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DNA barcoding

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Not to be confused with the DNA barcode involved in optical mapping of DNA.
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DNA barcoding is a method of species identification using a short section of DNA from a specific gene or genes. The premise of DNA barcoding is that by comparison with a reference library of such DNA sections (also called "sequences"), an individual sequence can be used to uniquely identify an organism to species, just as a supermarket scanner uses the familiar black stripes of the UPC barcode to identify an item in its stock against its reference database.[1] These "barcodes" are sometimes used in an effort to identify unknown species or parts of an organism, simply to catalog as many taxa as possible, or to compare with traditional taxonomy in an effort to determine species boundaries.[2]

Different gene regions are used to identify the different organismal groups using barcoding. The most commonly used barcode region for animals and some protists is a portion of the cytochrome c oxidase I (COI or COX1) gene, found in mitochondrial DNA. Other genes suitable for DNA barcoding are the internal transcribed spacer (ITS) rRNA often used for fungi and RuBisCO used for plants.[3][4][5] Microorganisms are detected using different gene regions. The 16S rRNA gene for example is widely used in identification of prokaryotes, whereas the 18S rRNA gene is mostly used for detecting microbial eukaryotes. These gene regions are chosen because they have less intraspecific (within species) variation than interspecific (between species) variation, which is known as the "Barcoding Gap".[6]

Some applications of DNA barcoding include: identifying plant leaves even when flowers or fruits are not available; identifying pollen collected on the bodies of pollinating animals; identifying insect larvae which may have fewer diagnostic characters than adults; or investigating the diet of an animal based on its stomach content, saliva or feces.[7] When barcoding is used to identify organisms from a sample containing DNA from more than one organism, the term DNA metabarcoding is used,[8][9] e.g. DNA metabarcoding of diatom communities in rivers and streams, which is used to assess water quality.[10]

Background

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DNA barcoding techniques were developed from early DNA sequencing work on microbial communities using the 5S rRNA gene.[11] In 2003, specific methods and terminology of modern DNA barcoding were proposed as a standardized method for identifying species, as well as potentially allocating unknown sequences to higher taxa such as orders and phyla, in a paper by Paul D.N. Hebert et al. from the University of Guelph, Ontario, Canada.[12] Hebert and his colleagues demonstrated the utility of the cytochrome c oxidase I (COI) gene, first utilized by Folmer et al. in 1994, using their published DNA primers as a tool for phylogenetic analyses at the species levels[12] as a suitable discriminatory tool between metazoan invertebrates.[13] The "Folmer region" of the COI gene is commonly used for distinction between taxa based on its patterns of variation at the DNA level. The relative ease of retrieving the sequence, and variability mixed with conservation between species, are some of the benefits of COI. Calling the profiles "barcodes", Hebert et al. envisaged the development of a COI database that could serve as the basis for a "global bioidentification system".

Methods

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Sampling and preservation

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Barcoding can be done from tissue from a target specimen, from a mixture of organisms (bulk sample), or from DNA present in environmental samples (e.g. water or soil). The methods for sampling, preservation or analysis differ between those different types of sample.

Tissue samples

To barcode a tissue sample from the target specimen, a small piece of skin, a scale, a leg or antenna is likely to be sufficient (depending on the size of the specimen). To avoid contamination, it is necessary to sterilize used tools between samples. It is recommended to collect two samples from one specimen, one to archive, and one for the barcoding process. Sample preservation is crucial to overcome the issue of DNA degradation.

Bulk samples

A bulk sample is a type of environmental sample containing several organisms from the taxonomic group under study. The difference between bulk samples (in the sense used here) and other environmental samples is that the bulk sample usually provides a large quantity of good-quality DNA. Examples of bulk samples include aquatic macroinvertebrate samples collected by kick-net, or insect samples collected with a Malaise trap. Filtered or size-fractionated water samples containing whole organisms like unicellular eukaryotes are also sometimes defined as bulk samples. Such samples can be collected by the same techniques used to obtain traditional samples for morphology-based identification.

eDNA samples

The environmental DNA (eDNA) method is a non-invasive approach to detect and identify species from cellular debris or extracellular DNA present in environmental samples (e.g. water or soil) through barcoding or metabarcoding. The approach is based on the fact that every living organism leaves DNA in the environment, and this environmental DNA can be detected even for organisms that are at very low abundance. Thus, for field sampling, the most crucial part is to use DNA-free material and tools on each sampling site or sample to avoid contamination, if the DNA of the target organism(s) is likely to be present in low quantities. On the other hand, an eDNA sample always includes the DNA of whole-cell, living microorganisms, which are often present in large quantities. Therefore, microorganism samples taken in the natural environment also are called eDNA samples, but contamination is less problematic in this context due to the large quantity of target organisms. The eDNA method is applied on most sample types, like water, sediment, soil, animal feces, stomach content or blood from e.g. leeches.[14]

DNA extraction, amplification and sequencing

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DNA barcoding requires that DNA in the sample is extracted. Several different DNA extraction methods exist, and factors like cost, time, sample type and yield affect the selection of the optimal method.

When DNA from organismal or eDNA samples is amplified using polymerase chain reaction (PCR), the reaction can be affected negatively by inhibitor molecules contained in the sample.[15] Removal of these inhibitors is crucial to ensure that high quality DNA is available for subsequent analyzing.

Amplification of the extracted DNA is a required step in DNA barcoding. Typically, only a small fragment of the total DNA material is sequenced (typically 400–800 base pairs)[16] to obtain the DNA barcode. Amplification of eDNA material is usually focused on smaller fragment sizes (<200 base pairs), as eDNA is more likely to be fragmented than DNA material from other sources. However, some studies argue that there is no relationship between amplicon size and detection rate of eDNA.[17][18]

HiSeq sequencers at SciLIfeLab in Uppsala, Sweden. The photo was taken during the excursion of SLU course PNS0169 in March 2019.

When the DNA barcode marker region has been amplified, the next step is to sequence the marker region using DNA sequencing methods.[19] Many different sequencing platforms are available, and technical development is proceeding rapidly.

Marker selection

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A schematic view of primers and target region, demonstrated on 16S rRNA gene in Pseudomonas. As primers, one typically selects short conserved sequences with low variability, which can thus amplify most or all species in the chosen target group. The primers are used to amplify a highly variable target region in between the two primers, which is then used for species discrimination. Modified from »Variable Copy Number, Intra-Genomic Heterogeneities and Lateral Transfers of the 16S rRNA Gene in Pseudomonas« by Bodilis, Josselin; Nsigue-Meilo, Sandrine; Besaury, Ludovic; Quillet, Laurent, used under CC BY, available from: https://www.researchgate.net/figure/Hypervariable-regions-within-the-16S-rRNA-gene-in-Pseudomonas-The-plotted-line-reflects_fig2_224832532.

Markers used for DNA barcoding are called barcodes. In order to successfully characterize species based on DNA barcodes, selection of informative DNA regions is crucial. A good DNA barcode should have low intra-specific and high inter-specific variability[12] and possess conserved flanking sites for developing universal PCR primers for wide taxonomic application. The goal is to design primers that will detect and distinguish most or all the species in the studied group of organisms (high taxonomic resolution). The length of the barcode sequence should be short enough to be used with current sampling source, DNA extraction, amplification and sequencing methods.[20]

Ideally, one gene sequence would be used for all taxonomic groups, from viruses to plants and animals. However, no such gene region has been found yet, so different barcodes are used for different groups of organisms,[citation needed] or depending on the study question.

For animals, the most widely used barcode is mitochondrial cytochrome C oxidase I (COI) locus.[21] Other mitochondrial genes, such as Cytb, 12S or 16S are also used. Mitochondrial genes are preferred over nuclear genes because of their lack of introns, their haploid mode of inheritance and their limited recombination.[21][22] Moreover, each cell has various mitochondria (up to several thousand) and each of them contains several circular DNA molecules. Mitochondria can therefore offer abundant source of DNA even when sample tissue is limited.[citation needed]

In plants, however, mitochondrial genes are not appropriate for DNA barcoding because they exhibit low mutation rates.[23] A few candidate genes have been found in the chloroplast genome, the most promising being maturase K gene (matK) by itself or in association with other genes. Multi-locus markers such as ribosomal internal transcribed spacers (ITS DNA) along with matK, rbcL, trnH or other genes have also been used for species identification.[citation needed] The best discrimination between plant species has been achieved when using two or more chloroplast barcodes.[24]

For bacteria, the small subunit of ribosomal RNA (16S) gene can be used for different taxa, as it is highly conserved.[25] Some studies suggest COI,[26] type II chaperonin (cpn60)[27] or β subunit of RNA polymerase (rpoB)[28] also could serve as bacterial DNA barcodes.

Barcoding fungi is more challenging, and more than one primer combination might be required.[29] The COI marker performs well in certain fungi groups,[30] but not equally well in others.[31] Therefore, additional markers are being used, such as ITS rDNA and the large subunit of nuclear ribosomal RNA (28S LSU rRNA).[32]

Within the group of protists, various barcodes have been proposed, such as the D1–D2 or D2–D3 regions of 28S rDNA, V4 subregion of 18S rRNA gene, ITS rDNA and COI. Additionally, some specific barcodes can be used for photosynthetic protists, for example the large subunit of ribulose-1,5-bisphosphate carboxylase-oxygenase gene (rbcL) and the chloroplastic 23S rRNA gene.[citation needed]

Reference libraries and bioinformatics

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Reference libraries are used for the taxonomic identification, also called annotation, of sequences obtained from barcoding or metabarcoding. These databases contain the DNA barcodes assigned to previously identified taxa. Most reference libraries do not cover all species within an organism group, and new entries are continually created. In the case of macro- and many microorganisms (such as algae), these reference libraries require detailed documentation (sampling location and date, person who collected it, image, etc.) and authoritative taxonomic identification of the voucher specimen, as well as submission of sequences in a particular format. However, such standards are fulfilled for only a small number of species. The process also requires the storage of voucher specimens in museum collections, herbaria and other collaborating institutions. Both taxonomically comprehensive coverage and content quality are important for identification accuracy.[33] In the microbial world, there is no DNA information for most species names, and many DNA sequences cannot be assigned to any Linnaean binomial.[34] Several reference databases exist depending on the organism group and the genetic marker used. There are smaller, national databases (e.g. FinBOL), and large consortia like the International Barcode of Life Project (iBOL).[35]

BOLD

Launched in 2007, the Barcode of Life Data System (BOLD)[36] is one of the biggest databases, containing about 780 000 BINs (Barcode Index Numbers) in 2022. It is a freely accessible repository for the specimen and sequence records for barcode studies, and it is also a workbench aiding the management, quality assurance and analysis of barcode data. The database mainly contains BIN records for animals based on the COI genetic marker. For plant identification, BOLD accepts sequences from matK and rbcL.

UNITE

The UNITE database[37] was launched in 2003 and is a reference database for the molecular identification of fungal (and since 2018 all eukaryotic) species with the nuclear ribosomal internal transcribed spacer (ITS) genetic marker region. This database is based on the concept of species hypotheses: you choose the % at which you want to work, and the sequences are sorted in comparison to sequences obtained from voucher specimens identified by experts.

Diat.barcode[permanent dead link‍]

Diat.barcode[38] database was first published under the name R-syst::diatom[39] in 2016 starting with data from two sources: the Thonon culture collection (TCC) in the hydrobiological station of the French National Institute for Agricultural Research (INRA), and from the NCBI (National Center for Biotechnology Information) nucleotide database. Diat.barcode provides data for two genetic markers, rbcL (Ribulose-1,5-bisphosphate carboxylase/oxygenase) and 18S (18S ribosomal RNA). The database also involves additional, trait information of species, like morphological characteristics (biovolume, size dimensions, etc.), life-forms (mobility, colony-type, etc.) or ecological features (pollution sensitivity, etc.).

Bioinformatic analysis

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In order to obtain well structured, clean and interpretable data, raw sequencing data must be processed using bioinformatic analysis. The FASTQ file with the sequencing data contains two types of information: the sequences detected in the sample (FASTA file) and a quality file with quality scores (PHRED scores) associated with each nucleotide of each DNA sequence. The PHRED scores indicate the probability with which the associated nucleotide has been correctly scored.

PHRED quality score and the associated certainty level
10 90%
20 99%
30 99.9%
40 99.99%
50 99.999%

In general, the PHRED score decreases towards the end of each DNA sequence. Thus some bioinformatics pipelines simply cut the end of the sequences at a defined threshold.

Some sequencing technologies, like MiSeq, use paired-end sequencing during which sequencing is performed from both directions producing better quality. The overlapping sequences are then aligned into contigs and merged. Usually, several samples are pooled in one run, and each sample is characterized by a short DNA fragment, the tag. In a demultiplexing step, sequences are sorted using these tags to reassemble the separate samples. Before further analysis, tags and other adapters are removed from the barcoding sequence DNA fragment. During trimming, the bad quality sequences (low PHRED scores), or sequences that are much shorter or longer than the targeted DNA barcode, are removed. The following dereplication step is the process where all of the quality-filtered sequences are collapsed into a set of unique reads (individual sequence units ISUs) with the information of their abundance in the samples. After that, chimeras (i.e. compound sequences formed from pieces of mixed origin) are detected and removed. Finally, the sequences are clustered into OTUs (Operational Taxonomic Units), using one of many clustering strategies. The most frequently used bioinformatic software include Mothur,[40] Uparse,[41] Qiime,[42] Galaxy,[43] Obitools,[44] JAMP,[45] Barque,[46] and DADA2.[47]

Comparing the abundance of reads, i.e. sequences, between different samples is still a challenge because both the total number of reads in a sample as well as the relative amount of reads for a species can vary between samples, methods, or other variables. For comparison, one may then reduce the number of reads of each sample to the minimal number of reads of the samples to be compared – a process called rarefaction. Another way is to use the relative abundance of reads.[48]

Species identification and taxonomic assignment

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The taxonomic assignment of the OTUs to species is achieved by matching of sequences to reference libraries. The Basic Local Alignment Search Tool (BLAST) is commonly used to identify regions of similarity between sequences by comparing sequence reads from the sample to sequences in reference databases.[49] If the reference database contains sequences of the relevant species, then the sample sequences can be identified to species level. If a sequence cannot be matched to an existing reference library entry, DNA barcoding can be used to create a new entry.

In some cases, due to the incompleteness of reference databases, identification can only be achieved at higher taxonomic levels, such as assignment to a family or class. In some organism groups such as bacteria, taxonomic assignment to species level is often not possible. In such cases, a sample may be assigned to a particular operational taxonomic unit (OTU).

In some cases, specimens with identical (COI) DNA barcodes clearly belong to different species, e.g. species of the fish genus Chromis.[50]

Applications

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Applications of DNA barcoding include identification of new species, safety assessment of food, identification and assessment of cryptic species, detection of alien species, identification of endangered and threatened species,[51] linking egg and larval stages to adult species, securing intellectual property rights for bioresources, framing global management plans for conservation strategies, elucidate feeding niches,[52] and forensic science.[53] DNA barcode markers can be applied to address basic questions in systematics, ecology, evolutionary biology and conservation, including community assembly, species interaction networks, taxonomic discovery, and assessing priority areas for environmental protection.

Identification of species

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Specific short DNA sequences or markers from a standardized region of the genome can provide a DNA barcode for identifying species.[54] Molecular methods are especially useful when traditional methods are not applicable. DNA barcoding has great applicability in identification of larvae for which there are generally few diagnostic characters available, and in association of different life stages (e.g. larval and adult) in many animals.[55] Identification of species listed in the Convention of the International Trade of Endangered Species (CITES) appendixes using barcoding techniques is used in monitoring of illegal trade.[56]

Detection of invasive species

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Alien species can be detected via barcoding.[57][58] Barcoding can be suitable for detection of species in e.g. border control, where rapid and accurate morphological identification is often not possible due to similarities between different species, lack of sufficient diagnostic characteristics[57] and/or lack of taxonomic expertise. Barcoding and metabarcoding can also be used to screen ecosystems for invasive species, and to distinguish between an invasive species and native, morphologically similar, species.[59] The high efficiency of DNA identification is shown relative to the traditional monitoring of biological invasions.[60]

Delimiting cryptic species

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DNA barcoding enables the identification and recognition of cryptic species.[61] The results of DNA barcoding analyses depend however upon the choice of analytical methods, so the process of delimiting cryptic species using DNA barcodes can be as subjective as any other form of taxonomy. Hebert et al. (2004) concluded that the butterfly Astraptes fulgerator in north-western Costa Rica actually consists of 10 different species.[62] These results, however, were subsequently challenged by Brower (2006), who pointed out numerous serious flaws in the analysis, and concluded that the original data could support no more than the possibility of three to seven cryptic taxa rather than ten cryptic species.[63] Smith et al. (2007) used cytochrome c oxidase I DNA barcodes for species identification of the 20 morphospecies of Belvosia parasitoid flies (Diptera: Tachinidae) reared from caterpillars (Lepidoptera) in Area de Conservación Guanacaste (ACG), northwestern Costa Rica. These authors discovered that barcoding raises the species count to 32, by revealing that each of the three parasitoid species, previously considered as generalists, actually are arrays of highly host-specific cryptic species.[64] For 15 morphospecies of polychaetes within the deep Antarctic benthos studied through DNA barcoding, cryptic diversity was found in 50% of the cases. Furthermore, 10 previously overlooked morphospecies were detected, increasing the total species richness in the sample by 233%.[65]

Barcoding is a tool to vouch for food quality. Here, DNA from traditional Norwegian Christmas food is extracted at the molecular systematic lab at NTNU University Museum.

Diet analysis and food web application

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DNA barcoding and metabarcoding can be useful in diet analysis studies,[66] and is typically used if prey specimens cannot be identified based on morphological characters.[67][68] There is a range of sampling approaches in diet analysis: DNA metabarcoding can be conducted on stomach contents,[69] feces,[68][70] saliva[71] or whole body analysis.[51][72] In fecal samples or highly digested stomach contents, it is often not possible to distinguish tissue from single species, and therefore metabarcoding can be applied instead.[68][73] Feces or saliva represent non-invasive sampling approaches, while whole body analysis often means that the individual needs to be killed first. For smaller organisms, sequencing for stomach content is then often done by sequencing the entire animal.

Barcoding for food safety

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DNA barcoding represents an essential tool to evaluate the quality of food products. The purpose is to guarantee food traceability, to minimize food piracy, and to valuate local and typical agro-food production. Another purpose is to safeguard public health; for example, metabarcoding offers the possibility to identify groupers causing Ciguatera fish poisoning from meal remnants,[74] or to separate poisonous mushrooms from edible ones (Ref).

Biomonitoring and ecological assessment

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DNA barcoding can be used to assess the presence of endangered species for conservation efforts (Ref), or the presence of indicator species reflective to specific ecological conditions (Ref), for example excess nutrients or low oxygen levels.

Forensic Science

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DNA barcoding is often used for species identification in forensic science cases. Unknown animal or plant samples at crime scenes can be found, collected, and identified, in hopes of linking it to a suspect and getting a conviction.[75] Poaching, killing of endangered species, and animal abuse are examples of crimes where DNA barcoding is used, since animal DNA is often found.[53][76] On the other hand, plant DNA is usually used as trace evidence to link a suspect to a crime scene.[77]

Potentials and shortcomings

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Potentials

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Traditional bioassessment methods are well established internationally, and serve biomonitoring well, as for example for aquatic bioassessment within the EU Directives WFD and MSFD. However, DNA barcoding could improve traditional methods for the following reasons; DNA barcoding (i) can increase taxonomic resolution and harmonize the identification of taxa which are difficult to identify or lack experts, (ii) can more accurately/precisely relate environmental factors to specific taxa (iii) can increase comparability among regions, (iv) allows for the inclusion of early life stages and fragmented specimens, (v) allows delimitation of cryptic/rare species (vi) allows for development of new indices e.g. rare/cryptic species which may be sensitive/tolerant to stressors, (vii) increases the number of samples which can be processed and reduces processing time resulting in increased knowledge of species ecology, (viii) is a non-invasive way of monitoring when using eDNA methods.[78]

Time and cost

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DNA barcoding is faster than traditional morphological methods all the way from training through to taxonomic assignment. It takes less time to gain expertise in DNA methods than becoming an expert in taxonomy. In addition, the DNA barcoding workflow (i.e. from sample to result) is generally quicker than traditional morphological workflow and allows the processing of more samples.

Taxonomic resolution

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DNA barcoding allows the resolution of taxa from higher (e.g. family) to lower (e.g. species) taxonomic levels, that are otherwise too difficult to identify using traditional morphological methods, like e.g. identification via microscopy. For example, Chironomidae (the non-biting midge) are widely distributed in both terrestrial and freshwater ecosystems. Their richness and abundance make them important for ecological processes and networks, and they are one of many invertebrate groups used in biomonitoring. Invertebrate samples can contain as many as 100 species of chironomids which often make up as much as 50% of a sample. Despite this, they are usually not identified below the family level because of the taxonomic expertise and time required.[79] This may result in different chironomid species with different ecological preferences grouped together, resulting in inaccurate assessment of water quality.

DNA barcoding provides the opportunity to resolve taxa, and directly relate stressor effects to specific taxa such as individual chironomid species. For example, Beermann et al. (2018) DNA barcoded Chironomidae to investigate their response to multiple stressors; reduced flow, increased fine-sediment and increased salinity.[80] After barcoding, it was found that the chironomid sample consisted of 183 Operational Taxonomic Units (OTUs), i.e. barcodes (sequences) that are often equivalent to morphological species. These 183 OTUs displayed 15 response types rather than the previously reported [81] two response types recorded when all chironomids were grouped together in the same multiple stressor study. A similar trend was discovered in a study by Macher et al. (2016) which discovered cryptic diversity within the New Zealand mayfly species Deleatidium sp. This study found different response patterns of 12 molecular distinct OTUs to stressors which may change the consensus that this mayfly is sensitive to pollution.[82]

Shortcomings

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Despite the advantages offered by DNA barcoding, it has also been suggested that DNA barcoding is best used as a complement to traditional morphological methods.[78] This recommendation is based on multiple perceived challenges.

Physical parameters

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It is not completely straightforward to connect DNA barcodes with ecological preferences of the barcoded taxon in question, as is needed if barcoding is to be used for biomonitoring. For example, detecting target DNA in aquatic systems depends on the concentration of DNA molecules at a site, which in turn can be affected by many factors. The presence of DNA molecules also depends on dispersion at a site, e.g. direction or strength of currents. It is not really known how DNA moves around in streams and lakes, which makes sampling difficult. Another factor might be the behavior of the target species, e.g. fish can have seasonal changes of movements, crayfish or mussels will release DNA in larger amounts just at certain times of their life (moulting, spawning). For DNA in soil, even less is known about distribution, quantity or quality.

The major limitation of the barcoding method is that it relies on barcode reference libraries for the taxonomic identification of the sequences. The taxonomic identification is accurate only if a reliable reference is available. However, most databases are still incomplete, especially for smaller organisms e.g. fungi, phytoplankton, nematoda etc. In addition, current databases contain misidentifications, spelling mistakes and other errors. There is massive curation and completion effort around the databases for all organisms necessary, involving large barcoding projects (for example the iBOL project for the Barcode of Life Data Systems (BOLD) reference database).[83][84] However, completion and curation are difficult and time-consuming. Without vouchered specimens, there can be no certainty about whether the sequence used as a reference is correct.

DNA sequence databases like GenBank contain many sequences that are not tied to vouchered specimens (for example, herbarium specimens, cultured cell lines, or sometimes images). This is problematic in the face of taxonomic issues such as whether several species should be split or combined, or whether past identifications were sound. Reusing sequences, not tied to vouchered specimens, of initially misidentified organism may support incorrect conclusions and must be avoided.[85] Therefore, best practice for DNA barcoding is to sequence vouchered specimens.[86][87] For many taxa, it can be however difficult to obtain reference specimens, for example with specimens that are difficult to catch, available specimens are poorly conserved, or adequate taxonomic expertise is lacking.[85]

Importantly, DNA barcodes can also be used to create interim taxonomy, in which case OTUs can be used as substitutes for traditional Latin binomials – thus significantly reducing dependency on fully populated reference databases.[88]

Technological bias

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DNA barcoding also carries methodological bias, from sampling to bioinformatics data analysis. Beside the risk of contamination of the DNA sample by PCR inhibitors, primer bias is one of the major sources of errors in DNA barcoding.[89][90] The isolation of an efficient DNA marker and the design of primers is a complex process and considerable effort has been made to develop primers for DNA barcoding in different taxonomic groups.[91] However, primers will often bind preferentially to some sequences, leading to differential primer efficiency and specificity and unrepresentative communities’ assessment and richness inflation.[92] Thus, the composition of the sample's communities sequences is mainly altered at the PCR step.  Besides, PCR replication is often required, but leads to an exponential increase in the risk of contamination. Several studies have highlighted the possibility to use mitochondria-enriched samples [93][94] or PCR-free approaches to avoid these biases, but as of 2018, the DNA metabarcoding technique is still based on the sequencing of amplicons.[91] Other biases enter the picture during the sequencing and during the bioinformatic processing of the sequences, like the creation of chimeras.

Lack of standardization

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Even as DNA barcoding is more widely used and applied, there is no agreement concerning the methods for DNA preservation or extraction, the choices of DNA markers and primers set, or PCR protocols. The parameters of bioinformatics pipelines (for example OTU clustering, taxonomic assignment algorithms or thresholds etc.) are at the origin of much debate among DNA barcoding users.[91] Sequencing technologies are also rapidly evolving, together with the tools for the analysis of the massive amounts of DNA data generated, and standardization of the methods is urgently needed to enable collaboration and data sharing at greater spatial and time-scale. This standardisation of barcoding methods at the European scale is part of the objectives of the European COST Action DNAqua-net [95] and is also addressed by CEN (the European Committee for Standardization).[96]

Another criticism of DNA barcoding is its limited efficiency for accurate discrimination below species level (for example, to distinguish between varieties), for hybrid detection, and that it can be affected by evolutionary rates[citation needed].

Mismatches between conventional (morphological) and barcode based identification

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It is important to know that taxa lists derived by conventional (morphological) identification are not, and maybe never will be, directly comparable to taxa lists derived from barcode based identification because of several reasons. The most important cause is probably the incompleteness and lack of accuracy of the molecular reference databases preventing a correct taxonomic assignment of eDNA sequences. Taxa not present in reference databases will not be found by eDNA, and sequences linked to a wrong name will lead to incorrect identification.[78] Other known causes are a different sampling scale and size between a traditional and a molecular sample, the possible analysis of dead organisms, which can happen in different ways for both methods depending on organism group, and the specific selection of identification in either method, i.e. varying taxonomical expertise or possibility to identify certain organism groups, respectively primer bias leading also to a potential biased analysis of taxa.[78]

Estimates of richness/diversity

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DNA Barcoding can result in an over or underestimate of species richness and diversity. Some studies suggest that artifacts (identification of species not present in a community) are a major cause of inflated biodiversity.[97][98] The most problematic issue are taxa represented by low numbers of sequencing reads. These reads are usually removed during the data filtering process, since different studies suggest that most of these low-frequency reads may be artifacts.[99] However, real rare taxa may exist among these low-abundance reads.[100] Rare sequences can reflect unique lineages in communities which make them informative and valuable sequences. Thus, there is a strong need for more robust bioinformatics algorithms that allow the differentiation between informative reads and artifacts. Complete reference libraries would also allow a better testing of bioinformatics algorithms, by permitting a better filtering of artifacts (i.e. the removal of sequences lacking a counterpart among extant species) and therefore, it would be possible obtain a more accurate species assignment.[101] Cryptic diversity can also result in inflated biodiversity as one morphological species may actually split into many distinct molecular sequences.[78] This will go a long way in generating DNA reference data which is crucial for environmental DNA-based biodiversity monitoring.

Megabarcoding

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Megabarcoding is a term used to describe high-throughput specimen-based DNA barcoding, where thousands of specimens can be barcoded simultaneously for species identification and discovery.[102][103][104][105][106]

Megabarcoding workflow

This is enabled by the use of third-generation sequencing platforms including PacBio (Sequel I/II) by Pacific Biosciences and MinION, PromethION by Oxford Nanopore Technology. As compared to Sanger sequencing, megabarcoding is faster and cheaper, allowing for the large-scale generation of DNA barcodes for thousands of species.[107]

Applications

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Megabarcoding can help fill the dark taxa. DNA barcode reference data gap for insects and accelerate species discovery,[108][109] understand species diversity patterns,[110][111][112] evaluate species richness,[113] generate rapid biodiversity species inventories,[114] track baseline shifts,[115] and matching life-history stages.[116]

Metabarcoding

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Differences in the standard methods for DNA barcoding and metabarcoding. While DNA barcoding points to find a specific species, metabarcoding looks for the whole community.
Main article: Metabarcoding

Metabarcoding is defined as the barcoding of DNA or eDNA (environmental DNA) that allows for simultaneous identification of many taxa within the same (environmental) sample, however often within the same organism group. The main difference between the approaches is that metabarcoding, in contrast to barcoding, does not focus on one specific organism, but instead aims to determine species composition within a sample.

Methodology

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The metabarcoding procedure, like general barcoding, covers the steps of DNA extraction, PCR amplification, sequencing and data analysis. A barcode consists of a short variable gene region (for example, see different markers/barcodes) which is useful for taxonomic assignment flanked by highly conserved gene regions which can be used for primer design.[117] Different genes are used depending if the aim is to barcode single species or metabarcoding several species. In the latter case, a more universal gene is used. Metabarcoding does not use single species DNA/RNA as a starting point, but DNA/RNA from several different organisms derived from one environmental or bulk sample.

Applications

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Metabarcoding has the potential to complement biodiversity measures, and even replace them in some instances, especially as the technology advances and procedures gradually become cheaper, more optimized and widespread.[118][119]

DNA metabarcoding applications include Biodiversity monitoring in terrestrial and aquatic environments, Paleontology and ancient ecosystems, Plant-pollinator interactions, Diet analysis and Food safety.

Advantages and challenges

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The general advantages and shortcomings for barcoding reviewed above are valid also for metabarcoding. One particular drawback for metabarcoding studies is that there is no consensus yet regarding the optimal experimental design and bioinformatics criteria to be applied in eDNA metabarcoding.[120] However, there are current joined attempts, like e.g. the EU COST network DNAqua-Net, to move forward by exchanging experience and knowledge to establish best-practice standards for biomonitoring.[78]

Artificial DNA barcoding

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In 2014, researchers from ETH Zurich suggested using artificial, sub-micrometer-sized DNA barcodes as an "invisible oil tag". The barcodes consist of synthetic DNA sequences inside magnetically recoverable silica particles. They can be added to food oil in a very small amount (down to 1 ppb) as a label, and can be retrieved at any time for authenticity test by PCR/sequencing. This method can be used to test olive oil for adulteration.[121]

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References

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  1. ^ "What is DNA Barcoding?". iBOL. Retrieved 2019-03-26.
  2. ^ Kress, W. John; Erickson, David L., eds. (2012). DNA Barcodes: Methods and Protocols. Methods in Molecular Biology. Vol. 858. Totowa, NJ: Humana Press. doi:10.1007/978-1-61779-591-6. ISBN 978-1-61779-590-9. S2CID 3668979.
  3. ^ Irinyi, L.; Lackner, M.; de Hoog, G. S.; Meyer, W. (2015). "DNA barcoding of fungi causing infections in humans and animals". Fungal Biology. 120 (2): 125–136. doi:10.1016/j.funbio.2015.04.007. PMID 26781368.
  4. ^ Schoch, Conrad L.; Seifert, Keith A.; Huhndorf, Sabine; Robert, Vincent; Spouge, John L.; Levesque, C. André; Chen, Wen; Fungal Barcoding Consortium (2012). "Nuclear ribosomal internal transcribed spacer (ITS) region as a universal DNA barcode marker for Fungi" (PDF). Proceedings of the National Academy of Sciences. 109 (16): 6241–6246. doi:10.1073/pnas.1117018109. ISSN 0027-8424. PMC 3341068. PMID 22454494.
  5. ^ CBOL Plant Working Group; Hollingsworth, P. M.; Forrest, L. L.; Spouge, J. L.; Hajibabaei, M.; Ratnasingham, S.; van der Bank, M.; Chase, M. W.; Cowan, R. S. (2009-08-04). "A DNA barcode for land plants". Proceedings of the National Academy of Sciences. 106 (31): 12794–12797. doi:10.1073/pnas.0905845106. ISSN 0027-8424. PMC 2722355. PMID 19666622.
  6. ^ Paulay, Gustav; Meyer, Christopher P. (2005-11-29). "DNA Barcoding: Error Rates Based on Comprehensive Sampling". PLOS Biology. 3 (12): e422. doi:10.1371/journal.pbio.0030422. ISSN 1545-7885. PMC 1287506. PMID 16336051.
  7. ^ Soininen, Eeva M; Valentini, Alice; Coissac, Eric; Miquel, Christian; Gielly, Ludovic; Brochmann, Christian; Brysting, Anne K; Sønstebø, Jørn H; Ims, Rolf A (2009). "Analysing diet of small herbivores: the efficiency of DNA barcoding coupled with high-throughput pyrosequencing for deciphering the composition of complex plant mixtures". Frontiers in Zoology. 6 (1): 16. doi:10.1186/1742-9994-6-16. ISSN 1742-9994. PMC 2736939. PMID 19695081.
  8. ^ Creer, Simon; Deiner, Kristy; Frey, Serita; Porazinska, Dorota; Taberlet, Pierre; Thomas, W. Kelley; Potter, Caitlin; Bik, Holly M. (2016). Freckleton, Robert (ed.). "The ecologist's field guide to sequence-based identification of biodiversity" (PDF). Methods in Ecology and Evolution. 7 (9): 1008–1018. doi:10.1111/2041-210X.12574. S2CID 87512991.
  9. ^ Leese, Florian; et al. (January 2018). "Why We Need Sustainable Networks Bridging Countries, Disciplines, Cultures and Generations for Aquatic Biomonitoring 2.0: A Perspective Derived from the DNAqua-Net COST Action". Advances in Ecological Research. 58: 63–99. doi:10.1016/bs.aecr.2018.01.001. hdl:1822/72852. ISBN 9780128139493.
  10. ^ Vasselon, Valentin; Rimet, Frédéric; Tapolczai, Kálmán; Bouchez, Agnès (2017). "Assessing ecological status with diatoms DNA metabarcoding: Scaling-up on a WFD monitoring network (Mayotte island, France)". Ecological Indicators. 82: 1–12. doi:10.1016/j.ecolind.2017.06.024. ISSN 1470-160X.
  11. ^ Woese, Carl R.; Kandler, Otto; Wheelis, Mark L. (1990). "Towards a natural system of organisms: proposal for the domains Archaea, Bacteria, and Eucarya" (PDF). Proceedings of the National Academy of Sciences. 87 (12): 4576–4579. Bibcode:1990PNAS...87.4576W. doi:10.1073/pnas.87.12.4576. OCLC 678728346. PMC 54159. PMID 2112744.
  12. ^ a b c Hebert, Paul D. N.; Cywinska, Alina; Ball, Shelley L.; deWaard, Jeremy R. (2003-02-07). "Biological identifications through DNA barcodes". Proceedings of the Royal Society B: Biological Sciences. 270 (1512): 313–321. doi:10.1098/rspb.2002.2218. ISSN 1471-2954. PMC 1691236. PMID 12614582.
  13. ^ Folmer, O.; Black, M.; Hoeh, W.; Lutz, R.; Vrijenhoek, R. (October 1994). "DNA primers for amplification of mitochondrial cytochrome c oxidase subunit I from diverse metazoan invertebrates". Molecular Marine Biology and Biotechnology. 3 (5): 294–299. ISSN 1053-6426. PMID 7881515.
  14. ^ Jelger Herder, Environmental DNA - a review of the possible applications for the detection of (invasive) species.
  15. ^ Schrader, C Then it can be this way because of DNA.; Schielke, A.; Ellerbroek, L.; Johne, R. (2012). "PCR inhibitors – occurrence, properties and removal". Journal of Applied Microbiology. 113 (5): 1014–1026. doi:10.1111/j.1365-2672.2012.05384.x. ISSN 1365-2672. PMID 22747964. S2CID 30892831.
  16. ^ Savolainen, Vincent; Cowan, Robyn S; Vogler, Alfried P; Roderick, George K; Lane, Richard (2005-10-29). "Towards writing the encyclopaedia of life: an introduction to DNA barcoding". Philosophical Transactions of the Royal Society B: Biological Sciences. 360 (1462): 1805–1811. doi:10.1098/rstb.2005.1730. ISSN 0962-8436. PMC 1609222. PMID 16214739.
  17. ^ Piggott, Maxine P. (2016). "Evaluating the effects of laboratory protocols on eDNA detection probability for an endangered freshwater fish". Ecology and Evolution. 6 (9): 2739–2750. doi:10.1002/ece3.2083. ISSN 2045-7758. PMC 4798829. PMID 27066248.
  18. ^ Ma, Hongjuan; Stewart, Kathryn; Lougheed, Stephen; Zheng, Jinsong; Wang, Yuxiang; Zhao, Jianfu (2016). "Characterization, optimization, and validation of environmental DNA (eDNA) markers to detect an endangered aquatic mammal". Conservation Genetics Resources. 8 (4): 561–568. doi:10.1007/s12686-016-0597-9. ISSN 1877-7252. S2CID 1613649.
  19. ^ D’Amore, Rosalinda; Ijaz, Umer Zeeshan; Schirmer, Melanie; Kenny, John G.; Gregory, Richard; Darby, Alistair C.; Shakya, Migun; Podar, Mircea; Quince, Christopher (2016-01-14). "A comprehensive benchmarking study of protocols and sequencing platforms for 16S rRNA community profiling". BMC Genomics. 17 (1): 55. doi:10.1186/s12864-015-2194-9. ISSN 1471-2164. PMC 4712552. PMID 26763898.
  20. ^ Kress, W. J.; Erickson, D. L. (2008-02-26). "DNA barcodes: Genes, genomics, and bioinformatics". Proceedings of the National Academy of Sciences. 105 (8): 2761–2762. Bibcode:2008PNAS..105.2761K. doi:10.1073/pnas.0800476105. ISSN 0027-8424. PMC 2268532. PMID 18287050.
  21. ^ a b Hebert, Paul D.N.; Ratnasingham, Sujeevan; de Waard, Jeremy R. (2003-08-07). "Barcoding animal life: cytochrome c oxidase subunit 1 divergences among closely related species". Proceedings of the Royal Society B: Biological Sciences. 270 (suppl_1): S96-9. doi:10.1098/rsbl.2003.0025. ISSN 1471-2954. PMC 1698023. PMID 12952648.
  22. ^ Blaxter, Mark L. (2004-04-29). Godfray, H. C. J.; Knapp, S. (eds.). "The promise of a DNA taxonomy". Philosophical Transactions of the Royal Society of London. Series B: Biological Sciences. 359 (1444): 669–679. doi:10.1098/rstb.2003.1447. ISSN 1471-2970. PMC 1693355. PMID 15253352.
  23. ^ Fazekas, Aron J.; Burgess, Kevin S.; Kesanakurti, Prasad R.; Graham, Sean W.; Newmaster, Steven G.; Husband, Brian C.; Percy, Diana M.; Hajibabaei, Mehrdad; Barrett, Spencer C. H. (2008-07-30). DeSalle, Robert (ed.). "Multiple Multilocus DNA Barcodes from the Plastid Genome Discriminate Plant Species Equally Well". PLOS ONE. 3 (7): e2802. Bibcode:2008PLoSO...3.2802F. doi:10.1371/journal.pone.0002802. ISSN 1932-6203. PMC 2475660. PMID 18665273.
  24. ^ Kress, W. John; Erickson, David L. (2007-06-06). Shiu, Shin-Han (ed.). "A Two-Locus Global DNA Barcode for Land Plants: The Coding rbcL Gene Complements the Non-Coding trnH-psbA Spacer Region". PLOS ONE. 2 (6): e508. Bibcode:2007PLoSO...2..508K. doi:10.1371/journal.pone.0000508. ISSN 1932-6203. PMC 1876818. PMID 17551588.
  25. ^ Janda, J. M.; Abbott, S. L. (2007-09-01). "16S rRNA Gene Sequencing for Bacterial Identification in the Diagnostic Laboratory: Pluses, Perils, and Pitfalls". Journal of Clinical Microbiology. 45 (9): 2761–2764. doi:10.1128/JCM.01228-07. ISSN 0095-1137. PMC 2045242. PMID 17626177.
  26. ^ Smith, M. Alex; Bertrand, Claudia; Crosby, Kate; Eveleigh, Eldon S.; Fernandez-Triana, Jose; Fisher, Brian L.; Gibbs, Jason; Hajibabaei, Mehrdad; Hallwachs, Winnie (2012-05-02). Badger, Jonathan H. (ed.). "Wolbachia and DNA barcoding insects: Patterns, potential, and problems". PLOS ONE. 7 (5): e36514. Bibcode:2012PLoSO...736514S. doi:10.1371/journal.pone.0036514. ISSN 1932-6203. PMC 3342236. PMID 22567162.
  27. ^ Links, Matthew G.; Dumonceaux, Tim J.; Hemmingsen, Sean M.; Hill, Janet E. (2012-11-26). Neufeld, Josh (ed.). "The Chaperonin-60 Universal Target Is a Barcode for Bacteria That Enables De Novo Assembly of Metagenomic Sequence Data". PLOS ONE. 7 (11): e49755. Bibcode:2012PLoSO...749755L. doi:10.1371/journal.pone.0049755. ISSN 1932-6203. PMC 3506640. PMID 23189159.
  28. ^ Case, R. J.; Boucher, Y.; Dahllof, I.; Holmstrom, C.; Doolittle, W. F.; Kjelleberg, S. (2007-01-01). "Use of 16S rRNA and rpoB Genes as Molecular Markers for Microbial Ecology Studies". Applied and Environmental Microbiology. 73 (1): 278–288. Bibcode:2007ApEnM..73..278C. doi:10.1128/AEM.01177-06. ISSN 0099-2240. PMC 1797146. PMID 17071787.
  29. ^ Bellemain, Eva; Carlsen, Tor; Brochmann, Christian; Coissac, Eric; Taberlet, Pierre; Kauserud, Håvard (2010). "ITS as an environmental DNA barcode for fungi: an in silico approach reveals potential PCR biases". BMC Microbiology. 10 (1): 189. doi:10.1186/1471-2180-10-189. ISSN 1471-2180. PMC 2909996. PMID 20618939.
  30. ^ Seifert, K. A.; Samson, R. A.; deWaard, J. R.; Houbraken, J.; Levesque, C. A.; Moncalvo, J.-M.; Louis-Seize, G.; Hebert, P. D. N. (2007-03-06). "Prospects for fungus identification using CO1 DNA barcodes, with Penicillium as a test case". Proceedings of the National Academy of Sciences. 104 (10): 3901–3906. doi:10.1073/pnas.0611691104. ISSN 0027-8424. PMC 1805696. PMID 17360450.
  31. ^ Dentinger, Bryn T. M.; Didukh, Maryna Y.; Moncalvo, Jean-Marc (2011-09-22). Schierwater, Bernd (ed.). "Comparing COI and ITS as DNA Barcode Markers for Mushrooms and Allies (Agaricomycotina)". PLOS ONE. 6 (9): e25081. Bibcode:2011PLoSO...625081D. doi:10.1371/journal.pone.0025081. ISSN 1932-6203. PMC 3178597. PMID 21966418.
  32. ^ Khaund, Polashree; Joshi, S.R. (October 2014). "DNA barcoding of wild edible mushrooms consumed by the ethnic tribes of India". Gene. 550 (1): 123–130. doi:10.1016/j.gene.2014.08.027. PMID 25130907.
  33. ^ Weigand, Hannah; Beermann, Arne J.; Čiampor, Fedor; Costa, Filipe O.; Csabai, Zoltán; Duarte, Sofia; Geiger, Matthias F.; Grabowski, Michał; Rimet, Frédéric (2019-03-14). "DNA barcode reference libraries for the monitoring of aquatic biota in Europe: Gap-analysis and recommendations for future work". bioRxiv. 678: 499–524. Bibcode:2019ScTEn.678..499W. doi:10.1101/576553. hdl:11250/2608962. PMID 31077928. S2CID 92160002.
  34. ^ Gottschling M, J Chacón, A Žerdoner Čalasan, St Neuhaus, J Kretschmann, H Stibor & U John (2020): Phylogenetic placement of environmental sequences using taxonomically reliable databases helps to rigorously assess dinophyte biodiversity in Bavarian lakes (Germany). Freshw Biol 65: 193–208. doi:10.1111/fwb.13413
  35. ^ Rdmpage (2016), International Barcode of Life project (iBOL) (Data Set), Institute of Biodiversity, Animal Health and Comparative Medicine, College of Medical, Veterinary and Life Sciences, University of Glasgow, doi:10.15468/inygc6, retrieved 2019-05-14
  36. ^ Ratnasingham, Sujeevan; Hebert, Paul D. N. (2007-01-24). "BARCODING: bold: The Barcode of Life Data System (http://www.barcodinglife.org): BARCODING". Molecular Ecology Notes. 7 (3): 355–364. doi:10.1111/j.1471-8286.2007.01678.x. PMC 1890991. PMID 18784790. {{cite journal}}: External link in |title= (help)
  37. ^ Nilsson, Rolf Henrik; Larsson, Karl-Henrik; Taylor, Andy F. S.; Bengtsson-Palme, Johan; Jeppesen, Thomas S.; Schigel, Dmitry; Kennedy, Peter; Picard, Kathryn; Glöckner, Frank Oliver (2019-01-08). "The UNITE database for molecular identification of fungi: handling dark taxa and parallel taxonomic classifications". Nucleic Acids Research. 47 (D1): D259 – D264. doi:10.1093/nar/gky1022. ISSN 0305-1048. PMC 6324048. PMID 30371820.
  38. ^ Rimet, Frederic; Gusev, Evgenuy; Kahlert, Maria; Kelly, Martyn; Kulikovskiy, Maxim; Maltsev, Yevhen; Mann, David; Pfannkuchen, Martin; Trobajo, Rosa (2019-02-14). "Diat.barcode, an open-access barcode library for diatoms". data.inrae.fr (Data Set). Portail Data Inra. doi:10.15454/TOMBYZ.
  39. ^ Rimet, Frédéric; Chaumeil, Philippe; Keck, François; Kermarrec, Lenaïg; Vasselon, Valentin; Kahlert, Maria; Franc, Alain; Bouchez, Agnès (2016). "R-Syst::diatom: an open-access and curated barcode database for diatoms and freshwater monitoring". Database. 2016: baw016. doi:10.1093/database/baw016. ISSN 1758-0463. PMC 4795936. PMID 26989149.
  40. ^ Schloss, Patrick D.; Westcott, Sarah L.; Ryabin, Thomas; Hall, Justine R.; Hartmann, Martin; Hollister, Emily B.; Lesniewski, Ryan A.; Oakley, Brian B.; Parks, Donovan H.; Robinson, Courtney J.; Sahl, Jason W.; Stres, Blaž.; Thallinger, Gerhard G.; Horn, David J.; van. Weber, Caroly F. (2009). "Introducing mothur : open-source, platform-independent, community-supported software for describing and comparing microbial communities". Applied and Environmental Microbiology. 75 (23): 7537–41. Bibcode:2009ApEnM..75.7537S. doi:10.1128/AEM.01541-09. OCLC 780918718. PMC 2786419. PMID 19801464.
  41. ^ Edgar, Robert C (2013-08-18). "UPARSE: highly accurate OTU sequences from microbial amplicon reads". Nature Methods. 10 (10): 996–998. doi:10.1038/nmeth.2604. ISSN 1548-7091. PMID 23955772. S2CID 7181682.
  42. ^ Caporaso, J Gregory; Kuczynski, Justin; Stombaugh, Jesse; Bittinger, Kyle; Bushman, Frederic D; Costello, Elizabeth K; Fierer, Noah; Peña, Antonio Gonzalez; Goodrich, Julia K (May 2010). "QIIME allows analysis of high-throughput community sequencing data". Nature Methods. 7 (5): 335–336. doi:10.1038/nmeth.f.303. ISSN 1548-7091. PMC 3156573. PMID 20383131.
  43. ^ Afgan, Enis; Baker, Dannon; Batut, Bérénice; van den Beek, Marius; Bouvier, Dave; Čech, Martin; Chilton, John; Clements, Dave; Coraor, Nate (2018-07-02). "The Galaxy platform for accessible, reproducible and collaborative biomedical analyses: 2018 update". Nucleic Acids Research. 46 (W1): W537 – W544. doi:10.1093/nar/gky379. ISSN 0305-1048. PMC 6030816. PMID 29790989.
  44. ^ Boyer, Frédéric; Mercier, Céline; Bonin, Aurélie; Le Bras, Yvan; Taberlet, Pierre; Coissac, Eric (2015-05-26). "obitools: aunix-inspired software package for DNA metabarcoding". Molecular Ecology Resources. 16 (1): 176–182. doi:10.1111/1755-0998.12428. ISSN 1755-098X. PMID 25959493. S2CID 39412858.
  45. ^ Elbrecht, Vasco (2019-04-30), GitHub - VascoElbrecht/JAMP: JAMP: Just Another Metabarcoding Pipeline., retrieved 2019-05-14
  46. ^ Normandeau, Eric (2020-01-21), GitHub - enormandeau/barque: Barque: Environmental DNA metabarcoding analysis., retrieved 2020-01-21
  47. ^ Callahan, Benjamin J; McMurdie, Paul J; Rosen, Michael J; Han, Andrew W; Johnson, Amy Jo A; Holmes, Susan P (July 2016). "DADA2: High-resolution sample inference from Illumina amplicon data". Nature Methods. 13 (7): 581–583. doi:10.1038/nmeth.3869. ISSN 1548-7091. PMC 4927377. PMID 27214047.
  48. ^ McMurdie, Paul J.; Holmes, Susan (2014). "Waste Not, Want Not: Why Rarefying Microbiome Data is Inadmissible". PLOS Computational Biology. 10 (4): e1003531. arXiv:1310.0424. Bibcode:2014PLSCB..10E3531M. doi:10.1371/journal.pcbi.1003531. PMC 3974642. PMID 24699258.
  49. ^ Valiente, Gabriel; Jansson, Jesper; Clemente, Jose Carlos; Alonso-Alemany, Daniel (2011-10-10). "Taxonomic Assignment in Metagenomics with TANGO". EMBnet.journal. 17 (2): 16–20. doi:10.14806/ej.17.2.237. hdl:2117/16286. ISSN 2226-6089.
  50. ^ Pyle, Richard L.; Earle, John L.; Greene, Brian D. (2008-01-01). "Five new species of the damselfish genus Chromis (Perciformes: Labroidei: Pomacentridae) from deep coral reefs in the tropical western Pacific". Zootaxa. 1671 (1). doi:10.11646/zootaxa.1671.1.2. ISSN 1175-5334.
  51. ^ a b Schnell, Ida Bærholm; Thomsen, Philip Francis; Wilkinson, Nicholas; Rasmussen, Morten; Jensen, Lars R.D.; Willerslev, Eske; Bertelsen, Mads F.; Gilbert, M. Thomas P. (April 2012). "Screening mammal biodiversity using DNA from leeches". Current Biology. 22 (8): R262 – R263. doi:10.1016/j.cub.2012.02.058. PMID 22537625. S2CID 18058748.
  52. ^ Subrata., Trivedi (2016). DNA Barcoding in Marine Perspectives : Assessment and Conservation of Biodiversity. Ansari, Abid Ali., Ghosh, Sankar K., Rehman, Hasibur. Cham: Springer International Publishing. ISBN 9783319418407. OCLC 958384953.
  53. ^ a b Dalton, Desiré Lee; de Bruyn, Marli; Thompson, Tia; Kotzé, Antoinette (2020-12-01). "Assessing the utility of DNA barcoding in wildlife forensic cases involving South African antelope". Forensic Science International: Reports. 2: 100071. doi:10.1016/j.fsir.2020.100071. ISSN 2665-9107. S2CID 213926390.
  54. ^ Hebert, Paul D. N.; Stoeckle, Mark Y.; Zemlak, Tyler S.; Francis, Charles M. (October 2004). "Identification of Birds through DNA Barcodes". PLOS Biology. 2 (10): e312. doi:10.1371/journal.pbio.0020312. ISSN 1545-7885. PMC 518999. PMID 15455034.
  55. ^ Costa, Filipe O; Carvalho, Gary R (December 2007). "The Barcode of Life Initiative: synopsis and prospective societal impacts of DNA barcoding of Fish". Genomics, Society and Policy. 3 (2): 29. doi:10.1186/1746-5354-3-2-29. ISSN 1746-5354. PMC 5425017.
  56. ^ Lahaye, R.; van der Bank, M.; Bogarin, D.; Warner, J.; Pupulin, F.; Gigot, G.; Maurin, O.; Duthoit, S.; Barraclough, T. G. (2008-02-26). "DNA barcoding the floras of biodiversity hotspots". Proceedings of the National Academy of Sciences. 105 (8): 2923–2928. doi:10.1073/pnas.0709936105. ISSN 0027-8424. PMC 2268561. PMID 18258745.
  57. ^ a b Xu, Song-Zhi; Li, Zhen-Yu; Jin, Xiao-Hua (January 2018). "DNA barcoding of invasive plants in China: A resource for identifying invasive plants". Molecular Ecology Resources. 18 (1): 128–136. doi:10.1111/1755-0998.12715. PMID 28865184. S2CID 24911390.
  58. ^ Liu, Junning; Jiang, Jiamei; Song, Shuli; Tornabene, Luke; Chabarria, Ryan; Naylor, Gavin J. P.; Li, Chenhong (December 2017). "Multilocus DNA barcoding – Species Identification with Multilocus Data". Scientific Reports. 7 (1): 16601. Bibcode:2017NatSR...716601L. doi:10.1038/s41598-017-16920-2. ISSN 2045-2322. PMC 5709489. PMID 29192249.
  59. ^ Nagoshi, Rodney N.; Brambila, Julieta; Meagher, Robert L. (November 2011). "Use of DNA barcodes to identify invasive armyworm Spodoptera species in Florida". Journal of Insect Science. 11 (154): 154. doi:10.1673/031.011.15401. ISSN 1536-2442. PMC 3391933. PMID 22239735.
  60. ^ Karabanov, D.P.; Bekker, E.I.; Pavlov, D.D.; Borovikova, E.A.; Kodukhova, Y.V.; Kotov, A.A. (1 February 2022). "New Sets of Primers for DNA Identification of Non-Indigenous Fish Species in the Volga-Kama Basin (European Russia)". Water. 14 (3): 437. doi:10.3390/w14030437. ISSN 2073-4441.
  61. ^ Thongtam na Ayudhaya, Pradipunt; Muangmai, Narongrit; Banjongsat, Nuwadee; Singchat, Worapong; Janekitkarn, Sommai; Peyachoknagul, Surin; Srikulnath, Kornsorn (June 2017). "Unveiling cryptic diversity of the anemonefish genera Amphiprion and Premnas (Perciformes: Pomacentridae) in Thailand with mitochondrial DNA barcodes". Agriculture and Natural Resources. 51 (3): 198–205. doi:10.1016/j.anres.2017.07.001.
  62. ^ Hebert, P. D. N.; Penton, E. H.; Burns, J. M.; Janzen, D. H.; Hallwachs, W. (2004-10-12). "Ten species in one: DNA barcoding reveals cryptic species in the neotropical skipper butterfly Astraptes fulgerator". Proceedings of the National Academy of Sciences. 101 (41): 14812–14817. Bibcode:2004PNAS..10114812H. doi:10.1073/pnas.0406166101. ISSN 0027-8424. PMC 522015. PMID 15465915.
  63. ^ Brower, Andrew V.Z. (June 2006). "Problems with DNA barcodes for species delimitation: 'Ten species' of Astraptes fulgerator reassessed (Lepidoptera: Hesperiidae)". Systematics and Biodiversity. 4 (2): 127–132. doi:10.1017/S147720000500191X. ISSN 1477-2000. S2CID 54687052.
  64. ^ Smith, M. A.; Woodley, N. E.; Janzen, D. H.; Hallwachs, W.; Hebert, P. D. N. (2006-03-07). "DNA barcodes reveal cryptic host-specificity within the presumed polyphagous members of a genus of parasitoid flies (Diptera: Tachinidae)". Proceedings of the National Academy of Sciences. 103 (10): 3657–3662. doi:10.1073/pnas.0511318103. ISSN 0027-8424. PMC 1383497. PMID 16505365.
  65. ^ Brasier, Madeleine J.; Wiklund, Helena; Neal, Lenka; Jeffreys, Rachel; Linse, Katrin; Ruhl, Henry; Glover, Adrian G. (November 2016). "DNA barcoding uncovers cryptic diversity in 50% of deep-sea Antarctic polychaetes". Royal Society Open Science. 3 (11): 160432. Bibcode:2016RSOS....360432B. doi:10.1098/rsos.160432. ISSN 2054-5703. PMC 5180122. PMID 28018624.
  66. ^ Pompanon, Francois; Deagle, Bruce E.; Symondson, William O. C.; Brown, David S.; Jarman, Simon N.; Taberlet, Pierre (April 2012). "Who is eating what: diet assessment using next generation sequencing: NGS DIET ANALYSIS". Molecular Ecology. 21 (8): 1931–1950. doi:10.1111/j.1365-294X.2011.05403.x. PMID 22171763. S2CID 10013333.
  67. ^ Valentini, Alice; Pompanon, François; Taberlet, Pierre (February 2009). "DNA barcoding for ecologists". Trends in Ecology & Evolution. 24 (2): 110–117. doi:10.1016/j.tree.2008.09.011. PMID 19100655.
  68. ^ a b c Kaunisto, Kari M.; Roslin, Tomas; Sääksjärvi, Ilari E.; Vesterinen, Eero J. (October 2017). "Pellets of proof: First glimpse of the dietary composition of adult odonates as revealed by metabarcoding of feces". Ecology and Evolution. 7 (20): 8588–8598. doi:10.1002/ece3.3404. PMC 5648679. PMID 29075474.
  69. ^ Harms-Tuohy, Ca; Schizas, Nv; Appeldoorn, Rs (2016-10-25). "Use of DNA metabarcoding for stomach content analysis in the invasive lionfish Pterois volitans in Puerto Rico". Marine Ecology Progress Series. 558: 181–191. Bibcode:2016MEPS..558..181H. doi:10.3354/meps11738. ISSN 0171-8630.
  70. ^ Kowalczyk, Rafał; Taberlet, Pierre; Coissac, Eric; Valentini, Alice; Miquel, Christian; Kamiński, Tomasz; Wójcik, Jan M. (February 2011). "Influence of management practices on large herbivore diet—Case of European bison in Białowieża Primeval Forest (Poland)". Forest Ecology and Management. 261 (4): 821–828. doi:10.1016/j.foreco.2010.11.026.
  71. ^ Nichols, Ruth V.; Cromsigt, Joris P. G. M.; Spong, Göran (December 2015). "Using eDNA to experimentally test ungulate browsing preferences". SpringerPlus. 4 (1): 489. doi:10.1186/s40064-015-1285-z. ISSN 2193-1801. PMC 4565800. PMID 26380165.
  72. ^ Agusti, N.; Shayler, S. P.; Harwood, J. D.; Vaughan, I. P.; Sunderland, K. D.; Symondson, W. O. C. (December 2003). "Collembola as alternative prey sustaining spiders in arable ecosystems: prey detection within predators using molecular markers". Molecular Ecology. 12 (12): 3467–3475. doi:10.1046/j.1365-294X.2003.02014.x. ISSN 0962-1083. PMID 14629361. S2CID 7985256.
  73. ^ Valentini, Alice; Miquel, Christian; Nawaz, Muhammad Ali; Bellemain, Eva; Coissac, Eric; Pompanon, François; Gielly, Ludovic; Cruaud, Corinne; Nascetti, Giuseppe (January 2009). "New perspectives in diet analysis based on DNA barcoding and parallel pyrosequencing: the trn L approach". Molecular Ecology Resources. 9 (1): 51–60. doi:10.1111/j.1755-0998.2008.02352.x. PMID 21564566. S2CID 5308081.
  74. ^ Friedman, Melissa; Fernandez, Mercedes; Backer, Lorraine; Dickey, Robert; Bernstein, Jeffrey; Schrank, Kathleen; Kibler, Steven; Stephan, Wendy; Gribble, Matthew (2017-03-14). "An Updated Review of Ciguatera Fish Poisoning: Clinical, Epidemiological, Environmental, and Public Health Management". Marine Drugs. 15 (3): 72. doi:10.3390/md15030072. ISSN 1660-3397. PMC 5367029. PMID 28335428.
  75. ^ Khan, F. M.; William, K.; Aruge, S.; Janjua, S.; Shah, S. A. (2018-03-04). "Illegal product manufacturing and exportation from Pakistan: Revealing the factuality of highly processed wildlife skin samples via DNA mini-barcoding". Nucleosides, Nucleotides and Nucleic Acids. 37 (3): 179–185. doi:10.1080/15257770.2018.1450507. PMID 29608392. S2CID 4623232.
  76. ^ Mwale, Monica; Dalton, Desire L.; Jansen, Raymond; De Bruyn, Marli; Pietersen, Darren; Mokgokong, Prudent S.; Kotzé, Antoinette (March 2017). Steinke, Dirk (ed.). "Forensic application of DNA barcoding for identification of illegally traded African pangolin scales". Genome. 60 (3): 272–284. doi:10.1139/gen-2016-0144. hdl:1807/75671. ISSN 0831-2796. PMID 28177847. S2CID 207093202.
  77. ^ Liu, Yanlei; Xu, Chao; Dong, Wenpan; Yang, Xueying; Zhou, Shiliang (2021-07-01). "Determination of a criminal suspect using environmental plant DNA metabarcoding technology". Forensic Science International. 324: 110828. doi:10.1016/j.forsciint.2021.110828. ISSN 0379-0738. PMID 34000616. S2CID 234768561.
  78. ^ a b c d e f Pawlowski, Jan; Kelly-Quinn, Mary; Altermatt, Florian; Apothéloz-Perret-Gentil, Laure; Beja, Pedro; Boggero, Angela; Borja, Angel; Bouchez, Agnès; Cordier, Tristan (2018). "The future of biotic indices in the ecogenomic era: Integrating (e)DNA metabarcoding in biological assessment of aquatic ecosystems". Science of the Total Environment. 637–638: 1295–1310. Bibcode:2018ScTEn.637.1295P. doi:10.1016/j.scitotenv.2018.05.002. hdl:20.500.12327/138. PMID 29801222.
  79. ^ Armitage, Patrick D.; Cranston, Peter S.; Pinder, L. C. V., eds. (1995). The Chironomidae. Dordrecht: Springer Netherlands. doi:10.1007/978-94-011-0715-0. ISBN 9789401043083. S2CID 46138170.
  80. ^ Beermann, Arne J.; Zizka, Vera M. A.; Elbrecht, Vasco; Baranov, Viktor; Leese, Florian (2018-07-24). "DNA metabarcoding reveals the complex and hidden responses of chironomids to multiple stressors". Environmental Sciences Europe. 30 (1): 26. doi:10.1186/s12302-018-0157-x. ISSN 2190-4715. S2CID 51802465.
  81. ^ Beermann, Arne J.; Elbrecht, Vasco; Karnatz, Svenja; Ma, Li; Matthaei, Christoph D.; Piggott, Jeremy J.; Leese, Florian (2018). "Multiple-stressor effects on stream macroinvertebrate communities: A mesocosm experiment manipulating salinity, fine sediment and flow velocity". Science of the Total Environment. 610–611: 961–971. Bibcode:2018ScTEn.610..961B. doi:10.1016/j.scitotenv.2017.08.084. PMID 28830056.
  82. ^ Macher, Jan N.; Salis, Romana K.; Blakemore, Katie S.; Tollrian, Ralph; Matthaei, Christoph D.; Leese, Florian (2016). "Multiple-stressor effects on stream invertebrates: DNA barcoding reveals contrasting responses of cryptic mayfly species". Ecological Indicators. 61: 159–169. doi:10.1016/j.ecolind.2015.08.024.
  83. ^ "The International Barcode of Life Consortium". International Barcode of Life. Retrieved 2019-03-29.
  84. ^ "Bold Systems v4". www.boldsystems.org. Retrieved 2019-04-02.
  85. ^ a b Ogwang, Joel; Bariche, Michel; Bos, Arthur R. (2020). "Genetic Diversity and Phylogenetic Relationships of Threadfin Breams (Nemipterus spp.) from the Red Sea and eastern Mediterranean Sea". Genome. 63 (3): 207–216. doi:10.1139/gen-2019-0163. PMID 32678985.
  86. ^ Schander, Christoffer; Willassen, Endre (2005). "What can biological barcoding do for marine biology?". Marine Biology Research. 1 (1): 79–83. doi:10.1080/17451000510018962. ISSN 1745-1000. S2CID 84070971.
  87. ^ Miller, S. E. (2007-03-20). "DNA barcoding and the renaissance of taxonomy". Proceedings of the National Academy of Sciences. 104 (12): 4775–4776. Bibcode:2007PNAS..104.4775M. doi:10.1073/pnas.0700466104. ISSN 0027-8424. PMC 1829212. PMID 17363473.
  88. ^ Ratnasingham, S. (2013). "A DNA-based registry for all animal species: the Barcode Index Number (BIN) system". PLOS ONE. 8 (7): e66213. Bibcode:2013PLoSO...866213R. doi:10.1371/journal.pone.0066213. PMC 3704603. PMID 23861743.
  89. ^ Leese, Florian; Elbrecht, Vasco (2015-07-08). "Can DNA-Based Ecosystem Assessments Quantify Species Abundance? Testing Primer Bias and Biomass—Sequence Relationships with an Innovative Metabarcoding Protocol". PLOS ONE. 10 (7): e0130324. Bibcode:2015PLoSO..1030324E. doi:10.1371/journal.pone.0130324. ISSN 1932-6203. PMC 4496048. PMID 26154168.
  90. ^ Elbrecht, Vasco; Vamos, Ecaterina Edith; Meissner, Kristian; Aroviita, Jukka; Leese, Florian (2017). "Assessing strengths and weaknesses of DNA metabarcoding-based macroinvertebrate identification for routine stream monitoring". Methods in Ecology and Evolution. 8 (10): 1265–1275. doi:10.1111/2041-210X.12789. ISSN 2041-210X.
  91. ^ a b c Pawlowski, J.; Kelly-Quinn, M.; Altermatt, F.; Apothéloz-Perret-Gentil, L.; Beja, P.; Boggero, A.; Borja, A.; Bouchez, A.; Cordier, T.; Domaizon, I.; Feio, M. J.; Filipe, A. F.; Fornaroli, R.; Graf, W.; Herder, J.; Van Der Hoorn, B.; Iwan Jones, J.; Sagova-Mareckova, M.; Moritz, C.; Barquín, J.; Piggott, J. J.; Pinna, M.; Rimet, F.; Rinkevich, B.; Sousa-Santos, C.; Specchia, V.; Trobajo, R.; Vasselon, V.; Vitecek, S.; et al. (October 2018). "The future of biotic indices in the ecogenomic era: Integrating (E)DNA metabarcoding in biological assessment of aquatic ecosystems". Science of the Total Environment. 637–638: 1295–1310. Bibcode:2018ScTEn.637.1295P. doi:10.1016/j.scitotenv.2018.05.002. hdl:20.500.12327/138. PMID 29801222.
  92. ^ Quince, Christopher; Sloan, William T.; Hall, Neil; D'Amore, Rosalinda; Ijaz, Umer Z.; Schirmer, Melanie (2015-03-31). "Insight into biases and sequencing errors for amplicon sequencing with the Illumina MiSeq platform". Nucleic Acids Research. 43 (6): e37. doi:10.1093/nar/gku1341. ISSN 0305-1048. PMC 4381044. PMID 25586220.
  93. ^ Huang, Quanfei; Li, Jiguang; Fu, Ribei; Tang, Min; Zhou, Lili; Su, Xu; Yang, Qing; Liu, Shanlin; Li, Yiyuan (2013-12-01). "Ultra-deep sequencing enables high-fidelity recovery of biodiversity for bulk arthropod samples without PCR amplification". GigaScience. 2 (1): 4. doi:10.1186/2047-217X-2-4. PMC 3637469. PMID 23587339.
  94. ^ Macher, Jan-Niklas; Zizka, Vera Marie Alida; Weigand, Alexander Martin; Leese, Florian (2018). "A simple centrifugation protocol for metagenomic studies increases mitochondrial DNA yield by two orders of magnitude". Methods in Ecology and Evolution. 9 (4): 1070–1074. doi:10.1111/2041-210X.12937. ISSN 2041-210X.
  95. ^ "DNAquaNet". Retrieved 2019-03-29.
  96. ^ CEN (2018) CEN/TC 230/WORKING GROUP 2 – Proposal for a new Working Group WG28 “DNA and eDNA methods” A plan to fulfil the DNA and eDNA standardization needs of EU legislation in Water Policy (Proposal following decisions of the 2017 Berlin Meeting of CEN/TC 230, its Working Groups and eDNA COST representatives)
  97. ^ Sloan, William T.; Read, L. Fiona; Head, Ian M.; Neil Hall; Davenport, Russell J.; Curtis, Thomas P.; Lanzén, Anders; Quince, Christopher (2009). "Accurate determination of microbial diversity from 454 pyrosequencing data". Nature Methods. 6 (9): 639–641. doi:10.1038/nmeth.1361. hdl:1956/6529. ISSN 1548-7105. PMID 19668203. S2CID 1975660.
  98. ^ Kunin, Victor; Engelbrektson, Anna; Ochman, Howard; Hugenholtz, Philip (2010). "Wrinkles in the rare biosphere: pyrosequencing errors can lead to artificial inflation of diversity estimates". Environmental Microbiology. 12 (1): 118–123. doi:10.1111/j.1462-2920.2009.02051.x. ISSN 1462-2920. PMID 19725865. S2CID 19870165.
  99. ^ Rob Knight; Reeder, Jens (2009). "The 'rare biosphere': a reality check". Nature Methods. 6 (9): 636–637. doi:10.1038/nmeth0909-636. ISSN 1548-7105. PMID 19718016. S2CID 5278501.
  100. ^ Zhan, Aibin; Hulák, Martin; Sylvester, Francisco; Huang, Xiaoting; Adebayo, Abisola A.; Abbott, Cathryn L.; Adamowicz, Sarah J.; Heath, Daniel D.; Cristescu, Melania E. (2013). "High sensitivity of 454 pyrosequencing for detection of rare species in aquatic communities". Methods in Ecology and Evolution. 4 (6): 558–565. doi:10.1111/2041-210X.12037. hdl:11336/2674. ISSN 2041-210X. S2CID 53576369.
  101. ^ Zhan, Aibin; He, Song; Brown, Emily A.; Chain, Frédéric J. J.; Therriault, Thomas W.; Abbott, Cathryn L.; Heath, Daniel D.; Cristescu, Melania E.; MacIsaac, Hugh J. (2014). "Reproducibility of pyrosequencing data for biodiversity assessment in complex communities". Methods in Ecology and Evolution. 5 (9): 881–890. doi:10.1111/2041-210X.12230. ISSN 2041-210X.
  102. ^ Chua, Physilia Y. S.; Bourlat, Sarah J.; Ferguson, Cameron; Korlevic, Petra; Zhao, Leia; Ekrem, Torbjørn; Meier, Rudolf; Lawniczak, Mara K. N. (10 March 2023). "Future of DNA-based insect monitoring". Trends in Genetics. 39 (7): 531–544. doi:10.1016/j.tig.2023.02.012. PMID 36907721. S2CID 257470926.
  103. ^ Srivathsan, Amrita; Hartop, Emily; Puniamoorthy, Jayanthi; Lee, Wan Ting; Kutty, Sujatha Narayanan; Kurina, Olavi; Meier, Rudolf (December 2019). "Rapid, large-scale species discovery in hyperdiverse taxa using 1D MinION sequencing". BMC Biology. 17 (1): 96. doi:10.1186/s12915-019-0706-9. PMC 6884855. PMID 31783752.
  104. ^ Srivathsan, Amrita; Lee, Leshon; Katoh, Kazutaka; Hartop, Emily; Kutty, Sujatha Narayanan; Wong, Johnathan; Yeo, Darren; Meier, Rudolf (December 2021). "ONTbarcoder and MinION barcodes aid biodiversity discovery and identification by everyone, for everyone". BMC Biology. 19 (1): 217. doi:10.1186/s12915-021-01141-x. PMC 8479912. PMID 34587965.
  105. ^ Srivathsan, Amrita; Baloğlu, Bilgenur; Wang, Wendy; Tan, Wei X.; Bertrand, Denis; Ng, Amanda H. Q.; Boey, Esther J. H.; Koh, Jayce J. Y.; Nagarajan, Niranjan; Meier, Rudolf (September 2018). "A MinION™-based pipeline for fast and cost-effective DNA barcoding". Molecular Ecology Resources. 18 (5): 1035–1049. doi:10.1111/1755-0998.12890. PMID 29673082. S2CID 4982474.
  106. ^ Meier, Rudolf; Wong, Winghing; Srivathsan, Amrita; Foo, Maosheng (February 2016). "$1 DNA barcodes for reconstructing complex phenomes and finding rare species in specimen-rich samples". Cladistics. 32 (1): 100–110. doi:10.1111/cla.12115. PMID 34732017. S2CID 83862072.
  107. ^ Hebert, Paul D. N.; Braukmann, Thomas W. A.; Prosser, Sean W. J.; Ratnasingham, Sujeevan; deWaard, Jeremy R.; Ivanova, Natalia V.; Janzen, Daniel H.; Hallwachs, Winnie; Naik, Suresh; Sones, Jayme E.; Zakharov, Evgeny V. (27 March 2018). "A Sequel to Sanger: amplicon sequencing that scales". BMC Genomics. 19 (1): 219. doi:10.1186/s12864-018-4611-3. PMC 5870082. PMID 29580219.
  108. ^ Srivathsan, Amrita; Ang, Yuchen; Heraty, John M.; Hwang, Wei Song; Jusoh, Wan F.A.; Kutty, Sujatha Narayanan; Puniamoorthy, Jayanthi; Yeo, Darren; Roslin, Tomas; Meier, Rudolf (4 August 2022). "Global convergence of dominance and neglect in flying insect diversity". bioRxiv. doi:10.1101/2022.08.02.502512. S2CID 251369606.
  109. ^ Fernandez-Triana, Jose L. (25 February 2022). "Turbo taxonomy approaches: lessons from the past and recommendations for the future based on the experience with Braconidae (Hymenoptera) parasitoid wasps". ZooKeys (1087): 199–220. doi:10.3897/zookeys.1087.76720. PMC 8897373. PMID 35585942.
  110. ^ Baloğlu, Bilgenur; Clews, Esther; Meier, Rudolf (December 2018). "NGS barcoding reveals high resistance of a hyperdiverse chironomid (Diptera) swamp fauna against invasion from adjacent freshwater reservoirs". Frontiers in Zoology. 15 (1): 31. doi:10.1186/s12983-018-0276-7. PMC 6092845. PMID 30127839.
  111. ^ Yeo, Darren; Srivathsan, Amrita; Puniamoorthy, Jayanthi; Maosheng, Foo; Grootaert, Patrick; Chan, Lena; Guénard, Benoit; Damken, Claas; Wahab, Rodzay A.; Yuchen, Ang; Meier, Rudolf (14 September 2021). "Mangroves are an overlooked hotspot of insect diversity despite low plant diversity". BMC Biology. 19 (1): 202. doi:10.1186/s12915-021-01088-z. PMC 8442405. PMID 34521395.
  112. ^ Geiger, Matthias; Moriniere, Jerome; Hausmann, Axel; Haszprunar, Gerhard; Wägele, Wolfgang; Hebert, Paul; Rulik, Björn (1 December 2016). "Testing the Global Malaise Trap Program – How well does the current barcode reference library identify flying insects in Germany?". Biodiversity Data Journal. 4 (4): e10671. doi:10.3897/BDJ.4.e10671. PMC 5136679. PMID 27932930.
  113. ^ Hebert, Paul D. N.; Ratnasingham, Sujeevan; Zakharov, Evgeny V.; Telfer, Angela C.; Levesque-Beaudin, Valerie; Milton, Megan A.; Pedersen, Stephanie; Jannetta, Paul; deWaard, Jeremy R. (5 September 2016). "Counting animal species with DNA barcodes: Canadian insects". Philosophical Transactions of the Royal Society B: Biological Sciences. 371 (1702): 20150333. doi:10.1098/rstb.2015.0333. PMC 4971185. PMID 27481785.
  114. ^ Telfer, Angela; et al. (30 August 2015). "Biodiversity inventories in high gear: DNA barcoding facilitates a rapid biotic survey of a temperate nature reserve". Biodiversity Data Journal. 3 (3): e6313. doi:10.3897/BDJ.3.e6313. PMC 4568406. PMID 26379469.
  115. ^ D'Souza, Michelle L.; van der Bank, Michelle; Shongwe, Zandisile; Rattray, Ryan D.; Stewart, Ross; van Rooyen, Johandré; Govender, Danny; Hebert, Paul D.N. (April 2021). "Biodiversity baselines: Tracking insects in Kruger National Park with DNA barcodes". Biological Conservation. 256: 109034. doi:10.1016/j.biocon.2021.109034. hdl:2263/81603. S2CID 233489409.
  116. ^ Yeo, Darren; Puniamoorthy, Jayanthi; Ngiam, Robin Wen Jiang; Meier, Rudolf (October 2018). "Towards holomorphology in entomology: rapid and cost-effective adult-larva matching using NGS barcodes: Life-history stage matching with NGS barcodes". Systematic Entomology. 43 (4): 678–691. doi:10.1111/syen.12296. S2CID 49211569.
  117. ^ Pierre, Taberlet (2018-02-02). Environmental DNA : for biodiversity research and monitoring. Bonin, Aurelie, 1979-. Oxford. ISBN 9780191079993. OCLC 1021883023.{{cite book}}: CS1 maint: location missing publisher (link)
  118. ^ Ruppert, Krista M.; Kline, Richard J.; Rahman, Md Saydur (January 2019). "Past, present, and future perspectives of environmental DNA (eDNA) metabarcoding: A systematic review in methods, monitoring, and applications of global eDNA". Global Ecology and Conservation. 17: e00547. doi:10.1016/j.gecco.2019.e00547.
  119. ^ Stoeck, Thorsten; Frühe, Larissa; Forster, Dominik; Cordier, Tristan; Martins, Catarina I.M.; Pawlowski, Jan (February 2018). "Environmental DNA metabarcoding of benthic bacterial communities indicates the benthic footprint of salmon aquaculture". Marine Pollution Bulletin. 127: 139–149. doi:10.1016/j.marpolbul.2017.11.065. PMID 29475645.
  120. ^ Evans, Darren M.; Kitson, James J. N.; Lunt, David H.; Straw, Nigel A.; Pocock, Michael J. O. (2016). "Merging DNA metabarcoding and ecological network analysis to understand and build resilient terrestrial ecosystems" (PDF). Functional Ecology. 30 (12): 1904–1916. doi:10.1111/1365-2435.12659. ISSN 1365-2435.
  121. ^ Puddu, M.; Paunescu, D.; Stark, W.J.; Grass, R.N. (2014). "Magnetically Recoverable, Thermostable, Hydrophobic DNA/Silica Encapsulates and Their Application as Invisible Oil Tags". ACS Nano. 8 (3): 2677–2685. doi:10.1021/nn4063853. PMID 24568212.
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