| Literature DB >> 22559142 |
Dominik R Laetsch1, Emanuel G Heitlinger, Horst Taraschewski, Steven A Nadler, Mark L Blaxter.
Abstract
BACKGROUND: Anguillicolidae Yamaguti, 1935 is a family of parasitic nematode infecting fresh-water eels of the genus Anguilla, comprising five species in the genera Anguillicola and Anguillicoloides. Anguillicoloides crassus is of particular importance, as it has recently spread from its endemic range in the Eastern Pacific to Europe and North America, where it poses a significant threat to new, naïve hosts such as the economic important eel species Anguilla anguilla and Anguilla rostrata. The Anguillicolidae are therefore all potentially invasive taxa, but the relationships of the described species remain unclear. Anguillicolidae is part of Spirurina, a diverse clade made up of only animal parasites, but placement of the family within Spirurina is based on limited data.Entities:
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Year: 2012 PMID: 22559142 PMCID: PMC3503875 DOI: 10.1186/1471-2148-12-60
Source DB: PubMed Journal: BMC Evol Biol ISSN: 1471-2148 Impact factor: 3.260
Anguillicolidae sequences
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| 56 | 1 | 867 | 46.94 | 54 | 2 | 653 663 | 51.43 52.22 | 49 | 29 | 550 | 30.55 - 31.64 | |
| 33 | 1 | 867 | 47.06 | 35 | 4 | 651 663 | 51.89 52.53 | 22 | 13 | 550 | 30.55 - 34.91 | |
| 15 | 1 | 867 | 47.06 | 18 | 1 | 663 | 51.9 | 15 | 10 | 550 | 30.55 - 31.27 | |
| 10 | 1 | 867 | 47.17 | 10 | 1 | 663 | 52.04 | 9 | 1 | 550 | 34.73 | |
| 6 | 1 | 867 | 47.47 | 6 | 1 | 651 | 51.31 | 1 | 1 | 550 | 32.73 | |
| Total | 120 | 5 | - | - | 133 | 9 | - | - | 96 | 54 | - | - |
Data collected for three genes (nSSU 5': the 5' one third of the nuclear small subunit ribosomal RNA gene; nLSU D2-D3: the D2-D3 region of the nuclear large subunit ribosomal RNA gene; COX1: the 5' half of the mitochondrial cytochrome oxidase 1 gene) for each of the five species of Anguillicolidae. #: successfully sequenced fragments, h: the number of unique sequences found, L: the length (in bp) of the fragments, GC (%): the GC-content (in case of multiple sequences a range is given).
Location of sampling sites
| | | | | ||
| AQT | Townsville, Queensland (Australia) | 19°18'S | 146°44'E | BS 2007 | |
| AQB | Brisbane, Queensland (Australia) | 27°38'S | 153°12'E | BS 2007 | |
| ATD | Deloraine, Tasmania (Australia) | 41°31'S | 146°39'E | LP 2008 | |
| CGG | Guangzhou, Guangdong (China) | 23°07'N | 113°15'E | HT 03/07 | |
| CGZ | Zhuhai, Guangdong (China) | 22°16'N | 113°34'E | HT 03/07 | |
| EAV | Albufera de Valencia (Spain) | 39°21'N | 0°20'W | PMR 01/09 | |
| GST | Steinfeld (Germany) | 49°02'N | 8°02'E | AK 2009 | |
| GRA | Rußheimer Altrhein (Germany) | 49°12'N | 8°25'E | EH, UW 2009 | |
| JPN | Natural water system, Wakayama (Japan) | 34°13'N | 135°10'E | HS 2006 2007 | |
| MAD | Ambatondrazaka (Madagascar) *** | 17°83'S | 48°41'E | OW 05/2008 | |
| POL | Sniardwy Lake, Mikolajki (Poland) | 53°45'N | 21°43'E | UW 2009 | |
| POR | Ribeira das Lampreias (Portugal) | 38°47'N | 9°01'W | JLC 03/09 | |
| SFH | Farm Dam, Fort Hare (South Africa) | 32°47'S | 26°50'E | HT 03/08 | |
| SKR | Koonap River (South Africa) | 32°1'S | 26°08'E | HT 03/08 | |
| SSD | Sunday’s River, Slagboom Dam (South Africa) | 33°22'S | 25°40'E | HT 03/08 | |
| SDD | Sunday’s River, Darlington Dam (South Africa) | 33°12'S | 25°8'E | HT 03/08 | |
| SGF | Great Fish River (South Africa) | 33°05'S | 26°46'E | HT 03/08 | |
| SNR | Nahoon River (South Africa) | 32°54'S | 27°48'E | HT 03/08 | |
| TUR | Asi River, Hatay (Turkey) | 36°24'N | 36°21'E | EG 12/08 | |
| TKR | Sinyuan, Kaoping River (Taiwan) | 22°30'N | 120°25'E | HT 9/06 | |
| TCU | Eel culturing pond, Budai, (Taiwan) | 22°38'N | 120°26'E | HT 9/06 |
Sampling locations for the nematodes including label prefix, information on geographic position (latitude and longitude), host species and information about sampling.
* Collectors are identified by their initials: AK: Albert Keim, BS: Björn Schäffner, EH: Emanuel Heitlinger, EG: Ercüment Genç, HT: Horst Taraschewski, JLC: José Lino Costa, LP: Lea Perseke, OW: Olaf Weyl, PMR: Pilar Muñoz Ruíz, KG: Kerstin Geiss and HS: Hiroshi Sato.
** Month (where known) and year(s).
*** A. papernai were obtained from An. mossambica that were purchased from a commercial eel supplier. According to the supplier, all eels originate from tributaries of the Mangory River. The exact localities of capture, holding conditions and periods prior to collection are however unknown.
Figure 1MOTU analysis of three marker loci from Anguillicolidaea. Variation in the number of MOTUs inferred at cut-offs ranging from 0 - 14% sequence divergence for specimens for which all three genes were sequenced (nSSU*, nLSU*, COX1*). Results of the MOTU analysis of the expanded COX1 dataset are included for comparison. Critical cutoff intervals for the different datasets are indicated in letters (A – E). b. Comparison of morphological species identified sensu Moravec and Taraschewski [2] with MOTU composition at the critical cutoff intervals (A – E).
Figure 2Phylogenetic analysis of nSSU sequences of Spirurina. Consensus phylogram of the analysis of the nSSU sequences from Spirurina using Bayesian Inference, rooted with Teratocephalus lirellus, a non-spirurine rhabditid. Branches are collapsed where possible based on taxonomic affiliations and major groups are highlighted. Bayesian posterior probabilities for internal branches are indicated. The scale bar indicates the average expected number of substitutions per site.
Figure 3Phylogenetic analysis of nSSU sequences of Spirurina B. Consensus phylogram of the analysis of the nSSU sequences from Spirurina B using Bayesian Inference, rooted with Cucullanus robustus (Spirurina A). Bayesian posterior probabilities for internal branches are indicated. The scale bar indicates the average expected number of substitutions per site.
Figure 4Phylogenetic analysis of nLSU sequences of Anguillicolidae. Consensus phylogram of the analysis of the nLSU sequences from Anguillicolidae and outgroups using Bayesian Inference. Bayesian posterior probabilities for internal branches are indicated. The scale bar indicates the inferred number of base substitutions per site.
Figure 5Phylogenetic analysis of COX1 sequences of Anguillicolidae. Consensus phylogram of the analysis of the COX1 sequences from Anguillicolidae and outgroups using Bayesian Inference. Bayesian posterior probabilities for internal branches are indicated. The scale bar indicates the average expected number of substitutions per site.
Figure 6Network analysis of COX1 sequences from Statistical parsimony network of 70 distinct A. crassus COX1 sequences. The three COX1 haplotypes containing four specimens that have the minority A. crassus 28 S rDNA D2-D3 haplotype are highlighted. A list of all specimens associated with each COX1 haplotype can be found in the Additional file 1.
Figure 7Host switching in the Anguillicolidae. Cladograms of the eel genus Anguilla (left tree, blue) [60] and its swim bladder parasites, the family Anguillicolidae (Nematoda: Anguillicoloidea) (right tree, green). The known host parasite relationships are indicated by: black lines = traditional host-parasite relationship, displaying low abundances and low pathogenicity (parasite endemic in host); red lines = novel host-parasite relationship, displaying high abundances and pathogenicity; orange lines = novel host-parasite relationship, displaying low abundances and pathogenicity; dashed orange lines = novel host-parasite relationship where completion of the life cycle has not been demonstrated.
Population designations for population structure analyses with COX1
| North-Eastern Europe | ALA | Åland Islands (Finland) | 16 | [ |
| North-Eastern Europe | OER | Kullen, Øresund/Kattegat (Sweden) | 30 | [ |
| North-Eastern Europe | COR | Slapton Ley, Cornwall (Great Britain) | 15 | [ |
| North-Eastern Europe | NEA | Lake Neagh (Great Britain) | 31 | [ |
| North-Eastern Europe | SHA | Lough Dergh, Shannon (Ireland) | 30 | [ |
| North-Eastern Europe | GRA | Rußheimer Altrhein (Germany) | 4 | * |
| North-Eastern Europe | GST | Steinfeld (Germany) | 1 | * |
| North-Eastern Europe | POL | Sniardwy Lake, Mikolajki (Poland) | 5 | * |
| North-Eastern Europe | C | Essen (Germany) | 3 | ** |
| Brittany | FRE | Bois Joli, Frémur (France) | 31 | [ |
| Brittany | VIL | Brain-sur-Vilaine (France) | 30 | [ |
| South-West Europe | LOI | Angers, Loire (France) | 32 | [ |
| South-West Europe | RHO | Camargue, Rhône (France) | 30 | [ |
| South-West Europe | ORI | Oria (Spain) | 30 | [ |
| South-West Europe | EAV | Albufera de Valencia (Spain) | 3 | * |
| South-West Europe | POR | Ribeira das Lampreias (Portugal) | 1 | * |
| South-West Europe | TIB | Roma, Tiber (Italy) | 30 | [ |
| South-West Europe | LB | Lake Bracchiano (Italy) | 10 | ** |
| Turkey | TUR | Asi River, Hatay (Turkey) | 4 | * |
| USA | STJ | St. Jones River (New Jersey, USA) | 32 | [ |
| Taiwan | KAO | Tung-Chiang, Kao-Ping River (Taiwan) | 46 | [ |
| Taiwan | TKR | Sinyuan, Kaoping River (Taiwan) | 4 | * |
| Taiwan | TCU | Eel culturing pond, Budai, (Taiwan) | 5 | * |
| China (Zhuhai) | CGZ | Zhuhai, Guangdong (China) | 14 | * |
| China (Guangzhou) | CGG | Guangzhou, Guangdong (China) | 2 | * |
| Japan (Mikawa) | MIK | Mikawa Bay (Japan) | 29 | [ |
| Japan (Yamaguchi) | YAM | Yamaguchi, Fushino (Japan) | 7 | [ |
| Japan (Wakayama) | JPN | Natural water system, Wakayama (Japan) | 5 | * |
* This work.
** Geiß, K. and B. Sures (2010). The swim bladder nematode A. novaezelandiae. Proceedings of the Joint Meeting of the German Societies of Parasitology and Protozoology, Düsseldorf, Germany.