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The
Effects of Developmental Temperature on Fecundity of Daphnia lumholtzi, an
Exotic Zooplankter
Denae
R. Nash1 and Charles L. Pederson2
1Biology
Department, Our Lady of the Lake University, San Antonio, Texas.
2Department
of Biological Sciences, Eastern Illinois University, Charleston, Illinois
Introduction
Daphnia
lumholtzi Sars is a species of crustacean
zooplankton native to Africa, India, and Australia that is believed to have been
introduced along with stocking of Nile perch into Fairfield Reservoir, Texas in
the early 1980s. Within two decades it has spread throughout most of the central
southeastern United States (Figure 1). Daphnia
lumholtzi typically have a late May appearance with a sharp midsummer
population peak. Like most exotics, this species usually invades disturbed
habitats which tend to have some other shared characteristics, including large
surface areas, high water clarity, relatively higher water temperatures, and
lower total phosphorus, and chlorophyll-a levels.
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Figure 1. Daphnia lumhotzi distribution
Courtesy
USGS |
Daphnia
lumholtzi
Daphnia
lumholtzi has extreme morphological features which may
interfere with feeding by natural predators. As a result, Daphnia lumholtzi may cause disruptions in the food
chain that could have serious ecological and economic implications.
Newton
Lake
Temperature
optima in excess of 25oC have been reported for Daphnia lumholtzi
by other investigators. Our objective was to investigate population dynamics of
this exotic zooplankter in Newton Lake (Figure 3),
a cooling lake for a coal-fired power plant in Jasper County, Illinois. This
reservoir has a surface water area of 667.7 hectares, a shore length of 94.9 km
and a maximum depth of 12.2 m. We sampled from 6 different location in the lake,
three from the warm arm and three from the cold arm (Figure
4).
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| Figure 3. |
Figure 4. |
Field
Sampling at Newton Lake
Every
two weeks from May 22, 2002 through July 3, 2002, two plankton samples were
collected from each site by doing vertical tows from surface to bottom with a
Wisconsin plankton net. Water samples also were obtained in order to determine
total phosphorus and chlorophyll-a levels. In addition, profiles of
temperature, pH, dissolved oxygen and light were made to determine the trophic
state of the lake and for consideration of variables that might affect
population dynamics of D. lumholtzi. During our six week sampling period,
trends in Newton Lake were towards lower total phosphorus concentrations,
relatively stable algal standing crop as indexed by chlorophyll-a, and
increased water clarity. Therefore, late in our sampling period Newton Lake
presumably became an ideal environment for D. lumholtzi and we would have
expected to see increasing population densities. However, by 3 July, D. lumholtzi
had disappeared from the Newton Lake zooplankton at all sites we had monitored (Figure
5).
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Figure 5. |
What
Happened to D. lumholtzi in Newton Lake?
While
other environmental factors tended more toward the presumed optimum, temperature
increased dramatically at all sites from 22 May through 3 July, 2002 (Figure
6). While gradual increase in temperature may have little impact on survival
of adults, a decline in fecundity may have resulted. We believe that individuals
may be acclimated to a relatively narrow temperature range while in the brood
chamber of their parent. We
predicted that upon "hatching," individuals placed outside this
temperature at maturity would experience decreased reproductive success. We
designed laboratory experiments to investigate the effects of temperature during
development and subsequent exposure temperature during maturation on life
history characteristics of adult Daphnia lumholtzi. We defined the
"developmental period" as time spent spent by offspring in the brood
chamber of an adult female and the "maturation period" as extending
from hatching through the end of the first adult instar, at which time either
ephippia were produced or a first clutch of neonates was released.
Methodology
Live
samples collected from the CA 2 site were maintained initially at 24oC
and then were split into 3 mass cultures grown at 23oC, 25oCand
28oC. From these mass cultures gravid females were put into
individual cultures to generate neonates for each of the three developmental
temperatures. Neonates which developed at each of these temperatures were
randomly assigned to one of three exposure temperatures (Figure
7). “Exposure organisms” were monitored daily and the following
data were recorded: mortality, age at first reproduction, number producing
ephippia or the number of neonates produced at the end of the first adult instar.
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Figure 7. |
Results
No
Mortality Observed Following Development at 25 oC.
Organisms
undergoing development at 25oC, experienced no mortality regardless
of subsequent exposure temperature (Figure 8).
However, mortality was observed in those individuals developing at 23oC
and 28oC suggesting that both 23oC and 28oC may
be stressful environments for D. lumholtzi.
Lower
Temperature During Development and Maturation Decreases Age at 1st Reproduction.
A
significant increase in age at first reproduction was observed in individuals
that developed at 23oC when compared to those which developed at 25oC
(p = 0.003) and 28oC (p = 0.0001). Differences in reproductive
maturity of individuals developed at 25oC and 28oC were
not significant (p > 0.05) (Figure 9).
Temperature
Moderation Delays Reproductive Maturity.
Two-factor
ANOVA revealed a significant increase (p = .024) in age at first reproduction in
individuals transferred to 25oC when compared to those transferred to
23oC, regardless of temperature during development. Time to
maturation was no different (p > 0.05) upon transfer to 28oC when
compared to that observed at the two lower temperatures (Figure
10). Interaction (p > 0.05) between independent variables was not
significant.
Development
at Moderate Temperature Increases 1st Clutch Size.
Exposure
temperature during maturation had no effect on clutch size. However, individuals
that developed at 25oC had significantly larger average
first clutch size (Figure 11) than those
which developed at 23oC (p = 0.016). Although the not statistically
significant (p > 0.05), clutch size also appeared to be decreased by
development at 28oC (vs. 25oC).
Elevated
Temperature During Maturation Increases Production of Ephippia.
Individuals
that were transferred to 23oC did not produce ephippia at maturity
regardless of the temperature regime during their developmental period. In
contrast, exposure to 28oC following development at lower
temperatures increased production of ephippia (Figure
12). A small number of individuals produced ephippia at maturity in 25oC
(one individual transferred from 25oC and one from or 28oC).
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| Figure 8. |
Figure 9. |
Figure 10. |
Figure 11. |
Figure 12. |
Conclusions
In
general, development at a moderate temperature (25oC) facilitates
survival regardless of the direction of temperature change during maturation,
whereas development at more extreme temperatures typically compromises adult
survival.
Exposure
to a moderate temperature (25oC) upon "hatching" results in
a significant delay in maturation, suggesting that individuals may forego
reproduction during periods of more benign environmental conditions. This delay
in reproductive maturity may be offset, at least in part, by production of
significantly larger clutches by neonates born to females at this temperature.
Although
development at extreme temperatures hastens reproductive maturity, these
individuals tend to produce smaller clutches of neonates at the end of the first
adult instar. Furthermore, individuals undergoing maturation at temperatures
above those at which they developed are more likely to produce ephippia at
reproductive maturity than are those in a cooler or more stable environment.
Production of fewer viable offspring, albeit earlier in the life span, may
precipitate a decline in population density when temperatures are increasing (or
decreasing).
Data
from laboratory experiments lead us to reject the null hypotheses that
developmental temperature and exposure temperature have no effect on fecundity
of D. lumholtzi. We believe that in situ population
dynamics may be explained by acclimation of individuals during the developmental
period (i.e., the time from deposition of eggs in the brood chamber of an adult
female to the release as neonates upon molting) as well as during the period of
maturation upon hatching.
Selected
References on Daphnia lumholtzi
Dzialowski,
A.R., O’Brian, W.J. and S. M. Swaffer. 2000. Range expansion and potential
dispersal mechanisms of the exotic cladoceran Daphnia lumholtzi.
Journal of Plankton Research 22(12):2205-2223.
Lennon,
J.T., Smith, V.H. and K. Williams. 2001. Influence of temperature on exotic Daphnia
lumholtzi and implications for invasion success. Journal of Plankton
Research 23 (4): 425-434.
Rawski,
E.L. 1997. Life history characteristics of Daphnia lumholtzi and its
susceptibility to an invertebrate predator. M.S. thesis, Eastern Illinois
University, Charleston, IL. 69 pp.
Work,
K.A. and M. Gophen. 1995. The invasion of Daphnia lumholtzi (Sars)
into Lake Texoma (USA). Arch. Hydrobiol. 133(3): 287-303.
Work,
K.A. and M. Gophen. 1999a. Factors which affect the abundance of an invasive
cladoceran, Daphnia lumholtzi, in U.S. reservoirs. Freshwater
Biology 43: 1-10.
Work,
K.A. and M. Gophen. 1999b. Environmental variability and the population
dynamics of the exotic Daphnia lumholtzi and native zooplankton in
Lake Texoma, U.S.A. Hydrobiologia 405: 11-23.
Acknowledgements
Assistance
in field collecting, experimental design and analyses were provided by Robert
Fischer, Scott Meiners, Brian Metzke, and Nick Owens (all of Eastern Illinois
University Department of Biological Sciences). Funding was provided by the NSF
Research Experience for Undergraduates and the Eastern Illinois University
Department of Biological Sciences.
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