WoRMS source details
Van Colen, C.; Montserrat, F.; Verbist, K.; Vincx, M.; Steyaert, M.; Vanaverbeke, J.; Herman, P.; Degraer, S.; Ysebaert, T. (2009). Tidal flat nematode responses to hypoxia and subsequent macrofauna-mediated alterations of sediment properties. Marine Ecology Progress Series. 381: 189-197.
178896
10.3354/meps07914 [view]
Van Colen, C.; Montserrat, F.; Verbist, K.; Vincx, M.; Steyaert, M.; Vanaverbeke, J.; Herman, P.; Degraer, S.; Ysebaert, T.
2009
Tidal flat nematode responses to hypoxia and subsequent macrofauna-mediated alterations of sediment properties
Marine Ecology Progress Series
381: 189-197
Publication
NeMys doc_id: 17952
Available for editors [request]
To assess the role of macrofauna-mediated sediment changes on nematode community
recovery, we examined the temporal development of macrobenthos, nematode communities and sediment
properties following hypoxia in 16 m2 replicated plots over a 6 mo period. Hypoxia drastically
changed nematode community composition (i.e. reduced diversity and abundances of all dominant nematodes,
except Odontophora spp.), but complete mortality, as was the case for the macrobenthos, did
not occur. Macrofauna diversity recovered slowly, but community composition approached that of control
communities after several months. In contrast, nematode diversity recovered to control values
within 1 mo but, subsequently, decreased again; hence, no clear convergence towards the control
community composition was apparent. This diversity decline and lack of community recovery was
mainly attributed to abundance overshoots of the epistrate feeding nematodes Chromadora spp., Daptonema
spp. and Ptycholaimellus ponticus in the treatments, which dominated the treatment community
after 2 mo. Nematode community reassembling was strongly related to the coupled macrobenthos-
environmental temporal development. The dynamics of 2 sediment characteristics, which were
both mediated by the colonizing macrobenthos, are presented as possible determinant factors for this
relationship: (1) low nematode post-settlement resuspension resulting from stable sediments at early
macrofauna recovery stages and (2) enhanced nematode reproduction and settlement success in a
dense microphytobenthos mat in relation to the temporal variation in macrobenthos grazing pressure
and bioturbation. In conclusion, the strong relationships between macrobenthos recovery, environmental
development and nematode community development after hypoxia highlight the importance
of macrobenthos–sediment interactions in the recovery and structuring of nematode communities.
Date
action
by
Anoplostoma viviparum (Bastian, 1865) Bütschli, 1874 (ecology source)
Chromadora Bastian, 1865 (ecology source)
Chromadorita Filipjev, 1922 (ecology source)
Daptonema Cobb, 1920 (ecology source)
Neochromadora Micoletzky, 1924 (ecology source)
Odontophora Bütschli, 1874 (additional source)
Oncholaimellus de Man, 1890 (additional source)
Paramonohystera Steiner, 1916 (ecology source)
Ptycholaimellus Cobb, 1920 (ecology source)
Ptycholaimellus ponticus (Filipjev, 1922) Gerlach, 1955 (ecology source)
Sabatieria de Rouville, 1903 (ecology source)
Sphaerolaimus Bastian, 1865 (ecology source)
Viscosia de Man, 1890 (ecology source)
Chromadora Bastian, 1865 (ecology source)
Chromadorita Filipjev, 1922 (ecology source)
Daptonema Cobb, 1920 (ecology source)
Neochromadora Micoletzky, 1924 (ecology source)
Odontophora Bütschli, 1874 (additional source)
Oncholaimellus de Man, 1890 (additional source)
Paramonohystera Steiner, 1916 (ecology source)
Ptycholaimellus Cobb, 1920 (ecology source)
Ptycholaimellus ponticus (Filipjev, 1922) Gerlach, 1955 (ecology source)
Sabatieria de Rouville, 1903 (ecology source)
Sphaerolaimus Bastian, 1865 (ecology source)
Viscosia de Man, 1890 (ecology source)