Exploring Biotic Impacts from Carcinus maenas Predation
and Didemnum vexillum Epibiosis on Mytilus edulis in the
Gulf of Maine
Linda A. Auker, Alison L. Majkut, and Larry G. Harris
Northeastern Naturalist, Volume 21, Issue 3 (2014): 479–494
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2014 NORTHEASTERN NATURALIST 21(3):479–494
Exploring Biotic Impacts from Carcinus maenas Predation
and Didemnum vexillum Epibiosis on Mytilus edulis in the
Gulf of Maine
Linda A. Auker1,*, Alison L. Majkut1,2, and Larry G. Harris3
Abstract - Mytilus edulis (Blue Mussel) is an ecologically important species in the Gulf of
Maine. However, many introduced species that have a direct negative impact on the Blue
Mussel have entered this system, some as predators (e.g., Carcinus maenas [Green Crab])
and others as aggressive epibionts (e.g., Didemnum vexillum [Carpet Sea Squirt]). Didemnum
vexillum has been increasing in abundance throughout the Gulf for the past 10 years
and form large mat-like growths on mussel beds, covering individual mussels completely.
The first part of our study used a predator-exclusion experiment to determine the impact
of predators on the plantigrade stage of the Blue Mussel life cycle. During this stage, no
epibiosis occurs due to a protective periostracum layer on the mussel shell. The second part
of our study used laboratory trials to assess how overgrowth by D.vexillum impacts predator
choice, handling time, and consumption of mussels. There were a significantly greater
number of Blue Mussel plantigrades on exclusion panels than on the exposed-cage control
panels. Green Crab and Nucella lapillus (Dog Whelk) predators were present on our nonexclusion
panels. In laboratory trials, Green Crab handling time of Blue Mussels was not
significantly different between mussels that were clean and mussels that were overgrown,
but crab behavior and overall consumption showed a greater selection for clean mussels.
This selection indicates an associational predator-resistance effect of D.vexillumt epibiont
on Blue Mussels. The results of our study, while focused on one specific predator species,
suggest that while young Blue Mussels with no epibionts are preyed upon heavily,
D.vexillum likely deters predators from older mussels. Because D.vexillum form large matlike
colonies that can cover a large area, their presence may have a significant impact on
community structure in the Gulf of Maine.
Introduction
Epibiosis and predation
The overgrowth of one living organism by another is known as epibiosis. Both
the overgrown organism (the basibiont) and the overgrowing organism (the epibiont)
are impacted by this relationship, as are other organisms that attempt to interact
with the basibiont (Buschbaum et al. 2007, Enderlein et al. 2003, Wahl 1989). Basibionts
may gain advantages from the relationship (mostly in the form of protection
from predation), but frequently suffer significant disadvantages (Burlakova et al.
2000; Buschbaum and Saier 2001; Haag et al. 1993; Ricciardi et al. 1995; Thieltges
2005; Wahl 1989, 1997). Such disadvantages may include decreased buoyancy
1Department of Biology, Siena College, 515 Loudon Rd., Loudonville, NY 12211. 2Boston
Heart Diagnostics, 175 Crossing Boulevard, Framingham, MA 01702. 3Department of
Biological Sciences, University of New Hampshire, 38 College Road, Durham, NH 03824.
Corresponding author - lauker@stlawu.edu.
Manuscript Editor: Melisa Wong
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of the basibiont, hindered motion, damage to surfaces, reduction of diffusion of
soluble materials, and direct competition with the epibiont (Wahl 1989).
Epibiosis can alter predator–prey relationships by creating a new interface on the
prey (Wahl et al. 1997). That is, predators may attack or avoid the epibiont leading
to profound positive or negative effects on the basibiont. When epibiosis changes
predator responses, it does so through either associational resistance or shared doom
(Wahl and Hay 1995). Associational resistance occurs when an epibiont deters
predator attacks, thus reducing the risk to itself and the basibiont host (Laudien
and Wahl 1999, Marin and Belluga 2005, Thieltges 2005, Thornber 2007, Vance
1978, Wahl and Hay 1995). This situation typically occurs when epibiont species
mask chemical cues from the basibiont (Wahl et al. 1997), or repels the predator
through chemical deterrence (Laudien and Wahl 2004, Wahl et al. 1997). Shared
doom occurs when predators consume the epibiont, resulting in either incidental or
deliberate consumption of the basibiont host (Buschbaum et al. 2007, Enderlein et
al. 2003, Farren and Donovan 2007, Wahl et al. 1997, Wahl and Hay 1995). In the
case of shared doom, epibionts may enhance attractive chemical cues (Wahl et al.
1997) or improve prey handling (Enderlein et al. 2003).
Mytilus edulis L. (Blue Mussel) is an important ecological species and a dominant
member of consumer-regulated stable communities in the Gulf of Maine
(Bertness et al. 2002). Blue Mussels are both a food source for multiple organisms
(Clark et al. 2006, DeGraaf and Tyrrell 2004, Field 1922, Norberg and Tedengren
1995, Shumway and Stickney 1975), and ecosystem engineers that form complex
mussel-bed habitats (Jones et al. 1994, Tsuchiya and Nishihira 1986). A positive
relationship has been shown between habitat complexity and biotic diversity (Dean
and Connell 1987).
The diversity of organisms associated with mussel beds includes several epibionts,
such as attached barnacles, hydroids, and algae (Suchanek 1978). Epibionts
become more common on individual Blue Mussels as they age and the antifouling
shell layer, or periostracum, sloughs off (Bers and Wahl 2004, Bers et al. 2006).
This sloughing typically occurs after juvenile Blue Mussels move from filamentous
algae, where they develop from plantigrade larvae, to mussel beds where they grow
into the adult stage (Bayne 1964).
The invasive ascidian Didemnum vexillum (Kott) (Carpet Sea Squirt) is an abundant
invasive species in the Gulf of Maine that readily colonizes living organisms,
including Blue Mussels, as an epibiont (Auker 2006, 2010; Auker and Oviatt 2008).
This species likely came from Asia as an epibiont on Crassostrea gigas (Thunberg)
(Pacific Oyster) imported to the Damariscotta River estuary in the 1950s (Dijkstra
et al. 2007, Lambert 2009). Didemnum vexillum was first documented in the estuary
in 1993, but anecdotal evidence indicated its presence since the late 1970s (USGS
2013; L.G. Harris, pers. observ.). Didemnum vexillum has also colonized other temperate
coastal environments on the east coast of the United States, including Cape
Cod (Carman and Grunden 2010) and Rhode Island (Auker and Oviatt 2008), and
continues to spread worldwide (USGS 2013). Didemnum vexillum has been increasing
in abundance throughout the Gulf for the past 10 years, forming large mat-like
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growths on Blue Mussel beds, covering individual Blue Mussels completely (L.
Auker, pers observ).
Didemnum vexillum is in a family of ascidians (Didemnidae) that are known to
possess antipredatory chemical defenses, either in the form of secondary metabolites
(Blunt et al. 2006, Lindquist et al. 1992, Prado et al. 2004, Vervoort et al. 1998)
or inorganic acids (Stoecker 1978, Stoecker 1980, but see Parry 1984). As a result,
fouling by D. vexillum may reduce predation on organisms that they overgrow.
There is concern that invasive species may reduce, or otherwise alter, the role of
ecosystem engineers, which in turn may negatively impact the surrounding ecosystem
(Crooks 2002). Blue Mussels in the Gulf of Maine are controlled by predators
including introduced crab species, e.g., Hemigrapsus sanguineus (De Haan) (Asian
Shore Crab) and Carcinus maenas L. (Green Crab) (DeGraaf and Tyrrell 2004, Tyrrell
et al. 2006). If overgrowth of Blue Mussels by D. vexillum prevents predation
on Mussels, this could have severe implications for both the mussels and the Gulf
of Maine ecosystem.
This paper will focus on how mussels are impacted by predation at two different
life stages—plantigrade Blue Mussels that have no epibionts and adults that have
been colonized by the invasive D. vexillum. The first goal of this study was to examine
the impacts of predation on a life-history stage of Blue Mussels that have no
epibionts, the plantigrade stage. Our second goal was to understand the impacts that
D. vexillum has on predation by a common Gulf of Maine predator, Green Crab, and
to determine whether the effect of D. vexillum overgrowth is one of associational
resistance or shared doom.
Methods
Predator-exclusion experiment
To test the effects of predation on newly settled plantigrade Blue Mussels,
we designed and deployed collectors (artificial turf doormats covering 5-cmlong
PVC pipes with a 2-cm diameter; modified from collectors used in Brenner
and Buck 2010, Harris et al. 2004, Walter and Liebezeit 2003) with and without
predator-exclusion cages. Exclusion panels consisted of five 50-cm-long artificial
turf mussel-collectors covered with 5-mm mesh. Control panels consisted of 5
uncovered turf panels. Cage controls consisted of five 5-mm mesh-covered turf
panels with large openings (approximately 200 cm2) cut in the mesh. We deployed
collector panels at the Hampton River Marina in Hampton, NH, off the side of a
floating dock where the water depth ranges 1.5–2.1 m, the average salinity ranges
29–31 psu (Deacon and Nash 2002), and the average water temperature was 1.7–2.8
°C (NOAA 2014). We suspended the panels about 1 m below the dock from 25 February
to 17 March 2012. After 3 weeks, we retrieved and disassembled the cages,
and thoroughly rinsed the turf panels with tap water in order to remove organisms
present on the panels. We placed all objects removed from the turf into a gridded
petri dish, and identified and counted all organisms. Our data satisfied the assumptions
for normality and equal variances, so we used a one-way analysis of variance
(ANOVA) and Tukey’s post-hoc test to determine if there were differences in newly
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settled (postlarval) Blue Mussel abundance among treatments. We also scored the
types and numbers of predators present, and we used a one-way ANOVA to determine
differences in predator presence among treatments.
Epibiont experiment
We collected Blue Mussels (mean shell length = 26.4 mm, SD = 3.1 mm) and
D. vexillum from underneath floating docks in New Castle, NH. We collected female
Green Crabs (mean carapace width = 37.1 mm SD = 5.2 mm) from intertidal areas
in New Hampshire and Rhode Island. We kept all animals except D. vexillum in a
closed, temperature-controlled (15 °C) system at the University of New Hampshire.
We fed the Green Crabs a maintenance diet of Blue Mussels every 2–3 days until one
week before the experiments, at which time we stopped feeding them. We collected
D. vexillum from floating docks immediately before all experiments to ensure the
organisms’ optimal health. Our experiments took place from late summer to mid-autumn
when D. vexillum is metabolically active in the Gulf of Maine (Dijkstra 2007).
Handling time and prey selection. For each trial, we filled a large basin (34 cm
x 43 cm x 11.5 cm deep) with sea water (salinity = 32 psu), placed a Sony®
Handycam
DCR-SR47 digital video camera on a tripod (55.5 cm to base of camera), and
aimed it at the basin. We placed 1 Blue Mussel with 90–100% D. vexillum cover
and 1 clean Mussel without D.vexillumcover on opposite corners at the far end of
the basin from the camera. Recording began as soon as a naïve Green Crab was
placed in the basin. Once we added the Green Crab, the set-up was left undisturbed
and the Green Crab was allowed to explore the basin at will for 30 minutes. At
the end of the 30-minute period (one trial), we recorded the type of Blue Mussel
ultimately consumed—overgrown or clean. If both Blue Mussels were consumed,
then we recorded the outcome as consumed. We completed 29 trials, all of which
were conducted during the day. We played back videos in a VLC Media Player
(VideoLAN 2009) and recorded measurements for each of the following variables
for each trial: (1) initial selection of Mussel as indicated by which the Green Crab
first approached; (2) handling time for each clean and each overgrown mussel,
and for D. vexillum alone (if it was removed from the Blue Mussel); and, (3) final
Blue Mussel selection as indicated by Blue Mussel consumed. Our data satisified
the assumptions for normal distribution and equal variances; thus, we conducted a
one-way ANOVA and Tukey’s post-hoc test to determine if significant differences
existed in handling time.
Consumption. For each trial, we filled two 10-gallon aquaria with seawater. One
aquarium contained 30 Blue Mussels free of epibionts. The second aquarium contained
30 Blue Mussels that were overgrown with D. vexillum. We added 6 Green
Crabs to each aquarium and left them undisturbed for 24 hours at 15 °C. After 24
hours, we removed the Green Crabs, isolated them in their respective groups, counted
the Blue Mussels consumed in each aquarium, and replenished each aquarium with
Blue Mussels to the original sum of 30 individuals. To see if the Green Crabs limited
their feeding due to satiation or because they were deterred by the overgrowth
of D. vexillum, we placed the Green Crabs in the treatment tanks opposite the one
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in which they fed in the previous 24 hours (i.e., control crabs were placed with
overgrown mussels, and vice versa). We again left these crabs to feed for 24 hours
undisturbed. At the end of this second period, we counted the number of Blue Mussels
consumed. We completed 5 trials and used new Green Crabs for each trial. We
conducted a paired t-test on the proportion of clean and overgrown Blue Mussels
consumed by each group of crabs.
Results
Predator exclusion
We observed significantly more Mussel plantigrades on exclusion panels
than on control or cage control panels (F2,12 = 6.78, P = 0.011; Fig. 1). A
Tukey’s HSD post-hoc test showed that there were significant differences between
the cage control treatment and the exclusion treatment (P = 0.015) and
between the control treatment and the exclusion treatment (P = 0.027). The
Figure 1. Effects of predator exclusion on settlement of Blue Mussel plantigrades in Hampton,
NH, in spring 2012. Error bars represent ± 1 standard error. The control cage (n = 5)
and no cage (control) treatments (n = 5) showed similar results (P = 0.95), indicating that
the cage construction had little effect on Blue Mussel settlement on the turf panels. The
panels in which predators were excluded (n = 5) showed significantly more settlement of
larvae (F2,12 = 6.78 P = 0.011), indicating that predators may be having a significant impact
on Blue Mussel survival at an early stage of the bivalve’s life-history.
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control and cage control treatments showed no significant differences in postlarval
abundance (P = 0.95). Therefore, the cage did not impact predation on the
postlarval mussels.
Mussel predators found on the panels in the cage control and control treatments
were Green Crabs and Nucella lapillus L. (Dog Whelk) (Fig. 2). Predators
were abundant on both the control and cage control panels but rare on the
exclusion panels (F2,12= 3.411, P = 0.067). Green Crabs (n = 1) and Atlantic Dog
Winlkes (n = 5) found on the exclusion panels were small enough to enter the
mesh surrounding the panel.
Figure 2. The number of predators found on turf panels in Hampton, NH, in spring 2012.
Error bars represent ± 1 standard error. The predators found were the Green Crab (crabs)
and the Dog Whelk (snails). The control (n = 5) and cage control treatments (n = 5) were
similar in having the greatest number of predators per panel upon retrieval. While the exclusion
cages (n = 5) had fewer or no predators, the difference between these panels and
the control panels was not significant, due to a large amount of variation among the panels
(F2,12= 3.411, P = 0.067).
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Handling time and selection experiments
More overgrown Blue Mussels were initially approached in selection experiments,
but more clean Blue Mussels were ultimately consumed; some overgrown
mussels (5 out of 29) were also consumed (Table 1). Green Crabs that initially approached
clean Blue Mussels only consumed clean Mussels, whereas Green Crabs
that approached overgrown Blue Mussels consumed either clean or overgrown Blue
Mussels (Table 2).
In 13 trials, Green Crabs approached the overgrown Blue Mussel first. However,
instead of attacking the Blue Mussel immediately (which Green Crabs did when
they approached clean Blue Mussels), the Green Crabs picked up D. vexillum and
moved it towards its own mouthparts as if it were assessing the ascidian. The ascidian
was never actually consumed, because within seconds after picking it up, the
Green Crab discarded it The result of this action was that the Green Crab removed
the ascidian from the Blue Mussel, creating a Blue Mussel identical to the control,
or clean, Blue Mussel. Every consumed Blue Mussel that was initially overgrown
had its ascidian epibiont removed by the Green Crab.
Green Crabs in 9 trials of our study showed no interest in either Blue Mussel
during either initial approach or final consumption. In 5 of these trials, they only
responded to the ascidian epibiont. In one of these trials, the Green Crab spent 39
s handling D. vexillum, and the rest of the trial attempting to escape the basin. In
other cases, the Green Crab spent from 12–161 s handling the ascidian, while ignoring
the Blue Mussels for the rest of the trial. In 4 trials, the Green Crab showed no
response to either Blue Mussel or D. vexillum.
The average time Green Crabs spent handling clean Blue Mussels (mean =
417 s, SD = 563 s) was not significantly different than time spent handling overgrown
Blue Mussels (mean = 251 s, SD = 425 s) (t56 = 1.265, P = 0.211; Fig. 3).
An average of 62 s (SD = 96.4 s) was spent handling just D. vexillum; this was
significantly less handling time than for either the clean or overgrown Blue Mussel
(F2,85 = 3.269, P = 0.043).
Consumption experiments
Crabs consumed more clean Blue Mussels than overgrown Blue Mussels
(Fig. 4). A paired t-test indicated a significant difference between the proportion of
clean Blue Mussels consumed in the first 24 hours and the proportion of overgrown
Blue Mussels consumed in the second 24 hours by the same crab group (t4 = 3.328,
P = 0.029). Green Crabs that were initially placed with overgrown Blue Mussels in
the first 24 hours of the experiment consumed significantly more clean Blue Mussels
in the second 24 hours (t4 = 3.766, P = 0.020).
Green Crab behavior in this experiment was consistent in each trial. Green
Crabs placed in tanks with overgrown Blue Mussels typically pulled off D. vexillum
before consuming the Blue Mussel. If the ascidian was growing in such a
way that it was difficult to remove, then that Blue Mussel was generally ignored.
Many of the untouched Blue Mussels in the overgrown tanks were heavily covered
with the ascidian.
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Table 2. Outcomes of Green Crab initial selection of clean or overgrown Blue Mussels. Crabs initially approaching clean mussels finally consumed clean
mussels or no mussels, whereas crabs that initially approached overgrown mussels finally consumed nothing, clean mussels, overgrown mussels, or assessed
the ascidians for an extended period of time. Numbers indicate the total number of Green Crabs observed. Some crabs consumed both mussels
during their trial (n = 3 [10.3%]).
Crab choice Nothing Clean mussel Overgrown mussel Ascidian only
Crabs initially approaching clean mussels finally consumed 2 (6.9%) 6 (20.7%) 0 (0.0%) 0 (0.0%)
Crabs initially approaching overgrown mussels finally consumed 8 (27.6%) 3 (10.3%) 4 (13.8%) 1 (3.4%)*
*The ascidian was not completely consumed, although observations indicate the Green Crab in one trial held the ascidian to its mouthparts for a prolonged
period of time for a taste.
Table 1. Green Crab selection of clean and overgrown Blue Mussels. Initial approach refers to the first Blue Mussel the Green Crab contacted during the
trial. Final choice means the type of mussel consumed by the end of the trial. Numbers indicate the total number of Green Crabs observed. Some crabs
consumed both mussels during their trial (n = 3 [10.3%]).
Crab choice Nothing Clean mussel Overgrown mussel Ascidian only
Initial approach 4 (14.8%) 8 (27.6%) 13 (44.8%) 5 (17.2%)
Final choice 18 (62.1%) 9 (31.0%) 5 (17.2%) 1 (3.4%)*
*The ascidian was not completely consumed, although observations indicate the Green Crab in one trial held the ascidian to its mouthparts for a prolonged
period of time for a taste.
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Discussion
Predators appear to have a significant impact on Blue Mussels at an early life
stage in which no epibiosis occurs. Postlarval Blue Mussels that are newly settled
on filamentous substrate during primary settlement lack epibionts; this age class of
Blue Mussels possesses a periostracum that has antifouling properties and keeps the
Blue Mussel clear of epibionts (Bers and Wahl 2004, Bers et al. 2006). Later, this
periostracum wears down and disappears, allowing epibionts to settle on the mussel
shell. In our experiments, we found significantly more Blue Mussel plantigrades
on predator-exclusion panels than on control or cage control panels after 3 weeks.
Thus, predators appear willing and capable of consuming unfouled plantigrades,
contributing to increased mortality at this life stage.
These results support the findings of previous studies that have found that predation
is the single-most important source of natural mortality in Mytilus (Seed
Figure 3. Mean handling time of clean Blue Mussels and those overgrown by D. vexillum
(Carpet Sea Squirt) by the Green Crab in a laboratory experiment (n = 29). Error bars represent
± 1 standard error. There was no significant difference in handling time between clean
Blue Mussels and those overgrown with D. vexillum in this study (t56 = 1.265, P = 0.211),
though the least amount of time was spent on handling Blue Mussels overgrown with
D. vexillum (F2,28 = 3.269 P = 0.043) . n = 16 trials in which clean Mussels were handled,
n = 16 trials in which overgrown Blue Mussels were handled, and n = 14 trials in which
D. vexillum was handled.
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and Suchanek 1992). Our study assessed predation on very small (less than 1 mm)
Blue Mussels, and several previous studies have focused on predator preference for
different size classes of Blue Mussels. For example, Asterias forbesii L. (Sea Star)
prefers Blue Mussels less than 70 mm in shell length (Campbell 1983). The Green
Crab has shown a similar preference in previous studies (Elner and Hughes 1978,
Juanes 1992). Strongylocentrotus droebachiensis (Müller) (Sea Urchin) preys on
Blue Mussels less than 16 mm in length (Briscoe and Sebens 1988), and Somateria
mollissima L. (Eider Duck) prefers Blue Mussels between 10–25 mm long (Raffaeli
et al. 1990).
The few predators found on our exclusion panels were small enough to fit
through the mesh. Interestingly, the most common predator we identified on the
exclusion panels was the predatory Atlantic Dog Winkle. This snail is consumed by
Green Crabs (Hughes and Elner 1979) and its relative abundance on the exclusion
panel may have been due to the near-complete exclusion of Green Crabs from these
Figure 4. Effect of overgrowth of Didemnum vexillum on Blue Mussel consumption by
Green Crabs in the laboratory. Error bars represent ± 1 standard error. Group 1 Green Crabs
were fed clean Blue Mussels in the first 24 hours of the experiment, and then overgrown
Blue Mussels in the second 24 hours of the experiment. They consumed significantly fewer
overgrown Mussels (t4 = 3.328, P = 0.029). Group 2 Green Crabs were fed overgrown Blue
Mussels in the first 24 hours, then fed clean Blue Mussels in the second 24 hours. These
crabs also consumed significantly fewer overgrown Blue Mussels (t4 = 3.766, P=0.020). n =
5 separate trials for each group.
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panels. The significantly greater quantities of Blue Mussels found on the exclusion
panels compared to the controls indicate that the low density of small Atlantic Dog
Winkles found on the predator-exclusion panels had little to no effect on Blue Mussel
plantigrade numbers.
In our study, because the Blue Mussel panels were left undisturbed for 3
weeks, we cannot determine exactly which predators fed on the Blue Mussels
present on our panels. However, because we found both Dog Whelks and Green
Crabs on our cages when we retrieved them, we assumed these were some of the
common predators active during this period of time. Although we also cannot verify
that all Blue Mussels on the non-exclusion panels were actually consumed and
not dislodged (without observing the panels for the full 3 weeks), we can assume
that any potential physical contact with the panel itself did not dislodge significant
numbers of plantigrades. Plantigrade Blue Mussels strongly attach to their
substrate, and considerable effort is required to remove them from panels (L.A.
Auker, pers. observ.). The protected cage control panels and the exposed control
panels were also statistically similar in the abundance of Blue Mussels found on
each; therefore, we were assured that removal from panels is most likely due to
predation rather than removal due to dislodging.
In consumption assays, Green Crabs consumed fewer overgrown Blue Mussels
than control Blue Mussels, suggesting an associational resistance effect of D. vexillum
epibiosis on Blue Mussels. Wahl et al. (1997) identified 4 stages of predator
activity: encounter, recognition, capture-handling, and consumption. They hypothesized
that epibiosis only affects recognition and capture-handling. In our study,
more overgrown Blue Mussels than control Blue Mussels were approached first,
and the ascidian did not instantly repel the predator; therefore, encounter was not
affected. However, the consumption stage was negatively affected because Green
Crabs consumed more clean Blue Mussels.
Didemnum vexillum deterred Green Crab predation indicating that the symbiont
provides an associational resistance to predation, a positive aspect of epibiosis for
the Blue Mussel in terms of providing a refuge from predation. It is unclear what
specifically deterred predation, although D. vexillum possesses an acidic tunic and
may possess additional chemical defenses. When D. vexillum’s tunic is disturbed,
surface-test cells break apart and release acid (S. Bullard, University of Hartford,
West Hartford, CT, pers. comm.). However, Parry (1984) suggested that this acid
is quickly neutralized by calcium spicules in the test or is buffered by seawater.
The Green Crabs in our choice experiment picked up and handled D. vexillum for
relatively long time periods (up to 161 s), so it is unclear if the Green Crab was
affected by the release of any acid. In the consumption experiments, Green Crabs
that were placed in tanks with control Blue Mussels ate more Blue Mussels than
Green Crabs placed in tanks with overgrown Blue Mussels. This proved true for
both Green Crabs that were initially placed with clean Blue Mussels and for Green
Crabs initially placed with overgrown Blue Mussels; in all trials, the presence of
D. vexillum reduced Blue Mussel consumption. This result supports earlier studies
that have shown that chemical extracts from members of the family Didemnidae
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contain predator deterrents (Blunt et al. 2006, Lindquist et al. 1992, Prado et al.
2004, Stoecker 1978, 1980, Vervoort et al. 1998, Wright et al. 2002).
Our results for the selection and consumption laboratory studies indicated
that D. vexillum decreases predator selection for the Blue Mussel (decreased
handling time, decreased final choice, and decreased overall consumption). The
selection experiments allowed observation of individual Green Crab behavior,
but contained chemical cues of both the Blue Mussel and ascidian, whereas
the consumption experiments provided a free-for-all scenario in which Green
Crabs were given a greater amount of prey of one type. In these experiments,
the clean Blue Mussel tanks contained Blue Mussel chemosensory cues, but the
overgrown Blue Mussel tanks contained both ascidian and mussel cues. Based on
our findings from the selection experiment, that handling time was not significantly
decreased in overgrown Blue Mussels, the results from the consumption
study indicate that the presence of the D. vexillum chemosensory cues have an
impact on Blue Mussel consumption.
The anti-predator resistance provided by D. vexillum to Blue Mussels may vary
with time of year. We used D. vexillum and Blue Mussels covered with the ascidian
collected within one to two days of the feeding trials for our study. During the winter
months, D. vexillum senesces and several potential predator species have been
observed feeding on the ascidian (Valentine et al. 2007). At this time, D. vexillum
may not provide any resistance to potential Blue Mussel predators; the ascidian
may even provide an additional source of food for predators, potentially resulting
in a shared doom scenario for Blue Mussels, in which predators are attracted to an
epibiont, and the basibiont is consequently consumed (Wahl et al. 1997).
Blue Mussel populations are controlled by several predators in the Gulf of
Maine, including Atlantic Dog Winkle, Sea Stars, and several native and invasive
species of crabs (Bordeau and O’Connor 2003, Seed and Suchanek 1992). If
D. vexillum reduces predation on Blue Mussels through associational resistance as
indicated in this study, several predatory species may be negatively affected. In the
top-down predator-controlled systems seen in our study area (Donahue et al. 2009),
community dynamics could be affected by this associational resistance (Wahl et al.
1997). For example, predators would consume fewer Blue Mussels when the latter
are overgrown, and resort to other species for food, or the predator populations
may decrease due to lack of food. Areas covered in these large mat-like D. vexillum
colonies would likely be most dramatically impacted. Although our study focused
on one predator, the Green Crab, we previously attempted this experiment with Sea
Stars in the laboratory and did not observe any instance of their consuming Blue
Mussels. Expanding this study into the field to look at other common predators’
preferences would be beneficial in understanding the implications of overgrowth
by a dominant invasive ascidian.
As for the individual Blue Mussel, the associational resistance effect from
overgrowth provides a trade-off for negative effects on growth. During the time
of year in which D. vexillum is most abundant, gamete production, shell-lip thickness,
and tissue production decrease in Blue Mussels (Auker 2010). The Blue
Northeastern Naturalist Vol. 21, No. 3
L.A. Auker, A.L. Majkut, and L.G. Harris
2014
491
Mussel may not grow as quickly when overgrown, but will likely be protected
from predation; this tradeoff may be particularly advantageous for Blue Mussels
that colonize the benthos and have both benthic (e.g., Sea Stars and crabs)
and pelagic (Tautogolabrus adspersus [Wahlbaum] [Cunner] and other fish species)
predators. Although Laudien and Wahl (2004) predicted that the decrease in
growth of Blue Mussels caused by an epibiont may prolong its susceptibility to
predation because smaller Blue Mussels are preferred over larger Blue Mussels
(e.g., Murray et al. 2007), our results suggest otherwise. Epibiotic D. vexillum’s
mat-like morphology, which tends to overgrow Blue Mussels completely and deter
predators, protects small Blue Mussels (less than 5 cm) from predation.
Overall, the results from this study suggest that predation is a significant factor
in plantigrade Blue Mussel-population abundance, a Blue Mussel life stage that
does not yet possess epibionts. We also observed that D. vexillum has a positive
effect on Blue Mussels by providing an anti-predator defense against the Green
Crab, a common predator in the Gulf of Maine. Protection from predation could
have strong implications for predators in areas dominated by D. vexillum growth
and has the potential to alter community dynamics in the Gulf of Maine.
Acknowledgments
The Hampton River Marina (Hampton, NH) provided floating-dock space for the deployment
and retrieval of our predator-exclusion panels. We wish to thank Emily Gamelin
for help in collecting animals for the laboratory experiments. Marian Litvaitis, Raymond
Grizzle, James Haney, and Stephan Bullard provided advice for the laboratory experiments,
which were conducted as part of Linda Auker’s Ph.D. Dissertation at the University of
New Hampshire. We would also like to thank S. Bullard, Melisa Wong, and an anonymous
reviewer for comments that greatly improved this manuscript.
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