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Benthic amphipods (Amphipoda: Gammaridea and Corophiidea) from the Mexican southeast sector of the Gulf of Mexico: checklist, new records and zoogeographic comments

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The southeast region of the Gulf of Mexico is considered to be biologically important, because it is a connection and transition zone between the Caribbean and the Gulf of Mexico, harboring great marine biodiversity. Nevertheless, benthic amphipods have been poorly studied in the Mexican southeast sector of the Gulf of Mexico with few studies listing species. The aim of this study is to provide an update checklist of species for the Mexican southeast sector (based on literature review and records from the present study) as well as a brief zoogeographical analysis for the Gulf of Mexico amphipod fauna, putting them in context with the fauna on the tropical western Atlantic. Fifty-five species were listed for the Mexican southeast sector; 36 of them showed a geographical extension to the Yucatan continental shelf representing 23 new records for the Mexican southeast sector, nine for the southeast region and four for the Gulf of Mexico. Based on the zoogeographical analysis, there is support of the application of Carolinian and Caribbean zoogeographic provinces to amphipods in the Gulf of Mexico.
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Accepted by G. Karaman: 11 Feb. 2013; published: 26 Mar. 2013
ZOOTAXA
ISSN 1175-5326 (print edition)
ISSN 1175-5334 (online edition)
Copyright © 2013 Magnolia Press
Zootaxa 3635 (2): 137173
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http://dx.doi.org/10.11646/zootaxa.3635.2.4
http://zoobank.org/urn:lsid:zoobank.org:pub:A64F4DF7-B31C-45FE-A9B3-BF933609D9DC
Benthic amphipods (Amphipoda: Gammaridea and Corophiidea)
from the Mexican southeast sector of the Gulf of Mexico: checklist,
new records and zoogeographic comments
CARLOS E. PAZ-RÍOS1 & PEDRO-LUIS ARDISSON2
Departamento de Recursos del Mar, Cinvestav, Carretera antigua a Progreso, km 6, Apdo. Postal 73, Cordemex 97310 Merida,
Yucatan, Mexico. E-mail: 1cpaz@mda.cinvestav.mx, 2ardisson@mda.cinvestav.mx
Abstract
The southeast region of the Gulf of Mexico is considered to be biologically important, because it is a connection and
transition zone between the Caribbean and the Gulf of Mexico, harboring great marine biodiversity. Nevertheless, benthic
amphipods have been poorly studied in the Mexican southeast sector of the Gulf of Mexico with few studies listing
species. The aim of this study is to provide an update checklist of species for the Mexican southeast sector (based on
literature review and records from the present study) as well as a brief zoogeographical analysis for the Gulf of Mexico
amphipod fauna, putting them in context with the fauna on the tropical western Atlantic. Fifty-five species were listed for
the Mexican southeast sector; 36 of them showed a geographical extension to the Yucatan continental shelf representing
23 new records for the Mexican southeast sector, nine for the southeast region and four for the Gulf of Mexico. Based on
the zoogeographical analysis, there is support of the application of Carolinian and Caribbean zoogeographic provinces to
amphipods in the Gulf of Mexico.
Key words: Yucatan, Crustacea, Peracarida, marine, biodiversity, biogeography
Introduction
Benthic amphipods inhabit a variety of substrata, including hard and soft bottoms, submerged aquatic vegetation
and other benthic organisms (e.g. sponges, corals, anemones, tunicates). The high morphological diversity of
amphipods dwelling on sandy sediments suggests a great adaptive radiation (Bousfield 1970). Benthic amphipods
obtain a great part of their food from the sediment or water column, displaying major feeding modes such as
detritivory, filter-feeding, herbivory, predatory, scavenging and sand-cleaning (Bousfield 1973; Biernbaum 1979).
This ecological diversity has conferred them the ability to colonize all marine habitats and a broad interval of
depth, from intertidal to abyssal zone (Thomas 1993; Escobar-Briones & Winfield 2003; LeCroy et al. 2009).
Biologically, the reproductive strategy in amphipods is to brood their eggs in a marsupium, releasing them as
miniature versions of adults (direct development), and in some cases providing parental care (Thiel 1999). Thereby
species show a trade-off condition to achieve reproductive success (Sainte-Marie 1991; William et al. 2001).
Amphipods are important for bioturbation because they promote the interchange of gases (mainly oxygen and
nitrogen) and contribute high rates of secondary production for energy flow to higher trophic levels (Marques &
Bellan-Santini 1993; Duffy & Hay 2000; Soliman & Rowe 2008). These ecological and biological traits have
positioned amphipods as one key link between the sediment and the water column.
Despite their importance, there are many marine regions where amphipods are often ignored, leaving a gap of
information which provides an erroneous assessment of the regional biodiversity. One approximation to solve this
crisis is to make checklists of species based on reliable identification or taxonomic revision. This is the first step in
establishing a framework of how many and which species are in which habitats (alpha, beta and gamma diversity).
According to Hendrickx and Harvey (1999), a checklist of species provides information about the complexity of
the biological communities and the live resources available, helping to recognize and to delimit the protected areas
and to identify potential anthropogenic impacts.
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Regarding amphipod fauna in the Gulf of Mexico (GM), the study of gammarideans sensu lato has been
constant and productive. It can be noted in the number of species, for instance, of the 418 species (excluding
anchialine, freshwater and troglobitic) documented in the tropical western Atlantic (TWA) (Ortiz et al. 2007), 131
of them (31%) have been reported in the GM (LeCroy et al. 2009). In addition, based on the composition and
abundance of benthic macrofauna, amphipods in the northeastern region of the GM represent the second most
important taxa, just below the polychaetes (Brooks et al. 2006).
However, excluding the relatively well-known amphipod fauna of the Florida Keys and Northwestern Cuba,
this taxon has been poorly studied in the southeast region of the GM. For instance, to date only two studies
recording benthic amphipods in the Mexican southeast sector have been published (Ortiz 1979; Oliva-Rivera &
Jiménez-Cueto 1997), becoming the sector with the lowest number of species in the GM (Escobar-Briones &
Winfield 2003). Likewise, only two studies describing the distribution and abundance patterns of species have been
published (Paz-Ríos 2008; Rodríguez-Pliego et al. 2011). More recently, in adjacent waters toward the southeastern
region Escobar-Briones and Jiménez-Guadarrama (2010) described the distribution and abundance patterns of
peracarids (including amphipods) on the Campeche Bank, although their analysis was at the family level. Simões et
al. (2010) provided a list of crustaceans for the coast of Yucatan State, including amphipods, but this list is partially
based on unconfirmed material from biological collections.
Therefore, for updating and providing new information on the amphipod fauna in southeastern GM, the aims
of this study are 1) to provide an annotated checklist of species for the Mexican southeast sector of the GM, 2) to
report geographical extensions for those species and 3) to provide a brief analysis of zoogeographical affinity of the
GM amphipod fauna inside the TWA amphipod fauna.
Methods
Study area. Sampling was carried out in the Yucatan continental shelf at 20–40 m depth, in the southeast region of
the GM (Fig 1). The Yucatan continental shelf includes the submerged portion of a shallow limestone plateau,
which is expanded 220 km toward the northeast (Logan et al. 1969). These same authors also state that the inner
continental shelf has a gentle slope from south to north and is bounded on the west, north, and east by a precipitous
continental slope that plunges from the submerged plateau margin to the abyssal depths of the GM and Caribbean.
The water column on the continental shelf forms part of a superficial layer (100–150 m) which is well-known as a
layer of mixture (Pica & Pineda 1991). The dominant current comes from a branch of the North Atlantic current,
which penetrates through the Yucatan strait to the GM (DiMarco et al. 2005). Substratum is mainly composed of
carbonated sand of autochthonous origin with more than 75% of carbonates, which reflects the presence of coral
reefs on the shelf (Logan et al. 1969; Balsam & Beeson 2003).
Sample collection and processing. Benthic samples were collected on board the R/V Onjuko during an
oceanographic cruise, “Yucatan 2004-A” (April 516, 2004) carried out by the Department of Oceanography of the
Mexican Navy. Eighteen stations were positioned (Fig 1A, Table 1) and each station was sampled in duplicate using a
Petite Ponar grab (0.23 m-2), excepting the stations 2, 14 and 18 due to adverse meteorological conditions.
Both sediment and fauna were analyzed. Sediment texture was analyzed following Bale and Kenny (2005) and is
characterized in Table 1. Faunal samples were anaesthetised with MgCl2, and then fixed with 10% formaldehyde
solution buffered with seawater before storage. The samples were washed through 500 μm size mesh and transferred
to 70% ethanol. Species were sorted and identified to the lower taxonomical level. All species are deposited in the
Colección de Invertebrados Bentónicos de Yucatán (CYMX), Cinvestav; each species herein reported has a catalog
number for the collection (collected and identified by C.E. Paz-Ríos). The classification of Gammaridea is based
on Martin and Davis (2001). The classification of Corophiidea is based on Myers and Lowry (2003); members of
family Caprellidae and Cyamidae were excluded.
Data analysis. An annotated checklist of amphipods on the Mexican southeast sector is provided. It constitutes
a compilation based on literature and records from identified species in the present study; doubtful records and
personal communication were excluded. The checklist includes material examined (if it is the case), distribution,
habitat and remarks (if necessary).
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BENTHIC AMPHIPODS IN SOUTHEASTERN GULF OF MEXICO
FIGURE 1. Localization of the study area in the Gulf of Mexico. (A) Sampling stations on the northern Yucatan continental shelf;
() sample not collected due to adverse meteorological conditions. (B) Nested spatial scales in the Gulf of Mexico for recording
the geographical extension of species; dashed line represents the Mexico's exclusive economic zones.
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TABLE 1. Summary information for sampling stations on the northern Yucatan continental shelf, southeastern Gulf of Mexico.
The sampling stations 12, 14 and 18 were not collected due to adverse meteorological conditions.
From identified species, the most abundant and widely distributed species were determined by the absolute
abundance (Ind) and relative frequency (%). To record the geographic extension of species three nested spatial scales
were established (Fig 1B): 1) Mexican southeast sector, 2) southeast region and 3) GM.
To explore the zoogeographical affinity of the GM fauna with the TWA fauna, a hierarchical cluster analysis
was applied to one species composition matrix of presence/absence. A matrix of species (excluding anchialine,
freshwater and troglobitic) for the TWA fauna was derived from compilation by Ortiz et al. (2007) for six regions:
Bahamas, Barbados, Bermuda, Caribbean, Florida and GM. Likewise, a matrix of species for the GM fauna was
derived from compilation by LeCroy et al. (2009) for four regions: Northeast, Southeast, Southwest and
Northwest. Thus, a total of 418 and 232 species were listed for the TWA and the GM, respectively. After that,
another matrix was generated from the two above compilations to carry out the analysis; to avoid redundant
information and ambiguous interpretations in analysis, of those regions proposed by Ortiz et al. (2007), the Florida
region was excluded and interchanged by the four regions of the GM employed by LeCroy et al. (2009). Thus, this
last matrix included 381 shared species among eight regions (Appendix 1). The Sorensen coefficient as similarity
index and the average linkage clustering were used to do the hierarchical cluster analysis due to the differences in
sample size and sampling effort at the different compilations. The statistical software used for analysis was
PRIMER v6 (Clarke & Gorley 2006).
Results
Faunal composition
Based on literature review and records from the present study, the amphipod fauna for the Mexican southeast sector
is made up so far by 55 species. The suborder Gammaridea is represented by 16 families, 26 genera and 34 species,
whereas the suborder Corophiidea is represented by nine families, 14 genera and 21 species.
Families with the highest numbers of species were Melitidae (8), Photidae (6), Ampeliscidae (5), Aoridae (4)
and Lysianassidae (4). These families represented 49% of all the fauna.
Station Coordinate Date Depth (m) Sediment texture
121°47’N 87°30’W 9 April 2004 19.6 Medium grain size, poorly sorted
222°02’N 87°30’W 9 April 2004 31.4 Fine grain size, poorly sorted
322°17’N 87°29’W 9 April 2004 43.8 Medium grain size, poorly sorted
422°17’N 88°00’W 10 April 2004 40.9 Medium grain size, poorly sorted
522°06’N 88°59’W 10April 2004 31.4 Coarse grain size, moderately sorted
621°53’N 88°00’W 10 April 2004 19.3 Medium grain size, moderately sorted
721°52’N 88°30’W 10 April 2004 20.9 Medium grain size, poorly sorted
822°03’N 88°30´W 10 April 2004 30.1 Fine grain size, very poorly sorted
922°17’N 88°30’W 10 April 2004 42.1 Fine grain size, moderately sorted
10 22°06’N 89°00’W 11 April 2004 42.2 Fine grain size, poorly sorted
11 21°59’N 89°00’W 11 April 2004 35.3 Medium grain size, poorly sorted
12 21°49’N 89°00’W 11 April 2004 24.9 -
13 21°28’N 90°24’W 14 April 2004 14.2 Medium grain size, moderately sorted
14 21°41’N 90°18’W 14 April 2004 33.9 -
15 21°53’N 90°17’W 15 April 2004 42.9 Fine grain size, moderately sorted
16 22°01’N 89°36’W 15 April 2004 40.5 Fine grain size, moderately sorted
17 21°49’N 89°35’W 15 April 2004 33.4 Medium grain size, poorly sorted
18 21°28’N 89°36’W 15 April 2004 22.5 -
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BENTHIC AMPHIPODS IN SOUTHEASTERN GULF OF MEXICO
A total abundance of 267 individuals was counted from the collected samples in the Yucatan continental shelf,
identifying an assemblage of 39 species. The most abundant and widely distributed species in the area were
Eudevenopus honduranus Thomas & Barnard, 1983 (60 Ind, 46%), Gammaropsis sp. B sensu LeCroy, 2000 (32
Ind, 54%), Acuminodeutopus naglei (Bousfield, 1973) (27 Ind, 46%) and Americhelidium americanum (Bousfield,
1973) (26 Ind, 46%).
Annotated checklist of amphipods on the Mexican southeastern sector
From the compilation of literature and records of the present study, so far 55 species have been recorded (listed
below) in the Mexican southeastern sector. Nineteen of these had been already recorded in the sector and the other
36 were added in the present study.
From identified species in the present study, 36 showed a geographical extension to the Yucatan continental
shelf. Twenty-three species are the first records for the Mexican southeast sector (two of which are also the first
records for the southwest region), nine species are the first records for the southeast region, and four species are the
first records for the GM. These species are indicated by a symbol ( ) preceding their names.
Order Amphipoda Latreille, 1816
Suborder Gammaridea Latreille, 1802
Family Ampeliscidae Costa, 1857
Ampelisca agassizi (Judd, 1896)
Material examined. CYMX-68-PY, 1 male, station 3; CYMX-69-PY, 1 female, station 9.
General distribution. Western Atlantic; eastern Pacific (Mills 1965, 1967; Ortiz et al. 2007; García-Madrigal
2008; LeCroy et al. 2009).
GM distribution. Louisiana; Mobile Bay (Goeke & Heard 1984); Perdido Key (Rakocinski et al. 1996);
Tamaulipas and Veracruz continental shelf (Escobar-Briones & Winfield 2003); Biloxi Bay (Pederson & Peterson
2002); Bay of Campeche (Winfield et al. 2006).
Habitat. Coarse sand or in fine to medium sand mixed with shell hash; at depths of 2 to 450 m (LeCroy 2002).
Remarks. First record for the southeast region.
Ampelisca brevisimulata Barnard, 1954
Material examined. CYMX-67-PY, 1 male, station 4.
General distribution. Western Atlantic; eastern Pacific (Barnard 1954a, b; Mills 1965; Ortiz et al. 2007;
García-Madrigal 2008; LeCroy et al. 2009).
GM distribution. Mexican southwestern continental shelf (Escobar-Briones & Winfield 2003); Veracruz
continental shelf (Winfield & Ortiz 2011).
Habitat. Sand to silt clay sediments; at depths of 11 to 172 m (García-Madrigal 2008).
Remarks. First record for the southeast region.
Ampelisca cristata Holmes, 1908
General distribution. Western Atlantic; eastern Pacific (Barnard 1954b; Mills 1967; Ortiz et al. 2007; García-
Madrigal 2008; LeCroy et al. 2009).
GM distribution. Off Port Charlotte; Yucatan continental shelf (Ortiz 1979); Florida Bay (LeCroy 2002).
Habitat. Sand sediments; at depths of 2 to 152 m (Ortiz et al. 2007; García-Madrigal 2008; LeCroy et al.
2009).
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Ampelisca lobata Holmes, 1908
General distribution. Western Atlantic; eastern Pacific (Barnard 1954b; Mills 1967; Ortiz et al. 2007; García-
Madrigal 2008; LeCroy et al. 2009).
GM distribution. central West Florida shelf; Yucatan continental shelf (Ortiz 1979); Río Soto la Marina
Lagoon (Cházaro-Olvera et al. 2002); Tamaulipas continental shelf (Winfield et al. 2006); Veracruz coral reef
system (Winfield et al. 2007a); Northwestern Cuba (Ortiz & Lalana 2010).
Habitat. Soft bottoms; from intertidal depths to 450 m (Ortiz et al. 2007; García-Madrigal 2008; LeCroy et al.
2009).
Ampelisca vadorum Mills, 1963
Material examined. CYMX-74-PY, 2 females, station 3; CYMX-73-PY, 1 female, station 10.
General distribution. Western Atlantic (Mills 1963, 1965; Bousfield 1973; Nelson 1995; Ortiz et al. 2007;
LeCroy et al. 2009).
GM distribution. Key Largo (Shoemaker 1933a); western Florida (Mills 1963); Gulf Coast of the USA (Mills
1965); Yucatan continental shelf (Ortiz 1979); Terminos Lagoon (Ledoyer 1986); off the Papaloapan river
(Escobar-Briones & Winfield 2003); Bay of Campeche (Winfield et al. 2006).
Habitat. Sand bottoms, often mixed with shell; from intertidal depths to 70 m (Bousfield 1973).
Family Amphilochidae Boeck, 1871
Gitana dominica Thomas & Barnard, 1990
Material examined. CYMX-71-PY, 1 female, 1 unsexed, station 2; CYMX-70-PY, 1 male, station 5; CYMX-
72-PY, 1 female, station 10.
General distribution. Caribbean (Thomas & Barnard 1990; Ortiz et al. 2007; Winfield & Escobar-Briones
2007).
GM distribution. Previously unreported.
Habitat. Sand among reef outcrop; at depths of 4 to 112 m (Thomas & Barnard 1990; Winfield & Escobar-
Briones 2007).
Remarks. First record for the GM. LeCroy (2002) reported to Gitana cf. dominica, one species very similar to
G. dominica which is presented at the northeastern Florida. The difference between records is in the serration of the
ventral margins of coxae 2–4, which is less on G. dominica than G. cf. dominica (LeCroy 2002).
Family Argissidae Walker, 1904
Argissa hamatipes (Norman, 1869)
Material examined. CYMX-89-PY, 1 female, station 1; CYMX-90-PY, 1 male, 1 unsexed, station 2; CYMX-
92-PY, 1 female, station 3; CYMX-91-PY, 1 female, station 5; CYMX-93-PY, 1 female, station 11.
General distribution. Arctic Ocean; Northeastern and Northwestern Atlantic; Northeastern Pacific; Southern
Africa (LeCroy 2002; LeCroy et al. 2009).
GM distribution. Southern Texas (McKinney 1977); Perdido Key (Rakocinski et al. 1996); Cape Romano;
Tampa Bay; Apalachee Bay; lower Florida Keys (LeCroy 2002); Louisiana continental shelf (Dubois et al. 2009).
Habitat. Pelagic, but mainly epibenthic on hard and soft bottoms; at depths of 2 to 1720 m (LeCroy 2002).
Remarks. First record for the Mexican southeast sector.
Family Bateidae Stebbing, 1906
Batea cuspidate (Shoemaker, 1926)
Material examined. CYMX-63-PY, 1 male, station 7.
General distribution. Central western Atlantic (Ortiz et al. 2007; LeCroy et al. 2009; Coleman 2011).
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BENTHIC AMPHIPODS IN SOUTHEASTERN GULF OF MEXICO
GM distribution. Western Florida (Shoemaker 1926; Ortiz 1991); off Key Largo (Shoemaker 1933a); Faro
Roncali; Playa Las Tumbas (Varela et al. 2003); lower Florida Keys; Florida Bay; Cape Sable; Port Richey;
Homosassa Island (LeCroy 2004); Bay of Campeche (Winfield et al. 2006); Northwestern Cuba (Ortiz & Lalana
2010).
Habitat. Thalassia sp. or Halodule sp. grassbeds, algae on sandy, shelly or muddy bottoms, live bottom areas
near corals and sponges with patches of sand or shell covered with green macroalga Caulerpa sp.; at depths of 1 to
49 m (Ortiz 1991; LeCroy 2004).
Remarks. First record for the Mexican southeast sector.
Family Hyalidae Bulycheva, 1957
Protohyale macrodactyla (Stebbing, 1899)
General distribution. Western Atlantic; Madagascar; western Africa (McKinney 1977; Ortiz et al. 2007;
LeCroy et al. 2009).
GM distribution. Yalahau Lagoon (Oliva-Rivera & Jiménez-Cueto 1997); Río Soto la Marina Lagoon;
Camaronera Lagoon; Terminos Lagoon (Cházaro-Olvera et al. 2002).
Habitat. Free-swimming on algae and hard substrates; from intertidal depths to shallow subtidal zone
(Bousfield & Hendrycks 2002; LeCroy et al. 2009).
Family Leucothoidae Dana, 1852
Anamixis cavatura Thomas, 1997
Material examined. CYMX-66-PY, 2 males, station 7.
General distribution. Tropical western Atlantic (Thomas 1997; LeCroy 2007; Ortiz et al. 2007; LeCroy et al.
2009; White 2011).
GM distribution. From the Mississippi Delta to Tampa; Florida Keys (Pearse 1912; Shoemaker 1933b;
Thomas 1997; White 2011); Northwestern Cuba (Varela et al. 2003; Ortiz & Lalana 2010).
Habitat. Coral rubble; internal cavities of small asconoid sponges and colonial ascidians; at depths of 1 to 5 m
(Thomas 1997; White 2011).
Remarks. First record for the Mexican southeast sector. This record extended its maximum depth from 5 m
(White 2011) to 20.9 m. Escobar-Briones and Winfield (2003) reported to this species “in the Bank of Campeche in
the southern Gulf”; however, no record of that occurrence had been established.
Family Liljeborgiidae Stebbing, 1899
Liljeborgia bousfieldi McKinney, 1979
Material examined. CYMX-31-PY, 1 male, station 7.
General distribution. Central western Atlantic (McKinney 1979; Oliva-Rivera & Jiménez-Cueto 1992; Ortiz et
al. 2007; LeCroy et al. 2009).
GM distribution. Florida Keys (Thomas 1993; LeCroy 2011).
Habitat. Among algae and on coral reefs; at depths of 0.5 to 3m (McKinney 1979; Thomas 1993).
Remarks. First record for the Mexican southeast sector. This record extended its maximum depth from 3 m
(McKinney 1979) to 20.9 m.
Listriella barnardi Wigley, 1966
Material examined. CYMX-15-PY, 1 female, station 1; CYMX-16-PY, 1 female, station 2; CYMX-14-PY, 2
males, 1 female, station 3.
General distribution. Western Atlantic (McKinney 1979; Thomas 1993; Nelson 1995; LeCroy et al. 2009;
LeCroy 2011).
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GM distribution. North Texas coast (McKinney 1979); Perdido Key (Rakocinski et al. 1996); Florida Keys
(Thomas 1993); Louisiana continental shelf (Dubois et al. 2009).
Habitat. Patches of Zostera sp. and Thalassia sp. grassbeds (Wigley 1966; Lewis 1984); common on soft
bottoms (McKinney 1979); at depths of 1 to 22 m (Thomas 1993; LeCroy 2011). They also are inhabitants of
polychaetes tubes (Bousfield 1973).
Remarks. First record for the Mexican southeast sector. This record extended its maximum depth from 22 m
(LeCroy 2011) to 43.8 m. Escobar-Briones et al. (2002) listed this species for Mexico; however, no record of that
occurrence had been established. LeCroy (2011) reviewed the morphology of this species for the Florida and GM
material, identifying several morphs over a wide range of locations, treating them as Listriella cf. barnardi. She
determined that no important morphological differences on those materials for considering them as another species.
Family Lysianassidae Dana, 1849
Hippomedon pensacola Lowry & Stoddart, 1997
Material examined. CYMX-7-PY, 1 female, station 4.
General distribution. South Atlantic Bight; GM (LeCroy 2007; LeCroy et al. 2009).
GM distribution. Santa Rosa Island (Lowry & Stoddart 1997); Apalachee Bay (LeCroy 2007).
Habitat. Infaunal in sandy beaches or muddy substrates; at depths of 5 to 34 m (Lowry & Stoddart 1997;
LeCroy et al. 2009).
Remarks. First record for the southeast region. This record extended its maximum depth from 34 m (LeCroy
2007) to 40.9 m.
Hippomedon sp. B sensu LeCroy, 2007
Material examined. CYMX-9-PY, 1 female, station 1; CYMX-10-PY, 2 females, station 3; CYMX-8-PY, 1
unsexed, station 8; CYMX-11-PY, 1 unsexed, station 10.
General distribution. South Carolina to southeastern Florida; GM (LeCroy 2007).
GM distribution. Cape Sable to Cape Romano; Tampa Bay (LeCroy 2007).
Habitat. In sandy bottoms; at depths of 8 to 17 m (LeCroy 2007).
Remarks. First record for the southeast region. This record extended its maximum depth from 17 m (LeCroy
2007) to 43.8 m. The main difference between this species and H. pensacola, the only other member of the genus
know from GM is, the lack of a notch on epimeron 3 and the presence of an expanded distal flange on the
dorsolateral margin of the peduncle of uropod 2 (LeCroy 2007).
Orchomenella thomasi Lowry & Stoddart, 1997
Material examined. CYMX-4-PY, 1 male, station 5.
General distribution. GM (LeCroy et al. 2009).
GM distribution. Sanibel Island (Lowry & Stoddart 1997); Louisiana coast (LeCroy 2007).
Habitat. Fine to medium sand with crushed shell, dead bryozoans or calcareous algae present; at depths of 10
to 73 m (Lowry & Stoddart 1997).
Remarks. First record for the southeast region.
Shoemakerella cubensis (Stebbing, 1897)
Material examined. CYMX-5-PY, 1 male, 1 female, station 7.
General distribution. GM; Caribbean (Lowry & Stoddart 1997; Ortiz et al. 2007; LeCroy et al. 2009).
GM distribution. Dry Tortugas to Panama City; Mississippi Delta (Thomas 1993; Lowry & Stoddart 1997);
Mexican southwestern continental shelf (Escobar-Briones & Winfield 2003); Veracruz coral reef system (Winfield
et al. 2007a); Northwestern Cuba (Ortiz & Lalana 2010); Tuxpan river (Winfield & Ortiz 2011).
Habitat. In grassbeds, rubble, mixed algae and sandy bottoms; at depths of 1 to 69 m (Lowry & Stoddart 1997;
LeCroy 2007).
Remarks. First record for the Mexican southeast sector.
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BENTHIC AMPHIPODS IN SOUTHEASTERN GULF OF MEXICO
Family Megaluropidae Thomas & Barnard, 1986
Gibberosus myersi (McKinney, 1980)
Material examined. CYMX-94-PY, 3 males, 1 unsexed, station 7.
General distribution. Western Atlantic; eastern Pacific (Thomas & Barnard 1986a; García-Madrigal 2008;
LeCroy et al. 2009).
GM distribution. Looe Key Reef (Thomas & Barnard 1986a); Perdido Key (Rakocinski et al. 1996); lower
Florida Keys to Cape Romano; Tampa Bay (LeCroy 2007).
Habitat. In or near grassbeds, and from fine to medium sand often mixed with shell; at depths of 1 to 29 m
(Thomas & Barnard 1986a; LeCroy 2007). This species feeds by perching upside down, filtering suspended
material from the water column (Thomas & Barnard 1986a).
Remarks. First record for the Mexican southeast sector.
Family Melitidae Bousfield, 1973
Ceradocus sheardi Shoemaker, 1948
General distribution. Tropical western Atlantic (Ortiz et al. 2007; Krapp-Schickel & Vader 2009; LeCroy et al.
2009).
GM distribution. Dry Tortugas (Shoemaker 1948); Yucatan continental shelf (Ortiz 1979); Northwestern Cuba
(Varela et al. 2003; Ortiz & Lalana 2010); central West Florida shelf (Ortiz 1979; Krapp-Schickel & Vader 2009);
Fish Haven off Louisiana (LeCroy et al. 2009).
Habitat. Coral rubble and sandy bottoms in the lagoon and fore-reef environment; at depths of 1 to 73 m
(Thomas 1993; Krapp-Schickel & Vader 2009).
Ceradocus shoemakeri Fox, 1973
Material examined. CYMX-3-PY, 1 male, station 7; CYMX-2-PY, 1 female, station 13.
General distribution. Tropical western Atlantic (Fox 1973; Martín & Díaz 2003; Ortiz et al. 2007; LeCroy et
al. 2009).
GM distribution. Dry Tortugas; Perdido Key; Apalachee Bay (LeCroy 2000); central West Florida shelf
(Krapp-Schickel & Vader 2009); Fish Haven off Louisiana (LeCroy et al. 2009); Northwestern Cuba (Ortiz &
Lalana 2010).
Habitat. Sandy bottoms, coral rubble, algae, sponges, and also occasionally found in grassbeds of Thallassia
testudinum (LeCroy 2000); at depths of 0.5 to 73 m (Krapp-Schickel & Vader 2009).
Remarks. First record for the southwest region and Mexican southeast sector.
Dulichiella appendiculata (Say, 1818)
General distribution. Northwestern Atlantic (Lowry & Springthorpe 2007).
GM distribution. Central West Florida shelf (Ortiz 1979); Florida Keys; Florida Bay to Louisiana (Sheridan
1980; LeCroy 2000; Lowry & Springthorpe 2007); Yalahau Lagoon (Oliva-Rivera & Jiménez-Cueto 1997);
Northwestern Cuba (Ortiz & Lalana 2010).
Habitat. Marine epibenthic, polyhaline on sponges, hydroids and bryozoans; at depths of <1 to 80 m (Lowry &
Springthorpe 2007; LeCroy et al. 2009).
Elasmopus levis (Smith, 1873)
General distribution. Northwestern Atlantic (Ortiz et al. 2007; LeCroy et al. 2009).
GM distribution. San Antonio Bay; Corpus Christi Bay; Laguna Madre of Texas; Port Isabel (McKinney
1977); Terminos Lagoon (Ledoyer 1986); Perdido Key (Rakocinski et al. 1996); Yalahau Lagoon (Oliva-Rivera &
Jiménez-Cueto 1997); Veracruz coral reef system (Winfield et al. 2007a); central West Florida shelf (Vader &
Krapp-Schickel 2012).
Habitat. Grassbeds, algae and sandy bottoms; at depths of 0 to 18 m (LeCroy 2000; LeCroy et al. 2009; Vader
& Krapp-Schickel 2012).
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Elasmopus rapax Costa, 1853
General distribution. Mediterranean Sea; Red Sea; eastern Atlantic; western Atlantic; Indo-Pacific (Hughes &
Lowry 2010).
GM distribution. Pigeon Key; Florida Bay (Pearse 1912); Key West (Pearse 1912; LeCroy 2000); Plantation
Key (Shoemaker 1933a); north Texas offshore; Texas offshore reefs; Port Isabel; Lobos Reef (McKinney 1977);
central West Florida shelf (Ortiz 1979); Yalahau lagoon (Oliva-Rivera & Jiménez-Cueto 1997).
Habitat. This species is found on a broad range of habitats (e. g. jetties, piers, rocks, dead coral, mangrove
roots, algae, sponges, sand bottom, mud bottom); occasionally it is also found on the carapace of the Loggerhead
sea turtle; at depths of 1 to 50 m (LeCroy 2000; LeCroy et al. 2009).
Jerbarnia americana Watling, 1981
General distribution. Northwestern Atlantic (Watling 1981; LeCroy et al. 2009).
GM distribution. Yucatan continental shelf (Ortiz 1979; Watling 1981); off Sanibel Island (Krapp-Schickel &
Vader 2009).
Habitat. Soft bottoms; at depths of 35 to 179 m (LeCroy et al. 2009).
Netamelita tabaci Thomas & Barnard, 1991
Material examined. CYMX-1-PY, 1 male, 1 unsexed, station 1; CYMX-58-PY, 2 males, station 5; CYMX-59-
PY, 1 unsexed, station 8.
General distribution. Caribbean (Thomas & Barnard 1991; Ortiz et al. 2007).
GM distribution. Previously unreported.
Habitat. Deep fore-reef sediments, with coralgal mud and Halimeda sp. flakes (Thomas & Barnard 1991).
Remarks. First record for the GM. This record extended its maximum depth from 29 m (Thomas & Barnard
1991) to 31.4 m.
Quadrimaera quadrimana (Dana, 1853)
General distribution. Tropical western Atlantic; Indo-Pacific (Krapp-Schickel & Ruffo 2000; Ruffo et al.
2000; LeCroy et al. 2009).
GM distribution. Florida Keys (Thomas 1993); Yalahau Lagoon (Oliva-Rivera & Jiménez-Cueto 1997);
Northwestern Cuba (Ortiz 2001; Ortiz & Lalana 2010).
Habitat. Coral rubble and rocks in the lagoon and fore-reef environment; at depths of 1 to 5 m (Thomas 1993;
LeCroy et al. 2009).
Remarks. As LeCroy (2000) pointed out, records of this species in the western Atlantic region prior to 2000
should be rechecked to ensure that they do not represent one of the closely similar species described by Ruffo et al.
(2000) and Krapp-Schickel and Ruffo (2000) from the quadrimana complex. For instance, Q. quadrimana was
recorded from southern Gulf of Mexico (Terminos Lagoon) as Maera quadrimana by Ledoyer (1986), but actually
it corresponds to Quadrimaera miranda (Ruffo, Krapp & Gable, 2000).
Family Melphidippidae Stebbing, 1899
Hornellia tequestae Thomas & Barnard, 1986
Material examined. CYMX-28-PY, 3 males, 3 females, 5 unsexed, station 1.
General distribution. Southeastern Florida; GM (LeCroy 2007; LeCroy et al. 2009).
GM distribution. Looe Key Reef (Thomas & Barnard 1986b); lower Florida Keys to Cape Romano (LeCroy
2007).
Habitat. Algal turf on dead coral, coral rubble and sandy shell bottoms in the fore-reef environment; at depths
of 2 to 45 m (Thomas & Barnard 1986b; Thomas 1993; LeCroy 2007).
Remarks. First record for the Mexican southeast sector.
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Family Oedicerotidae Lilljeborg, 1865
Americhelidium americanum (Bousfield, 1973)
Material examined. CYMX-52-PY, 1 female, station 1; CYMX-54-PY, 8 females, station 2; CYMX-56-PY, 2
females, station 3; CYMX-57-PY, 5 females, station 10; CYMX-55-PY, 3 males, 1 female, station 11; CYMX-53-
PY, 6 females, station 15.
General distribution. Western Atlantic (Bousfield 1973; LeCroy 2000; Ortiz et al. 2007; LeCroy et al. 2009).
GM distribution. Texas coast (McKinney 1977); Florida Keys (Thomas 1993); Perdido Key (Rakocinski et al.
1996); Veracruz continental shelf (Winfield et al. 2006).
Habitat. Burrowing species in medium to coarse well-sorted sediments from forereef, lagoon, and rubble zone
habitats; at depths of 1 to 76 m (Bousfield 1973; Thomas 1993; Winfield et al. 2006).
Remarks. First record for the Mexican southeast sector.
Hartmanodes nyei (Shoemaker, 1933)
Material examined. CYMX-29-PY, 1 unsexed, station 10; CYMX-30-PY, 1 female, station 15.
General distribution. Western Atlantic; eastern Pacific (LeCroy 2000; Ortiz et al. 2007; García-Madrigal 2008;
LeCroy et al. 2009).
GM distribution. Key West; off Key Largo (Shoemaker 1933a); Corpus Christi Bay (McKinney 1977); Florida
Keys (Thomas 1993); Perdido Key (Rakocinski et al. 1996); Cojímar Bay (Ortiz 2001); Camaronera Lagoon
(Cházaro-Olvera et al. 2002); Northwestern Cuba (Ortiz & Lalana 2010).
Habitat. Fine to medium sand in back reef, lagoon or open beach habitats; at depths of 1 to 7 m (Thomas 1993,
Rakocinski et al. 1996).
Remarks. First record for the Mexican southeast sector. This record extended its maximum depth from 7
(Rakocinski et al. 1996) to 42.9 m.
Family Phoxocephalidae Sars, 1891
Metharpinia floridana (Shoemaker, 1933)
Material examined. CYMX-19-PY, 1 unsexed, station 3; CYMX-18-PY, 2 females, station 7; CYMX-20-PY, 1
unsexed, station 8; CYMX-17-PY, 2 females, 4 unsexed, station 9.
General distribution. Western Atlantic (Shoemaker 1933a; Barnard 1980; Ortiz et al. 2007; LeCroy et al. 2009;
LeCroy 2011).
GM distribution. Florida Keys (Shoemaker 1933a; Barnard 1980; Thomas 1993); Yucatan continental shelf
(Ortiz 1979); Perdido Key (Rakocinski et al. 1996); Camaronera Lagoon (Cházaro-Olvera et al. 2002); Bank of
Campeche (Escobar-Briones & Winfield 2003); Bay of Campeche (Winfield et al. 2006); Veracruz continental
shelf (Winfield & Ortiz 2011).
Habitat. In plankton and sandy bottoms (Rakocinski et al. 1996; Thomas 1993; LeCroy 2011); at depths of 0 to
60 m (LeCroy 2011), but it has been also recorded to depth of 3360 m (Winfield et al. 2006).
Family Platyischnopidae Barnard & Drummond, 1979
Eudevenopus honduranus Thomas & Barnard, 1983
Material examined. CYMX-22-PY, 24 females, 11 unsexed, station 1; CYMX-21-PY, 7 females, station 2;
CYMX-24-PY, 1 male, 5 females, station 8; CYMX-23-PY, 2 females, station 9; CYMX-25-PY, 1 female, station
10; CYMX-26-PY, 7 females, 2 unsexed, station 11.
General distribution. Western Atlantic; eastern Pacific (Thomas & Barnard 1983; Ortiz et al. 2007; García-
Madrigal 2008; LeCroy et al. 2009; LeCroy 2011).
GM distribution. Off Panama City (Thomas & Barnard 1983); Florida Keys (Thomas 1993); Perdido Key
(Rakocisnki et al. 1996); Louisiana continental shelf (Dubois et al. 2009).
Habitat. Sandy and muddy bottoms where they are fast swimmers, rapid burrowers and effective predators; at
depths of 1 to 40 m (Thomas & Barnard 1983).
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Remarks. First record for the Mexican southeast sector. This record extended its maximum depth a few meters
from 40 (Thomas & Barnard 1983) to 42.2 m. Escobar-Briones et al. (2002) included this species for Mexico,
however, no record of that occurrence had been established. On the Yucatan continental shelf this species has been
documented as dominant on sandy bottoms, decreasing its abundance with depth (Paz-Ríos 2008).
Family Stenothoidae Boeck, 1871
Parametopella texensis McKinney, Kalke & Holland, 1978
Material examined. CYMX-12-PY, 2 unsexed, station 3.
General distribution. GM (LeCroy et al. 2009; LeCroy 2011).
GM distribution. Texas coast shelf (McKinney et al. 1978); Biloxi Bay (Pederson & Peterson 2002);
Camaronera Lagoon (Cházaro-Olvera et al. 2002).
Habitat. Sandy bottoms mixed with silt/clay; at depth of 1 to 18 (McKinney et al. 1978).
Remarks. First record for the southeast region. This record extended its maximum depth from 18 (McKinney
et al. 1978) to 43.8 m.
Family Synopiidae Dana, 1853
Metatiron bellairsi (Just, 1981)
Material examined. CYMX-35-PY, 1 male, 1 female, station 5; CYMX-36-PY, 1 female, station 7; CYMX-34-
PY, 2 females, station 11.
General distribution. Central western Atlantic (Just 1981; Barnard & Thomas 1989; Ortiz et al. 2007; LeCroy
2011).
GM distribution. Florida Bay; southwest Florida shelf (LeCroy 2011).
Habitat. Coral sand with detritus and in or near sparsely grassbeds; at depths of 2.5 to 34 (Just 1981; Barnard &
Thomas 1989; LeCroy 2011). Detailed biology and behavior of this species can be found in Just (1981).
Remarks. First record for the southeast region. This record extended its maximum depth by one meter from 34
(Barnard & Thomas 1989) to 35.3 m. Escobar-Briones et al. (2002) included this species for Mexico, however, no
record of that occurrence had been established. This species is very similar to the other species of the genus
reported in the GM, Metatiron triocellatus (Goeke, 1982); in fact Thomas (1993) pointed out that “they are closely
related that could be the same species”. LeCroy (2011) examined the morphology for both species and established
that they are distinct species.
Metatiron tropakis (Barnard, 1972)
Material examined. CYMX-27-PY, 1 female, station 1.
General distribution. Western Atlantic; eastern Pacific (Barnard 1972; LeCroy et al. 2009; LeCroy 2011).
GM distribution. Tampa Bay (Barnard 1972); offshore of West Bay; Lavaca Bay (McKinney 1977); Perdido
Key (Racocinski et al. 1996); Louisiana continental shelf (Dubois et al. 2009).
Habitat. In plankton and sandy bottoms; at depths of 3 to 157 m (Barnard 1972).
Remarks. First record for the southeast region. Escobar-Briones et al. (2002) included this species for Mexico,
however, no record of that occurrence had been established. This species can be easily distinguished from the other
two sympatric species M. bellairsi and M. triocellatus, because it has an accessory flagellum with four or five
articles; accessory eye composed of two rather than three ommatidia; and presences of dorsal spines on the telson.
Synopia ultramarina Dana, 1853
Material examined. CYMX-6-PY, 1 male, station 9.
General distribution. Cosmopolitan in warm-temperate, subtropical and tropical regions (Hughes 2009;
LeCroy et al. 2009).
GM distribution. Off Key Largo (Shoemaker 1933a); Looe Key Reef (Barnard & Thomas 1989); off southwest
Florida (LeCroy 2011).
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Habitat. Sandy bottoms or coral rubble near coral reefs; it is also a nektonic species which has often been
collected in light traps; at depths of 0 to 18 m (Barnard & Thomas 1989; Thomas 1993; Hughes 2009; LeCroy et al.
2009).
Remarks. First record for the Mexican southeast sector. This record extended its maximum depth from 18
(Hughes 2009) to 42.1 m. Although this species is widely distributed around the world, few records have been
documented in the GM, reflecting a poor sampling effort in the area. Barnard and Thomas (1989) pointed out that
species of this genus are rarely reported in modern times because they are found mainly in neritic waters or in
epipelagic waters and that if species were collected, it is unlikely that they will be identified by an expert.
Suborder Corophiidea Leach, 1814
Infraorder Corophiida Leach, 1814
Superfamily Aoroidea Stebbing, 1899
Family Aoridae Stebbing, 1899
Bemlos mackinneyi (Myers, 1978)
Material examined. CYMX-65-PY, 1 male, 2 females, station 2.
General distribution. GM (LeCroy et al. 2009).
GM distribution. Galveston (Myers 1978); central West Florida shelf; Dauphin Island (Myers 1981); Perdido
Key (Rakocinski et al. 1996); lower Florida Keys (LeCroy 2002).
Habitat. Sand or shell hash bottoms; at depths of 5 to 6 m (LeCroy 2002).
Remarks. First record for the Mexican southeast sector. This record extended its maximum depth from 6 m
(Myers 1981) to 31.4 m.
Bemlos spinicarpus inermis (Myers, 1979)
Material examined. CYMX-87-PY, 4 females, station 7; CYMX-85-PY, 1 female, station 10; CYMX-88-PY, 2
females, station 13.
General distribution. Tropical western Atlantic (Ortiz et al. 2007; LeCroy et al. 2009).
GM distribution. Central West Florida shelf (Myers 1981).
Habitat. Sand and shell hash bottoms; also in live bottom (e.g. growth of sponges, corals, bryozoans, algae); at
depths of 6 to 73 m (Myers 1981; LeCroy 2002).
Remarks. First record for the southeast region. The main characters to identify females of this species in the
GM after the key provided by LeCroy (2002) are: i) palmar margin convex and angle without tooth on propodus of
gnathopod 1, ii) propodus subequal to length of carpus in gnathopod 1, iii) inner ramus longer than peduncle in
uropod 3 and iv) distoventral process on peduncle of uropod 3 relatively long.
Sub-species was established here on base to the reported distribution, habitat and depth range; nevertheless, to
determine the actual sub-species it is necessary to examine male specimens.
Grandidierella bonnieroides Stephensen, 1948
General distribution. Cosmopolitan in tropical and temperate regions (Myers 1970, 2009; LeCroy et al. 2009).
GM distribution. Port St. Joe; Lake Pontchartrain; Baffin Bay (Myers 1970); Barataria Bay (Thomas 1976);
Terminos Lagoon (Ledoyer 1986); Yalahau Lagoon (Oliva-Rivera & Jiménez-Cueto 1997); Alvarado Lagoon
(Winfield et al. 2001); Río Soto la Marina Lagoon (Cházaro-Olvera et al. 2002); western coast of Florida; Florida
Keys (LeCroy 2002); Northwestern Cuba (Ortiz 2001; Ortiz & Lalana 2010).
Habitat. This species is widespread in the GM, occurring frequently in grassbeds or oyster reefs; at depths of 0
to 8 m (Heard 1982; LeCroy 2002).
Lembos unifasciatus reductus Myers, 1979
Material examined. CYMX-86-PY, 1 male, station 7.
General distribution. Tropical western Atlantic (Ortiz et al. 2007; LeCroy et al. 2009).
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GM distribution. Central West Florida shelf (Myers 1981); lower Florida Keys to Cape Romano; Apalachee
Bay (LeCroy 2002).
Habitat. Sand and shell bottoms; at depths of 2 to 73 m (Myers 1981; LeCroy 2002).
Remarks. First record for the Mexican southeast sector.
Family Unciolidae Myers & Lowry, 2003
Acuminodeutopus naglei (Bousfield, 1973)
Material examined. CYMX-84-PY, 1 female, station 4; CYMX-81-PY, 2 females, station 8; CYMX-83-PY, 3
females, station 10; CYMX-82-PY, 11 females, station 11; CYMX-79-PY, 2 females, station 13; CYMX-80-PY, 8
females, station 15.
General distribution. Western Atlantic (Bousfield 1973; Ortiz et al. 2007; Winfield & Escobar-Briones 2007;
LeCroy et al. 2009).
GM distribution. Captiva Island; central West Florida shelf; west of Egmont Key; St. Andrew Bay; Dauphin
Island (Myers 1981); Perdido Key (Rakocinski et al. 1996); Florida Keys to Cape Sable (LeCroy 2002).
Habitat. Grassbeds and soft sediments with shell debris; from intertidal depths to 55 m (Bousfield 1973; Myers
1981).
Remarks. First record for the southwest region and Mexican southeast sector.
Superfamily Chevalioidea Myers & Lowry, 2003
Family Chevaliidae Myers & Lowry, 2003
Chevalia aviculae Walker, 1904
General distribution. Circumtropical (Barnard & Thomas 1987b; LeCroy et al. 2009).
GM distribution. Central West Florida shelf; Yucatan continental shelf (Ortiz 1979); Florida Keys (Thomas
1993); Northwestern Cuba (Ortiz & Lalana 2010).
Habitat. Sandy bottoms; coral rubble and coral overhangs in the fore-reef environment; at depths of 2 to 56 m
(Ortiz 1979; Thomas 1993; LeCroy et al. 2009).
Remarks. Barnard and Thomas (1987b) showed that a C. aviculae species complex exists. Because of this,
LeCroy (2000) proposed that material previously reported as C. aviculae from the western Atlantic needs to be
reexamined to determine its status.
Chevalia carpenteri Barnard & Thomas, 1987
Material examined. CYMX-60-PY, 1 male, station 5.
General distribution. Central western Atlantic (LeCroy et al. 2009).
GM distribution. Looe Key Reef (Barnard & Thomas 1987b).
Habitat. Coral rubble with associated algae and coral overhangs in the fore-reef environment; at depths of 1 to
5 m (Barnard & Thomas 1987b; LeCroy 2000).
Remarks. First record for the Mexican southeast sector. This record extended its maximum depth from 5
(Barnard & Thomas 1987b) to 31.4 m.
Superfamily Corophioidea Leach, 1814
Family Ampithoidae Boeck, 1871
Ampithoe ramondi Audouin, 1826
General distribution. Cosmopolitan in warm-temperate and tropical regions (LeCroy et al. 2009).
GM distribution. Florida Keys (Shoemaker 1933b; Thomas 1993); Yucatan continental shelf (Ortiz 1979); Río
Soto la Marina Lagoon (Cházaro-Olvera et al. 2002); Northwestern Cuba (Ortiz 2001; Ortiz & Lalana 2010);
Veracruz coral reef system (Winfield et al. 2007a; Winfield et al. 2010).
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Habitat. Sandy bottoms, grassbeds, algae, polichaete colonies, ascidians and fouling communities; at depths of
<1 to 35 m (Thomas 1993; Ortiz et al. 2007; LeCroy et al. 2009).
Cymadusa filosa Savigny, 1816
General distribution. Cosmopolitan in tropical regions (Peart 2004; LeCroy et al. 2009).
GM distribution. Yalahau Lagoon (Oliva-Rivera & Jiménez-Cueto 1997); Northwestern Cuba (Ortiz 2001;
Ortiz & Lalana 2010).
Habitat. Grassbeds and as a tube-building species on algae; at depths of 0 to 5 m (Appadoo & Myers 2003;
Ortiz et al. 2007; LeCroy et al. 2009).
Remarks. Peart (2004) showed that a C. filosa species complex exists; records of this species by Pears (1912)
as Grubia compta and Shoemaker (1935) as Grubia filosa from the Florida Keys are synonymized with Cymadusa
setosa (Haswell, 1879). Further material from the southern GM needs to be reexamined to determine its actual
distribution in the Gulf basin.
Family Corophiidae Leach, 1814
Apocorophium louisianum (Shoemaker, 1934)
General distribution. Eastern Florida; GM (LeCroy 2004; LeCroy et al. 2009).
GM distribution. Lake St. Catherine; Sarasota Bay (Shoemaker 1947); Barataria Bay (Thomas 1976);
Terminos Lagoon (Ledoyer 1986; Cházaro-Olvera et al. 2002); Yalahau Lagoon (Oliva-Rivera & Jiménez-Cueto
1997); Biloxi Bay (Shoemaker 1947; Pederson & Peterson 2002); Alvarado Lagoon (Winfield et al. 2001).
Habitat. This species is widespread in the GM, occurring in grassbeds, sandy or muddy bottoms, and as a tube-
building species on wood, shell, leaves and submerged grasses; at depths of 1 to 15 m (Heard 1982; LeCroy 2004).
Infraorder Caprellida Leach, 1814
Superfamily Caprelloidea Leach, 1814
Family Podoceridae Leach, 1814
Podocerus kleidus Thomas & Barnard, 1992
Material examined. CYMX-13-PY, 1 male, station 7.
General distribution. Central western Atlantic (Ortiz et al. 2007; LeCroy et al. 2009).
GM distribution. Cudjoe Key (Thomas & Barnard 1992); Veracruz coral reef system (Winfield et al. 2007a);
Northwestern Cuba (Ortiz & Lalana 2010); southwest Florida (LeCroy 2011).
Habitat. Clinging to alga Gracilaria sp. (Thomas & Barnard 1992) and in tubes attached to erect substrates,
e.g. algae and gorgonians in areas of current flow and wave action (Thomas 1993); at depths of 1 to 13 m (Winfield
et al. 2007a; LeCroy 2011).
Remarks. First record for the Mexican southeast sector. This record extends its maximum depth from 13
(Winfield et al. 2007a) to 31.4 m.
Superfamily Neomegamphopoidea Myers, 1981
Family Neomegamphopidae Myers, 1981
Neomegamphopus kalanii Barnard & Thomas, 1987
Material examined. CYMX-64-PY, 1 male, 4 females, station 5.
General distribution. Southeastern Florida (Barnard & Thomas 1987a; Ortiz et al. 2007; LeCroy 2011).
GM distribution. Previously unreported.
Habitat. Sandy bottoms; at depths of 33 to 124 m (Barnard & Thomas 1987a).
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Remarks. First record for the GM. Another species of this genus is found in the GM (Florida),
Neomegamphopus hiatus Barnard & Thomas, 1987. Both species are very similar; Barnard and Thomas (1987a)
documented that “at first we believed specimens of N. kalanii might be untransformed juvenile of N. hiatus”, but
“no stage of transformation between the two species can be demonstrated”. To date those species are separated
(based on males) because N. kalanii has a carpus longer than wide, palm beaded, a carpal tooth not gaping, and a
remarkable propodus expanded proximally.
Superfamily Photoidea Boeck, 1871
Family Ischyroceridae Stebbing, 1899
Caribboecetes sp.
Material examined. CYMX-61-PY, 1 male, station 1; CYMX-62-PY, 2 females, station 6.
General distribution. Genus on the central western Atlantic, and Mexican Pacific (Just 1984; Ortiz & Lemaitre
1997; LeCroy 2007).
GM distribution. Genus previously unreported.
Habitat. Material collected in medium size and poorly/moderately sorted sand to depth of 19 m. Members of
this genus inhabit grass beds, sandy bottoms, and a variety of portable dwellings (e.g. gastropod shells, polychaete
tubes, claw tips from decapod molts scaphopod shells); at depths of 0.5 to 54 m (Just 1983, 1984).
Remarks. First record for the GM. This species is similar to Caribboecetes barbadensis Just, 1983 from
Barbados and Caribboecetes jenikarpae Just, 1984 from Mexican Pacific. Caribboecetes sp. differs from C.
barbadensis by bearing dorsolateral setae on peduncular article 5 of antenna 2 in a single row and by coxal plate 7
and article 2 of pereopod 7 with setose lateral surface. It differs from C. jenikarpae by displaying on article 2 of
pereopod 2 a strongly triangular anterolateral margin. Caribboecetes sp. presumably represents an undescribed
species.
Ericthonius brasiliensis (Dana, 1853)
Material examined. CYMX-33PY, 1 female, station 5.
General distribution. Cosmopolitan in temperate, subtropical and tropical regions (Ortiz et al. 2007; García-
Madrigal 2008; LeCroy et al. 2009; Gable et al. 2010).
GM distribution. Central and northern Texas shelf; Port Isabel (McKinney 1977); central West Florida shelf
(Ortiz 1979); Florida Keys (Thomas 1993); Perdido Key (Rakocinski et al. 1996); Yalahau Lagoon (Oliva-Rivera
& Jiménez-Cueto 1997); Cojímar Bay (Ortiz 2001); Biloxi Bay (Pederson & Peterson 2002); Camaronera Lagoon
(Cházaro-Olvera et al. 2002); Laguna Madre of Tamaulipas (Barba & Sánchez 2005); Sigsbee abyssal plain
(Winfield et al. 2006); Veracruz coral reef system (Winfield et al. 2007a, 2010); Northwestern Cuba (Ortiz &
Lalana 2010).
Habitat. This is a tube-dwelling fouling species and is often found in diverse soft and hard bottoms (e.g. rocks,
mangroves, oyster shells, sponges, sand, seagrasses), generally in shallow waters (1–10 m) (LeCroy 2007). It also
has been collected in deep waters (200–3690 m) (Winfield et al. 2006; LeCroy et al. 2009).
Ericthonius sp. A sensu LeCroy, 2007
Material examined. CYMX-32-PY, 1 male, 1 female, station 7.
General distribution. Southeastern and southwestern Florida (LeCroy 2007).
GM distribution. Lower Florida Keys to Cape Romano (LeCroy 2007).
Habitat. Grassbeds, from sandy shell to silty mud mixed with shell hash; at depths of 1 to 15 m (LeCroy 2007).
Remarks. First record for the Mexican southeast sector. This record extended its maximum depth from 15
(LeCroy 2007) to 20.9 m. This species is different from all western Atlantic species of Ericthonius in the
morphology of peraeopod 5 of the adult male. The basis is expanded posterodistally to form a wing-like process
and an expanded posterodistal margin on the merus; females are more easily distinguished by the presence of long
marginal setae on the anterior lobe of coxa 5 and the setae lacking on the margin of the basis of peraeopod 5
(LeCroy 2007).
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Family Photidae Boeck, 1871
Gammaropsis atlantica Stebbing, 1888
General distribution. Cosmopolitan in tropical regions (LeCroy 2000; LeCroy et al. 2009).
GM distribution. Yucatan continental shelf (Ortiz 1979); Florida Keys (Thomas 1993); Camaronera Lagoon
(Cházaro-Olvera et al. 2002); Northwestern Cuba (Ortiz & Lalana 2010).
Habitat. Sandy bottoms, coral Acropora sp., alga Halimeda sp. and coral rubble; at depths of <1 to 40 m
(Thomas 1993; LeCroy 2000; Ortiz et al. 2007).
Gammaropsis sp. B sensu LeCroy, 2000
Material examined. CYMX-41-PY, 1 male, 1 unsexed, station 2; CYMX-38-PY, 2 females, 3 unsexed, station
3; CYMX-42-PY, 2 males, 1 female, station 4; CYMX-43-PY, 3 females, 5 unsexed, station 5; CYMX-40-PY, 2
females, station 9; CYMX-44-PY, 1 male, 1 female, station 10; CYMX-39-PY, 1 male, 6 females, 3 unsexed,
station 11.
General distribution. Southwestern Florida (LeCroy 2000).
GM distribution. Lower Florida Keys to Cape Romano (LeCroy 2000).
Habitat. Material collected in fine-medium sand; at depths of 31.4 to 43.8 m.
Remarks. First record for the Mexican southeast sector. This species is different from all Gammaropsis species
in the TWA region by article 2 of mandibular palp relatively slender, much longer than article 3 and whit this last
article without subdistal anterior notch; rounded ocular lobe; gnathopod 2 of male densely setose with palmar angle
on propodus defined by small cusp and dactyl with setae on extensor margin; pereopod 3–4 with propodus linear
and longer than carpus; basis of pereopod 5 narrow, with approximately length twice width; and with ramus twice
length of peduncle (peduncle of uropod 3 not elongate).
Photis macromana Mckinney, Kalke & Holland, 1978
Material examined. CYMX-37-PY, 1 male, 1 female, station 5.
General distribution. Central western Atlantic (McKinney et al. 1978; Ortiz et al. 2007; LeCroy et al. 2009).
GM distribution. Florida Bay to Texas (McKinney et al. 1978; LeCroy 2000); Veracruz coral reef system
(Winfield et al. 2007a).
Habitat. Sandy bottoms; at depths of 3 to 42 m (McKinney et al. 1978; LeCroy 2000).
Remarks. First record for the Mexican southeast sector. LeCroy (2000) determined that male adult of P.
macromana is very similar to male subadult of Photis pugnator Shoemaker, 1945 in gnathopod 2. On base to the
key provided by the same author, currently those species can be separate by differences on coxa 3–5, as well as on
inner and outer ramus of uropod 3. LeCroy (2000) suggests taxonomical analyses to determine whether or not the
two species should be synonymized.
Photis melanica (McKinney, 1980)
Material examined. CYMX-47-PY, 1, male, 1 female, 4 unsexed, station 2; CYMX-48-PY, 1 female, station
10; CYMX-45-PY, 2 females, station 11.
General distribution. Central western Atlantic (McKinney 1980; Ortiz et al. 2007; LeCroy et al. 2009).
GM distribution. Texas coast (McKinney 1980); Florida Bay; Tampa Bay (LeCroy 2000).
Habitat. Fine sand or sandy mud bottoms with some shell hash present; at depths of 1 to 6 m (LeCroy 2000;
Martín & Díaz 2003).
Remarks. First record for the Mexican southeast sector. This record extended its maximum depth from 6
(LeCroy 2000) to 31.4 m.
Photis pugnator Shoemaker, 1945
General distribution. Northwestern Atlantic (Shoemaker 1945; LeCroy 2000).
GM distribution. Cedar Key; Tampa Bay; Sarasota Bay; Dry Tortuga (Shoemaker 1945); 7.5 Fathom Reef
(McKinney 1977, 1980); central West Florida shelf; Yucatan continental shelf (Ortiz 1979); Veracruz coral reef
system (Winfield et al. 2010).
Habitat. Hard and sandy bottoms, and in floating Sargassum sp. mats; at depths of 3 to 54 m (McKinney 1980;
LeCroy 2000; LeCroy et al. 2009).
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Photis sp. C sensu LeCroy, 2000
Material examined. CYMX-94-PY, 1 male, station 2; CYMX-51-PY, 1 male, 1 female, station 3; CYMX-46-
PY, 2 unsexed, station 7; CYMX-49-PY, 1 male, station 8; CYMX-50-PY, 1 female, station 9.
General distribution. Eastern Florida; GM (LeCroy 2000).
GM distribution. Florida Keys to Perdido Key (LeCroy 2000).
Habitat. Widespread species in fine and well sorted sand and in grassbeds; at depths of 1 to 8 m (LeCroy
2000).
Remarks. First record for the Mexican southeast sector. This record extended its maximum depth from 8
(LeCroy 2000) to 43.8 m. Two distinctive characteristics in the coxa 1 separate to this species from the other
species in the TWA region: a produced anteroventral angle, forming blunt process and a ventral margin with an
anterior gap in row of marginal setae.
Zoogeographical affinities
Affinity among the eight regions is displayed in four clusters with 40% of similarity. Three of these clusters
represented three independent regions (Bahamas, Bermuda and Barbados), whereas the fourth cluster represented
five related regions (NW, NE, SW, SE and Caribbean) (Fig 2B). Geographically, independent regions collectively
corresponded to fauna from the outer fringe of the Antillean arc, while related regions corresponded to fauna from
the GM and Caribbean (Fig 2A).
Fauna in the cluster with related regions displayed a gradual affinity southward in geographical distribution,
from the GM to the Caribbean. Northern regions (NE and NW) established the highest similarity (57%) with the
SW region also related (49%), while the SE region and Caribbean were also highly related (50%).
Zoogeographically, the similarity among regions resembles the two major provinces in the TWA: Carolinian
province and Caribbean province. Northern regions corresponded to fauna from the Carolinian province, the SW
region corresponded to turnover fauna from the Carolinian province to the Caribbean province, and the SE region
and Caribbean corresponded to fauna from the Caribbean province.
Discussion
Species richness. The study of amphipods in the GM is conducted by three countries: Cuba, Mexico and USA. The
most updated compilation has listed the greatest number of species for the southeast region (Fig 3); this region
harbors 66% of the amphipod diversity in the GM. Of the countries mentioned earlier, Cuba and USA have
contributed significantly with descriptions of new species and records. Thomas (1993) listed 52 species from the
Florida Keys alone, pointing out that “these species represent approximately one-third of the total number of
amphipod species found in the area”. On the other hand, Ortiz and Lalana (2010) recently listed 99 species from the
Cuban Gulf.
In the Mexican Gulf, amphipods from the southwest sector have been more heavily studied than those in the
southeast sector. This is reflected in the great number of species (66) recognized in the former sector. Studies
carried out in the southwest sector include those that focus on ecological roles (Corona et al. 2000; Winfield et al.
2007b), checklists of species (Cházaro-Olvera et al. 2002; Winfield et al. 2006, 2007a; Winfield & Ortiz 2011) and
description of new species (Winfield & Álvarez 2009; Winfield & Ortiz 2009, 2010, 2012). The few studies in the
southeast sector focus on the ecological distribution (Paz-Ríos 2008; Rodríguez-Pliego et al. 2011) and checklists
of species (Ortiz 1979; Oliva-Rivera & Jiménez-Cueto 1997; Simões et al. 2010). Nevertheless, due to the great
heterogeneity of habitat in the southeast sector (e.g. beaches, coastal lagoons, grassbeds, reefs), Escobar-Briones
and Jiménez-Guadarrama (2010) have suggested that the Campeche Bank on the southeast sector is like a
“hotspot” of biological diversity for peracarids associated with carbonated bottoms. Therefore, the reported
number of amphipod species here stated will increase with the exploration of new habitats (e.g. Alacranes Reef)
and description of new species (e.g. Caribboecetes sp.).
Four species previously reported in the region were excluded from the checklist of amphipods for the Mexican
southeast sector. Three of these species [Linguimaera hamigera (Haswell, 1879), Eudevenopus cf. metagracilis
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BENTHIC AMPHIPODS IN SOUTHEASTERN GULF OF MEXICO
(Barnard, 1964) and Pseudohaustorius carolinensis Bousfield, 1965] are listed in Ortiz (1979) and one [Bemlos
waipio (Barnard, 1970) as Lembos processifer Pirlot, 1938], is listed in Oliva-Rivera and Jiménez-Cueto (1997).
These species were excluded based on the atypical habitats and distribution ranges reported. In addition, these
species have not been listed for the GM in the most updated checklists of amphipods in the region by LeCroy
(2002, 2011), Ortiz et al. (2007), LeCroy et al. (2009) and Ortiz and Lalana (2010).
FIGURE 2. Zoogeographical affinity of amphipod fauna in the tropical western Atlantic. (A) Regions in the tropical western
Atlantic after Ortiz et al. (2007) and LeCroy et al. (2009); gray lines represent the borders of regions in the GM and gray arrows
represent the borders of the Carolinian and Caribbean provinces. (B) Cluster diagram of amphipod assemblage among regions of
the tropical western Atlantic.
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FIGURE 3. Number of amphipod species (Gammaridea and Corophiidea) in regions of the Gulf of Mexico. NE, Northeast; SE,
Southeast; SW, Southwest; NW, Northwest. Data based on LeCroy et al. (2009); family Caprellidae and Cyamidae excluded.
Another species previously recorded from the GM (see LeCroy et al. 2009), but excluded from this checklist
was Melita nitida Smith, 1873. This species was listed by Oliva-Rivera and Jiménez-Cueto (1997) from the
Yalahau Lagoon, but based on specimens recently examined from that lagoon; M. nitida actually represents Melita
planaterga Kunkel, 1910.
Zoogeographic comments. The two zoogeographical provinces mostly recognized and widely accepted for
the benthic macrofauna of the TWA are the Carolinian and Caribbean provinces (Hedgpeth 1953; Briggs 1974;
Barnwell & Thurman 1984; Kensley & Schotte 1989; Rabalais et al. 1999; Engle & Summers 2000; Salazar-
Vallejo 2000; Raz-Guzman et al. 2004; Neigel 2009; Briggs & Bowen 2012). The Carolinian province is located in
the northern GM and has been considered part of the warm-temperate province, which includes the northwestern
Atlantic coast from Cape Hatteras (North Carolina) to Cape Canaveral (Florida). The Caribbean province is located
in the southern GM and has been considered part of the tropical province, which extends to the Orinoco Delta
River. The approximate boundaries between Carolinian and Caribbean provinces in the GM are Cabo Rojo
(Veracruz) on the southwestern end and Cape Romano (Florida) on the northeastern end.
The hierarchical cluster analysis displayed an overlap between the amphipod fauna and the zoogeographical
provinces described above. In this case the use of multivariate statistical methods (e.g. similarity index and average
linkage clustering) for establishing zoogeographic provinces was not diminished, supporting its efficacy. The use
of these statistical methods has been widely accepted among researchers who have explored the zoogeographical
boundaries in different benthic taxa in the western Atlantic; including mysids (Escobar-Briones & Soto 1991),
gastropods (Diaz 1995), macroinfauna (Engle & Summers 2000), decapods (Wickstec & Packard 2005),
cumaceans (Watling 2009), amphipods, echinoderms, mollusks, polychaetes, sponges and stony corals
(Miloslavich et al. 2010).
Winfield et al. (2007c) listed the biotic components dominant for amphipods in the southwestern GM as
Endemic (29%), Caribbean (25%) and Carolinian (25%). In this respect, although the native species are the major
component, the shared affinity between Caribbean and Carolinian provinces is also denoting a faunal turnover, as is
expected in this region. Thus, the distributional patterns found for southern GM amphipods by Winfield et al.
(2007c) and the present study suggest a gradual zoogeographical change from the Carolinian-Caribbean province
(southwestern region) to the Caribbean province (southeastern region).
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Based on the analyzed data matrix in the present study, extreme levels of endemism were found in the fauna
from regions of the Antillean arc with the highest levels in Barbados (100%) and Bermuda (69%), characteristic to
distant islands, and with the lowest level in Bahamas (16%), characteristic to a connected archipelago. Intermediate
levels of endemism but denoting a strong biotic isolation were presented in the fauna from the Caribbean and GM
with 47% and 25%, respectively. Particularly, the level of endemism in the GM was estimated at 27% by LeCroy et
al. (2009), pointing out that this level will diminish with a better knowledge of species distribution. In the present
study the endemicity in the GM diminished slightly due to the calculation, as it had been predicted above; it was
estimated with 59 endemic species in the present study, instead of 62 endemic species in LeCroy et al. (2009). With
respect to the endemism in the GM regions, there is a geographic latitudinal and longitudinal difference, likely
related to a thermal biogeographic barrier and a sedimentary biogeographic barrier, respectively. Latitudinally,
northern regions with a warm-temperate regime (NW= 5%, NE= 21%) presented higher levels of endemism than
southern regions with a tropical regime (SW= 1.5%, SE= 15%). Longitudinally, eastern regions with carbonated
sediments (NE= 21%, SE= 15%) presented higher levels of endemism than western regions with terrigenous
sediments (NW= 5%, SW= 1.5%). Furthermore, the southwest region showed the lowest level of endemism,
suitable to a region where presumably come together both Carolinian and Caribbean provinces and there is a high
faunal turnover (dissimilarity) from the northwest region to the southwest region (57%).
To explain both distributions in the GM provinces we should focus on historical and ecological biogeography.
The former is concerned with historical meteorological/geological events which actually formed the Gulf basin
(e.g. continental drift, cycles of glaciations, emergence of the Central American Isthmus, emergence of the Florida
peninsula, redirection of the North Equatorial Current northward), which have been treated by Mills (1965), Briggs
(1970), McKinney (1977) and Neigel (2009). The latter investigates and describes current environmental traits in
the Gulf basin (e.g. currents, depth, sediment, temperature, seabed topography, biotic interactions), which have
been treated by Hedgpeth (1953), Rabalais et al. (1999), Wicksten and Packard (2005), Winfield et al. (2006) and
Richards et al. (2007). In summary, amphipod distribution in the GM may have originated via historical events in
the tropical Atlantic (Myers & Lowry 2009). Thus, although the influence of the east Pacific (via Central American
Isthmus) on the Caribbean (and after on the GM) was high, the influence from the Atlantic was stronger
(McKinney 1977; Myers & Lowry 2009). This is currently supported by the amphipod zoogeography of Winfield
et al. (2007c), where the biotic components with less dominance in the southwestern GM are Euritopic (16%) and
Oregonian (5%). Furthermore, of 969 species collectively reported so far in the tropical western Atlantic and
tropical eastern Pacific (Ortiz et al. 2007; García-Madrigal 2008; Foster et al. 2009), 59 species display a
contemporary amphiamerican distribution, representing roughly 6% of the tropical amphipods of America.
Acknowledgments
Thanks are due to Gildardo Alarcón Daowz (SEMAR, Mexico) for approving the participation of the first author in
the oceanographic cruise and to María Teresa Herrera-Dorantes (CINVESTAV, Mexico) for sorting the benthic
material. The first author thanks to Sara LeCroy (University of Southern Mississippi, USA) and Oliver Coleman
(Museums für Naturkunde, Germany) for providing literature and to Kristine White (University of the Ryukyus,
Japan) for valuable comments and suggestions on the manuscript. The authors thank to anonymous reviewers who
helped to improve the manuscript.
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Winfield, I., Abarca-Arenas, L.G. & Cházaro-Olvera, S.I. (2007a) Crustacean macrofoulers in the Veracruz coral reef system,
SW Gulf of Mexico: checklist, spatial distribution and diversity. Les Cahiers de Biologie Marine, 48, 287–295.
Winfield, I., Cházaro-Olvera, S. & Álvarez, F. (2007b) ¿Controla la biomasa de pastos marinos la densidad de los peracáridos
(Crustacea: Peracarida) en lagunas tropicales? Revista de Biología Tropical, 55, 43–53.
Winfield, I., Escobar-Briones, E. & Álvarez, F. (2001) Crustáceos peracáridos asociados a praderas de Ruppia maritima
(Ruppiaceae) en la laguna de Alvarado, México. Anales del Instituto de Biología, Universidad Nacional Autónoma de
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Winfield, I., Escobar-Briones, E. & Álvarez, F. (2007c) Clave para la identificación de los anfípodos bentónicos del Golfo de
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Winfield, I., Escobar-Briones, E. & Morrone, J.J. (2006) Update checklist and identification of areas of endemism of benthic
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Mexicana de Biodiversidad, 80, S165–S175.
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BENTHIC AMPHIPODS IN SOUTHEASTERN GULF OF MEXICO
APPENDIX 1. List of amphipod species in alphabetical order by geographic region used in the zoogeographic analysis. NE,
Northeast; SE, Southeast; SW, Southwest; NW, Northwest. Data based on Ortiz et al. (2007) and LeCroy et al. (2009).
Species Bermuda Bahamas Caribbean Barbados NE SE SW NW
Acanthohaustorius intermedius 1
Acanthohaustorius pansus 1 1
Acanthohaustorius shoemakeri 1
Acanthohaustorius uncinus 1 1
Actogidiella cultrifera 1
Acuminodeutopus heardi 1
Acuminodeutopus naglei 1 1 1
Americhelidium americanum 1 1 1 1 1
Americorchestia barbarae 1
Americorchestia heardi 1
Americorchestia salomani 1
Americorophium ellisi 1
Americorophium rioplatense 1
Ameroculodes edwardsi 1
Ameroculodes miltoni 1
Ampelisca abdita 1 1 1 1 1
Ampelisca abyssicola 1
Ampelisca agassizi 1 1 1
Ampelisca bicarinata 1 1 1 1 1
Ampelisca brevisimulata 1 1
Ampelisca burkeri 1 1
Ampelisca cristata cristata 1 1 1 1
Ampelisca cristata microdentata 1
Ampelisca cristoides 1
Ampelisca holmesi 1 1
Ampelisca lobata 1 1
Ampelisca parapacifica 1 1 1 1
Ampelisca parapanamensis 1
Ampelisca paria 1
Ampelisca pugetica 1
Ampelisca romigi 1
Ampelisca schellenbergi 1 1 1 1
Ampelisca vadorum 1 1 1 1 1
Ampelisca venetiensis 1
Ampelisca verrilli 1
Amphideutopus dolichocephalus 1
Amphilochus ascidicola 1
Ampithoe hirsutimanus 1
Ampithoe longimana 1 1 1 1
Ampithoe marcuzzii 1 1
Ampithoe pollex 1 1
Ampithoe ramondi 11 1
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APPENDIX 1. (Continued)
Species Bermuda Bahamas Caribbean Barbados NE SE SW NW
Ampithoe valida 1 1 1
Anamaera hixoni 1
Anamixis cavatura 1 1 1
Anamixis vanga 1 1
Anelasmopus kraui 1
Apocorophium acutum 1 1
Apocorophium lacustre 1 1 1
Apocorophium louisianum 1 1 1 1
Apocorophium simile 1 1 1 1 1
Apohyale media 1 1 1 1
Apohyale perieri 1 1
Apohyale wakabarae 1
Apolochus casahoya 1 1 1 1
Apolochus delacaya 1 1
Apolochus neapolitanus 1 1 1
Apolochus pillaii 1 1
Argissa hamatipes 1 1 1
Aristias captiva 1
Aroui americana 1
Aruga holmesi 1
Audulla chelifera 1 1 1
Batea bousfieldi 1
Batea campi 1 1
Batea carinata 1 1
Batea catharinensis 1 1 1 1 1
Batea cuspidata 1 1 1
Batea schotti 1
Batea transversa 1
Bemlos barnardi 1
Bemlos dentischium 1 1
Bemlos foresti 1 1
Bemlos habanensis 1
Bemlos kunkelae 1 1
Bemlos longicornis 1 1
Bemlos mackinneyi 1 1 1
Bemlos mayensis 1 1
Bemlos minimus 1
Bemlos sanmartini 1
Bemlos scolosternum 1
Bemlos setosus 1 1
Bemlos spinicapus inermis 1 1
Bemlos spinicarpus spincarpus 1 1
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APPENDIX 1. (Continued)
Species Bermuda Bahamas Caribbean Barbados NE SE SW NW
Bemlos tempus 1
Bemlos tigrinus 1
Bemlos unicornis 1 1 1 1
Biancolina brassicacephala 1 1
Biancolina lowryi 1
Boca campi 1
Boca elvae 1 1
Boca megachela 1
Bogidiella perla 1
Bogidiella virginalis 1
Bruzelia pericu 1
Bruzeliopsis turba 1
Byblis cubensis 1
Byblisoides blasensis 1
Caribboecetes barbadensis 1
Caribboecetes crassicornis 1
Caribboecetes intermedius 1
Caribboecetes justi 1
Caribboecetes pterycornis 1
Caribseba tropica 1 1 1
Cebocaris grutesca 1
Ceradocus rubromaculatus 1
Ceradocus sheardi 1 1 1 1 1
Ceradocus shoemakeri 1 1 1 1 1
Cerapus benthophilus 1 1 1
Cerapus cudjoe 1 1
Cerapus thomasi 1
Cerapus tubularis 1 1 1 1
Chelorchestia costaricana 1
Chelorchestia forceps 1 1 1
Chevalia aviculae 1 1 1
Chevalia carpenteri 1 1
Chevalia mexicana 1 1 1
Colomastix bousfieldi 1 1 1 1
Colomastix camura 1 1 1
Colomastix cornuticauda 1
Colomastix denticornis 1
Colomastix falcirama 1 1 1
Colomastix gibbosa 1 1 1
Colomastix halichondriae 1 1 1 1
Colomastix heardi 1 1
Colomastix irciniae 1 1
Colomastix janiceae 1 1 1 1
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APPENDIX 1. (Continued)
Species Bermuda Bahamas Caribbean Barbados NE SE SW NW
Colomastix pusilla 1
Colomastix tridenta 1 1 1 1
Concarnes concavus 1 1 1 1
Confodiopisa scopulorum 1
Corocubanus guitarti 1
Curidia debrogania 1 1
Cymadusa compta 1 1 1 1 1
Cymadusa filosa 1 1 1 1
Cyphocaris johnsoni 1
Cyphocaris tunicola 1
Dissiminassa homosassa 1 1
Deflexiodes intermedius 1
Dulichiella appendiculata 1 1 1 1 1
Dumosus atari 1 1 1
Eclecticus eclecticus 1
Elasmopus balkomanus 1 1 1
Elasmopus bampo 1
Elasmopus brasiliensis 1
Elasmopus lemaitre 1
Elasmopus levis 1 1 1 1 1
Elasmopus pectenicrus 1 1 1
Elasmopus pocillimanus 1 1 1 1 1
Elasmopus rapax 1 1 1 1 1
Elasmopus spinidactylus 1
Elasmopus thomasi 1 1
Ensayara entrichoma 1 1
Ensayara jumane 1
Eobrolgus spinosus 1 1
Ericthonius brasiliensis 1 1 1 1 1
Ericthonius rubricornis 1
Eriopisa incisa 1 1
Eudevenopus honduranus 1 1 1
Eudevenopus metagracilis 1
Eurythenes obesus 1
Eusirogenes adad 1
Eusiroides monoculoides 1
Eusiroides yucatanensis 1
Floresorchestia guadalupensis 1
Gammarella curvata 1
Gammaropsis arawakia 1
Gammaropsis atlantica 1 1 1
Gammaropsis sutherlandi 1
Gammaropsis togoensis 1 1 1
......continued on the next page
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APPENDIX 1. (Continued)
Species Bermuda Bahamas Caribbean Barbados NE SE SW NW
Gammarus mucronatus 1 1 1 1
Gammarus tigrinus 1
Garosyrrhoe bigarra 1
Garosyrrhoe luquei 1
Gibberosus myersi 1 1 1
Gitana dominica 1
Gitanopsis petulans 1
Gitanopsis templadoi 1
Globosolembos francanni 1
Globosolembos smithi 1 1 1 1 1
Grandidierella bonnieroides 1 1 1 1 1
Haploops setosa 1
Harpinia excavata 1
Harpinia intermedia 1
Hartmanodes nyei 1 1 1 1 1
Haustorius jayneae 1
Haustorius mexicanus 1
Heterophoxus oculatus 1
Hippomedon pensacola 1
Hoplopheonoides obesa 1
Hoplopheonoides shoemakeri 1
Hornellia atlanticus 1
Hornellia tequestae 1
Hourstonius laguna 1 1 1 1 1
Hourstonius tortugae 1 1 1
Hyale diplodactyla 1
Hyale pygmaea 1
Idunella sketi 1
Ileraustroe torpens 1
Iphimedia zora 1
Jassa marmorata 1 1 1 1
Jerbania americana 1 1
Latacunga comanita 1
Laticorophium baconi 1 1
Lembos unifasciatus reductus 1 1 1
Lembos unifasciatus unifasciatus 1 1 1
Lembos websteri 1
Lepechinella aberrantis 1
Lepechinella raua 1
Lepidactylus triarticulatus 1 1
Lepiduristes lepidus 1
Leptocheirus rhizophorae 1 1
Leucothoe ashleyae 1 1 1
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APPENDIX 1. (Continued)
Species Bermuda Bahamas Caribbean Barbados NE SE SW NW
Leucothoe ayrtonia 1
Leucothoe kensleyi 1 1
Leucothoe laurensi 1
Leucothoe panpulco 1
Leucothoe spinicarpa 1 1 1 1 1
Liljeborgia bousfieldi 1 1
Liocuna caeca 1
Listriella andresi 1
Listriella bahia 1 1
Listriella barnardi 1 1 1
Listriella carinata 1 1 1
Listriella Kensleyi 1
Listriella quintana 1
Lysianopsis alba 1 1 1 1
Lysianopsis hummelincki 1
Lysianopsis ozona 1 1
Maera diffidentia 1 1
Maera lucinae 1
Maera tinkerensis 1
Maera williamsi 1
Maeracoota galani 1
Maeropsis rathbunae 1
Mallacoota carausui 1 1
Marigidiella crassipes 1
Melita dentata 1
Melita elongata 1 1 1
Melita guanaense 1
Melita intermedia 1 1
Melita leiotelson 1
Melita longisetosa 1 1 1 1
Melita nitida 1 1 1 1 1
Melita persona 1
Melita planaterga 1 1 1
Melita stocki 1 1
Metaniphargus sabulonis 1
Metatiron bellairsi 1
Metatiron triocellatus 1 1
Metatiron tropakis 1 1 1
Metharpinia floridana 1 1 1 1
Microjassa bahamensis 1
Microjassa floridensis 1
Microjassa tetradonta 1
Microphoxus minimus 1
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BENTHIC AMPHIPODS IN SOUTHEASTERN GULF OF MEXICO
APPENDIX 1. (Continued)
Species Bermuda Bahamas Caribbean Barbados NE SE SW NW
Microprotopus raneyi 1 1 1 1
Microprotopus shoemakeri 1 1 1
Miramarassa sanchezi 1
Monocorophium acherusicum 1 1 1 1 1
Monocorophium insidiosum 1 1
Monocorophium tuberculatum 1 1
Nasagenia bacescui 1 1
Nasagenia comisariensis 1
Nasagenia yucatanensis 1 1
Neoischyrocerus vidali 1
Neomegamphopus heardi 1
Neomegamphopus hiatus 1 1 1
Neomegamphopus roosevelti 1
Nepanamixis dianthus 1
Netamelita barnardi 1 1
Netamelita brocha 1 1
Netamelita tabaci 1
Nototropis minikoi 1 1 1 1
Nototropis urocarinatus 1 1 1
Oediceroides synparis 1
Orchestia grillus 1 1
Orchomene stocki 1
Orchomenella perdido 1
Orchomenella thomasi 1
Orenoquia serrata 1
Paracentromedon carabicus 1
Parahaustorius longimerus 1
Parahaustorius obliquus 1
Parametopella cypris 1
Parametopella texensis 1 1 1
Paramicrodeutopus myersi 1 1 1
Parargissa galatheae 1
Parhyale fascigera 1 1 1
Parhyale hawaiensis 1 1 1 1
Parhyale inyacka 1
Parhyalella batesoni 1
Parhyalella whelpleyi 1 1
Pariphinotus seclusus 1 1
Pariphinotus seticoxa 1 1
Parpano cebus 1
Parpano composturus 1
Pedicorophium laminosum 1 1 1 1
Perioculodes cerasinus 11
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APPENDIX 1. (Continued)
Species Bermuda Bahamas Caribbean Barbados NE SE SW NW
Photis dentata 1
Photis longicaudata 1 1 1
Photis macromanus 1 1 1 1
Photis melanica 1 1 1 1
Photis pugnator 1 1 1 1
Photis reinhardi 1
Photis trapherus 1 1
Platorchestia platensis 1 1 1 1 1
Plesiolembos ovalipes 1 1
Plesiolembos rectangulatus 1 1 1 1
Podobothrus bermudensis 1
Podocerus brasiliensis 1 1 1 1 1
Podocerus chelonophilus 1
Podocerus cristatus 1
Podocerus kleidus 1 1
Podocerus lazowasemi 1
Podocerus tachyrheo 1
Pontogeneia bartschi 1
Proharpinia barbada 1
Protohadzia schoenerae 1 1 1
Protohaustorius bousfieldi 1 1
Protohyale macrodactyla 1 1
Psammogammarus bluefieldensis 1
Psammomelita uncinata 1
Pseudamphithoides bacescui 1 1 1
Pseudoamphitoides incurvaria 1
Pseudohaustorius americanus 1 1
Pseudomegamphopus excavatus 1
Quadrimaera ariel 1
Quadrimaera caliban 1
Quadrimaera ceres 1
Quadrimaera cristianae 1 1
Quadrimaera inaequipes 1
Quadrimaera miranda 1 1 1
Quadrimaera pacifica 1 1
Quadrimaera pieteri 1
Quadrimaera quadrimana 1 1 1
Quadrimaera sarae 1 1
Rachotropis lobata 1
Rachotropis portoricana 1
Resupinus spinicaudatus 1
Rimakoroga floridana 1
Seba robusta 1
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BENTHIC AMPHIPODS IN SOUTHEASTERN GULF OF MEXICO
APPENDIX 1. (Continued)
Species Bermuda Bahamas Caribbean Barbados NE SE SW NW
Sennaia bidactyla 1
Shoemakerella cubensis 1 1 1 1
Shoemakerella lowryi 1
Socarnopsis catacumba 1
Spathiopus cojimarensis 1
Spathiopus looensis 1
Stegocephaloides calypsonis 1
Stenothoe gallensis 1 1 1 1 1
Stenothoe georgiana 1 1
Stenothoe symbiotica 1
Stephonyx biscayensis 1 1
Stephonyx carinatus 1
Stephonyx incertus 1
Sunamphitoe pelagica 1 1
Synopia scheeleana 1
Synopia ultramarina 1 1 1
Syrrhoe papyracea 1
Tabatzius muelleri 1 1
Talorchestia fritzi 1
Talorchestia marcuzzi 1
Talorchestia margaritae 1
Tethygeneia longleyi 1
Thalassostygius exiguus 1
Thetorchestia antillensis 1 1
Thetorchestia karukerae 1
Thetorchestia sulensoni 1
Tiburonella morrocoyensis 1
Tiburonella viscana 1
Tropichelura gomezi 1 1
Tropichelura insulae 1
Tryphosella apalachicola 1 1
Tryphosella uristesi 1
Uhlorchestia uhleri 1 1 1
Unciola irrorata 1
Unciola serrata 1 1
Vemana compressa 1
Vemana lizata 1
Victoriopisa guanarocana 1
Westwoodilla longimana 1
... The latitudinal gradient in temperature through these provinces causes a warm-temperate condition on the Carolinian province and a tropical condition on the Caribbean province (Belanger et al., 2012;Neigel, 2009), that converges in the Gulf of Mexico (GoM) and influences the distribution pattern of marine species assemblages (Macpherson, 2002;Reuscher & Shirley, 2014). Preliminary findings on amphipod distribution from the GoM suggest that the species composition from the northern GoM shows affinity with the Carolinian ecoregion, and species composition from the southern GoM with Caribbean ecoregions (Paz-R ıos et al., 2014;Paz-R ıos & Ardisson, 2013;Raz-Guzm an & Soto, 2017;Winfield et al., 2007). A close analysis of the geographic distribution trends of amphipods from the Caribbean Sea has shown a significant similarity in species composition among ecoregions, even in those geographically distant, such as the Western Caribbean and Southern Caribbean ecoregions (Mart ın et al., 2013;Miloslavich et al., 2010). ...
... The first insight on the biogeographic affinity of the benthic amphipods from the Yucatan continental shelf (YCS) with tropical areas from the wNWA suggests affinities with both the Carolinian and Caribbean provinces (Paz-R ıos & Ardisson, 2013). The biological and ecological characteristics of amphipods (e.g., direct development, relatively high fecundity rates, local recruitment, limited capacity for dispersal, and extended parental care) suggest they are a feasible biological model to analyze biogeographic regionalization; furthermore, they have been used as potential 'markers' of Earth's historical events (Arfianti & Costello, 2020;Copilaş-Ciocianu et al., 2020). ...
Article
The biodiversity and biogeographic affinity of benthic amphipods from the Yucatan continental shelf with the warm Northwest Atlantic ecoregions were analysed using species occurrence data from benthic marine habitats of the continental shelf (< 200 m). A comprehensive collection of distributional data (presence-only) was obtained from different sources and newly-sampled material and sorted according to 12 ecoregions from the Northwest Atlantic. Distribution of species richness, taxonomic distinctness, endemism, and spatial replacement was analysed across ecoregions. The faunal relationships among ecoregions were explored using a clustering analysis based on the Sørensen dissimilarity index, and a cladistic analysis of distributions and endemism based on parsimony. Results from the Yucatan shelf showed a representative species pool from the highly diverse Northwest Atlantic amphipod fauna (202 spp.), with intermediate levels of endemism and taxonomic distinctness. Results from dissimilarity and parsimony showed two groups of amphipod assemblages consistent with two of the main biogeographic provinces in the Northwest Atlantic: Carolinian and Caribbean. The incorporation of the Yucatan shelf species assemblage, as an ecoregion into the used classification scheme, had implications on the amphipods biogeographic affinity identification. The Yucatan ecoregion led to a latitudinal spatial replacement of amphipod species across ecoregions and provinces, revealing that the Yucatan ecoregion has a higher biogeographic affinity with tropical ecoregions of the Caribbean province. The spatial replacement of amphipods suggests that the Southern Gulf of Mexico ecoregion has a higher affinity with warm-temperate ecoregions of the Carolinian province and is proposed as a transitional zone between the identified provinces.
... The original description of Chevalia aviculae did not adequately define the species. Consequently, there have been a number of mis-identifications of Chevalia aviculae that are probably new species (Barnard & Thomas, 1987;Souza-Filho et al, 2010), and a number of unconfirmed records of unillustrated and undescribed material from South Africa (K.H. Barnard, 1916;Griffiths, 1973Griffiths, , 1974aGriffiths, , 1974bGriffiths, , 1975Griffiths, , 1976Griffiths, , 1977, Mozambique (K.H. Barnard, 1955), the Red Sea (K.H. Barnard, 1937), Gulf of Mexico (Thomas, 1993;Paz-Rios & Ardisson, 2013) and Cuba (Ortiz & Lalana, 2010). Barnard and Thomas (1987) recognised that many of the earlier records of Chevalia aviculae warranted further consideration recognising a potential species complex and this hypothesis was later supported by other Chevalia workers (Lazo-Wasem, 1999;Myers, 2009). ...
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Full-text available
The amphipod family Chevaliidae Myers & Lowry, 2003 (Amphipoda: Senticaudata) contains two genera: Chevalia Walker, 1904 (13 species), and Bryoconversor Lörz, Myers & Gordon, 2014 (1 species). Chevalia is a marine genus with a cosmopolitan distribution in circumtropical and temperate waters. Prior to this study, records of Chevalia from Australian waters were limited. Here, we describe five new species of Chevalia from Australian waters, C. bardi sp. nov., C. burrewarra sp. nov., C. csiro sp. nov., C. freycinet sp. nov. and C. sprightly sp. nov. The original description of Chevalia aviculae no longer adequately defined the species and is redescribed based on syntypic material from East Cheval Paar, Sri Lanka. Additionally, new distribution records are provided for the New Zealand species Bryoconversor tutus Lörz, Myers & Gordon, 2014. Material reported is from both shallow and deep-water samples from 1–660 m depth. The prevalence of various gender and intersex states within specimens of chevaliids is discussed. An updated key to the 19 world species of Chevaliidae and a field guide to the seven known Australian and New Zealand species is provided.
... The SGoMx has been proposed as a transition zone between the Carolinian and Caribbean provinces (e.g. Paz-Ríos & Ardisson 2013, Raz-Guzmán & Soto 2017, Paz-Ríos et al. 2021. In this work, however, the SGoMx shows a homogeneous assemblage with a low degree of endemism (Figs. ...
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The biogeography of hydrozoans encompasses a broad scope of study that involves various challenges due to their diverse distributional strategies and life cycle characteristics. This work aims to study the biogeographic patterns of hydrozoans in the Gulf of Mexico. Occurrence records on hydrozoans were compiled through the Global Biodiversity Facility Information database and peer-reviewed literature. Biogeographic patterns were addressed through (1) the identification of biological assemblages, using hierarchical clustering with contiguity constraint; (2) the decomposition of beta diversity into species replacement, nestedness, and local contribution to beta diversity (LCBD); and (3) the identification of areas of endemism with a parsimony analysis of endemicity (PAE). The northern Gulf of Mexico and the Yucatán Peninsula contain a large hydrozoan assemblage that splits into smaller groups at different levels, characterized by species replacement and high LCBD values. By contrast, the southern Gulf of Mexico contains a homogenous assemblage, which exhibits low LCBD values and contributes strongly to nestedness. PAE identified 19 areas of higher-level endemism, concentrated mainly in shelf zones of the Yucatán and Florida peninsulas. The distribution patterns of hydrozoans in the Gulf of Mexico may be shaped by the life cycle characteristics of the taxa and the geological history of the region, relating either to neritic or oceanic zones. The northern Gulf reflects a heterogeneous biological composition with a complex biogeographical history, which makes this area of particular interest for future studies, as it likely represents a transition zone. This premise must be corroborated in the future.
... Since 2008, several studies have attempted to update the species inventory in the southern Gulf of Mexico reef with a special focus on cryptic and less charismatic taxa. This inventory is steadily increasing the knowledge of the region's species diversity of several groups such as fishes (Moreno-Mendoza et al., 2011;Robertson et al., 2016;Zarco-Perelló et al., 2014), crustaceans (Duarte et al., 2014;Escobar-Briones & Jiménez-Guadarrama et al., 2010;Paz-Ríos & Ardisson, 2013;Paz-Ríos et al., 2013a, b, 2018a, 2018bSantana-Moreno et al., 2013), echinoderms (Hernández-Díaz et al., 2013;Solís-Marín et al., 2015), cnidarians (González-Muñoz et al., 2013;Mendoza-Becerril et al., 2018), sponges (Ugalde et al., 2015) and mollusks (Ortigosa et al., 2013(Ortigosa et al., , 2015(Ortigosa et al., , 2018Reyes-Gómez et al., 2017;Sanvicente-Añorve et al., 2012). ...
... No se llegó a una identificación más detallada, pues hace falta trabajo taxonómico y conocimiento para las especies mexicanas del estado de Veracruz, ya que la primera publicación sobre este grupo y en general para los peracáridos data de la década de los 70´s con los trabajos de Bacescu, McKinney y Price y por las reorganizaciones e interpretaciones de los caracteres morfológicos de algunos investigadores (Winfield y Ortiz, 2011). Se ha documentado que H. azteca se distribuye ampliamente en los sistemas costeros del golfo de México (Ortiz et al., 2007;Hernández et al., 2010b;Montalvo-Urgel et al., 2010;Paz-Ríos y Ardisson, 2013;Mirya-Vidal et al., 2016). Casset et al. (2001) reportaron que las poblaciones de dos especies del género Hyalella, mostraron variaciones relacionadas al ciclo de la vegetación sumergida. ...
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The first list of groups of benthic invertebrates Mandinga lagoon complex (MLC) is presented. Seven collections were carried out in dry seasons from 2008 to 2015 and one in rainy in 2015. The endo-benthic organisms were collected with a dredge and the epi-benthic organisms, with a renfro and seine net. All organisms were identified to the permissible level. The list consists of a total of 43 groups, distributed in eight phylums, seven classes, nine orders, 16 families and three types of larvae. The groups Decapoda (10), Gastropoda (8), Amphipoda (4), Bivalvia (3), Tanaidacea (3) and Isopoda (3), were the most diverse, followed to by the groups that were determined at higher levels a Family (12). The diversity of groups is similar to that of other coastal systems in Veracruz, where the orders Decapoda, Amphipoda and Tanaidacea were the most diverse, followed by Isopoda. The results of the present investigation represent an important contribution for the knowledge of the diversity of the system studied and the distribution of the groups in Veracruz and the Gulf of Mexico.
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This book presents many of the species that inhabit the intertidal rocky shores and reveals a part of the wonderful biodiversity of the north coast of the state of Rio de Janeiro. It allows the reader to deepen knowledge on the taxonomy and ecology of the crustacean fauna of the region and it will be an important tool for taxonomy. Sheets of 63 species are presented, containing photos, morphological description and information on distribution, habitat and ecology, as well as taxonomic comments when necessary. Schemes of the external morphology of the groups were inserted to facilitate the description of the species and the reader's understanding. A cheklist of species with locations of occurrence is also presented. The research aimed to fill the knowledge gap about the rocky shore crustacean fauna, and the results allowed not only to know the local fauna, but also to describe two species new to science. The species Pseudozeuxo fischeri was recorded only on the rocky shores of Areias Negras beach, in the municipality of Rio das Ostras (RJ), while Apseudomorpha brasiliensis was recorded only in the Santana Archipelago, located eight kilometers off the coast of Macaé (RJ). The study is especially important considering that some of the collection areas of this study are located within four conservation units: Monumento Natural dos Costões Rochosos and the Área de Relevante Interesse Ecológico de Itapebussus (Rio das Ostras municipality), in addition to the Parque Natural Municipal Arquipélago de Santana and Área de Preservação Ambiental do Arquipélago de Santana (Macaé municipality). It is important to point out that the region has been affected by different anthropic impacts, including those derived from oil activities and the expansion of the Port of Imbetiba, which can threaten the biodiversity of the Santana Archipelago and other places. In addition to informing about the biodiversity found in each of the locations, the book is an alert to the need to preserve this beautiful fauna, so that future generations can also admire it.
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O livro apresenta muitas das espécies que habitam o entremarés dos costões rochosos e revela uma parte da maravilhosa biodiversidade do litoral norte do estado do Rio de Janeiro. Permite ao leitor aprofundar conhecimentos na taxonomia e ecologia da fauna de crustáceos da região constituirá importante ferramenta para taxonomia. São apresentadas fichas de 63 espécies com fotos, descrição morfológica e informações sobre distribuição, hábitat e ecologia além de comentários taxonômicos quando necessário. Esquemas da morfologia externa dos grupos foram inseridos para facilitar a descrição das espécies e a compreensão do leitor. Uma lista de espécies com as localidades de ocorrência é apresentada. Essa pesquisa visou preencher uma lacuna de conhecimento sobre a fauna de crustáceos que habita os costões rochosos da região. Os resultados desse projeto permitiram também descrever duas espécies novas à ciência! A espécie Apseudomorpha brasiliensis foi registrada apenas no Arquipélago de Santana, localizado a oito quilômetros da costa de Macaé (RJ), enquanto Pseudozeuxo fischeri foi registrada apenas nos costões rochosos da praia de Areias Negras, no município de Rio das Ostras (RJ). Esse estudo é especialmente importante considerando que as áreas de coleta encontram-se dentro de seis Unidades de Conservação municipais: o Monumento Natural dos Costões Rochosos e a Área de Relevante Interesse Ecológico de Itapebussus (Município de Rio das Ostras), o Parque Natural Municipal Arquipélago de Santana e Área de Preservação Ambiental do Arquipélago de Santana (Município de Macacé), além da Área de Proteção Ambiental Marinha de Armação dos Búzios e Área de Proteção Ambiental do Mangue de Pedras (Município de Armação dos Búzios). É importante salientar que a região tem sido afetada por diferentes impactos antrópicos, incluindo aqueles derivados das atividades petrolíferas e da expansão do Porto de Imbetiba que podem ameaçar a biodiversidade do Arquipélago de Santana e de outros locais. Além de informar sobre a biodiversidade encontrada em cada uma das localidades, o livro é um alerta para a necessidade de preservar essa belíssima fauna, para que próximas gerações possam também admirá-la.
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The amphipod genus Jassa Leach, 1814 now comprises 24 species that occur in temperate regions of both hemispheres on solid substrates from the lower intertidal zone to 500 m depth. The propensity for some species to form dense colonies in water intake structures and offshore platforms has brought them to attention as an unwanted pest. Based on the examination of ~25,000 specimens from ~1,100 museum and private collections, it is evident that some species of Jassa have been transported by human vectors since at least the 19th century and now occur widely. Their colonial, tube-living habit enables such transport, and collection records document them on ships, buoys and portable water systems as well as on natural movable substrates such as logs, drift algae and larger crustaceans. Because Jassa can be so readily found, but species discrimination has had a problematic history, the purpose of this monograph is to assist researchers to identify species through illustrations, descriptions, keys and habitat summaries. Seven species which were named in the 19th century but whose names have lapsed are placed in the context of currently known species. Two new species, J. laurieae n. sp. and J. kimi n. sp. are described, and J. monodon (Heller, 1866) and J. valida (Dana, 1853) are resurrected. Jassa mendozai Winfield et al., 2021 is submerged under J. valida, and J. cadetta Krapp et al., 2008 and J. trinacriae Krapp et al., 2010 are submerged under J. slatteryi Conlan, 1990. Morphological differences are related to current understanding of growth, behaviour and ecology. CO1 analysis suggests a Southern Hemisphere origin with diversification northward and an evolutionary direction toward greater physiological plasticity, leading to success in long distance transport and establishment in exotic locations. Correct identification of Jassa world-wide will facilitate further research on this ecologically important genus and will allow for differentiation of indigenous from exotic introductions.
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Amphipod species collected during three oceanographic campaigns (2010–2012) were analyzed to describe their spatiotemporal community distribution trends and their relationships with bottom water and sediment variables. The results show that the species richness (117 spp.) did not reach its maximum value according to the species accumulation curve (up to 187 spp.). Multivariate analyses and constrained ordinations techniques detected three main amphipod assemblages along the longitudinal gradient (i.e., Western Caribbean, Mid-Yucatan, and West-Yucatan) and during two temporal hydrographic scenarios (i.e., upwelling in 2010–2011 and non-upwelling in 2012). In 2010–2011, low values in species richness and abundance from the Western Caribbean and eastern Mid-Yucatan assemblages were associated with relatively low bottom-water temperatures from the upwelling systems. In 2012, the absence of upwelling and the occurrence of a warm-core anticyclonic eddy seemed to cause an increase in species richness and abundance in the three assemblages. The hydrographic variability and sediment characteristics are suggested as the major environmental drivers that shapes the soft-bottom amphipod community structure and diversity in the Yucatan continental shelf.
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Frog crabs are marine brachyurans predominantly tropical-subtropical adapted for inhabiting soft sandy bottoms across a wide bathymetric range. In the Gulf of Mexico, seven species of the superfamily Raninoidea have been reported. This study documents further records of 495 frog crabs collected in the south-southwest Gulf of Mexico, belonging to Raninoides louisianensis Rathbun, 1933 (88.1%), Raninoides lamarcki A. Milne-Edwards and Bouvier, 1923 (10.3%), Lysirude nitidus (A. Milne-Edwards, 1880) (1.2%), and Raninoides laevis (Latreille, 1825) (0.4%). The updated records of Raninoidea species from the Gulf of Mexico (based on literature review and results from the present study) extend the geographical distribution of R . louisianensis to the entire Gulf of Mexico. These records indicate that the south-southwest and east-southeast geographic sectors (both in the tropical portion of the Gulf of Mexico) have the highest number of species (6); further, the lower bathymetric limit for R . louisianensis and R . lamarcki is extended. A cluster analysis based on presence/absence data using the Jaccard similarity coefficient provided additional support indicating that the eight geographic sectors of the Gulf of Mexico were closely related (≥0.6) in terms of species composition.
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Se presenta una lista con 52 especies de crustáceos peracáridos distribuidas en 10 estaciones de estudio ubicadas en la costa Sur de la Península de Guanahacabibes, en la región occidental de Cuba. De estas especies, 10 han resultado ser nuevos registros para aguas cubanas de los cuales 5 son isópodos, 4 son anfípodos y 1 es un cumáceo. También se presenta una lista con las 30 especies de decápodos que fueron observados o colectados durante los muestreos.
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A new species of amphipod of the genus Lysianopsis from the Veracruz Coral Reef System, SW Gulf of Mexico is described. Lysianopsis adelae n. sp., was collected in the sediments at the base of the sponge Aplysina fistularis at a depth of 10 m. The differences among L. alba, L. hummelincki, and L. ozona, recorded from Gulf of Mexico and Caribbean Sea are pointed out and they are compared with the new species.
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The three major groups of marine and estuarine macroinvertebrates of the tidal marshes of the northern Gulf are: polychaete worms, mollusks and crustaceans. Information on the recognition characters, distribution, habitat, and biology of each species is given.-from US Govt Report Announcements, 16, 1982
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The 53 species of Mysidacea recorded in the Gulf of Mexico belong to the Lophogastridae, Petalophthalmidae, and Mysidae, the last being the most diverse with 48 species. The other two families include species distributed in open waters and restricted to the NE sector of the Gulf. Some 65% of the species in the Gulf are restricted to coastal areas, living in seagrass beds and coral reefs; 39% of the species occur in both coastal and continental shelf areas. Information for species occurring in archibenthic, bathypelagic and abyssal zones is scarce. Endemic species comprise 37% of the mysid composition of the Gulf. Affinity to the Virginian Province is 14%, and 28% Caribbean-Antillean. Amphi-American and amphi-Atlantic species represent 3% each of the fauna. Some 15% of the species are eurytopic faunistic components. -from English summary