Non-human DNA testing can investigate which organism contributed material, whether samples may share an individual source or how material relates to a population. These are different questions. A species barcode does not ordinarily identify one animal, tree or fungal individual.
The laboratory selects targets for the suspected material and the question, then evaluates the sequence against appropriate references. A high similarity score is useful information, but is not by itself a confidence percentage, a unique species assignment or proof of a legal offence.
Taxonomic identification is applied to plant and wildlife material in Botanical Evidence: An Overview and Wildlife Crime and Biological Evidence.
- Barcode
- A selected genetic region used for taxonomic comparison with appropriate references.
- Barcode Gap
- Separation of observed within- and between-taxon variation for a specified marker and dataset.
- Voucher
- An authenticated specimen associated with reference information.
- Metabarcoding
- Marker-based sequencing used to investigate multiple taxa in a sample.
- Introgression
- Transfer of genetic material between lineages through hybridisation and subsequent breeding.
Mitochondrial Targets and Their Limits
Mitochondrial targets can offer relatively high starting copy numbers in suitable animal specimens, helping some analyses of processed or degraded material. This advantage depends on cell type, preservation, target length and the assay. It does not mean that every somatic cell contains the same hundreds of mitochondria or that nuclear markers always fail first.
Animal mitochondrial sequence often varies usefully between taxa. However, mutation rates and within-species diversity differ, and a clear barcode gap is not guaranteed. Incomplete lineage sorting, hybridisation and introgression can make a mitochondrial lineage shared across named taxa.
In the usual animal inheritance model, mitochondrial markers mainly follow maternal history. A hybrid may carry the mitochondrial type of its maternal lineage while having mixed nuclear ancestry. Appropriate nuclear markers can therefore be needed for a hybrid or ancestry question.
Nuclear copies of mitochondrial sequences can also complicate amplification or interpretation in some taxa. Assay specificity, sequence quality and the biological context need assessment. A mitochondrial result must not be treated as a complete description of the organism’s ancestry or individual identity.
Choosing Animal, Plant and Fungal Markers
COI is widely used in animal barcoding, with a standard target of roughly 650 bases and shorter approaches for some compromised specimens. Cytochrome b is another useful animal mitochondrial target, especially in many vertebrate applications. Neither marker is universally superior or the only permissible choice.
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The rbcL/matK combination is an established core plant-barcode proposal, not a guarantee of species resolution in every land plant. ITS is a principal fungal barcode, while some groups need additional loci. Plants do have mitochondrial cytochrome genes; the reason for different barcode practice is not that those genes are categorically absent.
A broad-range primer pair may miss some taxa, amplify background or preferentially recover one component of a mixture. A short target can help recovery while losing diagnostic information. Choose and validate the marker for the intended scope rather than assume every published “universal” primer covers all possible evidence.
From Specimen to Interpretable Sequence
Record the item, condition and sampling location before destructive work. Tissue, hair, feather, bone, wood, plant powder and processed food have different extraction challenges. Appropriate controls and contamination prevention matter for non-human casework just as they do for human DNA.
Extraction aims to recover relevant targets and reduce inhibitors. Human-specific quantification does not measure all non-human DNA. A broad total-DNA result may include microbes or background, so its relevance depends on the assay. Non-human workflows do not all require the same quantification step.
Amplification and sequencing follow validated methods. Review raw data, primer regions, quality, possible mixtures and controls rather than accepting an automatically generated consensus. Bidirectional sequencing can improve assessment where appropriate, but a generic statement that every accreditation framework mandates the same sequencing direction is unwarranted.
Sanger sequencing can yield a dominant sequence or a mixed trace. An apparently clean sequence does not establish that no minor species was present, because amplification can be selective. If the question involves mixtures, choose a validated approach capable of answering it.
Record the sequence region and usable length, quality criteria, query method, reference identifiers and relevant alternatives. Preserve enough data and analysis settings to permit technical review. A named commercial kit must be described accurately rather than invented to make an example appear specific.
Reference Databases and Similarity Scores
BOLD provides barcode-oriented data and identification tools; GenBank provides broad sequence submissions and associated metadata. Their coverage, release and search options change. Some references have strong voucher and taxonomic support while others have limited information; neither resource is universally error-free.
Assess relevant reference identity, accession or record version, voucher provenance, sequence coverage and inclusion of close relatives. Two databases agreeing may reflect the same underlying record, not independent confirmation. A missing close taxon can make the top available hit misleading.
A 99-percent identity over a short fragment is not a 99-percent probability of species identity. The meaning depends on the marker, aligned length, within- and between-taxon variation and data quality. Conversely, one fixed cutoff does not automatically convert every lower score into a defensible genus assignment.
Where the region cannot separate relevant species, report the supported group or unresolved alternatives. Additional suitable markers, authenticated references or morphology may help. Querying both databases can be useful, but is not a universal sufficient or mandatory recipe replacing method validation.
Do not invent an accession, voucher or numeric search output in a teaching case. A real report should make its actual reference evidence traceable and explain limitations, including taxonomic change and geographic coverage.
Wildlife, Food and Plant Applications
Species testing can help investigate whether a seized biological product contains a regulated taxon or whether food contains an undeclared ingredient. The analytical question might be presence, taxonomic identity, hybrid status or individual association; sampling and method capability should match that question.
CITES regulates international trade in listed taxa through specified controls. Appendix, population, annotations, source, dates, permits and exemptions can all matter. A sequence assigned to a listed species does not alone establish that the transaction was illegal, and Appendix I is not an unqualified ban on every specimen in every circumstance.
For food mixtures, presence of DNA does not directly measure ingredient mass or prove deliberate substitution. Different tissues, processing and marker copy number can affect detection. Assess the sampling plan, validated detection limits, controls and the relevant labelling or regulatory question.
Plant and timber work can combine morphology, genetic and chemical methods. Species and geographical origin remain different questions. A Convention on Biological Diversity reference or generic wildlife statute does not itself resolve a particular timber-trade allegation.
US, UK, Indian, Canadian, Australian and other authorities have different implementing requirements. Legal assessment depends on the actual taxon, population, transaction and date. Species lists and population-specific exceptions can change, so an undated global count or blanket elephant listing is insufficient.
Mixtures, Individual Comparisons and Reporting
Mixtures can be examined through suitable species-specific assays, sequencing approaches, metabarcoding or other validated methods. Next-generation sequencing is not the only possible solution, and it does not guarantee a complete inventory. Primer bias, depth, contamination and references affect detection.
Metabarcoding read proportions are not automatically biomass or ingredient percentages. Low-level signals need interpretation against controls and the validated reporting threshold. Failure to detect a taxon does not prove absence below the method’s capability or outside the sampled portion.
Individual comparison within a species may use nuclear STRs, SNPs or other informative targets. Microsatellites are not the only possible method. The relevant population structure, relatedness, marker dependence and reference coverage affect statistical weight.
A species barcode, a population assignment and a same-individual comparison should be reported separately. A candidate geographic association can be limited by incomplete sampling; a taxonomic result can remain useful even where no individual probability can be calculated.
Explain the taxonomic resolution actually supported and the alternatives that remain. Analytical association is not a verdict about ownership, poaching, smuggling or intent. Those conclusions require the wider evidence and applicable legal assessment.
Check Your Understanding
Sources
- 1.Barcode of Life Data Systems · BOLD
- 2.GenBank Overview · NCBI
- 3.Conservation Genetics: Species and Individual Questions · US Fish and Wildlife Service
- 4.How CITES Works · CITES Secretariat
- 5.CITES Convention Text · CITES Secretariat