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Nutritional Quality of Natural Foods of Juvenile Desert Tortoises (Gopherus agassizii): Energy, Nitrogen, and Fiber Digestibility

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Wild Desert Tortoises, Gopherus agassizii, are eating different foods now than they were decades ago, because exotic plant species have invaded and flourished in the Mojave Desert over the last century. Reservations about the nutritional quality of exotic vegetation compared to native vegetation led us to conduct feeding experiments with growing, juvenile Desert Tortoises. We determined the digestibility of dry matter, energy, fiber, and nitrogen in four foods: Achnatherum hymenoides (a native grass), Schismus barbatus (an exotic grass), Malacothrix glabrata (a native forb), and Erodium cicutarium (an exotic forb). The largest nutritional differences among diets were between food types (fresh forbs and dry grasses) rather than between native and exotic species. The two grass diets were higher in fiber content and they contained less digestible energy than the two forb diets. The grasses contained little protein, and tortoises actually lost mass and body nitrogen while eating them. The exotic forb yielded more energy and nitrogen per unit dry mass than did the native forb, but this may be related to differences in phenological stages and associated fiber contents of these foods when they were collected. Juvenile tortoises gained weight rapidly when eating forbs and showed no evidence of having a lower digestive capability than did adults, despite their small size and immaturity. Estimates of nitrogen requirements compared to annual nitrogen intake on these diets suggested that growth of juveniles may be limited in part by dietary nitrogen.
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Nutritional Quality of Natural Foods of Juvenile Desert Tortoises
(Gopherus agassizii): Energy, Nitrogen, and Fiber Digestibility
LISA C. HAZARD,
1
DANIELLE R. SHEMANSKI,AND KENNETH A. NAGY
Department of Ecology and Evolutionary Biology, University of California, Los Angeles, 621 Young Drive South,
Los Angeles, California 90095-1606 USA
ABSTRACT.—Wild Desert Tortoises, Gopherus agassizii, are eating different foods now than they were
decades ago, because exotic plant species have invaded and flourished in the Mojave Desert over the last
century. Reservations about the nutritional quality of exotic vegetation compared to native vegetation led us
to conduct feeding experiments with growing, juvenile Desert Tortoises. We determined the digestibility of
dry matter, energy, fiber, and nitrogen in four foods: Achnatherum hymenoides (a native grass), Schismus
barbatus (an exotic grass), Malacothrix glabrata (a native forb), and Erodium cicutarium (an exotic forb). The
largest nutritional differences among diets were between food types (fresh forbs and dry grasses) rather than
between native and exotic species. The two grass diets were higher in fiber content and they contained less
digestible energy than the two forb diets. The grasses contained little protein, and tortoises actually lost mass
and body nitrogen while eating them. The exotic forb yielded more energy and nitrogen per unit dry mass
than did the native forb, but this may be related to differences in phenological stages and associated fiber
contents of these foods when they were collected. Juvenile tortoises gained weight rapidly when eating forbs
and showed no evidence of having a lower digestive capability than did adults, despite their small size and
immaturity. Estimates of nitrogen requirements compared to annual nitrogen intake on these diets suggested
that growth of juveniles may be limited in part by dietary nitrogen.
The species composition of plants is changing
in the Mojave Desert as exotic species invade
and flourish there (Brooks, 2000); nonnative
species now comprise 66%of the annual plant
biomass in wet years and 91%in dry years
(Brooks and Berry, 2006). These introduced
plants, especially the now-abundant Schismus
barbatus and Erodium cicutarium, are being eaten
by both juvenile and adult Desert Tortoises
(Gopherus agassizii) (Hansen et al., 1976; Nagy
and Medica, 1986; Barboza, 1995; Peterson,
1996b), and there is concern about the nutri-
tional quality of these plants (Nagy et al., 1998;
Oftedal, 2002). By consuming substantial
amounts of introduced vegetation, are juvenile
tortoises getting less of the nutrients, such as
nitrogen and energy, which they need for
growth? As grasses expanded in the beginning
of the Miocene, herbivorous rodent biodiversity
also expanded, indicating adaptation by these
mammals to this increasingly available, but
low-quality, food source (Stevens and Hume,
1995).
In this study, we examined the nutritional
quality of native and exotic plants eaten by
Desert Tortoises by conducting a series of
feeding experiments. We fed four separate diets
in turn to juvenile Desert Tortoises—two native
plants (one grass and one forb) and two exotic
plants (one grass and one forb). We measured
food intake, collected and analyzed the voided
feces, and estimated by difference the juvenile
tortoises’ abilities to digest and retain dry
matter, fiber, energy, and nitrogen (an index of
protein) from each food plant. We hypothesized
that, within food type, exotic plants would in
general have lower nutritional value than native
plants.
MATERIALS AND METHODS
Animals.—Twenty captive-bred neonate and
juvenile (0.5–1.5 yr old) Desert Tortoises (G.
agassizii) were donated or loaned by members of
the California Turtle and Tortoise Club. While
the housing status prior to donation was not
known for all animals, most were housed with
adult tortoises (often the parents) and, therefore,
would have had the opportunity for coproph-
agy of adult feces, with resulting inoculation of
their digestive tracts with beneficial gut mi-
crobes. The animals were allowed several weeks
to acclimate to the controlled temperature (24.5
61uC) and humidity (23 620%rh) in a
vivarium room at the University of California,
Los Angeles. Each tortoise was housed individ-
ually in a plastic bin (39 325 314 cm), which
contained a shelter (a 16-ounce cardboard soft
1
Corresponding Author. Present address: Depart-
ment of Biology and Molecular Biology, Montclair
State University, Montclair, New Jersey 07043, USA;
E-mail: hazardl@mail.montclair.edu
Journal of Herpetology, Vol. 43, No. 1, pp. 38–48, 2009
Copyright 2009 Society for the Study of Amphibians and Reptiles
drink cup cut in half vertically and laid on its
side, cut side down). A fluorescent ‘‘full
spectrum’’ lamp (Reptisun 5.0, Zoo Med Labo-
ratories, Inc.) was placed 25–30 cm above the
animals to provide the ultraviolet B light
necessary for vitamin D synthesis. Heat from a
25-watt spotlight placed at one end of each bin
provided a thermal gradient from 27.7–31.9uC
(on average) during daytime hours (0700–2100).
Diets.—Mediterranean grass (S. barbatus), an
exotic annual grass, was collected at Fort Irwin
near Barstow, California, and near Lancaster,
California. Indian rice grass (Achnatherum hyme-
noides), a native perennial grass, was collected at
Fort Irwin and near Phelan, California. Both
grass species were collected during early and
midsummer, after the grasses were brown and
dried, which is when wild tortoises eat them
(Nagy and Medica, 1986). Their digestibility
was measured during that autumn and winter.
Erodium cicutarium, or filaree, an exotic annual
forb in the geranium family, was collected near
Lancaster, and Malacothrix glabrata, or desert
dandelion, which is a native annual forb in the
sunflower family, was obtained in Yucca Valley,
California. The two forbs were collected several
times during the following springtime, when
green and succulent, and in the flowering and
early fruiting phenological stage. We collected
only those parts of food plants that juvenile
tortoises are known to eat (Oftedal et al., 2002).
Foods were sealed in plastic bags and placed on
ice during transport.
In the laboratory, the dry grasses were
chopped in a Wiley mill, sifted to bite-sized
pieces (2–4 mm in length), and stored in a
drying oven at 60uC until they were used. Forbs
were first cleaned of any remaining detritus,
chopped into bite-sized pieces with a sharp
French knife, placed into several small sealed
plastic bags, and refrigerated or frozen until
used. Periodically, we took samples from the
bag of green forbs currently in use for measure-
ment of water content (drying at 60uCto
constant mass). This allowed us to calculate
the amount of dry food matter offered to each
tortoise from measurements of the mass of fresh
matter offered each day.
Feeding Trials.—The 20 tortoises were sorted
into two groups of 10, each group having
similar means and ranges of body mass. For
the grass feeding trials, one group of 10 (mean
mass 83 644 g) was offered A. hymenoides, and
the other (mean mass 92 638 g) was given S.
barbatus. The tortoises given A. hymenoides
remained healthy during the 133-day trial.
However, two animals offered S. barbatus
became ill and died very early in the study,
and two others refused to eat and were
excluded from the experiment, resulting in a
total of six animals in that group. After the grass
trials were completed, all 16 remaining tortoises
were used for the two forb diets, which were
offered consecutively. Tortoises were first given
E. cicutarium, which was available in early
spring that year, for 90 days. Following the E.
cicutarium trial, M. glabrata was still unavailable
in the field, so the animals were given finely
chopped leaves of commercially available kale
(Brassica oleracea, a cabbage variant, in the
mustard family) for 20 days before starting the
90-day M. glabrata feeding trial. For grasses,
passage rate as determined by the throughput
times of bite-sized pieces of plastic surveyors
tape was long (mean 21 64 days, range 9–40
days). Therefore, lengthy trials were needed to
allow the tortoises to adjust to a new diet and to
ensure that the feces collected during a partic-
ular trial would be from the diet fed at that time.
In all trials, food was weighed (wet mass) and
placed in small, low-sided Petri dishes in each
animal’s bin daily. Feces were collected daily,
and uneaten food was collected every 10 days.
A tray, cut from a waxed paper cup and
designed to catch and hold excreta, was taped
to the posterior end of each tortoise’s plastron.
This facilitated collection of excreta and simpli-
fied clean separation of urinary wastes from
feces, it reduced opportunities for coprophagy
(consumption of feces) and contamination of
food with feces and urine, and it kept the bins
cleaner. Drinking water was offered to the
animals every 10 days, by placing them in a
bowl of shallow water for about 15 min, during
the last 50 days of the grass feeding trials and
during the last 40 days of the forb feeding trials.
Accurate dry matter digestibility (DMD;
grams retained/gram ingested) measurements
were critical, because digestibilities of all other
nutrients were calculated from these numbers.
Because tortoises may only defecate once every
few days, longer trial periods improve the
accuracy of the measurement of rate of feces
output. For the grasses, we determined that
trials of at least 125 days were needed to obtain
consistent and reliable results; shorter measure-
ment periods resulted in much higher variation
in DMD. For the forbs E. cicutarium and M.
glabrata, the last 40 days of the 90-day trials gave
consistent results and were used for DMD
measurements.
We initially used the ‘‘pulse’’ method to
measure digestibility. We force-fed six 1 33–
5 mm pieces of plastic tape to each tortoise
every 10 days, varying color each time, and
started new feces collection vials when the next
color tape was found in the feces. Therefore,
feces collection periods were not necessarily
congruent with ort collection periods. This
method provides a direct measure of the
DESERT TORTOISE NUTRITION 39
amount of dry matter retained by the animal
from the food eaten between markers. However,
it assumes that the markers provide a reliable
indicator of food passage (that is, they move
through the gut at the same rate as the food).
Plastic tape markers in this study did not track
food passage reliably, necessitating switching to
the ‘‘steady-state’’ method. In this method, the
amount of food eaten in a given time period is
measured, and the feces produced during that
same time period are collected. This requires the
assumptions that (1) the animals have not
become constipated or developed diarrhea
and, thus, have not produced more or less feces
than normal, and (2) the animals have not
grown substantially. An increase in size during
the trial would lead to an overestimate of DMD,
because of an increase in the total amount of
feces stored in the animal. This method also
requires that the feces being collected are from
the food type being tested. To ensure this, we
fed test diets for at least 30 days before
beginning sample collections. During the grass
trials, steady-state digestibility was measured
from the day the second or third marker was
recovered from each tortoise (start of a new
fecal vial) to the last day grass was fed, 18
January 2000. Therefore, the total length of the
period varied somewhat among tortoises (125 6
7 days).
To determine growth rate, tortoises were
periodically weighed, and shell dimensions
(carapace length, shell width between the fourth
and fifth marginal scutes, and maximal shell
height at the same distance from the anterior
end, Nagy et al., 2002) were measured. Both
mass and shell ‘‘volume’’ (length 3width 3
height, all in cm) changes were used as
measures of growth.
Sample Analyses.—Feces and duplicate sam-
ples of food were dried to constant mass at
60uC, and then homogenized in a SPEX mixer-
mill for chemical analysis. Energy contents of
subsamples of food and feces were measured at
UCLA with a Phillipson microbomb calorime-
ter, in which each food and feces sample was
analyzed in duplicate or triplicate, and using
benzoic acid as the standard. Subsamples that
differed by more than 1.5%were reanalyzed.
Fiber and nitrogen content in the food and feces
were determined at the Division of Agriculture
and Natural Resources Analytical Laboratory,
University of California, Davis. Total nitrogen
was determined via the combustion gas analyz-
er method (Dumas, 1981), and the ankom
method (Ankom TechnologyH) was used to
measure neutral detergent fiber (Van Soest,
1985). Some analyses required larger sample
mass than was available for some animals,
reducing sample sizes for energy content to
nine for M. glabrata, for nitrogen content to nine
for A. hymenoides, and fiber content to seven for
A. hymenoides, five for S. barbatus, and six each
for M. glabrata and E. cicutarium.
Data Analysis.—To examine nutrient digest-
ibility (amount of nutrient retained relative to
nutrient ingested) and availability (amount of
nutrient retained relative to amount of food
ingested), we constructed bicoordinate utiliza-
tion plots (Raubenheimer and Simpson, 1994),
and calculated ‘‘traditional’’ digestibilities for
individuals, for comparison with earlier papers
using this method. We expressed amounts of
nutrients ingested and retained as daily rates to
adjust for differences in trial duration. Slopes of
the utilization plots give values equivalent to
traditional apparent digestibility and availabil-
ity values. Slope data were statistically analyzed
using analysis of covariance, where the re-
sponse variable was nutrient retained and the
effect variables were diet, nutrient intake, and
diet 3nutrient intake interaction. P-values of
0.05 or less were considered statistically signif-
icant. A significant interaction term indicated
that diets had differing slopes (different digest-
ibilities or availabilities). The 95%confidence
intervals (standard error of regression coeffi-
cient xt
0.05[2], [n22]
) were then calculated for the
slope of each diet (Zar, 1984); diets with
nonoverlapping confidence intervals were con-
sidered to be significantly different from one
another. Statistical tests were performed using
JMP 5.0 for Mac (SAS Institute, Cary, NC) or
calculated according to Zar (1984).
Our measurements of digestibility are termed
‘‘apparent’’ digestiblities to indicate that we did
not measure ‘‘true’’ digestibilities, because feces
contain not only undigested nutrients, but also
nutrients from endogenous sources such as
mucoproteins, pancreatic and intestinal en-
zymes, sloughed epithelial cells, salivary, gas-
tric, and bile secretions, and bacterial nitrogen
and amino acids from the ileum (Caine et al.,
1999).
RESULTS
Food Composition, Intake Rates, and Tortoise
Growth Rates.—The energy contents of the four
diets were similar (Table 1), although desert
dandelion contained about 5%less, on a dry
matter basis (a significant difference), than the
other three foods. The forbs had about five
times more nitrogen in them than the grasses
(Table 1). About half of the dry matter in the
grasses was neutral detergent fiber, whereas
fiber content of the forbs was much lower, at
about 37%in desert dandelion and 19%in
filaree (Table 1).
40 L. C. HAZARD ET AL.
Food consumption rates (milligrams dry
food/day) were significantly correlated with
body mass for all four foods, and the relation-
ships were directly proportional (slopes of log-
transformed data not different from 1.0; Fig. 1).
Mass-specific intake rates were higher for forbs
than for grasses but did not differ within those
categories (Table 1).
Tortoises grew while eating both forbs; mean
growth rates for these foods did not differ from
one another (Table 1). Tortoises eating the
grasses did not grow but instead lost body
mass and shell volume at low but statistically
significant rates: mean rates of change of mass
and shell volume for each grass diet were
negative and significantly different from zero
rate of change but not different from one
another (Table 1). Tortoises were offered drink-
ing water periodically throughout all trials;
thus, decreases in body mass were not simply
the result of loss of body water while eating dry
grasses. Growth rate was positively correlated
with dry matter intake rate for the forbs, but
slopes for grasses did not differ from zero:
higher grass intake did not result in more
growth (Fig. 2).
Nutrient Digestibility and Availability.—For all
four diets, there was a close linear relationship
TABLE 1. Nutrient content (mg/g or kJ/g of dry food) of four food plants of juvenile Desert Tortoises and
rates of voluntary food intake and growth for captive juvenile Desert Tortoises consuming those foods. Native
grass: Achnatherum hymenoides. Exotic grass: Schismus barbatus. Native forb: Malacothrix glabrata. Exotic forb:
Erodium cicutarium. Within rows, significant differences between means (shown with SD in parentheses) are
indicated by different letter superscripts (ANOVA and Tukey’s t-tests). Negative growth rates for A. hymenoides
and S. barbatus were significantly different from zero growth.
Grasses Forbs
Native Exotic Native Exotic
Food composition
Energy (kJ/g dry matter) 17.2 (0.11)
a
17.4 (0.01)
a
16.6 (0.21)
b
17.5 (0.11)
a
Nitrogen (mg/g dry matter) 6.5 (0.45)
a
8.6 (0.31)
b
29.3 (1.4)
c
42.2 (0.87)
d
Fiber (mg/g dry matter) 498 (31)
a
501 (13)
a
367 (24)
b
192 (18)
c
Food Intake Rate (mg dry matter 3
[g body mass]
21
3day
21
) 1.65 (0.46)
a
1.43 (0.37)
a
4.05 (1.13)
b
5.22 (1.82)
b
Growth rate
%mass change 3day
21
20.045 (0.038)
a
20.043 (0.025)
a
0.139 (0.128)
b
0.162 (0.133)
b
%volume change 3day
21
20.027 (0.038)
a
20.040 (0.019)
a
0.126 (0.124)
b
0.164 (0.131)
b
FIG. 1. Relationships between food intake rates
(milligrams dry food/day) and body mass for juvenile
Desert Tortoises eating four foods. Slopes did not
differ from each other or from 1.0. Open circles: native
grass (Achnatherum hymenoides); open triangles: exotic
grass (Schismus barbatus); closed circles: native forb
(Malacothrix glabrata); closed triangles: exotic forb
(Erodium cicutarium).
FIG. 2. Relationship between growth rate and food
intake rate for juvenile Desert Tortoises. Open circles:
native grass (Achnatherum hymenoides); open triangles:
exotic grass (Schismus barbatus); closed circles: native
forb (Malacothrix glabrata); closed triangles: exotic forb
(Erodium cicutarium). Slopes for forbs were significant
and did not differ; slopes for grasses did not differ
from zero.
DESERT TORTOISE NUTRITION 41
between dry matter intake and dry matter
retained (Fig. 3). Slopes of the lines differed:
the digestibility of dry matter was significantly
lower in the grasses and M. glabrata than in the
exotic forb E. cicutarium (Table 2). Intercepts of
the regression lines for dry matter digestibility
and for nearly all nutrient digestibilities (with
the exception of S. barbatus nitrogen, see below)
did not differ significantly from zero.
Energy digestibility and availability were
very similar to dry matter digestibility and
were lowest in the grasses, moderate in desert
dandelion (although not significantly different
from the grasses), and highest in filaree, which
provided nearly twice as much energy per unit
dry food than did the grasses (Table 2).
The forbs were good sources of digestible
nitrogen. Nitrogen digestibility was 67%for
Malacothrix and 73%for Erodium and did not
differ significantly between the forbs (Table 2).
Nitrogen availability on a dry matter basis was
higher for Erodium because of the higher
nitrogen content of that food. When tortoises
ate the grasses, they actually lost more nitrogen
in their feces than they consumed in their food.
Therefore, nitrogen digestibility and availability
values were negative for the grasses, although
the slope for Achnatherum digestibility did not
differ significantly from zero (P50.056,
Table 2). Regression lines for Schismus nitrogen
digestibility and availability had y-axis inter-
cepts that differed from zero (y-intercept 6SE
50.478 60.125 for both lines). Nitrogen loss
increased with increasing dry matter intake
(Fig. 4), suggesting that nitrogen loss was not
simply a result of low amounts of food eaten.
Fiber digestibility tended to be higher in the
desert dandelion than in the other three diets,
but there were no statistically significant differ-
ences among diets (Table 2). Fiber availability
on a dry matter basis was significantly lower for
filaree than for desert dandelion and Schismus
because of the low fiber content of filaree;
Achnatherum did not differ from any of the
other three diets.
DISCUSSION
There are many ways to evaluate the nutri-
tional value of foods, ranging from their
proximate chemical composition to their eco-
logical importance to populations (Oftedal,
2002). We evaluated two nutritional parameters
in this study, digestibility (a relative index of the
animal’s ability to extract a nutrient from a
food) and availability (the amount of useable
nutrient an animal gets from one unit of a food)
for dietary energy, nitrogen (an index of
protein), and fiber. Each of these conveys
different information about the nutritional
value of these food plants for juvenile tortoises.
Exotic versus Native Species.—The native and
exotic grasses had similar energy, nitrogen, and
fiber contents, although nitrogen content was
slightly higher for Schismus (Table 2). Digest-
ibility and availability (dry matter basis) of
energy and fiber did not differ between the two
grasses; however, nitrogen digestibility and
availability (very low for both grasses) were
lower for Schismus than for Achnatherum (de-
spite the slightly higher nitrogen content of
Schismus) and was significantly lower than zero
only for Schismus. The overall nutritional value
of the grasses does not appear to differ. Nutrient
content of forbs was more varied, with Erodium
having more nitrogen, less fiber, and slightly
more energy per gram than Malacothrix.Erodium
had higher dry matter and energy digestibility
and availability, higher nitrogen availability,
and lower fiber availability than did Malaco-
thrix. The nutritional value of the forbs does
vary somewhat and is likely in part caused by
differences in fiber content (see below), not
necessarily because of differences in the geo-
graphic origin of the food.
Grass versus Forb Species.—Overall, the forbs
had higher nutritional value than the grasses.
The forbs provided juvenile tortoises with more
energy and nitrogen per unit dry food than did
the grasses. Desert dandelion yielded about 14–
21%more energy, and filaree provided about
46–56%more energy per gram DM ingested
than did the dry grasses. Tortoises gained
nitrogen rapidly (desert dandelion) or very
FIG. 3. Dry matter utilization plot for four foods
eaten by juvenile Desert Tortoises. Open circles: native
grass (Achnatherum hymenoides); open triangles: exotic
grass (Schismus barbatus); closed circles: native forb
(Malacothrix glabrata); closed triangles: exotic forb
(Erodium cicutarium). Slopes and statistics for regres-
sion lines are given in Table 2.
42 L. C. HAZARD ET AL.
rapidly (filaree) while consuming green forbs,
but lost nitrogen at low rates while eating dry
grass. Nitrogen loss increased with increasing
dry mass of grass consumed. In general, the
nutritional differences between grasses and
forbs are larger than any differences between
exotic and native species (Table 2; Fig. 4).
However, the grasses we used were dead and
dried, whereas the forbs were green and
growing when harvested. Thus, part of this
difference may be the result of the different
phenological stages of the grasses and forbs.
Fresh green S. barbatus contains more nitro-
gen than does dry senescent S. barbatus (Ofte-
dal et al., 2002), but in spring, tortoises often
ignore grasses and instead select green
forbs (Nagy and Medica, 1986; Henen, 1997;
Oftedal, 2002). Tortoises eating fresh green
S. barbatus were able to digest 63%of its dry
matter, 59%of its energy, and 54%of its
nitrogen and obtained 10.6 kJ of energy and
10.2 mg nitrogen per gram of dry food (calcu-
lated from values in Barboza, 1995). Thus,
grasses can yield just as much energy and about
30–55%as much nitrogen as do forbs when both
are consumed at an early phenological stage.
Tortoises in the western Mojave Desert may
select forbs in the spring to better obtain
nutrients other than energy (e.g., nitrogen,
water, phosphorus). In summer, dried grasses
provide energy but little else. In addition to
nitrogen loss, juvenile tortoises lose phosphorus
on these foods and gain other nutrients (e.g.,
calcium, magnesium) only at low rates (L. C.
Hazard, D. R. Shemanski, and K. A. Nagy,
unpubl. data).
TABLE 2. Digestibility and availability (dry matter basis) of nutrients in four diets eaten by juvenile Desert
Tortoises. Native grass: Achnatherum hymenoides. Exotic grass: Schismus barbatus. Native forb: Malacothrix glabrata.
Exotic forb: Erodium cicutarium. Slopes are the regression coefficients (digestibility or availability) for utilization
plots (Figs. 3 and 4), with standard errors (SE) and R
2
-values for the regressions. *, P,0.05. **, P,0.01. ***, P,
0.001. Ratios are the traditional ratio-based digestibility values (retained/ingested for each individual; mean
[SD]) for comparison with previous studies. Within nutrient categories, diets sharing a letter in superscript are
not significantly different (ANCOVA and nonoverlap of 95%confidence intervals for slopes; ANOVA and
Tukey’s t-tests for ratios). Data for adults are from Nagy et al. (1998) and Meienberger et al. (1993).
Nutrient Diet N
Nutrient digestibility (mg or kJ retained per mg or kJ ingested)
Slope (SE) R
2
Ratio (SD) Adult ratio (SD)
Dry matter Native grass 10 0.49 (0.05)
a
0.92*** 0.42 (0.10)
a
0.47 (0.05)
Exotic grass 6 0.50 (0.05)
a
0.96*** 0.45 (0.06)
a
0.50 (0.08)
Native forb 16 0.58 (0.02)
a
0.98*** 0.56 (0.04)
b
0.70 (0.03)
Exotic forb 16 0.70 (0.01)
b
0.99*** 0.71 (0.04)
c
0.63 (0.05)
Energy Native grass 10 0.48 (0.06)
a
0.91*** 0.39 (0.10)
a
0.46 (0.06)
Exotic grass 6 0.45 (0.05)
a
0.96*** 0.40 (0.06)
a
0.48 (0.08)
Native forb 9 0.57 (0.03)
a
0.98*** 0.51 (0.05)
b
0.73 (0.03)
Exotic forb 16 0.69 (0.02)
b
0.99*** 0.72 (0.05)
c
0.69 (0.05)
Nitrogen Native grass 9 20.23 (0.10)
b
0.43 20.31 (0.16)
a
0.07 (0.10)
Exotic grass 6 20.83 (0.10)
a
0.94** 20.32 (0.21)
a
20.07 (0.18)
Native forb 16 0.67 (0.02)
c
0.99*** 0.63 (0.05)
b
0.79 (0.01)
Exotic forb 16 0.73 (0.02)
c
0.99*** 0.75 (0.05)
c
0.72 (0.05)
Fiber Native grass 7 0.46 (0.12)
a
0.74* 0.27 (0.17)
a
Exotic grass 5 0.52 (0.03)
a
0.99*** 0.43 (0.06)
a
Native forb 6 0.76 (0.07)
a
0.97*** 0.67 (0.07)
b
Exotic forb 6 0.42 (0.11)
a
0.80* 0.52 (0.08)
b
Nutrient Diet N
Nutrient availability (mg or kJ retained per g dry matter intake)
Slope (SE) R
2
Ratio (SD)
Energy (kJ/g) Native grass 10 8.3 (1.0)
a
0.91*** 6.7 (1.8)
a
7.8 (1.0 )
Exotic grass 6 7.7 (0.8)
a
0.96*** 6.9 (1.0)
a
8.3 (0.3)
Native forb 9 9.4 (0.5)
a
0.98*** 8.4 (0.9)
b
11.4 (0.4)
Exotic forb 16 12.1 (0.3)
b
0.99*** 12.6 (0.9)
c
10.9 (0.4)
Nitrogen (mg/g) Native grass 9 21.5 (0.7)
b
0.43 22.0 (1.1)
a
0.3 (1.4)
Exotic grass 6 27.1 (0.9)
a
0.94** 22.8 (1.8)
a
20.5 (0.3)
Native forb 16 19.9 (0.6)
c
0.99*** 18.8 (1.4)
b
21.3 (0.4)
Exotic forb 16 30.8 (0.8)
d
0.99*** 31.5 (2.0)
c
18.1 (1.3)
Fiber (mg/g) Native grass 7 231 (61)
a, b
0.74* 136 (83)
b
Exotic grass 5 257 (13)
b
0.99*** 215 (28)
b
Native forb 6 278 (25)
b
0.97*** 245 (24)
b
Exotic forb 6 81 (21)
a
0.80* 99 (16)
a
DESERT TORTOISE NUTRITION 43
FIG. 4. Utilization plots for digestibility and availability of nutrients for four diets eaten by juvenile Desert
Tortoises. Open circles: native grass (Achnatherum hymenoides); open triangles: exotic grass (Schismus barbatus);
closed circles: native forb (Malacothrix glabrata); closed triangles: exotic forb (Erodium cicutarium). Graphs on left
show nutrient digestibility (nutrient retained vs. nutrient intake) and graphs on right show nutrient availability
(nutrient retained vs. dry matter intake). Inset graph for nitrogen shows digestibility data for grasses on an
expanded scale for clarity. Slopes and statistics for regression lines are given in Table 2. (A) Energy digestibility.
(B) Energy availability. (C) Nitrogen digestibility. (D) Nitrogen availability. (E) Fiber digestibility. (F)
Fiber availability.
44 L. C. HAZARD ET AL.
Fiber Effects.—Fiber in foods of herbivorous
animals provides energy directly to the intesti-
nal microbes which can ferment cellulose, and
the fermentation products also provide energy
to the host animal (Bondi, 1987; Dierick et al.,
1989; Baer et al., 1997a). In addition, the
intestinal microbes provide their host with other
nutrients, such as some vitamins. However, the
relative difficulty of digesting fiber can be
nutritionally disadvantageous when foods con-
tain relatively high levels of fiber (Swart et al.,
1993; Baer et al., 1997b; Souffrant, 2001). The dry
grasses contained much more fiber than did the
forbs (Table 1), and this probably accounts for
their relatively low energy availability values
(Table 2). The difference in fiber content of the
forbs likely reflects the different phenological
ages of the two species when they were
collected. Desert dandelion plants were difficult
to find that year, because of drought conditions,
but some were finally located in Yucca Valley,
along the southeastern margin of the Mojave
Desert. Although they were still flowering, by
then they were more mature and apparently
woodier when collected than was the filaree we
had harvested much earlier in the year. Also, to
have sufficient mass of Malacothrix to feed the
animals for the duration of the trial, we
included stems in the finely chopped food
given to the tortoises, whereas stems were
excluded for Erodium. In a previous digestibility
study on adult Desert Tortoises, desert dande-
lion and filaree had equivalent digestibilities
and availabilities of energy and nitrogen (Nagy
et al., 1998; see Discussion below). Moreover,
the dry matter digestibility of the desert
dandelion used in that study was 70%, which
is substantially higher than the 58%measured
for desert dandelion in this study. Dry matter
digestibility in the current study was negatively
correlated with dietary fiber content (R
2
50.995;
P,0.001; Fig. 5).
Juveniles versus Adults.—Digestibility and
availability of energy and nitrogen for juvenile
tortoises were comparable to values for adult
Desert Tortoises fed the same foods in previous
studies (Meienberger et al., 1993; Nagy et al.,
1998). Given that the juveniles we studied
weighed less than 10%of the adult tortoises
studied earlier, and that there are allometric
reasons to expect lower digestibilities in small
reptilian herbivores (Pough, 1973; Wilson and
Lee, 1974), it is perhaps surprising that juveniles
were able to digest dry matter, energy, and
nitrogen just as well as did adults on three of
the four diets (Table 2). The digestibility of
nutrients in Malacothrix was substantially lower
(by 12–17%) for juveniles, which is probably the
result of the greater fiber content and age of the
dandelion plants eaten by the juvenile tortoises
(see above). Food passage times in juveniles
eating dry grass averaged 21 64 days (range 9–
40 days), essentially (and surprisingly) the same
as adult passage time (about 22 days, range 15–
30, Meienberger et al., 1993). Thus, we find little
evidence that digestive physiology was influ-
enced by body mass within the range of masses
of the tortoises we studied (from the smallest
juvenile at 33 g to the largest adult at 4,440 g).
Growth.—Tortoises lost mass and shell vol-
ume when eating grasses but gained mass and
volume when eating forbs. This is partly a result
of the lower availability of nutrients in dry
grasses. However, voluntary intake rates for
grasses were far lower than rates for forbs
(Table 1). Tortoises eating grasses simply may
have not eaten enough dry matter to maintain
body mass. Meienberger et al. (1993) found that
adult tortoises eating dry S. barbatus grass ad
libitum also lost body mass and suggested that
their tortoises were unable to eat dry grass
quickly enough to maintain or gain body mass
because the physical structure of the grass filled
the gut lumen at a relatively low density of dry
matter compared to green leaves. However, our
results suggest that the dry grasses were
qualitatively different from the forbs. When
tortoises ate grasses, increased dry matter intake
resulted in greater loss of nitrogen (Fig 4) and
no mass gain (Fig. 2). Increases in dry matter
intake would also result in increased fecal dry
matter output. The endogenous secretions and
associated substances (e.g., mucous and
sloughed epithelial cells) necessary to physical-
ly eliminate the waste matter may contain
FIG. 5. Effect of dietary fiber content (mean 6SD
for duplicate samples) on dry matter digestibility
(DMD; utilization plot regression coefficient 6SE) for
four diets eaten by juvenile Desert Tortoises. Open
circle: native grass (Achnatherum hymenoides); open
triangle: exotic grass (Schismus barbatus); closed circle:
native forb (Malacothrix glabrata); closed triangle:
exotic forb (Erodium cicutarium). DMD 520.0006(mg
fiber/g dry matter) +0.808; R
2
50.995; P50.003.
DESERT TORTOISE NUTRITION 45
enough nitrogen to account for the nitrogen
loss, and this nitrogen would increase with
increasing food intake. Thus, it appears that
tortoises that eat dry grasses to obtain energy do
so at a substantial cost in terms of nitrogen and
probably water. This is consistent with other
studies that have shown that tortoises feeding in
the summer are in negative nitrogen balance
(Peterson, 1996a).
In free-living adult tortoises, body masses
change more rapidly and extensively in re-
sponse to variations in water balance than they
do to changes in energy balance (Nagy and
Medica, 1986; Henen et al., 1998); thus, a
correlation between dry matter intake and mass
change rates may be obscured in data from a
field population. However, tortoises in this
study should have been fully hydrated contin-
uously, because drinking water was offered
regularly. Our study reveals that juvenile
tortoises can grow rapidly (up to 0.5%of body
mass added per day) while they are eating
succulent green forbs.
Nitrogen Limitation.—Using published data,
we estimated the increase in total body nitrogen
during the second year of life for wild juvenile
tortoises, and compared it to estimated net
nitrogen intake when feeding on the diets
studied here. During the second year of a
tortoise’s life, total body mass increases from
35–54 g, and dry mass increases from 6.1–12.6 g
(Nagy et al., 1997). There are no available data
for nitrogen content of Desert Tortoises, but
protein content of reptiles averages 74.7%of dry
matter (Boyd and Goodyear, 1971). Assuming
that one sixth of the mass of the protein is
nitrogen, total body nitrogen would increase
from 758 mg to 1,575 mg during the second
year, a net gain of 817 mg. During that year, a
juvenile tortoise eats an estimated 96.8 g of food
(Nagy, 1972). Approximately 66%of this food is
eaten in the spring when green food is available,
and the remaining 34%is eaten during the
summer and is likely to be dried grasses.
Assuming a diet of native foods (Malacothrix
and Achnatherum), a tortoise would take in
1,274 mg of nitrogen in the spring but then lose
49 mg in the summer, for a net intake of
1,225 mg. Similarly, a tortoise feeding on exotic
species (Erodium and Schismus) would gain
1,968 mg nitrogen in the spring and lose
235 mg in the summer, for a net intake of
1,733 mg. These net intake estimates for native
and exotic diets are 1.50 and 2.12 times the
estimated requirement for growth, respectively.
This does not take into account loss of nitrog-
enous waste in urine as a part of normal protein
turnover, nor the importance of nitrogen as a
vehicle for excretion of potassium in an insol-
uble form (potassium urate salts) if high levels
of potassium are present in the food (Oftedal
and Allen, 1996). Therefore, the small margin of
safety above the estimated nitrogen require-
ment suggests that nitrogen is likely to be a
limiting nutrient for growing juvenile tortoises.
However, because the total amount of nitrogen
lost when feeding on grasses is small relative to
nitrogen gained in the spring, feeding on
nitrogen-poor dry grasses may still be beneficial
if other nutrients such as energy can be
obtained. Chuckwallas (Sauromalus obesus) are
known to store nitrogen when feeding on
succulent high-protein plants in spring, which
offsets losses when feeding on dry summer
foods (Nagy, 1975). Nitrogen is not necessarily
the only limiting nutrient for Desert Tortoises;
similar calculations for several minerals showed
that phosphorus is also obtained in amounts
just above estimated requirements (L. C. Haz-
ard, D. R. Shemanski, and K. A. Nagy, unpubl.).
There appeared to be few nutritional differ-
ences within food type (forb or grass) between
native and exotic plant foods fed to captive
tortoises. However, the broader context of the
ecology of the Desert Tortoise must also be
considered. The dominant invasive species,
Schismus spp., E. cicutarium, and Bromus rubens,
are increasing overall annual plant biomass but
with a reduction in native plant diversity,
possibly including preferred food plants of
Desert Tortoises (Brooks, 2000; Brooks and
Berry, 2006). If tortoises are forced either to
switch from native forbs to potentially less
nutritious exotic grasses or to spend more time
searching out the less available native forbs,
there may still be ecological or nutritional
consequences for animals in the wild. Addi-
tionally, the dramatically increased biomass of
invasive grasses, although potentially providing
additional food for tortoises and other herbi-
vores, also increases the frequency of wildfires
(Brooks and Esque, 2002), which may impact
tortoises directly through increased mortality or
indirectly through alterations to the Mojave
Desert ecosystem.
Acknowledgments.—We thank the California
Turtle and Tortoise Club and D. Morafka for
loaning us juvenile tortoises for this study. We
also thank the staff at the DANR Analytical
Laboratory at the University of California at
Davis for fiber and nitrogen analysis, and C.
Park and J. Nakai for their assistance with
animal husbandry. We especially thank D.
Morafka for his support and facilitation. Finan-
cial support and means were provided by the
Academic Senate and the Department of Ecol-
ogy and Evolutionary Biology of the University
of California, Los Angeles, and by the Director-
ate of Public Works (M. Quillman, Natural and
46 L. C. HAZARD ET AL.
Cultural Resources Manager) of the U.S. Army
National Training Center at Fort Irwin, Califor-
nia, via a contract with the California State
University, Dominguez Hills Foundation. The
UCLA Office for the Protection of Research
Subjects (ARC 98-160-02) approved this study.
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48 L. C. HAZARD ET AL.
... This difference can be explained by age, because younger animals have greater mass-specific metabolic rates which result in higher food intake in terms of body mass, in comparison to adults. Most previous studies that evaluated the temperature effect force-fed the animals, making it impossible to determinate voluntary food intake (Harlow et al. 1976;Hazard et al. 2009;Zimmerman and Tracy 1989). Studies of lizard, tortoise and turtle species (Carlos et al. 2016;De La Ossa et al. 2009;McConnachie and Alexander 2004;Waldschmidt et al. 1986) described significantly greater food intakes at higher temperatures due to increased metabolism (Bentley and Schmidt-Nielsen 1966), similar to the results reported in the current study with regard to mass-specific daily intakes of food, digestible nutrients and digestible energy in terms of metabolic body mass. ...
... Despite the temperature effect, the mean minimum retention time (4.6 days) was within the range reported for C. carbonaria (3.6-6.1 days; Madera-Vergara et al. 2010). In relation to maximum retention time, the mean value (10.9 days) was close to values reported for herbivorous reptiles (from 6.2 to 14.3 days; Barboza 1995a;Bjorndal 1987;Hatt et al. 2005;Hazard et al. 2009). ...
... Basic requirements to maintain an efficient gut microflora are body temperature (preferably high), constant food supply, slow passage of digesta, anaerobic conditions, gut pH control and removal of fermentation waste products (Bjorndal 1987). Greater fluctuations in environmental temperatures and long periods of hibernation and/or aestivation in some reptiles may make it difficult to maintain efficient microflora under those conditions, and re-inoculation by coprophagic behaviour may be necessary (Bjorndal 1987;Hazard et al. 2009), although the prevalence of this remains unknown. Temperature effects of enzymatic affinity have been described, such as increased proteolytic activity at preferred temperatures in carnivorous reptiles (Diefenbach 1975), decreased secretion of gastric juice at declining temperatures in herbivorous reptiles (Wright et al. 1957), and greater apparent digestive efficiencies of sugars and lipids at higher temperatures due to sugar-digesting enzymes and lipase activity (Beaupre et al. 1993;Harwood 1979) and bile acids secretion (Pafilis et al. 2007) in lizards. ...
Preprint
Full-text available
Temperature effect on digestive response is still unknown in most reptile species as is the case with the red-footed tortoise (Chelonoidis carbonaria). Hatchlings were fed with two diets, one high in fiber (14.16% crude fiber, 39.20% neutral detergent fiber dry matter basis, DMB) and one high in starch (27.71% DMB), housed at 30°C or 20°C, to evaluate the temperature effect on food intake (FI), digesta passage, apparent digestive efficiency (Da), and growth. At 30°C the animals showed higher FI and digestible energy (DEI), as well as metabolic mass-specific intake of digestible nutrients and energy (DEImm, 99.48±14.30 versus 43.18±17.26 kJ kg-0.86 day-1; P<0.001); daily gain (0.98±0.26 versus 0.32±0.11 g day-1; P<0.001), and growth of carapace length (0.25±0.05 versus 0.09±0.02 mm day-1; P<0.001) and width (0.15±0.03 versus 0.05±0.01 mm day-1; P<0.001). DEI at 30°C was expressed: (R2=0.67). Non-diet effect was observed on digesta passage, however, at 20°C the transit (5.50±1.36 versus 3.60±1.05 days; P<0.01) and retention times (13.80±1.29 versus 8.90±1.15 days; P<0.001) were longer than at 30°C. Animals housed at colder conditions also presented lower gut content (30.39±13.39 versus 40.45±9.76 g Kg-1; P<0.05) and gut fill time (0.08±0.01 versus 0.02±0.01 g day-1; P<0.001). Da were similar between temperatures but due to the diet effect, hatchlings fed the high starch diet presented higher DM and energy coefficients. Environmental temperature influences the digestive response and growth of C. carbonaria. Overall digestive efficiency was temperature-independent but rather influenced by diet quality and composition.
... Research on the digestibility and nutritional characteristics of potential plants available to wild desert tortoises provided answers to why tortoises selected and preferred certain species in altered habitats (e.g., . Barboza (1995), in experimental studies of feeding different diets to tortoises, reported loss of body mass from the grass diet, a finding later supported by feeding trials with both native and non-native annuals (forbs and grasses) for juvenile tortoises (Hazard et al., 2009;Hazard et al., 2010;Drake et al., 2016). Further, young tortoises gained weight and grew when eating forbs but did not thrive on either native or nonnative grasses (Hazard et al., 2009;Hazard et al., 2010). ...
... Barboza (1995), in experimental studies of feeding different diets to tortoises, reported loss of body mass from the grass diet, a finding later supported by feeding trials with both native and non-native annuals (forbs and grasses) for juvenile tortoises (Hazard et al., 2009;Hazard et al., 2010;Drake et al., 2016). Further, young tortoises gained weight and grew when eating forbs but did not thrive on either native or nonnative grasses (Hazard et al., 2009;Hazard et al., 2010). Jennings (2002) and Jennings and Berry (2015) detailed the preferences of wild tortoises for selected species of forbs and herbaceous perennial plants using observations of bite counts by species during a wet year. ...
... During years with high, above average precipitation, a high diversity of native annual species is likely to bloom and thus be available as potential forage for tortoises (SI-1). In contrast, in extremely dry years-such as occurred in 1989 and 2012-most annuals did not germinate, leaving tortoises with little or no available food-or only with poor quality non-native annual grasses (Hazard et al., 2009;Hazard et al., 2010;SI-1). ...
Article
Full-text available
Populations of the threatened desert tortoise (Gopherus agassizii) continue to decline throughout the geographic range, in part because of degraded and fragmented habitats in the Mojave and western Sonoran deserts. The species is herbivorous and highly selective in choice of plant species. To increase options for recovery, we analyzed behaviors, patterns of movements while foraging, and parts of plants consumed during a superbloom. We characterized foraging routes and the habitat strata and microhabitats where tortoises traveled to eat preferred wildflower species. Tortoises walked one foraging route per day in early spring, often switched to two routes per day in middle and late spring with rise of midday temperatures. They chose habitat strata (primarily hills and ephemeral stream channels) and three of seven microhabitats for foraging on preferred food plants. Preferred microhabitats were intershrub open space and small (1-2 m wide) ephemeral stream channels. They rarely took bites of forbs growing under and in the dripline of shrubs or nonnative forbs and grasses. Tortoises typically did not select specific plant parts to eat but important exceptions occurred. For example, they usually ignored the inflorescences of the annual Eremothera boothii and, when eating the non-native annual Erodium cicutarium, tended to focus on fruits. All such information aids recovery efforts to restore declining tortoise populations.
... This difference can be explained by age, because younger animals have greater mass-specific metabolic rates which result in higher food intake in terms of body mass, in comparison to adults. Most previous studies that evaluated the temperature effect force-fed the animals, making it impossible to determinate voluntary food intake (Harlow et al. 1976;Hazard et al. 2009;Zimmerman and Tracy 1989). Studies of lizard, tortoise and turtle species (Carlos et al. 2016;De La Ossa et al. 2009;McConnachie and Alexander 2004;Waldschmidt et al. 1986) described significantly greater food intakes at higher temperatures due to increased metabolism (Bentley and Schmidt-Nielsen 1966), similar to the results reported in the current study with regard to mass-specific daily intakes of food, digestible nutrients and digestible energy in terms of metabolic body mass. ...
... Despite the temperature effect, the mean minimum retention time (4.6 days) was within the range reported for C. carbonaria (3.6-6.1 days; Madera-Vergara et al. 2010). In relation to maximum retention time, the mean value (10.9 days) was close to values reported for herbivorous reptiles (from 6.2 to 14.3 days; Barboza 1995a;Bjorndal 1987;Hatt et al. 2005;Hazard et al. 2009). ...
... Basic requirements to maintain an efficient gut microflora are body temperature (preferably high), constant food supply, slow passage of digesta, anaerobic conditions, gut pH control and removal of fermentation waste products (Bjorndal 1987). Greater fluctuations in environmental temperatures and long periods of hibernation and/or aestivation in some reptiles may make it difficult to maintain efficient microflora under those conditions, and re-inoculation by coprophagic behaviour may be necessary (Bjorndal 1987;Hazard et al. 2009), although the prevalence of this remains unknown. Temperature effects of enzymatic affinity have been described, such as increased proteolytic activity at preferred temperatures in carnivorous reptiles (Diefenbach 1975), decreased secretion of gastric juice at declining temperatures in herbivorous reptiles (Wright et al. 1957), and greater apparent digestive efficiencies of sugars and lipids at higher temperatures due to sugar-digesting enzymes and lipase activity (Beaupre et al. 1993;Harwood 1979) and bile acids secretion (Pafilis et al. 2007) in lizards. ...
Article
Temperature effect on digestive response is still unknown in most reptile species as is the case with the red-footed tortoise (Chelonoidis carbonaria). Hatchlings were fed with two diets, one high in fiber (14.16% crude fiber, 39.20% neutral detergent fiber dry matter basis, DMB) and one high in starch (27.71% DMB), housed at 30°C or 20°C, to evaluate the temperature effect on food intake (FI), digesta passage, apparent digestive efficiency (Da), and growth. At 30°C the animals showed higher FI and digestible energy (DEI), as well as metabolic mass-specific intake of digestible nutrients and energy (DEImm, 99.48±14.30 versus 43.18±17.26 kJ kg-0.86 day-1; P<0.001); daily gain (0.98±0.26 versus 0.32±0.11 g day-1; P<0.001), and growth of carapace length (0.25±0.05 versus 0.09±0.02 mm day-1; P<0.001) and width (0.15±0.03 versus 0.05±0.01 mm day-1; P<0.001). DEI at 30°C was expressed: (R2=0.67). Non-diet effect was observed on digesta passage, however, at 20°C the transit (5.50±1.36 versus 3.60±1.05 days; P<0.01) and retention times (13.80±1.29 versus 8.90±1.15 days; P<0.001) were longer than at 30°C. Animals housed at colder conditions also presented lower gut content (30.39±13.39 versus 40.45±9.76 g Kg-1; P<0.05) and gut fill time (0.08±0.01 versus 0.02±0.01 g day-1; P<0.001). Da were similar between temperatures but due to the diet effect, hatchlings fed the high starch diet presented higher DM and energy coefficients. Environmental temperature influences the digestive response and growth of C. carbonaria. Overall digestive efficiency was temperature-independent but rather influenced by diet quality and composition.
... Tortoise habitats will gain from the reduction of non-native grasses and harmful non-native forbs (e.g., African mustard). Grasses, whether native or non-native, are poor forage and harmful for juveniles and all sizes of tortoises if forbs are not consumed as part of the diet (Hazard et al., 2009;Drake et al., 2016). Much of the geographic range, including the study area on EAFB, has invasive, non-native annual grasses, and African mustard has rapidly invaded parts of the Mojave Desert (Brooks and Berry, 2006;Minnich and Sanders, 2000). ...
... The situation is acute during drought years because nonnative species (e.g., Schismus spp., Bromus spp.) composed 91% of the biomass in dry years in the western Mojave (Brooks and Berry, 2006). Production of annual forbs following winter rains is essential for the growth of small tortoises: forbs provide energy, nutrients, and minerals (Nagy and Medica, 1986;Hazard et al., 2009;Hazard et al., 2010). The altered food supply, when coupled with prolonged years of drought, reduces the capacity of juveniles to grow and increases the time to reach sexual maturity. ...
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In the Mojave Desert, timing and amounts of precipitation profoundly affect the availability of water and annual plant foods necessary for the threatened Agassiz’s desert tortoise (Gopherus agassizii) to survive, especially during prolonged droughts. As part of recovery actions to increase declining populations, we translocated 83 juvenile and young desert tortoises raised in head-start pens for 4–10 years to a new location 15 km away during the fall of 2013 and 2014. We tracked them for 9 years during a megadrought, during multiple years of low rainfall, and a few years when precipitation neared or exceeded long-term norms. We evaluated behaviors and how precipitation and forage availability affected survival. At the end of the study, 21.6% of tortoises were alive, and six had grown to adulthood. Annual models of survival indicated that tortoise size was the driving variable in most years, followed by the number of repeatedly used burrows during periods of temperature extremes. Other variables affecting survival in ≥1 year were vegetation, movements during the first 2 years post-translocation, and condition index, a measure of health. Tortoises moved more, expanded home ranges, and grew rapidly in years when winter rainfall approached or exceeded long-term norms and annual plants were available to eat. During dry years, movements and growth were limited. Exceptions to this pattern occurred in the last year of study, a dry year: tortoises grew and moved more, and home ranges increased. The increase in size and approaching adulthood may have stimulated greater traveling. Some left the study area, indicating a need for large release areas. We may have aided survival by offering water twice yearly when handling because some tortoises drank and increased in mass up to 40%. Prolonged droughts and hotter temperatures can limit the recovery of populations, reduce the survival of young tortoises, and increase the time to maturity.
... The negative impacts on nutrition by tortoises eating poor-quality food plants were first illuminated in the studies by Meienberger et al. (1993) and Peterson (1996), each of which documented weight losses and negative nitrogen balances by adult desert tortoises following the consumption of dried grasses in summer. A more recent experimental study showed that juvenile desert tortoises also lost mass from eating dried grasses, yet juveniles gained mass when eating succulent forbs (Hazard, 2009). Once the nutrient composition of a plant is determined, challenges remain because relating the estimates for the various component nutrients (e.g., nitrogen, phosphorus) and physiologically relevant plant structures (e.g., fiber content) to tortoise nutritional requirements can be difficult. ...
... Once the nutrient composition of a plant is determined, challenges remain because relating the estimates for the various component nutrients (e.g., nitrogen, phosphorus) and physiologically relevant plant structures (e.g., fiber content) to tortoise nutritional requirements can be difficult. For example, the benefits of a large amount of a "good" nutrient such as nitrogen can Food Selection by a Desert Herbivore be offset by the presence of a large amount of a "bad" nutrient such as potassium or a high content of fiber can decrease the effective availability of a key nutrient even if the plant contains a high amount of this nutrient (Hazard, 2009). Despite these complications, these early nutritional studies are promising. ...
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A previous study on the feeding habits of Moorish tortoises in west-central Morocco suggests that these animals are selective herbivores, but the nutritional consequences have not been examined. Because of the potassium excretion load, which requires water and/or nitrogen loss, we predicted that tortoises do not have salt glands. Moorish tortoises prefer plants rich in water and protein but low in potassium (PEP index). To this end, we studied the spring diet of adult tortoises in an arid steppe in west-central Morocco during two seasons of relatively dry years (2011-2012) using feces analyses. We also estimated the relative abundance of potential food plants by stratified sampling under the canopy of jujube bushes Ziziphus lotus . We statistically compared diet to plant abundance. Finally, we assessed plant species’ nutritional composition (water, crude protein, and potassium) available to tortoises. Results showed that species assemblages differed significantly between the two plant communities in both years. Nevertheless, tortoises consumed only about 5-6 and nearly the same species at the study site in 2011 and 2012, respectively. The plants consumed by the tortoises had the highest positive PEP index values indicating that there was more water and nitrogen in the food than is needed to excrete potassium.
... Hazard and colleagues fed juvenile desert tortoises different diets of either grasses or forbes and found that the diets containing between 18 to 26% CP and 19 to 37% Fiber produced positive growth in the growing tortoises, while diets that were strictly grass and contained 4 to 5% CP and 49 to 50% Fiber were inadequate for growth and led to weight loss in the animals. 10 The animals fed the inadequate diet lost body mass and shell volume on these diets. As turtles mature, the amount of dietary protein required for maintenance decreases, allowing adult turtles to subsist on diets as low as 10 to 12% CP. ...
Article
Chelonian nutrition is still a young, but very important field of study. This article provides practical feeding advice for tortoises and freshwater and terrestrial turtles. Areas covered include the different feeding ecology of different types of chelonians, their digestive physiology, growth rate, body condition scoring, an overview of what types of diets items can be used in captive diets, and examples of diets used for various species of chelonians.
... Areas in this region with high NDVI values tend to be associated with high invasive grass cover and fire activity (Horn and St. Clair, 2017;Syphard et al., 2017;Underwood et al., 2019), so we suspect that NDVI better captured effects of invasive plant cover than did our variable of the number of pixels with >10% annual herbaceous vegetation. Invasive grasses are less nutritious to desert tortoises than native forbs (Drake et al., 2016;Hazard et al., 2009Hazard et al., , 2010Nagy et al., 1998), so high NDVI values may reflect areas with high invasive grass cover that have been abandoned by tortoises over time. ...
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Data from long‐term monitoring programs, such as the US Fish and Wildlife Service (USFWS) line distance sampling (LDS) program for Mojave desert tortoises (Gopherus agassizii), are increasingly being used in new ways to elucidate trends in population dynamics. We used the USFWS LDS data in a novel way to generate range‐wide predictions of occupancy, colonization, and local extinction rates from 2001 to 2018. We developed a dynamic occupancy model to answer fundamental questions posed by Bureau of Land Management personnel regarding how G. agassizii are distributed across the landscape over space and time. We transformed the LDS data into detection/nondetection data and constructed a Bayesian dynamic occupancy model using several time‐varying (e.g., temperature, precipitation, normalized difference vegetation index, fire, and a proxy for invasive grasses) and static covariates (e.g., soil properties, topography, distance to roads, distance to urban areas) hypothesized to influence G. agassizii occupancy dynamics. We estimated that over the entire time series (2001–2018) the probability of G. agassizii occupancy is declining in over one quarter (26%) of the range, largely in the northeastern part of the range, but that from 2011 to 2018, 77% of the range has a declining trend. Drawing on these model outputs, we developed an interactive, web‐based tool for exploring trends in dynamic occupancy across the species range, allowing users to focus on areas of management interest or concern.
... We counted multiple stems as a single plant if the stems bifurcated after exiting the ground. Because annual forbs may have more nutritional value for tortoises than grasses [39,40], we also calculated the proportion of annual stems that were grass (i.e., the fraction, by stem count, of the total number of annuals that were one or more annual grass species) or forbs. ...
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Animals may select habitat to maximize the benefits of foraging on growth and reproduction, while balancing competing factors like the risk of predation or mortality from other sources. Variation in the distribution of food resources may lead animals to forage at times or in places that carry greater predation risk, with individuals in poor quality habitats expected to take greater risks while foraging. We studied Mojave desert tortoises (Gopherus agassizii) in habitats with variable forage availability to determine if risk aversion in their selection of habitat relative was related to abundance of forage. As a measure of risk, we examined tortoise surface activity and mortality. We also compared tortoise body size and body condition between habitats with ample forage plants and those with less forage plants. Tortoises from low forage habitats selected areas where more annual plants were nutritious herbaceous flowering plants but did not favor areas of greater perennial shrub cover that could shelter them or their burrows. In contrast, tortoises occupying high forage habitats showed no preference for forage characteristics, but used burrows associated with more abundant and larger perennial shrubs. Tortoises in high forage habitats were larger and active above ground more often but did not have better body condition. Mortality was four times higher for females occupying low forage habitat than those in high forage habitat. Our results are consistent with the idea that tortoises may minimize mortality risk where food resources are high, but may accept some tradeoff of greater mortality risk in order to forage optimally when food resources are limiting.
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This datasheet on Erodium cicutarium covers Identity, Overview, Distribution, Dispersal, Hosts/Species Affected, Diagnosis, Biology & Ecology, Environmental Requirements, Natural Enemies, Impacts, Uses, Prevention/Control, Further Information.
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Captive chelonians should be fed a natural diet to achieve a growth rate similar to that of free-ranging animals. A wide range of commercially formulated foods dedicated to chelonians is available. Feeding commercial foods has the advantage of convenience. On the other hand, species-specific information on the nutritional requirements of chelonians is not available yet. The aim of this study was to analyse and evaluate commercial pellets and feeds for chelonians. Commercial pellets (ntortoise = 7, nturtle = 7, from 6 companies) dedicated to carnivorous aquatic turtles and herbivorous terrestrial tortoises, and other aquatic turtle feeds (lyophilised beef heart, dried aquatic invertebrates, and whole frozen fish) were bought in pet shops. Whole frozen fish served as a reference feed for carnivorous aquatic turtles. The chemical composition as well as calcium (Ca) and phosphorus (P) contents were determined. Single-sample t-test was used with the label information as null hypothesis and the results of own parallel analyses for crude protein (CP), ether extract (EE), crude fibre (CF), Ca and P. The labelling of some of the pellets was deficient as nutritive values, Ca or P data were missing (tortoise pellets: 4 out of 7; turtle pellets: 5 out of 7). The label data differed significantly (p<0.05) from the results of our own analysis for 13 out of the 14 pellets. None of the tortoise pellets met the requirements of the animals completely. Because of the inadequate Ca:P ratio only one turtle pellet could be accepted. Accordingly, none of the commercial pellets can be recommended as main or only feed. Key words: nutrition; pellet; metabolic bone disease; chelonian VREDNOTENJE KOMERCIALNIH ŽELV IN KRME ZA ŽELVE Izvleček: Želve v ujetništvu je potrebno hraniti z naravno krmo, da dosežejo podobno stopnjo rasti kot živali v prosti reji. Na voljo je širok izbor komercialno pripravljene hrane za želve. Prednost hranjenja želv s komercialno hrano je priročnost, vendar podatki o prehranskih potrebah za posamezne vrste želv še niso na voljo. Namen te raziskave je bil analizirati in ovrednotiti komercialne pelete in krmo za želve. V trgovinah za živali smo od 6 podjetij kupili komercialne pelete (npeleti za vodne želve = 7, npeleti za kopenkse želve = 7) za mesojede vodne in rastlinojede kopenske želve ter drugo krmo za vodne želve (liofilizirano goveje srce, posušene vodne nevretenčarje in zamrznjene cele ribe). Zamrznjene cele ribe smo uporabili kot referenčno krmo za mesojede vodne želve. Določili smo kemično sestavo in vsebnost kalcija (Ca) ter fosforja (P). Za ničelno hipotezo smo uporabili T-test enega vzorca s podatki na etiketi in rezultate lastne paralelne analize za surove beljakovine (an gl. crude proteins, CP), ekstrakt etra (angl. ether extract, EE), surovo vlaknino (angl. crude fibre, CF), Ca in P. Oznake nekaterih peletov so bile pomanjkljive, saj so manjkali podatki o hranilnih vrednostih, Ca in P (npeleti za kopenske želve = 4 od 7, npeleti za vodne želve = 5 od 7). Podatki na etiketi so se bistveno razlikovali (p < 0,05) od rezultatov naše analize pri 13 od 14 vrst peletov. Nobeni peleti za kopenske želve niso v celoti izpolnjevali potreb živali. Zaradi neustreznega razmerja Ca : P smo kot ustrezno določili le eno izmed 7 vrst peletov za vodne želve, zaradi česar nobenih od komercialnih peletov nismo določili kot priporočljivih za glavno ali edino krmo za želve. Ključne besede: prehrana; peleti; presnovna bolezen kosti; želve
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The total daily (24 hr) energy expenditure of the large (mean weight 240 g) herbivorous lizard Egernia cunninghami has been calculated, and partitioned into the daily costs of maintenance, food-gathering, and thermoregulatory activity. Energy expenditure was calculated from equations relating oxygen consumption rate to activity, body weight and body temperatures. Duration of activity was recorded for lizards of known weight observed continuously during daylight hours in the field. The daily cycle of body temperature of each observed lizard was assembled from the normal activity temperatures, heating and cooling rates and retreat temperatures. Although the weight-relative energy costs of maintenance and activity are much smaller for E. cunninghami than the 4 g insectivore Uta stansburiana, the cost per individual is considerably greater for the larger lizard. However, E. cunninghami is active for a much shorter portion of its time abroad (≤ 8%, ≤ 25 min day-1) than U. stansburiana (30%, 235 min day-1) and uses less of the total daily energy expenditure in activity (10% cf. 40%). The average duration of thermoregulatory movement was 2.6 min for E. cunninghami cf. at least 78 min for U. stansburiana. Little time is spent by E. cunninghami in foraging for the leaves and flowers of legumes; food-gathering effectiveness, the percentage of metabolized energy used for activities other than food-gathering, is estimated between 91 and 95%. It is suggested that the paucity of large carnivorous lizards results from the prohibitive costs of gathering vertebrate prey.
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How do female desert tortoises (Gopherus agassizii) reproduce every year despite variability in winter rainfall and food availability? To answer this question, I measured energy budgets of individual female desert tortoises from July 1987 to July 1989. Females produced eggs in years with low levels of winter annual plants by relaxing their control of energy and water homeostasis. They tolerated large deficits and surpluses in their body dry-matter composition (both nonlipid and lipid) on a seasonal, annual, and longer time scale. They could increase body energy content (lipid and nonlipid energy) before winter and use this reserve (especially nonlipid energy) the following spring to produce eggs. Females used high-protein foods and rainwater, when available, to achieve energy surpluses that helped them survive periods of low resource availability (e.g., during hibernation and droughts). Adjusting seasonal and annual field metabolic rates (FMR) and food requirements to levels of food availability, they still managed to produce eggs, even in a drought year. Egg production in 1988 (mean ± 1 SD: 3.56 ± 1.94 eggs, N = 9) did not differ from that in 1989 (3.00 ± 2.69 eggs, N = 9); both were lower than during 1983-1987 (6.75 ± 3.05 eggs, N = 100). Energy per se did not limit egg production in 1988 and 1989, but the availability of nonlipid energy (probably protein) limited egg production in 1988 and was limiting in spring 1989. Yet, water was the primary resource limiting egg production in 1989. Females forgoing egg production in 1989 accumulated body nonlipid energy and lost less total body water than did females producing eggs. Females that produced eggs in 1989 forfeited body nonlipid energy. In 1988 and 1989, the paucity of new annual plants in spring contributed to a lower egg production. The amount of annuals that germinate in summer can affect egg production, because females stored nonlipid energy during summer 1988 when eating these annuals, and allocated this energy to eggs in the following spring (1989). Tortoises stored lipids during summer when consuming dry annuals. These lipids are critical for surviving the winter, but females forfeited body water and nonlipid dry matter to digest the dry annuals. Reproductive effort (RE) was higher during the drought year (July 1988-July 1989: RE = 26.1%) than during the wetter year (July 1987-July 1988: RE = 13.0%) because tortoises reduced FMR by 70-90% in 1989. Compared to two other chelonians, RE of desert tortoises was consistent with the K-selected trend of lower RE for larger, long-lived, and late-maturing species. Forfeiting body condition to produce only a few eggs, even under a great environmental stress, was consistent with a life history strategy called bet hedging.
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1. We recommend the use of bicoordinate plots, termed utilization plots, for the analysis of nutrient budgets. 2. Utilization plots explore the relationship between nutrient uptake (intake or absorption from the gut) and the various compartments to which ingested nutrients are allocated. 3. They provide more information, and are numerically less problematic, than ratio-based nutritional indices.