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Brown,	
  Courtney	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  BIOL	
  831E	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  Spring	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  2	
  May	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  1	
  
Influence of High Volume Human Populations on the Common
Starfish, Asterias rubens
Courtney N. Brown, Department of Biology, University of Nebraska at Kearney, Kearney, NE
68849
Brown,	
  Courtney	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  BIOL	
  831E	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  Spring	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  2	
  May	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  2	
  
ABSTRACT1	
  
The goal of this study was to examine the influence of high volume human populations2	
  
on the near-shore populations of the starfish species Asterias rubens, or the Common Starfish.3	
  
Specifically, the purpose of this study was to examine the relationship of human populations and4	
  
the arm damage that A. rubens incurs from these human populations. For two separate beaches5	
  
with similar conditions aside from human population, sixty-five A. rubens starfish were collected6	
  
from thirteen random, different feeding spots of pre-designated criteria. Five A. rubens7	
  
specimens were collected from each of these spots, including ones that had missing or damaged8	
  
arms. Arm lengths were measured from the center of the starfish to the outermost point of each9	
  
arm. These lengths were averaged for each A. rubens measured, and an overall average was10	
  
calculated. When compared statistically, the overall average arm length of the A. rubens at the11	
  
beach with the smaller human population was found to be significantly different than the overall12	
  
average arm length for the beach with the larger human population. These results suggest that13	
  
high volume human populations do influence the size of Asterias rubens in a beach	
  setting.	
  	
  14	
  
15	
  
Key Words: Asterias rubens, arm damage, habitat, human interference, conservation	
  16	
  
17	
  
18	
  
19	
  
20	
  
21	
  
22	
  
23	
  
24	
  
Brown,	
  Courtney	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  BIOL	
  831E	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  Spring	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  2	
  May	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  3	
  
INTRODUCTION1	
  
Disruption of a habitat by humans can cause lasting effect (Sano et al., 1987). Over time,2	
  
the more humans disturb a habitat, including that of starfish such as Asterias rubens, the less3	
  
food a species within that habitat will be able to obtain (Sano et al., 1987). As in all species,4	
  
when food supply is low many changes will occur (Vevers, 1949). Some of these changes may5	
  
be irreversible (Whilde, 1985). When the food supply diminishes, individual starfish size trends6	
  
smaller through time. (Menge, 1972). In addition, high levels of human impact cause physical7	
  
damage to the bodies of starfish, causing them to have to regenerate limbs (Ramsay et al., 2001).8	
  
While regeneration is one of the defining traits of starfish, continued regeneration will require9	
  
energy from the starfish that would be used differently if a specimen did not have to deal with so10	
  
much damage (Ramsay et al., 2001). Energy that would have gone toward reproduction or11	
  
hunting larger prey would have to go toward arm regeneration (Barker and Nichols, 1983).12	
  
Starfish that regenerate limbs multiple times due to constant damage can lose up to 40% of their13	
  
lipids and 85% of the amount of kilojoules in their pyloric caeca (Lawrence and Larrain, 1994).14	
  
While large, this loss of lipids and energy is not necessarily lethal for starfish (Lawrence et al.,15	
  
1999). However, starfish with arms that are lost multiple times will have a lowered ability to feed16	
  
(Ramsay et al., 2001). Furthermore, a continuously damaged habitat on top of arm loss will17	
  
result in decreased size of the starfish, including misshapen or shorter limbs (Marrs et al., 2000).18	
  
Starfish arm regeneration is not a cost-free attribute for any starfish species	
  (Bingham and19	
  
Burr, 2000). While this regenerative ability is helpful and allows starfish to escape many20	
  
potentially life-threatening situations (Ramsay et al., 2000), the starfish does trade a lot of energy21	
  
to regenerate a lost appendage (Bingham and Burr, 2000). This energy used for regeneration will22	
  
lower the ability of the starfish to reproduce (Bingham and Burr, 2000). Also, when starfish has23	
  
Brown,	
  Courtney	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  BIOL	
  831E	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  Spring	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  2	
  May	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  4	
  
to regenerate arms more than normal, and it does not have enough energy to do this since it1	
  
cannot catch prey as well, the arms can come back shorter and not quite equal to the other arms2	
  
(Ramsay et al., 2001). However, starfish having a normal, pentameral symmetry is advantageous3	
  
to the organism (Wu et al., 2012). A starfish that has all five of its arms is best at autotomy, or4	
  
self-amputation, which gives it a better chance of escaping a deadly situation in comparison to5	
  
starfish that do not have that pentameral shape (Wu et al., 2012). In combination with autotomy,6	
  
starfish with five arms have an advantage in detection, turning over, and adherence versus those7	
  
with a different number of arms (Wu et al., 2012).8	
  
Humans influence the environment of starfish in more ways than one. For example, the9	
  
starfish caught by towed, bottom fishing gears are adversely affected as well as areas that were10	
  
subjected to different levels of fishing intensity (Ramsay et al., 2001). This does not only result11	
  
in arm loss that will result in regeneration as a means of repair (Ramsay et al., 2001). In an even12	
  
worse scenario, starfish will not lose the arm, but will have its ambularal ossicles damaged13	
  
(Ramsay et al., 2001). These little plates that cover the arm of starfish, when damaged, can cause14	
  
misshapen arms that do not heal (Ramsay et al., 2001). This type of damage can result in reduced15	
  
fitness and reduced ability to capture prey, which can result in reduced size and reduced arm16	
  
length (Ramsay et al., 2001). The continued, potentially severe damage often has more severe17	
  
repercussions than simply not being able to capture prey and reduced size. The starfish with18	
  
missing or damaged arms showed a 44 – 69% decrease in egg production seven months after arm19	
  
loss (Bingham and Burr, 2001). Even 19 months after the arm damage or arm loss occurred,20	
  
lowered egg reproduction was still evident (Bingham and Burr, 2001). It is estimated that even21	
  
normal arm damage, such as partial arm loss from a predator, can reduce the ability of a starfish22	
  
to reproduce by 7 – 10% (Bingham and Burr, 2001).23	
  
Brown,	
  Courtney	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  BIOL	
  831E	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
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  2	
  May	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  5	
  
There are quite a few factors regarding starfish feeding and the specific prey starfish will1	
  
pursue (Menge, 1972). Some of these factors include the caloric content of the potential prey,2	
  
how easy the prey is to capture, and the size of the prey (Menge and Menge, 1974). While3	
  
starfish are typically food generalists, the type of prey they tend to search for is usually4	
  
influenced by the environment that they live in (Menge, 1983; Gallagher et al., 2008). If human5	
  
interactions with the environment of Asterias rubens has altered the environment or cause6	
  
excessive arm damage or arm removal at, then this species of starfish will have a difficulty7	
  
catching prey (Marrs et al., 2000). This includes being able to pry open bivalves (Marrs et al.,8	
  
2000). In addition, starfish that are disfigured or constantly missing an arm will not be able to go9	
  
after the normal size of prey they have been known to seek (Marrs et al., 2000).10	
  
The major goal of this study is to determine if a beach with more human traffic11	
  
negatively impacts the size of starfish in a beach setting in comparison to a beach with much less12	
  
human traffic. Specifically, this study will examine the average arm length of the Common13	
  
starfish, Asterias reubens. A second goal is to examine conservation methods of near-shore14	
  
habitats of the Asterias reubens in regards to human interference.15	
  
16	
  
MATERIALS AND METHODS17	
  
Animals18	
  
All specimens used in this study are invertebrates of one starfish species, Asterias rubens.19	
  
Even though neither the Guide for the Use and Care of Laboratory Animals (NAS, 2011) nor a20	
  
review board will be needed for this study, it is a goal of this study not to damage any animals or21	
  
disturb their habitat. Sixty-five specimens of A. rubens will be obtained by hand from shallow22	
  
feeding spots less than a meter deep on both beach study sites. Feeding spots are defined as the23	
  
Brown,	
  Courtney	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  BIOL	
  831E	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  Spring	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  2	
  May	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  6	
  
shallow, rocky tide pool areas found near the shores of both beaches. The species of starfish1	
  
being examined usually eats bivalves, but will eat small crustaceans and other echinoderms if2	
  
necessary in order to survive (Tuya and Duarte, 2012). All of these organisms exist in the3	
  
feeding spots along with A. rubens. To randomize the selection of the feeding spots, twenty-five4	
  
spots will be located and numbered before the study is conducted. The names of the spots will be5	
  
entered in Excel and, using the random function, thirteen spots will be chosen. Five specimens6	
  
will be carefully removed from each feeding area. Each specimen obtained will then have its7	
  
arms measured with a standard ruler. Natural rubber gloves will be worn to decrease contact with8	
  
the A. rubens. This will help to prevent any mishandling or dropping of the specimen due to9	
  
spines that can be irritating to touch. Specimens of A. rubens that do not have all of their legs10	
  
intact will still be measured so that results will not be incorrect or skewed.11	
  
No A. rubens will be permanently removed, sacrificed, or modified during the duration of12	
  
the study. Each specimen will be removed from its habitat, have its arms measured, and returned13	
  
to its original location. All arm measurements and weather conditions will be logged on custom14	
  
logbook sheets.15	
  
16	
  
Arm Length Average17	
  
Arms on each A. rubens will be measured and noted. The arm lengths will then be18	
  
averaged for each starfish. The arm of each starfish will be measured from the center of the19	
  
specimen to the tip of each arm. These averages will then be used for statistical analysis.20	
  
21	
  
Weather Conditions and Feeding Location Marking22	
  
Weather conditions will be monitored closely, recorded, and should be similar and close23	
  
Brown,	
  Courtney	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  BIOL	
  831E	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
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  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
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  7	
  
to optimal conditions for the study on both beaches. Optimal conditions, in this study, would1	
  
mean no rain, an average humidity of 75% to 80%, an average wind velocity of 24.14 to 32.192	
  
kph, and an average temperature of 23.85° to 25.85° Celsius for both beaches. Weather will be3	
  
recorded for both beaches each day the study is conducted. Specifically, temperature, humidity,4	
  
wind velocity, tide height, and tide speed will be measured in regards to weather. The study will5	
  
not be conducted in inclement weather, including thunderstorms of any severity. For records,6	
  
each A. rubens feeding spot will be noted in terms of latitude and longitude with a GPS receiver7	
  
– a Bushnell 360310BG Backtrack D-Tour.8	
  
9	
  
Statistical Analysis10	
  
The data will be tested for normality using the Shapiro-Wilks test. Provided that the data11	
  
collected is normal, it will be analyzed using the Student’s t-test. The level of significance will12	
  
be α = 0.05. This means that if the calculated p-value for average arm length is less than the13	
  
significance level, or p < 0.05, the null hypothesis of the average arm length of the starfish on the14	
  
two beaches no different will be rejected in favor of the alternative hypothesis. However, if the15	
  
data is shown to be non-normal, then the Wilcoxon rank-sum test can be used as an alternative to16	
  
a Student’s t-test.17	
  
18	
  
RESULTS19	
  
The data sets collected from both Wrightsville Beach, NC and Myrtle Beach, SC were20	
  
shown to be normal and have equal variances, allowing a Student’s t-test to be used to examine21	
  
the data. The overall average arm length of the Asterias rubens specimens that were collected22	
  
and measured from Wrightsville Beach, NC were significantly different (p=0.001) in comparison23	
  
Brown,	
  Courtney	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  BIOL	
  831E	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  Spring	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  2	
  May	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  8	
  
to the overall average arm length of the Asterias rubens specimens that were collected and1	
  
measured from Myrtle Beach, SC (Wrightsville 8.77 + 1.28; Myrtle 8.09 + 1.06. The five2	
  
individual averaged arm lengths were larger for the Asterias rubens data set collected from3	
  
Wrightsville Beach, NC.4	
  
5	
  
DISCUSSION6	
  
The interference by humans on starfish habitats has been known to lead to increased7	
  
instances of arm damage and an overall reduction in size of starfish species over time8	
  
(Barthelemy, 1992). Anywhere up to 80 – 85% of the kilojoules of energy that Asterias rubens9	
  
stores can be used to regenerate lost limbs (Fan et al., 2005; Franco et al., 2012). If this energy10	
  
expenditure can lead to an overall reduction in size, normal prey such as the mussel Mytilus11	
  
edulis or other smaller species of starfish may become harder to catch by Asterias rubens (Allen,12	
  
1983; Dolmer, 1998). In addition, if arm damage occurs often and in multiple arms, prying13	
  
mussels open can become increasingly difficult for Asterias rubens (Anger et al., 1977; Jackson14	
  
et al., 2008). The observation of significant differences in overall Asterias rubens arm length on15	
  
the shores of Wrightsville Beach, NC and Myrtle Beach, SC suggests that interference from high16	
  
volume human populations does influence these arm length differences when other conditions17	
  
are similar. The beach with the larger human population, Myrtle Beach, had the smaller overall18	
  
arm length as well as smaller individual average arm lengths. This is consistent with the19	
  
observation that increased human interference, physical, mechanical, or otherwise, on starfish20	
  
populations correlates with increased damage to members of these populations (Kaiser, 1996;21	
  
Joly-Turquin et al., 2009). The larger the volume of a human population, the more damaged22	
  
limbs Asterias rubens seem to have. In addition, the observation in this study is consistent with23	
  
Brown,	
  Courtney	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  BIOL	
  831E	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  Spring	
  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
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  9	
  
the observation that continued injuries to members of a starfish population will lead to an overall1	
  
decrease in size to cut back on the energy used to regenerate limbs. If Asterias rubens have limbs2	
  
that are smaller in general, less energy will be spent to regenerate those limbs after damage or3	
  
loss has occurred.4	
  
The ways high volume human populations influence arm lengths can upset the balance of5	
  
the ecosystem that exists in near-shore feeding spots as well. Since Asterias rubens cannot pry6	
  
open mussels or successfully prey on other starfish species if they are missing or have damaged7	
  
arms, this can lead to a number of problems involving the population control of other species8	
  
(Kamermans et al., 2009). Asterias rubens typically preys on and are most successful with9	
  
averaged sized mussels, not under or over sized ones (Norberg and Tedengren, 1995). If Asterias10	
  
rubens are not able to prey on mussels, such as Mytilus edulis, it can lead to that particular size11	
  
or species of mussel overcrowding a habitat and not allowing other, smaller species of mussels to12	
  
coexist with them (Yamada et al., 1992; Kulakovskii and Lezin, 1999; Reimer et al., 1999). Also,13	
  
if Asterias rubens cannot hunt smaller starfish or outcompete other starfish species in their14	
  
habitat, problems can still occur (Zeidler, 1992; Saier, 2001). Either situation would allow15	
  
another species of starfish to overpopulate a habitat and upset the balance of that habitat (Penney16	
  
and Griffiths, 1984). Asterias rubens can also be reduced in size enough or damaged enough to17	
  
become easier prey to more species (Aldrich, 1976). Other species in a habitat that are not18	
  
normally predators may become predators if Asterias rubens are reduced in size or are19	
  
continuously damaged (Arrontes and Underwood, 1991). Regardless of the main cause for20	
  
Asterias rubens not being able to obtain prey, mortality rates of this species if they are deprived21	
  
of a food source or have a harder time obtaining it (Paine, 1976; Bergmann and Moore, 2001).22	
  
The loss of the ability to prey on mussels is the biggest, since Asterias rubens need sterols to23	
  
Brown,	
  Courtney	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
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  10	
  
function and mussels are a major source of them (Voogt and Rheenen, 1976).1	
  
It is important to try and limit the amount of damage dealt to Asterias rubens populations2	
  
by human interference. Asterias rubens can already face difficulty thriving by other3	
  
environmental changes, and human interference can only add to these problems (Guillou et al.,4	
  
2012). Changes such as ocean acidification can suppress the immune system of Asterias rubens5	
  
(Hernroth et al., 2011). In addition, increased salinity can lead to decreased adhesive tenacity as6	
  
well as slowed or improper development in Asterias rubens (Saranchova and Kulakovskii, 1982;7	
  
Berger and Naumov, 1996). Environmental changes alone can lead to abnormal behavior in8	
  
Asterias rubens, such as retreating to deeper waters, since this species of starfish does not9	
  
tolerate environmental changes as well as other competitive starfish species (Smith, 1940;10	
  
Shulgina, 2006). Even sediment changes can lead to a change in the vertical distribution of11	
  
starfish (Kurihara, 1999). These environmental changes, coupled with human interference in12	
  
high levels, can lead to Asterias rubens that are very easy to damage or easily lose their limbs13	
  
(Rogers et al., 2001; Hotchkiss, 2008). At minimum, if this human interference is lowered,14	
  
Asterias rubens could face less amounts of damage or lost limbs.15	
  
16	
  
ACKNOWLEDGEMENTS17	
  
Thanks to Dr. Marc Albrecht for assistance with editing suggestions for this manuscript18	
  
and guidance throughout the entire research project it is based around and to the UNK19	
  
Department of Biology for technical assistance and the chance to design and carry out this20	
  
research project21	
  
Brown,	
  Courtney	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
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  831E	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
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REFERENCES
Aldrich, J. C. (1976). The spider crab Libinia emarginata Leach, 1815 (Decapoda Brachyura)
and the starfish, an unsuitable predator but a cooperative prey. Crustaceana, 31(2), 151-
156.
Allen, P. L. (1983). Feeding behaviour of Asterias rubens (L.) on soft bottom bivalves: A study
in selective predation. Journal of Experimental Marine Biology and Ecology, 70(1), 79-
90.
Anger, K., Rogal, U., Schriever, G. and Valentin, C. (1977). In-situ investigations on the
echinoderm Asterias rubens as a predator of soft-bottom communities in the western
Baltic Sea. Helgol. Wiss. Meeresunters., 29(4), 439-459.
Arrontes, J. and Underwood, A. J. (1991). Experimental studies on some aspects of the feeding
ecology of the intertidal starfish Patiriella exigua. Journal of Experimental Marine
Biology and Ecology, 148(2), 255-269.
Barker, M. F. and Nichols, D. (1983). Reproduction, recruitment and juvenile ecology of the
starfish, Asterias rubens and Marthasterias glacialis. Journal of the Marine Biological
Association of the United Kingdom, 63(4), 745-765.
Barthelemy, G. (1992). Study on biological control of the proliferation of the starfish: Asterias
rubens in Bay of Quiberon. Societe Francaise de Malacologie, Paris (France). Accessed
02 July 2013.
Berger, V. Y. and Naumov, A. D. (1996). The effect of salinity upon the adhesive tenacity of
Asterias rubens starfishes. Russian Journal of Marine Biology, 22(2), 95-96.
Bergmann, M. and Moore, P. G. (2001). Mortality of Asterias rubens and Ophiura ophiura
Brown,	
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discarded in the Nephrops fishery of the Clyde Sea area, Scotland. ICES Journal of
Marine Science, 58(3), 531-542.
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Leptasterias hexactis. Canadian Journal of Zoology, 78(4), 596-605.
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Kurihara, T. (1999). Effects of sediment type and food abundance on the vertical distribution of
the starfish Asterina pectinifera. Marine Ecology Progress Series, 181, 269-277.
Kulakovskii, E. and Lezin, P. A. (1999). Influence of the starfish Asterias rubens (Forcipulata,
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Lawrence, J. M., Byrne, M., Harris, L., Keegan, B. and Freeman, S. (1999). Sublethal arm loss in
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  831E	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
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  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
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  17	
  
Table 1. Averages for individual and overall arm length of collected Asterias rubens specimens from
Wrightsville Beach, NC and Myrtle Beach, SC.
_____________________________________________________________________________________
Arm 1 Arm 2 Arm 3 Arm 4 Arm 5 Overall Average
Wrightsville (n=65) 8.75 + 1.49 8.79 + 1.40 8.77 + 1.50 8.82 + 1.46 8.74 + 1.56 8.77 + 1.28*
Myrtle (n=65) 8.16 + 1.41 8.06 + 1.45 7.93 + 1.54 8.08 + 1.55 8.26 + 1.17 8.09 + 1.06*
_____________________________________________________________________________________
Values in Table 1 are means + standard deviations. Arm lengths expressed in centimeters (cm). Starfish
were measured from center to the tip of each arm, even if the arm had been damaged or removed. Starfish
from each location were taken from randomly selected feeding spots of pre-determined criteria. Weather
conditions for collection days were of pre-determined criteria and were similar for both beach collection
sites. *When the overall average arm lengths are compared in a two-tailed t-test, the p-value = 0.001,
which is less than the alpha level of α = 0.05.
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  18	
  
Figure 1. Legend
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  2014	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
  	
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  19	
  
Figure 1. Average arm length of individual arms of Asterias rubens collected from Myrtle Beach, SC and
Wrightsville Beach, NC. Arm lengths are measured in centimeters to the nearest tenth. Error bars are with
the standard deviation of each averaged arm length. n = 65 for each group and includes damaged or
missing arms.

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Brown, Courtney - Biology 831F Manuscript Final Draft

  • 1. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    1   Influence of High Volume Human Populations on the Common Starfish, Asterias rubens Courtney N. Brown, Department of Biology, University of Nebraska at Kearney, Kearney, NE 68849
  • 2. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    2   ABSTRACT1   The goal of this study was to examine the influence of high volume human populations2   on the near-shore populations of the starfish species Asterias rubens, or the Common Starfish.3   Specifically, the purpose of this study was to examine the relationship of human populations and4   the arm damage that A. rubens incurs from these human populations. For two separate beaches5   with similar conditions aside from human population, sixty-five A. rubens starfish were collected6   from thirteen random, different feeding spots of pre-designated criteria. Five A. rubens7   specimens were collected from each of these spots, including ones that had missing or damaged8   arms. Arm lengths were measured from the center of the starfish to the outermost point of each9   arm. These lengths were averaged for each A. rubens measured, and an overall average was10   calculated. When compared statistically, the overall average arm length of the A. rubens at the11   beach with the smaller human population was found to be significantly different than the overall12   average arm length for the beach with the larger human population. These results suggest that13   high volume human populations do influence the size of Asterias rubens in a beach  setting.    14   15   Key Words: Asterias rubens, arm damage, habitat, human interference, conservation  16   17   18   19   20   21   22   23   24  
  • 3. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    3   INTRODUCTION1   Disruption of a habitat by humans can cause lasting effect (Sano et al., 1987). Over time,2   the more humans disturb a habitat, including that of starfish such as Asterias rubens, the less3   food a species within that habitat will be able to obtain (Sano et al., 1987). As in all species,4   when food supply is low many changes will occur (Vevers, 1949). Some of these changes may5   be irreversible (Whilde, 1985). When the food supply diminishes, individual starfish size trends6   smaller through time. (Menge, 1972). In addition, high levels of human impact cause physical7   damage to the bodies of starfish, causing them to have to regenerate limbs (Ramsay et al., 2001).8   While regeneration is one of the defining traits of starfish, continued regeneration will require9   energy from the starfish that would be used differently if a specimen did not have to deal with so10   much damage (Ramsay et al., 2001). Energy that would have gone toward reproduction or11   hunting larger prey would have to go toward arm regeneration (Barker and Nichols, 1983).12   Starfish that regenerate limbs multiple times due to constant damage can lose up to 40% of their13   lipids and 85% of the amount of kilojoules in their pyloric caeca (Lawrence and Larrain, 1994).14   While large, this loss of lipids and energy is not necessarily lethal for starfish (Lawrence et al.,15   1999). However, starfish with arms that are lost multiple times will have a lowered ability to feed16   (Ramsay et al., 2001). Furthermore, a continuously damaged habitat on top of arm loss will17   result in decreased size of the starfish, including misshapen or shorter limbs (Marrs et al., 2000).18   Starfish arm regeneration is not a cost-free attribute for any starfish species  (Bingham and19   Burr, 2000). While this regenerative ability is helpful and allows starfish to escape many20   potentially life-threatening situations (Ramsay et al., 2000), the starfish does trade a lot of energy21   to regenerate a lost appendage (Bingham and Burr, 2000). This energy used for regeneration will22   lower the ability of the starfish to reproduce (Bingham and Burr, 2000). Also, when starfish has23  
  • 4. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    4   to regenerate arms more than normal, and it does not have enough energy to do this since it1   cannot catch prey as well, the arms can come back shorter and not quite equal to the other arms2   (Ramsay et al., 2001). However, starfish having a normal, pentameral symmetry is advantageous3   to the organism (Wu et al., 2012). A starfish that has all five of its arms is best at autotomy, or4   self-amputation, which gives it a better chance of escaping a deadly situation in comparison to5   starfish that do not have that pentameral shape (Wu et al., 2012). In combination with autotomy,6   starfish with five arms have an advantage in detection, turning over, and adherence versus those7   with a different number of arms (Wu et al., 2012).8   Humans influence the environment of starfish in more ways than one. For example, the9   starfish caught by towed, bottom fishing gears are adversely affected as well as areas that were10   subjected to different levels of fishing intensity (Ramsay et al., 2001). This does not only result11   in arm loss that will result in regeneration as a means of repair (Ramsay et al., 2001). In an even12   worse scenario, starfish will not lose the arm, but will have its ambularal ossicles damaged13   (Ramsay et al., 2001). These little plates that cover the arm of starfish, when damaged, can cause14   misshapen arms that do not heal (Ramsay et al., 2001). This type of damage can result in reduced15   fitness and reduced ability to capture prey, which can result in reduced size and reduced arm16   length (Ramsay et al., 2001). The continued, potentially severe damage often has more severe17   repercussions than simply not being able to capture prey and reduced size. The starfish with18   missing or damaged arms showed a 44 – 69% decrease in egg production seven months after arm19   loss (Bingham and Burr, 2001). Even 19 months after the arm damage or arm loss occurred,20   lowered egg reproduction was still evident (Bingham and Burr, 2001). It is estimated that even21   normal arm damage, such as partial arm loss from a predator, can reduce the ability of a starfish22   to reproduce by 7 – 10% (Bingham and Burr, 2001).23  
  • 5. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    5   There are quite a few factors regarding starfish feeding and the specific prey starfish will1   pursue (Menge, 1972). Some of these factors include the caloric content of the potential prey,2   how easy the prey is to capture, and the size of the prey (Menge and Menge, 1974). While3   starfish are typically food generalists, the type of prey they tend to search for is usually4   influenced by the environment that they live in (Menge, 1983; Gallagher et al., 2008). If human5   interactions with the environment of Asterias rubens has altered the environment or cause6   excessive arm damage or arm removal at, then this species of starfish will have a difficulty7   catching prey (Marrs et al., 2000). This includes being able to pry open bivalves (Marrs et al.,8   2000). In addition, starfish that are disfigured or constantly missing an arm will not be able to go9   after the normal size of prey they have been known to seek (Marrs et al., 2000).10   The major goal of this study is to determine if a beach with more human traffic11   negatively impacts the size of starfish in a beach setting in comparison to a beach with much less12   human traffic. Specifically, this study will examine the average arm length of the Common13   starfish, Asterias reubens. A second goal is to examine conservation methods of near-shore14   habitats of the Asterias reubens in regards to human interference.15   16   MATERIALS AND METHODS17   Animals18   All specimens used in this study are invertebrates of one starfish species, Asterias rubens.19   Even though neither the Guide for the Use and Care of Laboratory Animals (NAS, 2011) nor a20   review board will be needed for this study, it is a goal of this study not to damage any animals or21   disturb their habitat. Sixty-five specimens of A. rubens will be obtained by hand from shallow22   feeding spots less than a meter deep on both beach study sites. Feeding spots are defined as the23  
  • 6. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    6   shallow, rocky tide pool areas found near the shores of both beaches. The species of starfish1   being examined usually eats bivalves, but will eat small crustaceans and other echinoderms if2   necessary in order to survive (Tuya and Duarte, 2012). All of these organisms exist in the3   feeding spots along with A. rubens. To randomize the selection of the feeding spots, twenty-five4   spots will be located and numbered before the study is conducted. The names of the spots will be5   entered in Excel and, using the random function, thirteen spots will be chosen. Five specimens6   will be carefully removed from each feeding area. Each specimen obtained will then have its7   arms measured with a standard ruler. Natural rubber gloves will be worn to decrease contact with8   the A. rubens. This will help to prevent any mishandling or dropping of the specimen due to9   spines that can be irritating to touch. Specimens of A. rubens that do not have all of their legs10   intact will still be measured so that results will not be incorrect or skewed.11   No A. rubens will be permanently removed, sacrificed, or modified during the duration of12   the study. Each specimen will be removed from its habitat, have its arms measured, and returned13   to its original location. All arm measurements and weather conditions will be logged on custom14   logbook sheets.15   16   Arm Length Average17   Arms on each A. rubens will be measured and noted. The arm lengths will then be18   averaged for each starfish. The arm of each starfish will be measured from the center of the19   specimen to the tip of each arm. These averages will then be used for statistical analysis.20   21   Weather Conditions and Feeding Location Marking22   Weather conditions will be monitored closely, recorded, and should be similar and close23  
  • 7. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    7   to optimal conditions for the study on both beaches. Optimal conditions, in this study, would1   mean no rain, an average humidity of 75% to 80%, an average wind velocity of 24.14 to 32.192   kph, and an average temperature of 23.85° to 25.85° Celsius for both beaches. Weather will be3   recorded for both beaches each day the study is conducted. Specifically, temperature, humidity,4   wind velocity, tide height, and tide speed will be measured in regards to weather. The study will5   not be conducted in inclement weather, including thunderstorms of any severity. For records,6   each A. rubens feeding spot will be noted in terms of latitude and longitude with a GPS receiver7   – a Bushnell 360310BG Backtrack D-Tour.8   9   Statistical Analysis10   The data will be tested for normality using the Shapiro-Wilks test. Provided that the data11   collected is normal, it will be analyzed using the Student’s t-test. The level of significance will12   be α = 0.05. This means that if the calculated p-value for average arm length is less than the13   significance level, or p < 0.05, the null hypothesis of the average arm length of the starfish on the14   two beaches no different will be rejected in favor of the alternative hypothesis. However, if the15   data is shown to be non-normal, then the Wilcoxon rank-sum test can be used as an alternative to16   a Student’s t-test.17   18   RESULTS19   The data sets collected from both Wrightsville Beach, NC and Myrtle Beach, SC were20   shown to be normal and have equal variances, allowing a Student’s t-test to be used to examine21   the data. The overall average arm length of the Asterias rubens specimens that were collected22   and measured from Wrightsville Beach, NC were significantly different (p=0.001) in comparison23  
  • 8. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    8   to the overall average arm length of the Asterias rubens specimens that were collected and1   measured from Myrtle Beach, SC (Wrightsville 8.77 + 1.28; Myrtle 8.09 + 1.06. The five2   individual averaged arm lengths were larger for the Asterias rubens data set collected from3   Wrightsville Beach, NC.4   5   DISCUSSION6   The interference by humans on starfish habitats has been known to lead to increased7   instances of arm damage and an overall reduction in size of starfish species over time8   (Barthelemy, 1992). Anywhere up to 80 – 85% of the kilojoules of energy that Asterias rubens9   stores can be used to regenerate lost limbs (Fan et al., 2005; Franco et al., 2012). If this energy10   expenditure can lead to an overall reduction in size, normal prey such as the mussel Mytilus11   edulis or other smaller species of starfish may become harder to catch by Asterias rubens (Allen,12   1983; Dolmer, 1998). In addition, if arm damage occurs often and in multiple arms, prying13   mussels open can become increasingly difficult for Asterias rubens (Anger et al., 1977; Jackson14   et al., 2008). The observation of significant differences in overall Asterias rubens arm length on15   the shores of Wrightsville Beach, NC and Myrtle Beach, SC suggests that interference from high16   volume human populations does influence these arm length differences when other conditions17   are similar. The beach with the larger human population, Myrtle Beach, had the smaller overall18   arm length as well as smaller individual average arm lengths. This is consistent with the19   observation that increased human interference, physical, mechanical, or otherwise, on starfish20   populations correlates with increased damage to members of these populations (Kaiser, 1996;21   Joly-Turquin et al., 2009). The larger the volume of a human population, the more damaged22   limbs Asterias rubens seem to have. In addition, the observation in this study is consistent with23  
  • 9. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    9   the observation that continued injuries to members of a starfish population will lead to an overall1   decrease in size to cut back on the energy used to regenerate limbs. If Asterias rubens have limbs2   that are smaller in general, less energy will be spent to regenerate those limbs after damage or3   loss has occurred.4   The ways high volume human populations influence arm lengths can upset the balance of5   the ecosystem that exists in near-shore feeding spots as well. Since Asterias rubens cannot pry6   open mussels or successfully prey on other starfish species if they are missing or have damaged7   arms, this can lead to a number of problems involving the population control of other species8   (Kamermans et al., 2009). Asterias rubens typically preys on and are most successful with9   averaged sized mussels, not under or over sized ones (Norberg and Tedengren, 1995). If Asterias10   rubens are not able to prey on mussels, such as Mytilus edulis, it can lead to that particular size11   or species of mussel overcrowding a habitat and not allowing other, smaller species of mussels to12   coexist with them (Yamada et al., 1992; Kulakovskii and Lezin, 1999; Reimer et al., 1999). Also,13   if Asterias rubens cannot hunt smaller starfish or outcompete other starfish species in their14   habitat, problems can still occur (Zeidler, 1992; Saier, 2001). Either situation would allow15   another species of starfish to overpopulate a habitat and upset the balance of that habitat (Penney16   and Griffiths, 1984). Asterias rubens can also be reduced in size enough or damaged enough to17   become easier prey to more species (Aldrich, 1976). Other species in a habitat that are not18   normally predators may become predators if Asterias rubens are reduced in size or are19   continuously damaged (Arrontes and Underwood, 1991). Regardless of the main cause for20   Asterias rubens not being able to obtain prey, mortality rates of this species if they are deprived21   of a food source or have a harder time obtaining it (Paine, 1976; Bergmann and Moore, 2001).22   The loss of the ability to prey on mussels is the biggest, since Asterias rubens need sterols to23  
  • 10. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    10   function and mussels are a major source of them (Voogt and Rheenen, 1976).1   It is important to try and limit the amount of damage dealt to Asterias rubens populations2   by human interference. Asterias rubens can already face difficulty thriving by other3   environmental changes, and human interference can only add to these problems (Guillou et al.,4   2012). Changes such as ocean acidification can suppress the immune system of Asterias rubens5   (Hernroth et al., 2011). In addition, increased salinity can lead to decreased adhesive tenacity as6   well as slowed or improper development in Asterias rubens (Saranchova and Kulakovskii, 1982;7   Berger and Naumov, 1996). Environmental changes alone can lead to abnormal behavior in8   Asterias rubens, such as retreating to deeper waters, since this species of starfish does not9   tolerate environmental changes as well as other competitive starfish species (Smith, 1940;10   Shulgina, 2006). Even sediment changes can lead to a change in the vertical distribution of11   starfish (Kurihara, 1999). These environmental changes, coupled with human interference in12   high levels, can lead to Asterias rubens that are very easy to damage or easily lose their limbs13   (Rogers et al., 2001; Hotchkiss, 2008). At minimum, if this human interference is lowered,14   Asterias rubens could face less amounts of damage or lost limbs.15   16   ACKNOWLEDGEMENTS17   Thanks to Dr. Marc Albrecht for assistance with editing suggestions for this manuscript18   and guidance throughout the entire research project it is based around and to the UNK19   Department of Biology for technical assistance and the chance to design and carry out this20   research project21  
  • 11. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    11   REFERENCES Aldrich, J. C. (1976). The spider crab Libinia emarginata Leach, 1815 (Decapoda Brachyura) and the starfish, an unsuitable predator but a cooperative prey. Crustaceana, 31(2), 151- 156. Allen, P. L. (1983). Feeding behaviour of Asterias rubens (L.) on soft bottom bivalves: A study in selective predation. Journal of Experimental Marine Biology and Ecology, 70(1), 79- 90. Anger, K., Rogal, U., Schriever, G. and Valentin, C. (1977). In-situ investigations on the echinoderm Asterias rubens as a predator of soft-bottom communities in the western Baltic Sea. Helgol. Wiss. Meeresunters., 29(4), 439-459. Arrontes, J. and Underwood, A. J. (1991). Experimental studies on some aspects of the feeding ecology of the intertidal starfish Patiriella exigua. Journal of Experimental Marine Biology and Ecology, 148(2), 255-269. Barker, M. F. and Nichols, D. (1983). Reproduction, recruitment and juvenile ecology of the starfish, Asterias rubens and Marthasterias glacialis. Journal of the Marine Biological Association of the United Kingdom, 63(4), 745-765. Barthelemy, G. (1992). Study on biological control of the proliferation of the starfish: Asterias rubens in Bay of Quiberon. Societe Francaise de Malacologie, Paris (France). Accessed 02 July 2013. Berger, V. Y. and Naumov, A. D. (1996). The effect of salinity upon the adhesive tenacity of Asterias rubens starfishes. Russian Journal of Marine Biology, 22(2), 95-96. Bergmann, M. and Moore, P. G. (2001). Mortality of Asterias rubens and Ophiura ophiura
  • 12. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    12   discarded in the Nephrops fishery of the Clyde Sea area, Scotland. ICES Journal of Marine Science, 58(3), 531-542. Bingham, B. L. and Burr, J. (2000). Causes and consequences of arm damage in the sea star Leptasterias hexactis. Canadian Journal of Zoology, 78(4), 596-605. Dolmer, P. (1998). The interactions between bed structure of Mytilus edulis L. and the predator Asterias rubens L. Journal of Experimental Marine Biology and Ecology, 228(1), 137- 150. Fan, T. J., Du, Y. T., Cong, R. S., Sun, W. J. and Tang, Z. H. (2005). Histological examination of arm regeneration process in starfish Asterias rollestoni. Periodical of Ocean University of China, 35(4), 559-563. Franco, C. F., Soares, R., Pires, E., Santos, R. and Coelho, A. V. (2012). Radial nerve cord protein phosphorylation dynamics during starfish arm tip wound healing events. Electrophoresis, 33(24), 3764-3778. Gallagher, T., Richardson, C. A., Seed, R. and Jones, T. (2008). The seasonal movement and abundance of the starfish, Asterias rubens in relation to mussel farming practice: a case study from the Menai Strait, UK. Journal of Shellfish Research, 27(5), 1209-1215. Guillou, M., Joly-Turquin, G., Leyzour, S., Pernet, P. and Dubois, P. (2012). Factors controlling juvenile growth and population structure of the starfish Asterias rubens in intertidal habitats: field and experimental approaches. Journal of the Marine Biological Association of the United Kingdom, 92(2), 367-378. Hernroth, B., Baden, S., Thorndyke, M. and Dupont, S. (2011). Immune suppression of the echinoderm Asterias rubens (L.) following long-term ocean acidification. Aquatic Toxicology, 103(3-4), 222-224.
  • 13. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    13   Hotchkiss, F. H. C. (2008). Starfish arm stumps: Wound closure patterns and regeneration models. Gulf of Mexico Science, 26(2), 152. Jackson, A. C., Murphy, R. J. and Underwood, A. J. (2008). Patiriella exigua: grazing by a starfish in an overgrazed intertidal system. Marine Ecology Progress Series, 376, 153- 163. Joly-Turquin, G., Dubois, P., Coteur, G., Danis, B. and Leyzour, S. (2009). Effects of the Erika Oil Spill on the common starfish Asterias rubens, evaluated by field and laboratory studies. Archives of Environmental Contamination and Toxicology, 56(2), 209-220. Kaiser, M. J. (1996). Starfish damage as an indicator of trawling intensity. Marine Ecology Progress Series, 134, 303-307. Kamermans, P., Blankendaal, M. and Perdon, J. (2009). Predation of shore crabs (Carcinus maenas (L.)) and starfish (Asterias rubens L.) on blue mussel (Mytilus edulis L.) seed from wild sources and spat collectors. Aquaculture, 290(3-4), 256-262. Kurihara, T. (1999). Effects of sediment type and food abundance on the vertical distribution of the starfish Asterina pectinifera. Marine Ecology Progress Series, 181, 269-277. Kulakovskii, E. and Lezin, P. A. (1999). Influence of the starfish Asterias rubens (Forcipulata, Asteriidae) on vital activity of the bivalve mollusk blue mussel Mytilus edulis (Mytilida, Mytilidae). The Russian Journal of Zoology, 78(5), 596-600. Lawrence, J. M., Byrne, M., Harris, L., Keegan, B. and Freeman, S. (1999). Sublethal arm loss in Asterias amurensis, A. rubens, A. vulgaris, and A. forbesi (Echinodermata : Asteroidea). Vie et Milieu, 49(1), 69-73. Lawrence, J. M. and Larrain, A. (1994). The cost of arm autotomy in the starfish Stichaster striatus. Marine ecology progress series, 109(2-3), 311-313.
  • 14. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    14   Marrs, J., Wilkie, I. C., Sköld, M., Maclaren, W. M. and J. D. McKenzie. (2000). Size-related aspects of arm damage, tissue mechanics, and autotomy in the starfish Asterias rubens. Marine Biology, 137(1), 59-70. Menge, B. A. (1972). Competition for food between two intertidal starfish species and its effect on body size and feeding. Ecology, 53(4), 635-644. Menge, B. A. (1983). Components of predation intensity in the low zone of the New England rocky intertidal region. Oecologia, 58(2), 141-155. Menge, B. A. (1972). Foraging strategy of a starfish in relation to actual prey availability and environmental predictability. Ecological Monographs, 42(1), 25-50. Menge, J. L. and Menge, B. A. (1974). Role of resource allocation, aggression and spatial heterogeneity in coexistence of two competing intertidal starfish. Ecological Monographs, 44(2), 189-209. The National Academy of Sciences (NAS). The Guide for the Use and Care of Laboratory Animals, 8th Edition. Washington D. C.: The National Academies Press, 2011. Print. Norberg, J. and Tedengren, M. (1995). Attack behavior and predatory success of Asterias rubens L. related to differences in size and morphology of the prey mussel Mytilus edulis L. Journal of Experimental Marine Biology and Ecology, 186(2), 207-220. Paine, R. T. (1976). Size-limited predation: an observational and experimental approach with the Mytilus-Pisaster interaction. Ecology, 57(5), 858-873. Penney, A. J. and Griffiths, C. L. (1984). Prey selection and the impact of the starfish Marthasterias glacialis (L.) and other predators on the mussel Choromytilus meridionalis (Krauss). Journal of Experimental Marine Biology and Ecology, 75(1), 19-36.
  • 15. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    15   Ramsay, K., Bergmann, M., Veale, L. O., Richardson, C. A., Kaiser, M. J., Vize, S. J. and Feist, S. W. (2001). Damage, autotomy and arm regeneration in starfish caught by towed demersal fishing gears. Marine Biology, 138(3), 527-536. Ramsay, K., Kaiser, M. and Richardson, C. (2001). Invest in arms: Behavioural and energetic implications of multiple autotomy in starfish (Asterias rubens). Behavioral Ecology and Sociobiology, 50(4), 360-365. Ramsay, K., Turner, J. R., Vize, S. J. and Richardson, C. A. (2000). A link between predator density and arm loss in the starfish Marthasterias glacialis and Asterias rubens. Journal of the Marine Biological Association of the United Kingdom, 80(3), 565-566. Reimer, O. (1999). Increased gonad ratio in the blue mussel, Mytilus edulis, exposed to starfish predators. Aquatic Ecology, 33(2). 185-192. Reimer, O., Olsson, B. and Tedengren, M. (1995). Growth, physiological rates and behavior of Mytilus edulis exposed to the predator Asterias rubens. Marine and Freshwater Behaviour and Physiology, 25(4), 233-244. Rogers, S. I., Ellis, J. R, Dann, J. S. (2001). The association between arm damage of the common starfish, Asterias rubens, and fishing intensity determined from aerial observation. Sarsia, 86(2), 107-112. Saier, B. (2001). Direct and indirect effects of seastars Asterias rubens on mussel beds (Mytilus edulis) in the Wadden Sea. Journal of Sea Research, 46(1), 29-42. Sano, M., Shimizu, M. and Nose, Y. (1987). Long-term effects of destruction of hermatypic corals by Acanthaster planci infestation on reef fish communities at Iriomote Island, Japan. Marine Ecology, 37, 191-199.
  • 16. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    16   Saranchova, O. L. and Kulakovskii, E. (1982). Water salinity effect on different developmental stages of the starfish Asterias rubens and the common mussel Mytilus edulis. The Russian Journal of Marine Biology, 1, 34-39. Shulgina, G. I. (2006). Learning of inhibition of behavior in the sea star Asterias rubens. Journal of Evolutionary Biochemistry and Physiology, 42(2), 161-165. Smith, G. F. M. (1940). Factors limiting distribution and size in the starfish. Journal of the Fisheries Research Board of Canada, 5(1), 84-103. Tuya, F. and Duarte, P. (2012). Role of food availability in the bathymetric distribution of the starfish Marthasterias glacialis (Lamk.) on reefs of northern Portugal. Scientia Marina (Barcelona), 76(1), 9-15. Vevers, H. G. (1949). The biology of Asterias Rubens L.: Growth and reproduction. Journal of the Marine Biological Association of the United Kingdom, 28(1), 165-187. Voogt, P. A. and Rheenen, J. W. (1976). On the origin of the sterols in the sea star Asterias rubens. Comparative Biochemistry and Physiology, 54(4), 479-482. Whilde, A. (1985). The food of starfish Asterias rubens L. on cultivated and derelict oyster fisheries. Irish Naturalists' Journal, 21(12), 528-532. Wu, L., Chengcheng, J., Sishuo, W. and Jianhao, Lv. (2012). The advantages of the pentameral symmetry of the Starfish. Cornell University Library. Accessed 31 June 2013. Yamada, S. B., Menge, B. A., Baldwin, B. C. and Metcalf, H. (1992). Does starfish removal increase mussel productivity? Journal of Shellfish Research, 11(2), 551. Zeidler, W. (1992). Introduced starfish pose threat to scallops. Australian Fisheries, 51(10), 28- 29.
  • 17. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    17   Table 1. Averages for individual and overall arm length of collected Asterias rubens specimens from Wrightsville Beach, NC and Myrtle Beach, SC. _____________________________________________________________________________________ Arm 1 Arm 2 Arm 3 Arm 4 Arm 5 Overall Average Wrightsville (n=65) 8.75 + 1.49 8.79 + 1.40 8.77 + 1.50 8.82 + 1.46 8.74 + 1.56 8.77 + 1.28* Myrtle (n=65) 8.16 + 1.41 8.06 + 1.45 7.93 + 1.54 8.08 + 1.55 8.26 + 1.17 8.09 + 1.06* _____________________________________________________________________________________ Values in Table 1 are means + standard deviations. Arm lengths expressed in centimeters (cm). Starfish were measured from center to the tip of each arm, even if the arm had been damaged or removed. Starfish from each location were taken from randomly selected feeding spots of pre-determined criteria. Weather conditions for collection days were of pre-determined criteria and were similar for both beach collection sites. *When the overall average arm lengths are compared in a two-tailed t-test, the p-value = 0.001, which is less than the alpha level of α = 0.05.
  • 18. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    18   Figure 1. Legend
  • 19. Brown,  Courtney                                  BIOL  831E                                  Spring  2014                                      2  May  2014                                    19   Figure 1. Average arm length of individual arms of Asterias rubens collected from Myrtle Beach, SC and Wrightsville Beach, NC. Arm lengths are measured in centimeters to the nearest tenth. Error bars are with the standard deviation of each averaged arm length. n = 65 for each group and includes damaged or missing arms.