Tylenchidae is a widely distributed soil-inhabiting nematode family characterized by a weak stylet, an undifferentiated non-muscular pharyngeal corpus, and a filiform tail. Currently, it comprises 412 nominal species belongs to 44 genera and estimated species number ranged from 2,000 to 10,000 species (Qing and Bert, 2019). Regardless of their abundance, the delimitation of taxa in this group remains poorly documented and highly uncertain. Consequently, there is no consensus regarding their classification from species level up to family level (Andrássy, 2007; Brzeski, 1998; Qing and Bert, 2019; Siddiqi, 2000).
With the improved availability of genetic sequencing, molecular sequences in species diagnosis and phylogeny analysis have consolidated them as one of the most powerful tools in current taxonomy. Among marker genes, the ribosomal RNA (rRNA) genes are being used as the standard barcode for almost all animals and successfully resolved several groups in Nematoda (Bert et al., 2008; Holterman et al., 2006; Subbotin et al., 2006). However, rRNA genes are problematic in Tylenchidae phylogeny and the unresolved status is unlikely to be improved by intensive species sampling (Qing et al., 2017; Qing and Bert, 2019). Therefore, finding a proper molecular marker gene is crucial for the Tylenchidae study. In this study we examined the mitochondrial Cytochrome Oxidase I gene (COI) of 12 species belong to Tylenchidae (sensu (Geraert, 2008)), the goal is to evaluate the potential of COI sequences for the identification of Tylenchidae species; and compare the resolution, sequences variability, and tree topologies obtained from one COI and two rRNA markers (i.e. 18S and the 28S rRNA).
Materials and methods
Samples collection and processing
Soil samples were collected in China from 2018 to 2019. The details on sampling locations and habitats were given in Table 1. The nematodes were extracted from soil samples by Baermann tray and subsequently collected by a 400 mesh sieve (37 μm opening) after 24 hr of incubation. For morphological analysis, the extracted nematodes were manually picked up, fixed with 4% formalin, rinsed several times with deionized water and then transferred to anhydrous glycerin, following the protocol of Seinhorst (1962) and Sohlenius and Sandor (1987).
Table 1.
List species examined in this study and their corresponding sampling locations.
| Species | GPS coordinates | Al. | Vegetation environment | |||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Labrys fujianensis | 26°04´52.9˝N,119°14´26.7˝E | 28 | Scrubland soil with ferns and bamboo | |||||||||||
| Labrys fuzhouensis | 26°08´57.6˝N,119°17´34.4˝E | 107 | Rhizosphere of Alpinia zerumbet | |||||||||||
| Coslenchus rafiqi | 26°05´08.2˝N,119°14´10.0˝E | 27 | Swamp soil | |||||||||||
| Coslenchus costatus | 26°05´00.9˝N, 119°14´32.6˝E | 25 | Rhizosphere soil of bamboo | |||||||||||
| Boleodorus thylactus | 26°08´57.6˝N,119°17´34.4˝E | 107 | Rhizosphere soil of Alpinia zerumbet | |||||||||||
| Aglenchus geraerti | 26°09´09.2˝N,119°17´35.7˝E | 88 | Rhizosphere soil of grass near the bamboo | |||||||||||
| Basiria aberrans | 26°09´56.3˝N,117°55´34.2˝E | 644 | Rhizosphere soil of peanut | |||||||||||
| Filenchus vulgaris | 26°05´00.9˝N,119°14´32.6˝E | 25. | Rhizosphere soil of bamboo | |||||||||||
| Lelenchus leptosoma 1 | 26°05´00.9˝N,119°14´32.6˝E | 25. | Rhizosphere soil of bamboo | |||||||||||
| Lelenchus leptosoma 2 | 26°08´57.3˝N,119°17´34.1˝E | 107 | Rhizosphere soil of Litchi chinensis | |||||||||||
| Malenchus bryanti | 43°48´53.1˝N,125°24´40.3˝E | 225 | Rhizosphere soil of aspen | |||||||||||
| Tylenchus arcuatus | 26°05´23.9˝N,119°14´00.3˝E | 12 | Rhizosphere soil of locust tree | |||||||||||
| Psilenchus hilarulus | 26°05´09.4˝N,119°13´50.2˝E | 7 | Rhizosphere soil of grass | |||||||||||
| Taxa | ||||||||||||||
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| Nucleotide composition | Tylenchidae | Criconematina | Hoplolaimina | |||||||||||
| GC | 28.72 | 22.54 | 29.42 | |||||||||||
| GC 1st | 39.80 | 28.07 | 38.82 | |||||||||||
| GC 2nd | 35.14 | 35.07 | 36.61 | |||||||||||
| GC 3rd | 11.23 | 4.48 | 12.84 | |||||||||||
| LFJ | LFZ | CR | AG | BA | BT | PH | CC | FV | LL1 | LL2 | MB | TA | LB | |
|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
| LFJ | 99.5 | |||||||||||||
| LFZ | 78.9 | 99.5 | ||||||||||||
| CR | 83.0 | 81.4 | 100 | |||||||||||
| AG | 83.2 | 81.3 | 99.8 | 99.5 | ||||||||||
| BA | 79.8 | 76.2 | 81.5 | 81.3 | 99.5 | |||||||||
| BT | 78.7 | 76.6 | 82.4 | 82.3 | 79.4 | 99.8 | ||||||||
| PH | 72.5 | 73.5 | 77. 8 | 77.7 | 73.2 | 77.2 | 100 | |||||||
| CC | 80.5 | 78.2 | 87.5 | 87.3 | 79.8 | 80.8 | 75.7 | 98.6 | ||||||
| FV | 82.4 | 79.5 | 83.3 | 83.2 | 80.9 | 82.5 | 76.3 | 82.4 | 100 | |||||
| LL1 | 76.8 | 76.8 | 81.0 | 81.1 | 71.7 | 73.9 | 70.8 | 77.6 | 75.1 | 96.0 | ||||
| LL2 | 79.2 | 81.2 | 84.4 | 84.2 | 75.5 | 79.0 | 75.1 | 82.8 | 80.1 | 86.9 | 97.7 | |||
| MB | 81.1 | 78.8 | 82.6 | 82.5 | 78.1 | 81.8 | 74.8 | 81.0 | 82.7 | 74.0 | 79.6 | 99.7 | ||
| TA | 82.4 | 79.2 | 88. 9 | 88.8 | 81.8 | 85.6 | 78.5 | 83.7 | 83.8 | 76.7 | 81.3 | 84.7 | 100 | |
| LB | 84.1 | 81.2 | 86.6 | 87.0 | 81.5 | 81.5 | 72.9 | 87.2 | 84.3 | 77.9 | 84.6 | 84.0 | 84.9 | 0 |






