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With the aim of expanding the possibilities of identifying termite species, in the present study we generated genetic data based on sequences of the mitochondrial gene encoding cytochrome c oxidase subunit II (COII) for termites (Blattodea: Isoptera) occurring in the state of Paraíba, northeastern Brazil. The genetic data were obtained from 135 COII sequences identified in 28 genera and 48 species. These are the first COII sequences for 15 taxa (31.2%) available in public sources. Using delimitation methods based on distance (ASAP and ABGD) and tree (GMYC, bPTP, mPTP and PTP), we confirmed the efficiency of this technique in delimiting most species. However, the assessment of intraspecific and interspecific variation revealed the occurrence of species with intraspecific genetic variation classified as high (> 2%). The analysis of identification efficiency based on our genetic data revealed a high rate of correct identifications (91.80% to 100%), confirming the efficiency of COII in species identification. The generation of these genetic data contributed as an alternative method for future identifications, allowed the understanding of the phylogenetic diversity of some termite species in Paraíba and the application of new molecular techniques to collect data on the conservation of the state.
Introduction
Termites are eusocial insects of the order Blattodea [1], organized into specific castes, each with different morphological and physiological characteristics related to the different functions they perform in the colony [2]. There are 2,994 species of living termites [3], with great diversity and biomass in tropical regions [4–6]. In Brazil, at least 350 species of termites have been identified, classified into five families: Kalotermitidae, Heterotermitidae, Rhinotermitidae, Serritermitidae and Termitidae [3].
Usually, external and/or internal morphological characters are used to determine the taxa of these eusocial insects, with the soldier caste containing the most useful characters for taxonomy [7,8]. However, it is worth noting that the presence of soldiers is not observed in all termite species. This is the case of the species of the subfamily Apicotermitinae, which occur in the Neotropical region. Due to this characteristic, the delimitation of genera or species in this group is mainly based on the worker caste, with the internal characters being the most analyzed [9], which complicates taxonomic work and leads to a knowledge gap about the diversity of Apicotermitinae in the Neotropical region [10].
Although traditional identification is applied to species that have soldiers, the morphological approach has some limitations in certain situations due to intraspecific variation, old descriptions with sparse diagnoses and the presence of cryptic species [11–13]. In order to reduce the existing limitations when only morphological characters are used in the description and identification of termite species, some authors have started to analyze other parameters besides morphology [14–17], which has led to an increase in information to distinguish species. One of these parameters is molecular characters, which were originally used more in studies focused on understanding phylogeny or phylogeographic relationships [18–21]. In recent years, however, these traits have proven useful for species identification and delimitation, with DNA barcoding being an example of the methods used to achieve these results [22–24].
In termites, the mitochondrial gene (mtDNA) encoding cytochrome c oxidase subunit II (COII) has been shown to be an efficient gene for species delimitation and identification. This polymorphic gene [25,26] can be easily amplified in termites [26] and is recommended for the use of DNA barcoding in soil-feeding termites and non-soldier caste specimens [10,14]. However, in order for the analysis of COII sequences to be used for species identification, genetic data must be generated and deposited in public repositories so that sequence comparisons can be made in the future with already known and deposited information [27–29]. There are numerous efforts in the literature to create a database for insects [30–34].
Aware that the use of exclusively morphological traits in termite identification has its limitations, and considering that most genetic data refer to groups with greater charismatic attraction [29], especially in easily accessible locations [35], the present study aims to generate genetic data using the mitochondrial COII gene for termite species occurring in the state of Paraíba. This state is located in an area of Brazil that is poorly explored in terms of genetic data generation and currently has 78 species (Vasconcellos & Chaves 2024, Alexandre Vasconcellos; Rozzanna Esther Cavalcanti Reis de Figueirêdo Chaves, 2024, “Biodiversidade de Cupins da Paraíba, Brasil”, https://doi.org/10.48472/DATAPB/Z0VB1K, DATAPB, V1). We also test the efficiency of the COII gene in delimiting the termite species present in this region. Finally, the generation of these genetic data will allow the acquisition of molecular characteristics that will help in the identification of the termites present in this region.
Materials e methods
Data collection
To generate this genetic data, 238 specimens were used and assigned to 64 morphological species. The specimens came from collections in different municipalities of the state of Paraíba (Fig 1), located in northeastern Brazil between latitudes 6º02’12” and 8º19’18” S and longitudes 34º45’54” and 38º45 ‘45” W (see Table S1), and were deposited in the Isoptera collection of the Federal University of Paraíba, Brazil. The collection was approved by the Brazilian Institute of Wildlife and Environment/Ministry of Environment (SISBIO license number 72602−4).
[Figure omitted. See PDF.]
The information about the collection sites and other relevant details about the samples can be found in Table S1. The map was created with QGIS 3.38.2.
The identification of the collected specimens was based on morphological characteristics using identification keys [8,36] and species descriptions of termites from the literature. In addition, comparisons were made with previously identified specimens deposited in the Isoptera collection of the UFPB. Most identifications were made using individuals of the soldier caste; however, for species belonging to the subfamily Apicotermitinae, individuals of the worker caste were used.
The state’s vegetation varies throughout its territory, with Caatinga being the predominant biome, but Atlantic Forest and coastal forests are also present. According to the Köppen classification, the region comprises different climate zones: tropical with a dry winter season (Aw), humid tropical (Am), tropical with a dry season (As), and semi-arid (Bsh) [377]. The amount of precipitation varies between 300 mm and 1900 mm at a temperature of around 24°C [37].
Amplifying and sequencing
For DNA extraction, the heads of specimens from the soldier and worker castes were used to reduce the risk of contamination with the genetic material of the symbionts in the termite gut [15]. The Blood & Tissue DNA Mini Kit (Ludwig Biotec, Alvorada, Brazil) was used for the extraction, following the protocol suggested by the manufacturer. The primers Mod – A-Tleu (5’ CAG ATA AGT GCA TTG GAT TT 3’) and B- tLys (5’ GTT TAA GAG ACC AGT ACT TG 3’) were used to amplify the region of the mitochondrial gene encoding cytochrome c oxidase subunit II (COII) [38,39]. Polymerase chain reaction (PCR) amplification was performed according to the following protocol: 5.0 μL 1 × Colorless GoTaq® Flexi Buffer (Promega Corp., Madison, WI); 5.0 μL 0.2 mM dNTP; 5.0 μL of each primer at 0.2 mM (forward and reverse); 3.0 μL 2 mM MgCl2; 0.2 μL 1U Taq polymerase (Promega Corp., Madison, WI); and 2 μL extracted DNA, for a total volume of 25 μL. The amplification cycle included an initial denaturation of 2 minutes at 94°C, annealing of 45 seconds at 47°C, an extension of 1 minute at 72°C and a final extension of 10 minutes at 72°C. The success of amplification was assessed by electrophoresis in a 2% agarose gel using Safer, a non-mutagenic dye, and visualized under ultraviolet light. Successful PCR products were bidirectionally sequenced using an ABI 3130 Genetic Analyzer (Applied Biosystems).
Analysis of the data
Analyzes to check the quality of the sequences obtained and for editing and assembly, if required, were performed using GENEIOUS v 9.1.3 software [40]. Alignment was performed in the same software using the MAFFT v.7.017 [41] module in the default configuration. To confirm the absence of contaminants, a BLAST was performed on the NCBI website (NCBI- https://blast.ncbi.nlm.nih.gov/Blast.cgi, accessed May 10, 2023). To complete the database, COII sequences from termites collected in Paraíba that were already available in the GenBank repository, were also added (see Table S2).
Species delimitation
For the analyzes, the species were grouped by family, as various studies aimed at understanding the evolutionary processes within the infraorder Isoptera have shown that the families diverged millions of years ago [42–44]. In addition, the most recent classification for termites based on molecular data [45] was used. Two approaches were used to delimit species: Distance and Tree [46]. In the distance method, we performed the automatic analysis barcode gap discovery (ABGD) [47] online (https://bioinfo.mnhn.fr/abi/public/abgd/abgdweb.html; accessed June 20, 2023) with the Kimura-2 parameter (K2P) distance model [48] and the following settings: Pmim = 0.001; Pmax = 0.2; Step = 20; Nb bins = 20, and the relative gap width (x) = 0.5. We also run the Assemble Species by Automatic Partitioning (ASAP) analysis [49] online (https://bioinfo.mnhn.fr/abi/public/asap/; accessed June 20, 2023) with the same model and default settings. In ASAP, only the partition that had the lowest asap score value was considered (asap score of Kalotermitidae = 2.00, Heterotermitidae = 1.50 and Termitidae = 5.00).
When delimiting species based on phylogenetic trees, we performed the following analyzes: Poisson Tree Process [50] (mPTP, PTP and bPTP) and Generalized Mixed Yule Coalescent (GMYC) [51,52]. We have evaluated the best nucleotide substitution model for the tree method delineation using the XSEDE JmodelTest2 program [53,54], on the CIPRES v. portal. 3.3 [55] (https://www.phylo.org/portal2/login!input.action; accessed on June 20, 2023). The result obtained for the three families was the GTR + I + G model.
The mPTP [56] was performed online (https://mptp.h-its.org/#/tree; accessed June 20, 2023), using the default settings and removing sequences that belonged to the outgroup. For the other analyzes, PTP, bPTP and GMYC, iTaxo Tools software was used [46]. The ultrametric tree used in the GMYC analysis was generated using the program BEAST v1.10.4 [57] with the following parameters: relaxed clock with lognormal distribution, the Yule process speciation model, GTR + I + G and constant population size. The number of generations used in the CIPRES v. environment. 3.3 [55] varied depending on the family analyzed (Kalotermitidae = 2.5 x 10⁸ generations, Heterotermitidae = 2 x 10⁸ generations, Termitidae = 3.5 x 10⁸ generations). The program Tracer v1.7.2 [58] was used to evaluate the results based on ESS values that were considered satisfactory (ESS > 200). In addition, the program TreeAnnotator v1.10.4 [57] was used to create a consensus tree, excluding the first 10% as “burn-in”.
To represent the phylogenies, we created trees with the maximum likelihood method using the IQ- Tree web server [59] (http://iqtree.cibiv.univie.ac.at; accessed June 20, 2023)The trees were visualized with the software Figtree v1.4.4. Sequences from GenBank were used as an external group in all analyzes. However, a different external group was used for each family analyzed in this work (see Table S2).
Intra and interspecific divergence
MEGA11 software [60] was used to assess intraspecific and interspecific divergence (mean and maximum intraspecific variation and minimum distance to nearest neighbor species) for the sequenced COII gene sequences, using the Kimura 2-parameter (K2P) distance model [48] with the settings provided by the program. This distance model was chosen because previous studies have used it to calculate genetic variation. Despite potential problems with thresholds, we opted for the default threshold of 2%, which is commonly cited in DNA barcoding studies [61]. This analysis included all three families together.
Specimen identification
The success of the identification of termites from the state of Paraíba using the COII gene was verified using the Best Match (BM), Best Close Match (BCM), and BOLD Identification Criterion (BIC) using the Species Identity and Evolution package (SPIDER v. 1.3) [62] in program R [63]. Performing these analyzes involves a sequence-based identification simulation in which each sequence is treated as an unknown specimen, and our data library is used to assign a species-level identification. No singletons were used in the queries, and all analyzes were performed using the K2P model.
In this study, we analyzed distances in four different scenarios: (i) 1%, as defined by the BOLD system [64]; (ii) 2%, as proposed by Hebert, Ratnasingham, and de Waard (2003), and commonly used as a threshold for insect DNA barcoding [65]; (iii) a percentage determined by the “localMinima” function in SPIDER, which calculates genetic distance based on the data [62]; and (iv) a percentage determined by the “ ThreshVal “ function, also included in SPIDER, which calculates the genetic interval with the smallest cumulative error [62].
Results
Sampling and data set
Of the 64 species originally considered for inclusion in the genetic data, sequences were obtained for 48 species from the state of Paraíba. The genetic data contain 135 sequences, with an average of 2.8 specimens per species. However, it should be noted that these genetic data contain five singletons, for species such as Cryptotermes brevis (Walker, 1853), Ibitermes inflatus Vasconcellos, 2002, Nasutitermes callimorphus Mathews, 1977, Neotermes hirtellus (Silvestri, 1901) and Tauritermes bandeirai Scheffrahn & Vasconcellos, 2020. The analyzed sequences had a length of 601 base pairs for Heterotermitidae, 610 base pairs for Kalotermitidae, and 605 base pairs for Termitidae. All sequences were deposited (Table S1), and the first COII sequence of 15 taxa (31.2%) was deposited in the GenBank repository.
Species delimitation
The number of possible species varied depending on the delimitation method used. Based on the morphological approach, the following number of species was considered for each family: six species for the Kalotermitidae, three for the Heterotermitidae, and 39 for the Termitidae. However, the Heterotermitidae was the only family in which all molecular delimitations matched the morphological delimitations (Fig 2). In the Kalotermitidae, there were only two methods that did not agree with the morphological delimitation: mPTP, which considered four possible species, and GMYC, which combined two possible species (Fig 3). In the case of Termitidae, the delimitations resulted in different values: 40 for ASAP, ABGD- initial partition in 38, ABGD- recursive partition in 39, GMYC in 52, bPTP in 46, mPTP in 40 and PTP in 46 (Fig 4).
[Figure omitted. See PDF.]
The numbers represent the bootstrap values of the nodes. Each bar represents a specific delimitation method: Morphological, ASAP (Assemble Species by Automatic Partitioning), ABGDin (Automatic Barcode Gap Discovery: initial partition), ABGDrec (Automatic Barcode Gap Discovery: recursive partition), GMYC (Generalized Mixed Yule Coalescent), bPTP (Bayesian Poisson Tree Process), mPTP (multi-rate Poisson Tree Process) and PTP (Poisson Tree Process); gray colored bars show divergences to the morphological delimitation.
[Figure omitted. See PDF.]
The numbers represent the bootstrap values of the nodes. Each bar represents a specific delimitation method: Morphological, ASAP (Assemble Species by Automatic Partitioning), ABGDin (Automatic Barcode Gap Discovery: initial partition), ABGDrec (Automatic Barcode Gap Discovery: recursive partition), GMYC (Generalized Mixed Yule Coalescent), bPTP (Bayesian Poisson Tree Process), mPTP (multi-rate Poisson Tree Process) and PTP (Poisson Tree Process); gray colored bars show divergences to the morphological delimitation.
[Figure omitted. See PDF.]
The numbers represent the bootstrap values of the nodes. Each bar represents a specific delimitation method: Morphological, ASAP (Assemble Species by Automatic Partitioning), ABGDin (Automatic Barcode Gap Discovery: initial partition), ABGDrec (Automatic Barcode Gap Discovery: recursive partition), GMYC (Generalized Mixed Yule Coalescent), bPTP (Bayesian Poisson Tree Process), mPTP (multi-rate Poisson Tree Process) and PTP (Poisson Tree Process); gray colored bars show the divergence to the morphological delimitation.
Intraspecific and interspecific divergence
Intraspecific genetic divergence ranged from 0% to 6.03% (Table S3), with a mean of 0.14% and a standard deviation of 0.80%. Interspecific genetic divergence ranged from 1.65% to 22.48% (Table S2), with a mean of 17% and a standard deviation of 6.02%. Some species did not meet the predetermined standard of 2%, such as Syntermes molestus (Burmeister, 1839) and Anoplotermes meridianus (Emerson, 1925), which had maximum intraspecific divergence values of 6.03% and 2.03%, respectively. In addition, species with low interspecific divergence were identified, namely Nasutitermes ephratae (Holmgren, 1910) and Nasutitermes coxipoensis (Holmgren, 1910) with 1.65% (as shown in Table S2). By plotting the intraspecific and interspecific variation values of the three families together, we were able to visualize the amplitude of the gap in the barcode based on the analyzed data (Fig 5a). It was found that the intraspecific and interspecific divergence values overlap (Fig 5b), which means that it is not possible to determine the barcoding gap for the constructed database.
[Figure omitted. See PDF.]
(a) Intra- and interspecific divergence values found in all three families together; (b) focus on species that do not fit the given 2% pattern. Am (Anoplotermes meridianus), Nc (Nasutitermes coxipoensis), Ne (Nasutitermes ephratae) and Sm (Syntermes molestus).
Specimen identification
When using SPIDER (Table 1) to test the feasibility of species identification from the genetic data, we were able to obtain a total of 130 correct identifications when using the BM method. The number of correct identifications using the BCM method ranged from 124 (limit of 1% and 1.06%) to 129 (limit of 2%). Finally, with the BIC method, the hit rate varied between 119 (limit of 2%) and 126 (limit of 1.55%).
[Figure omitted. See PDF.]
Discussion
The sequence encoding COII has been shown to be a gene that can be used to delimit termite species from the state of Paraiba, with most delimitations being consistent with identifications based on morphological characteristics. This type of result confirms what we found in the literature [66], but in the present study it was not possible to identify a barcode gap due to overlap between intraspecific and interspecific values. Applying an integrative approach using different methods to strengthen the reliability of taxonomic classification [67] and including at least three analyzes with different criteria for species delimitation [34], we found that only two species showed discrepancies in morphological identification: Neocapritermes opacus (Hagen, 1858) and Syntermes molestus (Fig 4).
In the species Neocapritermes opacus, discrepancies were found in the delimitation by the tree method (GMYC, bPTP and PTP). Regarding the morphological characteristics of the species, it has already been mentioned in the literature that individuals differ in size [68]. Nevertheless, the specimens used to extract the sequences of this species exhibited a number of morphological features that can identify them as Neocapritermes opacus, with a labrum on the anterior side with three lobules, a pronotum almost twice as wide as long, and a moderately curved left mandible (Fig 6b-d).
[Figure omitted. See PDF.]
(a) Maximum likelihood (ML) tree showing the relationship between the specimens used to obtain the Neocapritermes opacus sequences. The specimen coded OR500403 was delineated as a different species using the GMYC, bPTP and PTP methods. Photos of soldiers from the same batch from which the specimen was taken for sequencing; (b) OR500403; (c) OR500401; (d) OR500402. Photo by the author.
High intraspecific variation was detected in the species Syntermes molestus (6.03%), which resulted in one of the sequences being classified as originating from a different species in all delimitations (Fig 4). However, the specimens used for DNA extraction showed morphological features belonging to the species in question, such as a very small or absent first marginal tooth of the right mandible, anteriorly converging sides of the head with strongly hooked mandibular tips, a posteriorly widening postmentum with only two hairs at the anterior corners, and a maximum width of the head greater than 2.9 [69] (Fig 7b-d). Based on the results obtained, we believe that there may be considerable intraspecific variation that requires a more detailed study of the populations of these animals.
[Figure omitted. See PDF.]
(a) Maximum Likelihood (ML) tree showing the relationship between the specimens used to obtain the Syntermes molestus sequences. The specimen coded OR493222 was delineated as a different species in all methods. Photographs of soldiers from the same batch from which the specimen was taken for sequencing; (b) OR493222; (c) OR493223; (d) OR493224. Photo by the author.
Apart from Syntermes molestus, other results have shown that not all species considered in the compilation of this database meet the 2% standard (Anoplotermes meridianus, Nasutitermes ephratae and Nasutitermes coxipoensis), and this result is also found in the literature for other groups of invertebrates with the standard DNA barcoding gene, a mitochondrial gene encoding cytochrome c oxidase subunit I [70]. This type of result demonstrates that using a fixed value to delimit species in DNA barcoding does not cover the full range of evolutionary aspects that may exist in a community [34]. It also emphasizes the importance of calculating specific thresholds for each empirical dataset rather than relying on default values for species delimitation [47].
The species N. ephratae and N. coxipoensis were found to have an interspecific divergence of less than 2% (1.65%), which meant that the delimitation by the initial ABGD classification was recognized as a single species (Fig 4), as it is a method based on the distance between pairs and this low value of interspecific divergence affects the results [47]. Although these two species can be identified by the morphological characteristics of the soldiers [7,71], they pose a major challenge for accurate differentiation. This is because they are species with similar morphology [6666], which is why behavioral characteristics began to be recorded in addition to morphological characteristics to increase the reliability of identification. One of these obvious differences lies in the nests of the two species. N. ephratae builds arboreal nests (Fig 8c), which vary in color from light to dark. In addition, there is a reinforced chamber inside the nest in which the king and queen live [72]. In contrast, N. coxipoensis has epigeal nests (Fig 8e) with an irregular outer surface [73].
[Figure omitted. See PDF.]
(a) Maximum Likelihood (ML) Tree showing the relationship between N. ephratae and N. coxipoensis. (b) Soldier of N. ephratae; (c) Nest of N. ephratae; (d) Soldier of N. coxipoensis; (e) Nest of N. coxipoensis. Photo by the author.
Regarding the morphology of the soldier caste of these species, N. ephratae has an elongate rather than broad head, with a nasus extending about half the width of the head [74–75] (Fig 8b). (Fig 8b). In contrast, in the soldiers of N. coxipoensis, the tip of the nasus is lighter in color, while the head is dark brown. The body, on the other hand, has a more yellowish color, which can vary to a dark brown. The pronotum of these soldiers takes the shape of a saddle, with an irregular anterior margin, and finally the abdominal tergites are smooth [71] (Fig 8d). The grouping of individuals of these species into a single species by one method and the low interspecific divergence emphasize the need for integrative taxonomy to provide a more reliable species delimitation [76].
Although Anoplotermes meridianus has an intraspecific divergence of more than 2% (2.03%), all sequences in all delimitations were determined to belong to a single species based on genetic distance. The specimens used for DNA extraction have features that identify them as Anoplotermes meridianus, such as the enteric valve unarmed, which has six regular cushions with rounded and smooth scales at the base (Fig 9b-d) [77]. Regarding the external morphology of the worker, an abdomen with a darker shade stands out due to its diet, while the antenna is composed of 14 articles, the third article being twice as large as the second [78].
[Figure omitted. See PDF.]
(a) Maximum likelihood (ML) tree showing the relationship between the specimens used to obtain the sequences of Anoplotermes meridianus with the specimen coded OR478718 delineated as a different species by bPTP and PTP. (bd) Photos of enteric valve from workers from the same batch from which the sample for sequencing was taken; (b) OR478716; (c) OR478717; (d) OR478718. Photo by the author.
There are some studies that attempt to expand the knowledge of the descriptive characteristics of the species of the genus Anoplotermes (Termitidae: Apicoterminae) [79,80]. However, these studies do not provide specific information on the description of Anoplotermes meridianus. Considering this gap, it is important to conduct review studies dedicated to this particular species to deepen our understanding of the characteristic traits that identify it and to clarify its relationship with other species within the genus, as Anoplotermes meriadianus has already been shown to be a possible sister group to Humutermes Bourguignon & Roisin, 2016 (Termitidae: Apicoterminae), demonstrating that the genus Anoplotermes is a paraphyletic group [81].
For genetic data to be used as a means of facilitating the identification of specimens, it is necessary to know whether it is possible to identify specimens to species level with it. In this regard, the number of correct identifications varied between 91.50% and 100%, with not a single incorrect identification, proving that it is possible to identify most termite species using the COII sequences. In comparison with other studies that have generated genetic data for different groups, we found similar results, e.g., for the genetic data of mosquitoes from French Guiana with a minimum hit rate of 98.7% [82], for the genetic data of Neotropical Odonata occurring in the Alto Prata basin with a minimum hit rate of 79% [33], and for the genetic data of butterflies from South America, which achieved a minimum accuracy of 95% [83].
The results of the best-match analysis showed a 100% identification success rate. However, it should be emphasized that this method has an inherent bias as it only considers nearby sequences, regardless of genetic distance [31]. Due to this limitation, some researchers have started to propose the use of BCM as a replacement for BM for general analyzes [82]. When the genetic distance threshold is increased in the analyzes (BCM and BIC), variation in the hit rate and specimen identification is observed. This variation is attributed to the presence of species with high intraspecific variation, which makes the assignment of certain sequences difficult [84]. At a threshold of 2% in the BIC method, the sequences of N. ephratae and N. coxipoensis specimens were categorized as ambiguous due to the low interspecific divergence between these two species
Although it was not possible to find a barcode gap value in this study, the species delimitations using COII showed a high convergence rate with the morphological delimitation (95.83%), indicating that it is a gene capable of delimiting termite species, and the genetic data showed that it can be used as a termite species identification tool. Although it was not possible to obtain all the sequences of the termite species present in the state of Paraíba, the information collected in this study represents a significant advance in the field of taxonomy. This advance is particularly noteworthy because it contributes the genetic data of 15 species to public databases and because 14% of the termite species already known to occur in Brazil have been sequenced here. In addition, this genetic data is another tool that helps in the identification of species. This usefulness is emphasized by the fact that regional genetic data help to improve the accuracy of identifications [84].
Conclusions
The creation of a genetic data of COII sequences of termites from the state of Paraíba is a significant advance both for taxonomy and for the conservation of Brazilian biodiversity. This initiative is particularly important in a region where there is a lack of studies to understand phylogenetic diversity. In addition, the genetic data provide essential support for conducting biomonitoring through mass sequencing. Our results suggest that the COII gene is effective in delimiting species and is predominantly consistent with morphological identifications. Although it was not possible to identify a DNA barcode gap due to the overlaps found, this limitation did not prevent us from proving the efficiency of COII, as a minimum capacity of 91.50% correct identifications was achieved.
Supporting information
S1 Table. List of investigated species and termites with the corresponding GenBank accession numbers.
https://doi.org/10.1371/journal.pone.0328685.s001
(ODS)
S2 Table. GenBank accession numbers retrieved for subsequent analysis.
https://doi.org/10.1371/journal.pone.0328685.s002
(ODS)
S3 Table. Intraspecific and interspecific divergence for the COII gene of the analyzed species.
https://doi.org/10.1371/journal.pone.0328685.s003
(ODS)
Acknowledgments
We authors would like to thank Dr. Flávia Maria da Silva Moura and Dr. Tiago Carrijo for their comments that helped improve this article.
References
1. 1. Krishna K, Grimaldi DA, Krishna V, Engel MS. Treatise on the Isoptera of the world. Bull Am Mus Nat Hist. 2013.
* View Article
* Google Scholar
2. 2. Eggleton P, Tayasui I. Feeding groups, lifetypes and the global ecology of termites. Ecol Res. 2001;16:941–60.
* View Article
* Google Scholar
3. 3. Constantino R. 2023 [cited 24 Jun 2023]. Available: http://164.41.140.9/catal//.
* View Article
* Google Scholar
4. 4. Eggleton P, Abe T, Bignell DE, Higashi M. Termites: evolution, sociality, symbioses, ecology. Global Patterns of Termite Diversity. Dordrecht, The Netherlands: Kluwer Academic Publishers. 2000. p. 25–51.
5. 5. Engel MS, Grimaldi DA, Krishna K. Termites (Isoptera): their phylogeny, classification, and rise to ecological dominance. Am Mus Novit. 2009;:1–27.
* View Article
* Google Scholar
6. 6. Tuma J, Eggleton P, Fayle TM. Ant-termite interactions: an important but under-explored ecological linkage. Biol Rev Camb Philos Soc. 2020;95(3):555–72. pmid:31876057
* View Article
* PubMed/NCBI
* Google Scholar
7. 7. Emerson AE. The termites of Kartabo Bartica District, British Guiana. Society of the Zoological Park. 1925.
8. 8. Constantino R. An illustrated key to Neotropical termite genera (Insecta: Isoptera) based primarily on soldiers. Zootaxa. 2002;67: 1–40.
* View Article
* Google Scholar
9. 9. Noirot C. The gut of termites (Isoptera). Comparative anatomy, systematics, phylogeny. II. - Higher termites (Termitidae). Ann Société Entomol Fr. 2001;37:431–71.
* View Article
* Google Scholar
10. 10. Bourguignon T, Šobotník J, Dahlsjö CAL, Roisin Y. The soldierless Apicotermitinae: insights into a poorly known and ecologically dominant tropical taxon. Insect Soc. 2015;63(1):39–50.
* View Article
* Google Scholar
11. 11. Davison D, Darlington JPEC, Cook CE. Species-level systematics of some Kenyan termites of the genus Odontotermes (Termitidae, Macrotermitinae) using mitochondrial DNA, morphology, and behaviour. Insectes soc. 2001;48(2):138–43.
* View Article
* Google Scholar
12. 12. Roy V, Demanche C, Livet A, Harry M. Genetic differentiation in the soil-feeding termite Cubitermes sp. affinis subarquatus: occurrence of cryptic species revealed by nuclear and mitochondrial markers. BMC Evol Biol. 2006;6: 102.
* View Article
* Google Scholar
13. 13. Cheng S, Kirton LG, Panandam JM, Siraj SS, Ng KK-S, Tan S-G. Evidence for a higher number of species of Odontotermes (Isoptera) than currently known from Peninsular Malaysia from mitochondrial DNA phylogenies. PLoS One. 2011;6(6):e20992. pmid:21687629
* View Article
* PubMed/NCBI
* Google Scholar
14. 14. Hausberger B, Kimpel D, van Neer A, Korb J. Uncovering cryptic species diversity of a termite community in a West African savanna. Mol Phylogenet Evol. 2011;61(3):964–9. pmid:21896335
* View Article
* PubMed/NCBI
* Google Scholar
15. 15. Bourguignon T, Šobotník J, Hanus R, Krasulová J, Vrkoslav V, Cvačka J, et al. Delineating species boundaries using an iterative taxonomic approach: the case of soldierless termites (Isoptera, Termitidae, Apicotermitinae). Mol Phylogenet Evol. 2013;69(3):694–703. pmid:23891950
* View Article
* PubMed/NCBI
* Google Scholar
16. 16. Aparatermes thornatus (Isoptera: Termitidae: Apicotermitinae), a New Species of Soldierless Termite from Northern Amazonia. Fla Entomol. 2019;102(1):141.
* View Article
* Google Scholar
17. 17. Carvalho A, Rocha MM, Koroiva R, Monteiro SRP, Vasconcellos A. New species of grigiotermes (Apicotermitinae, Termitidae) from the Northern Atlantic forest, delimited by morphological and molecular data. Sociobiology. 2024;71(1):e9708.
* View Article
* Google Scholar
18. 18. Bourguignon T, Lo N, Šobotník J, Ho SYW, Iqbal N, Coissac E, et al. Mitochondrial phylogenomics resolves the global spread of higher termites, ecosystem engineers of the tropics. Mol Biol Evol. 2017;34(3):589–97. pmid:28025274
* View Article
* PubMed/NCBI
* Google Scholar
19. 19. Rocha MM, Morales-Corrêa E Castro AC, Cuezzo C, Cancello EM. Phylogenetic reconstruction of Syntermitinae (Isoptera, Termitidae) based on morphological and molecular data. PLoS One. 2017;12(3):e0174366. pmid:28329010
* View Article
* PubMed/NCBI
* Google Scholar
20. 20. de Faria Santos A, Fernandes Carrijo T, Marques Cancello E, Coletto Morales-Corrêa E Castro A. Phylogeography of nasutitermes corniger (Isoptera: Termitidae) in the neotropical region. BMC Evol Biol. 2017;17(1):230. pmid:29169320
* View Article
* PubMed/NCBI
* Google Scholar
21. 21. de Faria Santos A, Cancello EM, Morales AC. Phylogeography of nasutitermes ephratae (Termitidae: Nasutitermitinae) in neotropical region. Sci Rep. 2022;12(1):11656. pmid:35804053
* View Article
* PubMed/NCBI
* Google Scholar
22. 22. Johnson A, Forschler BT. Biodiversity and distribution of reticulitermes in the Southeastern USA. Insects. 2022;13(7):565. pmid:35886741
* View Article
* PubMed/NCBI
* Google Scholar
23. 23. Zaman M, Khan IA, Schmidt S, Murphy R, Poulsen M. Morphometrics, distribution, and DNA barcoding: an integrative identification approach to the genus odontotermes (Termitidae: Blattodea) of Khyber Pakhtunkhwa, Pakistan. Forests. 2022;13(5):674.
* View Article
* Google Scholar
24. 24. Vellupillai NM, Ab Majid AH. Phylogenetic relationship of subterranean termite Coptotermes gestroi (Blattodea: Rhinotermitidae) inhabiting urban and natural habitats. Heliyon. 2023;10(1):e23692. pmid:38192757
* View Article
* PubMed/NCBI
* Google Scholar
25. 25. Cameron SL, Whiting MF. Mitochondrial genomic comparisons of the subterranean termites from the Genus Reticulitermes (Insecta: Isoptera: Rhinotermitidae). Genome. 2007;50(2):188–202. pmid:17546084
* View Article
* PubMed/NCBI
* Google Scholar
26. 26. Monaghan MT, Wild R, Elliot M, Fujisawa T, Balke M, Inward DJG, et al. Accelerated species inventory on Madagascar using coalescent-based models of species delineation. Syst Biol. 2009;58(3):298–311. pmid:20525585
* View Article
* PubMed/NCBI
* Google Scholar
27. 27. Dayrat B. Towards integrative taxonomy. Biol J Linn Soc. 2005;85(3):407–15.
* View Article
* Google Scholar
28. 28. Ekrem T, Willassen E, Stur E. A comprehensive DNA sequence library is essential for identification with DNA barcodes. Mol Phylogenet Evol. 2007;43(2):530–42. pmid:17208018
* View Article
* PubMed/NCBI
* Google Scholar
29. 29. Monchamp M-E, Taranu ZE, Garner RE, Rehill T, Morissette O, Iversen LL, et al. Prioritizing taxa for genetic reference database development to advance inland water conservation. Biol Conserv. 2023;280:109963.
* View Article
* Google Scholar
30. 30. Dinca V, Zakharov EV, Hebert PDN, Vila R. Complete DNA barcode reference library for a country’s butterfly fauna reveals high performance for temperate Europe. Proc Biol Sci. 2011;278(1704):347–55. pmid:20702462
* View Article
* PubMed/NCBI
* Google Scholar
31. 31. Raupach MJ, Barco A, Steinke D, Beermann J, Laakmann S, Mohrbeck I, et al. The application of DNA barcodes for the identification of marine crustaceans from the north sea and adjacent regions. PLoS One. 2015;10(9):e0139421. pmid:26417993
* View Article
* PubMed/NCBI
* Google Scholar
32. 32. Hendrich L, Morinière J, Haszprunar G, Hebert PDN, Hausmann A, Köhler F, et al. A comprehensive DNA barcode database for Central European beetles with a focus on Germany: adding more than 3500 identified species to BOLD. Mol Ecol Resour. 2015;15(4):795–818. pmid:25469559
* View Article
* PubMed/NCBI
* Google Scholar
33. 33. Koroiva R, Pepinelli M, Rodrigues ME, Roque F de O, Lorenz-Lemke AP, Kvist S. DNA barcoding of odonates from the Upper Plata basin: database creation and genetic diversity estimation. PLoS One. 2017;12(8):e0182283. pmid:28763495
* View Article
* PubMed/NCBI
* Google Scholar
34. 34. Koroiva R, Rodrigues LRR, Santana DJ. DNA barcoding for identification of anuran species in the central region of South America. PeerJ. 2020;8:e10189. pmid:33150083
* View Article
* PubMed/NCBI
* Google Scholar
35. 35. Hughes AC, Orr MC, Ma K, Costello MJ, Waller J, Provoost P, et al. Sampling biases shape our view of the natural world. Ecography. 2021;44(9):1259–69.
* View Article
* Google Scholar
36. 36. Constantino R. Chave ilustrada para identificação dos Gêneros de Cupins (Insecta: Isoptera) que ocorrem no Brasil. Pap Avulsos Zool. 1997;40:387–448.
* View Article
* Google Scholar
37. 37. Francisco PRM, Medeiros RM de, Santos D, Matos RM de. Köppen’s and thornthwaite climate classification for Paraíba state. Rev Bras Geogr Física. 2015;8(4):1006–16.
* View Article
* Google Scholar
38. 38. Simon C, Frati F, Beckenbach A, Crespi B, Liu H, Flook P. Evolution, weighting, and phylogenetic utility of mitochondrial gene sequences and a compilation of conserved polymerase chain reaction primers. Ann Entomol Soc Am. 1994;87(6):651–701.
* View Article
* Google Scholar
39. 39. Miura T, Roisin Y, Matsumoto T. Molecular phylogeny and biogeography of the nasute termite genus Nasutitermes (Isoptera: Termitidae) in the pacific tropics. Mol Phylogenet Evol. 2000;17(1):1–10. pmid:11020299
* View Article
* PubMed/NCBI
* Google Scholar
40. 40. Kearse M, Moir R, Wilson A, Stones-Havas S, Cheung M, Sturrock S, et al. Geneious basic: an integrated and extendable desktop software platform for the organization and analysis of sequence data. Bioinforma Oxf Engl. 2012;28(12):1647–9. pmid:22543367
* View Article
* PubMed/NCBI
* Google Scholar
41. 41. Katoh K, Standley DM. MAFFT multiple sequence alignment software version 7: improvements in performance and usability. Mol Biol Evol. 2013;30(4):772–80. pmid:23329690
* View Article
* PubMed/NCBI
* Google Scholar
42. 42. Bourguignon T, Lo N, Cameron SL, Šobotník J, Hayashi Y, Shigenobu S, et al. The evolutionary history of termites as inferred from 66 mitochondrial genomes. Mol Biol Evol. 2015;32(2):406–21. pmid:25389205
* View Article
* PubMed/NCBI
* Google Scholar
43. 43. Bucek A, Šobotník J, He S, Shi M, McMahon DP, Holmes EC, et al. Evolution of termite symbiosis informed by transcriptome-based phylogenies. Curr Biol. 2019;29(21):3728–3734.e4. pmid:31630948
* View Article
* PubMed/NCBI
* Google Scholar
44. 44. Chouvenc T, Šobotník J, Engel MS, Bourguignon T. Termite evolution: mutualistic associations, key innovations, and the rise of Termitidae. Cell Mol Life Sci. 2021;78(6):2749–69. pmid:33388854
* View Article
* PubMed/NCBI
* Google Scholar
45. 45. Hellemans S, Rocha MM, Wang M, Romero Arias J, Aanen DK, Bagnères A-G, et al. Genomic data provide insights into the classification of extant termites. Nat Commun. 2024;15(1):6724. pmid:39112457
* View Article
* PubMed/NCBI
* Google Scholar
46. 46. Vences M, Miralles A, Brouillet S, Ducasse J, Fedosov A, Kharchev V, et al. iTaxoTools 0.1: kickstarting a specimen-based software toolkit for taxonomists. Megataxa. 2021;6(2).
* View Article
* Google Scholar
47. 47. Puillandre N, Lambert A, Brouillet S, Achaz G. ABGD, automatic barcode gap discovery for primary species delimitation. Mol Ecol. 2012;21(8):1864–77. pmid:21883587
* View Article
* PubMed/NCBI
* Google Scholar
48. 48. Kimura M. A simple method for estimating evolutionary rates of base substitutions through comparative studies of nucleotide sequences. J Mol Evol. 1980;16(2):111–20. pmid:7463489
* View Article
* PubMed/NCBI
* Google Scholar
49. 49. Puillandre N, Brouillet S, Achaz G. ASAP: assemble species by automatic partitioning. Mol Ecol Resour. 2021;21(2):609–20. pmid:33058550
* View Article
* PubMed/NCBI
* Google Scholar
50. 50. Zhang J, Kapli P, Pavlidis P, Stamatakis A. A general species delimitation method with applications to phylogenetic placements. Bioinforma Oxf Engl. 2013;29(22):2869–76. pmid:23990417
* View Article
* PubMed/NCBI
* Google Scholar
51. 51. Pons J. DNA‐based identification of preys from non‐destructive, total DNA extractions of predators using arthropod universal primers. Mol Ecol Notes. 2006;6(3):623–6.
* View Article
* Google Scholar
52. 52. Fujisawa T, Barraclough TG. Delimiting species using single-locus data and the Generalized Mixed Yule Coalescent approach: a revised method and evaluation on simulated data sets. Syst Biol. 2013;62(5):707–24. pmid:23681854
* View Article
* PubMed/NCBI
* Google Scholar
53. 53. Darriba D, Taboada GL, Doallo R, Posada D. jModelTest 2: more models, new heuristics and parallel computing. Nat Methods. 2012;9(8):772. pmid:22847109
* View Article
* PubMed/NCBI
* Google Scholar
54. 54. Towns J, Cockerill T, Dahan M, Foster I, Gaither K, Grimshaw A, et al. XSEDE: accelerating scientific discovery. Comput Sci Eng. 2014;16(5):62–74.
* View Article
* Google Scholar
55. 55. Miller MA, Pfeiffer W, Schwartz T. Creating the CIPRES Science Gateway for inference of large phylogenetic trees. In: 2010 Gateway Computing Environments Workshop (GCE), 2010.
* View Article
* Google Scholar
56. 56. Kapli P, Lutteropp S, Zhang J, Kobert K, Pavlidis P, Stamatakis A, et al. Multi-rate Poisson tree processes for single-locus species delimitation under maximum likelihood and Markov chain Monte Carlo. Bioinformatics. 2017;33(11):1630–8. pmid:28108445
* View Article
* PubMed/NCBI
* Google Scholar
57. 57. Drummond AJ, Suchard MA, Xie D, Rambaut A. Bayesian phylogenetics with BEAUti and the BEAST 1.7. Mol Biol Evol. 2012;29(8):1969–73. pmid:22367748
* View Article
* PubMed/NCBI
* Google Scholar
58. 58. Rambaut A, Drummond AJ, Xie D, Baele G, Suchard MA. Posterior summarization in bayesian phylogenetics using tracer 1.7. Syst Biol. 2018;67(5):901–4. pmid:29718447
* View Article
* PubMed/NCBI
* Google Scholar
59. 59. Trifinopoulos J, Nguyen L-T, von Haeseler A, Minh BQ. W-IQ-TREE: a fast online phylogenetic tool for maximum likelihood analysis. Nucleic Acids Res. 2016;44(W1):W232-5. pmid:27084950
* View Article
* PubMed/NCBI
* Google Scholar
60. 60. Tamura K, Stecher G, Kumar S. MEGA11: Molecular Evolutionary Genetics Analysis Version 11. Mol Biol Evol. 2021;38(7):3022–7. pmid:33892491
* View Article
* PubMed/NCBI
* Google Scholar
61. 61. Hebert PDN, Ratnasingham S, deWaard JR. Barcoding animal life: cytochrome c oxidase subunit 1 divergences among closely related species. Proc Biol Sci. 2003;270 Suppl 1(Suppl 1):S96–9. pmid:12952648
* View Article
* PubMed/NCBI
* Google Scholar
62. 62. Brown SDJ, Collins RA, Boyer S, Lefort M-C, Malumbres-Olarte J, Vink CJ, et al. Spider: an R package for the analysis of species identity and evolution, with particular reference to DNA barcoding. Mol Ecol Resour. 2012;12(3):562–5. pmid:22243808
* View Article
* PubMed/NCBI
* Google Scholar
63. 63. R Development Core Team. R a language and environment for statistical computing. https://www.r-project.org/. 2020.
* View Article
* Google Scholar
64. 64. Ratnasingham S, Hebert PDN. bold: The Barcode of Life Data System (http://www.barcodinglife.org). Mol Ecol Notes. 2007;7(3):355–64. pmid:18784790
* View Article
* PubMed/NCBI
* Google Scholar
65. 65. Zhang C, Yang R, Wu L, Luo C, Guo X, Deng Y, et al. Molecular phylogeny of the Anopheles hyrcanus group (Diptera: Culicidae) based on rDNA-ITS2 and mtDNA-COII. Parasit Vectors. 2021;14(1):454. pmid:34488860
* View Article
* PubMed/NCBI
* Google Scholar
66. 66. Roy V, Constantino R, Chassany V, Giusti-Miller S, Diouf M, Mora P, et al. Species delimitation and phylogeny in the genus Nasutitermes (Termitidae: Nasutitermitinae) in French Guiana. Mol Ecol. 2014;23(4):902–20. pmid:24372711
* View Article
* PubMed/NCBI
* Google Scholar
67. 67. Carstens BC, Pelletier TA, Reid NM, Satler JD. How to fail at species delimitation. Mol Ecol. 2013;22(17):4369–83. pmid:23855767
* View Article
* PubMed/NCBI
* Google Scholar
68. 68. Krishna K, Araujo RL. A revision of the neotropical termite genus Neocapritermes (Isoptera, Termitidae, Termitinae). Bull Am Mus Nat Hist. 1968;138:Article 3.
* View Article
* Google Scholar
69. 69. Constantino R. Revision of the neotropical termite genus Syntermes Holmgren (Isoptera: Termitidae). University of Kansas. 1995.
70. 70. Lin X, Stur E, Ekrem T. Exploring genetic divergence in a species-rich insect genus using 2790 DNA barcodes. PLoS One. 2015;10(9):e0138993. pmid:26406595
* View Article
* PubMed/NCBI
* Google Scholar
71. 71. Holmgren N. Versuch einer Monographie der amerikanischen Eutermes-Arten. Gräfe & Sillem. 1910.
72. 72. Thorne BL. Differences in nest architecture between the neotropical arboreal termites nasutitermes corniger and nasutitermes ephratae (Isoptera: Termitidae). Psyche J Entomol. 1980;87(3–4):235–43.
* View Article
* Google Scholar
73. 73. Laffont ER. Nest architecture, colony composition and feeding substrates of nasutitermes coxipoensis (Isoptera, Termitidae, Nasutitermitinae) in subtropical biomes of Northeastern Argentina. Sociobiology. 2014;59(4):1297–313.
* View Article
* Google Scholar
74. 74. Banks N. Antillean Isoptera. Bull Mus Comp Zool. 1919;62:475–89.
* View Article
* Google Scholar
75. 75. Snyder TE. New termites from Venezuela, with keys and a list of the described venezuelan species. Am Midl Nat. 1959;61(2):313.
* View Article
* Google Scholar
76. 76. Curry CJ, Gibson JF, Shokralla S, Hajibabaei M, Baird DJ. Identifying North American freshwater invertebrates using DNA barcodes: are existing COI sequence libraries fit for purpose?. Freshw Sci. 2018;37(1):178–89.
* View Article
* Google Scholar
77. 77. Constantini JP. Estudo taxonômico dos Apicotermitinae da Mata Atlântica. Universidade de São Paulo. 2018. http://www.teses.usp.br/teses/disponiveis/38/38131/tde-30102018-172307/
78. 78. Silvestri F. Contribuzione alla conoscenza dei Termitidi e Termitofili dell’America Meridionale. Premiato stab. tip. Vesuviano. 1903.
79. 79. Bourguignon T, Scheffrahn RH, Nagy ZT, Sonet G, Host B, Roisin Y. Towards a revision of the Neotropical soldierless termites (Isoptera: Termitidae): redescription of the genusGrigiotermes Mathews and description of five new genera. Zool J Linn Soc. 2016;176(1):15–35.
* View Article
* Google Scholar
80. 80. Bourguignon T, Scheffrahn RH, Křeček J, Nagy ZT, Sonet G, Roisin Y. Towards a revision of the Neotropical soldierless termites (Isoptera:Termitidae): redescription of the genus Anoplotermes and description of Longustitermes, gen. nov. Invert Syst. 2010;24(4):357.
* View Article
* Google Scholar
81. 81. Carrijo TF, Castro D, Wang M, Constantini JP, Bourguignon T, Cancello EM, et al. Diminishing the taxonomic gap in the neotropical soldierless termites: descriptions of four new genera and a new Anoplotermes species (Isoptera, Termitidae, Apicotermitinae). Zookeys. 2023;1167:317–52. pmid:37397162
* View Article
* PubMed/NCBI
* Google Scholar
82. 82. Talaga S, Leroy C, Guidez A, Dusfour I, Girod R, Dejean A, et al. DNA reference libraries of French Guianese mosquitoes for barcoding and metabarcoding. PLoS One. 2017;12(6):e0176993. pmid:28575090
* View Article
* PubMed/NCBI
* Google Scholar
83. 83. Lavinia PD, Núñez Bustos EO, Kopuchian C, Lijtmaer DA, García NC, Hebert PDN, et al. Barcoding the butterflies of southern South America: Species delimitation efficacy, cryptic diversity and geographic patterns of divergence. PLoS One. 2017;12(10):e0186845. pmid:29049373
* View Article
* PubMed/NCBI
* Google Scholar
84. 84. Bergsten J, Bilton DT, Fujisawa T, Elliott M, Monaghan MT, Balke M, et al. The effect of geographical scale of sampling on DNA barcoding. Syst Biol. 2012;61(5):851–69. pmid:22398121
* View Article
* PubMed/NCBI
* Google Scholar
Citation: Paulino Monteiro SR, Carvalho A, Ferreira RR, Figueirêdo RECR, Vasconcellos A, Koroiva R (2025) Efficiency of the cytochrome c oxidase subunit II gene for the delimitation of termite species (Blattodea: Isoptera) in the state of Paraíba, northeastern Brazil. PLoS One 20(9): e0328685. https://doi.org/10.1371/journal.pone.0328685
About the Authors:
Sara Rikeley Paulino Monteiro
Roles: Conceptualization, Data curation, Formal analysis, Investigation, Project administration, Supervision, Writing – original draft
E-mail: [email protected]
Affiliations: Laboratório de Termitologia, Departamento de Sistemática e Ecologia, Centro de Ciências Exatas e da Natureza, Universidade Federal da Paraíba, João Pessoa, Paraíba, Brazil, Instituto de Ciências Biológicas, Universidade Federal do Pará, Belém, Pará, Brazil
ORICD: https://orcid.org/0000-0002-0048-0353
Antonio Carvalho
Roles: Investigation, Writing – review & editing
Affiliation: Laboratório de Termitologia, Departamento de Sistemática e Ecologia, Centro de Ciências Exatas e da Natureza, Universidade Federal da Paraíba, João Pessoa, Paraíba, Brazil
Renan Rodrigues Ferreira
Roles: Investigation, Writing – review & editing
Affiliation: Laboratório de Termitologia, Departamento de Sistemática e Ecologia, Centro de Ciências Exatas e da Natureza, Universidade Federal da Paraíba, João Pessoa, Paraíba, Brazil
Rozzanna Esther C. R. Figueirêdo
Roles: Investigation, Writing – review & editing
Affiliation: Laboratório de Termitologia, Departamento de Sistemática e Ecologia, Centro de Ciências Exatas e da Natureza, Universidade Federal da Paraíba, João Pessoa, Paraíba, Brazil
Alexandre Vasconcellos
Roles: Conceptualization, Funding acquisition, Writing – review & editing
Affiliation: Laboratório de Termitologia, Departamento de Sistemática e Ecologia, Centro de Ciências Exatas e da Natureza, Universidade Federal da Paraíba, João Pessoa, Paraíba, Brazil
Ricardo Koroiva
Roles: Conceptualization, Funding acquisition, Writing – review & editing
Affiliations: Laboratório de Termitologia, Departamento de Sistemática e Ecologia, Centro de Ciências Exatas e da Natureza, Universidade Federal da Paraíba, João Pessoa, Paraíba, Brazil, Departamento de Engenharia e Meio Ambiente, Universidade Federal da Paraíba, Rio Tinto, Paraíba, Brazil
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1. Krishna K, Grimaldi DA, Krishna V, Engel MS. Treatise on the Isoptera of the world. Bull Am Mus Nat Hist. 2013.
2. Eggleton P, Tayasui I. Feeding groups, lifetypes and the global ecology of termites. Ecol Res. 2001;16:941–60.
3. Constantino R. 2023 [cited 24 Jun 2023]. Available: http://164.41.140.9/catal//.
4. Eggleton P, Abe T, Bignell DE, Higashi M. Termites: evolution, sociality, symbioses, ecology. Global Patterns of Termite Diversity. Dordrecht, The Netherlands: Kluwer Academic Publishers. 2000. p. 25–51.
5. Engel MS, Grimaldi DA, Krishna K. Termites (Isoptera): their phylogeny, classification, and rise to ecological dominance. Am Mus Novit. 2009;:1–27.
6. Tuma J, Eggleton P, Fayle TM. Ant-termite interactions: an important but under-explored ecological linkage. Biol Rev Camb Philos Soc. 2020;95(3):555–72. pmid:31876057
7. Emerson AE. The termites of Kartabo Bartica District, British Guiana. Society of the Zoological Park. 1925.
8. Constantino R. An illustrated key to Neotropical termite genera (Insecta: Isoptera) based primarily on soldiers. Zootaxa. 2002;67: 1–40.
9. Noirot C. The gut of termites (Isoptera). Comparative anatomy, systematics, phylogeny. II. - Higher termites (Termitidae). Ann Société Entomol Fr. 2001;37:431–71.
10. Bourguignon T, Šobotník J, Dahlsjö CAL, Roisin Y. The soldierless Apicotermitinae: insights into a poorly known and ecologically dominant tropical taxon. Insect Soc. 2015;63(1):39–50.
11. Davison D, Darlington JPEC, Cook CE. Species-level systematics of some Kenyan termites of the genus Odontotermes (Termitidae, Macrotermitinae) using mitochondrial DNA, morphology, and behaviour. Insectes soc. 2001;48(2):138–43.
12. Roy V, Demanche C, Livet A, Harry M. Genetic differentiation in the soil-feeding termite Cubitermes sp. affinis subarquatus: occurrence of cryptic species revealed by nuclear and mitochondrial markers. BMC Evol Biol. 2006;6: 102.
13. Cheng S, Kirton LG, Panandam JM, Siraj SS, Ng KK-S, Tan S-G. Evidence for a higher number of species of Odontotermes (Isoptera) than currently known from Peninsular Malaysia from mitochondrial DNA phylogenies. PLoS One. 2011;6(6):e20992. pmid:21687629
14. Hausberger B, Kimpel D, van Neer A, Korb J. Uncovering cryptic species diversity of a termite community in a West African savanna. Mol Phylogenet Evol. 2011;61(3):964–9. pmid:21896335
15. Bourguignon T, Šobotník J, Hanus R, Krasulová J, Vrkoslav V, Cvačka J, et al. Delineating species boundaries using an iterative taxonomic approach: the case of soldierless termites (Isoptera, Termitidae, Apicotermitinae). Mol Phylogenet Evol. 2013;69(3):694–703. pmid:23891950
16. Aparatermes thornatus (Isoptera: Termitidae: Apicotermitinae), a New Species of Soldierless Termite from Northern Amazonia. Fla Entomol. 2019;102(1):141.
17. Carvalho A, Rocha MM, Koroiva R, Monteiro SRP, Vasconcellos A. New species of grigiotermes (Apicotermitinae, Termitidae) from the Northern Atlantic forest, delimited by morphological and molecular data. Sociobiology. 2024;71(1):e9708.
18. Bourguignon T, Lo N, Šobotník J, Ho SYW, Iqbal N, Coissac E, et al. Mitochondrial phylogenomics resolves the global spread of higher termites, ecosystem engineers of the tropics. Mol Biol Evol. 2017;34(3):589–97. pmid:28025274
19. Rocha MM, Morales-Corrêa E Castro AC, Cuezzo C, Cancello EM. Phylogenetic reconstruction of Syntermitinae (Isoptera, Termitidae) based on morphological and molecular data. PLoS One. 2017;12(3):e0174366. pmid:28329010
20. de Faria Santos A, Fernandes Carrijo T, Marques Cancello E, Coletto Morales-Corrêa E Castro A. Phylogeography of nasutitermes corniger (Isoptera: Termitidae) in the neotropical region. BMC Evol Biol. 2017;17(1):230. pmid:29169320
21. de Faria Santos A, Cancello EM, Morales AC. Phylogeography of nasutitermes ephratae (Termitidae: Nasutitermitinae) in neotropical region. Sci Rep. 2022;12(1):11656. pmid:35804053
22. Johnson A, Forschler BT. Biodiversity and distribution of reticulitermes in the Southeastern USA. Insects. 2022;13(7):565. pmid:35886741
23. Zaman M, Khan IA, Schmidt S, Murphy R, Poulsen M. Morphometrics, distribution, and DNA barcoding: an integrative identification approach to the genus odontotermes (Termitidae: Blattodea) of Khyber Pakhtunkhwa, Pakistan. Forests. 2022;13(5):674.
24. Vellupillai NM, Ab Majid AH. Phylogenetic relationship of subterranean termite Coptotermes gestroi (Blattodea: Rhinotermitidae) inhabiting urban and natural habitats. Heliyon. 2023;10(1):e23692. pmid:38192757
25. Cameron SL, Whiting MF. Mitochondrial genomic comparisons of the subterranean termites from the Genus Reticulitermes (Insecta: Isoptera: Rhinotermitidae). Genome. 2007;50(2):188–202. pmid:17546084
26. Monaghan MT, Wild R, Elliot M, Fujisawa T, Balke M, Inward DJG, et al. Accelerated species inventory on Madagascar using coalescent-based models of species delineation. Syst Biol. 2009;58(3):298–311. pmid:20525585
27. Dayrat B. Towards integrative taxonomy. Biol J Linn Soc. 2005;85(3):407–15.
28. Ekrem T, Willassen E, Stur E. A comprehensive DNA sequence library is essential for identification with DNA barcodes. Mol Phylogenet Evol. 2007;43(2):530–42. pmid:17208018
29. Monchamp M-E, Taranu ZE, Garner RE, Rehill T, Morissette O, Iversen LL, et al. Prioritizing taxa for genetic reference database development to advance inland water conservation. Biol Conserv. 2023;280:109963.
30. Dinca V, Zakharov EV, Hebert PDN, Vila R. Complete DNA barcode reference library for a country’s butterfly fauna reveals high performance for temperate Europe. Proc Biol Sci. 2011;278(1704):347–55. pmid:20702462
31. Raupach MJ, Barco A, Steinke D, Beermann J, Laakmann S, Mohrbeck I, et al. The application of DNA barcodes for the identification of marine crustaceans from the north sea and adjacent regions. PLoS One. 2015;10(9):e0139421. pmid:26417993
32. Hendrich L, Morinière J, Haszprunar G, Hebert PDN, Hausmann A, Köhler F, et al. A comprehensive DNA barcode database for Central European beetles with a focus on Germany: adding more than 3500 identified species to BOLD. Mol Ecol Resour. 2015;15(4):795–818. pmid:25469559
33. Koroiva R, Pepinelli M, Rodrigues ME, Roque F de O, Lorenz-Lemke AP, Kvist S. DNA barcoding of odonates from the Upper Plata basin: database creation and genetic diversity estimation. PLoS One. 2017;12(8):e0182283. pmid:28763495
34. Koroiva R, Rodrigues LRR, Santana DJ. DNA barcoding for identification of anuran species in the central region of South America. PeerJ. 2020;8:e10189. pmid:33150083
35. Hughes AC, Orr MC, Ma K, Costello MJ, Waller J, Provoost P, et al. Sampling biases shape our view of the natural world. Ecography. 2021;44(9):1259–69.
36. Constantino R. Chave ilustrada para identificação dos Gêneros de Cupins (Insecta: Isoptera) que ocorrem no Brasil. Pap Avulsos Zool. 1997;40:387–448.
37. Francisco PRM, Medeiros RM de, Santos D, Matos RM de. Köppen’s and thornthwaite climate classification for Paraíba state. Rev Bras Geogr Física. 2015;8(4):1006–16.
38. Simon C, Frati F, Beckenbach A, Crespi B, Liu H, Flook P. Evolution, weighting, and phylogenetic utility of mitochondrial gene sequences and a compilation of conserved polymerase chain reaction primers. Ann Entomol Soc Am. 1994;87(6):651–701.
39. Miura T, Roisin Y, Matsumoto T. Molecular phylogeny and biogeography of the nasute termite genus Nasutitermes (Isoptera: Termitidae) in the pacific tropics. Mol Phylogenet Evol. 2000;17(1):1–10. pmid:11020299
40. Kearse M, Moir R, Wilson A, Stones-Havas S, Cheung M, Sturrock S, et al. Geneious basic: an integrated and extendable desktop software platform for the organization and analysis of sequence data. Bioinforma Oxf Engl. 2012;28(12):1647–9. pmid:22543367
41. Katoh K, Standley DM. MAFFT multiple sequence alignment software version 7: improvements in performance and usability. Mol Biol Evol. 2013;30(4):772–80. pmid:23329690
42. Bourguignon T, Lo N, Cameron SL, Šobotník J, Hayashi Y, Shigenobu S, et al. The evolutionary history of termites as inferred from 66 mitochondrial genomes. Mol Biol Evol. 2015;32(2):406–21. pmid:25389205
43. Bucek A, Šobotník J, He S, Shi M, McMahon DP, Holmes EC, et al. Evolution of termite symbiosis informed by transcriptome-based phylogenies. Curr Biol. 2019;29(21):3728–3734.e4. pmid:31630948
44. Chouvenc T, Šobotník J, Engel MS, Bourguignon T. Termite evolution: mutualistic associations, key innovations, and the rise of Termitidae. Cell Mol Life Sci. 2021;78(6):2749–69. pmid:33388854
45. Hellemans S, Rocha MM, Wang M, Romero Arias J, Aanen DK, Bagnères A-G, et al. Genomic data provide insights into the classification of extant termites. Nat Commun. 2024;15(1):6724. pmid:39112457
46. Vences M, Miralles A, Brouillet S, Ducasse J, Fedosov A, Kharchev V, et al. iTaxoTools 0.1: kickstarting a specimen-based software toolkit for taxonomists. Megataxa. 2021;6(2).
47. Puillandre N, Lambert A, Brouillet S, Achaz G. ABGD, automatic barcode gap discovery for primary species delimitation. Mol Ecol. 2012;21(8):1864–77. pmid:21883587
48. Kimura M. A simple method for estimating evolutionary rates of base substitutions through comparative studies of nucleotide sequences. J Mol Evol. 1980;16(2):111–20. pmid:7463489
49. Puillandre N, Brouillet S, Achaz G. ASAP: assemble species by automatic partitioning. Mol Ecol Resour. 2021;21(2):609–20. pmid:33058550
50. Zhang J, Kapli P, Pavlidis P, Stamatakis A. A general species delimitation method with applications to phylogenetic placements. Bioinforma Oxf Engl. 2013;29(22):2869–76. pmid:23990417
51. Pons J. DNA‐based identification of preys from non‐destructive, total DNA extractions of predators using arthropod universal primers. Mol Ecol Notes. 2006;6(3):623–6.
52. Fujisawa T, Barraclough TG. Delimiting species using single-locus data and the Generalized Mixed Yule Coalescent approach: a revised method and evaluation on simulated data sets. Syst Biol. 2013;62(5):707–24. pmid:23681854
53. Darriba D, Taboada GL, Doallo R, Posada D. jModelTest 2: more models, new heuristics and parallel computing. Nat Methods. 2012;9(8):772. pmid:22847109
54. Towns J, Cockerill T, Dahan M, Foster I, Gaither K, Grimshaw A, et al. XSEDE: accelerating scientific discovery. Comput Sci Eng. 2014;16(5):62–74.
55. Miller MA, Pfeiffer W, Schwartz T. Creating the CIPRES Science Gateway for inference of large phylogenetic trees. In: 2010 Gateway Computing Environments Workshop (GCE), 2010.
56. Kapli P, Lutteropp S, Zhang J, Kobert K, Pavlidis P, Stamatakis A, et al. Multi-rate Poisson tree processes for single-locus species delimitation under maximum likelihood and Markov chain Monte Carlo. Bioinformatics. 2017;33(11):1630–8. pmid:28108445
57. Drummond AJ, Suchard MA, Xie D, Rambaut A. Bayesian phylogenetics with BEAUti and the BEAST 1.7. Mol Biol Evol. 2012;29(8):1969–73. pmid:22367748
58. Rambaut A, Drummond AJ, Xie D, Baele G, Suchard MA. Posterior summarization in bayesian phylogenetics using tracer 1.7. Syst Biol. 2018;67(5):901–4. pmid:29718447
59. Trifinopoulos J, Nguyen L-T, von Haeseler A, Minh BQ. W-IQ-TREE: a fast online phylogenetic tool for maximum likelihood analysis. Nucleic Acids Res. 2016;44(W1):W232-5. pmid:27084950
60. Tamura K, Stecher G, Kumar S. MEGA11: Molecular Evolutionary Genetics Analysis Version 11. Mol Biol Evol. 2021;38(7):3022–7. pmid:33892491
61. Hebert PDN, Ratnasingham S, deWaard JR. Barcoding animal life: cytochrome c oxidase subunit 1 divergences among closely related species. Proc Biol Sci. 2003;270 Suppl 1(Suppl 1):S96–9. pmid:12952648
62. Brown SDJ, Collins RA, Boyer S, Lefort M-C, Malumbres-Olarte J, Vink CJ, et al. Spider: an R package for the analysis of species identity and evolution, with particular reference to DNA barcoding. Mol Ecol Resour. 2012;12(3):562–5. pmid:22243808
63. R Development Core Team. R a language and environment for statistical computing. https://www.r-project.org/. 2020.
64. Ratnasingham S, Hebert PDN. bold: The Barcode of Life Data System (http://www.barcodinglife.org). Mol Ecol Notes. 2007;7(3):355–64. pmid:18784790
65. Zhang C, Yang R, Wu L, Luo C, Guo X, Deng Y, et al. Molecular phylogeny of the Anopheles hyrcanus group (Diptera: Culicidae) based on rDNA-ITS2 and mtDNA-COII. Parasit Vectors. 2021;14(1):454. pmid:34488860
66. Roy V, Constantino R, Chassany V, Giusti-Miller S, Diouf M, Mora P, et al. Species delimitation and phylogeny in the genus Nasutitermes (Termitidae: Nasutitermitinae) in French Guiana. Mol Ecol. 2014;23(4):902–20. pmid:24372711
67. Carstens BC, Pelletier TA, Reid NM, Satler JD. How to fail at species delimitation. Mol Ecol. 2013;22(17):4369–83. pmid:23855767
68. Krishna K, Araujo RL. A revision of the neotropical termite genus Neocapritermes (Isoptera, Termitidae, Termitinae). Bull Am Mus Nat Hist. 1968;138:Article 3.
69. Constantino R. Revision of the neotropical termite genus Syntermes Holmgren (Isoptera: Termitidae). University of Kansas. 1995.
70. Lin X, Stur E, Ekrem T. Exploring genetic divergence in a species-rich insect genus using 2790 DNA barcodes. PLoS One. 2015;10(9):e0138993. pmid:26406595
71. Holmgren N. Versuch einer Monographie der amerikanischen Eutermes-Arten. Gräfe & Sillem. 1910.
72. Thorne BL. Differences in nest architecture between the neotropical arboreal termites nasutitermes corniger and nasutitermes ephratae (Isoptera: Termitidae). Psyche J Entomol. 1980;87(3–4):235–43.
73. Laffont ER. Nest architecture, colony composition and feeding substrates of nasutitermes coxipoensis (Isoptera, Termitidae, Nasutitermitinae) in subtropical biomes of Northeastern Argentina. Sociobiology. 2014;59(4):1297–313.
74. Banks N. Antillean Isoptera. Bull Mus Comp Zool. 1919;62:475–89.
75. Snyder TE. New termites from Venezuela, with keys and a list of the described venezuelan species. Am Midl Nat. 1959;61(2):313.
76. Curry CJ, Gibson JF, Shokralla S, Hajibabaei M, Baird DJ. Identifying North American freshwater invertebrates using DNA barcodes: are existing COI sequence libraries fit for purpose?. Freshw Sci. 2018;37(1):178–89.
77. Constantini JP. Estudo taxonômico dos Apicotermitinae da Mata Atlântica. Universidade de São Paulo. 2018. http://www.teses.usp.br/teses/disponiveis/38/38131/tde-30102018-172307/
78. Silvestri F. Contribuzione alla conoscenza dei Termitidi e Termitofili dell’America Meridionale. Premiato stab. tip. Vesuviano. 1903.
79. Bourguignon T, Scheffrahn RH, Nagy ZT, Sonet G, Host B, Roisin Y. Towards a revision of the Neotropical soldierless termites (Isoptera: Termitidae): redescription of the genusGrigiotermes Mathews and description of five new genera. Zool J Linn Soc. 2016;176(1):15–35.
80. Bourguignon T, Scheffrahn RH, Křeček J, Nagy ZT, Sonet G, Roisin Y. Towards a revision of the Neotropical soldierless termites (Isoptera:Termitidae): redescription of the genus Anoplotermes and description of Longustitermes, gen. nov. Invert Syst. 2010;24(4):357.
81. Carrijo TF, Castro D, Wang M, Constantini JP, Bourguignon T, Cancello EM, et al. Diminishing the taxonomic gap in the neotropical soldierless termites: descriptions of four new genera and a new Anoplotermes species (Isoptera, Termitidae, Apicotermitinae). Zookeys. 2023;1167:317–52. pmid:37397162
82. Talaga S, Leroy C, Guidez A, Dusfour I, Girod R, Dejean A, et al. DNA reference libraries of French Guianese mosquitoes for barcoding and metabarcoding. PLoS One. 2017;12(6):e0176993. pmid:28575090
83. Lavinia PD, Núñez Bustos EO, Kopuchian C, Lijtmaer DA, García NC, Hebert PDN, et al. Barcoding the butterflies of southern South America: Species delimitation efficacy, cryptic diversity and geographic patterns of divergence. PLoS One. 2017;12(10):e0186845. pmid:29049373
84. Bergsten J, Bilton DT, Fujisawa T, Elliott M, Monaghan MT, Balke M, et al. The effect of geographical scale of sampling on DNA barcoding. Syst Biol. 2012;61(5):851–69. pmid:22398121
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