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Lionfish (Pterois volitans [Linnaeus, 1758]) Show no Diet Preference and
Sex Ratio Difference Between the Atlantic and Caribbean Coasts of
Vieques, Puerto Rico
Lindsay M Ridlen and Marc C Albrecht*
Biology Department, University of Nebraska, Kearney, Nebraska, USA
*Corresponding author: Marc C Albrecht, Biology Department, University of Nebraska, 240111th Ave, Kearney Nebraska, 68849, USA, Tel: 308-865-8713; E-
mail:albrechtm@unk.edu
Received date: March 08, 2016; Accepted date: April 30, 2016; Published date: May 07, 2016
Copyright: © 2016 Ridlen, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use,
distribution and reproduction in any medium, provided the original author and source are credited.
Abstract
Invasive red lionfish (P. volitans) were captured by Hawaiian sling in the coastal waters of Vieques Puerto Rico.
Specimens were weighed, measured for length, and dissected to determine sex and recover stomach contents for
identification. Vieques Puerto Rico has the Atlantic Ocean on the north side, and the Caribbean on the south. We
compared the measured parameters and found that there were no significant differences between fishes captured in
the Atlantic versus the Caribbean. While there appeared to be a difference in the frequency of invertebrates eaten
on two sides of Vieques, it was not statistically significant. This study indicates lionfish living in different habitats
have a wide diet and may grow at similar rates in shallow coastal habitats.
Keywords: Invasive red lionfish; Caribbean; Ecozones; Fisher's exact
test
Introduction
Invasive species are so commonly reported today that some articles
now advocate their impact is both inevitable and less of a problem than
previously thought [1]; this is not true for the lionfish (Pterois
volitans). The lionfish has successfully invaded the Caribbean causing
dramatic reductions in biomass and biodiversity of native species [2,3].
Ecosystem disruption and lowered biodiversity have also resulted [4,5].
Reductions in fish catch for human food and recreation have also
resulted from the increase of lionfish in the Caribbean [6].
Successful invasive species out-compete native species for resources
such as food. One question about invasive species is: are they
successful in different habitats in the areas they invade? In other words,
does an invasive species utilize resources similarly in different habitats?
The island of Vieques provides an opportunity to examine if lionfish
have similar life histories and diets in two marine habitats that are
spatially close but are substantially different.
Lionfish have spread throughout the Caribbean over the last 30
years, reaching Puerto Rico and surrounding islands about 6 years ago
[7,8]. This study examined lionfish from the Atlantic Ocean (south side
of Vieques) and the Caribbean Sea (north side of Vieques) to determine
if there were any differences in total standard length, sex ratio, or diet.
Difference may indicate some variation in life history or food
preference that could be used to help control the spread and
abundance of this species in the Western Hemisphere.
Materials and Methods
This survey was done in the coastal waters of Vieques, Puerto Rico.
This island is 7 km off the southeast coast of Puerto Rico, it is
approximately 4.5 km wide and 32 km long with an area of 350 sq. km.
The climate is subtropical with a number of ecozones from subtropical
wet forest to semi-arid on the eastern end of the island. The climate is
similar to other islands in the Greater Antilles group and the North
Equatorial Current is the primary influence on the marine habitat [9].
The north coast of Vieques opens to the Atlantic and is shallow to
Puerto Rico. The south coast of Vieques is the Caribbean Sea and the
water depth drops off to several hundred meters within a few
kilometers of the shore.
Lionfish were collected from Vieques, Puerto Rico between May 18
and 21 2015. Fish were collected using hand nets and Hawaiian slings
and snorkel gear. Lionfish were captured from five locations around
Vieques: Mosquito Pier (18⁰ 8’ 23” N 65⁰ 30’ 36” W), Esperanza Bay
(18⁰ 5’ 39” N 65⁰ 28’ 19” W), Cayo Afuera (18° 5’ 22” N 65° 28’ 20” W),
and La Chiva (18° 6’ 46” N 65° 23’ 14” W). Water temperatures were
obtained from a NOAA station on the south coast of Vieques (Station #
9752695) and a buoy 20 km north of Vieques (COICOOS Buoy PR3).
These areas were close to shore either in seagrass areas or rocky areas
adjacent to seagrass areas [9].
During collection lionfish were stowed in a large (71 × 18 cm) Zoo
Keeper [10] containment device. Fish were marked with labeled fishing
hooks passed through the lower jaw or caudal fin at the time of
capture. Fish that were not killed by capture were euthanized by
severing the spinal cord or by pithing. Prior to dissection all fish were
weighed using a digital scale. Both total standard length and total
length were taken using a fish measuring board.
During dissection all spines were cut off the pectoral, pelvic, dorsal,
and anal fins and placed into a bottle for disposal. Dissection of the gut
cavity was used to identify sex of the fish. Gonads were located along
the ventral side of the swim bladder on the dorsal side of the cavity and
identified following Green et al. [11]. The stomachs were removed
from the fish and opened for inspection. Prey fish were identified using
Humann and DeLoach [12]. Unidentifiable items were not considered
in data analysis.
Journal of Coastal Zone Management
Ridlen and Albrecht, J Coast Zone Manag 2016, 19:2
http://dx.doi.org/10.4172/jczm.1000425
Research Article Open Access
J Coast Zone Manag
ISSN: JCZM, an open access journal
Volume 19 • Issue 2 • 1000425
Results
The collection areas are shown in Figure 1 [13]. The collection areas
were shallow-water areas amenable to snorkel collection of fish. These
are areas are categorized as seagrass areas or colonized pavement/
patchy seagrass by NOAA survey [14]. Water temperatures during the
test were not measured directly however we have obtained data from
two monitoring stations. The Atlantic water temperature was measured
by a buoy with a sensor 1m under the surface and recorded an average
temperature of 27.9°C during the study period [15]. A NOAA tide level
station on the Esperanza pier where some lionfish collection was done
has a sensor approximately 1.8 m under the surface and recorded an
average water temperature of 28.4 during the study period [16].
Figure 1: Map of Vieques, Puerto Rico showing location areas, circles, and scale bar [13]. The coast of Puerto Rico can be seen on the west side
of the map.
A total of 25 lionfish were captured, 12 females, 11 males, and 2
individuals that were too small to have developed gonads. Table 1 gives
the average mass and total standard lengths of the fish are show with
standard errors. Anderson-Darling tests for mass and total standard
length indicated both sets of data were non-normally distributed (p =
0.0031 and p = 0.0084 respectively). The data distribution for the mass
data was log transformed to normality allowing for t-tests to be
conducted on these data. The total standard length data were tested by
Mann Whitney U-test.
All fish Atlantic side fish
Caribbean side
fish
Fish mass 122.3 (± 13.9) 134.0 (± 21.3) 104.8 (± 13.44)
Total standard
length
15.19 (± 0.570) 15.73 (± 0.888) 14.38 (± 0.455)
Male mass 152.4 (± 25.8) 165.5 (±32.7) 117.6 (± 36.4)
Female mass 93.7 (± 9.27) 85.70 (± 32.7) 99.4 (± 13.4)
Male length 15.58 (± 0.781) 16.35 (± 0.940) 13.53 (± 0.219)
Female length 14.36 (± 0.424) 13.82 (± 0.545) 14.74 (± 0.603)
Table 1: P. volitans masses from the individuals collected in shallow
waters of Vieques, Puerto Rico. Masses are in grams with standard
errors in parentheses.
The mass t-test showed male and female fish were different weights
(t-value 2.09, p-value = 0.0491) with males being heavier. Fish were not
significantly different in mass between the Atlantic and Caribbean side
of Vieques.
Total standard length (H-statistic = 0.05, p-value = 0.815) and mass
(H-statistic 0.03, p-value 0.870) were not significantly different
between the two sides of Vieques as tested by Kruskal-Wallis test. There
were 5 females and 8 males caught on the Atlantic side of Vieques,
while 7 females and 4 males caught on the south coast. When tested by
Fisher’s Exact test this was found to not be a significant difference (p =
0.414).
Thirteen fish had stomachs with undigested contents. They
contained 26 prey items, 21 of which were identified. Stomach contents
in descending order of abundance were: Atlantic grey shrimp
(Litopenaeus setiferus), banded coral shrimp (Stenopus hispidus),
silverside (Hypoatherina harringtonensis), sardines (Harengula
humeralis), and damselfish (Stegastes varabilis). Prey items were
categorized as either invertebrate or vertebrate for analysis. The
occurrence of the two prey types found on the Atlantic versus the
Caribbean side of Vieques was tested by Fisher’s Exact test. The result,
p = 0.0978, suggests there was no difference in the prey type being
eaten on the two sides Vieques. However this result should be
interpreted with caution as the small sample size was small.
Citation: Lindsay M Ridlen, Marc C Albrecht (2016) Lionfish (Pterois volitans [Linnaeus, 1758]) Show no Diet Preference and Sex Ratio
Difference Between the Atlantic and Caribbean Coasts of Vieques, Puerto Rico. J Coast Zone Manag 19: 425. doi:10.4172/jczm.
1000425
Page 2 of 3
J Coast Zone Manag
ISSN: JCZM, an open access journal
Volume 19 • Issue 2 • 1000425
Discussion
The only significant difference in lionfish was between the sexes in
mass. P. volitans collected in shallow water on the two sides of Vieques
did not show any significant differences in the other parameters
measured. This indicates lionfish appear unaffected by differences in
substrate, currents, prey species take, and other aspects associated by
living in two different habitats. The similar sex ratio seen on the two
sides of Vieques agrees with result seen by Barbour et al. [17] off the
coast of North Carolina, where they caught a total of 927 males and
718 females.
These results were unexpected. Other species show that the two
marine bodies (Caribbean and Atlantic) that meet in Vieques have
distinct differences. While Rhizophora mangle (red mangrove) is a tree
species, and thus may have less ability to disperse than lionfish, the
species has had millions of years in which to intermix genetically
around this small island. However, the R. mangle on the north side of
the island is more similar to Florida populations, over 1,500 km away,
than populations on the south side of Vieques, about 10 km away [18].
A similar pattern, though at a larger spatial scale was found to be true
of the native giant land crab, Cardisoma guanhumi [19].
Butterfield et al. [20] have done a wide-scale study of the lionfish
phylogeographic structure of the Caribbean and Western Atlantic.
They found a genetic break between the area of Puerto Rico, the Virgin
Islands, and Bonaire and the other areas of the Caribbean and Western
Atlantic. The study however did not look at the spatial scale of
individual islands or the border between the Caribbean and Atlantic
specifically [20].
This study demonstrated how plastic the diets of lionfish can be as
well as how shallow-water individuals are similar while living in
different marine microhabitats. Their adaptability combined with the
ability of a mature female lionfish to produce over 2 million eggs per
year contributes to the rapid population growth of this species in new
habitats. Only strong human hunting pressure has been found to keep
P. volitans numbers low, and even this is only partially effective [21].
References
1. Marris E (2014) Opinion: it’s time to stop thinking that all non-native
species are evil. National Geographic.
2. Arias-Gonzáles JE, Gonzáles CG, Cabrera JL, Christensen V (2011)
Predicted impact of the invasive lionfish Pterois volitans on the food web
of a Caribbean coral reef. Environ. Res. 111: 917-925.
3. Kulbicki M, Beets J, Chabanet P, Cure K, Darling E, et al. (2012)
Distribution of Indo Pacific lionfishes Pterois spp. in their native ranges:
implications for the Atlantic invasion. Mar Ecol Prog Ser 446: 189-205.
4. Lesser MP, Slattery M (2011) Phase shift to algal dominated communities
at mesophotic depths associated with lionfish (Pterois volitans) invasion
on a Bahamian coral reef. Biol Invasions 13: 1855-1868.
5. Green SJ, Akins JL, Maljkovic AM, Cote IM (2012a) Invasive lionfish
drive Atlantic coral reef fish declines. Plos One: 7.
6. Morris JA, Akins JL (2009) Feeding ecology of invasive lionfish (Pterois
volitans) in Bahamian archipelago. Environ Biol Fish 86: 389-399.
7. Schofield PJ (2010) Update on geographic spread of invasive lionfishes
(Pterois volitans [Linnaeus, 1758] and P. miles [Bennett, 1828]) in the
Western North Atlantic Ocean, Caribbean Sea and Gulf of Mexico. Aquat
Invasions 5: 11-122.
8. Toledo-Hernández C, Velez-Zuazo X, Ruizdiaz CP, Patricia AR, Mege P,
et al. 2014. Population ecology and genetics of the invasive lionfish in
Puerto Rico. Aquat. Invasions 9: 227-237.
9. Bauer LJ, Menza C, Foley KA, Kendall MS (2008) An ecological
characterization of the Marine Resources of Vieques, Puerto Rico Part I:
Historical Data Synthesis. Prepared by the National Centers for Coastal
Ocean Science (NCCOS) Biogeography Branch in cooperation with the
Office of Response and Restoration. Silver Spring, MD> NOAA Technical
Memorandum NOS NCCOS: 121.
10. Zkstore (2016) Zoo Keeper Containment System.
11. Green SJ, Akins JL, Morris JA (2012b) Lionfish dissection: techniques and
applications. NOAA Technical Memorandum NOS NCCOS 139: 1-24.
12. Humann P, DeLoach N (2014) Reef Fish Identification: Florida Caribbean
Bahamas. Jacksonville, Florida. New World Publications.
13. ESRI (2016) Environmental Systems Research Institute. ArcGIS Online
Maps.
14. NOAA (2001) U.S. National Oceanic and Atmospheric Administration.
National Ocean Service, National Centers for Coastal Ocean Science
Biogeography Program. 2001. Benthic Habitats of Puerto Rico and the
U.S. Virgin Islands. CD-ROM. Silver Spring, MD: National Oceanic and
Atmospheric Administration.
15. CariCOOS (2016) Caribbean Coastal Ocean Observing System. Data
retrieved for moored buoy PR303.
16. NOAA (2016) U.S. National Oceanic and Atmospheric Administration.
Tides and Currents Tidal Stations, Station # 9752695.
17. Barbour AB, Allen MS, Frazer TK, Sherman KD (2011) Evaluating the
potential efficacy of invasive lionfish (Pterois volitans) removals. Plos
One: 6.
18. Albrecht M, Kneeland K, Lindroth E, Foster J (2013) Genetic diversity
and relatedness of the mangrove Rhizophora mangle L. (Rizophoraceae)
using amplified fragment polymorphism (AFLP) among locations in
Florida, USA and the Caribbean. Journal of Coast Conser 17: 483-491.
19. Amaral MA, Albrecht M, McKinley AS, Ferreira de Carvalho AM, de
Sousa SC (2015) Mitochondrial DNA Variation reveals a sharp genetic
break within the distribution of the blue land crab Cardisoma guanhumi
in the Western Central Atlantic. Molecules 20: 15158-15174.
20. Butterfield JS, Diaz-Ferguson E, Silliman BR, Saunders JW, Buddo D
(2015) Wide-ranging phylogeographic structure of invasive red lionfish in
the Western Atlantic and Greater Caribbean. 2015 Marine Biology 162:
773-781.
21. de León R, Vane K, Bertuol P, Chamberland VC, Simal F (2013)
Effectiveness of lionfish removal efforts in Southern Caribbean. Endang
Species Res 22: 175-182.
Citation: Lindsay M Ridlen, Marc C Albrecht (2016) Lionfish (Pterois volitans [Linnaeus, 1758]) Show no Diet Preference and Sex Ratio
Difference Between the Atlantic and Caribbean Coasts of Vieques, Puerto Rico. J Coast Zone Manag 19: 425. doi:10.4172/jczm.
1000425
Page 3 of 3
J Coast Zone Manag
ISSN: JCZM, an open access journal
Volume 19 • Issue 2 • 1000425

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Ridlen Journal of Coastal Zone Management

  • 1. Lionfish (Pterois volitans [Linnaeus, 1758]) Show no Diet Preference and Sex Ratio Difference Between the Atlantic and Caribbean Coasts of Vieques, Puerto Rico Lindsay M Ridlen and Marc C Albrecht* Biology Department, University of Nebraska, Kearney, Nebraska, USA *Corresponding author: Marc C Albrecht, Biology Department, University of Nebraska, 240111th Ave, Kearney Nebraska, 68849, USA, Tel: 308-865-8713; E- mail:albrechtm@unk.edu Received date: March 08, 2016; Accepted date: April 30, 2016; Published date: May 07, 2016 Copyright: © 2016 Ridlen, et al. This is an open-access article distributed under the terms of the Creative Commons Attribution License, which permits unrestricted use, distribution and reproduction in any medium, provided the original author and source are credited. Abstract Invasive red lionfish (P. volitans) were captured by Hawaiian sling in the coastal waters of Vieques Puerto Rico. Specimens were weighed, measured for length, and dissected to determine sex and recover stomach contents for identification. Vieques Puerto Rico has the Atlantic Ocean on the north side, and the Caribbean on the south. We compared the measured parameters and found that there were no significant differences between fishes captured in the Atlantic versus the Caribbean. While there appeared to be a difference in the frequency of invertebrates eaten on two sides of Vieques, it was not statistically significant. This study indicates lionfish living in different habitats have a wide diet and may grow at similar rates in shallow coastal habitats. Keywords: Invasive red lionfish; Caribbean; Ecozones; Fisher's exact test Introduction Invasive species are so commonly reported today that some articles now advocate their impact is both inevitable and less of a problem than previously thought [1]; this is not true for the lionfish (Pterois volitans). The lionfish has successfully invaded the Caribbean causing dramatic reductions in biomass and biodiversity of native species [2,3]. Ecosystem disruption and lowered biodiversity have also resulted [4,5]. Reductions in fish catch for human food and recreation have also resulted from the increase of lionfish in the Caribbean [6]. Successful invasive species out-compete native species for resources such as food. One question about invasive species is: are they successful in different habitats in the areas they invade? In other words, does an invasive species utilize resources similarly in different habitats? The island of Vieques provides an opportunity to examine if lionfish have similar life histories and diets in two marine habitats that are spatially close but are substantially different. Lionfish have spread throughout the Caribbean over the last 30 years, reaching Puerto Rico and surrounding islands about 6 years ago [7,8]. This study examined lionfish from the Atlantic Ocean (south side of Vieques) and the Caribbean Sea (north side of Vieques) to determine if there were any differences in total standard length, sex ratio, or diet. Difference may indicate some variation in life history or food preference that could be used to help control the spread and abundance of this species in the Western Hemisphere. Materials and Methods This survey was done in the coastal waters of Vieques, Puerto Rico. This island is 7 km off the southeast coast of Puerto Rico, it is approximately 4.5 km wide and 32 km long with an area of 350 sq. km. The climate is subtropical with a number of ecozones from subtropical wet forest to semi-arid on the eastern end of the island. The climate is similar to other islands in the Greater Antilles group and the North Equatorial Current is the primary influence on the marine habitat [9]. The north coast of Vieques opens to the Atlantic and is shallow to Puerto Rico. The south coast of Vieques is the Caribbean Sea and the water depth drops off to several hundred meters within a few kilometers of the shore. Lionfish were collected from Vieques, Puerto Rico between May 18 and 21 2015. Fish were collected using hand nets and Hawaiian slings and snorkel gear. Lionfish were captured from five locations around Vieques: Mosquito Pier (18⁰ 8’ 23” N 65⁰ 30’ 36” W), Esperanza Bay (18⁰ 5’ 39” N 65⁰ 28’ 19” W), Cayo Afuera (18° 5’ 22” N 65° 28’ 20” W), and La Chiva (18° 6’ 46” N 65° 23’ 14” W). Water temperatures were obtained from a NOAA station on the south coast of Vieques (Station # 9752695) and a buoy 20 km north of Vieques (COICOOS Buoy PR3). These areas were close to shore either in seagrass areas or rocky areas adjacent to seagrass areas [9]. During collection lionfish were stowed in a large (71 × 18 cm) Zoo Keeper [10] containment device. Fish were marked with labeled fishing hooks passed through the lower jaw or caudal fin at the time of capture. Fish that were not killed by capture were euthanized by severing the spinal cord or by pithing. Prior to dissection all fish were weighed using a digital scale. Both total standard length and total length were taken using a fish measuring board. During dissection all spines were cut off the pectoral, pelvic, dorsal, and anal fins and placed into a bottle for disposal. Dissection of the gut cavity was used to identify sex of the fish. Gonads were located along the ventral side of the swim bladder on the dorsal side of the cavity and identified following Green et al. [11]. The stomachs were removed from the fish and opened for inspection. Prey fish were identified using Humann and DeLoach [12]. Unidentifiable items were not considered in data analysis. Journal of Coastal Zone Management Ridlen and Albrecht, J Coast Zone Manag 2016, 19:2 http://dx.doi.org/10.4172/jczm.1000425 Research Article Open Access J Coast Zone Manag ISSN: JCZM, an open access journal Volume 19 • Issue 2 • 1000425
  • 2. Results The collection areas are shown in Figure 1 [13]. The collection areas were shallow-water areas amenable to snorkel collection of fish. These are areas are categorized as seagrass areas or colonized pavement/ patchy seagrass by NOAA survey [14]. Water temperatures during the test were not measured directly however we have obtained data from two monitoring stations. The Atlantic water temperature was measured by a buoy with a sensor 1m under the surface and recorded an average temperature of 27.9°C during the study period [15]. A NOAA tide level station on the Esperanza pier where some lionfish collection was done has a sensor approximately 1.8 m under the surface and recorded an average water temperature of 28.4 during the study period [16]. Figure 1: Map of Vieques, Puerto Rico showing location areas, circles, and scale bar [13]. The coast of Puerto Rico can be seen on the west side of the map. A total of 25 lionfish were captured, 12 females, 11 males, and 2 individuals that were too small to have developed gonads. Table 1 gives the average mass and total standard lengths of the fish are show with standard errors. Anderson-Darling tests for mass and total standard length indicated both sets of data were non-normally distributed (p = 0.0031 and p = 0.0084 respectively). The data distribution for the mass data was log transformed to normality allowing for t-tests to be conducted on these data. The total standard length data were tested by Mann Whitney U-test. All fish Atlantic side fish Caribbean side fish Fish mass 122.3 (± 13.9) 134.0 (± 21.3) 104.8 (± 13.44) Total standard length 15.19 (± 0.570) 15.73 (± 0.888) 14.38 (± 0.455) Male mass 152.4 (± 25.8) 165.5 (±32.7) 117.6 (± 36.4) Female mass 93.7 (± 9.27) 85.70 (± 32.7) 99.4 (± 13.4) Male length 15.58 (± 0.781) 16.35 (± 0.940) 13.53 (± 0.219) Female length 14.36 (± 0.424) 13.82 (± 0.545) 14.74 (± 0.603) Table 1: P. volitans masses from the individuals collected in shallow waters of Vieques, Puerto Rico. Masses are in grams with standard errors in parentheses. The mass t-test showed male and female fish were different weights (t-value 2.09, p-value = 0.0491) with males being heavier. Fish were not significantly different in mass between the Atlantic and Caribbean side of Vieques. Total standard length (H-statistic = 0.05, p-value = 0.815) and mass (H-statistic 0.03, p-value 0.870) were not significantly different between the two sides of Vieques as tested by Kruskal-Wallis test. There were 5 females and 8 males caught on the Atlantic side of Vieques, while 7 females and 4 males caught on the south coast. When tested by Fisher’s Exact test this was found to not be a significant difference (p = 0.414). Thirteen fish had stomachs with undigested contents. They contained 26 prey items, 21 of which were identified. Stomach contents in descending order of abundance were: Atlantic grey shrimp (Litopenaeus setiferus), banded coral shrimp (Stenopus hispidus), silverside (Hypoatherina harringtonensis), sardines (Harengula humeralis), and damselfish (Stegastes varabilis). Prey items were categorized as either invertebrate or vertebrate for analysis. The occurrence of the two prey types found on the Atlantic versus the Caribbean side of Vieques was tested by Fisher’s Exact test. The result, p = 0.0978, suggests there was no difference in the prey type being eaten on the two sides Vieques. However this result should be interpreted with caution as the small sample size was small. Citation: Lindsay M Ridlen, Marc C Albrecht (2016) Lionfish (Pterois volitans [Linnaeus, 1758]) Show no Diet Preference and Sex Ratio Difference Between the Atlantic and Caribbean Coasts of Vieques, Puerto Rico. J Coast Zone Manag 19: 425. doi:10.4172/jczm. 1000425 Page 2 of 3 J Coast Zone Manag ISSN: JCZM, an open access journal Volume 19 • Issue 2 • 1000425
  • 3. Discussion The only significant difference in lionfish was between the sexes in mass. P. volitans collected in shallow water on the two sides of Vieques did not show any significant differences in the other parameters measured. This indicates lionfish appear unaffected by differences in substrate, currents, prey species take, and other aspects associated by living in two different habitats. The similar sex ratio seen on the two sides of Vieques agrees with result seen by Barbour et al. [17] off the coast of North Carolina, where they caught a total of 927 males and 718 females. These results were unexpected. Other species show that the two marine bodies (Caribbean and Atlantic) that meet in Vieques have distinct differences. While Rhizophora mangle (red mangrove) is a tree species, and thus may have less ability to disperse than lionfish, the species has had millions of years in which to intermix genetically around this small island. However, the R. mangle on the north side of the island is more similar to Florida populations, over 1,500 km away, than populations on the south side of Vieques, about 10 km away [18]. A similar pattern, though at a larger spatial scale was found to be true of the native giant land crab, Cardisoma guanhumi [19]. Butterfield et al. [20] have done a wide-scale study of the lionfish phylogeographic structure of the Caribbean and Western Atlantic. They found a genetic break between the area of Puerto Rico, the Virgin Islands, and Bonaire and the other areas of the Caribbean and Western Atlantic. The study however did not look at the spatial scale of individual islands or the border between the Caribbean and Atlantic specifically [20]. This study demonstrated how plastic the diets of lionfish can be as well as how shallow-water individuals are similar while living in different marine microhabitats. Their adaptability combined with the ability of a mature female lionfish to produce over 2 million eggs per year contributes to the rapid population growth of this species in new habitats. Only strong human hunting pressure has been found to keep P. volitans numbers low, and even this is only partially effective [21]. References 1. Marris E (2014) Opinion: it’s time to stop thinking that all non-native species are evil. National Geographic. 2. Arias-Gonzáles JE, Gonzáles CG, Cabrera JL, Christensen V (2011) Predicted impact of the invasive lionfish Pterois volitans on the food web of a Caribbean coral reef. Environ. Res. 111: 917-925. 3. Kulbicki M, Beets J, Chabanet P, Cure K, Darling E, et al. (2012) Distribution of Indo Pacific lionfishes Pterois spp. in their native ranges: implications for the Atlantic invasion. Mar Ecol Prog Ser 446: 189-205. 4. Lesser MP, Slattery M (2011) Phase shift to algal dominated communities at mesophotic depths associated with lionfish (Pterois volitans) invasion on a Bahamian coral reef. Biol Invasions 13: 1855-1868. 5. Green SJ, Akins JL, Maljkovic AM, Cote IM (2012a) Invasive lionfish drive Atlantic coral reef fish declines. Plos One: 7. 6. Morris JA, Akins JL (2009) Feeding ecology of invasive lionfish (Pterois volitans) in Bahamian archipelago. Environ Biol Fish 86: 389-399. 7. Schofield PJ (2010) Update on geographic spread of invasive lionfishes (Pterois volitans [Linnaeus, 1758] and P. miles [Bennett, 1828]) in the Western North Atlantic Ocean, Caribbean Sea and Gulf of Mexico. Aquat Invasions 5: 11-122. 8. Toledo-Hernández C, Velez-Zuazo X, Ruizdiaz CP, Patricia AR, Mege P, et al. 2014. Population ecology and genetics of the invasive lionfish in Puerto Rico. Aquat. Invasions 9: 227-237. 9. Bauer LJ, Menza C, Foley KA, Kendall MS (2008) An ecological characterization of the Marine Resources of Vieques, Puerto Rico Part I: Historical Data Synthesis. Prepared by the National Centers for Coastal Ocean Science (NCCOS) Biogeography Branch in cooperation with the Office of Response and Restoration. Silver Spring, MD> NOAA Technical Memorandum NOS NCCOS: 121. 10. Zkstore (2016) Zoo Keeper Containment System. 11. Green SJ, Akins JL, Morris JA (2012b) Lionfish dissection: techniques and applications. NOAA Technical Memorandum NOS NCCOS 139: 1-24. 12. Humann P, DeLoach N (2014) Reef Fish Identification: Florida Caribbean Bahamas. Jacksonville, Florida. New World Publications. 13. ESRI (2016) Environmental Systems Research Institute. ArcGIS Online Maps. 14. NOAA (2001) U.S. National Oceanic and Atmospheric Administration. National Ocean Service, National Centers for Coastal Ocean Science Biogeography Program. 2001. Benthic Habitats of Puerto Rico and the U.S. Virgin Islands. CD-ROM. Silver Spring, MD: National Oceanic and Atmospheric Administration. 15. CariCOOS (2016) Caribbean Coastal Ocean Observing System. Data retrieved for moored buoy PR303. 16. NOAA (2016) U.S. National Oceanic and Atmospheric Administration. Tides and Currents Tidal Stations, Station # 9752695. 17. Barbour AB, Allen MS, Frazer TK, Sherman KD (2011) Evaluating the potential efficacy of invasive lionfish (Pterois volitans) removals. Plos One: 6. 18. Albrecht M, Kneeland K, Lindroth E, Foster J (2013) Genetic diversity and relatedness of the mangrove Rhizophora mangle L. (Rizophoraceae) using amplified fragment polymorphism (AFLP) among locations in Florida, USA and the Caribbean. Journal of Coast Conser 17: 483-491. 19. Amaral MA, Albrecht M, McKinley AS, Ferreira de Carvalho AM, de Sousa SC (2015) Mitochondrial DNA Variation reveals a sharp genetic break within the distribution of the blue land crab Cardisoma guanhumi in the Western Central Atlantic. Molecules 20: 15158-15174. 20. Butterfield JS, Diaz-Ferguson E, Silliman BR, Saunders JW, Buddo D (2015) Wide-ranging phylogeographic structure of invasive red lionfish in the Western Atlantic and Greater Caribbean. 2015 Marine Biology 162: 773-781. 21. de León R, Vane K, Bertuol P, Chamberland VC, Simal F (2013) Effectiveness of lionfish removal efforts in Southern Caribbean. Endang Species Res 22: 175-182. Citation: Lindsay M Ridlen, Marc C Albrecht (2016) Lionfish (Pterois volitans [Linnaeus, 1758]) Show no Diet Preference and Sex Ratio Difference Between the Atlantic and Caribbean Coasts of Vieques, Puerto Rico. J Coast Zone Manag 19: 425. doi:10.4172/jczm. 1000425 Page 3 of 3 J Coast Zone Manag ISSN: JCZM, an open access journal Volume 19 • Issue 2 • 1000425