This study presents the taxonomic description of two new sponge species that are intimately associated with the hyperarid mangrove ecosystem of Qatar. The study includes a preliminary evaluation of the sponges' potential bioactivity against pathogens. Chalinula qatari sp. nov. is a fragile thinly encrusting sponge with a vivid maroon colour in life, often with oscular chimneys and commonly recorded on pneumatophores in the intertidal and shallow subtidal zone. Suberites luna sp. nov. is a massive globular-lobate sponge with a greenish-black colour externally and a yellowish orange colour internally, recorded on pneumatophores in the shallow subtidal zone, with large specimens near the seagrass ecosystem that surrounds the mangrove. For both species, a drug extraction protocol and an antibacterial experiment was performed. The extract of Suberites luna sp. nov. was found to be bioactive against recognized pathogens such as Staphylococcus epidermidis, Staphylococcus aureus and Enterococcus faecalis, but no bioactive activity was recorded for Chalinula qatari sp. nov. This study highlights the importance of increasing bioprospecting effort in hyperarid conditions and the importance of combining bioprospecting with taxonomic studies for the identification of novel marine drugs.
This study presents the taxonomic description of two new sponge species that are intimately associated with the hyperarid mangrove ecosystem of Qatar. The study includes a preliminary evaluation of the sponges' potential bioactivity against pathogens. Chalinula qatari sp. nov. is a fragile thinly encrusting sponge with a vivid maroon colour in life, often with oscular chimneys and commonly recorded on pneumatophores in the intertidal and shallow subtidal zone. Suberites luna sp. nov. is a massive globular-lobate sponge with a greenish-black colour externally and a yellowish orange colour internally, recorded on pneumatophores in the shallow subtidal zone, with large specimens near the seagrass ecosystem that surrounds the mangrove. For both species, a drug extraction protocol and an antibacterial experiment was performed. The extract of Suberites luna sp. nov. was found to be bioactive against recognized pathogens such as Staphylococcus epidermidis, Staphylococcus aureus and Enterococcus faecalis, but no bioactive activity was recorded for Chalinula qatari sp. nov. This study highlights the importance of increasing bioprospecting effort in hyperarid conditions and the importance of combining bioprospecting with taxonomic studies for the identification of novel marine drugs.
The Persian-Arabian Gulf (PAG) is considered an extreme marine environment due to its
hyperthermic and hypersaline conditions [1-3]. The environment in the southwestern coast
of the PAG is particularly extreme. This shallow-water region and the associated
mangrove settings has hyperarid conditions with temperature and salinity reaching
values as high as 49°C and 75 ppt [4-7], levels much
higher than the East coast of the Gulf [1-3,7-11]. The southwestern coast forms an isolated
marine province with a high rate of marine endemism and lower species richness than
the eastern coast of PAG, the latter receives an influx of waters from the Indian
Ocean which results in a higher diversity of species [1,12-15]. The high rate of endemism found in the
western coast of PAG, and the as yet, low number of taxonomic descriptions [1,14] for the region, indicate potential for the
discovery of species new-to-science.Marine ecosystems have considerable potential for bioprospecting, and several new
drugs are described and isolated every year, yet these natural resources, which can
produce economic and societal benefits, remain largely unexplored [16-20]. A significant majority of new marine
natural products have come from sponges (Phylum Porifera) [21]. Chemical compounds isolated from sponges
have been found to have anti-inflammatory, antibiotic, anticancer and anticoagulant
properties [22-30]. Sponges are multicellular
invertebrates [31-33] that have evolved as filter
feeders in aquatic environments. Sponges naturally process a huge volume of water
daily and as a consequence, may concentrate a wide variety of pathogens [34,35]. Due to this, sponges have developed
effective defence systems based on bioactive secondary metabolites including
antibacterial substances [33,36].Despite their economic importance, virtually nothing is known about sponge diversity
in the coastal areas in the Gulf, with only a few sponge records from the Arabian
Sea and adjacent areas [1,28,37,38]. Environmental stress has been shown to
concentrate toxins in sponges [39], and higher temperatures to be related with the bioactivity [21]. Therefore, the study of
marine sponges in the extreme, hyperarid conditions found in the Southwest of PAG
has potential for both the discovery of potential bioactive metabolites and species
new to science.The aims of this study are to describe two new sponge species and provide a
preliminary evaluation of their bioactivities against pathogens.
Material and methods
Study area
Shallow-water hyperarid mangrove ecosystems were studied at Al-Khor (25.69502778,
51.54694444) and Al-Dhakira (25.749228, 51.539267), Qatar. These areas do not
experience any input of fresh water, but saline tidal channels are present.
Areas of seagrass and oyster beds, interspersed with rocky substrate, surround
and extend out from the mangroves in the shallow subtidal zone (<1 m) (Fig 1). The coastal zones of
Qatar are characteristic by gently sloping shores and a large tidal range which
result in large intertidal and shallow subtidal zones.
Fig 1
Collection localities in Qatar: (A) the location of Qatar within the
Persian-Arabian Gulf (PAG); (B) the location of the studied mangrove
settings and the other locations around Qatar that was searched for
sponge species; (C) the studied mangrove settings in Al-Khor and
Al-Dhakira highlighting the large area with shallow depth around the
mangrove; (D) schematic profile of the mangrove ecosystem in the coastal
intertidal zone with the forest area and the shallow subtidal zone with
patches of seagrass and oyster-beds (rocks).
Collection localities in Qatar: (A) the location of Qatar within the
Persian-Arabian Gulf (PAG); (B) the location of the studied mangrove
settings and the other locations around Qatar that was searched for
sponge species; (C) the studied mangrove settings in Al-Khor and
Al-Dhakira highlighting the large area with shallow depth around the
mangrove; (D) schematic profile of the mangrove ecosystem in the coastal
intertidal zone with the forest area and the shallow subtidal zone with
patches of seagrass and oyster-beds (rocks).
Taxonomy and systematics
Sponges were collected in the intertidal and subtidal zones in the studied arid
mangrove ecosystem. Most specimens were collected by snorkelling and freediving
at the edge of tidal mangrove channels. Field studies did not involve endangered
or protected species and there is no specific permission required for collection
of Porifera in these locations. Specimens were photographed in
situ using underwater cameras (Mark-ii and Fantasea housing
FG7X-II). Large pieces of each species were transported to the laboratory and
preserved in 70% ethanol. Methods for identification followed standard taxonomic
procedures [31,32,40]. In the laboratory, thick longitudinal
and cross sections were hand-cut using a scalpel, dehydrated in 98% alcohol,
clarified in clove oil and mounted in Canada Balsam on microscope slides. These
were used to examine the choanosomal and ectosomal skeleton. A small piece of
tissue was dissolved in bleach to make a slide of the sponge spicules, the
resulting spicules were washed in several changes of water and alcohol then
mounted using Canada Balsam on microscope slides. The spicule and skeleton
slides were observed and photographed using a compound microscope (Olympus
CX22Led with an attached Nikon 7200 and an Olympus BX53 with camera DP73) and
scanning electronic microscope (FEI Quanta-200). Spicule measurements were made
using Olympus cellSens software and are presented as minimum length (mean
length) maximum length by minimum width (mean width) maximum width, n = X.
Specimen vouchers were deposited in the marine collection of the Environment
Science Centre at Qatar University (ESC-QU). Holotypes of each new species have
been donated to the Natural History Museum of London (NHMUK).
Nomenclature acts
The electronic edition of this article conforms to the requirements of the
amended International Code of Zoological Nomenclature, and hence the new names
contained herein are available under that Code from the electronic edition of
this article. This published work and the nomenclatural acts it contains have
been registered in ZooBank, the online registration system for the ICZN. The
ZooBank LSIDs (Life Science Identifiers) can be resolved and the associated
information viewed through any standard web browser by appending the LSID to the
prefix "http://zoobank.org/". The LSID for this
publication is: urn:lsid:zoobank.org:pub:91890F03-5B54-4826-8280-C30E93E02405.
The electronic edition of this work was published in the PlosOne journal with an
eISSN 1932-6203 and has been archived and is available from the following
digital repositories: PubMed Central, LOCKSS.
Ecological description
After the first taxonomic identification, more than 50 freediving and snorkelling
were performed in the tidal channels surrounding mangroves, and seagrasses, to
identify zonation and distribution of the described species. In addition several
dives were undertaken in shallow subtidal zones around Qatar, including Um-Bab,
Dukhan and Janan Island in the west Coast, Shamal, Al-Ruwais and Fuwarit in the
North coast and Al-Khor, Al-Dhakira, Doha, Al-Alyia Island, Al-Wakrah and
Sea-Line in the east coast (Fig
1). Visual identification of sponges was performed based on the
general shape, texture and colour of the described new species. Ecological
information from these surveys is presented in the taxonomic description
section.
Antibacterial experiments
Details about the extraction methods of the chemicals from the studied sponges,
the bacterial strains that were used (17 bacteria species), and the methodology
used to identify the antibacterial bioactivity of the studied species are
provided in the supporting information (S1 File). Methods and procedures based in
references [23,26,41].
Chalinula qatari sp. nov., morphology, skeleton and
spiculation.
Morphology: Living specimens (A) attached to mangrove pneumatophores in
the riparian zone, (B, C) in the intertidal zone, (D) under limestone in
the channels between the mangroves. Skeleton and spicules: (E)
choanosomal skeleton; (F) embryos; (G) ascending spicule tracts; (H)
oxeas, showing immature thinner forms; (I) choanosomal skeleton showing
thickness of encrustation on a mangrove root; (J) embryo; (K) Cross
section of ectosome (specialised ectosomal skeleton absent); (L)
choanosomal skeleton showing length of secondary spicule tracts; (M)
close up of ascending primary spicule tract. Electronic microscopy of
(N) large, thick oxea (O) thinner oxea.
Chalinula qatari sp. nov., morphology, skeleton and
spiculation.
Morphology: Living specimens (A) attached to mangrove pneumatophores in
the riparian zone, (B, C) in the intertidal zone, (D) under limestone in
the channels between the mangroves. Skeleton and spicules: (E)
choanosomal skeleton; (F) embryos; (G) ascending spicule tracts; (H)
oxeas, showing immature thinner forms; (I) choanosomal skeleton showing
thickness of encrustation on a mangrove root; (J) embryo; (K) Cross
section of ectosome (specialised ectosomal skeleton absent); (L)
choanosomal skeleton showing length of secondary spicule tracts; (M)
close up of ascending primary spicule tract. Electronic microscopy of
(N) large, thick oxea (O) thinner oxea.
Material examined
Holotype. NHMUK 2020.3.26.1 (ESC-QU00674) Al-Khor, Qatar,
Arabian-Persian Gulf, 25.69502778, 51.54694444, 0.3 m, collected from
pneumatophores in tidal-channels, May 2018. Paratypes. NHMUK
2020.3.26.2 (ESC-QU00420), Al-Dhakira, Qatar, Arabian-Persian Gulf,
25.749228, 51.539267, intertidal zone collected encrusting pneumatophores
June 2015, 1 specimen; ESC-QU01327, Al-Dhakira, Qatar Arabian-Persian Gulf,
25.749228, 51.539267 (<1 m), collected encrusting pneumatophores, Feb
2019, 3 specimens.
Morphology
A thinly encrusting sponge with a thickness of around 4 mm (Fig 2I) and a maximum
observed diameter of 40 cm. Oscular chimneys were present on some specimens.
These had the form of small cones around 6 mm in diameter with an elevation
of around 8 mm. Oscules were 2–5 mm in diameter. Oscular chimneys were
observed mainly in the specimens in the mangrove roots (Fig 2A–2D).
Surface
Surface uneven.
Consistency
Compressible, very soft and fragile, easily damaged.
Colour
Most living specimens are a vivid maroon colour (Fig 2A, 2B and 2D). However, those living
in stressful situations, such as intertidal specimens in summer conditions,
may bleach to a pale yellow (Fig 2C). In alcohol specimens are pale yellow.
Skeleton
The choanosomal skeleton is an anisotropic reticulation with paucispicular
primary tracts, 1–3 spicules in diameter (Fig 2G, 2L and 2M). The secondary tracts
are unispicular (Fig
2L), usually about two spicules long (Fig 2L). There is no ectosomal skeleton
(Fig 2K), the ends
of the primary tracts of the choanosome project beyond the surface,
rendering it slightly hispid.
Spicules
Oxeas, 69.2 (80.5) 96.2 μm length by 1.1 (2.5) 4.0 μm width, n = 25 (Fig 2H, 2M and 2N). Mature
fusiform oxeas with 83 (86.4) 96.2 μm length by 3.0 (3.4) 4.0 μm width
(Fig 2H and 2N);
while young spicules commonly observed were shorter, thinner, and more
sharply pointed with 69.2 (74.1) 77.8 μm length by 1.1 (1.4) 1.9 μm width
(Fig 2H and 2O). No
microscleres.
Ecology
Found growing on the pneumatophores of mangrove Avicennia
marina (Forssk.) Vierh., in the intertidal and subtidal zones
along tidal channels (Fig
2A–2C), and on the underside of limestone rocks in tidal channels
(Fig 2D). Also found
in seagrass and algal beds connected directly with the mangrove habitat.
Etymology
Named for the general type locality, Qatar, and the colouration, which is
similar to that of the Qatari flag.
Distribution
Currently only known from the holotype and paratype localities in the
mangroves at Al-Dhakira and Al-khor, planted mangrove in the Al-Wakrah in
the south of Doha, and in the mangroves at Shamal in the north-east of
Qatar. All locations are on the east coast of Qatar, south-western coast of
the Arabian/Persian Gulf.
Antibacterial Bioactivity
Extracts from Chalinula qatari
sp. nov. did not show any antibacterial bioactivity against the
test pathogens.
Remarks
No significant differences in skeletal morphology or spiculation were
observed between the paratypes. The proportion of smaller young oxeas did
vary amongst the paratypes; with each specimens presenting a different ratio
of large and thin spicules. Embryos with young spicules were visible in some
individuals (Fig 2F and
2J) these were always concentrated in the basal layer (Fig 2E).The possession of an isodictyal skeleton of diactinal megascleres, and a
regular anisotropic reticulation with recognisable ascending primary tracts,
places this species in Order Haplosclerida Topsent, 1928, Sub-order
Haplosclerina Topsent, 1928. The presence of a choanosomal skeleton with
unispicular secondary lines assigns this species to Family Chalinidae Gray,
1867. Within the Chalinidae we assign this species to genus
Chalinula on the basis that the secondary tracts of the
choanosomal skeleton are mostly two spicules long and multispicular fibre
tracts are not present throughout the sponge [42].Chalinula has 25 currently accepted species worldwide [42], none of which have
been recorded in the PAG. Three species occur in related biogeographic
areas: Chalinula camerata (Ridley, 1884) from the Indian
Ocean and Red Sea, Chalinula confusa (Dendy, 1922) from the
Seychelles, and Chalinula saudiensis Vacelet, Al Sofyani,
Al Lihaibi & Kornprobst, 2001 from the Red Sea [43-45]. In addition to the
Chalinula species, since the taxonomy of this family is
confused, we considered species from closely related genera.
Haliclona (Reniera) debilis Pulitzer-Finali, 1993,
which has similar colour and also occurs in mangroves, is known from the
north-west Indian Ocean [46,47]. A
comparison of these four species with the new C.
qatari
sp. nov. is presented in Table 1. The main characteristics that
differentiate Chalinula qatari
sp. nov. from those congeners are the colour in life (maroon),
the presence and sizes of the oscular chimneys, the encrusting thickness,
the size of the spicules (oxeas) and the habitat preferences, dwelling in
the intertidal and shallow subtidal zones at hypersaline mangroves.
Table 1
Taxonomic comparisons of the new species Chalinula
qatari sp. nov. with target congener from family
Chalinidae.
Chalinula qatari sp.
nov.
C.
saudiensis
C.
camerata
C.
confusa
Haliclona (Reniera)
debilis
Vacelet et al., 2001
(Ridley, 1884)
(Dendy, 1922)
Pulitzer-Finali, 1993
ECOLOGY
ecosystem
Mangrove
Black Coral Reef
Seagrass (Halimeda) adjacent to
mangroves
Depth/zone
Mid to low Intertidal/shallow
subtidal
20–30 m
Upper eulittoral
substratum
Living
substrate (mangrove roots); and limestones
dead coral
heads
Muddy
sand
MORPHOLOGY
Colour
Maroon,
Blue
Pale brown–soft leather
Dark brown
Bright pinkish purple
Thickness (mm)
encrusting (4)
encrusting (10–20)
Subcylindrical Lamellae (1–2)
Erect, branched
Coalescing tubes
Projections
Oscular chimneys sometimes present (8 mm
high; 6 mm width).
none
Longitudinal series of vents
Coalescing tubes 30 mm high; 5mm
wide
Oscules
(mm) diameter
2–5
2–6
SKELETON
Choanosomal Primary Tracs
anisotropic reticulation;
paucispicular
Reticulation; paucispicular
Polispicular
paucispicular
Secondary tracts
unispicular generally two spicules
long
unispicular generally two spicules
long
multispicular
unispicular
Ectosomal skeleton
absent
absent
Present
absent
SPICULES
Type
oxeas
oxeas
oxeas
oxeas
Length (μm)
83(86.4)96.2 mature; 69.2(74.1)77.8
young
110–181 mature; 60 young
180
150 mature
70–85
Width
3.0(3.4)4.0 mature; 1.1(1.4)1.9
young
1.5–4.5 mm mature; 0.5young
7
6 mature
3–4.5
Order Suberitida Chombard & Boury-Esnault, 1999Family Suberitidae Schmidt, 1870Genus Suberites Nardo, 1833Suberites luna Giraldes & Goodwin 2020 sp.
nov.urn:lsid:zoobank.org:act:174C5AD0-3132-4D07-A172-2014A77CBDC8Fig 3
Fig 3
Suberites luna
sp. nov., morphology, skeleton and spiculation: (A, B)
growing on mangrove pneumatophores in the riparian zone; (C) just
collected and cut; (D) large compound oscule; (E) large specimens
close to seagrass; (F) specimen just collected. Slides of fresh
specimens, (G) cross section of choanosomal skeleton; (H) plumose
choanosomal skeleton in cross section, (I) palisade of subtylostyles
in the ectosome. Slide in cross section of dried specimen showing
plumose choanosomal skeleton (J). Electronic Microscopy, (K, L, M)
showing different head shapes of the subtylostyles; (N) the
subtylostyles types (I), (II) and (III).
Suberites luna
sp. nov., morphology, skeleton and spiculation: (A, B)
growing on mangrove pneumatophores in the riparian zone; (C) just
collected and cut; (D) large compound oscule; (E) large specimens
close to seagrass; (F) specimen just collected. Slides of fresh
specimens, (G) cross section of choanosomal skeleton; (H) plumose
choanosomal skeleton in cross section, (I) palisade of subtylostyles
in the ectosome. Slide in cross section of dried specimen showing
plumose choanosomal skeleton (J). Electronic Microscopy, (K, L, M)
showing different head shapes of the subtylostyles; (N) the
subtylostyles types (I), (II) and (III).Holotype. NHMUK 2020.3.26.3 (ESC-QU0067) Al-Khor, Qatar,
Arabian-Persian Gulf, 25.69502778, 51.54694444, <1 m collected from
pneumatophores in tidal channels bordering hyperarid mangroves, May 2018;
Paratypes. NHMUK 2020.3.26.4 (ESC-QU 00419) Al-Khor, Qatar,
Arabian-Persian Gulf, 25.749228, 51.539267, 1.5 m, collected from rock/sand
substrate in the hyperarid mangrove bay, June.2015, 1 specimen; ESC-QU
01432, ESC-QU 01436 and ESC-QU 01437, Al-Dhakira Qatar, Arabian-Persian
Gulf, 25.749228, 51.539267, 1–2 m, collected from shells, soft rock on sand
substrate in the seagrass peripheral to the hyperarid mangrove, May 2018, 3
specimens.Massive globular-lobate sponge (Fig 3A–3F), with some large specimens 20–60 cm diameter and
10–20 cm high. The sponge exterior is dense and compact. The interior
choanosomal tissue has many pores and is cavernous. Oscules are infrequent,
the largest observed was around 8 mm in diameter (Fig 3D) and was on the apex of a
lobe.Velvety surface with macroscopically smooth appearance (Fig 3A–3F).Compact, firm, slightly compressible and elastic; hard to tear. A slime is
produced when torn.Live colour is greenish-black and internally a yellowish orange (Fig 3A–3F). When preserved
in alcohol the tissue becomes grey.Plumose skeleton with ascending tracts of large subtylostyles, 10 to 50
spicules wide (Fig 3J and
3H). Ectosomal skeleton formed of a palisade of smaller
subtylostyles (Fig
3I).
Spiculation
Subtylostyles, 10 (491) 843 μm by 2.9 (6.4) 13.1 μm (n = 234) (Fig 3N). A multimodal
pattern of spicule length was observed (Fig 4), with three main sizes of
tylostyles (subtylostyles): (I) smaller spicules with 110 (174) 196 by 2.9
(4.2) 5.9 μm, most likely ectosomal in distribution; (II) robust
subtylostyles with 400–500 by 5 (7.8)13.1 μm width, found in the
sub-ectosomal choanosomal skeleton; (III) long subtylostyles, >600 μm
length by 5.6 (6.6)10.4 μm (Fig
3N), part of the deep choanosomal skeleton forming the ascending
tracts in the plumose skeleton.
Fig 4
Histogram of subtylostyle length (n = 234, showing three
potential size categories. I-III.
Found on hard substrates in mangrove and seagrass habitats in the subtidal
zone. Observed on the pneumatophores of Avicennia marina in
the channels of the riparian zone of the arid mangrove ecosystems (Fig 3A). Several times
this species was found close to Chalinula qatari
sp. nov. Very abundant with large specimens (more than 50 cm
diameter) in the subtidal zone around the mangroves (Fig 3E) and at the edges of the seagrass
habitat. Found in soft sediment, but mostly attached to small pieces of hard
substrate within the sediment, such as small soft-rocks and shells. There
was a higher abundance of this species at sites with low current.This species was nicknamed the ‘moon-surface sponge’ by the collectors due to
its appearance. The name reflects both this and the importance of the moon
in the Muslim culture.Recorded from mangrove ecosystems on the east coast of Qatar from Shamal to
Al-Wakrah, south-western coast of the Arabian/Persian Gulf.
Antibacterial bioactivity
Fractions A and B of Suberites luna
sp. nov. showed antibiotic activity against three species of
bacteria (Staphylococcus epidermidis,
Staphylococcus aureus, Enterococcus
faecalis), 17% of those tested (Fig 5). Fractions D and E (see S1
File) were effective against only 6% (Enterococcus
faecalis) of the bacteria tested in this study (Fig 5A and 5B). Fraction C
(S1
File) showed no antibacterial activity against any of the
bacterial strains.
Fig 5
Bioactivity experiment with Suberites luna sp.
nov..
(A) zone of inhibition (highlighted in red) over three species of
bacteria; (F) and the chart highlighting the zone of inhibition.
Bioactivity experiment with Suberites luna sp.
nov..
(A) zone of inhibition (highlighted in red) over three species of
bacteria; (F) and the chart highlighting the zone of inhibition.Significant differences in skeleton and spiculation of the paratypes was not
observed. However, there was some variation in external form with some
specimens being much larger and more lobate than others (Fig 3E). This species is
included within the Family Suberitidae Schmidt, 1870 and Genus
Suberites Nardo, 1833 due to its massively
globular-lobate shape, possession of a spicule complement consisting only of
tylostyles, and the presence of an ectosomal palisade formed of bouquets of
smaller tylostyles than those of the choanosome [48]. Genus Suberites
has 80 species worldwide [48-50]
but only a few congeners have been previously recorded in the Indian Ocean
and Red Sea [37,50-53]. These are
S. bengalensis Lévi, 1964 recorded
from India (1190 m depth) (see [49]; S.
clavatus Keller, 1891 and S.
tylobtusus Lévi, 1958 from the Red Sea;
S. radiatus Kieschnick, 1896 from
Indonesia [50]; and
S. diversicolor Becking & Lim,
2009 from Singapore, Indonesia, Vietnam, Australia [49] and more recently recorded from the
East of PEG [54]. A
sixth species Suberitescarnosus (Johnston, 1842) was
previously recorded from the Indian Ocean, more specifically from the
Seychelles and Minicoy Islands and the coast of India (Mumbai) [55-57]. However,
S. carnosus and all the variations
within this species complex including var.
depressus, var.
incrustans, var.
novaezealandiae and var.
ramosus are not now considered to inhabit any marine
province in the Indian Ocean [50] and therefore this species and its
variants were discarded from this comparison. A comparison with the
aforementioned biogeographically related species is presented in Table 2. Based in the
spicules size and types, the main divergent characteristic that
differentiate those species and one of the only descriptions recorded for
all congeners.
Table 2
Taxonomic comparisons of the new species Suberites
luna sp. nov with target congener from family
Suberitidae.
We could not compare Suberites radiatus because, as noted by
Becking and Sim [49],
the original description is extremely brief and vague and the type specimen
seems to have been lost. Some biogeographically related species mentioned in
the Table 2 also
differ from Suberites luna
sp. nov. in terms of morphology and habitat preferences.
Suberites bengalensis is a deep-sea species recorded
from 1190 m [49];
S. tylobtusus, when living, is a
bright orange colour [50]. Suberites diversicolor has spicules of a
similar size range to S. luna. However, it
has a more uniform distribution of spicules across this size range whereas
there is a gap in size of around 200 μm between the smallest category of
(ectosomal) spicules of our specimens and those found in the larger two
categories (choanosomal). Suberites diversicolor is also
much more variable in colour, ranging from purple-brown and olive green to
red-orange, where our specimens are always greenish-black. In addition, the
holotype locality of S. diversicolor is an
anchialine lake, the other areas it has been recorded from (Indonesian
coastal mangroves, Singapore, lake systems in Vietnam, and a man-made pool
in Darwin northern Australia) also had low salinities, and it seems to be
restricted to areas with salinities between 26 and 29 psu [49]. Suberites
luna
sp. nov. was recorded from shallow coastal waters with
salinities from 42 to >60 psu and water temperatures reaching 36°C.
Studies have demonstrated that different sponge species inhabit waters of
differing salinities [58] and lethal effects was recorded when exposing some sponge
species to elevated temperatures [59]. We argue that S.
diversicolor would be unlikely to be found in the
conditions found in the PAG. Although S.
diversicolor was reported from the PAG from Bushehr,
Iran [54], we believe
these records need to be revisited. It has been noted that even in the type
locality S. diversicolor may represent a
species complex [60].Summarizing, the main characteristics that differentiate Suberites
luna
sp. nov. from the related congeners are the internal (yellow)
and external (dark olive) colour in life, the massive globular-lobate shape,
the spicule size range and number of spicule categories (Table 2) and the habitat
preference, dwelling in the subtidal zone in a hypersaline mangrove
ecosystem.
Discussion
The discovery of Suberites luna
sp. nov. and Chalinula qatari
sp. nov. on mangroves on the west coast of the PAG highlights the lack
of taxonomic study of sponge species in the Gulf but also the biogeographic
isolation of the studied hyperarid mangrove habitats. These two species new to
science, together with the other endemic species that have been found in this
habitat [15] support the
concept that the west coast of PAG is an isolated marine province. Theoretically,
the intense hyperarid conditions found in the west coast of PAG create a
biogeographic barrier that isolates an endemic biodiversity adapted to the intense
temperature and salinity conditions [1,3]. The deeper
waters and constant water input from the Indian Ocean result in less extreme arid
conditions on the eastern coast of the PAG, and this area shares several species
with tropical Indian Ocean areas (e.g. gastropods and decapods) [12,13]. The high temperatures and salinities found
on the western PAG coast might kill non adapted sponge species, as was demonstrated
for tropical sponge species reaching 33°C [59], preventing colonisation by sponges from
neighbouring provinces. Recent studies on the biodiversity of bioturbating crabs
[61], based in the same
arid mangrove setting, support the theory that the southwest coast of PAG is an
isolated marine province. A mangrove setting in an isolated marine province that
houses an abundant endemic shrimp Palaemon khori De Grave &
Al-Maslamani, 2006 [7,15] that occurs only in this
mangrove setting in Qatar and remains absent in the entire Arabian Gulf [62] (BWG pers. Observ.). It is
possible the two new sponge species are also endemic to this mangrove setting in the
type locality. If they are it would bring the number of endemic species known to
three. This highlights the conservation importance of this forest ecosystem in a
desert region. Further study of the western PAG sponge fauna is needed to fully
understand its biodiversity and biogeographic affinities with neighbouring
regions.Suberites luna
sp. nov. exhibited antibacterial activity against three common
pathogenic gram-positive bacterial species, Staphylococcus aureus,
S. epidermidis and Enterococcus
faecalis. Although this is a preliminary study it highlights the
potential of the toxins produced by Suberites luna
sp. nov. for the development of a new antibacterial drug, including
drugs for resistant bacteria. Future studies are required to chemically isolate the
toxin of Suberites luna
sp. nov. and evaluate its uses in treatment of bacteraemia and other
bacterial infections. Despite the negative antibiotic effect of Chalinula
qatari
sp. nov. the fact other studies on the family Chalinidae have found
metabolites indicate that it might merit future research. The sulphated sterolChalinulasterol, has been isolated from the family Chalinidae
[63]. Additionally, a
unidentified species from family Chalinidae recorded in the PAG presented antifungal
and antibacterial activity [64]. These results highlight the importance of increasing the effort in
taxonomic study and study of the metabolites of the marine species of the west coast
of the PAG.
Antibacterial studies on extracts from Chalinula qatari
sp. nov. and Suberites luna sp. nov.
Authors: Dirk Erpenbeck; Oliver Voigt; Ali M Al-Aidaroos; Michael L Berumen; Gabriele Büttner; Daniela Catania; Adel Naguib Guirguis; Gustav Paulay; Simone Schätzle; Gert Wörheide Journal: Mar Pollut Bull Date: 2016-01-07 Impact factor: 5.553
Authors: M Nazemi; M Alidoust Salimi; P Alidoust Salimi; A Motallebi; S Tamadoni Jahromi; O Ahmadzadeh Journal: J Mycol Med Date: 2014-06-13 Impact factor: 2.391
Authors: Rob W M Van Soest; Nicole Boury-Esnault; Jean Vacelet; Martin Dohrmann; Dirk Erpenbeck; Nicole J De Voogd; Nadiezhda Santodomingo; Bart Vanhoorne; Michelle Kelly; John N A Hooper Journal: PLoS One Date: 2012-04-27 Impact factor: 3.240
Authors: Sergey A Dyshlovoy; Sergey N Fedorov; Larisa K Shubina; Alexandra S Kuzmich; Carsten Bokemeyer; Gunhild Keller-von Amsberg; Friedemann Honecker Journal: Biomed Res Int Date: 2014-07-23 Impact factor: 3.411
Authors: Sonia Boughattas; Dana Albatesh; Albandari Al-Khater; Bruno W Giraldes; Asma A Althani; Fatiha M Benslimane Journal: Ecol Evol Date: 2021-12-07 Impact factor: 2.912