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First published online August 22, 2008
Journal of Experimental Biology 211, 2773-2778 (2008)
Published by The Company of Biologists 2008
doi: 10.1242/jeb.019133
Methyl farnesoate couples environmental changes to testicular development in the crab Carcinus maenas
Department of Biology, University of Central Florida, Orlando, FL 32816, USA
* Author for correspondence (e-mail: dborst{at}mail.ucf.edu)
Accepted 16 June 2008
| Summary |
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Key words: methyl farnesoate, testis, crustacean, salinity, reproduction, temperature
| INTRODUCTION |
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|
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A useful model system for such studies is the green crab (also known as the
shore crab) Carcinus maenas, an abundant crustacean found in rocky
intertidal zones (Menge,
1995
). This species was introduced to the East Coast of North
America from Europe in the early nineteenth century and reached the West Coast
approximately 20years ago (Cohen et al.,
1995
). These euryhaline crabs can tolerate a wide range of
salinities (1.4–52 ppt salinity) and temperatures (0–30°C)
(Crothers, 1968
;
Cohen et al., 1995
). Most
importantly, many of the eyestalk neuropeptides in this species have been
identified (Webster, 1998
),
and hemolymph levels of MF can be manipulated by salinity
(Lovett et al., 2001
).
C. maenas can have a range of colors on its ventral surface (e.g.
light green, yellow, orange and red). Nevertheless, these crabs are usually
divided into two groups: green-phase crabs and red-phase crabs
(Kaiser et al., 1990
;
McKnight et al., 2000
). As one
of these colors is the green phase, we will refer to individuals of C.
maenas hereafter simply as `crabs' to avoid the cumbersome term
`green-phase green crabs'.
These color phases differ substantially in terms of their physiology and
behavior. Green-phase animals tend to be smaller than red-phase animals and
molt more frequently. However, after they become red-phase animals, they molt
infrequently (Kaiser et al.,
1990
; McGaw et al.,
1992
; Reid et al.,
1997
; Wolf, 1998
).
Red-phase crabs are generally more sensitive to environmental stress than
green-phase crabs; they extract oxygen from seawater less effectively and are
less tolerant of hypoxia (Reid and
Aldrich, 1989
). Red-phase crabs are less effective osmoregulators
and have higher mortality rates when exposed to low salinity seawater
(Reid et al., 1989
;
McGaw and Naylor, 1992a
;
McGaw and Naylor, 1992b
).
However, red-phase animals are more robust (thicker carapace, larger chela
muscles) and aggressive and have greater mating success than green-phase
animals. These, and other observations, have led to suggestions that the two
color phases represent a trade-off between molting and mating. Green-phase
crabs put most of their resources into rapid growth but when they become
red-phase crabs they put most of their resources into reproduction
(Reid et al., 1997
).
These physiological and behavioral differences affect the environments the
crabs inhabit. Red-phase animals tend to live in deeper water along open
shores where the water is cooler and is closer to full-strength seawater. By
contrast, green-phase crabs migrate into inlets and estuaries during high tide
during the summer (Crothers,
1968
; Hunter and Naylor,
1993
; Warman et al.,
1993
). Thus, green-phase animals are more likely to experience
higher water temperatures and brackish water during the summer compared with
red-phase crabs.
In the present study, we show that red-phase crabs are more likely to have detectable MF in their hemolymph than green-phase crabs. In addition, the testicular index (TI) of red-phase animals is higher than that in green-phase animals. Furthermore, our results indicate that environmental factors differentially affect MF levels in the two color phases. These results are consistent with the hypothesis that MF stimulates testicular development. To test this hypothesis, we show that environmental factors that increase MF levels also stimulate testicular development. The MF levels in these two color phases appear to be responsible, in part, for the different reproductive activities of these males.
| MATERIALS AND METHODS |
|---|
|
|
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Treatments
For some experiments, crabs were given a hyposalinity challenge by placing
them in dilute SW (5 ppt) at 11 or 18°C for 24 h. MF levels were analyzed
by taking hemolymph samples (0.5 ml) immediately prior to the transfer and 24
h later at the end of the challenge. Studies with [14C]inulin
indicate that the hemolymph volume of these animals ranges from 20 to 25% of
their wet body mass (G.P.C.N. and D.W.B., unpublished data), hence 0.5 ml of
hemolymph is approximately 4% of the crab's total hemolymph volume. Previous
studies demonstrate that MF levels are not affected by this sampling frequency
or volume (Lovett et al.,
2001
). Some animals were bilaterally eyestalk-ablated (ESA) by
removing the eyestalks and then applying boric acid powder and Vaseline®
to the wound. Animals were anesthetized on ice for at least 10 min prior to
surgery or dissection. These animals were bled one day prior to ESA and then
at the indicated times after ESA. Some animals were bled sequentially but
never more frequently than 24 h.
Measurement of methyl farnesoate (MF) levels
Hemolymph levels of MF were determined using a high-performance liquid
chromatography (HPLC) method that has been previously described and validated
for C. maenas (Borst and
Tsukimura, 1991
). Briefly, hemolymph (0.5 ml unless otherwise
noted) was withdrawn through the arthrodial membrane of the coxa of a walking
leg. It was added to 2.5 ml acetonitrile and 4% NaCl to give a total volume of
4.5 ml. The mixture was extracted with 1.5 ml hexane containing 20 ng of
cis,trans-MF (used as an internal standard) and the hexane
supernatant was analyzed by normal-phase HPLC (silica column; 1.9% diethyl
ether in hexane; 220 nm). We calculated the MF content of each sample by
comparing its MF peak area with that of an MF standard. The lower limit of MF
detection was 2 ng ml–1.
Effect of salinity, temperature, ESA and MF treatment on testicular development
Male green-phase crabs were acclimated to 33 ppt SW at 11°C for at
least one week. As stress often causes a small transient rise in MF levels
(Lovett et al., 2001
), the
handling of these animals was limited and they were not bled. Some males were
treated with 1 µg MF (Echelon Biosciences; Salt Lake, UT, USA). As MF is
hydrophobic, we limited adsorption loss by suspending it, immediately prior to
injection, in modified Pantin's saline
(Laufer et al., 1987
)
containing 5% ethanol and 1% bovine serum albumin (BSA; Sigma-Aldrich Chemical
Co., St Louis, MO, USA). Control animals were treated with the vehicle
solution. MF and vehicle-treated animals were injected with 200 µl of the
solution, through the arthrodial membrane of the coxa of the third walking
leg, on days one, five and 10. The TI values of these animals were determined
on day 15.
In a second experiment, males were treated with temperature, hyposalinity or ESA. Group 1 crabs (the initial control) were dissected on the first day of the experiment. Crabs in group 2 (intact) and group 3 (ESA) were maintained in 33 ppt SW at 11°C. Crabs in groups 4 and 5 were held in 18°C SW with a salinity of 33 ppt or 5 ppt, respectively. Animals from groups 2–5 were dissected on day 15, and their TI values were determined. No deaths or injuries occurred during the experiment.
Statistical analysis
The data were analyzed using Instat Software (GraphPad; San Diego, CA,
USA). A two-tailed t-test was used to compare MF levels between the
two different treatment groups. For data expressed as the percentage of a
population, Fisher's exact test was used. Data with multiple groups were
analyzed by one-way analysis of variance (ANOVA) followed by the
Student–Newman–Keuls test to determine significance.
| RESULTS |
|---|
|
|
|---|
|
|
Since acclimation to SW at 18°C might induce the enzymes of the MF synthetic pathway, we also investigated the effect of ESA on red- and green-phase males in 33 ppt SW at 11°C. Red-phase males were analyzed for MF approximately one week prior to ESA, and only those animals that had no detectable MF were included in this study. None of the animals in either color phase had detectable MF in hemolymph samples taken one day prior to ESA, whereas every animal in both groups had detectable MF 24 h after ESA. The MF levels of green-phase males (6.2±0.9 ng ml–1, N=6) 24 h after ESA were significantly (P<0.001; t-test) lower than the levels observed in red-phase males (21.8±5.3 ng ml–1, N=5). However, MF levels in green-phase males rose over time and on day 5 reached a level that was similar to the levels observed in red-phase males (Fig. 3A).
|
The above data indicate that environmental factors (e.g. temperature and salinity) can affect MF production in C. maenas. We tested the potential impact of such factors on male reproduction. Green-phase males were initially housed in 33 ppt SW at 11°C. In one study, MF levels were increased by injecting males with 1 µg MF on days one, five and 10 while control animals were treated with the vehicle (Fig. 4A). By day 15, the TI of the MF-treated animals had increased by 119% (P<0.01; t-test). The TI of these treated animals was similar to the TI observed earlier in red-phase males (Fig. 1B).
|
| DISCUSSION |
|---|
|
|
|---|
Red-phase males were much more likely to have MF in their hemolymph
compared with green-phase animals. This observation correlates with the high
TIs of red-phase animals, consistent with the idea that MF stimulates
testicular growth either directly or indirectly in crustaceans
(Kalavathy et al., 1999
;
Nagaraju et al., 2003
;
Nagaraju et al., 2006
;
Reddy et al., 2004
). These
observations are similar to previous studies in the spider crab (Libinia
emarginata), which demonstrated a correlation between the reproductive
status of males and MF synthesis by the mandibular organ (MO) and hemolymph
levels of MF (Sagi et al.,
1993
; Sagi et al.,
1994
). It should be noted that the correlations between MF levels
and male reproduction are weak, since the majority of the red-phase males do
not show detectable MF but still have a high TI. The most likely explanation
for this is that the spontaneous release of MF is episodic
(Borst and Tsukimura, 1992
) and
the half-life of MF is short. In the lobster Homarus americanus, we
estimated that the half-life of MF is less than 60 min
(Tsukimura and Borst, 1992
).
However, a sustained elevation of MF does not appear to be necessary for a
biological effect. MF treatments, such as those shown in
Fig. 4A, would only cause a
transient elevation of MF in these animals. Nevertheless, this treatment still
affected testicular growth significantly.
Our data show that the two color phases differ profoundly in their
responses to temperature and salinity. Previous studies showed that MF levels
in C. maenas males increase when animals are exposed to dilute SW for
more than 8 h (Lovett et al.,
2001
). In the Lovett et al. study, only green-phase animals were
used because red-phase animals gave inconsistent results. These observations
were confirmed by the current study. Untreated red-phase animals often have
detectable MF, and the levels in these animals were similar to the levels
observed in animals that responded to low salinity. Another significant
difference between the two color phases is the temperature dependence of their
response to a hyposalinity challenge. Red-phase males responded to a challenge
at both temperatures (11 and 18°C) whereas green-phase males were only
responsive at 18°C.
Eyestalk removal has been shown to increase MF levels in a wide variety of
crustaceans, including L. emarginata
(Laufer et al., 1987
),
Cancer pagurus (Borst et al.,
2002
), Callinectes sapidus
(Henry and Borst, 2006
) and
Oziotelphusa senex senex
(Nagaraju et al., 2005
).
Consistent with these observations, ESA increased MF levels in both green- and
red-phase C. maenas males at 11°C. Clearly, green-phase animals
can synthesize MF when held at 11°C. Thus, their lack of a response to
hyposalinity at 11°C does not reflect an inability to produce MF.
Nevertheless, the levels of MF observed in green-phase males 24 h after ESA
were significantly lower than those observed in red-phase males. This suggests
that the initial synthesis capacity of green-phase males is not as great as it
is in red-phase males. The difference in MF levels between green- and
red-phase animals disappears 5 days after ESA. This probably reflects the
hypertrophy of the MO, which is known to occur after ESA
(Borst et al., 1994
;
Nagaraju et al., 2004
).
Although a hyposalinity challenge had no significant effect on the MF levels of green- or red-phase animals after ESA, there was a modest effect in SW at 18°C. This suggests that the eyestalk is the major regulator of MF levels in response to salinity. By contrast, temperature significantly affected the MF levels of ESA animals. It is unclear whether this is due to a temperature effect on overall metabolism or to a regulatory mechanism that is eyestalk independent.
Several compounds may regulate MF production by the MO, some of which are
found in the eyestalk. Indeed, the simplest explanation for the elevation of
MF levels of C. maenas, and other crustaceans, after ESA is that the
eyestalk contains a compound that directly inhibits MF production by the MO.
Several putative MO-inhibiting hormones (MOIHs) have been isolated from the
sinus glands of C. pagurus
(Wainwright et al., 1996
) and
L. emarginata (Liu and Laufer,
1996
). Although these peptides can decrease MF synthesis by MO
in vitro, they have not been shown to function as MOIHs in
vivo. Indeed, relatively large amounts of both peptides are required to
inhibit the MO in vitro, arguing against their role in regulating
this gland in vivo. The sinus glands of C. pagurus and
H. americanus contain another, as yet unidentified, peptide that
inhibits MF production in vivo but does not appear to act directly on
the MO (Borst et al., 2002
). In
addition, allatostatin has been shown to stimulate MF production by MO in
vitro (Kwok et al.,
2005
), although it has not been shown to affect MF production
in vivo. Clearly, more work needs to be done before we fully
understand the mechanisms involved in regulating MF synthesis by this
tissue.
Our present study provides strong evidence that MF has an important role in
regulating male testicular development. A role for MF in male reproduction has
been inferred from several previous studies. For example, the size of the MO
in the male lobster (H. americanus) increases after sexual maturity
(Waddy et al., 1995
).
Likewise, MF synthesis rates by spider crab MO incubated in vitro
were correlated with reproductive behavior
(Sagi et al., 1993
;
Sagi et al., 1994
). In
addition, MF treatment has been shown to increase testicular growth in a
number of crustacean species, including the freshwater field crab O. senex
senex (Kalavathy et al.,
1999
; Reddy et al.,
2004
), and the freshwater prawn Macrobrachium
malcholamsonii (Nagaraju et al.,
2003
). Our observations confirm these previous studies and
demonstrate that MF treatment can stimulate testicular growth in green-phase
animals.
The eyestalk is also known to regulate testicular function in crustaceans.
tsu found that the removal of eyestalks from young male Potama
dehaani resulted in a rapid increase in the size of the testes and male
genital ducts (
tsu,
1961
). Likewise, ESA of Litopenaeus vannamei increased
their testicular index and doubled mating frequency
(Chamberlain and Lawrence,
1981
). These, and other, studies have led to the proposal that the
eyestalk contains a gonad-inhibiting hormone (GIH)
(Kulkarni et al., 1984
;
Ye et al., 2006
). In the
present investigation, we demonstrate that ESA stimulates testicular growth in
green-phase males of C. maenas. As ESA increases MF levels, and MF
treatment alone can stimulate testicular growth, it seems likely that MF
couples ESA to gonad growth in these animals. However, it should be noted that
the green-phase males used in this study were large and were presumably
nearing sexual maturity. If so, their responses to environmental conditions
and other treatments may be different from the responses that would occur in
younger (smaller) green-phase males. At younger stages, ESA may affect
testicular development via mechanisms that do not include MF.
Finally, our present data show that environmental factors, such as
temperature and salinity, can affect MF levels and thereby stimulate
testicular growth. During the summer, green-phase animals are abundant in
estuaries (Crothers, 1968
;
Hunter and Naylor, 1993
;
Warman et al., 1993
), where
the water is likely to be brackish and warmer. Thus, it seems likely that
green-phase crabs will have a larger TI at the end of this season. Whether
green-phase crabs seek an estuarine environment because it stimulates MF
production and thereby increases gonad growth is not clear. Nevertheless,
these observations provide a unique insight into how behavior, the environment
and physiology might interact in the reproductive strategies of this
crustacean. Determining these interactions will afford a more comprehensive
view of how reproduction is regulated in this species and probably other
crustaceans.
| Acknowledgments |
|---|
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