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Biodiversity Journal , 2012, 3 (1): 13-40

Nematodes in aquatic environments: adaptations and survival strategies

Qudsia Tahseen

Nematode Research Laboratory, Department of , Aligarh Muslim University, Aligarh-202002, India; e-mail: [email protected].

ABSTRACT are found in all substrata and sediment types with fairly large number of that are of considerable ecological importance. Despite their simple body organization, they are the most complex forms with many metabolic and developmental processes comparable to higher taxa. Nematoda represents a diverse array of taxa present in subterranean environment. It is due to the formative constraints to which these individuals are exposed in the interstitial system of medium and coarse sediments that they show pertinent characteristic features to survive successfully in aquatic environments. They represent great degree of mor - phological adaptations including those associated with cuticle, sensilla, pseudocoelomic in - clusions, stoma, and tail. Their cycles as well as development seem to be entrained to the environment type. Besides exhibiting feeding adaptations according to the substrata and sediment type and the kind of food available, the aquatic nematodes tend to wi - thstand various stresses by undergoing cryobiosis, osmobiosis, anoxybiosis as well as thio - biosis involving sulphide detoxification mechanism.

KEY WORDS Adaptations; fresh water nematodes; marine nematodes; morphology; ; development.

Received 24.01.2012; accepted 23.02.2012; printed 30.03.2012

IntroductIon cesses comparable to higher taxa; they demonstrate remarkable abilities to withstand stress and adverse The diversity of life is not distributed conditions. The elegans uniformly across the world and its diversification is (Maupas, 1900) survived the crash of space shuttl, not an automated process but requires some charac - Columbia that hit the ground with an impact 2,295 teristics of form and function that allow successful times the force of Earth's gravity (Cosgrove-Ma - exploitation of new habitats. Such species are, the - ther, 2003). refore, considered "plastic" or "malleable" that with Many species survive the unfavourable condi - modifiable genetic material can change or adapt tions by demonstrating anhydrobiosis, , when subjected to evolutionary selective pressures. osmobiosis or cryobiosis. The key to their success Nematodes, the most numerous of all Metazoa in in all types of and biotopes is their mor - number of individuals, exist in all habitats that can phological plasticity, physiological adaptability and support life. ecological diversity. Being ubiquitous, they can be as dynamic as the Nematodes are basically aquatic that re - habitat types and can change through time. With a quire a film of water to move. They may exist as deceptively simple anatomical design, they are re - free-living, commensals or parasites in all types of ferred as typical representatives of Metazoa (Nelson aquatic habitats viz., freshwater, brackish, marine et al., 1982). However, they are the most complex systems; in extreme environments including sea-ice forms with many metabolic and developmental pro - to hydrothermal vents. They may be found in clay, 14 Qudsia Tahseen

gravel, epiphytes, on sea grasses and . Their Morphological characteristics , soft and flexible bodies are well suited to allow bending in the interstitial system of sand The aquatic nematodes are quite varied morpho - grains/particles (Heip et al., 1985; Strayer, 1985; logically and no single species can be considered a Traunspurger, 1996 a, b). true representative. However, the similarity in fresh A number of factors affect their distribution viz., water as well as marine forms on account of their seasons, latitude, water depth, geochemical proper - aquatic habitats reflects convergent evolution. Most ties of the sediment, temperature, salinity, water aquatic nematodes have elongated cylindrical bo - movement, oxygen content, species interaction, re - dies of about one to several millimeters length ex - source partitioning and (Jensen, 1981; cept ~9 m long whale parasite Placentonema 1987a; Joint et al., 1982; Bouwman et al., 1984; gigantissima (Gubanov, 1951). The dark subterra - Platt & Lambshead, 1985; Ólafsson, 1992; Giere, nean environment has led to loss or reduction in 1993; Hendelberg & Jensen, 1993; Soetaert et al., body pigmentation, hence, the nematodes appear 1994; Modig & Ólafsson, 1998; Steyaert et al., whitish-semi transparent or transparent. 1999; Wetzel et al., 2002; Armenteros et al., 2009). They are characterized by slender, spindle- The present article highlights the habitat-speci - shaped bodies with enhanced swimming abilities. fic features of aquatic nematodes, their adaptations Wriggling or undulatory propulsion by alternate and compatibility to the environmental conditions. pushing and bending, is typically found due to presence of only longitudinal musculature. Howe - Major aquatic groups ver, some aquatic species can "jump" by bending of their bodies followed by a sudden relaxation Phylum Nematoda includes a diverse array of (e.g. Theristus ). taxa specific to a variety of aquatic habitats. The ty - The members of and Draco - pical composition of the freshwater meiofauna dif - nematidae move by "looping" with an alternate fers much from that in marine realm with adhesion and detachment of their anterior and po - nematodes more numerous in sediments than in the sterior body ends whereas the desmoscolecids water co lumns (Bell & Sherman, 1980; Sibert, move by contractive waves. 1981). Most species of are found in The cuticle of aquatic nematodes may be smo - fresh water ecosystems with the exception of few oth (most ), annulated (, tylenchids, aphelenchids and rhabditids whereas , most ), punctated only few species are reported from polar freshwa - (, many , Comeso - ters (Maslen, 1979). matidae), or provided with complicated and com - The species of , as pact structures (many Chromadoridae). well as inhabit both fresh water as There may be diverse types of cuticular modifi - well as marine environments (De Ley et al., 2005). cations (Figs. 1-3 , 5, 9, 10). Some nematodes may In , the fresh water representatives mainly have longitudinal ridges or (Figs. 11-13, 15, belong to , , 16, 18) aiding in swimming. Punctations in the and and to a lesser extent . The form of dots (punctation) or pores arranged irre - taxa Enoplida, , Chromadorida and gularly or in rows, are also common in many aqua - Monhysterida are predominantly marine. About tic taxa (Figs. 8, 9, 14). The punctations may fuse 4000 species of free-living marine forms have been into compact structures in many chromadorids accounted through various faunal surveys (Jensen, (e.g., Spilophorella paradoxa de Man, 1888; 1981; Sharma & Webster, 1983; Vanreusel et al., Chromadorella spp.). Often the cuticular surface is 1992). Estuarine nematodes show greater taxono - covered with a dense “fur” of ectosymbiotic sulfur- mic affinities to freshwater nematodes and can to - oxidizing to thrive in sulfur-rich marine se - lerate significant changes in salinity (Forster, 1998; diments (Nussbaumer et al., 2004; Ott et al., 2008). Warwick, 1981a). Aquatic nematodes usually possess long, hair- The nematode species with fresh water affilia - like sensilla called setae, relatively more developed tions are most abundant at the upper edge of the in - in marine forms, compared to slightly-raised or tertidal zone where the marine influence is often mammellate sensilla of terrestrial nematodes. Body weak (Nicholas et al., 1992). (so matic) sensilla (commonly found in Monhyste rida, Nematodes in aquatic environments: adaptations and survival strategies 15

Figures 1-9. Cuticular modifications. Figs. 1-3: Epsilonema pustulatum after Karssen et al. 2000. Fig. 4: Desmoscolex sp. Fig. 5: Glochinema sp. Fi g. 6: Plectus sp. Fig. 7: Goezia leporini after Martins and Yoshitoshi, 2003. Fig. 8: Cruznema sp. Fig. 9: Achroma - dora sp. (Scale bar: 1-3, 7 =1 µm; 4-6, 8, 9 = 10 µm). 16 Qudsia Tahseen

Figures 10-18. Cuticular modifications. Fig. 10: Epsilonema pustulatum after Karssen et al., 2000. Fig. 11: Mononchoides sp. Fig. 12: Fictor sp. Fig. 13: Plectus zelli. Fig. 14: Pelodera teres . Fig. 15: Diplogastrellus sp. Fig. 16: Panagrellus sp. Fig. 17: sp. Fig. 18: Chiloplacus sp. (Scale bar: 10 = 1 µm; 11-18 = 10 µm). Nematodes in aquatic environments: adaptations and survival strategies 17

Araeolaimida, Chromadorida and Enoplida) may be The utility of ocelli in aquatic habitats with par - arranged in rows or distributed randomly; in ab - ticular reference to marine environment, is the ne - sence of eyes, the symmetry of the tactile sensilla gative phototaxis to move to deeper layers/strata, as and the flexible body serve to guide the crawling observed in bioculata (Schultze in between sand grains, debris etc. In aquatic Carus, 1857); Oncholaimus vesicarius (Wieser, habitats the nematode setae of 5 to 10 µm length 1959); Enoplus anisospiculus Nelson et al., 1972 dominate with shortest setae mostly found in nema - (Croll, 1966; Croll et al., 1972; Bollerup & Burr, todes of littoral zone. Other types of sensilla include 1979; Burr & Burr, 1975; Burr, 1979; Burr, 1984). caudal setae (Figs. 110, 111) and terminal setae It probably explains the absence of ocelli in nema - (Figs. 102, 111, 113, 114, 117). todes inhabiting littoral sand. Few nematodes use The terrestrial nematodes usually have the pri - photosensitivity to determine the photoperiod for mitive arrangement (Fig. 32) of labial sensilla (6 successful completion of life cycle. Haemoglobin inner labials + 6 outer labials + 4 cephalics) con - instead of melanin, in some nematodes including trary to the configuration in many aquatic nemato - mermithids, serves an optical and light-shadowing des (6 + 10) where outer labials are situated at the function (Ellenby, 1964; El lenby & Smith, 1966; level of cephalic sensilla (Fig. 23) or there may be Croll & Smith, 1975; Burr et al., 2000). additional setae (Figs. 24, 28). The jointed setae The metanemes (Fig. 92) are spindle-shaped/fi - (Fig. 23) found in some aquatic nematodes are com - lamentous proprioceptors (Hope & Gardiner, 1982) parable to jointed appendages of indica - or stretch receptors (Lorenzen, 1978, 1981), found ting some relationship among these ecd ysozoans. in the lateral hypodermal chords of marine enoplids Amphids, the bilaterally symmetrical sensory (e.g., Enoplus Dujardin, 1845; Deontostoma and structures demonstrating the first evidence of cilia, Oxyonchus Filipjev, 1927) lying parallel or at an are involved in many behavioural functions and are angle of 10-30° to the main body axis. Metanemes comparable to olfactory organs. Coomans (1979) sug - are sensitive to the dorsoventral bending of nema - gested a mechanoreceptive, secretory as well as pho - tode body thus controlling the body volume. toreceptive function to amphids. Some marine enoplids especially Thoracosto - In aquatic nematodes, the amphids are relatively mopsidae possess a pair of sense organs known as complex, conspicuous and post-labial and mainly cephalic slits (de Man, 1886) or cephalic organs (Fi - circular (Figs. 20, 22, 28), loop-shaped (Figs. 72, lipjev, 1927), latero-ventrally placed between the 73), spiral, (Figs. 64, 65, 78), shepherd's crook, poc - circlets of the labial sensilla (Fig. 96). The cephalic ket-like and rarely pore-like compared to the am - organs may possess club-shaped cirri (chemosen - phids of land-dwelling nematodes that are usually sory/mechanosensory) in species having powerful pore-like or -like (Figs. 25, 31, 32) and occasio - buccal armature (Wieser, 1953) e.g., Oxyonchus nally round or spiral-shaped. Although there is little dentatus (Ditlevsen, 1918) Filipjev, 1927. physiological evidence for photosensitivity in ne - Crystalloids (Figs. 82, 83), the crystal-like in - matodes, ocelli have been defined as discrete pho - clusions or irregular electron dense deposits (Fig. toreceptors (Croll, 1970) and commonly found in 84) occurring subcutaneously or in pseudocoelom, marine genera viz., Thoracostoma Marion, 1870, have been observed in many fresh water (e.g., Mon - Phanoderma Bastian, 1865, Eurystomina Filipjev, hystera Bastian, 1865; Ironus Bastian, 1865; Tobri - 1921, Calyptronema Filipjev, 1921 etc. lus Andrássy, 1959; Tripyla Bastian, 1865) sensu Species may be provided with compact conglo - Alekseyev and Dizendorf, 1981; Andrássy 1958, merations of pigments (Figs. 81, 94, 95) viz., Eno - 1981, 1984; Juget, 1969; Micoletzky, 1922, 1925; plus spp., Pseudocella trichodes (Leuckart, 1849), Riemann, 1970; Jacobs & Heyns, 1990) and marine with diffuse pigments in the cervical region inside nematodes e.g., Sabatieria Rouville, 1903; Sphae - pharynx ( Deontostoma Filipjev, 1925; Oncholai - rolaimus Bastian, 1865; Terschellingia de Man, mus Dujardin, 1845 and Chromadorina Filipjev, 1888 (Nicholas et al., 1987). The ultrastructural, 1918) or outside pharynx in epidermis/pseudocoe - ecophysiological and physical microanalysis further lom ( de Man, 1888). Eye spots are revealed high sulphur content of the osmiophilic often provided with a hyaline “lens” or comparable and homogeneous crystalloids (Nuss & Trimkow - structure (Fig. 93) e.g., Symplocostoma Bastian, ski, 1984). Other reports suggested their role in de - 1865 and Araeolaimus . toxification or preventing harmful accumulation of 18 Qudsia Tahseen

metal sulphides in the tissues (Nuss, 1984; Nicholas veloped renette cell has secretory role in tube-buil - et al., 1987) or in storing food during adverse con - ding e.g., Ptycholaimellus Cobb, 1920 (Jensen, ditions (Bird et al., 1991). 1988). The secretory role has been also verified in Body pores (Figs. 85, 86) are common among Sphaerolaimus gracilis de Man, 1876 (Turpeen - many Enoplea . Generally a body pore leads through niemi & Hyvärinen, 1996) and Monhystera disjun - a canal to a unicellular, merocrine hypodermal cta (Van De Velde & Coomans, 1987). gland (Fig. 87) and an associated bipolar neurocyte The number and structure of along with e.g., Chromadorina germanica (Butschli, 1874). other genital components though taxo nomically im - However, Electron Microscopy revealed multivesi - portant, do not show much difference from those of cular complexes similar to Golgi bodies (Lippens, terrestrial nematodes and are largely specific of high er 1974). Some marine e.g., Ptycholaimellus taxa (Lorenzen, 1981, 1994). Ovaries in aquatic ne - ponticus (Filipjev, 1922) Gerlach, 1955 with a sy - stem of body pores and hypodermal glands mo - matodes generally tend to be long and well develo - dify the sedimentary microenvironments by ped reflecting high fecundity. Likewise the position building tubes (Hope & Murphy, 1969). of vulva usually varies from middle (e.g., members The diversity in nematodes revolves mostly of Tobrilidae, etc.) to posterior (e.g., mon - around the evolution of stoma and one or more hysterids) in aquatic nematodes. pharyngeal bulbs. The stoma or buccal cavity, The females are usually didelphic-amphidelphic usually a triradiate structure bounded by three or with antidromously reflexed (outstretched in Cyto - six lips, exhibits variations reflecting the different laimium exile Cobb, 1920) ovaries. However, mon - feeding modes (Wieser, 1953; Jensen, 1987b; hysterids represent mono-prodelphic females while Moens & Vincx, 1997; Traunspurger, 1997. the gonad can be mono-opisthodelphic in most spe - The buccal cavity may be absent or minute cies of . There is a connection between (Figs. 48-51) to spacious, unarmed type (Figs. 33, the reproductive and digestive systems in some On - 34) in non selective deposit feeder species. The ne - cholaimidae through demanian system (Figs. 97- matodes feeding on possess a buccal cavity 101), which varies from simple (e.g., Viscosia de armed with small to moderate-sized teeth (Jensen, Man, 1890) to highly-developed one (e.g., Adon - 1982; Romeyn & Bouwman, 1983; Romeyn et al., cholaimus Filipjev, 1918 and Oncholaimus ). 1983; Moens & Vincx, 1997). The buccal cavities The demanian system serves the functions of of powerful predators may further be armed with maintaining viability of spermatozoa, releasing a immoveable armature/teeth (Figs. 37-40, 52-59), sex attractant, facilitating deposition and tran - rows of small denticles or moveable structures ter - sfer of to the intestine, and elimination of ex - med mandibles or jaws (Figs. 60, 63). cess deposited in females through the Pharynx, the anterior muscular part of the gut digestive system (Eyualem et al., 2006). The aqua - with a tri-radiate lumen does not show habitat-wise tic male nematodes may possess one (monorchic) specificity b ut largely varies according to the fee - or two (diorchic) testes largely depending on the ta - ding modes. In marine nematodes the pharynx is xonomic group they belong to. Typically, the cuti - largely cylindrical with posterior part gradually cularised spicules and gubernaculum and the genital supplements/papillae are also not habitat-specific. expanding, occasionally forming a muscular bulb. Most aquatic nematodes possess long filamen - The dorsal gland orifice usually opens through the tous tails and propel themselves faster by its whipping stegostom while pharyngeal gland nuclei are lo - ac tion (Gerlach, 1953, 1971; Wieser, 1959; Warwick, cated in part. The pharyngeo-intestinal jun - 1971; Riemann, 1974). Nevertheless, the tail shape can ction (cardia) and intestine do not show aquatic be vari able from round, conical, cylindroid-clavate to adaptations. elongat ed-filiform (Figs. 102-112). In most marine ne - The secretory-excretory cell (renette cell = matodes it may be provided with caudal setae, speci - ventral gland, cervical gland or excretory cell) fically confined to terminus as terminal setae (Fig. opens through a ventral pore between mid pharynx 111). Often the bluntly-rounded tail terminus bears a to anterior intestine (Bird & Bird, 1991) except spinneret- the outlet for caudal glands’ (Figs. 113-117) Monhystera disjuncta Bastian, 1865 and some Iro - sticky secretion (Distem) that helps in anchorage to an nidae having a labial location (Van de Velde & object or substratum. This phenomenon of nictation is Coomans, 1987). In marine nematodes, the well de - a foraging adaptation in aquatic nematodes. Nematodes in aquatic environments: adaptations and survival strategies 19

Figures 19-32. Modifications in anterior sensilla. Fig. 19: Chronogaster sp. Fig. 20: Monhystera sp. Fig. 21: Mononchus aquaticus . Fig. 22: Hoffmanneria sp. Fig. 23: Pri - smatolaimus sp. Fig. 24: Sabatieria lyonessa . Fig. 25: sp. Fig. 26: Goezia leporini after Martins & Yoshitoshi, 2003. Fig. 27: Rhaptothyreus sp. Fig. 28: Epsilonema pustulatum after Karssen et al., 2000. Fig. 29: Theristus sp. www.nem.wur.nl/UK/In+the+picture/Gallery/. Fig. 30: tridentatus after Santos & Moravec, 2009. Fig. 31: Cephalobus sp. Fig. 32: Myctolaimus kishtwarensis Hussain, Tahseen, Khan & Jairajpuri, 2004(Scale bar = 10 µm). 20 Qudsia Tahseen

Figures 33-47. Modifications in anterior sensilla. Fig. 33: Paramesonchium sp. Fig. 34: Cervonema sp. Fig. 35: Prodesmodora sp. Fig. 36: Rhabdocoma sp. Fig. 37: Apha - nolaimus sp. Fig. 38: Amphimonhystera sp. Fig. 39: Platycoma sp. Fig. 40: Wieseria sp. Fig. 41: Ceramonema sp.; Fig. 42: Diplopeltoides sp. Fig. 43: Paramesacanthion sp. Fig. 44: Pheronous sp. Fig. 45: Cyatholaimium sp. Fig. 46: To - brilus sp. Fig. 47: Coninckia sp. Nematodes in aquatic environments: adaptations and survival strategies 21

reproduction and development not occurring through vulva, but through punctu - ring of the cuticle followed by the formation of ter - Reproductive mechanisms do differ among ne - minal ducts as a part of the demanian system. The matodes in different habitats. Mostly marine nema - excess sperms are thus discharged into the intestine todes are dioecious and amphimictic with obligate (Coomans et al., 1988). bisexuality thus enhancing the chances of fertiliza - The a quatic habitats with high wave action also tion and promoting high genetic variation. Howe - led to conditions of ovoviviparity in nematodes. ver, sex ratio is significantly influenced by Monhystera paludicola de Man, 1880 shows intra- temperature in Pellioditis marina Bastian, 1865 uterine hatching thus avoiding the risk of loosing () and Diplolaimelloides meyli Timm, the in fast-flowing waters (Hofmanner, 1913; 1961 (Monhysteridae), with more males at higher Hofmanner & Menzel, l915; Juget, 1967). Al - temperatures (dos Santos et al., 2008). though facultative ovoviviparity has been also ob - Amictic reproduction is mostly common in the served in the shallow water populations, this spatially and temporally variable environments characteristic was frequently expressed in toxic en - (Townsend et al., 2003) thus conforming well to the vironments (Van Gaever et al., 2006). Some spe - large proportions of species without males in varia - cies of Monhystera are characterised by a ble or in occasionally stressed ha - specialized with associated cells and glands bitats (Nicholas, 1975). The sex ratio in some (Figs. 88, 89) and a . The uterus is elongated and its length increases marine forms lean towards femaleness to reproduce with age (Jacobs & Heyns, 1990) so as to hold and more in to sustain in the unstable environ - protect greater number of developing juveniles in ment. The changes in growth rate as well as the du - stressed conditions (Otto, 1936; Schiemer et al., ration of life cycle are further indicative of the 1969; Otto & Schiemer et al., 1973). The highly in - volatility of environment (Palacin et al., 1993). determinate mode of cell division (Justine, 2002) in The fresh water species inhabiting shallow some aquatic enoplids contrary to normal determi - water bodies or those subject to repeated drying nate/ mosaic cell division tends to regulate the de - and wetting, tend to be without males (Grootaert, velopment in stressed environments. 1976; Wharton, 1986; Ocaña, 1991a) thus opting In some marine nematodes, such as Pellioditis for e.g., Eumonhystera Andrássy, marina the cell lineage with polyclonal cell fate di - 1981; Plectus Bastian, 1865; Rhabdolaimus de stribution allows a faster Man, 1880. Organisms living in isolated and un - by reducing the need for cell migrations (Houtho - stable habitats have evolved cryptobiosis, self-fer - ofd et al., 2003) resulting in extremely short gene - tilization, and passive dispersal, benefiting them in ration time (Moens et al., 1996). Many small the challenging conditions. species have short generation times of usually Life cycle stages often provide a means of sur - about one month or less (Gerlach, 1971; Heip et viving changes in the environment. The laid eggs, al., 1985). However, the period of development va - with their sticky/complex rugose/spinose shell ries from 3 days in Rhabditidae to 12 months in (Figs. 90, 91) surface, adhere to sediment particles. some Chromadoridae and Enoplidae (Houthoofd et The eggs may further be provided with entangling al., 2003). Faster development shortens the vulne - devices such as byssi or polar filaments to resist rable period of embryo to disturbances thus pre - water current in fresh water habitats. Experimen - venting embryonic deformities and/or arrest. tally a 5°C increase in temperature produces up to Nevertheless, the generation time and fecundity are a six-fold increase in the number of eggs laid (War - markedly temperature dependent. wick, 1981c). The sperms of some aquatic nemato - Another aquatic bacterivore Rhabdolaimus is des may possess a pseudoflagellum (a protoplasmic stated to survive as dauer stage in warm dry and hair) unlike the typically round or amoeboid (cra - acidic (Dmowska, 2000; Beier & Traunspur - wling) sperms of terrestrial forms. Retention of the ger, 2001). It has been reported that marine nema - nuclear envelope in mature spermatozoa has also todes from oligotrophic regions of are been reported (Lee, 2002). One unique feature smaller in size than those from sites showing hi - found in some marine species is traumatic insemi - gher level of flux (Udalov et al., nation (Maertens & Coomans, 1979; Chabaud et al., 2005). Such smaller nematodes produce fewer eggs 1983; Coomans et al., 1988), a type of than larger nematodes. 22 Qudsia Tahseen

This leads to the lower rate of reproduction growth and by bioturbating sediments around detri - and therefore, to the lower proportion of juveni - tus (Riemann & Schrage, 1978; Meadows & Tufail, les. The “male: female” ratio tends to be 0.7 while 1986) hence increasing porosity and light penetra - a ratio of 0.4–0.6 has been found in nematode tion. Thus the meiofaunal nematodes affect mat communities from deep-sea hydrothermal vents communities through bioturbation and grazing (Zekely et al., 2006). (Höckelmann et al., 2004). The habitat preference has been observed in Ecological adaptations some marine nematode families (Tietjen, 1977) e.g., muds: , ; muddy Light reaches only in the upper layers of the sands: Comesomatidae, Monhysteridae, Desmodo - water column; hence photosynthesis is limited to a ridae, Linhomoeidae; fine sands: Monhysteridae, few 100 meters water depth. The main energy Comesomatidae, Desmodoridae, Axonolaimidae; source for deep bottom dwellers, therefore, comes medium-coarse sands: Monhysteridae, Desmodori - from the primary production at the surface. The or - dae, Chromadoridae; clean, coarse sands: Epsilone - ganisms inhabiting this niche are mostly extremo - matidae and families of Draconematoidea. Current philes, tolerant of extremely low temperatures transport apparently plays a significant role in the (<0°C) and have an adaptation to high pressure as dispersal of certain meiobenthic nematodes. well. Aquatic nematodes, like their terrestrial coun - However, the nematodes occurring in the surfa - terparts, serve as food for small or cial layers of the sediments seem to be the most af - fungi and can be categorized as herbivores, carni - fected ( Witthöft-Mühlmann et al., 2007). Some vores, omnivores, predators, bacterivores and fun - species like Sabatieria pukhra (Schneider, 1906) givores with a range of food sources viz., algae, and Odontophora setosa (Allgen, 1929) found in diatoms, aquatic vegetation, bacteria, fungi, other the deeper sediment layers are rarely suspended small invertebrates including nematodes. (Eskin & Palmer, 1985). The species diversity and Littoral macrophytes, their associated periphy - the occurrence of the nematodes are influenced tons and free-floating biofilms also provide limited mainly by wind speed and river discharge. In calm in situ resources for nematodes (Peters & Traun - weather and low discharge, species diversity is re - spurger, 2005). The nature of the organic substrate duced and deposit feeders dominate. in the environment changes with time. Different The feeding habits can be inferred from the phy - food supplies influence species compositions and siognomic characters of buccal cavities (Wieser, their succession (Ferris & Matute, 2003; Ruess, 1960; Wieser & Kanwisher, 1961; Boucher, 1973; 2003; Ruess & Ferris, 2004; Michiels & Traun - Platt, 1977; Romeyn & Bouwman, 1983; Jensen, spurger, 2005; Ferris & Bongers, 2006) directly as 1987b) and associated structures (Bouwman et al., well as indirectly. 1984) in aquatic species. The epistrate feeders e.g., During the settling of food resources from sur - Eudiplogaster paramatus (Schneider, 1938); Chro - face to deep floor, much of the photosynthetic deri - madorita tenuis (Schneider, 1906) etc. are toothless ved material is mineralized. Larval forms of or possess a small tooth in buccal cavity to break soft-bodied including nemato - open cell membranes and suck out the cell contents des are adapted to take advantage (Manahan, 1990) (juice feeders); deposit feeders (particulate feeders) of the organic carbon as dissolved organic material with or without tooth, swallow the whole food item (DOM). In marine environments, the meiofauna and prevent its escape e.g., Daptonema biggi (Ger - builds the trophic linkage between bacteria and ma - lach, 1965) Lorenzen, 1977 (swallowing diatoms), crobenthos (Kuipers et al., 1981) and constitute an Linhomoeus gittingsi Jensen, 1986 (engulfing sul - energy sink (McIntyre, 1969). phide-oxidising bacteria. Besides the direct consumption of , ne - Sediments with high silt content generally show matodes carry out double remineralization and abundance of deposit-feeders (Heip et al., 1985) cycle in carbon twenty times their mass annually usually scoring 2 or 3 on the coloniser-persister (Platt & Warwick, 1980). Thus nematodes facilitate scale (Bongers et al., 1991, 1995), characterised by the detrital conversion by mechanical breakdown short life cycles and a high colonisation ability of the detritus, of limiting nutrients to (Schratzberger et al., 2007). Predators with buccal bacteria, producing films conducive to bacterial cavities armed with movable/protrusible mandibles Nematodes in aquatic environments: adaptations and survival strategies 23

Figures 48-63. Modifications in stoma. Fig. 48: Bujaurdia sp. Fig. 49: Plectus sp. Fig. 50: Onyx sp. Fig. 51: Tripylina sp. Fig. 52: Odontophora sp. Fig. 53: Udonchus sp. Fig. 54: Diplogastrellus sp. Fig. 55: Achromadora sp. Fig. 56: Enoplolaimus sp. Fig. 57: Mononchoides sp. Fig. 58: Odontopharynx sp. Fig. 59: Fictor sp. Fig. 60: Prismatolaimus sp.; Fig. 61: Onchulus sp. Fig. 62: Ioton - chus sp. Fig. 63: Odontophora sp. www.nem.wur.nl/UK/In+the+picture/Gallery/ (Scale bar = 10 µm). 24 Qudsia Tahseen

Figures 64-80. Modifications in stoma. Fig. 64: Oxystomina sp. Fig. 65: Ceramonema sp. Fig. 66: Pseudocella sp. Fig. 67: Barbonema sp. Fig. 68: Odontanti - coma sp. Fig. 69: Neochromadora sp. Fig. 70: Cobbia sp. Fig. 71: Gammarinema sp. Fig. 72: Gomphionema sp. Fig. 73: Parodontophora sp. Fig. 74: Bathylaimus sp. Fig. 75: Ptycholaimellus sp. Fig. 76: Synonchium sp. Fig. 77: Octonchus sp. Fig. 78: Calyptronema sp. Fig. 79: Filipjevia sp. Fig. 80: Ditlevsenella sp. Nematodes in aquatic environments: adaptations and survival strategies 25

for swallowing the whole prey (e.g., members of xybiosis); in extreme cases of prolonged quie - Thoracostomopsidae, Enoplidae, ) scence, the metabolic rate may fall below detec - can be largely classified as persisters; and the sca - table levels and appear to cease. This extreme vengers with buccal cavity provided with a lumened dormant condition is referred to as anabiosis onchium (tooth-like structure) to feed on dead ani - (Wharton, 1986) or alternatively as cryptobiosis mals or suck the cell contents of injured animals (Cooper & van Gundy, 1971). Unlike diapause, e.g., oncholaimids and enchelidiids. the dormant state ends when the environmental Bonger’s (1990) colonizer-persister classifica - stress is relieved . tion of nematodes holds good for terrestrial and fre - Temperature . Many biological structures, such shwater habitats, however, it has less application as enzymes and lipid bilayer membranes may show in marine habitat (Bongers et al., 1991; Fraschetti molecular instability or fluidity due to temperature et al., 2006), partly due to a lack of empirical sup - extremes. Increasing temperatures can increase re - port for the classification of some marine genera action rates and can cause protein denaturation, re - and the absence of extreme colonisers and persi - sulting in complete and often irreversible loss of sters in most marine habitats. Nevertheless, Saba - function (Hochachka & Somero, 1984). In fresh tieria has been found to be a good colonizer water ecosystems such as springs, nematodes gene - showing dominance in anthropogenically disturbed rally tend to avoid high temperatures above 43°C sediments (Tietjen, 1980). and high ionic concentrations (Ocana, 1991a, b) ex - The individuals have evolved life-history cha - cept terrestris (Stephenson, 1942). At hy - racteristics (e.g. rapid growth rate, ability to adapt drothermal vents, however, temperature can range to a wide range of environmental conditions) that from 2°C to 400°C and animals may have occasio - allow them to quickly establish in newly exposed nal brief contact with temperature difference of habitats or disturbed sediments in high densities 100°C (Chevaldonné et al., 1992; Delaney et al., (Thistle, 1981; Moore & Bett, 1989; Somerfield et 1992; Cary et al., 1998; Desbruyères et al., 1998). al., 1995). The environmental constraints restrict The deep sea is a relatively inhospitable envi - species establishment and mediate interactions bet - ronment for metazoans with constantly low (~2 °C) ween successful colonists (Schratzberger et al., ambient temperature, high pressure, absence of 2008) Leptolaimus de Man, 1876 found at physi - light and scarce organic carbon. Adaptation to the cally disturbed sites, is not classified as truly oppor - deep sea includes presence of more “fluid” proteins tunistic species (Modig & Ólafsson, 1998). and lipids to counter the high pressure and low tem - Ullberg & Ólafsson (2003) hypothesised that perature (Hochachka & Somero, 1984). Low tem - the agility of such small, surface-dwelling nema - peratures may slow or impede many biochemical tode species with high dispersal potential (Lee et reactions and decrease the fluidity of lipids, a factor al., 2001; Commito & Tita, 2002) might be an of primary importance to cell membrane function evolutionary response towards higher levels of (McMullin et al., 2000). competence for coping with disturbance (Schratz - Most of the adaptations that enable polar inter- berger et al., 2009). tidal inverteb rates to survive freezing, are associa - ted with their ability to withstand aerial exposure. Adaptations to stress Nematodes surviving the freezing, exhibit low metabolic rate and slow growth rate and the ina - Many aquatic nematodes can adapt physiologi - bility to survive at temperatures above 3-8°C. The cally to environmental challenges (Samoiloff et al., bacterial-feeder, Plectus murrayi Yeates, 1970 1980, 1983; Mutwakil et al., 1997; Doroszuk et al., (Timm, 1971) inhabiting semi-aquatic and terre - 2006). Fresh water as well as deep sea environ - strial biotopes in the Antarctic McMurdo Dry Val - ments offer much hostile and extreme conditions leys, has its distribution limited by organic carbon compared to other aquatic habitat types. Therefore, and moisture and survives extreme desicca - the physiological challenges faced by nematodes tion, freezing conditions, and other types of stres - are greater in these ecosystems. ses (Adhikari et al., 2010). A variety of environmental stresses may trigger The Antarctic nematode, Panagrolaimus davidi quiescence viz., desiccation or high temperature Timm, 1971 shows both freeze-avoidance and (anhydrobiosis), low temperature (cryobiosis), freeze-tolerance strategies thus experiencing free - osmotic stress (osmobiosis) and low oxygen (ano - zing temperatures over nine months of the year and 26 Qudsia Tahseen

facing regular cycles of freezing and thawing in rias (Israel) for 8 months of a year (Por & Masry, spring; the nematode thus undergoes cryoprotective 1968). High salinity and high temperature are less dehydration instead of freezing when held at its nu - common physiological stresses for aquatic nemato - cleation temperature for a longer period, or when des than low oxygen. In springs, Udonchus Cobb, cooled at a slower rate (Wharton et al., 2003). 1913 and Rhabdolaimus have been reported to to - P. davidi is the only animal known to survive ice lerate high salinity and temperature (Ocaña, 1991a, crystallizat ion within its cells (Wharton et al., b). However, the Mesodorylaimus macrospi - 2005). With slower cooling rates, the water inside culum Zullini, 1988 seems to withstand stress (Tu - the worm is super cooled, thereby creating a dorancea & Zullini, 1989) in intermittent lakes that vapor pressure difference between the ice in the are subject to high salinity and temperature. medium and the nematode. Besides synthesizing The ability to survive under anaerobic condi - trehalose, P. davidi produces a protein that inhi - tions may thus be quite widespread among nema - bits the activity of organic ice nucleators though todes, although different mechanisms may be the sequence of this protein has no homology with involved (Schiemer & Duncan, 1974; Bryant et al., any other anti-freeze or ice-nucleating proteins 1983). The presence of Theristus anoxybioticus Jen - (Wharton et al., 2005). sen, 1995 at the oxygenated sediment surface of Oxygen . Many meiobenthic species persist muddy sediment suggested that even this facultative over extensive periods under hypoxic and anoxic anaerobe nematode needs to reach oxygen for its conditions (Wetzel et al., 2002). Nematodes are reproduction (Jensen, 1995). the most tolerant organisms as their species ri - Thus, survival under anoxia would be possible chness does not change in hypoxic-anoxic condi - only under critical conditions. For reproduction on tions though their species composition and the other hand, especially for the development of trophic structure display significant changes eggs, there must be another more efficient pa - (Gambi et al., 2009). thway of energy production (Riess et al., 1999) al - Jensen (1987a) found that species, living in dee - though nitrate respiration has never been reported per sediment layers were significantly more slender in nematodes so far. than their oxybiotic, surface-dwelling congeners, In shallow beaches drifting macroalgal mats in however, nematodes of the genera Desmoscolex the summer months induce anoxic and sulfidic con - Claparède, 1863; Tricoma Cobb, 1894 and Cobbio - ditions with devastating effects on members of the nema Filipjev, 1922 have been reported mostly from benthic . Other disturbances like eutrophica - the anoxic depths (> 300 m) of the Black Sea (Zait - tion in conjunction with density-stratified water sev et al., 1987). At some places even Desmoscolex masses frequently results in severe oxygen deple - and Bolbolaimus Cobb, 1920 are replaced by the tion of bottom waters, especially during the sum - species ( Chromadorella Filipjev, 1918, Sabatiera mer months, leading to hypoxic (dissolved oxygen Rouville 1903 and Polysigma Cobb 1920) more to - concentration <2 mg l -1 ) or even anoxic (dissolved lerant to the extreme conditions (Gambi et al., 2009). oxygen concentration of 0 mg l -1 ) conditions (Ro - Oxygen stress is successfully tackled by the senberg et al., 1992). While most hypoxic events fresh water genera of Monhysteridae and Tobrili - affect the fauna in deeper sublittoral regions below dae (Triplonchida) having prevalence in the habi - a thermo- or halocline; eutrophication has also tats with limited or no oxygen (Nuss, 1984; been attributed to the increase in benthic macroal - Jacobs, 1987). Low oxygen concentrations are to - gae (Rosenberg, 1985; Hull, 1987; Raffaelli et al., lerated well by most (Ocana, 1993). 1991; Kolbe et al., 1995). Such species survive anaerobic sediments by anae - There is induction of Hb synthesis in many in - robic metabolism, facultative anaerobic metabo - under stressful conditions (hypoxia, temperature increase and CO poisoning). The lism or quiescence (Bryant et al., 1983). Few mud-dwelling nematode Enoplus brevis Bastian, species can cope with changing oxygen levels by 1865 with a pharyngeal haemoglobin (Hb) shows alternating between aerobic and anaerobic meta - feeding rates under hypoxia than the related, E. bolism similar to the mechanism found in the in - communis Bastian, 1865 that lacks Hb (Atkinson, sect parasite carpocapsae Weiser, 1977). Hb may be associated with vital functions 1955 (Shih et al., 1996). in euryhaline invertebrates living in widely dif - Likewise a species Allodorylaimus andrassyi ferent salinities and pH and lacking significant (Meyl, 1955) Andrássy, 1986 (Dorylaimida) found osmotic, ionic, and acid-base regulatory capaci - to survive in oxygen-free sediments of Lake Tibe - ties (Weber & Vinogradov, 2001). Nematodes in aquatic environments: adaptations and survival strategies 27

Figures 81-91. Fig. 81: Pigment spot in Enoplus sp. Fig. 82, 83: Crystalloids in pseudocoelom of Tobrilus sp. and Ironus sp. Fig. 84: Ultra structure showing longitudinal section of muscle fibres with crystalloids and electron-dense bodies. Fig. 85, 86: Body pores in Cryptonchus sp. and Ptycholaimellus sp. Fig. 87: Hypodermal gland openings. Fig. 88, 89: glands associated with uterus and vagina. Fig. 90, 91: Egg shells with rugose or spinose surface [Scale bar: 81-83, 85-89, 90, 91 = 10 µm; 84 = 1 µm). 28 Qudsia Tahseen

and summer with sufficient meltwater from adja - cent snowbanks. The water content of these sites varies from saturated to completely dry (Wharton, 1998) and the nematode faces changes in external osmotic concentration (Wharton, 2003). Panagro - laimus davidi maintains its internal osmotic con - centration above that of the external medium and is thus an hyperosmotic regulator. The nematode achieves regulation under hypo - smotic stress more rapidly than under hyperosmotic stress (Wharton, 2010). The nematodes found in coastal zones are exposed to conditions of rapid de- and rehydration similar to the and lichens. Drying initially decreases rates of anaerobic micro - bial processes in sediments due to reduced oxygen penetration (Baldwin & Mitchell, 2000). Differen - ces among aquatic and terrestrial species in resi - stance to desiccation and inundation cause shifts in community composition along hydro-period gra - dients (Larned et al., 2007). The ability to enter anhydrobiosis may be one of the most important and widespread adaptations in evolutionary terms amongst nematodes but not expressed in species of stable habitats. Freshwater nematodes of temporary ponds commonly enter quiescence in response to water stress (Wharton, 1986; Womersley & Ching, 1989). The phenome - Figure 92: Metaneme (AF: anterior filament, PF: posterior non is also common in nematodes of polar regions filament, Sc: Scapulus, SC: sensory cell). Fig. 93: pigment (Pickup & Rothery, 1991; Wharton & Barclay, spot. Fig. 94: Ocellus. Fig. 95: Ocellus surrounded by pig - ments. Fig. 96: Anterior end of nematode with cephalic 1993; Wharton, 2004). Important information on organ (CO). Figures 97-101: Demanian system (Os: Osmo - anhydrobiosis has been provided by several wor - sium; Uv: Uvette; MD: Main duct; DE: Ductus entericus; kers (Cooper & van Gundy, 1971; Demeure & DU: Ductus uterinus). Freckman, 1981; Wharton, 1986; Womersley, 1987; Barrett, 1991; McSorley, 2003). The onset of anhydrobiosis marks a gradual water Water. The aquatic nematodes face two basic loss from 75-80% to 2-5% in anhydrobiotic forms problems of water gain or water loss depending (Demeure & Freckman, 1981). The fresh water ne - upon the type of surrounding environment. matodes Actinolaimus hintoni Lee 1961 and Dorylai - Marine nematodes the osmoconformers, often mus keilini Lee, 1961 were revived from cryptobiotic live in water that has a very stable composition and, (anabiotic) stage in dried mud (Lee, 1961). hence, they have a very constant internal osmola - Anhydrobiotic nematodes contain large amounts rity. Many invertebrates that osmoconform achieve of sugars, especially the disaccharide trehalose, a tissue tolerance by increasing intracellular osmola - dimer of glucose that protects cells by replacing rity by mobilization of amino acids, thereby balan - water associated with membranes and proteins. cing extracellular fluid. However, most species are killed if drying oc - This reduces the osmotic gradient across cell curs too quickly whereas repeated events of drying membranes and maintains constant cell volume and rehydration decrease viability of nematodes (Schmidt-Nielsen, 1997; Kirk et al., 2002). (Demeure & Freckman, 1981; Barrett, 1991). An - Panagrolaimus davidi , an Antarctic nematode, is hydrobiotic nematodes rehydrate in water, but there associated with ornithogenic soils (Porazinska et al., is an average lag time (from less than an hour to se - 2002) in coastal areas that are ice-free during spring veral days) between immersion and their return to Nematodes in aquatic environments: adaptations and survival strategies 29

normal activity (Cooper & Van Gundy, 1971; Whar - al together. Some marine nematodes e.g., Oncholai - ton, 1986; Barrett, 1991). Recovery is improved if mus campylocercoides De Coninck & Stekhoven, rehydration is slow, and nematodes are exposed to 1933; Sabatieria wieseri Platt, 1985; Terschellingia high relative humidity before being immersed in longicaudata de Man, 1907; Sphaerolaimus papil - water. Anhydrobiosis involves decreased cuticular latus Kreis, 1929; Siphonolaimus ewensis Warwick permeability and the condensation or packing toge - & Platt, 1973; Pontonema vulgare Bastian, 1865, ther of tissues with increased levels of trehalose or while living in sulphidic transition zones convert (Demeure & Freckman, 1981; Wharton, hydrogen sulphide to elemental sulphur which tem - 1986; Womersley, 1987; Barrett, 1991). Coiling is porarily reduces the concentration and toxic effect a typical behavioral response observed in anhydro - of H 2S and also provides an energetic 'deposit' for biotic nematodes. latter oxidation to thiosulphate, sulphite or sulphate Pollutants. Environmental pollution is an im - under oxic conditions (Thiermann et al., 2000). portant cause of stress in natural populations. Besi - Many nematodes (, Desmodo - des affecting the population dynamics, it can also ridae) harbour symbiont chemoautotrophic bacteria lead to genetic changes (mutations) and adaptations. (Hentschel et al., 2000; Ott et al., 2008; Bayer et al., The nematode bioassays lead to detection of a wide 2009) that oxidize sulfide and fix CO 2. The Hbs of range of chemical concentrations with distinct toxic these organisms bind sulfide without covalent mo - effects of lethality, developmental inhibition and dification of the heme groups and facilitates its tran - mutagenicity. Most studies have been undertaken sport or diffusion thus protecting the tissues from using the continental species sulfide poisoning. Goodey, 1945 against few studies carried out on These symbionts, in turn, constitute the worms' aquatic nematodes to determine pollution and toxi - major food source and are acquired from the envi - city in marine environments (Warwick, 1981b; Sa - ronment and shed off at every moult but reacquired moiloff & Wells, 1984; Bogaert et al., 1984; from the environment. The mechanisms of sym - Vranken et al., 1991). biont recruitment from the environment (Bulghe - Aller & Aller (1992) showed that meiofauna ac - resi et al., 2006) have shown that Ca 2+-dependent tivity stimulated solute fluxes and reaction rates, lectin Mermaid mediates symbiont–symbiont and particularly aerobic decomposition and associated worm–symbiont attachment in oneistus processes such as nitrification in the oxic zone of (Ott et al., 1995). the marine sediments. Among toxicants, sulfide is Thick tubes or cuticles reduce or prevent expo - perhaps the most abundant with its impacts on bio - sure of some external tissues to sulfide with Pty - logical systems well documented (Somero et al., cholaimellus serving a good example (Nehring et 1989; Grieshaber & Völkel, 1998). al., 1990). The effect of mercury contamination was Sulfide, in just micromolar amounts, is capable rather confusing as low doses of mercury appeared of impairing biological processes and may seve - to have much more drastic effects than the medium rely inhibit aerobic metabolism by interfering with and high doses. cellular respiration and oxygen transport in diffe - Austen and McEvoy (1997) observed that low rent metazoan (Somero et al., 1989; Vismann, doses of copper and zinc seem too toxic to kill all 1991; Grieshaber & Völkel, 1998; Szabó, 2007). the bacteria and meiofauna in the samples so that In the mitochondria, sulfide may poison the respi - complete decomposition of nematodes did not ratory enzyme cytochrome c oxidase, thus inhibi - occur (Hermi et al., 2009). Schratzberger et al. ting ATP production by the electron transport (2009) found Araeolaimus bioculatus (de Man, chain and is capable of inhibiting muscular con - 1876) to be intolerant to mercury contamination, traction independent of its effects on aerobic me - with effects observed even at the low concentration tabolism (Julian et al., 1998). used (0.084 ppm dw). Thus an organism adopts the strategies to avoid Marylynnia stekhoveni (Wieser, 1954) was cate - sulfide, switch to anaerobic metabolism (Grieshaber gorized as ‘‘opportunistic’’ at low and medium mer - & Völkel, 1998), exclude sulfide from sensitive tis - cury doses with Hg(L) and Hg(M) concentrations sues, or oxidize sulfide to less toxic forms. Most in - whereas Prochromadore lla neapolitana (de Man, habitants of vent and seep environments do not 1876) Micoletzky, 1924 was found to be a ‘‘mercury- re alistically have the option of avoiding sulfide resistant’’ species (Schratzberger et a l., 2009). 30 Qudsia Tahseen

Pollutants also modify the distribution and laimoidea, Chromadorida, , Monhy - abundances of nematodes through indirect ecologi - sterida, and Araeolaimida) whereas the almost ex - cal interactions (Johnston & Keough, 2003). If pol - clusively non-marine Rhabditida are derived from lution decreases abundance of a competitively the ancestor of the Monhysterida or Araeolaimida dominant species, inferior competitors may increase (Meldal et al., 2007). in abundance not as a direct result of the contami - The similarity in cuticular structure of Acan - nant but due to altered competition. Copper causes thonchu s Cobb, 1920 (Wright & Hope, 1968), decrease in recruitment and abundance of a number Chromadorina Filipjev, 1918 (Lippens, 1974), of organisms (Johnston & Keough, 2000, 2003; and Caenorhabditis (Epstein et al., 1971; Zuc - Mayer-Pinto et al., 2010). Thus metazoans largely kerman et al., 1973) lends circumstantial evi - detoxify absorbed or ingested metals by using dence to the hypothesis that the metal-binding proteins (metallothioneins) and for - arose from chromadorid-like ancestors. Howe - ming subcellular inclusions. ver, a reinterpretation of the cuticular structure These mechanisms often act jointly to consoli - by Decraemer et al. (2003) suggested that this is date and enclose excess metals, which then accu - a homoplasic character that has appeared inde - mulate within tissues and/or skeletal structures over pendently in several . time (Beeby, 1991; Lu oma & Carter, 1991). The Though aquatic nematodes can not be treated metal detoxification strategies used by nematodes separately as far as the phylogenetic grouping is are not very different from those used by other or - concerned. Nevertheless, one of these lineages in - ganisms (McMullin et al., 2000) for example the cludes marine, freshwater and terrestrial taxa, sug - existence of , the heavy metal-bin - gesting that early were characterised by ding peptides, in nematodes that are synthesized much greater osmotic tolerance than early Dory - by and fungi when exposed to metals laimia (De Ley, 2006). (Monserrat et al., 2003). Most e noplids include large predators with big hooks or teeth in more or less complex arrangements Phylogenetic implications as well as some additional sensory structures such as eyespots and the stretch receptors (metanemes). Assuming that all life originated in the sea and They are interesting phylogenetically because of that metazoan phyla evolved more than 550 million possessing some features, presumably ancestral wi - years ago (mya) during the period thin Nematoda viz., a highly indeterminate mode of (Conway, 1993; Valentine et al., 1996, 1999; Fe - development (Justine, 2002) and retention of the nu - donkin & Waggoner, 1997; Peterson & Davidson, clear envelope in mature spermatozoa (Lee, 2002). 2000), it can be assumed that the ancestral nema - The ventrally spiral amphid was considered tode was also marine. plesiomorhic by Lorenzen (1981), yet the non-spi - Nematodes also lack an informative re - ral form seemed to be a secondary character loss. cord (the oldest known fossil, Cretacimermis libani Li kewise, the presence of ocelli is usually conside - Poinar et al., 1994 (Poinar, 2003) dates to around red to be a primitive character though these struc - 135 mya). Filipjev (1929, 1934) and Lambshead & tures are the most complex photoreceptors that the Schalk (2001) have accepted the marine ancestry of nematodes possess. Nematoda while De Ley & Blaxter (2002, 2004) Coomans (1979) suggested that the pigment considered a terrestrial origin for the Nematoda. spots and their associated amphidial photoreceptors As highly productive terrestrial ecosystems exi - are less elaborate and may represent a stage that ori - sted in the Precambrian there might have been ginated later in the evolution and so have not yet chances of supporting the evolution of a new phy - achieved great complexity. lum (Kenny & Knauth, 2001). Nevertheless, a ma - Nevertheless, the occurrence in nematodes with rine origin of the Nematoda can be traced as some both types of photoreceptors: rhabdomeric and ci - terrestrial taxa of current phylogeny have been liary, supports Vanfleteren & Coomans’s (1976) and found nested within marine clades. Sharma et al.’s (2006) conclusion that morphologi - The strongest evidence for a marine ancestry of cal characters used in the classification are not the Nematoda comes from the Chromadorea: the enough to recognize phyla along the main lines of basal clades are all predominantly marine (Micro - evolution. Nematodes in aquatic environments: adaptations and survival strategies 31

Figures 102-112. Modifications at posterior body end. Fig. 102: Anaplectus sp. Fig. 103: Panagrellus sp. Fig. 104: Rhabdolaimus sp. Fig. 105: Tripylina sp. Fig. 106: Chrono - gaster sp. Fig. 107: Plectus sp.; Fig. 108: Tobrilus sp. Fig. 109: sp. Fig. 110: Epsilonema pustulatum after Karssen et al., 2000. Fig. 111: Desmoscolex sp. Fig. 112: Cryptonchus sp. Figures 113-117. Modifications at tail terminus. Fig. 113: Plectus sp. Fig. 114: Chronogaster sp. Fig. 115: Epsilonema pustulatum after Karssen et al., 2000. Fig. 116: Do - rylaimopsis variabilis Muthumbi et al., 1997. Fig. 117: Tobrilus sp. (Scale bar: 102-112 = 10 µm; 113-117 = 1 µm). 32 Qudsia Tahseen

conclusIon gurov O.L. (eds.). Freilebende und Phytopathogene Nematofaunen aus dem Fernen Osten, Akademia Aquatic nematodes are of vital importance as a Nauk. USSR, Fernstliches wiss Zentrum, Biol Bo - very significant portion of the energy flow in the denk Ist Wladiwostok, 8-11. Aller R.C. & Aller J.Y., 1992. Meiofauna and solute tran - benthic system passes through these nematodes. sport in marine muds. Limnology and Oceanography, However, one of the main reasons for the aquatic 37: 1018-1033. nematodes being ignored is that they are not of di - Andrássy I., 1958. Erd- und süßwassernematoden aus rect benefit or nuisance to man. Their role in stimu - Bulgarien. Acta Zoologica Academiae Scientiarum lating bacterial metabolism is now well documented Hungaricae, 4: 1-88. (Tenore et al., 1977; Tietjen, 1980) and they have Andrássy I., 1981. Revision of the order Monhysterida an important and direct influence on the producti - (Nematoda) inhabiting soil and inland waters. Opu - scula Zoologica, Budapest, 17/18: 13-47. vity of shallow waters by enhancing nutrient rege - Andrássy I., 1984. Klasse Nematoda (Ordnungen Mon - neration in the sediments. hysterida, Desmoscolecida, Araeolaimida, Chroma - They also affect the texture (Cullen, 1973) and dorida, Rhabditida). Bestimmungsbücher zur the physical characteristics of sediments by mu - Bodenfauna Europas. Berlin-Stuttgart, 509 pp. cous secretion, which are significant for dredging Armenteros M., Ruiz-Abierno A., Fernández-Garcés R., and dumping operations. It can be further said that Pérez-García J.A., Díaz-Asencio L., Vincx M. & De - the story of their adaptations to a particular envi - craemer W., 2009. Biodiversity patterns of free-li - ronment type is far more complex than could be in - ving marine nematodes in a tropical bay: Cienfuegos, Caribbean Sea. Estuarine, Coastal and Shelf Science, ferred. Despite the recent information gained, 85: 179-189. studies are required on the plesiomorphous forms, Atkinson H.J., 1977. The role of pharyngeal haemoglo - the mutants and the apomorphs to reveal how far bin in the feeding of the marine nematode, Enoplus deviations exist. brevis . Journal of Zoology, 183: 465-471. Future researches should further consider the Austen M. & McEvoy J., 1997. The use of offshore me - detailed structure and anatomy of the receptors as iobenthic communities in laboratory microcosm ex - modification in them are reflected in changes in be - periments: response to heavy metal contamination. Journal of Experimental Marine and Eco - haviour. Although the nematode is logy, 211: 247-261. considered to be a conservative system with a rather Baldwin D. & Mitchell A., 2000. The effects of drying small number of cells, different behavioural pat - and re-flooding on the sediment and soil nutrient dy - terns exist according to the different environments namics of lowland river–floodplain systems: a syn - and ecological niches occupied by the species. thesis. Regulated Rivers: Research and Management, 16: 457-467. Barrett J., 1991. Anhydrobiotic nematodes. Agricultural Zoology Reviews, 4: 161-176. AcknowlEdgEMEnts Bayer C., Heindl N.R., Rinke C., Lücker S., Ott J.A. & Bulgheresi S., 2009. Molecular characterization of The financial assistance provided by Ministry the symbionts associated with marine nematodes of of Environment, Department of Science and Te - the genus Robbea . Environmental Microbiology Re - chnology, New Delhi and Third World Academy ports, 1: 136-144. of Science, Italy is being acknowledged here Beeby A., 1991. Toxic metal uptake and essential metal with thanks. regulation in terrestrial invertebrates: A review. In: Newman M.C. & McIntosh A.W. (eds.), Metal Eco - toxicology, Concepts and Applications. Lewis Publi - shers, Boca Raton, 65-90. rEfErEncEs Beier S. & Traunspurger W., 2001. The meiofauna com - munity of two German streams as indicator of pollu - Adhikari B.N., Tomasel C.M., Li G., Wall D.H. & Adams tion. Journal of Aquatic Stress and B.J., 2010. The Antarctic nematode Plectus murrayi : Recovery, 8: 387-405. an emerging model to study multiple stress survival. Bell S.S. & Sherman K.M., 1980. A field investigation of Cold Spring Harbor Protocols, 10.1101/pdb.emo142. meiofaunal dispersal: tidal resuspension and implica - Alekseyev V.M. & Dizendorf Z.A., 1981. Nematoden der tions. Marine Ecology Progress Series, 3: 245-249. Gattung Tobrilus (Nernatoda, Enoplida) aus dem Sii - Bird A.F. & Bird J., 1991. The structure of nematodes, den des Fernen Ostens. In: Eroshenko A.S. & Belo - 2nd edition. Academic Press, San Diego, 316 pp. Nematodes in aquatic environments: adaptations and survival strategies 33

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