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Checklist of Nematodes (Nematoda: Adenophorea) from Southeast Continental Shelf of India

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A checklist of free-living marine nematode species recorded from the continental shelf region of southeast coast of India is presented (10°34.03’ to 15°14.48’ N and from 79°52.13’ to 80°53.87’E). The checklist comprise 191 species belonging to 97 genera in 32 families currently know from the area. We provided a synthesis of the taxonomical and ecological work carried out until now that could guide to future research
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Journal of species lists and distribution
Chec List
414
Lists o f species
Check List 8(3): 414-420, 2012
© 2012 Check List and Authors
ISSN 1809-127X (available at www.checklist.org.br)
nematofaunal studies done in the Indian subcontinent
covered mostly the Western continental shelf (Harkantra
et al. 1980; Sajan et al. 2010) and shallow coastal waters
(Timm, 1961; 1967; Ansari et al. 1980) and no information
is available on the distribution and species level
composition of nematodes in the Southeast coast of India.
Therefore the present investigation was undertaken on the
meiobenthos especially on nematodes in the continental
shelf of the Southeast coast of India.

Study site
The study area extends from 10°34.03’ to 15°14.48’
N and from 79°52.13’ to 80°53.87’E in the continental
shelf region of the Southeast coast of India (Figure 1).
Totally 35 sediment samples were collected along 6
transects (off Karaikkal, Parangipettai, Cheyyur, Chennai,
Tammenapatanam and Singarayakonda) at the depths of
30-50m, 50-75m, 75-100m, 100-150m, 150-175m and
above 175m. In addition one more transect was sampled,
due to the presence of an industrial cluster in Cuddalore-
SIPCOT (State Industries Promotion Corporation of Tamil
Nadu), at 30-50m and above 175m depths. In these
industrial cluster units mainly produced PVC pipes, paints,
pharmaceutical products and fertilizers. These industries
play a major role in this region and the industrial units
      
The study area map was drawn with the help of SURFER
8.0.
Data collection
Meiofaunal samples for the present study were
collected onboard FORV (Fishery and Oceanographic
Research Vessel) “Sagar Sampada” during Cruise No.
260 under the program of “Marine Benthos of Indian
EEZ” founded by Centre for Marine Living Resources and
Ecology (CMLRE), Ministry of Earth Sciences (MoES),
Government of India. Two samples were collected using a

Sedimentary habitats cover most of the ocean bottom
and therefore constitute the largest single ecosystem on
earth in spatial coverage (Schratzberger et al. 2007).
Benthic organisms which occupy these habitats make
       
nitrogen and sulphur cycling, water column process,
pollutant distribution and fate, secondary production and
transport and stability of sediments (Snelgrove et al. 1997).
     
earth are nematodes (Bongers and Ferries 1999). Free
living marine nematodes are usually the most abundant
metazoans inhabiting marine benthic ecosystems, often
representing more than 60-90% of the benthic meiofauna
(Sajan et al. 2010).

chain through way of degradation and mineralization of
organic matter is high. Nematodes have short life span,
high fecundity (Vranken and Heip 1983), represent several
tropic levels (herbivores, bacterial feeders and carnivores)
and at least some species can be easily cultured (Heip et al.
1985). By virtue of their wide range of adaptations, marine
nematodes have exploited all seashores and seabed
habitats. An important feature of nematode population is
the large number of species present in any habitat, often
an order of magnitude higher than for any other taxon
(Platt and Warwick 1980).
Whereas the importance of parasitic nematodes has
been recognised for many decades, this is not the case for
free-living marine nematode species, especially those of
aquatic environments. They remain poorly understood,
despite the fact that they are extremely abundant and
diverse, often numbering millions per square meter in
sediments, and occur in more habitats than any other
metazoan group (Heip et al. 1985). While few studies
have been carried out on nematodes in and around the
Indian waters, nematode communities of the Indian shelf
sediments received cursory attention. More over the
 A checklist of free-living marine nematode species recorded from the continental shelf region of southeast
coast of India is presented (10°34.03’ to 15°14.48’ N and from 79°52.13’ to 80°53.87’E). The checklist comprise 191 species
belonging to 97 genera in 32 families currently know from the area. We provided a synthesis of the taxonomical and
ecological work carried out until now that could guide to future research
Annamalai University, Faculty of marine Sciences, Centre of Advanced Study in Marine biology. Parangipettai – 608 502, Tamil Nadu, India.
* Corresponding author. E-mail: casthameem@gmail.com
Kapuli Gani Mohamed Thameemul Ansari*, Seerangan Manokaran, Sanjeevi Raja, Syed Ajmal Khan
and Somasundharanair Lyla
Checklist of Nematodes (Nematoda: Adenophorea) from
Southeast Continental Shelf of India
415
Ansari et al. | Nematodes from Southeast Continental Shelf of India
 1. Depths sampled at various transects of southeast continental
shelf of India.
Smith McIntyre grab (having a bite area of 0.2 m2) from
each depth. Immediately after the grab was hauled to the
deck and sub-samples were taken from undisturbed grab
samples using a glass corer (with an internal diameter
of 2.5 cm and a length of 15 cm) from the middle of grab
sample 
in buffered formalin at a concentration of 4%. The replicate
core samples were processed separately in the laboratory
and data were pooled for analyses.
Sample processing
In the laboratory, samples were washed through a set
of 0.5 mm and 0.063 mm sieves. The sediment retained
in the 0.063 mm sieve was decanted to extract meiofauna
following the method (Higgins and Thiel, 1988). Sorting of

 followed by
Armenteros et al. (2008). The meiofaunal organisms were
stained with Rose Bengal prior to extraction and were
sorted and enumerated under a stereomicroscope (Meiji,
Japan). All the nematodes were mounted onto glass slides,
using the formalin-ethanol-glycerol technique by Vincx
       
the highest taxonomic level possible using the compound
      
of 1000x) following the standard pictorial keys of Platt
and Warwick (1983; 1988), Warwick et al. (1998) and the
NeMys Database (Steyaert et al. 2005).
The collected specimens is currently deposited in
CMLRE (Centre for Marine Living Resource and Ecology),
MoES (Ministry of Earth Sciences), Government of India,
whose available voucher numbers are provided (Table 1).
These lists could be found in “Achievements of FORV Sagar
Sampada 1997-2010” published in National Symposium
entitled “Indian Ocean Marine Living Resources
(IndoMLR)”, held at CMLRE, Kochi, India 2010.

A total of 4218 individuals were collected and 191
species belonging to 97 genera and 32 families were

from the Western continental shelf of India (Sajan et al.
2010). In the present study, the abundance (mean ± SE)
of nematodes decreased with increase in depth. The
maximum abundance of 207.7±19.19 no. of ind. /10cm2
was noticed in 30-50m depth and the minimum in >175m
depth (34.6±6.66 no. of ind. /10cm2). Highest number
of species was recorded in 30-50m depth (151 species)
followed by 100-150m depth (120 species), 75-100m
depth(100 species), 50-75m depth (95 species) , 150-
175m depth (80 species) and >175m depth(58 species)
(Table 1). As observed in the present study, decline in
abundance, number of species and families with increase
in depth was reported (Ansari et al. 1980; Parulekar et al.
1982; Muthumbi et al. 2004; Sajan and Damodaran 2007;
Sajan et al. 2010) in the Indian shelf sediments and (De
Bovee et al. 1990; Tietjen 1992; Soltwedel 2000; Liu et al.
2007; De Leonardis et al. 2008; Armenteros et al. 2009)
from other parts of the world. Transect-wise variation was
less distinct in the faunal composition. However, such a
variation was noticed in the abundance of nematodes in
the entire shelf (Sajan et al. 2010).
Seventeen families such as Anoplostomatidae,
Oxystominidae, Oncholaimidae, Trefusiidae,
Chromadoridae, Comesomatidae, Cyatholaimidae,
Desmodoridae, Microlaimidae, Leptolaimidae,
Ceramonematidae, Desmoscolecidae, Monhysteridae,
Xyalidae, Sphaerolaimidae, Linhomidae and
Axonolaimidae were found in the entire study area. Some
       
and Epsilonematidae were restricted only in 30-50m
depth range, Meyliidae in 50-75m depth and Enoplidae in
75- 100m depth. Totally 29 out of 32 nematode families
were recorded in 30-50m depth followed by 27 families
in 50-75m and 100-150m depths. While behind 100m
depth all the 32 nematode families were found and
beyond 100m depth 28 families were recorded. However
Enoplidae, Enchelidiidae, Epsilonematidae and Meyliidae
were not recorded. At the edge of the shelf (beyond 175m)
only 18 families were recorded. Ironidae, Leptosomatidae
and Draconematidae were present in all the depth ranges
except > 175m depth (Table 1). Similar results were
reported by Sajan and Damodaran (2007) in Western
continental shelf of India.
The present study most of the free-living marine

that lack of literature. The generic composition in the
southeast continental shelf of India showed the presence
of all the depths genera like Anoplostoma, Halalaimus,
Oxystomina, Viscosia, Dorylaimopsis, Sabatieria,
Paralongicyatholaimus, Tricoma, Thalassomonhystera,
Daptonema, Terschellingia and Odontophora (Table 1) as
found in various shelf sediments (Vanreusel et al. 1992;
Soetaert and Heip 1995; Muthumbi et al. 2004; Sajan and
Damodaran 2007; Sajan et al. 2010). In the importance
of industrial cluster transect (Cuddalore SIPCOT),
nematode species like Mesocanthion sp., Neochromadora
416
Ansari et al. | Nematodes from Southeast Continental Shelf of India
 1. List of species collected at seven transects and each in six depths (1 – 30-50m, 2 = 50-75m, 3= 75-100m, 4 = 100-150m, 5 = 150- 175m and 6
= > 175m) along the continental shelf region of the southeast coast of India (x – present, - absent).
sp. and Epsilonema pustulatum were recorded only in this
transect. Genus Neochromadora was noticed as indicators
for oil pollution and heavy metal contamination (Platt
and Warwick 1988). There is no information regarding
list of free-living marine nematode species, distribution,
diversity and pollution aspect studies in the southeast
continental shelf of India. Therefore, the present study
data is valuable for further ecological, qualitative and
quantitative research on free-living marine nematodes in
this region.
 CMLRE NUMBER 1 2 3 4 5 6

Enoplus sp. - - - x - - -

Enoplolaimus longicaudatus (Southern, 1914) CMLRE 4/061 - - - - x -
Mesacanthion sp. - x - - - - -
Paramesacanthion sp. CMLRE 4/068 x x - x - -
Thoracostomopsis sp. - - - - x - -

Anoplostoma viviparam (Bastian, 1865) - x x x x x x
Anoplostoma sp. - x x x x x x

Anticoma eberthi Bastian, 1865 CMLRE 4/006 - - - x - -
Anticoma sp. - x x x x - -

Dolicholaimus sp. - x - - x - -
Syringolaimus sp. - x x x x x -

Leptosomatum sp. - x - x - - -
Platycoma sp. - x x - x - -
Thoracostoma sp. - x - - - x -

Halalaimus capitulates Boucher, 1977 - x - - - - -
Halalaimus gracilis De man, 1888 - x x x x x x
Halalaimus longicaudatus (Filipjev, 1927) - x x x x x x
Halalaimus sp. - x x x x x x
Nemanema sp. - - x - - - x
Oxystomina elongata (Butschili, 1874) - x x x x x x
Oxystomina sp. CMLRE 4/060 x x x x x x

Metoncholaimus scanicus (Allgen, 1935) CMLRE 4/039 and 4/78 x - - - - -
Oncholaimellus calvadosicus De Man, 1890 CMLRE 4/057 - - - x - -
Oncholaimellus sp. - - x - x x x
Viscosia abyssorum (Allgen, 1933) - x - - - - -
Viscosia elegans (Kreis, 1924) - x x x x x x
Viscosia glabra (Bastian, 1865) CMLRE 4/038 x - x x x -
Viscosia langrunensis (De Man, 1890) CMLRE 4/037 x x x x x x
Viscosia viscosa (Bastian, 1865) - x x x x x x
Viscosia sp. - x x x x x x

Belbolla sp. CMLRE 4/076 x - - - - -
Pareurystomina sp. CMLRE 4/058 x x - x x -

Tripyloides marinus (Butschli, 1874) - x - - x - -
Tripyloides sp. CMLRE 4/059 x - - - - -

Halanonchus sp. - x x x x x x
Trefusia longicaudata De Man, 1893 - x x x x - -
Trefusia sp.1 - x x x x - -
Trefusia sp.2 - x x - x - -

Chromadora sp. - x x x - - -
Chromadorina granulopigmentata (Weiser, 1951) CMLRE 4/013 x x - x - -
Neochromadora poecilosomoides (Filipjev, 1918) CMLRE 4/079 x - - - - -
417
Ansari et al. | Nematodes from Southeast Continental Shelf of India
 CMLRE NUMBER 1 2 3 4 5 6
Prochromadorella sp. - - - - - - x
Siplophorella sp. - x x x x x x

Comesoma sp. - x x - - - -
Dorylaimopsis punctata Ditlevsen, 1918 - x x x x x -
Dorylaimopsis sp. - x x x x x x
Laimella sp. - - - - x - x
Metacomesoma sp. - x - - - - -
Paracomesoma dubuim (Filipjev, 1918) - - - x - - -
Paracomesoma sp. CMLRE 4/066 x x - x x x
Sabatieria breviseta Stekhoven, 1935 - x x x x x -
Sabatieria celtica Southern, 1914 CMLRE 4/030 x x x x - -
Sabatieria longisetosa (Kries, 1929) - x - x - x -
Sabatieria ornata (Ditlevsen, 1918) - x x x - x -
Sabatieria praedatrix De Man, 1907 CMLRE 4/031 x x - x - x
Sabatieria pulchra (Schneider, 1906) CMLRE 4/032 x x x x x x
Sabatieria punctata (Kreis, 1924) CMLRE 4/033 x x x x x -
Sabatieria sp.1 - x x x x x x
Sabatieria sp.2 - x x x x - -

Comesa cuanensis (Platt, 1982) CMLRE 4/017 x x - - - -
Paraethmolaimus sp. - x - - - - -

Cyatholaimus sp. CMLRE 4/065 x - - x - -
Longicyatholaimus sp. - x x x x - x
Metacyatholaimus sp. - - - - x - -
Paracanthonchus longicaudatus Warwick, 1971 CMLRE 4/072 x - - x - -
Paracanthonchus platti Vadhyar, 1980 - - x - - - -
Paracanthonchus sp. - x - - x x x
Paracyatholaimus sp. CMLRE 4/071 - - x x - -
Paralongicyatholaimus minutus Warwick, 1971 - x x x x x x
Paralongicyatholaimus sp. CMLRE 4/040 x x x x x x
Pomponema sp. - x x - x - -

Cheironchus sp. - x - - - - -
Gammanema sp. - x - - - - -
Halichoanolaimus robustus (Bastian, 1865) - - - - x - -
Synonchiella sp. CMLRE 4/069 - x - - - x
Synonchium sp. - - x - - - -

Catanema sp. - - x - - - -
Chromaspirina inglisi Warwick, 1970 CMLRE 4/014 x - - - - -
Chromaspirina parapontica Luc and De Coninck, 1959 CMLRE 4/015 x - - x - -
Chromaspirina sp. - x - x x - -
Desmodora (Desmodora) scaldensis De Man, 1889 - x - x - x -
Desmodora (Desmodora) schulzi Gerlach, 1950 CMLRE 4/025 - - x - x -
Echinodesmadora sp. - x - - x - -
Leptonemella sp. - - - - x - -
Metachromadora (Bradylaimus) suecica (Allgen, 1929) CMLRE 4/056 x - - - - -
Metachromadora (Chromadoropsis) vivipara (De Man, 1907) - x - - - - -
Metachromadora sp.1 - x - x x x -
Metachromadora sp.2 CMLRE 4/055 x x x x x x
Paradesmodora sp. CMLRE 4/047 x x - x x -
Pseudonchus northumbriensis Warwick, 1969 CMLRE 4/053 - x - x - -
Pseudonchus sp. CMLRE 4/052 x x x x - x
Spirinia sp. - x x x x x -

Draconema claparedii (Gerlach, 1952) - x - - - - -
Draconema sp. - - - x - - -

Epsilonema pustulatum (Gerlach, 1952) CMLRE 4/077 x - - - - -
 1. Continued.
418
Ansari et al. | Nematodes from Southeast Continental Shelf of India
 CMLRE NUMBER 1 2 3 4 5 6

Aponema sp. - x x - x - -
Belbolaimus teutonicus Riemann, 1966 - x x - - - -
Belbolaimus sp. CMLRE 4/041 x x - x - -
Calomicrolaimus honestus (De Man, 1922) CMLRE 4/011 - - - x - -
Calomicrolaimus spirifer (Warwick, 1970) - x - x x - -
Calomicrolaimus sp. CMLRE 4/012 x - x x - -
Microlaimus acinaces Warwick and Platt, 1971 - - x - - - -
Microlaimus conothelis (Lorenzen, 1973a) CMLRE 4/027 x - - - - -
Microlaimus robustidens Stekhoven and De Connick, 1933 CMLRE 4/026 x - x x x -
Microlaimus sp.1 - x x x x x x
Microlaimus sp.2 CMLRE 4/028 x x - x - -

Camacolaimus barbatus Warwick, 1970 - x - - - - -
Camacolaimus langicauda De Man, 1922 - x - - x - -
Camacolaimus sp. CMLRE 4/070 x x x x x -
Deontolaimus sp. - - x - - - x
Leptolaimus ampullaceus Warwick, 1970 CMLRE 4/062 x - - - x -
Laptolaimus elegans (Stekhoven and De Coninck, 1933) - x - - x x -
Leptolaimus papillinger De Man, 1876 CMLRE 4/063 x - - - - -
Leptolaimus sp. - x - - x - -
Leptolaimoides sp. - x - - - - -
Stephanolaimus sp. - x - - - - -

Dasynemoides albaensis (Warwick and Platt, 1973) - - - x - - -
Metadasynemoides sp. CMLRE 4/075 x - x x x x
Pselionema longiseta Ward, 1974 - x x - x x -
Pselionema sp.- x x - x x -

Gerlachius sp. - - x - - - -

Desmoscolex falcatus Lorenzen, 1972 - x - - - - -
Desmoscolex sp. - x - x - - -
Quadricoma scanica (Allgen, 1935) - x - - - - -
Tricoma brevirostris (Southern, 1914) - x x x x x x
Tricoma longirostris (Southern, 1914) CMLRE 4/074 x x x x x x
Tricoma sp. - x x x x x x

Southernia sp. - - x x x - -

Diplolaimelloides sp. - x - - - - -
Paramonhystera buetschlii (Bresslau and Stekhoven 1935) - - - x x - x
Paramonhystera riemanni (Platt, 1973) - - - x - - -
Paramonhystera sp.1 - x x x x x x
Paramonhystera sp.2 CMLRE 4/029 - - x x - x
Thalassomonhystera parva (Bastian, 1865) - x - x - x x
Thalassomonhystera venusta (Lorenzen, 1979) - x x x x x x
Thalassomonhystera sp. CMLRE 4/067 x x x x x x

Cobbia trefusiaeformis De Man, 1907 CMLRE 4/016 x - - - - -
Cobbia sp. - - - x - - -
Daptonema biggi (Gerlach, 1965) CMLRE 4/020 - - x - - -
Daptonema hirsutum (Vitiello, 1967) CMLRE 4/018 - - - - x -
Daptonema normandicum (De Man, 1890) CMLRE 4/019 x x x x x x
Daptonema oxycerca (De Man, 1888) - x x x x x -
Daptonema procerum (Gerlach, 1951) - - - x - - -
Daptonema psammoides (Warwick, 1970) CMLRE 4/021 - x x - - -
Daptonema setifer (Gerlach, 1952) - x - - - - -
Daptonema tenuispiculum (Ditlevsen, 1918) CMLRE 4/022 x x x x x x
Daptonema sp.1 - x x x x x x
Daptonema sp.2 CMLRE 4/023 x x x x x x
 1. Continued.
419
Ansari et al. | Nematodes from Southeast Continental Shelf of India
 CMLRE NUMBER 1 2 3 4 5 6
Daptonema sp.3 CMLRE 4/024 - x x x x x
Echinotheristus sp. - - - - x - -
Theristus longus Platt, 1973 CMLRE 4/064 x x x x - -
Theristus ensifer Gerlach, 1951 CMLRE 4/080 x - x - - -
Theristus sp.1 - x x x x - -
Theristus sp.2 - - - x - - -

Sphaerolaimus balticus Schneider, 1906 CMLRE 4/035 - x - x x -
Sphaerolaimus gracilis De man, 1884 CMLRE 4/036 x - - x - -
Sphaerolaimus islandicus Ditlevsen, 1926 - x x x x x x
Sphaerolaimus sp. - x x - - x -

Astomonema southwardorum Austen, Warwick and Ryan, 1993 CMLRE 4/009 x - x x - -
Astomonema sp. - - x x x - -
Siphonolaimus cobbi Riemann, 1966 CMLRE 4/034 - - x x - -
Siphonolaimus sp. - x - - - - -

Eleutherolaimus sp. - x - - - - -
Linhomoeus hirsutus Bastian, 1865 - - - - x - -
Linhomoeus sp.1 - x - x x x -
Linhomoeus sp.2 - x x - - - -
Megadesmolaimus sp. CMLRE 4/054 x - - x - -
 (De Man, 1907) CMLRE 4/042 x x x x x -
Metalinhomoeus longiseta Kreis, 1929 - - x - x x -
Metalinhomoeus sp. - x x x x x x
Paralinhomoeus conicaudatus (Allgen, 1930) CMLRE 4/049 x - x x - x
Paralinhomoeus lepturus (De Man, 1907) - x - x x - -
Paralinhomoeus uniovarium Warwick, 1970 CMLRE 4/048 x - - - - -
Paralinhomoeus sp. - x x x x - x
Terschellingia communis De Man, 1888 - x x x x x x
Terschellingia longicaudata De Man, 1907 - x x x x x x
Terschellingia sp.CMLRE 4/050 x x x x x x

Ascolaimus elongates (Butschli, 1874) - x - - x - -
Ascolaimus sp. CMLRE 4/051 x x x x x x
Axonolaimus paraspinosus Stekhoven and Adam, 1931 CMLRE 4/010 x - - - x -
Axonolaimus sp. - x - - x x -
Odontophora exharena Warwick and Platt, 1973 CMLRE 4/043 x - - x x -
Odontophora longisetosa (Allgen, 1928) CMLRE 4/044 x - x x x x
Odontophora rectangula Lorenzen, 1971 CMLRE 4/045 x - x x x x
Odontophora setosa (Allgen, 1929) - x - x x - -
Odontophora sp.1 CMLRE 4/046 x x x x x x
Odontophora sp.2 - x x x x x x
Parodontophora sp. - - - x - - -

Araeolaimus elegans De Man, 1888 CMLRE 4/007 x x x x - -
Araeolaimus sp.1 - x x x - x -
Araeolaimus sp.2 CMLRE 4/008 x x - x x -
 1. Continued.
 We would like to thank to an anonymous referee
for comments which helped to improve the manuscript.
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: December 2011
: March 2012
: June 2012
: Simone Chinicz Cohen
... Khan et al., 2016;Ansari et al., 2016 references therein). However, previous studies (Ansari et al., 2012a(Ansari et al., , 2012b(Ansari et al., , 2016 provide a detailed account of free-living nematode community structure across BoB shelf region but nematode functional attributes such as trophic diversity, size and biomass spectrum have not been studied. In particular, only limited number of studies globally have investigated ecosystem changes using nematode community with respect to functional attributes such as tropical diversity, body size and individual biomass (e.g. ...
... In the Bay of Bengal (southwest continental shelf), a total of 4235 free-living marine nematode specimens were examined. These specimens were represented by 191 species belonging to 97 genera and 32 families (see Ansari et al., 2012a for species list). The trends in nematode abundance, species richness and individual biomass decreased with increasing depth (see Table 1). ...
Article
Depth and latitudinal patterns of nematode functional attributes were investigated from 35 stations of Bay of Bengal (BoB) continental shelf. We aim to address whether depth and latitudinal variations can modify nematode community structure and their functional attributes (trophic diversity, size and biomass spectra). Global trend of depth and latitudinal related variations have also been noticed from BoB shelf in terms of nematode abundance and species richness, albeit heterogeneity patterns were encountered in functional attributes. Index of trophic diversity values revealed higher trophic diversity across the BoB shelf and suggested variety of food resource availability. However, downstream analysis of trophic status showed depth and latitude specific patterns but not reflected in terms of size and biomass spectrum. The peaks at different positions clearly visualized heterogeneity in distribution patterns for both size and biomass spectrum and also there was evidence of availability of diversified food resources. Nematode biomass spectra (NBS) constructed for nematode communities showed shift in peak biomass values towards lower to moderate size classes particularly in shallower depth but did not get reflected in latitudes. However, Chennai and Parangipettai transects demonstrated shift in peak biomass values towards higher biomass classes explaining the representation of higher nematode abundance. Our findings concluded that depth and latitudes are physical variables; they may not directly affect nematode community structure and functional attributes but they might influence the other factors such as food availability, sediment deposition and settlement rate. Our observations suggest that the local factors (seasonal character) of phytodetrital food flux can be very important for shaping the nematode community structure and success of nematode functional heterogeneity patterns across the Bay of Bengal shelf.
... Most Paralongicyatholaimus species were described for the Continental Shelf of Temperate Northern Atlantic realm, except for P. complicatus from the Coastal Zone in Temperate South America. P. minutus and P. macramphis are the broader distributed, recorded in five (Warwick, 1971b;Boyd et al., 2000;Chinnadurai and Fernando, 2007;Sajan and Damodaran, 2007;Ansari et al., 2012;Lampadariou and Eleftheriou, 2018) and three ecoregions (Lorenzen, 1972;Long and Ross, 1999;Pérez-García et al., 2020), respectively. ...
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Nematoda is a very species-rich phylum that has successfully adapted to almost all types of ecosystems. Despite their abundance and ecological importance, the taxonomic knowledge of nematodes is still limited and the identification of species is not trivial. In Cyatholaimidae, a relatively common and abundant family of free-living nematodes, the identification of organisms is challenging due to the overlap of some generic diagnoses and the absence of updated systematic reviews. Here we systematically reviewed the knowledge about the family diversity, providing a list of valid species, the diagnostic characters to genus level, and the geographical and habitat distribution of species. The review systematized a total of 619 records. The occurrences were classified into biogeographic ecoregions and habitats. Cyatholaimidae includes 211 valid species, classified in 20 genera. The genera can be differentiated based on six diagnostics characters, namely: pattern of cuticle ornamentation; number of longitudinal rows of pore-complex in cuticle; structures of the buccal cavity; presence/absence of pharyngeal bulb; pre-cloacal supplements aspect; and the shape of gubernaculum. Cyatholaimidae includes mainly marine species, mostly occurring in the Coastal Zone. Four and three species were registered in freshwater and terrestrial habitats, respectively, all classified in the genus Paracyatholaimus. About 38% of the valid species occur in more than one type of habitat, under very different environmental conditions, suggesting a broad niche. The occurrence of congeneric species in different habitats types indicates that, throughout the evolutionary history of the family, multiple ecological shift events have occurred. The family occurs worldwide in 74 ecoregions, and the majority of the records and species are in the North Sea and Western Mediterranean. Most species are endemic to one ecoregion, and examples of broadly distributed ones may be a result of misidentifications or cases of long-distance dispersal, especially for those associated with biological substrates.
... In India, studies exploring community composition, diversity or taxonomy of free-living marine nematodes from coastal environments are largely limited. To date, many free-living marine nematode taxa belonging to Order Chromadorida have been reported from coastal benthic domains of this subcontinent (Ansari et al., 2012c). In this chapter, perspectives on the studies undertaken on exploring free-living marine nematode community composition including based on taxonomy are discussed along with updated checklist of taxa reported from the coasts of India. ...
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Molluscs are benthic macro invertebrates and play an important role in the intertidal ecosystem. The present study aimed to assess the distribution of Molluscan fauna in the intertidal regions of North Andaman Island. The intertidal habitat of the study areas mainly composed of rocky, sandy and muddy regions. In this study, we have collected both live and dead shells from all study sites, and 102 species of gastropods and 17 species of bivalves were recorded. Gastropods are commonly occurring in various substrates such as beneath rocks, muddy, sandy, whereas most of bivalves found at soft substratum and as burrowers on coral and rocks. Among seven study sites, the species richness was highest in Kalipur (82 species), followed by Ram Nagar (20 species). High similarity was observed between Durgapur and Ross Island (74%) and lowest between Ram Nagar and Aerial Bay (28%). A total 89 species were recorded at rocky substratum followed by 58 species in sandy and only 20 species found at muddy substratum. Habitat heterogeneity, geographical distance, physiochemical factors and ecological communities could characterize speciescomposition and distribution among intertidal study areas.
... In India, studies exploring community composition, diversity or taxonomy of free-living marine nematodes from coastal environments are largely limited. To date, many free-living marine nematode taxa belonging to Order Chromadorida have been reported from coastal benthic domains of this subcontinent (Ansari et al., 2012c). In this chapter, perspectives on the studies undertaken on exploring free-living marine nematode community composition including based on taxonomy are discussed along with updated checklist of taxa reported from the coasts of India. ...
... Free-living nematodes play an important role in the functioning of marine ecosystems 32 . Recently, it has reported that the family Sphaerolaimidae of the species Sphaerolaimus balticus and S. islandicus from the Southeast continental shelf of India 33 . The freeliving marine nematodes of genera Sphaerolaimus has also been reported in the central west coast of India 34 . ...
Article
Occurrence of the marine nematode family Sphaerolaimidae is the first report in the mangrove vegetation of Andaman Islands. Samples have been collected from South Andaman Islands. Important taxonomic features of two newly reported species of genus Sphaerolaimus are described and illustrated. © 2017, National Institute of Science Communication and Information Resources (NISCAIR). All rights reserved.
... Similar trends have been observed in other mangrove ecosystems located along both the coasts of India ( Ali et al.1983;Krishnamorthy et al. 1984;Rao et al. 1986;Chinnadurai & Fernando 2006a, 2006bKumary 2008;Ansari et al. 2014). The present checklist contains more species than most other checklists of nematodes from India ( Sajan & Damodaran 2007-157 species;Bhadury et al. 2015-33 species;Ansari et al. 2015-64 species) except for Ansari et al. (2012) which reported 191 species of marine nematodes from the continental shelf region of south western Bay of Bengal. Of the 179 species of free-living marine nematodes reported, 78 species are new records for the Sundarbans mangrove ecosystem and 6 species are new distributional record for Indian waters (see Fig 2). ...
Article
The present study provides an updated species checklist for free-living marine nematode species from the world’s largest contiguous mangrove ecosystem, the Sundarbans (India and Bangladesh). The species checklist includes information available from Sundarbans from the 1950s to the present (2016), using the most recent taxonomic classification of nematodes. The species list contains 179 species in 84 genera and 29 families. Four families, Xyalidae (22 species), Linhomoeidae (18 species), Desmodoridae (16 species) and Chromadoridae (15 species) were most speciose. The genera Halalaimus (9 species), Sabatieria and Daptonema (8 species each) were most species rich; 50 genera were represented by just a single species. Six species are new distributional records for Indian waters. The species checklist is the most extensive list of free-living marine nematodes from the Sundarbans mangrove ecosystem to date and provides a framework for studying biogeography of free-living marine nematodes from mangrove ecosystems globally.
Article
Plant parasitic nematodes are destructive endoparasites having deleterious effect on about 5000 agricultural crops notably vegetables, fruits, field crops, ornamental plants, and even human health. The immense damage caused by nematodes has been estimated as US $150 billion per annum (21.3%) despite of the availability of commercialized nematicides. Nevertheless, crop protection is still dependent on the development of novel chemicals due to development of pesticide resistance line by diverse pathogens. The utilization of heterocyclic moieties in agricultural industry is considered as an effectual practice to manage plant diseases either as systemic or non-systemic. These scaffolds consist of heteroatoms in their ring structure such as N, S, O, which give a boost to their biological activity as reported. The principal heterocyclic scaffolds are the benzimidazole, pyridine, nicotinic acid, pyrrole, indole, isatin, triazine, triazole, pyrazole, amides, imidazole, cinnamic acid, oxadiazole, coumarin, thiadiazole, etc. derivatives which owing to their marvelous structural diversity are widely exploited. The prime purpose of the review is to provide information to researchers around the globe about varied heterocyclic scaffold decorations that have been employed for the synthesis of potential nematicidal candidates from 2000 onwards and their utilization to combat complex destructive biotic stress. Therefore, this review assembled the considerable synthetic chemistry and nematicidal investigation of moieties against various plant parasitic pathogens along with structure-activity relationship studies. The scientific details provided in the article will highlight the importance of heterocyclic compounds in the agricultural industry and may pave a pathway for the development of novel nematicides.
Chapter
Animals are the major contributor to biodiversity with the presence of 1,637,932 valid and extant species under 34 phyla, while it is estimated that a total of around 5–30 million species are available on this planet. India contributes only 6.02% of known species of animals with 102,161 species. Apart from Subphylum Vertebrata under the Phylum Chordata, all the animals under 34 phyla are considered as invertebrate faunal communities and harbor a total of 1,518,677 species across the world, while India represents 92,357 species with the share of 6.08% of invertebrate faunal groups under 28 phyla. Despite immense importance and services as well as intrinsic values like pollination, biogeochemical cycles, nutrient cycle, filtration and purification of the ecosystem, protection of coastal areas, providing food, economic sustainability, etc., the invertebrate group of faunal communities remains underprivileged faunal groups. Hence, it is notably important to conserve these significant groups of faunal communities for the sustenance of biodiversity and human welfare.KeywordsBiodiversityEcosystemNicheInvertebrateConservation
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Benthic communities represents the major component of aquatic sedimentary biodiversity and play important roles in major ecosystem processes beside serving as excellent proxy for tracking environmental and anthropogenically induced changes. Chilika lagoon, the largest brackish water lagoon of Asia, is a hot spot for biodiversity and harbors rich aquatic flora and fauna. Numerous studies have been undertaken to date with a focus towards unraveling assemblage structure and diversity of benthic macrofauna and meiofauna from Chilika lagoon. Among benthic macrofauna, Gastropods, Bivalves and Polychaetes are major players in terms of abundance and diversity. In case of meiobenthos, Free-Living Marine Nematodes and Foraminifera constitute major components in terms of abundance and diversity in Chilika lagoon. Lesser known groups of meiobenthos have not been fully explored from this ecosystem. The baseline level information obtained from cataloguing biodiversity of benthic fauna in Chilika lagoon could ultimately form the basis for its long-term ecological monitoring as well as the role of these groups towards sustaining rich fisheries in this unique lagoonal environment.
Article
The present study investigates the impact of monsoon on meiofaunal and free-living nematode communities of the Sundarban estuarine system (SES) both from taxonomic and functional point of view. In 2013, SES experienced an unusual rainfall event followed by cloud burst event at upper Himalayan regime. Average meiobenthic abundance declined considerably in the study area from early phase of monsoon (EM) (699 ± 1569.4 ind. 10 cm−2) to later one (LM) (437 ± 949.9 ind. 10 cm−2) probably due to high annual rainfall which completely flushed the estuary. Free-living marine nematodes were the dominant group among all other meiobenthic taxa in both phases of monsoon. Nematode community was made up of 49 genera in 22 families. Comesomatidae, Chromadoridae, Linhomoeidae and Xylidae were the richest and most abundant families. During both phases of monsoon, stations, which were represented by fine sediments and high amount of organic carbon, harbored higher meiofaunal densities and nematode diversity with a strong dominance of 1B and 2B trophic guilds of nematodes. Different feeding guilds of nematode would be able to reveal anthropogenic-induced stress, which could be useful in assessing ecological quality of estuarine ecosystems. The present study indicates that climate change mediated unusual monsoonal precipitation may notoriously affect the meiobenthic assemblages in tropical estuaries like SES. Thus, this study could be an important first stepping stone for monitoring the future environmental impact on meiobenthic community in the largest mangrove region of the world.
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The efficiency of sorting of meiofaunal taxa from coarse and muddy marine sediments is assessed. For sandy sediments (mean % Silt + clay (S/C) = 8.5), the manual mixing in tap water and immediate decantation, repeated ten times, offers a 100 % efficiency. For muddy sediments, two sets of random samples (mean % S/C = 39 and 56 respectively) were compared using a flotation technique in a high density sugar solution. There are no differences in the efficiency of extraction using: manual mix in 200 mL flasks (method 1) and machine (vortex) mix in several 50 mL centrifuge tubes (method 2). Method 1 is recommended because of shorter time of processing, reduced potential error of manipulation and efficiency is independent of sediment size particle. For quantitative extraction of nematodes, three repeated extractions are acceptable; however, the sorting of less abundant taxa (e.g. copepods) should demand more processing steps.
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The nematode community structure of several shelf break and deep-sea stations in the North Atlantic and the Mediterranean is compared using data from the literature. Samples from 2 Mediterranean deep-sea canyons have a unique fauna of predatory and scavenging nematodes (e.g. Synonchiella, Halichoanolaimus, Gammanema) which comprise some 20 to 30% of the community, while some of the typical deep-sea genera (Theristus, Acantholaimus) are only marginally present. The nematode generic composition of the other sites reveals a gentle transition from the shelf break (Bay of Biscay; Mediterranean) over the slope (Mediterranean) towards the continental rise, abyssal plain and hadal depths (Bay of Biscay, Puerto Rico Trench, HEBBLE site, Hatteras Abyssal Plain). At all these sites predators and omnivores are less abundant (
Article
The meiobenthos communities of two fine sandy stations of 190m and 325m depth in the Fulf of Biscay off the Spanish coast were investigated in relation to (sediment composition, chlorophyll a content and redox values). Nematodes, the dominant taxon, were studied in detail. Their communities are relatively poor in densities (840 and 779 individuals per 10cm2) and biomass (0.137 and 0.334 mg dwt/10cm2) compared to those of shallow coastal areas. The dominance of small species (mean individual biomass 0.169 and 0.423 μg dwt) and a low total biomass can be related to the low chlorophyll a content (maximum of 1.14 μg/g). However, the number of nematode genera is much higher (46 and 62 genera per station) than on the continental shelves (often less than 40 species per 10cm2). Sabatieria, Daptonema, Minolaimus, Richtersia and Halalaimus are the dominant genera. There are also characteristic genera for the abyssal zone. The low food supply is considered as an important structuring factor. -from Authors
Article
Meiofaunal standing stock and nematode community structure were investigated in the western continental shelf of India by collecting samples from every degree square of the shelf during two cruises of the FORV (Fishery and Oceanographic Research Vessel) Sagar Sampada, conducted in 1998 and 2001. Samples were collected from 30, 50, 100 and 200 m depths using a Smith Mc Intyre grab. Meiofaunal density ranged from 8 Ind. 10 cm−2 to 1208 Ind. 10 cm−2 and biomass from 0.07 mg 10 cm−2 to 6.11 mg 10 cm−2. Nematodes were the dominant meiofaunal group, contributing 88% of the density and 44% of the biomass. Harpacticoid copepods were the second important taxa, contributing 8% of both biomass and density. Altogether, 154 species of nematodes belonging to 28 families were recorded from the study area. Numerically, Desmodora spp., Dorylaimopsis sp., Tricoma spp., Theristus spp. and Halalaimus spp. were the dominant species. In general, there was a decrease in biomass and density of meiofauna and species diversity of nematodes with increase in depth. There was a 67% drop in species number from 51 to 100 m (106 species) to the shelf edge (35 species). Species richness and diversity indices showed consistent decrease with depth. The species dominance index was higher below 150 m depth. ANOSIM (from PRIMER) showed a significant difference between the nematodes of the near shore and shelf edge. Latitudinal variation was observed only in the number of nematode species. Biomass and abundance of nematodes were found to increase from coarse to fine sediment, while copepods showed an opposite trend. Multivariate analyses of nematode communities did not reveal any latitudinal or substratum differences. Variables such as depth, latitude, organic matter (OM) and amount of clay were the most relevant parameters influencing the biomass and density of meiofauna, while depth and temperature were the important parameters explaining the distribution of the nematode communities along the western Indian shelf.