally chosen knowing the
adult geese studied would have molted their flight feathers and thus could not
fly, and that there was little or no suitable brooding habitat for the goslings
away from the corporate property. This meant the geese had to remain within
audible distance of the Bird-X audio alarm/alert call systems. In this manner,
we could determine learning, memory and habitation rates to continual playback
conditions using free ranging geese.
On 5 June, as goose numbers on the plots stabilized following nesting, two
“Bird X-Peller” prototype audio systems were placed roughly 300 m apart; one
at the southeast corner of the central bluegrass plot, the other at the
northcentral section of the western bent grass plot. Before the units were
activated, they were left in place for 10 days, and data collection continued to
assure that goose response was to call playback and not a reaction to presence
of the speakers and post-mounted units.
The call systems were activated about 10:00 hours June 14th. Geese
were observed for the next two weeks to evaluate plot usage by geese with
alarm/alert calls playing at 5-10 minute intervals dawn to dusk. During the
first week following system activation goose counts were made hourly for all
time blocks to assist in determining when they first reappeared on the test
plots. First day data was supplemented by description of behavioral responses
and actions of geese during the first hours of playback. After two weeks the
units were turned off and remained off for three weeks to allow geese an
opportunity to recover from constant call playback. The units were then moved to
alter the directional source of the sound, turned on and the reaction of the
geese was recorded again. Observations continued until evidence of habituation
reappeared. Goose movement away from plots or absence during normal use hours
was considered indication of efficacy of alarm and alert calls in dispersing
geese from test plots. Goose presence upon the plots while calls were still
being played was considered evidence that habituation to the calls had occurred.
One-way ANOVA was used to determine whether significant changes in geese
counted/hour/plot occurred with call playback in three designated phases of the
study: 1- pretest phase (before call unit use); 2- playback phase; 3-
post-habituation playback phase. One-way ANOVA was also used with goose counts
on the various test plots to determine grass preferences, changes in weekly
usage and daily hours of goose usage of plots across the study phases, and at
various mean temperatures, cloud cover and wind strength per observation block.
RESULTS
Activation of the first X-Peller unit on June 14 was done while 125-130 adult
geese and 1-3 week old goslings were present on or adjacent to the bent grass
plot near the large western pond (within 150 m of call unit). Another 150-155
adult geese and goslings were present on the putting green and lawn 40-60 m
south of the bluegrass test plot. At the first call playback of the western unit
all geese and goslings within 150 m of the unit immediately began running toward
the pond. When calls stopped 12 seconds later they gradually slowed to a walk
with heads fully erect in alert posture and continued toward the pond while
looking about. They had just begun to relax 7 minutes later when the unit played
again and once more sent them running for water. Geese 300 m away at the putting
green, especially adults with goslings, raised their heads at each call of the
distant unit and stayed in alert postures, moving nervously, grouping goslings
together.
The second call unit, located about 125 m northeast of the putting green (300
m from the first) was activated twenty minutes after the first unit’s playback
began. At this additional stimulus, geese and goslings near the putting green
all first walked quickly into the pond and milled about in alert postures. After
two more sets of call playback from both units the geese exited the water and
walked away across open lawn to points >.3 Km from the units. Addition of a
second call unit’s alarm call playback distant from the first appeared to
increase overall agitation of geese and stimulated them to leave the area.
Within minutes of the second unit’s call playback there were no geese to be
seen on the test plots, ponds, or lawns of the adjacent corporate grounds,
leaving more than 35 hec completely cleared of geese. Those areas remained
completely clear of geese for 4 days after call units were activated. The large
area cleared indicates the X-Pellers worked over a much greater range than the 7
acres/unit the manufacturer had claimed in literature accompanying them.
First signs of habituation appeared late on the fifth day as a few geese
began returning to test plots to feed. Within 2 more days most remaining geese
returned to the test plots, apparently drawn by the sight of the other geese
feeding there, though statistically significant reduced use of test plot areas
distant from the safety of water remained evident. By the 8th or 9th day, unless
they were near the X-Pellers, most geese did little more than raise their heads
to alert postures when alarm call playback occurred. Reactivation of X-Peller
playback in the 8th week caused geese to temporarily resume alert postures, but
did not lead geese to leave the area.
Results of goose numbers observed on the test plots are divided into three
phases representing pre-sound system activation (phase 1) data; sound system
activated (phase 2) data; and post habituation tests after a three-week break
from call playback (phase 3). One-way ANOVA of average numbers of geese
observed/hour on each plot across the three phases of the study and indicated:
significantly fewer geese in phases 2 and 3 than in phase 1 on both the blue
grass and mixed grass plots, F (2,77) = 8.37, p<.05 and F (2,77) = 3.95,
p<.05, respectively; and, no significant difference across phases for the
Bent grass plot, F (2,77) =.2, N.S.
The Canada geese studied significantly preferred the bent grass test plot
over the other two grass forms, F (2, 237)= 15.25, p< .05, as indicated by
higher numbers of geese observed there during all observation periods. Average
numbers of geese observed on each plot for all phases/observations were 215.3,
48.3, and 24.6 for the bent grass, bluegrass and mixed plot, respectively.
Weekly goose numbers on each plot are reflected in Table 2. Weeks 1-3 represent
pre-call system use samples; weeks 4 and 5 represent weeks of X-Peller/call use;
and, week 8 was when the units were reactivated after being shut off for three
weeks. The data corresponds to number of geese observed per plot with all
observation periods per block being summed for the week. ANOVA’s indicated
that there was no significant change for the bent grass, F (5, 74) = 1.92, N.S.
and significant changes for the bluegrass and mixed plot, F (5,74) = 7.04,
p<.05 and F (5, 74) = 5.74, p<.05, respectively. A separate analysis of
the bent grass plot for week four alone would make the reduction in goose
numbers for the week following unit activation much more obvious since the
numbers dropped to zero for five days of that week.
Table 1- Average number of geese counted on test plots per hour in each phase
|
Phase 1 |
Phase 2 |
Phase 3 |
| Bent grass Plot |
241.7 |
202.9 |
168.3 |
| Bluegrass Plot |
89.49 |
4.6 |
24 |
| Mixed Plot |
51.82 |
0 |
0 |
Table 2- Average number of geese on the plots for the data collection weeks
of study
Pre-call playback periods Post call playback periods
|
Weeks
|
1 |
2 |
3 |
4* |
5 |
8 |
| Bent grass Plot |
9.7 |
393.1 |
255.9 |
73.3 |
332.5 |
168.3 |
| Bluegrass Plot |
18.8 |
79.9 |
149.3 |
3.6 |
5.6 |
24 |
| Mixed Plot |
8.2 |
13.4 |
121.4 |
0 |
0 |
0 |
*First week of alarm/alert call playback
Preferred goose use times for grass test plots based on one hour data
collection
system are reflected in Figure 1. No significant differences in goose
numbers/time were found for any grass type, but a trend was evident for greater
numbers on the bent grass between 11:00 and 13:00 hours.
Figure 1. Daily Patterns of Test Plot Use Prior to Call Playback.
When goose use of the test plots was correlated with wind strength and with
cloud cover difference was not significant for the heavily used bent grass
plots. Significant differences existed for both conditions for the bluegrass and
mixed grass plots as wind speed increased, F (2, 77) = 8.89, p<.05,
F(2,77)=3.01, p<.005 and as cloud cover increased F(2, 77) = 7.17, p<.05
and F(22, 77) = 3.70, p<.05, indicating geese were more likely to use open
test plots as wind speed and cloud cover increased.
ANOVA of temperature and number of geese observed on each grass test plot
indicated there was a significant inverse relationship between temperature and
the number of geese on the bluegrass plot: r (78) = -.384, p<.05, and for the
mixed grass plot r (78) = -.368, p<.05., but not for the bent grass.
DISCUSSION
Tests comparing goose use of the grass plots from weeks 1-3 (phase 1) and
weeks 4 and 5 (phase 2) showed that the sound system did in fact discourage
geese from feeding on the plot. During pre-call playback versus playback phases
of the study, the goose numbers dropped significantly on the bluegrass,
declining from 149.3 to 3.6 per hour on the bluegrass, as well as from 121.4 to
0 per hour for the mixed plot. The bent grass also showed a decrease (255.9 to
73.3) in mean numbers of geese feeding during the observed hours with the latter
figure reflecting geese returning at the end of the first week of call playback,
as well as absence of geese during the first five days of X-Peller use. The
decrease in geese on the bent grass plot would be significant if only goose
numbers from days 1-5 after implementation were to be used. Still these figures
don’t adequately show what the initial reaction was when the alarm/alert calls
were first played.
Soon after call playback was initiated by both call units, the entire goose
population fled from the area in alert postures. They couldn’t take flight
because they had molted their flight feathers, so they walked off keeping the
goslings close beside. In fact, beginning by the time the calls had been
repeated 4-5 times by each call unit, roughly 30 minutes after the first call
was played, not a single goose was seen near test plot areas for four full days.
On the fifth day after X-Peller activation, two geese entered the Bent Grass
plot. Thereafter more geese moved on to the Bent Grass plot to feed over the
course of several days and habituation was soon complete, so goose numbers rose
quickly in week 5. Goose numbers remained significantly below phase 1 numbers on
the Bluegrass and mixed grass plots even into the 5th week, probably indicating
that geese were reluctant to feed that far from the water while the call units
were functioning even once habituation had begun.
While the data indicate that the geese habituated rather quickly to the call
playback, it doesn’t mean the use of recorded alarm calls would be ineffectual
in other circumstances. By using flightless geese with goslings confined to a
test area where they could not escape from the continual 5-10 minute cycle of
playback of the alarm and alert calls by both units, played from dawn to dusk
daily, the study was able to define the maximum rate at which habituation could
occur. Since both goslings and adults needed high quality feed to support their
rapid growth and feather replacement respectively, and that feed was only
available on the test plots and putting green, geese had little option but to
approach the call units and learn to ignore them to gain food for themselves and
their young. If one considers the number of call playbacks heard per goose over
five days, at one call playback per 7.5 minutes, on average, for each of two
call units (18 alarm calls per hour) 15 hours per day, that amounts to roughly
1080 calls over four days, or 1350 calls over the 5 days before wholesale
habituation began to occur.
Geese which had the option of flying away to someplace out of hearing range
of the call units when they first broadcast alarm calls might well be expected
to delay habituation for months or longer if that many calls must be heard
before they cease to respond to them. As long as there are alternate areas that
the geese might use to meet daily needs, and which are out of hearing range of
the call units, they might well never return to the original site where call
units were in use.
Prior tests using playback of alarm calls recorded under conditions which
make them more likely to actually be true alarm calls rather than the
“distress calls” distributed by Cornell University as alarm calls, reported
that the calls were effective on flighted geese at Tennessee campgrounds and
continued to disperse geese for the full 6 weeks of testing (Mott and Timbrook
1988). Further tests of our recordings in field settings when all geese have
flight feathers to facilitate rapid escape from the playback area are planned to
define rates of habituation under those circumstances.
Rapid habituation in confined geese gives evidence of how quickly the giant
Canada goose may learn to recognize a specific call and to what limits it will
perceive a given call as being the same call when played repeatedly without
additional stimulus. The call used in this study was a single repeated copy of
an alarm call with no alteration in frequency or duration parameters. We are
currently modifying the call digitally to provide variation in frequency and
duration of call components, which should make it much more difficult for geese
to recognize and define as being from a single individual, since these
parameters are thought to form the basis for individual recognition of calls in
both individual and duetted call series of the species (Whitford 1996). This
modification may in turn increase efficacy and assist in delaying habituation in
future tests of the alarm call playback system.
Prior to this test it was not known whether this call’s playback would
initiate fixed action patterns of escape behavior within the geese or how long
it would require for them to discriminate and habituate to a taped alarm call.
The study has effectively answered how long habituation requires under
continuous daily exposure to a single copy of the alarm call. Call playback in
week 8 evidenced little response other than birds assuming alert postures and
grouping together. There was some movement away from the call sources, but not
the mass egress seen in the first use. Thus, the geese remembered the call and
retained the habituation response to it at least three weeks after if first
developed..
Observed preference for various grasses by the geese were largely expected
based on prior observation of feeding activity at the test site. There was a
strong preference for the Bent Grass, followed by the Blue Grass and last the
mixed grasses. Yet, this may have been influenced strongly by the presence of
the large pond and the safety water represents to flightless geese. The pond was
nearest to the Bent Grass, with the smaller pond being near the Blue Grass, and
the mixed grass plot farthest removed from any water. Preference for
palatability of Bent Grass may explain why the geese, after the alarm call
playback began, rapidly returned to eat the Bent Grass. Or, it may be that
proximity to the larger body of water, and therefore safety, caused geese to
feed preferentially on the Bent Grass plot as they habituated to the calls.
Since all grass test plots were kept short, highly fertilized and thus highly
nutritious, grass species should be assumed the basis for selection preference,
if water proximity is ignored. Geese select grass that is easier to digest and
yields more calories/gr and selection of bent grass may reflect this preference
(Conover 1991).
The peak time-periods of goose use of food plots showed that all three plots
evidenced higher goose numbers during the 11a.m. to 1 p.m. time period. This may
reflect preferred feeding times of the species, or more probably may reflect
that landscaping crews were on lunch break so mowing and other lawn maintaining
activities were at a daily minimum during these times. In prior study of the
species feeding tended to be episodic with heaviest feeding during early to
mid-morning, and again during midday and mid-afternoon time periods (Whitford
1987).
Data indicate that strong breezes didn’t deter geese from feeding and may
have actually led to an increased use of the mixed grass plot. Additionally,
goose numbers were observed to increase as cloud cover increased. Both increased
wind strength and cloud cover would help reduce heat absorption and keep birds
cool while feeding in open areas of test plots otherwise exposed to full sun. On
warm sunny days geese tend to seek shade during warmest hours and feed in the
open more in morning and afternoons (Whitford 1987). That theory is supported by
results of temperature/feeding correlation tests which indicated that a decrease
in temperature corresponded to an increase in geese on the bluegrass and mixed
grass plots. In any case, neither wind, temperature, or cloud cover appeared to
play a significant role in how the geese responded to alarm call playback.
An important aspect to remember about this study is that the geese were
flightless and accompanied by young goslings with no suitable brood rearing
habitat near the study site, other than the grass test plots. This is a major
factor in understanding that the geese could not get out of hearing range of the
calls and meet food needs of the goslings, adult females which had not fed for
four weeks while incubating nests, and molting adults all in need of extensive
feeding to gain/regain lost weight and provide protein for feather growth. This
is an important consideration because it implies that alarm call use when the
geese can leave the audible range should greatly delay habituation response.
Thus, the calls may prove useful for long term removal of geese from areas they
are not wanted if used solely on flighted geese.
MANANGEMENT IMPLICATIONS
Data collection in the three phases permitted before-and-after comparison of
goose use of the three plots with call playback and without. The first playback
phase evidenced clear response to alert and alarm calls, and defined for a
single specific call what constitutes a maximum habituation rate under continual
call playback condition. The third phase showed there was no significant change
from the second week of phase 2, meaning geese recalled the call playback as
non-threatening.
The implications of these tests provide some hope that companies, farmers and
communities that wished to remove geese from their lands may benefit from proper
limited use of call units broadcasting alarm and alert calls. Clearly, there is
evidence for giant Canada geese of memory of calls that have been habituated to
in the recent past. By finding that geese can habituate within five to seven
days and that they can remember to ignore that call, we are one step closer to
defining applications and limitations of audio playback of Alarm and alert calls
for goose dispersal. Results imply that alarm calls have greatest chance of long
term success during fall and winter months when geese are mobile and less likely
to experience repeated exposure to call playback. The next step in research will
be to try a similar test with a mobile flock unexposed to the call playback and
able to escape the playback area entirely to see if they also habituate, and how
long it takes under such circumstances. Such tests are being completed at
present and results should be available by mid-summer of 2002.
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