Tortoise population dynamics serves as the key component of the overall model.
Inputs from the four other submodels coalesce in this section and determine the
potential impacts that different levels of habitat quality, and eventually training
impacts too, will have on the desert tortoise population at Fort Irwin. Because
the desert tortoise is both an endangered species and an indicator species for
desert ecological conditions, the information generated in this sub-model should
be valuable for developing effective management strategies.
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Approach -
Five "stocks" represent number of desert tortoises at different
stages of the life cycle. Factors such as birth, death, recruitment, and
mortality change the number of tortoises in each of these stocks, and these
influences vary in intensity depending on changes in habitat condition over
time. These five cohorts consist of eggs, hatchlings, juveniles, adults,
and elders, divided according to their age.
Only the female members of the tortoise population are represented in the
model. Four desert tortoise populations were analyzed and resulted indicated
that in all four populations the sex ratios were close to 1:1 (Berry, 1976).
Therefore, the total tortoise population is achieved by doubling the female
population total.
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Model -
Eggs
Tortoise births in the model take place as a result of adult and elder egg-laying
(elder tortoises are assumed to have a lower reproductive rate). Breeding
activities in the wild take place during the spring, with peak breeding
in March and June and eggs are laid in the model after a three month gestation,
during the months of May thru July (Luckenbach, 1981; Woodbury & Hardy,
1948). Research and observation of tortoises under natural conditions indicates
that females can produce either one or two clutches of eggs per year (Ernst
& Barbour, 1972; Luckenbach, 1981), but other research indicates not all
females lay a clutch every year (Hohman, Ohmart, & Schwartzmann, 1980).
This model assumes that on average each adult female lays 1.84 clutches
per season and, consequently, the model sub-divides the proportion of adult
tortoises that reproduce as the following: 100% of the population lay eggs
in May, 80% in June, and 4% in July. This assumption is based off of fieldwork
that found the percentage of reproductive females observed laying one clutch
was 100%, and 84% of females laid a second clutch during that same breeding
season (Turner, Berry, Burge, Hayden, Nicholson, & Bickett, 1984).
Clutch size averages from four to five eggs, although num bers as low as
two and as high as fourteen have been documented (Ernst & Barbour, 1972;
Luckenbach, 1981). The model assumes a correlation between tortoise condition
and habitat quality such that if the vegetative cover is sparse and water
availability low, fewer eggs will be produced; whereas, good habitat conditions
result in higher egg production levels--up to a maximum of fourteen eggs
per clutch per reproductive female (Hohman, et al., 1980).
While the literature provides some description of egg survivorship rates,
this information is not specific and assumptions have to be made about the
interaction and importance of different factors affecting egg mortality.
Research has found that "it is common for 50% of a clutch from desert
tortoises in captivity to be infertile, and similar losses may occur in
the wild" (Luckenbach, 1981), and that predation could account for
approximately 23% of prenatal mortality in one desert tortoise population
(Turner, et al., 1984).
Under natural conditions, incubation generally has been observed to vary
between 90 and 120 days (Luckenbach, 1981). As mentioned above, the model
assumes a 90 day incubation time. Immediately after eggs emerge from their
shells, they move into the hatchling cohort of the model.
Hatchlings
From the desert tortoise literature, the actual annual mortality rate of
hatchlings is not known (Turner, et al., 1984). So, like egg survivorship,
assumptions were made to calculate hatchling survivorship. Hatchling survival
depends on when the tortoises are hibernating or aestivating, predation,
and natural causes including inadequate food or water supply. With the exception
of eggs, all cohorts of tortoises hibernate and estivate (Medica, Bury,
& Luckenbach, 1980). Hibernation generally occurs during the fall and winter
in the months November through February (Luckenbach, 1981), and aestivation
usually occurs in midsummer when temperatures approach 39.5 degrees Celsius,
at which point tortoises would experience severe thermal stress and may
die if they do not seek shade or cooler temperatures of burrows (Luckenbach,
1981). The summer months associated with aestivation are June and July (Nagy
& Medica, 1986). Given the one month time-step, the model operates off of
the average monthly temperature which doesn't reach 39.5 degrees C during
the 20-year record, 1970-1990. Thus, estivation doesn't significantly influence
tortoise behavior within the model.
When not hibernating, hatchling mortality is the sum of the proportion that
die due to predation (we assume up to 32%) and natural causes, including
inadequate food or water supply (constant of 10% in all cells). Based on
the information that predation of young tortoises, and particularly hatchlings,
tends to be higher than predation on adults (Luckenbach, 1981), we assume
predation is a more important mortality factor. Under the best conditions,
a total of 85% of the hatchlings survive, and under the worst conditions,
a total of 58% survive. This gives some variation about the mean value of
79% used by Luke (Luke, 1987-1991), that we assume represents "average"
to "good" conditions. This number differs greatly from previous
estimates of 1-3% survival (Anonymous 1973 cited in Luke, 1987).
Tortoises remain in the hatchling cohort until their shells completely ossify,
which usually occurs when the tortoise is five years old (Luckenbach, 1981).
"Hatchling time" in the model is set accordingly. The reason for
basing the age-class division, the "hatchling cohort," on the
level of shell development is that a soft-shelled tortoise is much more
vulnerable to predation than a tortoise with a hardened shell (Luckenbach,
1981). For example, raven predation on desert tortoises is primarily restricted
to hatchlings whose shells are less than 110 mm maximum carapace length--in
other words, small tortoises with soft shells . So, higher mortality rates
distinguish hatchlings from the next cohort--juveniles.
Juveniles
Juvenile desert tortoises are those individuals who have ossified shells
but who have not yet reached sexual maturity. This indicates that predation
rates are lower in juveniles than hatchlings. Like the two preceeding cohorts,
the literature available doesn't offer substantial empirical descriptions
of survivorship within the juvenile population. Again, survivorship within
the model is based on our best assumptions. When not hibernating, mortality
is the sum of the proportion that die due to predation (we assume up to
22%), inadequate food (up to 4.4%), and inadequate water supply (up to 13.2%).
We also have added a constant proportion of 1.7% of juveniles die each month
(regardless of the season) due to diseases (frequency of disease has been
assumed to be density-independent in another model--see Luke, 1990 p. 256).
Under best conditions, a total of 87.1% of juveniles survive and under worst
condition a total of 38.9% survive. This gives some variation about the
mean value of 83% used by Luke (1990), which we assume represents "average"
to "good" conditions. During hibernation, a constant 2.7% die--due
to disease (1.7%) and other unknown factors (1%; undocumented).
Juveniles usually mature into adults sometime between the ages of fifteen
and twenty, though it can take more or less time depending on habitat conditions
(Woodbury & Hardy, 1948). The model assumes an average recruitment rate
of 17.5 years. Juveniles enter the next cohort, adults, at 22.5 years of
age.
Adults
Total adult mortality has been estimated to be between 1% and 2% per year
(Luckenbach, 1981; Turner, et al., 1984), and as a result, is lower than
the mortality of younger tortoises. Yet to complete the adult survivorship
functions, we made assumptions about mortality based on predation, food
and water supply, disease, and other natural causes. "Adult_Survive"
is calculated the same way as the juvenile survivorship rates. The only
differences between the adult and juvenile rates are that predation of juveniles
is higher than adults. Tortoises remain adults until 62.5 years. All surviving
adults older than 62.5 years move into the final cohort, elders.
Elders
This is the second adult cohort in the model, and the reason for dividing
the adult population in this way is to distinguish between those mature
individuals who can reproduce, and those who are reproducing but at a generally
lower rate, the elder tortoises. In the model, elders can survive up to
ten years. The maximum age that can be reached by a tortoise in our model
is about 75 years, which is supported by the literature on desert tortoises
(Turner, et al., 1984).