Zoo Biology 29 : 615–625 (2010)
HUSBANDRY REPORT
Successful Captive Breeding of
Mitchell’s Water Monitor, Varanus
mitchelli (Mertens 1958), at Perth Zoo
Glen Gaikhorst,1 James McLaughlin,2 Brian Larkin,3 and Meagan McPharlin3
1
Native Species Breeding Program, Perth Zoo, South Perth, Western Australia,
Australia
2
CSIRO Marine and Atmospheric Research, Centre for Environmental and Life
Sciences (CELS), Floreat, Western Australia, Australia
3
Reptiles, Perth Zoo, South Perth, Western Australia, Australia
Mitchell’s water monitors (Varanus mitchelli) have been maintained on display at
Perth Zoo since 1997. They are generally a timid species but have been maintained
and bred in a mixed species water feature exhibit. In this article we describe their
captive management and behavior with an insight into their reproductive biology.
Between 2002 and 2005, 11 clutches were laid ranging from 13 to 27 (X ¼ 20) eggs
from one female. Egg size ranged between 3.00 and 6.08 g (X ¼ 4:77 g) in weight,
22.8 and 31.9 mm (X ¼ 28:3 mm) in length, and 11.1 and 19.3 mm (X ¼ 17:1 mm)
in width. Oviposition included double and triple clutches ranging between 41 and
60 days apart (X ¼ 48 days), events n 5 6. Four clutches were incubated at three
different temperatures and hatchlings emerged after 157–289 days. The weight of
the hatchlings ranged between 2.60 and 4.52 g (X ¼ 4:34 g). Total length ranged
between 140.1 and 178.0 mm (X ¼ 165:9 mm) and snout–vent length ranged from
53.8 to 70.0 (X ¼ 64:4 mm). Juvenile growth and development information is
presented from hatching through to approximately 3 years of age. Zoo Biol
29:615–625, 2010.
r 2009 Wiley-Liss, Inc.
Keywords: behavior; captive management; growth and development; reproductive biology
Correspondence to: Glen Gaikhorst, Native Species Breeding Program, Perth Zoo, Labouchere Road,
South Perth, WA 6951, Australia. E-mail: glen.gaikhorst@perthzoo.wa.gov.au
Received 13 August 2008; Accepted 22 December 2008
DOI 10.1002/zoo.20244
Published online 18 May 2009 in Wiley Online Library (wileyonlinelibrary.com).
r 2009 Wiley-Liss, Inc.
616 Gaikhorst et al.
INTRODUCTION
Mitchell’s water monitor (Varanus mitchelli) is a common species whose
distribution extends from the Kimberley of Western Australia through the Northern
Territory into the extreme northwest of Queensland [Cogger, 2000; Ehmann, 1992;
Vincent and Wilson, 1999; Schultz and Doody, 2004]. It inhabits areas with
permanent or semi-permanent water bodies. The water is either fresh or brackish with
thick riparian vegetation consisting of Pandanus, Melaleuca, freshwater mangroves,
and bamboo or rocky habitats on the edge of water ways [Schultz and Doody, 2004].
Generally, the color is quite variable from dark brown to bluish black, blackish
gray to olive gray above, covered in a scattering of yellowish or cream flecks, spots,
or ocelli, whereas the sides of the neck and throat are bright yellow to orange with
black flecks. The underbelly is pale in color [Cogger, 2000; Vincent and Wilson,
1999; Schultz and Doody, 2004; Steel, 1997]. The tail is 1.7–2.1 times longer than the
head and body length [Storr, 1980] and is laterally compressed and double keeled
[Steel, 1997]. The nostrils are upward and outward facing to assist with living in a
semi-aquatic environment. Mitchell’s water monitor is medium-sized with a total
length (TL) of 60–96 cm [Vincent and Wilson, 1999]. It is a member of the Odatria
subgenus, which comprises 17 species including sister species V. semiremex and
V. timorensis [Schultz and Doody, 2004].
Its wild diet consists of arthropods, fish, frogs, small reptiles and their eggs,
and small mammals and birds. The diet changes seasonally with the advent of the
wet-season flooding [Shine, 1986; Steel, 1997; Schultz and Doody, 2004]. Breeding
usually occurs in the dry season with females depositing eggs between April and June
[Shine, 1986; James et al., 1992; Vincent and Wilson, 1999]. Clutch sizes in the wild
have been recorded at 3–11 [Ehmann, 1992], 7–12 [Shine, 1986], and 12 [Steel, 1997;
Schultz and Doody, 2004; James et al., 1992; Vincent and Wilson, 1999], and in
captivity there is a report of up to 20 eggs [Schultz and Doody, 2004]. Very little is
known about the biology of this species as Mitchell’s water monitor has been kept in
captivity only rarely, with one record of successful captive breeding being published
[Schultz and Doody, 2004]. Similar species have been maintained and bred in
captivity including V. semiremex [Jackson, 2005], V. mertensi [Eidenmüller and
Wicker, 1995; Vincent and Wilson, 1999], and V. timorensis [Debitter, 1981;
Eidenmüller, 1986; Bennett, 1998].
Reproduction of V. mitchelli at Perth Zoo began in 2001 with one small clutch
of eggs laid on the enclosure’s surface. All the eggs were dehydrated except one,
which was artificially incubated and hatched. This breeding event and data were
reported by Schultz and Doody [2004]. This article reports on the subsequent
successful breeding of V. mitchelli from 2002 to 2005 at Perth Zoo (Figs. 1 and 2).
METHODS
Study Animals
The male was a wild-caught adult of unknown age, collected on 26/04/1997
from Kununurra, Western Australia. The female was originally a wild-collected
specimen from northwest Western Australia; however, the collection date and the
location are unknown. She was donated under permit to Perth Zoo by the University
of Western Australia on 03/02/2000.
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Captive Breeding of Mitchell’s Water Monitor 617
32
9
8
28
7
26
24
6
22
5
Change in mass (g)
Change in size (mm)
30
20
Egg length
Egg diameter
Egg mass
18
16
4
3
27 Oct 02
31 May 02
Date
Fig. 1. Mean (7s.e.m.) changes in egg length, diameter, and mass between laying and 8 days
prior to first eggs hatching from clutch 2 during incubation.
450
SVL
60
400
TL
WT
50
300
40
250
30
200
150
Weight (g)
Length (mm)
350
20
100
10
50
0
0
20
40
60
80
100
120
140
0
160
Time (weeks)
Fig. 2. Mean of 11 individuals’ (7s.e.m.) growth in weight (WT), snout–vent length (SVL),
and total length (TL) over time.
Housing
The V. mitchelli were housed together (see Fig. 3) in a display enclosure
measuring 370 cm 300 cm 120 cm. The enclosure is mock rocked along the back
with the viewing area and sides made of glass panels with a swinging door for keeper
access. The substrate was a mock rock floor with a small area of pea gravel and sand,
tapering down into a pond at the bottom. The pond also housed six pink-eared
turtles (Emydura victoriae), a primitive archerfish (Toxotes lorentzi), and blue catfish
(Arius graeffei). The enclosure habitat provided a permanent source of water for the
monitors and was continuously pumped through a sand filter. The pond was heated
via four 300 W aquarium heaters and maintained a water temperature range of
24–261C in summer and 22–241C in winter.
Zoo Biology
618 Gaikhorst et al.
Fig. 3. Pair of Mitchell’s water monitors (Varanus mitchelli) basking in the public exhibit at
Perth Zoo. Male left, female right.
Fig. 4. (a) Front of nest box located in V. mitchelli exhibit in which clutches of eggs were
deposited. (b) Nest box in V. mitchelli exhibit with lid removed.
Branches were provided for climbing, allowing the lizard’s vantage spots for
basking under the ultraviolet (UV)/heat lamps, bark hides, and a mock rock heat
pad (set at 30–351C). A concrete nest box was provided, which was triangular in
shape (400 mm 400 mm 400 mm triangle 300 mm deep) with an entry hole close
to the top lip (see Fig. 4a, b). The box was mock rocked to visually blend with the
furnishings of the exhibit and was filled with a layer of moist sand and peat mix
(50/50) to a depth of approximately 250 mm to aid in oviposition. Artificial lighting
was provided over the exhibit with halogen bulbs (Sylvania Aqua-arc HSI-TD
150 W, MA) and there were several basking spots heated by five heat and UV lamps
(two infra-red 375 W globes (MA) and three Osram ultra-vitalux (MA) or Radium
ultra-vitalux 300 W globes, MA). These provided adequate heat and UV rays for the
animals. Basking sites were maintained around 351C. Seasonal photoperiod was
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Captive Breeding of Mitchell’s Water Monitor 619
maintained through the lighting system, which was on a timer system providing
variation in day length with a longer exposure in summer than winter. The animals
were maintained together all year round and only disturbed if weighing or physical
examinations were required.
Juveniles were housed separately in opaque/clear plastic tubs within a steel
rack system. The dimensions of the tubs were 300 mm 600 mm 280 mm. Three
racks were used in total holding 12 tubs in each. Each tub had a 100 W spotlight that
supplied a hot basking area on pieces of Hardiflexs sheet (James Hardie, Welshpool,
WA, Australia) to a heat of 35–401C (approximately 30 cm away). Each tub also had
exposure to a 40 W Repti-sun fluorescent bulb (CA) and a 40 W Repti-glo
fluorescent bulb (CA) at 30 cm to provide UV to the young monitors.
Within the tubs, white sand was used as substrate to a depth of 30 mm. Hardy
fencing material was cut into 200 or 150 mm squares and siliconed together with
glass marbles in between. These were used to supply hide spots between the hardy
fence layers as well as provide a basking site. Pieces of bark were also used around
the tub as refuges. A water bowl was placed at the far end of the heated area.
Because of the intense heat created by the lighting, a large reverse cycle airconditioning unit was used to maintain the ambient air temperature at around 251C.
All eggs were incubated in a Repti-life (Reptile Incubator, Lyons Electronic
Company, Chula Vista, CA) reptile egg incubator.
Husbandry
All enclosures were serviced daily. This included cleaning and changing of
water bowls, removing fecal matter, and checking animal well-being. In the display
enclosure, cleaning included removing old food items, picking up slough, and
removing/scrubbing urate stains off the mock rock. A large bacterial filtration
system (approximately 120 l), for the display pond and waterfall, aided in
maintaining water quality. This was serviced daily and reverse cycle cleaned once
a week. The entire filter was stripped and cleaned approximately every 4 months.
The juvenile monitors required a more humid environment (60% or greater);
therefore, the immediate area around the water bowl was moistened daily and
enclosures misted with hand units as required. Lighting and heating equipment was
changed as required.
Diet
Mitchell’s water monitor is an active forager and feeds on a variety of animals
in the wild [Vincent and Wilson, 1999]. At Perth Zoo, the monitors were fed three
times a week. Their primary diet consisted of large crickets, wood cockroaches, small
mice (or chopped mice), fish (whitebait, pilchards, or bluebait), and prawns, which
were dusted with calcium carbonate powder (Wednesdays and Fridays) and a 1:1
Herptevite (Rep-Cal Research Labs, Los Gatos, CA)/calcium carbonate mix on
Mondays. Each feed consisted of approximately 30–50 g of food per animal, which
was adjusted according to the condition of the animals. For example, during the
breeding season or when the female was seen to be gravid, small extra feeds were
given as required to assist with egg development.
Juveniles were fed daily initially on a diet of small invertebrates consisting of
crickets and small wood cockroaches dusted with calcium carbonate powder
(Wednesdays and Fridays) and a 1:1 Herptevite/calcium carbonate mix on Mondays.
Zoo Biology
620 Gaikhorst et al.
Once feeding reliably, they were introduced to chopped fish, diced mice, or dead
pinkie mice. Sizes of the food items offered increased with age. Adults and juveniles
could be fed via tongs or by scatter feeding. Water was supplied to all animals via
large water bowls and cleaned on a daily basis. The water bowls were large enough to
allow the animals to submerge.
Measurements and Observations
Growth measurement data were recorded from 11 juvenile monitors from
clutch 5 over a 3-year period. Weight measurements were taken on precision
electronic scales. For more accurate data, scales to the second decimal gram were
used particularly while the animals were small. To prevent the animals from escaping,
small zip-lock bags (Glad zip-lock bags (CA), sandwich size, Australia) were used to
temporarily hold the animals while their weight was recorded. Two length
measurements were recorded—snout–vent length (SVL) and TL. Snout–vent
measurement is from the tip of the snout to the cloaca and TL was measured from
the tip of the snout to the tip of the tail. Length measurements were taken with a clear
ruler, to the nearest millimeter. All measurements were recorded every 2 weeks for 12
months and then opportunistically for a further 2 years. All measurements were taken
from the actual time of birth so that data could be plotted on the same scale.
Changes in egg size were recorded from clutch 2 (n 5 20) at the time of
oviposition and 8 days prior to hatching. Eggs were measured by weight, length, and
width. Weight was recorded on precision electronic scales and length and width
measurements were taken using calipers and recorded to 0.1 mm. Observations on
specific events (such as behavior or reproductive activities) were made opportunistically during feeding events or routine monitoring of the animals.
Analysis
Size parameters were expressed as mean7s.e.m. and comparisons made using
paired t-test. Differences were considered significant if Po0.05.
RESULTS
Behavior and Breeding Information
Adult
We found Mitchell’s water monitor to be a nervous species that did become
more relaxed in time and with keeper interaction. The pair could be maintained
together for long term and only required separation to stop breeding or after an
aggressive confrontation where short-term medical intervention was required. The
animals were often observed lying on each other under basking lights but the female
displayed more basking behavior than the male. The male preferred to lie under a
piece of wood on the heat pad.
During courtship, the male became very interested in the female, displaying
rapid head movements and nuzzling her sides and head. Head movements consisted
of bobbing and sideways jerking. The male was often observed lying parallel to the
female with one forelimb on her back. No open mouth aggression was recorded at
this time. Copulation occurred on and off the ground and composed of the pair lying
parallel to each other with his cloaca pushed under/alongside hers and tails coiled. It
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Captive Breeding of Mitchell’s Water Monitor 621
was difficult to determine for how long the pair mated each time but we estimate it to
be 15–45 min. The period from copulation to oviposition ranged between 18 and 36
days (X ¼ 28 days, n 5 7).
The female when gravid became distended in the abdomen and lost physical
condition of her tail exposing the vertebrae above the cloaca. Feeding would increase
at this time. She received extra feeding to assist in egg development and in an attempt
to keep her in good physical condition. She would stop feeding 1–8 days prior to
oviposition. During this time she would spend long periods under the UV/heat
lighting basking or pacing the enclosure, digging test holes 1–2 days prior to
oviposition. When oviposition was imminent, the female became very restless often
pacing and exploring the enclosure. This was often observed in the afternoon period.
Once satisfied with the nest site (often in the nest box), she entered, dug a burrow,
and resided in it for several hours laying the clutch before backfilling the hole and
returning to her enclosure to bask. Prior to oviposition, the female’s body weight
ranged from 318 to 393 g and postoviposition dropped to 206–260 g. The female
began feeding again 24–48 hr after oviposition was completed. Clutches laid in the
nest box were used in the incubation and hatchling data.
Aggression toward the male was recorded on one occasion 2 days after oviposition
with blood drawn from the male after he presented to her for an attempted breeding
event. He was bitten on the snout and neck. This also occurred during feeding sessions in
which both individuals inflicted head injuries on one another. No aggression was seen
toward the E. victoriae or the fish species in the pond.
Juveniles
Juveniles were very timid, often only observed retreating to hides when a keeper
was present, but their timid nature decreased with age. Enclosures housing multiple
individuals were tried initially with juveniles, but dominance interactions and
competition occurred between individuals, and therefore subsequently only single
individuals were kept in enclosures. Careful inspection of the enclosure was required
to prevent escapes as juveniles were capable of squeezing out of the smallest gaps.
Clutches
Eleven clutches were recorded between 16/4/2002 and 27/9/2005 with clutches
laid in almost all months, though they varied greatly between different years. The
breeding period was between April and May in 2002, between June and July in 2002,
and between January and March in 2004. The year 2005 had two periods of
November 2004 and January 2005, then again from June to September. Double
clutching occurred five times and a triple clutch occurred once. Multiple clutch
intervals ranged between 41 and 60 days (X ¼ 48 days), events n 5 6. Clutch size
varied between 13 and 27 eggs with an average number of 20 eggs produced
(excluding clutch 8 from this analysis). Egg size ranged between 3.00 and 6.08 g
(X ¼ 4:77 g) in weight, 22.8 and 31.9 mm (X ¼ 28:3 mm) in length, and 11.1 and
19.3 mm (X ¼ 17:1 mm) in width as seen in Table 1.
Artificial Incubation
Four clutches (43 eggs in total) were artificially incubated. The eggs were
prepared for incubation in 1:1 water to vermiculite by weight mixture. A depth of
approximately 40 mm of vermiculite was put in clear rectangular plastic containers
Zoo Biology
622 Gaikhorst et al.
TABLE 1. The mass, length, and width (mean and range) of eggs from 11 clutches laid by one
female
Clutch
number
Date of
oviposition
Clutch size
Mass (g)
Mean (range)
Length (mm)
Mean (range)
Width (mm)
Mean (range)
1
2
3
4
5
6
7
8
9
10
11
16/04/2002
31/05/2002
07/06/2003
18/07/2003
18/01/2004
02/03/2004
06/11/2004
10/01/2005
19/06/2005
07/08/2005
27/09/2005
16
20
23
20
23
19
22
6a
13
14
27
5.55 (4.72–6.08)
4.77 (4.38–5.10)
4.19 (3.81–4.55)
4.55 (4.35–4.88)
4.85 (3.85–5.51)
5.27 (4.71–5.79)
4.17 (3.44–4.83)
5.56 (5.10–5.80)
4.00 (3.00–5.00)
Not recorded
Not recorded
30.3 (28.5–31.4)
28.6 (27.0–31.0)
27.9 (26.1–30.7)
27.7 (26.8–30.6)
28.7 (26.0–30.5)
29.3 (23.0–31.9)
28.0 (25.1–29.7)
28.0 (23.0–31.1)
26.5 (22.8–30.7)
Not recorded
Not recorded
18.5 (17.6–19.3)
17.3 (17.0–18.0)
16.4 (16.1–17.2)
17.3 (16.6–17.9)
17.6 (16.8–18.2)
17.6 (15.5–18.5)
15.7 (11.1–17.0)
17.9 (17.3–18.3)
15.9 (14.1–17.9)
Not recorded
Not recorded
a
Suspected more eggs laid in the water and destroyed by turtles.
Fig. 5. (a) Hatchling Mitchell’s water monitor (V. mitchelli) with head protruded from a slit
in egg. (b) Juvenile Mitchell’s water monitor (V. mitchelli) 2 hr after hatching.
with 8–10 eggs half buried in each container. Lids were placed over the eggs and they
were aired daily for appropriate gas exchange.
Two clutches were maintained at 30–311C and hatched after 157–185 days. The
third clutch was maintained at 28–291C and hatched after 226–229 days and the
fourth clutch was incubated at 26–271C and hatched after 255–287 days. Clutch
hatching success was not measured because only the numbers required for Perth
Zoo’s animal collection were incubated, whereas the remaining eggs were discarded.
Eggs from clutch 2 were measured and numbered upon starting incubation and
approximately 8 days prior to hatching we found that the eggs’ width and weight had
increased (Po0.005), but the length was maintained (Fig. 1).
Hatchlings
Hatching was recorded in the months of September to January with peak
hatchings occurring in September and November. Pipping was observed at all hours
of the day but was primarily seen first thing in the morning during the first inspection
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Captive Breeding of Mitchell’s Water Monitor 623
(see Fig. 5a). This meant that pipping probably commenced sometime during the
night. Once pipping had started, juveniles emerged from the egg between 24 and
48 hr later (see Fig. 5b). Juvenile’s measurements (weight, TL, and SVL) were
recorded and can be seen in Table 2. Weight of the hatchlings ranged between 2.60
and 4.52 g, averaging 4.34 g (n 5 49). TL ranged between 140.1 and 178.0 mm,
averaging 165.9 mm (n 5 33), and SVL ranged between 53.8 and 70.0, averaging
64.4 mm (n 5 33). The weight of the hatchling reduced when incubation was
extended under lower temperatures. Eggs incubated at 30–311C had average juvenile
hatchling weights of 3.69 g, whereas those incubated at 26–291C had average
hatchling weights of 3.47 g (Po0.04). Hatchlings sloughed their skin for the first time
4–10 days posthatching and also began feeding within this time.
DISCUSSION
During the captive maintenance of Mitchell’s water monitors at Perth Zoo,
they were easily bred and kept in captivity. Although timid initially, adults settled
down and became good display animals within a multispecies exhibit. Minimal
health issues arose and injuries that did occur were often minor and required little
attention. Aggression observed was not considered to be any different from that seen
in normal monitor interactions. Observations of feeding and oviposition site
selection were similar to those described by Irwin [1996], although prior to the female
being provided with a nest box, eggs were deposited randomly around the enclosure
suggesting that no sites were preferred.
Captive reproduction was easily achieved in this species; indeed, the pair had to
be separated in order to stop producing clutches. Breeding behavior such as head
bobbing, nuzzling, and reproductive engagement was similar to that found in other
varanid species [Horn and Visser, 1997]. Double clutching was achieved on five
occasions. This is well documented in other species [Horn and Visser, 1989; Irwin,
1996]. A triple clutch was produced once. One clutch contained 27 eggs. This is more
than the maximum number previously reported for other members of the Odatria
group—21 eggs in V. semiremex [Jackson, 2005] and 18 eggs in V. accanthurus [Horn
and Visser, 1997]. Information from field studies suggests that clutch size ranges
from 7 to 12 [Schultz and Doody, 2004], which is considerably smaller than those
found in this study.
Temperature is important for hatching success. High or fluctuating temperatures
have been previously shown to result in poor hatching in V. primordius and
V. baritji [Husband, 2001]. In the absence of any previous reports of hatching in
captivity for V. mitchelli, eggs in this study were kept at three different temperatures of
26–27, 28–29, and 30–311C. Fortunately, healthy hatchlings were achieved at all
temperatures used, although longer incubation times occurred at lower temperatures,
which is consistent with observations on other varanid species [Horn and Visser, 1997]
and reptiles in general [Köhler, 2005]. Longer incubation times resulted in smaller
juveniles in weight with no ill effects. Lower weight is a result of additional stored
resources in the egg being metabolized by the neonate prior to hatching [Köhler, 2005].
The increase in egg weight prior to hatching in this study was the result of an
increase in width rather than length of the egg, increasing the overall volume of the
eggs. This is considered to be normal egg growth development [Köhler, 2005]. The
rate of growth of hatchlings varies considerably between species. This study showed
Zoo Biology
624 Gaikhorst et al.
Zoo Biology
TABLE 2. The incubation information and mass, snout–vent length, and total length (mean and range) of hatchlings from four clutches
Clutch
number
Oviposition
1
16/04/2002
2
31/05/2002
3
07/06/2003
5a
18/01/2004
a
Incubation time
(days) and
Dates of hatching
temp. (1C)
27/09/2002–21/
10/2002
03/11/2002–27/
11/2002
19/1/2004–22/1/
2004
30/9/2004–1/11/
2004
161–185 days
30–311C
157–181 days
30–311C
226–229 days
28–291C
255–287 days
26–271C
Number hatched
Snout–vent
length (mm)
Mean (range)
Total length (mm)
Mean (range)
Mass (g) Mean
(range)
at
N 5 16
Not recorded
Not recorded
3.74 (3.17–3.96)
at
N 5 18
64.7 (55.0–70.0)
166.3 (150.0–178.0)
3.65 (3.10–4.52)
at
N54
64.0 (62.0–66.0)
167.3 (161.0–170.0)
3.42 (3.28–3.55)
at
N 5 11
64.5 (53.8–70.0)
164.2 (140.1–173.5)
3.53 (2.60–3.85)
Growth measurement data in juvenile monitors were recorded from clutch 5.
Captive Breeding of Mitchell’s Water Monitor 625
an increase in daily weight for V. mitchelli of approximately 0.3 g per day (see Fig. 2).
This compares with weight increases of approximately 0.6 g per day for V. varius
[Boylan, 1995] and 6 g per day for V. komodoensis [Lemm et al., 2004]. Boylan [1995]
fed a range of food types in a similar method to this study suggesting a similarity in
the growth pattern. The difference in weight would be owing to the relative size of
the different species. Lemm et al. [2004] conducted their research on growth rates of
Komodo dragons using turkey mince as the base diet. This could have influenced the
growth rate of their study animals and explain the high rate of growth. The sizes of
the animals may also be a factor. V. mitchelli is very small compared with
V. komodoensis; therefore, the rate of growth in weight may be dramatically reduced.
In summary, this study has shown that V. mitchelli can be bred successfully in
captivity and provides data on breeding behavior, oviposition, egg incubation and
hatching, and the growth and development of hatchlings.
ACKNOWLEDGMENTS
We thank Ric Dunlop, Perth Zoo’s Supervisor of Reptiles, Helen Robertson
and John Lemon Curators (at the time) of Australian fauna, as well as Perth Zoo’s
Research and Ethics Committee for their assistance with the project. We also thank
Phil Matson for the supervision, assistance, and comments on the manuscript.
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