The breeding biology of the Snail Kite was studied in Florida from 1968-1977 and intermittently from 1978-1980. Breeding occurred every month, but not in the same year. Peak egg-laying occurred from February through April or generally about 81 d before the onset of the rainy season in mid- or late May. Courtship displays, copulation, and duration of copulation are described. Mean egg-laying interval was 2.2 d, and clutch size ranged from 1-6 eggs ([x bar] = 2.92). The frequency of large clutches (4-6 eggs) was significantly greater before 1940 than after. Incubation, which was shared by both sexes, lasted 24-30 d ([x bar] = 27.4). Egg length and breadth, eggshell thickness and weight, and whole egg volume and weight are presented. Hatching success was 57.5%. Mean hatching success for all clutches was 1.7 young or 2.3 per successful clutch. Hatching success of 2- and 3-egg clutches did not differ significantly. The nestling period averaged 28.7 d (range 23-34). The interval between fledging of the first and last nestling in 1 brood was up to 5 d. An average of 2.0 young were raised per successful nest, and 50.5% of the nests were successful. The mean percent of successful nests per year for the 11-yr period (excluding the drought year 1971 in which there was no nesting) was 56.5 (range 17.1-84.6/yr). Nestling mortality was 37% overall, but was less during favorable high water conditions. Twenty-two factors are identified as causing nesting failure in kites, principal among these was predation (44%).
U.S. Fish and Wildlife Service
Patuxent Wildlife Research Center
Southeast Field Station
School of Forest Resources
University of Georgia
Athens, Georgia 30602 USA
ASPECTOS DE LA REPRODUCCION DE ROSTRHAMUS SOCIABILIS PLUMBEUS
EN FLORIDA
Sinopsis.--Desde 1968 a 1977 y luego de forma interrumpida de 1978 a 1980, se estudi6
la biologia reproductiva de Rostrhamus sociabilis plumbeus en Florida. E1 ave aova en cu-
alquier mes, pero no a traves del mismo afio. E1 pico de la puesta de huevos ocurre de
febrero a abril; por lo general 81 d previo al comienzo de la 6poca de 11uvia que ocurre en
mayo. E1 int6rvalo promedio entre la puesta de huevos result6 ser 2.2 d y la camada vari6
de 1-6 huevos ( -- 2.92). La frecuencia de camadas grandes (4-6 huevos) result6 ser
significativamente major previo a 1940, que despus de esta fecha. La incubaci6n 11evada
a cabo por ambos sexos, tom6 de 24-30 d ( = 27.4). E1 57% de los huevos eclosionaron.
E1 xito de eclosionamiento fue de 1.7 polluelos para todas las camadas y 2.3 por camada
exitosa. E1 xito de eclosionamiento de camadas de 2 o 3 huevos, no fue significativamente
diferente. Los polluelos permanecieron en el nido de 23-34 d ( = 28.7). E1 intrvalo entre
volar el primero y el filtimo polluelo fue mayor de 5 d. E1 50% de los nidos fueron exitosos
y produjeron un promedio de 2 pichones. En 11 aftos de trabajo (excluyendo 1971 que fue
un afio extremadamente seco) el 6xito de los nidos vari6 de 17.1 a 84.6% ( -- 56.5%). La
mortalidad de los polluelos fue de 37% aunque menor en aftos con niveles altos de agua.
Se identificaron 24 factores de mortalidad, siendo el principal la depredaci6n (44%).
The first nest of the Snail Kite (Rostrhamus sociabilis plumbeus) was
found in Florida on 28 February 1870 near the headwaters of the Miami
River (in what was then the Everglades and is now downtown Miami)
by Charles J. Maynard (Baird et al. 1874, Maynard 1881). While much
of the breeding biology of the Snail Kite has been described, many gaps
persist (Bailey 1884; Baird et al. 1874; Bendire 1892; Bent 1937; Brown
and Amadon 1968; Chandler and Anderson 1974; Hayerschmidt 1970;
Howell 1932; Maynard 1881; Nicholson 1926; Sprunt 1942, 1945, 1947;
Stieglitz and Thompson 1967; Sykes 1979; Townsend 1927). This paper
expands our knowledge of the breeding biology and presents an overview
of the bird's reproduction to include: breeding season and its relationship
to annual hydric cycles, courtship and mating behavior, clutch size, egg
laying, incubation, egg characteristics, hatching, length of nestling period,
reproductive success, and reasons for nesting failure.
METHODS
I studied Snail Kites in Florida from 1968 through 1977 and inter-
mittently from 1978 through 1980. The primary objective was to gather
information pertinent to more effective management since the species is
considered endangered within the United States (Committee on Rare
and Endangered Wildlife Species 1966). Principal study areas were the
headwaters of the St. Johns River, the Savannas, marshes on the west
side of Lake Okeechobee, Loxahatchee National Wildlife Refuge, Con-
servation Area 2A (GA2A), and Gonservation Area 3A (GA3A) (see
Sykes 1979, 1983a, 1984).
Reproductive information was compiled from 427 nests and egg sets
(museum material 148, this study 266, literature 13). Data from 1883
through 1967 were obtained from egg sets in collections at 25 institutions
(Sykes 1984) and from the literature. The data span 1 83 intermittently
through 1967 and annually from 1968 through spring 1978. Breeding
success was not determined for 1979 and 1980 in this study. Together
with data from this study, egg sets provided information on locality, state
of incubation, clutch size, and date of collection and were used to deter-
mine approximate dates of egg laying. I used extreme caution in treat-
ment of the old egg data to avoid biases and mistakes by egg collectors.
I was unable to determine which months egg laying began for several
hundred clutches. Linear measurements of eggs were made with a vernier
caliper to the nearest 0.1 mm. Eggshell thickness was measured by in-
serting a modified micrometer through the hole drilled by the collector
at the equator of the shell. Three readings to the nearest 0.001 mm were
taken of each egg and averaged. All measurements of eggshell thickness
included the shell membrane.
Eggshells and whole eggs were weighed with a triple-beam balance to
the nearest 0.1 g. Eggshell material collected after 1968 was air dried
and weighed in an air conditioned room. Eggshell thicknesses and weights
from pre- and post-DDT periods were compared. Whole egg volume
was determined by the water displacement method in a graduated beaker
and measured to the nearest cubic centimeter. Daily or alternate day
observations were made at selected sites to determine start of courtship
and nest building activities. Nests were located by systematic searching
and watching adult behavior (i.e., carrying nesting materials, etc.). Ac-
tivities at nests were observed from blinds placed 8-10 m from the nests
and from a distance using a 30 x spotting scope on an airboat or vehicle
on dikes in the marshes. Nests (N = 266) were checked at intervals of
4-8 d to determine nesting success and causes of failure, and selected
others (N = 21) were checked every 1-3 d to determine the lengths of
incubation and nestling periods. Eggs at selected nests, from the time
laid, were numbered with soft graphite pencil at each end for identifi-
cation. The normal approximation to Chi-square (Steel and Torrie 1980)
was used to test the difference (Z value) in clutch sizes.
Rainfall and temperature data were adapted from Thomas (1974).
Water levels are not shown for CA2A after 1971 as no nesting was
recorded in that area after 1970 (Sykes 1979). Water level data were
adapted from Monthly Report of Operations of the Central and Southern
Florida Flood Control Project (U.S. Army Corps of Engineers 1968-
1978).
RESULTS AND DISCUSSION
Breeding Season
Howell (1932) noted that breeding seasons began as early as January,
but usually in late February, and extended to the middle of June. Bent
(1937) listed egg dates from 15 February to 20 July (N = 68), and
Sprunt (1942) first reported fall nesting. From 1968 to 1976, breeding
occurred every month (Table 1), but not in the same year. Egg laying
generally began 10-30 d after the start of courtship and nest building
activities.
Peak egg laying months (Table 1) were February, March, and April
(67.4%; N = 198 clutches), with substantial activity in January (11.6%)
and May (8.2%). The least nesting activity occurred in July-September
(1.3%). Breeding pairs at the same locality are asynchronous, therefore
kites near each other may be building a nest, laying or incubating eggs,
or caring for nestlings or fledgings. The start of breeding activities in
Florida varied year to year. Peak egg laying generally occurred 81 d
(95% CI = 61-101 d) before the rainy season began in mid to late May
(Table 2, Fig. 1). In some years, autumn breeding began in the latter
part of the rainy season in October or early November. Most breeding
activity took place during the cooler months since higher temperatures
and the rainy season occurred during late spring to mid fall (Thomas
1974). In Surinam the breeding season is January-July and coincides
with the rainy season (Haverschmidt 1970).
Courtship and Mating
Snail Kite courtship advertisement has been partly described (Bent
1937, Haverschmidt 1970, Stieglitz and Thompson 1967, Townsend
1927). Most displaying was by males. These displays took place through-
out the day, in the air or at a perch, and close to the nesting site. Aerial
displays frequently included stick carrying in the bill and vocalizations.
The stick may be dry or with green leaves and several males may display
TABLE 1.
P. W. Sykes, Jr.
Clutches begun by month.
j. Field Ornithol.
Spring 1987
This study Combined a
No. of No. of
Month clutches % clutches %
Jan 26 16.7 34 11.6
Feb 35 22.4 67 22.8
Mar 36 23.1 66 22.5
Apr 21 13.5 65 22.1
May 10 6.4 24 8.2
Jun 5 3.2 12 4.1
Jul 1 0.6 1 0.3
Aug 2 1.3 2 0.7
Sep 1 0.6 I 0.3
Oct 5 3.2 5 1.7
Nov 9 5.8 11 3.7
Dec 5 3.2 6 2.0
Total 156 100 294 100
a Data from museum material (1881-1964) and this study.
simultaneously. Courtship flights occurred at heights up to 300 m, but
were usually 100 m or less above the marsh. Most displays lasted 1-5
min, however, Stieglitz and Thompson (1967) reported one that lasted
nearly an hour.
Six types of aerial displays were observed with some individual vari-
ation. Usually only one maneuver occurred per display but sometimes
they were in combination (8%).
Undulating fiight.--In undulating flight (N = 346, 64% of displays),
the bird flew upward from the horizontal at an angle of 40 ø or less, then
partly folded the wings and dived at an angle less than 40 ø . The dive
was checked abruptly, and the cycle repeated, often up to 6 times. The
amplitude usually ranged from 10-30 m.
Slow fiight.--Slow flight (N = 109, 20%) was performed at a height
of 30 m or less. In this display, wing beats were slowed, and the depth
of the downstrokes was exaggerated with a slight hesitation at the lowest
point of the stroke.
Pendulum.--The pendulum (N = 36, 7%) was a shallow dive with
some wing flapping followed by a tight turn and the process repeated.
Mutual soaring.--Mutual soaring (N = 28, 5%) by a male and pro-
spective mate consisted of the pair flying parallel close together, while
executing dives, turns, rolls, etc.
Turnbling.--In tumbling (N = 17, 3%), the bird dived with wings
partly folded and turned completely over end-to-end several times before
checking the descent and leveling off.
Grappling.--In grappling flight (N = 7, 1%), the kite rolled or turned
its body to the side with the feet outstretched. This was performed by a
lone male or a male with a prospective mate.
oo oo I
..... Temper ture N=294 Clutches
:: .... Rainfall
o
CO o' .e' '.. ß
..." ."0 ..... ß ..... ß ..... 0 --*' .'"- ß '-
e- .e"' / 'o ".
co .' / .. 'o
/ [ .. "-. Max.
*o,
o / t'.
/
(. t ". Min.
ß
/ ?,, \ '-
E / ,, \
ß / ,, \Max.
J'-- I %Min.
/ \
of ]o, ,/#
o
z
Distribution by Months
FIGURE 1. The onset of egg laying for the Snail Kite by months in relation to range of
mean monthly rainfall and temperature in South Florida.
In non-aerial displays (N = 41) the male flew from perch to perch
with a stick in his bill close to a female and occasionally perched beside
her. Posturing and vocalizations frequently occurred between male and
female.
Once the pair bond was established, mating activity ensued. The re-
ceptive female perched in a tree, bush, on an exposed dead snag, or at
the nest. Greeting calls sometimes were exchanged. Male pre-copulatory
behavior included courtship feeding of an extracted apple snail (Pomacea
paludosa) or presenting a small twig. In mating, the female crouched
with tail tilted slightly to one side. The male mounted from the rear
while holding onto her back feathers with his talons. He positioned the
rear of his body and tail at a downward angle, at which time copulation
took place. Copulation lasted 3-30 s (x = 17, SE = 4.0, N = 22), after
which the male generally flew away. I do not know if brief copulations
were successful or how many copulations were required to fertilize a full
clutch of eggs. Copulations were observed from the early stages of nest
construction through laying of eggs.
Copulation took place during early incubation if the clutch was not
yet completed. This was observed at 1112 h on 8 February 1974 in a
nest containing 2 eggs (the full clutch for this nest was 4 eggs). Copu-
lation by the pair was repeated at 1236, 1559, and 1834 h.
Clutch Size
Clutch size in Florida is 1-6, with 3 eggs being the most frequent
(Bendire 1892, Howell 1932, Maynard 1881). The clutch size is reported
to be 2 and 3 in Argentina (Bendire 1892) and Surinam (Haverschmidt
1970) respectively. Mean clutch size in this study was 2.92 (Table 3).
The number of 1-egg clutches (3%) may be low because some pre-1968
egg sets had insufficient data to determine whether the clutch was 1-egg
or simply incomplete; these questionable clutches were not used.
Large clutches (4, 5, and 6 eggs; N = 26) were significantly more
frequent (Z = 3.37, P < 0.001) for the pre-1940 period (Table 3).
Although 4 and 5-egg clutches were once fairly common, I found only
one 4-egg clutch in my study and know of one other (R. Chandler, pers.
comm.) among 266 clutches. This post-1940 reduction is probably related
to habitat decline (Sykes 1983a).
Egg Laying
Eggs usually are laid between dawn and 1000 h based on 5 clutches.
Eighteen 3-egg clutches (January-June) had a mean laying interval of
2.2 d (SE = 0.08) and a range of 2-3 d. The laying interval was the
same within a single clutch. Chandler and Anderson (1974) reported
laying intervals of 2-4 d for kites with 3-egg clutches at Lake Okeecho-
bee.
Incubation
Both sexes shared incubation duties. The changeover of such duties
took place on or near the nest. On occasion, the incubating bird left the
nest before its mate arrived, leaving the eggs unattended for 1-3 min.
The usual call at the changeover was a soft, "ku-wak," given once or
twice by one or both members of the pair. The female sometimes gave a
low short series of "kaa-kaa-kaa."
Both males and females frequently brought a dry stick, a green twig
with leaves, or other material to the nest. Nesting material was given to
the mate to arrange on the nest or placed on the structure by the incoming
bird. Males often fed extracted apple snails to incubating females. The
presentation of gifts usually accompanied changeover of incubating du-
ties. Stick-giving behavior by the male has also been reported in Surinam
(Haverschmidt 1970). During the changeover of incubating duties or
upon arrival of the male with nesting material, the female on occasion
nibbled the base of the male's bill, head, or neck feathers. The presen-
tation of gifts and nibbling behavior may have helped reinforce the pair
bond.
T^BLE 3. Clutch size by decades.
Range in
Decade N SE clutch size
1881-1890 2 3.00 1.00 2-4
1891-1900 21 3.24 0.26 1-5
1901-1910 12 3.33 0.59 2-5
1911-1920 43 3.23 0.12 1-5
1921-1930 47 3.00 0.10 2-6
1931-1940 8 2.88 0.68 2-4
1941-1950 3 2.67 1.49 2-3
1951-1960 6 2.67 0.56 2-3
1961-1970 31 2.87 0.11 2-3
1971-1980 140 2.75 0.04 2-4
Total 313 2.92 0.04 1-6
One member of a pair incubated through the night while the other
slept nearby or at a communal roost (pers. obs.). The female tended to
assume the night shift (N = 200+ observations), but at 3 nests on 8
occasions males were found incubating through the night. Incubation at
night by the male is known for only a few raptors (Brown and Amadon
1968). The first changeover of incubating duty for the day took place
within an hour after dawn and the relieved bird flew off to hunt (pers.
obs.). The mean diurnal incubation interval was 58 min (range 3-299
rain, N = 57). There was no significant difference (P > 0.5) in the
incubation interval between members of a pair (N = 3); males incubated
for an average of 60 min (SE = 12.5, N = 28) and females for 55 min
(SE = 8.5, N = 29). During diurnal incubation, the attending individual
slept, rearranged nesting materials, preened, called, watched birds and
aircraft flying over, turned eggs, or changed incubating position. Incu-
bating posture was with the head erect, head lowered with tail higher
than head, or head lowered with the chin resting on rim of the nest. The
number of changes (N = 50) in incubating position was 1-25 per incu-
bating interval and averaged 5.3 (SE = 0.7). Incubating position changes
averaged every 11.5 min (SE = 0.76, range 1-100, N = 262). Incubating
birds faced in any compass direction with the orientation independent of
wind direction.
Eggs were turned 1-3 times per day (N = 16 observations); females
turned eggs more frequently (87.5%, N = 14, 3 pairs) than males. Egg
turning was accomplished in 1-3 min and usually occurred before noon
(93%).
Incubation averaged 27.4 d (SE = 0.1, range 24-30 d, N = 21 nests).
The incubation period at Lake Okeechobee was 26-28 d (Chandler and
Anderson 1974), whereas for captive R. s. sociablis from Argentina at
Patuxent Wildlife Research Center, Laurel, Maryland, it ranged from
24-26 d (G. F. Gee, pers. comm.). Incubation started anytime after the
first egg was laid but generally after the second was deposited.
Egg Characteristics
The eggs are usually oblong oval in shape, although some tend to be
elliptical. The shell surface is smooth and dull, and the ground color is
dull white with variable markings (Fig. 2, also see Bent 1937). Intensity
of brown pigments varied between and within clutches.
Bent (1937) listed an average length of eggs of 44.2 mm and breadth
of 36.2 mm (N -- 65). These measurements correspond closely with my
larger sample (N -- 317, Table 4). Eggshell thickness is variable in the
same egg and between eggs. Shell weight is perhaps a better indicator of
any biological problem (Anderson and Hickey 1972, Hickey and Ander-
son 1968, Porter and Wiemeyer 1969, Ratcliffe 1967). No significant
difference was found for eggshell weights (t = 0.53, P 0.6) for the
pre- (1944 and earlier) and post-DDT (1945 and later) periods.
The mean fresh egg weight was 31.7 g (N -- 23). The mean loss of
egg weight (primarily water loss) during incubation was 16.3%, similar
to most birds (Rahn and Ar 1974). The nests were built over water and
the nest bowls lined with green materials which insured a more uniform
high relative humidity and probably helped minimize water loss from
the eggs.
Hatching
Hatching was asynchronous. The interval between hatching of suc-
cessive eggs within a clutch ranged from less than a day up to 6 d. The
nestling can be heard calling within the egg 24-48 h prior to hatching
and emerges 6-14 h (,i = 8.2, $E = 1.0, N = 9 eggs, 8 clutches) after
the egg is first pipped.
In Florida from 1968 through 1978, hatching success was 57.5% (Ta-
ble 5). Chandler and Anderson (1974) reported hatching success of 53.7%
for kites at Lake Okeechobee. Kites averaged 2.3 chicks per nest at
hatching in clutches where one or more eggs hatched, but 39 of 127 nests
failed. Where at least one egg hatched, 2% hatched 1 egg, 13% 2 eggs,
and 85% 3 eggs. In the only 4-egg clutch I observed, 3 eggs hatched.
Hatching success by clutch size and month is summarized in Table 6.
There was no significant difference (P > 0.4) in hatching success be-
tween 2- and 3-egg clutches. Other clutch sizes were too few for com-
parison. The months with the largest number of successful hatches were
March (31%), April (23%), and February (19%).
Nestling Period
The nestling period as used in this paper is the period extending from
hatching to fledging. Nestling periods ranged from 23-34 d with a mean
of 28.7 d. In the same brood, the interval between fledging of the first
and last nestling was up to 5 d (. = 2.3, SE = 0.2, N = 20) and may
have been longer in a few cases. The interval between fiedging of siblings
appears to be independent of brood size. The attentiveness of individual
pairs in care of young varied widely.
FIGURE 2. Snail Kite eggs from Florida showing variation in markings.
Breeding Success
From 1968-1978, 50.0% of the nests (102 of 204) were successful,
and fledged 201 young or 2.0 (range 1.4-2.5) young per successful nest
or 0.99 young for all nests in which one or more eggs were laid. In a
smaller more limited study at Lake Okeechobee 1966-1973, 82 eggs were
laid, 44 hatched (53.7%), and 31 young fledged (37.8%) (Chandler and
Anderson 1974). Mean annual nesting success for the 11-yr period, ex-
cluding the drought year of 1971 when no breeding was recorded, was
56.5% (range 17.1-84.6).
Brown and Amadon (1968) and Newton (1979) showed that breeding
success is usually less than 50% among Falconiformes but varies widely.
The range of success rates for the Snail Kite in Florida was within this
norm. The year-to-year variation appears to be due to environmental
variability. Breeding success was lowest in the dryer years (Fig. 3; also
see Sykes 1983b) and highest during wetter times when food was more
abundant and predation lower (Sykes 1987, unpubl. data). A breeding
success between 40-50% (see Table 7) is probably adequate to maintain
the species in Florida. Nestling mortality from 1968-1978 was 37%. The
kite population increased significantly from 81 to 651 birds (r = 0.981,
P < 0.001) between 1974 and 1980 under favorable habitat conditions
ooo
ooo o
oo
oooo
o
ooo
oooooooo
',.-.-'
bOO
ß .
ooooooo
o o
oo
oooo
o o
oo
o o o
o o o
o o o
Water Depths
ß . .... ß Lake Okeechobee
'" ...... ,', CA2A
o---,-o CA3A
01
Nests
&
68 7"0
100 O
z
:? O
,' O
oo:? .'50 u.
.! - ..
O
ß ...... /o-."'r ':d' '
m
', ". .::.;'" Oroun
--- \ ...... .-.---.-.* ,o' .... s'%?œ .... '"'
ß % ß .' I '"
[tY: ; ,- /
ß '.= .' ; / ,,,
ß % 0 m
mS0 0
.,J
I I I ß I I mm
72 74 7S 78
YEAR
FIGURE 3. Relationship of successful nesting (%) by the Snail Kite in Florida per year
with the lowest depth of marsh flooding at the end of the annual dry season, late April-
early May, at three prindpal breeding areas.
of high water levels at Lake Okeechobee and in CA3A (Sykes 1983b).
The greater abundance of snails during this period of favorable condi-
tions was probably the reason for the lower nestling mortality.
The kite's breeding season was timed to take advantage of increasing
seasonal water levels in Florida's marshes and avoid the period of intense
local summer storms with heavy rains and strong winds. Most young
had fledged when the rainy season commenced in May and water levels
began to rise. Apple snail activity and abundance increased to a high
level in April and continued through summer and early fall (Hanning
1978, pers. obs.). Thus, the kite's prey was more active, widespread, and
available at the time when most juvenile kites are learning to hunt and
become self-sufficient.
T^3LE 7. Breeding success of the Snail Kite in Florida 1968-1978. a
Nests Young
Fledged per
Percent Total number successful
Year Successful successful fledged nest b
1968 11 84.6 24 2.2
1969 8 80.0 13 1.6
1970 8 44.4 12 1.5
1971 c -- -- 0 --
1972 3 50.0 7 2.3
1973 12 35.3 29 2.4
1974 6 17.1 11 1.8
1975 14 48.3 35 2.5
1976 22 73.3 30 1.4
1977 8 53.3 20 2.5
1978 11 78.6 20 1.8
Tal 103 50.5 201 2.0
a Incorporates 1968-1976 data (Sykes 1979) but excludes nests placed in nesting struc-
tures at Lake Okeechobee (Sykes and Chandler 1974, Roderick Chandler pers. comm.).
b Only those nests in which the exact number of young fledged was known were used to
derive these figures.
c Severe drought conditions throughout peninsular Florida; no nesting attempts observed.
Reasons for Nesting Failure
Nesting failure resulted from predation, adverse weather, weak nesting
substrate, human disturbance, and miscellaneous causes (Table 8). Be-
tween 1968 and 1978, 14 false starts (4% of the nesting attempts ob-
served) were recorded (not included in Table 8). In 13 cases, nests were
never completed and in one, the nest was completed but no eggs laid.
Only 4 cases of nest desertion were observed, all contained eggs. The
reasons for desertion were not determined. For the documented nesting
failures (N = 81), 67% contained eggs and 33% nestlings. If the nest
failed, particularly during the egg stage or early in the nesting season
(N-- 9), the birds usually renested. This was determined from color
banded individuals and recognition of a few unmarked birds by plumage
characteristics.
Most predation (58%) was not traceable to specific predators, but I
suspect that the Everglades rat snake (Elaphe obsoleta rossalleni) was
responsible for many of the losses (Table 8). Snakes will on occasion
attempt to ingest nestlings that are too large for them to swallow. In two
such cases, the nestlings probably suffocated, as the feathers of the head
and neck were matted with mucous from the snake's mouth while the
remainder of the plumage was in the normal dry condition. The Ever-
glades rat snake is widespread in southern Florida (Carr and Goin 1959),
highly arboreal, and one of the most common snakes in the nesting
habitats of the kite (pers. obs.).
Nestlings at two nests at Loxahatchee National Wildlife Refuge may
TABLE 8.
P. W. Sykes, Jr.
Factors responsible for nesting failure.
j. Field Ornithol.
Spring 1987
% of
mot-
% of tality
total within
mor- cate-
Decimating factor tality gory Eggs
Number of nests
Contents at time of
failure
Eggs
or
Young young
Total
Predation 44 36
Unknown predator 58 18 3 21
Everglades rat snake (Elaphe
obsoleta) 17 3 3 6
Probably Everglades rat snake 8 2 1 3
Fish Crow (Corvus ossifragus) 5 5 2
Crow, species undetermined 3 1 1
Cottonmouth moccasin
(Agkistrodon piscivorus) 3 1 1
Probably cottonmouth mocassin 3 1 1
Ant (Crematogaster atkinsoni) a 3 1 1
Adverse weather 22 18
Strong winds without rain 55 7 3 10
Long period of heavy rain 22 1 3 4
Low temperatures 11 2 2
Heavy rain with hail 6 1 1
Heavy rain with strong winds 6 1 1
Weak nesting substrate 16 13
Nest fell down 100 10 3 13
Human disturbance 9 7
Fire set by humans 57 3 1 4
Airboats 29 2 2
Activity near nests 14 1 1
Eggs did not hatch 4 3
Eggs probably infertile 67 2 2
Eggs infertile 33 1 1
Ectoparasites 3 2
Heavy mite infestation 100 2 2
Disease 1 1
Pneumonia b 100 2 2
Accident 1 1 1
Nestling fell from nest 100 1 1
Total -- 54 27 1 82
Percent -- 66 33 1 100
a Sykes and Chandler (1974).
b Diagnosis of dead nestlings was made by the National Fish and Wildlife Health Lab-
oratory, Madison, Wisconsin.
have been taken by a Great Horned Owl (Bubo virginianus). Both nests
were highly visible and within the territory of a pair of nesting owls.
The young kites were too large to have been swallowed by a snake, and
they disappeared overnight. There was no evidence of struggle at the
nest or immediate surroundings and during that period no corvids were
observed in that area of the refuge. These two losses are included under
unknown predator in Table 8.
Crows (Corvus spp.) were reported to occasionally rob kite nests of
eggs on the eastern edge of the Everglades in the late 1800s (Bailey
1884). During my study the Fish Crow (C. ossifragus) took eggs at two
nests on the headwaters of the St. Johns River. Reservoirs in which the
kites nested on the St. Johns are small and close to upland habitats (Sykes
1983a, 1984). Common (C. brachyrhynchos) and Fish Crows are now
uncommon in the extensive marshes of the Everglades, except for Com-
mon Crows along the Tamiami Trail (U.S. Hwy. 41), and are usually
restricted to upland margins or cypress and mangrove forests. With few
exceptions, kites nest away from such areas.
Circumstantial evidence suggests that kite eggs were destroyed by a
Boat-tailed Grackle (Quiscalus major) in 1956 at Lake Okeechobee
(Wachenfeld 1956). More recently, 9 clutches were reported lost to grackle
predation (Chandler and Anderson 1974). On several occasions I have
watched Boat-tailed Grackles show no interest in Snail Kite eggs, al-
though they were within less than 5 m of unattended nests with eggs in
view. If grackles do take kite eggs, it may be localized behavior.
During long periods of rain (i.e., up to 3 d) some nestlings die from
exposure or from a secondary agent. Two nestlings that died from pneu-
monia (Table 8) were probably soaked first by rain and then contracted
the disease. Also, rainy weather makes hunting more difficult for adults
(pers. obs.) and nestlings already stressed from being wet may not survive
if feeding is reduced.
All kite nests were built over water and those placed in cattails (Typha
angustifolia and T. domingensis) were frequently lost (Sykes and Chan-
dler 1974). The leaves of cattails are not rigid enough to support nests
in strong winds (>24 km/h) during storms or prolonged windy periods.
Cattail leaves were further weakened as nesting substrates when water
levels were lowered. Also, nests built in cattails settled, some as much as
a meter, and often tipped, dumping their contents into the water. Twelve
of the 13 nests that failed because the nest fell or tipped were in cattails
and the remaining nest was placed on a rotten tree stub that broke.
Human-caused fires often sweep through kite nesting habitats in Flor-
ida during the dry season, November-April (Hofstetter 1974, Robertson
1953, Sykes 1979), and usually were more severe than natural fires from
lightning that occurred during the wet season, May-October (Hofstetter
1974, Robertson 1953). Nicholson (1926) reported several nests on the
headwaters of the St. Johns River destroyed by fire. In my study 4 nests
were lost to fires.
Human disturbances to nesting kites probably were not overt acts.
From my observations, people either did not know a nest was present or
failed to recognize the behavior of nesting adults. Incubating birds near
frequently used boat trails were repeatedly flushed. Also, nests may be
blown down from the prop wash of an airboat propeller or run over.
Such was much more likely to occur with frog hunters who operate at
night.
Unhatched eggs presumed to be infertile have been reported in Florida
(Chandler and Anderson 1974, Sprunt 1945, Stieglitz and Thompson
1967). In my study, one nest had and two others were suspected to have
infertile eggs (full term incubation with no trace of embryonic develop-
ment).
Additional factors may be responsible for nesting failure in the Snail
Kite in Florida. One nestling fell from its nest, became lodged by the
neck in the forked stem of a small tree, and died when it could not free
itself; and ectoparasitic mites (Ornithonyssus bursa) were responsible for
the death of young at two nests (Sykes and Forrester 1983).
ACKNOWLEDGMENTS
I express appreciation to those who assisted with the field work and to Ray C. Erickson
for encouragement and support throughout the study. In particular I thank Roderick Chan-
dler for aid at Lake Okeechobee and for providing some data on kite nesting for that area.
Stephen Mountainspring helped with statistical analysis. For review of the manuscript and
suggestions for its improvement, I thank Louis B. Best, James O. Evrard, George F. Gee,
Stephen Mountainspring, John C. Ogden, and J. Michael Scott.
LITERATURE CITED
ANDERSON, D. W., AND J. j. HICKEY. 1972. Eggshell changes in certain North American
birds. Pp. 515-540, in K. H. Voous, ed. Proc. 15th Int. Ornithol. Cong. The Hauge,
Netherlands.
BAILEY, H. B. 1884. Breeding habits of the Everglade Kite. Auk 1:95.
BAIRD, S. F., T. M. BREWER, AND R. RIDGWA3/4. 1874. A history of North American
birds. Little, Brown & Co., Boston.
BENDIRE, C. 1892. Life histories of North American birds. U.S. Natl. Mus. Spec. Bull.
No. 1.
BENT, A. C. 1937. Life histories of North American birds of prey. Part 1. U.S. Natl.
Mus. Bull. 167.
BROWN, L., AND D. AMADON. 1968. Eagles, hawks and falcons of the world. Vol. 1.
McGraw-Hill Book Co., New York.
CARR, A., AND C. J. COIN. 1959. Guide to the reptiles, amphibians, and fresh-water
fishes of Florida. Univ. Florida Press, Gainesville.
CHANDLER, R., AND J. M. ANDERSON. 1974. Notes on Everglade Kite reproduction.
Amer. Birds 28:856, 858.
COMMITTEE ON RARE AND ENDANGERED WILDLIFE SPECIES. 1966. Rare and endangered
fish and wildlife of the United States. U.S. Dept. Interior, Bur. Sport Fisheries and
Wildl., Resour. Publ. 34.
HANNING, G. W. 1978. Aspects of reproduction in Pomacea paludosa (Mesogastropoda:
Philidae). Unpubl. MS thesis, Florida State Univ., Tallahassee.
HAVERSCHMIDT, F. 1970. Notes on the Snail Kite in Surinam. Auk 87:580-584.
HICKEY, J. J., AND D. W. ANDERSON. 1968. Chlorinated hydrocarbons and eggshell
changes in raptorial and fish-eating birds. Science 162:271-273.
HOFSTETTER, R.H. 1974. The effect of fire on the pineland and sawgrass communities
of Southern Florida. Pp. 201-212, in P. J. Gleason, ed. Environments of South Florida:
present and past. Miami Geol. Soc. Mem. 2, Miami, Florida.
HOWELL, A.H. 1932. Florida bird life. Dept. Game and Fresh Water Fish, Tallahassee.
MAYNARD, C.J. 1881. The birds of eastern North America. C. J. Maynard and Co.,
Newtonville, Massachusetts.
NEWTON, I. 1979. Population ecology of raptors. Buteo Books, VeTmillion, South Dakota.
NICHOLSON, D.J. 1926. Nesting habits of the Everglade Kite in Florida. Auk 43:62-67.
PORTER, R. D., AND S. N. TIEMEYER. 1969. Dieldrin and DDT: effects on Sparrow
Hawk eggshells and reproduction. Science 165:199-200.
RATCLIFFE, D. A. 1967. Decrease in eggshell weight in certain birds of prey. Nature
215:208-210.
RAHN, H., AND m. mR. 1974. The avian egg: incubation time and water loss. Condor 76:
147-152.
ROBERTSON, W. B., JR. 1953. A survey of the effects of fire in Everglades National Park.
Natl. Park Serv. Rep. (mimeo, 169 pp.), Homestead, Florida.
SPRUNT, A., JR. 1942. Remarkable nesting date of the Everglade Kite. Auk 59:585-586.
1945. The phantom of the marshes. Audubon Mag. 47:15-22.
1947. Snail Hawks of the sawgrass. Fauna 9:77-79.
STEEL, 'R. G. D., AND J. H. TORRIE. 1980. Principles and procedures of statistics: a
biometrical approach. 2nd ed. McGraw-Hill Book Co., New York.
STIEGLITZ, W. O., AND R. C. THOMPSON. 1967. Status and life history of the Everglade
Kite in the United States. U.S. Fish and Wildl. Serv. Spec. Sci. Rep., Wildl. No. 109.
SYKES, P. W., JR. 1979. Status of the Everglade Kite in Florida--1968-1978. Wilson
Bull. 91:495-511.
1983a. Snail Kite use of the freshwater marshes of South Florida. Florida Field
Nat. 11:73-88.
1983b. Recent population trend of the Snail Kite in Florida and its relationship
to water levels. J. Field Ornithol. 54:237-246.
ß 1984. The range of the Snail Kite and its history in Florida. Bull. Fl. State Mus.
Biol. Sci. 29(6):211-264.
1987. The feeding habits of the Snail Kite in Florida, USA. Colonial Waterbirds
10:iin press).
, AND R. CHANDLERß 1974. Use of artificial nest structures by Everglade Kites.
Wilson Bull. 86:282-284.
, AND D. J. FORRESTERß 1983. Parasites of the Snail Kite in Florida and summary
of those reported for the species. Florida Field Nat. 11:111-116.
THOMAS, T. M. 1974. A detailed analysis of climatological and hydrological records of
South Florida with reference to man's influence upon ecosystem evolution. Pp. 82-
122, in P. J. Gleason, ed. Environments of South Florida: present and past. Miami
Geol. Soc. Mem. 2, Miami, Florida.
TOWNSEND, C. W. 1927. Notes on the courtship of the Lesser Scaup, Everglade Kite,
Crow, and Boat-tailed and Great-tailed Grackles. Auk 44:549-554.
WACHENFELD, m. W. 1956. Present status of Everglade Kite. Linnaean News-letter
10(3):1.
U.S. ARMY CORPS OF ENGINEERSß 1968-1978. Monthly report of operations of the Cen-
tral and Southern Florida Flood Control Project. Dist. Office, Jacksonville, Florida.
Received 12 June 1986; accepted 15 Nov. 1986.