Next Article in Journal
The Effectiveness of the Use of Ultrasound Methodology (Applied to Live Animals) to Assess the Quality of Meat
Previous Article in Journal
17α-Methyltestosterone Affected Growth, Gonadal Development, and Intestinal Microbial Analysis in the Giant Freshwater Prawn (Macrobrachium rosenbergii)
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

New Data on Rhinogobius chiengmaiensis and Rhinogobius mekongianus in Thailand by DNA Barcoding and Morphological Methods

by
Siriluck Tuncharoen
1,
Paiboon Panase
1,
Nontree Panprommin
2,
Eakapol Wangkahart
3,
Supranee Ruenkoed
4,
Keatipong Mongkolwit
4 and
Dutrudi Panprommin
1,*
1
School of Agriculture and Natural Resources, University of Phayao, Phayao 56000, Thailand
2
Department of Fisheries, Aquatic Plants and Ornamental Fish Research Institute, Bangkok 10900, Thailand
3
Faculty of Technology, Mahasarakham University, Mahasarakham 44150, Thailand
4
Advance Pharma Vietnam Co., Ltd., Ho Chi Minh City 10000, Vietnam
*
Author to whom correspondence should be addressed.
Animals 2025, 15(6), 871; https://doi.org/10.3390/ani15060871
Submission received: 5 February 2025 / Revised: 13 March 2025 / Accepted: 13 March 2025 / Published: 19 March 2025
(This article belongs to the Section Animal Genetics and Genomics)

Simple Summary

Morphology and DNA barcoding were utilized for the identification of two Rhinogobius species, R. chiengmaiensis and R. mekongianus, along with Eugnathogobius siamensis and Pseudogobiopsis oligactis for comparative analysis. Eleven samples were collected from natural habitats in Thailand. The collaboration between morphological analysis and DNA barcoding reveals the accuracy and precision in distinguishing these four gobiid species. Our research provides essential reference data to support the management of fishery resources, aquaculture practices, and conservation efforts.

Abstract

A combination of morphological analysis and DNA barcoding (partial sequences of the cytochrome c oxidase I (COI) gene) was used to differentiate four gobiid fish species in the family Oxudercidae. Rhinogobius chiengmaiensis and Rhinogobius mekongianus were found in Thailand, while Eugnathogobius siamensis and Pseudogobiopsis oligactis were used for comparative purposes. Morphological identification relied on appearances, counts, and measurements. The 707-base pair COI sequences from eleven samples of four gobiid species were compared with reference sequences in public databases to confirm their scientific names. The average AT content was 51.8 ± 0.5% and the GC content was 48.2 ± 0.5%. Intraspecific genetic distances ranged from 0.00–0.28%, while interspecific genetic distances ranged from 0.86–16.63%. A neighbor-joining (NJ) phylogenetic tree depicted the relationships among the COI sequences of these species. Morphological analysis and COI sequences successfully distinguished the four gobiid species. Notably, the COI sequences of R. chiengmaiensis, R. mekongianus, and E. siamensis were previously unreported, hence, this study is the first report to add their sequences to public databases. These results can serve as valuable information for the management of aquatic resources, conservation, and aquaculture efforts.

1. Introduction

The family Oxudercidae (or Gobionellidae) belongs to the order Gobiiformes, and comprises approximately 86 genera and 598 species that are found worldwide from freshwater to marine habitats [1]. Species in this family were previously classified in the subfamily Oxudercinae of the family Gobiidae according to their taxonomic arrangement, following Nelson [2]. Later, when the taxonomy of fish in this taxa was verified, it was revised that the subfamily Oxudercinae was separated from the family Gobiidae with the status of the family Oxudercidae [1]. One distinguishing feature of the family Oxudercidae, as compared to the family Gobiidae, is the presence of elongated and slender suspensoria structures [1,3].
Rhinogobius, a genus within the family Oxudercidae, contains the most species of freshwater gobies found in the lakes and streams across East and Southeast Asia, including Thailand [4,5,6]. Rhinogobius species exhibit characteristics that are commonly observed in gobies, such as their small body size, the fusion of their pelvic fins to form a disc-like structure on the ventral side, and an elongated and rounded body [7,8]. Moreover, this genus exhibits an elongated form of the head, characterized by a long snout. Presently, the genus Rhinogobius is recognized to encompass more than 80 distinct species, and ongoing taxonomic research is consistently discovering and documenting new species such as R. sangenloensis in Southern China [5], R. maxillivirgatus in Eastern China [9], R. yangminshanensis in Taiwan [10], and R. aonumai aonumai and R. aonumai ishigakiensis in Japan [11]. In addition, two new species, R. rong and R. nami, have recently been described from central Vietnam [12]. However, Panitvong [13] notes that only three Rhinogobius species are currently recognized in Thailand: R. chiengmaiensis, R. mekongianus, and R. giurinus.
Rhinogobius chiengmaiensis exhibits a broad distribution in the upper region of the Chao Phraya river, whereas R. mekongianus is found inhabiting the Mekong river basin [14]. In 2013, Panitvong [13] found R. giurinus within a stream located in Chiang Rai province, Northern Thailand. Nevertheless, there remains limited documentation of the presence of this species in Thailand. Therefore, this study focused on two species, R. chiengmaiensis, and R. mekongianus. Although these two species are found in different natural habitats, they share some similarities in appearance, such as small size, elongated body shape, and the pattern of colors. They are currently becoming popular as ornamental fish, causing the natural population trend to decrease, especially in the case of R. chiengmaiensis. The conservation statuses of R. chiengmaiensis and R. mekongianus were assessed by the International Union for Conservation of Nature (IUCN) as vulnerable (VU) and least concern (LC), respectively (as of February 2025). Hence, both morphological and molecular identification methods were required to distinguish between these two species.
The morphological identification of fish species involves the assessment of meristic and morphometric characteristics. Meanwhile, morphological identification, DNA barcoding, or the standard sequences of the cytochrome c oxidase I (COI) gene have been commonly employed for global species bioidentification [15], including the case of fishes [16,17,18,19,20]. Both morphological identification and DNA barcoding have distinct advantages and disadvantages. Morphological identification is typically conducted by experienced fish taxonomists, while DNA barcoding is employed for identifying fish species even in cases of incomplete samples such as fish fillets [21], or the various developmental stages such as the eggs [22] or larval stage [23]. Collaboration between morphological identification and DNA barcoding enhances the accuracy of fish species identification and contributes to the expansion of the COI gene sequences in public databases for further analysis.
The objective of this research was to differentiate between two species of the genus Rhinogobius, namely R. chiengmaiensis and R. mekongianus, through the application of both morphological identification and DNA barcoding techniques. Furthermore, the research also focused on studying two other species within the family Oxudercidae, namely Eugnathogobius siamensis and Pseudogobiopsis oligactis. These two species were analyzed in comparison to two species of the genus Rhinogobius. This research provided the first report of the COI sequences of R. chiengmaiensis, R. mekongianus, and E. siamensis. The COI sequences of all four species were expanded and deposited into the GenBank and BOLD databases to serve as reference sequences for aiding in the identification of unknown species and establishing a database for specifying of new species within the family Oxudercidae, especially the genus Rhinogobius.

2. Materials and Methods

2.1. Sample Collection

Seven live samples of two species belonging to the genus Rhinogobius, R. chiengmaiensis and R. mekongianus were obtained using swings in September 2024 from collectors of fish from nature with known sources (Figure 1 and Table 1). In addition, four samples of two other species of the family Oxudercidae, E. siamensis and P. oligactis, were also received. All samples were photographed and anesthetized with 0.2 g/L of MS-222 (Sigma, St. Louis, MO, USA) solution. Whole samples were preserved in absolute ethanol at room temperature for morphological identification. This animal use protocol has been approved by the Institutional Animal Care and Use Committee, University of Phayao (No. UP-AE 1-011-67).

2.2. Morphological Identification

After 2–3 min of immersion in ethanol, all samples were immediately identified based on morphological appearances, including body shape, mouth and eye size. Counts and measurements following the Nagao Natural Environment Foundation’s criteria [24] were performed on the left side of the samples. Fin rays were counted for the dorsal, pectoral, pelvic, and anal fins. The longitudinal, predorsal, and circumcaudal scales were also recorded. Measurements were taken point to point with digital vernier calipers to the nearest 0.01 mm. Subunits of the head were presented as proportions of head length (HL). Measurements of head and body parts were provided as proportions of standard length (SL).

2.3. Molecular Identification

After morphological identification, a small piece of right pectoral fin from each sample was used for the extraction of the genomic DNA using the GF-1 Nucleic Acid Extraction kit (Vivantis Technologies Sdn. Bhd., Selangor Darul Ehsan, MA, USA). The quantity and quality of the extracted DNA was determined using a NanoDrop Microvolume Spectrophotometer (Thermo Fisher Scientific Inc., Waltham, MA, USA) and 1.2% agarose gel electrophoresis at 100 V for 30 min, respectively.
A 707 bp fragment of the COI gene was amplified for each sample using the equal volume of each 10 µM primer, namely FishF1 (5′-TCAACCAACCACAAAGACATTGGCAC-3′), FishF2 (5′-TCGACTAATCATAAAGATATCGGCAC-3′), FishR1 (5′-TAGACTTCTGGGTGGCCAAAGAATCA-3′), and FishR2 (5′-ACTTCAGGGTGACCGAAGAATCAGAA-3′) [20], with the PCR technique. Each PCR reaction mixture included of 1 µL of extracted DNA (approximately 100 ng/µL), 2.25 µL of 10× Taq buffer, 0.8 µL of 50 mM MgCl2, 1 µL of 2.5 mM dNTP mix, 1 µL of 10 µM mixed primers, 0.2 µL of 1 U Taq DNA polymerase (BIO-HELIX Co., Ltd., New Taipei City, Taiwan), and nuclease-free water to 25 µL. The thermal cycling conditions included an initial denaturation at 95 °C for 2 min followed by 35 cycles of denaturation at 94 °C for 30 s, annealing at 54 °C for 30 s, and extension at 72 °C for 1 min, with a final extension at 72 °C for 10 min. The PCR products were analyzed using 1.2% agarose gel electrophoresis stained with Novel Juice (BIO-HELIX Co., Ltd., New Taipei City, Taiwan). The target bands were then purified to remove unwanted reagents using the HiYield™ Gel/PCR DNA Fragments Extraction kit (RBC Bioscience Corp., New Taipei City, Taiwan), following the manufacturer’s instructions.
The purified PCR products were sequenced bidirectionally at ATGC Co., Ltd. (Pathum Thani, Thailand) using primer FishF1/FishF2 for the 3′ end and FishR1/FishR2 for the 5′ end. Two sequences of each sample were aligned and assembled using the Clustal Omega program [25] version 1.2.4. All sequences covering the primer sequences were searched for the stop codon, deletion, and insertion using the Open Reading Frame Finder website (ORF finder; https://www.ncbi.nlm.nih.gov/orffinder/, accessed on 12 October 2024). The scientific name of each sample was investigated by comparing its sequence with reference sequences in two public databases, namely the GenBank (https://www.ncbi.nlm.nih.gov/, accessed on 12 October 2024) using the Basic Local Alignment Search Tool (BLAST) program [26] and BOLD (https://boldsystems.org/, accessed on 12 October 2024). Each sample was assigned a scientific name based on the top match with a minimum of 99% sequence similarity.
The percentage of base composition of the four gobiid species was calculated using the MEGA11 program [27]. The intraspecific and interspecific genetic distances were calculated using the MEGA11 program with the Kimura-2-parameter (K2P) distance model [28]. Because the COI sequences of R. chiengmaiensis, R. mekongianus, and E. siamensis have not been reported in any databases, several sequences of other fish species of the genus Rhinogobius and P. oligactis were downloaded from GenBank and BOLD databases for construction of a neighbor-joining (NJ) tree [29] to analyze their evolutionary relationship. The tree was generated using the MEGA11 program with 1000 bootstrap replications, using nucleotide sequences of equal length. A COI sequence from Oxyeleotris marmorata, a member of the family Butidae, was used as an outgroup.

3. Results

3.1. Morphological Identification

Although these two species of the genus Rhinogobius showed very similar characteristics, their appearances were clearly different (Table 2), including two other members of the family Oxudercidae, E. siamensis and P. oligactis. A short description of the four gobiid species examined in this study is provided below.
Rhinogobius chiengmaiensis Fowler, 1934
D1. vi–vii; D2. i,7–8; P1. i,14; P2. 12 (total); A. i,6–7; C. branched 10
First dorsal fin with 6–7 single rays; i,7-8 second dorsal fin: i,14 pectoral fin rays: 12 (total) pelvic fin rays: i,6-7 anal fin rays: 10 caudal branched rays; ctenoid scale; longitudinal scales 29–30; predorsal scales 3–4; circumcaudal scales 12; body elongate, moderate slender (15.85 ± 0.31%SL); pelvic fins origin slightly in front of opercula margin (29.71 ± 2.56 vs. 31.82 ± 1.67%SL); pelvic fins length 19.37 ± 1.15%SL; mouth moderate large (35.50 ± 3.86%HL), maxillary extending to middle of eyes; eyes diameter 20.16 ± 1.39%HL.
Rhinogobius mekongianus (Pellegrin & Fang, 1940)
D1. vi; D2. i,7-8; P1. i,14; P2. 12 (total); A. i,6-7; C. branched 10
First dorsal fin with 6–7 single rays; i,7-8 second dorsal fin: i,14 pectoral fin rays: 10 (total) pelvic fin rays: i,6 anal fin rays: 12 caudal branched rays; ctenoid scale; longitudinal scales 29–30; predorsal scales 3–4; circumcaudal scales 12; body elongate, very slender (13.28 ± 0.54%SL); pelvic fins origin slightly in front of opercula margin (29.33 ± 0.18 vs. 30.50 ± 0.38%SL); pelvic fins length 17.88 ± 1.17%SL; mouth moderate large (39.19 ± 2.06%HL), maxillary extending to middle of eyes; eyes diameter 19.74 ± 0.57%HL.
Eugnathogobius siamensis (Fowler, 1934)
D1. vi; D2. i,6-7; P1. i,16-18; P2. 10 (total); A. i,6; C. branched 12-14
First dorsal fin with 6 single rays; i,6-7 second dorsal fin: i,16-18 pectoral fin rays: 10 (total) pelvic fin rays: i,6 anal fin rays: 12-14 caudal branched rays; large ctenoid scale; longitudinal scales 24; predorsal scales 7; circumcaudal scales 12; body elongate, moderate slender (18.08 ± 2.29%SL); pelvic fins origin slightly behind opercula margin (33.31 ± 1.54 vs. 32.60 ± 1.24%SL); pelvic fins length 24.85 ± 0.35%SL; caudal fin length 22.61 ± 3.17%SL; mouth large (48.33 ± 12.41%HL), maxillary extending well beyond posterior margin of eyes in male and extending to middle of eyes in female; small eyes, diameter 13.16 ± 0.72%HL.
Pseudogobiopsis oligactis (Bleeker, 1875)
D1. vi; D2. i,6-7; P1. i,14; P2. 12-14 (total); A. i,7-8; C. branched 12-14
First dorsal fin with 6 single rays; i,6-7 second dorsal fin: i,14 pectoral fin rays: 12-14 (total) pelvic fin rays: i,7-8 anal fin rays: 12-14 caudal branched rays; large ctenoid scale; longitudinal scales 24–25; predorsal scales 7; circumcaudal scales 10; body elongate, moderate slender (15.88 ± 0.51%SL); pelvic fins origin slightly behind opercula margin (36.06 ± 0.37 vs. 35.86 ± 3.28%SL); pelvic fins length 22.75 ± 0.36%SL; mouth large (63.24 ± 0.80%HL), maxillary extending well beyond posterior margin of eyes; small eyes, diameter 12.63 ± 0.19%HL. The diagnostic key to all four gobiid species in this study was provided as follows:
Diagnostic key to species of four gobiid in this study
1aLarge ctenoid scales; longitudinal scales 24–25; predorsal scales 7; pelvic fins origin slightly behind the opercular margin2
1bModerate ctenoid scales; longitudinal scales 29–30; predorsal scales 3–4; pelvic fins origin slightly behind the opercular margin 3
2aLarge head, head length 35.86 ± 3.28%SL, head width 62.30 ± 3.15%HL; large mouth (63.24 ± 0.80%HL), maxillary extending well beyond the posterior margin of the eyes; pelvic fin length 22.75 ± 0.36%SLPseudogobiopsis oligactis
2bSmall head, head length 32.60 ± 1.24%SL, head width 55.61 ± 3.85%HL; moderately large mouth (48.33 ± 12.41%HL), maxillary extending from the middle of the eyes to well beyond the posterior margin of the eyes; pelvic fin length 24.85 ± 0.35%SL Eugnathogobius siamensis
3aModerately large mouth, maxillary extending to the middle of the eyes (35.50 ± 3.86%HL); moderately slender body, body depth at pelvic fin origin 15.85 ± 0.31%SL; pelvic fin length 19.37 ± 1.15%SL; caudal fin length 24.77 ± 0.54%SL Rhinogobius chiengmaiensis
3bModerately large mouth, maxillary extending to the middle of the eyes (39.19 ± 2.06%HL); very slender body, body depth at pelvic fin origin 13.28 ± 0.54%SL; pelvic fin length 17.88 ± 1.17%SL; caudal fin length 27.34 ± 2.28%SL Rhinogobius mekongianus

3.2. Molecular Identification

The 707 bp fragments of the COI gene were successfully amplified from all samples using the PCR technique. The 235 amino acid residues were translated without stop codon, deletion, or insertion for any sequences. From sequence alignment, two sequences of R. chiengmaiensis showed 100% similarity (1 haplotype). While five sequences of R. mekongianus showed 99.4% similarity (4 haplotypes), four bases were different. Two COI sequences of R. chiengmaiensis and five COI sequences of R. mekongianus were compared to reference sequences in GenBank, showing the highest similarity to Rhinogobius virgigena at 95.85% and 95.44–95.72%, respectively, with 99% query coverage. Similarly, these sequences exhibited the highest similarity to R. virgigena in the BOLD database, with an identity of 96.22% for R. chiengmaiensis and 95.91–96.22% for R. mekongianus (Table 3).
The COI sequences of E. siamensis and P. oligactis demonstrated complete similarity, with each species showing a haplotype. Sixteen bases were different from each species. For comparison with the reference sequences in the GenBank, two COI sequences of E. siamensis showed the highest similarity to P. oligactis at 98.14% with 99% query coverage. Similarly, two COI sequences of P. oligactis showed the highest similarity to P. oligactis at 99.29% with 100% query coverage. Based on the BOLD database, two sequences of each species showed the highest similarity to P. oligactis at 98.93% and 99.85% identities, respectively (Table 3).
The average base compositions of eleven COI sequences were T (29.0 ± 1.3%), C (28.6 ± 0.1%), A (22.9 ± 0.9%), and G (19.5 ± 0.5%), as shown in Table 4. The GC content was 48.2 ± 0.5% at all sites, while the AT content was 51.8 ± 0.5%. Pseudogobiopsis oligactis presented the highest GC content (49.1 ± 0.0%), while R. mekongianus had the lowest (47.8 ± 0.1%).
The intraspecific genetic distances were 0.00% for R. chiengmaiensis, E. siamensis and P. oligactis, and 0.28% for R. mekongianus (Table 5), while the average intraspecific distance was 0.07%. In contrast, the interspecific genetic distances ranged from 0.86–16.63%. The lowest distance was between R. chiengmaiensis and R. mekongianus (0.86%). The highest distances were between R. chiengmaiensis and P. oligactis (16.63%) and R. chiengmaiensis and E. siamensis (15.38%), followed by R. mekongianus and P. oligactis (12.00%) and R. mekongianus and E. siamensis (11.02%), respectively. Meanwhile, the distance between P. oligactis and E. siamensis was 1.64%. The average interspecific distance was 9.59%. Thus, the interspecific genetic distance was 137-fold greater than the intraspecific genetic distance.
The NJ phylogenetic tree presented the relationship between the COI sequences of the four gobiid species of this study and other species retrieved from the GenBank and BOLD databases (Figure 2). Two major clades were clearly delineated, one comprising Rhinogobius species and the other including E. siamensis and P. oligactis, family Oxudercidae. Within these groups, R. chiengmaiensis showed the greatest similarity to R. mekongianus, while E. siamensis and P. oligactis clustered together. Additionally, the COI sequence of O. marmorata, family Butidae, was distinctly separated from the other sequences.

4. Discussion

The morphometric characters of R. chiengmaiensis and R. mekongianus provided in this study aligned with findings from previous research [4,14,30,31]. Rhinogobius chiengmaiensis and R. mekongianus exhibited quite similar appearances; however, they differed in certain characteristics such as the number of rays in the pelvic fin, anal fin, and caudal branch, as well as the diameter of the eyes. Additionally, a notable distinguishing characteristic was the body shape, with R. mekongianus being more slender compared to R. chiengmaiensis.
The concise characterizations of E. siamensis and P. oligactis presented in this study were also consistent with the descriptions provided in previous research [32,33]. Considerable confusion has arisen in accurately distinguishing between these two gobiid fish species due to their similar appearances, particular the coloration of their head and body [24] and greatly enlarged jaws [34]. In addition, these two species have been greatly confused, as evidenced by their synonyms being swapped between genera in FishBase, a global fish species database (https://www.fishbase.se/, accessed on 31 October 2024). At one time, the invalid names Pseudogobiopsis siamensis and Eugnathogobius oligactis were used for E. siamensis and P. oligactis, respectively. In 2009, Larson [32] conducted a review of the gobiid fish genera Eugnathogobius and Pseudogobiopsis, which significantly enhanced the ability to distinguish between these two species.
To accurately identify these four gobiid species, which exhibit highly similar external characteristics, it is essential to employ molecular data and DNA barcoding, alongside traditional taxonomic methods. This integrative approach ensures precise identification of these closely related fish species. Xia et al. [9] examined the COI sequences of the newly discovered species R. maxillivirgatus, revealing that it is closely related to its nearest species, R. wuyanlingensis, while still being distinct. In addition, the 707 bp fragments of the COI gene, which include primer sequences in this study, did not compromise comparability with previous studies that utilized a 655 bp fragment, as the same primers were employed for fish species identification.
Due to low identity percentages, the COI sequences of two fish species belonging to the genus Rhinogobius in Thailand have not yet been reported in any databases. Thus, this study was the first investigation to report the COI sequences of R. chiengmaiensis and R. mekongianus. Additionally, the COI sequences of E. siamensis have also been initially provided. A search in the Data Portal (https://portal.boldsystems.org/, accessed on 26 February 2025) of the BOLD database for these three fish species also confirmed that no records had been reported previously. A total of eleven COI sequences were deposited in the GenBank database with accession numbers PQ193904-PQ193914 (Table 1).
The average AT content (51.8 ± 0.5%) was greater than the average GC content (48.2 ± 0.5%) due to the average T being the highest in the base composition of eleven sequences, followed by C and A, respectively. The highest average thymine base composition was exhibited in several fishes including freshwater fishes of Bangladesh [16], marine and coastal fishes of Bangladesh [17], fish species in the Taiwan Strait [18], four fish species in the family Notopteridae [19], and Wallago attu [35]. Furthermore, the average G content was the lowest, representing a clear pattern of anti-G bias [16,17].
This study confirmed that the COI sequences were effective for distinguishing the four gobiid species based on genetic distance analysis. The average intraspecific genetic distances were low (0.00–0.28%), while the average interspecific genetic distances were significantly higher (0.86–16.63%). Generally, the intraspecific genetic distances based on the COI gene for animal species are usually less than 2% [36], including fishes [20]. These findings aligned with previous studies on fish species in the Taiwan Strait [18], four fish species in the family Notopteridae [19], and Cyprinidae fish in the midstream of the Yangtze river [37]. The average interspecific genetic distance was 137 times higher than the average intraspecific genetic distance. Hebert et al. [38] suggested that a 10-fold COI sequence difference between the average interspecific and intraspecific differences serve as a criterion for animal species differences. However, the small sample size in this study was one of its limitations.
The evolutionary relationship of the COI sequences among the four fish species and the other species is shown in Figure 2, according to the fish taxonomy of Nelson et al. [1]. The species in the family Oxudercidae, which consisted of Rhinogobius spp., E. siamensis, and P. oligactis, were clearly separated from O. marmorata, that belongs to the family Butidae. One major clade was the Rhinogobius species. The COI sequences of R. chiengmaiensis and R. mekongianus were the closest species, which agreed with their morphological identification, followed by R. virgigena and other Rhinogobius species. The second clade comprised E. siamensis and P. oligactis, indicating a close evolutionary relationship between these two species. The genera Eugnathogobius and Pseudogobiopsis were categorized as a part of the Mugilogobius lineage, whereas the genus Rhinogobius was classified to the Acanthogobius lineage, for which the phylogenetic analysis was similar to studies conducted by Agorreta et al. [39].
At present, these four gobiid species are increasingly popular as ornamental fish. They are often collected from the wild, which may lead to a decline in their natural populations. Furthermore, the IUCN has assessed one species, R. chiengmaiensis, as vulnerable (VU), indicating that this species is at considerable risk of becoming endangered in its natural habitat unless effective conservation measures are implemented [40]. The remaining species were assessed as least concern (LC). Therefore, promoting the commercial breeding of these fish can resolve this problem. A few research studies have been conducted on the breeding of these four gobiid fish species, including R. chiengmaiensis [41]. However, these fish have very similar appearances, making accurate species identification necessary before breeding. Furthermore, the results of this study will contribute to species identification and serve as information for future research on new fish species in the genus Rhinogobius.

5. Conclusions

The species R. chiengmaiensis and R. mekongianus have been identified through both morphological and molecular methods. Additionally, E. siamensis and P. oligactis, members of the family Oxudercidae, were also identified. The morphology of the four gobiid species exhibited distinctive characteristics, although some species displayed considerable similarity. For molecular identification, DNA barcoding proves to be an effective approach for distinguishing between these four species, considering both intraspecific and interspecific genetic distances as well as phylogenetic analysis. Moreover, this study is the first to report the COI sequences for R. chiengmaiensis, R. mekongianus, and E. siamensis. These findings can enhance selective breeding by providing molecular marker for species identification and diversity assessment. Additionally, the COI sequences of the four gobiid species serve as essential references for identifying new gobiid species.

Author Contributions

Conceptualization, S.T. and D.P.; methodology, S.T., N.P., and D.P.; software, S.T. and D.P.; validation, S.T. and D.P.; formal analysis, S.T., N.P., and D.P.; investigation, S.T., P.P., N.P., E.W., S.R., K.M., and D.P.; resources, S.T., N.P., and D.P.; data curation, S.T. and D.P.; writing—original draft preparation, S.T. and D.P.; writing—review and editing, S.T., P.P., N.P., E.W., S.R., K.M., and D.P.; visualization, S.T. and D.P.; supervision, D.P.; project administration, D.P.; funding acquisition, D.P. All authors have read and agreed to the published version of the manuscript.

Funding

This research was supported by the University of Phayao and Thailand Science Research and Innovation Fund (Fundamental Fund 2025, Grant No. 5051/2567).

Institutional Review Board Statement

This study was approved by the Institutional Animal Care and Use Committee, University of Phayao (No. UP-AE 1-011-67).

Informed Consent Statement

Not applicable.

Data Availability Statement

All sequences of the COI gene have been deposited under GenBank accession numbers PQ193904-PQ193914.

Acknowledgments

We are grateful to Chitnarong Sirisathitkul and Yaowarat Sirisathitkul for their suggestions on this manuscript. Additionally, we would like to thank Kanokwan Timkon, Auttpon Timkon, and Ketjarin Kheawnil for providing some samples.

Conflicts of Interest

Authors Supranee Ruenkoed and Keatipong Mongkolwit were employed by the company Advance Pharma Vietnam Co., Ltd. The remaining authors declare that the research was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.

References

  1. Nelson, J.S.; Grande, T.C.; Wilson, M.V.H. Fishes of the World, 5th ed.; John Wiley & Sons, Inc.: Hoboken, NJ, USA, 2016. [Google Scholar]
  2. Nelson, J.S. Fishes of the World, 4th ed.; John Wiley & Sons, Inc.: Hoboken, NJ, USA, 2006. [Google Scholar]
  3. Thacker, C.E. Phylogenetic placement of the European sand gobies in Gobionellidae and characterization of gobionellid lineages (Gobiiformes: Gobioidei). Zootaxa 2013, 3619, 369–382. [Google Scholar] [CrossRef]
  4. Chen, I.S.; Kottelat, M.; Miller, P.J. Freshwater gobies of the genus Rhinogobius from the Mekong basin in Thailand and Laos, with descriptions of three new species. Zool. Stud. 1999, 38, 19–32. [Google Scholar]
  5. Chen, I.S.; Miller, P.J. A new freshwater goby of Rhinogobius (Teleostei: Gobiidae) from Hainan Island, southern China. J. Mar. Sci. Technol. 2013, 21, 124–129. [Google Scholar]
  6. Kottelat, M. Zoogeography of the fishes from Indochinese inland waters with an annotated check-list. Bull. Zool. Mus. Univ. Amst. 1989, 12, 1–55. [Google Scholar]
  7. McCraney, W.T.; Thacker, C.E.; Alfaro, M.E. Supermatrix phylogeny resolves goby lineages and reveals unstable root of Gobiaria. Mol. Phylogenet. Evol. 2020, 151, 106862. [Google Scholar] [CrossRef]
  8. Thacker, C.E.; Roje, D.M. Phylogeny of Gobiidae and identification of gobiid lineages. Syst. Biodivers. 2011, 9, 329–347. [Google Scholar] [CrossRef]
  9. Xia, J.H.; Wu, H.L.; Li, C.H.; Wu, Y.Q.; Liu, S.H. A new species of Rhinogobius (Pisces: Gobiidae), with analyses of its DNA barcode. Zootaxa 2018, 4407, 553. [Google Scholar] [CrossRef]
  10. Chen, I.S.; Wang, S.C.; Shao, K.T. A new freshwater gobiid species of Rhinogobius Gill, 1859 (Teleostei: Gobiidae) from northern Taiwan. Zootaxa 2022, 5189, 29–44. [Google Scholar] [CrossRef]
  11. Suzuki, T.; Oseko, N.; Yamasaki, Y.Y.; Kimura, S.; Shibukawa, K. A new species with two new subspecies of Rhinogobius (Teleostei: Gobiidae) from Yaeyama Group, the Ryukyu Islands, Japan. Bull. Kanagawa Pref. Mus. (Nat. Sci.) 2022, 51, 9–34. [Google Scholar]
  12. Maeda, K.; Kobayashi, H.; Iida, M.; Tran, H.D. Taxonomy of freshwater gobies of the genus Rhinogobius (Oxudercidae, Gobiiformes) from central Vietnam, with descriptions of two new species. Zootaxa 2024, 5493, 507–541. [Google Scholar] [CrossRef]
  13. Panitvong, N. Freshwater Fishes of Thailand; Parbpim Ltd.: Bangkok, Thailand, 2020. [Google Scholar]
  14. Suvarnaraksha, A.; Utsugi, K. A Field Guild of the Northern Thai Fishes; Maejo University: Chiang Mai, Thailand; Nagao Natural Environment Foundation: Tokyo, Japan, 2023. [Google Scholar]
  15. Hebert, P.D.N.; Cywinska, A.; Ball, S.L.; deWaard, J.R. Biological identifications through DNA barcodes. Proc. R. Soc. Lond. B 2003, 270, 313–321. [Google Scholar] [CrossRef]
  16. Ahmed, M.S.; Datta, S.K.; Zhilik, A.A. Molecular diversity of freshwater fishes of Bangladesh assessed by DNA barcoding. Bangladesh J. Zool. 2020, 48, 1–19. [Google Scholar] [CrossRef]
  17. Ahmed, M.S.; Datta, S.K.; Saha, T.; Hossain, Z. Molecular characterization of marine and coastal fishes of Bangladesh through DNA barcodes. Ecol. Evol. 2021, 11, 3696–3709. [Google Scholar] [CrossRef]
  18. Bingpeng, X.; Heshan, L.; Zhilan, Z.; Chunguang, W.; Yanguo, W.; Jianjun, W. DNA barcoding for identification of fish species in the Taiwan Strait. PLoS ONE 2018, 13, e0198109. [Google Scholar] [CrossRef]
  19. Seetapan, K.; Panprommin, N.; Wangkahart, E.; Ruenkoed, S.; Panprommin, D. COI-high resolution melting analysis for discrimination of four fish species in the family Notopteridae in Thailand. Zool. Anz. 2024, 309, 90–97. [Google Scholar] [CrossRef]
  20. Ward, R.D.; Zemlak, T.S.; Innes, B.H.; Last, P.R.; Hebert, P.D.N. DNA barcoding Australia’s fish species. Philos. Trans. R. Soc. B 2005, 360, 1847–1857. [Google Scholar] [CrossRef]
  21. Panprommin, D.; Manosri, R. DNA barcoding as an approach for species traceability and labeling accuracy of fish fillet products in Thailand. Food Control 2022, 136, 108895. [Google Scholar] [CrossRef]
  22. Breitbart, M.; Kerr, M.; Schram, M.J.; Williams, I.; Koziol, G.; Peebles, E.; Stallings, C.D. Evaluation of DNA metabarcoding for identifying fish eggs: A case study on the West Florida Shelf. PeerJ 2023, 11, e15016. [Google Scholar] [CrossRef]
  23. Chen, W.; Li, C.; Li, X.; Li, J.; Li, Y. Unraveling the drifting larval fish community in a large spawning ground in the Middle Pearl River using DNA barcoding. Animals 2022, 12, 2555. [Google Scholar] [CrossRef]
  24. Nagao Natural Environment Foundation. Fishes of the Indochinese Mekong; Nagao Natural Environment Foundation: Tokyo, Japan, 2021. [Google Scholar]
  25. Sievers, F.; Higgins, D.G. Clustal Omega, accurate alignment of very large numbers of sequences. Methods Mol. Biol. 2014, 1079, 105–116. [Google Scholar]
  26. Altschul, S.F.; Gish, W.; Miller, W.; Myers, E.W.; Lipman, D.J. Basic local alignment search tool. J. Mol. Biol. 1990, 215, 403–410. [Google Scholar] [CrossRef]
  27. Tamura, K.; Stecher, G.; Kumar, S. MEGA11: Molecular evolutionary genetics analysis version 11. Mol. Biol. Evol. 2021, 38, 3022–3027. [Google Scholar] [CrossRef]
  28. Kimura, M. A simple method for estimating evolutionary rates of base substitutions through comparative studies of nucleotide sequences. J. Mol. Evol. 1980, 16, 111–120. [Google Scholar] [CrossRef]
  29. Saitou, N.; Nei, M. The neighbor-joining method: A new method for reconstructing phylogenetic trees. Mol. Biol. Evol. 1987, 4, 406–425. [Google Scholar]
  30. Chen, I.S.; Cheng, Y.H.; Shao, K.T. A new species of Rhinogobius (Teleostei: Gobiidae) from the Julongjiang Basin in Fujian Province, China. Ichthyol. Res. 2008, 55, 335–343. [Google Scholar] [CrossRef]
  31. Kottelat, M. Fishes of Laos; WHT Publications Ltd.: Colombo, Sri Lanka, 2001. [Google Scholar]
  32. Larson, H.K. Review of the gobiid fish genera Eugnathogobius and Pseudogobiopsis (Gobioidei: Gobiidae: Gobionellinae), with descriptions of three new species. Raffles Bull. Zool. 2009, 57, 127–181. [Google Scholar]
  33. Tan, H.H.; Lim, K.K.P. Rediscovery of the bigmouth stream goby, Pseudogobiopsis oligactis (Actinopterygii: Gobiiformes: Gobionellidae) in Singapore. Nat. Singap. 2011, 4, 363–367. [Google Scholar]
  34. Smith, H.M. The freshwater fishes of Siam, or Thailand. Bull. U.S. Natl. Mus. 1945, 188, 1–622. [Google Scholar]
  35. Sajjad, A.; Jabeen, F.; Ali, M.; Zafar, S. DNA barcoding and phylogenetics of Wallago attu using mitochondrial COI gene from the River Indus. J. King Saud Univ. Sci. 2023, 35, 102725. [Google Scholar] [CrossRef]
  36. Hebert, P.D.N.; Ratnasingham, S.; de Waard, J.R. Barcoding animal life: Cytochrome c oxidase subunit 1 divergences among closely related species. Proc. R. Soc. Lond. B 2003, 270 (Suppl. S1), S96–S99. [Google Scholar] [CrossRef]
  37. Shen, Y.; Guan, L.; Wang, D.; Gan, X. DNA barcoding and evaluation of genetic diversity in Cyprinidae fish in the midstream of the Yangtze River. Ecol. Evol. 2016, 6, 2702–2713. [Google Scholar] [CrossRef] [PubMed]
  38. Hebert, P.D.N.; Stoeckle, M.Y.; Zemlak, T.S.; Francis, C.M. Identification of birds through DNA barcodes. PLoS Biol. 2004, 2, e312. [Google Scholar] [CrossRef] [PubMed]
  39. Agorreta, A.; San Mauro, D.; Schliewen, U.; Van Tassell, J.L.; Kovačić, M.; Zardoya, R.; Rüber, L. Molecular phylogenetics of Gobioidei and phylogenetic placement of European gobies. Mol. Phylogenet. Evol. 2013, 69, 619–633. [Google Scholar] [CrossRef] [PubMed]
  40. International Union for Conservation of Nature. The IUCN Red List of Threatened Species. 2023. Available online: https://www.iucnredlist.org/ (accessed on 2 February 2025).
  41. Pornsopin, P.; Sirisuksa, T.; Kantiyawong, S.; Surajit, T. Study on Cultivation of Chiangmai Stream Goby (Rhinogobius Chiengmaiensis Fowler, 1934); Inland Aquaculture Research and Development Division: Bangkok, Thailand, 2022. [Google Scholar]
Figure 1. Rhinogobius chiengmaiensis (A) and Rhinogobius mekongianus (B).
Figure 1. Rhinogobius chiengmaiensis (A) and Rhinogobius mekongianus (B).
Animals 15 00871 g001
Figure 2. A neighbor-joining (NJ) tree was constructed using eleven COI nucleotide sequences from four gobiid species, highlighted in bold, in comparison with multiple sequences sourced from the GenBank and BOLD databases (GenBank and BOLD accession numbers). The bootstrap values are presented above the branches. A COI sequence of Oxyeleotris marmorata was designated as the outgroup species. The scale bar corresponds to the number of substitutions per site.
Figure 2. A neighbor-joining (NJ) tree was constructed using eleven COI nucleotide sequences from four gobiid species, highlighted in bold, in comparison with multiple sequences sourced from the GenBank and BOLD databases (GenBank and BOLD accession numbers). The bootstrap values are presented above the branches. A COI sequence of Oxyeleotris marmorata was designated as the outgroup species. The scale bar corresponds to the number of substitutions per site.
Animals 15 00871 g002
Table 1. Primary information about eleven COI sequences in this study.
Table 1. Primary information about eleven COI sequences in this study.
SpeciesGenBank Accession No.Sample SizeCollection Site
Rhinogobius chiengmaiensisPQ193904-PQ1939052Ping river basin, Chiang Mai province
Rhinogobius mekongianusPQ193906-PQ1939105Kok River, Chiang Mai province
Eugnathogobius siamensisPQ193911-PQ1939122Surat Thani province
Pseudogobiopsis oligactisPQ193913-PQ1939142Satun province
Table 2. Morphometry of R. chiengmaiensis, R. mekongianus, E. siamensis, and P. oligactis.
Table 2. Morphometry of R. chiengmaiensis, R. mekongianus, E. siamensis, and P. oligactis.
CharactersR. chiengmaiensisR. mekongianusE. siamensisP. oligactis
SL (mm)28.82 ± 0.5129.16 ± 2.9530.48 ± 2.9829.42 ± 3.68
As % of SL
Head length31.82 ± 1.6730.50 ± 0.3832.60 ± 1.2435.86 ± 3.28
Head width16.46 ± 3.0615.23 ± 1.9018.11 ± 0.5722.39 ± 3.17
Body depth at P215.85 ± 0.3113.28 ± 0.5418.08 ± 2.2915.88 ± 0.51
Body depth at A14.80 ± 0.2411.78 ± 0.3716.49 ± 1.9413.52 ± 0.72
Snout to D137.28 ± 1.5939.66 ± 2.0239.56 ± 3.0645.14 ± 1.75
Snout to D259.50 ± 2.5759.01 ± 3.4761.91 ± 2.2158.13 ± 0.89
Snout to A65.08 ± 1.8964.27 ± 0.3165.00 ± 1.7563.29 ± 2.38
Snout to P229.71 ± 2.5629.33 ± 0.1833.31 ± 1.5436.06 ± 0.37
D1 base length15.24 ± 2.4014.46 ± 1.1813.16 ± 0.138.84 ± 0.50
D1 base length20.62 ± 2.9417.39 ± 0.9816.95 ± 0.2916.31 ± 1.47
A base length14.19 ± 0.0113.72 ± 0.1715.85 ± 1.1613.31 ± 3.12
C length24.77 ± 0.5427.34 ± 2.2822.61 ± 3.17-
Caudal peduncle length20.60 ± 1.0319.72 ± 0.1520.53 ± 1.5213.95 ± 2.88
Caudal peduncle depth11.55 ± 0.389.62 ± 0.5411.38 ± 0.4410.56 ± 0.56
P1 length20.74 ± 6.9425.48 ± 1.8428.63 ± 0.5622.70 ± 0.37
P2 length19.37 ± 1.1517.88 ± 1.1724.85 ± 0.3522.75 ± 0.36
As % of HL
Snout length29.76 ± 1.4427.92 ± 2.7127.98 ± 0.7527.79 ± 0.01
Eye diameter20.16 ± 1.3919.74 ± 0.5713.16 ± 0.7212.63 ± 0.19
Postorbital length50.08 ± 0.0452.34 ± 2.1358.87 ± 0.0359.58 ± 0.17
Interorbital space21.93 ± 0.0116.35 ± 1.2219.13 ± 0.0319.99 ± 1.23
snout to maxilla35.50 ± 3.8639.19 ± 2.0648.33 ± 12.4163.24 ± 0.80
Head width51.54 ± 6.9349.97 ± 6.8755.61 ± 3.8562.30 ± 3.15
SL: standard length; HL: head length; D1: first dorsal fin; D2: second dorsal fin; P1: pectoral fin; P2: pelvic fin; A: anal fin; C: caudal fin. The values are presented as the mean ± standard error.
Table 3. Comparison of the COI sequences of four gobiid species with reference sequences in the GenBank and BOLD databases, percentage identity and query cover.
Table 3. Comparison of the COI sequences of four gobiid species with reference sequences in the GenBank and BOLD databases, percentage identity and query cover.
SpeciesGenBank
Accession No.
GenBankBOLD
Species% IdentityQuery
Cover (%)
Species% Identity
R. chiengmaiensisPQ193904- PQ193905Rhinogobius virgigena95.8599Rhinogobius virgigena96.22
R. mekongianusPQ193906- PQ193910Rhinogobius virgigena95.44–95.7299Rhinogobius virgigena95.91–96.22
E. siamensisPQ193911- PQ193912Pseudogobiopsis oligactis98.1499Pseudogobiopsis oligactis98.93
P. oligactisPQ193913- PQ193914Pseudogobiopsis oligactis99.29100Pseudogobiopsis oligactis99.85
Table 4. The average nucleotide composition, GC content, and AT content (%) of all sites in the COI sequences of the four fish species.
Table 4. The average nucleotide composition, GC content, and AT content (%) of all sites in the COI sequences of the four fish species.
SpeciesNucleotide Composition (%)%GC
Content
%AT
Content
TCAG
R. chiengmaiensis29.7 ± 0.028.8 ± 0.022.3 ± 0.019.2 ± 0.048.0 ± 0.052.0 ± 0.0
R. mekongianus30.0 ± 0.128.5 ± 0.022.2 ± 0.119.3 ± 0.147.8 ± 0.152.2 ± 0.1
E. siamensis27.4 ± 0.028.6 ± 0.024.3 ± 0.019.7 ± 0.048.3 ± 0.051.7 ± 0.0
P. oligactis27.3 ± 0.028.7 ± 0.023.6 ± 0.020.4 ± 0.049.1 ± 0.050.9 ± 0.0
Average29.0 ± 1.328.6 ± 0.122.9 ± 0.919.5 ± 0.548.2 ± 0.551.8 ± 0.5
The values are presented as the mean ± standard error.
Table 5. The average K2P intraspecific and interspecific genetic distances (%) were determined for the four fish species.
Table 5. The average K2P intraspecific and interspecific genetic distances (%) were determined for the four fish species.
SpeciesR. chiengmaiensisR. mekongianusE. siamensisP. oligactis
R. chiengmaiensis0.00
R. mekongianus0.860.28
E. siamensis15.3811.020.00
P. oligactis16.6312.001.640.00
Disclaimer/Publisher’s Note: The statements, opinions and data contained in all publications are solely those of the individual author(s) and contributor(s) and not of MDPI and/or the editor(s). MDPI and/or the editor(s) disclaim responsibility for any injury to people or property resulting from any ideas, methods, instructions or products referred to in the content.

Share and Cite

MDPI and ACS Style

Tuncharoen, S.; Panase, P.; Panprommin, N.; Wangkahart, E.; Ruenkoed, S.; Mongkolwit, K.; Panprommin, D. New Data on Rhinogobius chiengmaiensis and Rhinogobius mekongianus in Thailand by DNA Barcoding and Morphological Methods. Animals 2025, 15, 871. https://doi.org/10.3390/ani15060871

AMA Style

Tuncharoen S, Panase P, Panprommin N, Wangkahart E, Ruenkoed S, Mongkolwit K, Panprommin D. New Data on Rhinogobius chiengmaiensis and Rhinogobius mekongianus in Thailand by DNA Barcoding and Morphological Methods. Animals. 2025; 15(6):871. https://doi.org/10.3390/ani15060871

Chicago/Turabian Style

Tuncharoen, Siriluck, Paiboon Panase, Nontree Panprommin, Eakapol Wangkahart, Supranee Ruenkoed, Keatipong Mongkolwit, and Dutrudi Panprommin. 2025. "New Data on Rhinogobius chiengmaiensis and Rhinogobius mekongianus in Thailand by DNA Barcoding and Morphological Methods" Animals 15, no. 6: 871. https://doi.org/10.3390/ani15060871

APA Style

Tuncharoen, S., Panase, P., Panprommin, N., Wangkahart, E., Ruenkoed, S., Mongkolwit, K., & Panprommin, D. (2025). New Data on Rhinogobius chiengmaiensis and Rhinogobius mekongianus in Thailand by DNA Barcoding and Morphological Methods. Animals, 15(6), 871. https://doi.org/10.3390/ani15060871

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop