Identification of historical specimens and wildlife seizures originating from highly degraded sources of kangaroos and other macropods
- First Online:
- Cite this article as:
- Spencer, P.B.S., Schmidt, D. & Hummel, S. Forensic Sci Med Pathol (2010) 6: 225. doi:10.1007/s12024-009-9119-3
- 277 Views
Forensic investigations are an important area in the regulation of food mis-description, wildlife seizures and the international trade in wildlife and its products. An early, but important stage in dealing with many biological materials that are submitted for forensic scrutiny is species identification. We describe a method and new primers to amplify three small DNA fragments of the cytochrome b region of the mitochondrial DNA that are suitable for marsupial species identification from degraded sources, such as wildlife seizures. They were designed as consensus sequences from a comparison of 21 marsupial species. The primers also contained sequences intended specifically not to amplify human DNA, thereby reducing the likelihood of amplifying contaminants. Examples of the utility of these primers are given using a range of conditions that may be applied using such an approach, including (1) field-collected sub-fossil bones, (2) an example of museum mis-identification from a specimen collected in 1930 and (3) a skull collected from Bernier Island, in the harsh mid-west of Western Australia.
In Australia, forensic investigations are important in a range of wildlife areas including the regulation of fraudulent description of food products, wildlife seizures and the international trade in wildlife and its products . One such group, the kangaroos are internationally recognized iconic wildlife. The group belong to the superfamily Macropodoidea (or macropods), and contain about 45 living species in Australia . There is currently no specific method or comparative database to identify DNA from highly degraded sources of kangaroo species in Australia. Modern molecular techniques have enabled the extraction and sequencing of DNA from old or museum specimens such as bone, teeth, feathers or skin [3–6]. Access to this degraded DNA provides an invaluable resource for wildlife protection, systematics and conservation research over a large time scale. Museum specimen sequences have already proved crucial to a number of wildlife genetic studies e.g. [5, 7–9]. It is estimated that the world’s natural history museums hold in the order of 1.5 billion specimens  and these, from a genetic perspective, have hitherto been greatly under-utilised. It is also recognised that the world’s mammals are declining rapidly . The advantages of using museum specimens over fresh specimens are well recognised and include the possibility that fresh specimens may be costly to obtain due to the remoteness of habitat, the behaviour of the species or the fact that the species under investigation may exist in politically sensitive regions . Museum collections may also contain specimens from species which are now extinct [10, 12]. Use of museum specimens may therefore be both time and cost saving, and importantly, allow access to information which may no longer be obtainable from living systems.
In Australia there are an increasing number of studies that have utilised old museum specimens for marsupial research e.g. [13, 14] but there remains little general information about this potentially powerful application to marsupial fauna. Future marsupial research may need to rely to a greater extent on museum specimens due to Australia’s recognised small mammal decline, high extinction rates, habitat destruction and fragmentation  and difficulty in obtaining specimens . For example in the case of endangered species persisting in fragmented habitats, an understanding of the historical changes (using museum or sub-fossil material) is crucial for conservation.
An important consideration in analysing ancient DNA (aDNA) sources is that the material is often highly degraded. For repeatability, the amplification of the targeted sequence information should be from primers that give a PCR product as short as possible (preferably <200 bp ). We applied this approach to our sequencing of the cytochrome b (cyt b) region of the mitochondrial genome for three marsupial specimens. Cytochromeb is a well defined region with adequate variation to discriminate marsupial taxa e.g. [8, 16, 17] and has been very widely used, and commonly is amplified by ‘universal primers’ [18, 19] or in the identification of forensic samples [20, 21]. Technical difficulties inherent to the analysis of small quantities of DNA generally tend to limit the efficiency of this approach. Two of the limitations with using these universal primers for museum specimens (particularly marsupials) are that the fragments are generally too large for successful amplification when the DNA is highly degraded and by virtue of the fact that they are ‘universal’, they have not been designed specifically for the taxa under investigation and may amplify non-target DNA.
In order to answer questions on sample identification of marsupial museum specimens and those sourced from degraded samples, we designed a set of primers to amplify three relatively small amplicons of the cytochrome b gene in the marsupial mitochondrion. Using these primers, we demonstrated that it was possible to (1) obtain authentic amplicons from a range of macropod species, (2) obtain such DNA from different types of material (bone and teeth) and (3) identify and assign each specimen to a species.
Materials and methods
Samples and source material for degraded-source DNA analysis
Details of specimens, condition and DNA yield from marsupials
DNA conc (ng/μl)
DNA yield (ng/mg sample)
Bleached skull (partial) collected at Mt. Keith Station, W.A in 2001. No bones in vicinity of skull. Exposed for >6 months
Femur sampled from museum specimen labelled Notomys alexis
Suspect mis-labelled. Collected in 1930, Canning stock Route, W.A.
Partial bleached skull (crushed) collected from Bernier Island, W.A. in 1989
sub-fossil Euro (Macropus robustus). This sample was collected as a crushed skull, which included the complete set of upper molar teeth (Sample identification Gö01; Table 1). The partial bleached skull was collected in the field at Mt. Keith Station, Western Australia. No other bones were found in the vicinity of the skull, suggesting that it had been exposed for a considerable period of time, although we do not have an exact period of exposure. This specimen was intended to represent a ‘typical’ field sample, where the specimen was obviously in a poor state of preservation and has been exposed to extreme ambient temperatures (0–45°C; Meekathara weather station). Duplicate DNA extractions were performed on samples of bone and tooth material (i.e. a total of four extractions were carried out on this specimen). Each extract was carried out separately (details given in Table 1).
mis-labelled museum specimen (a “Notomys”). A single DNA extraction was carried out on a small section (0.34 g) of the femur from a museum specimen labelled “Notomys alexis”, collected in 1930 on the Canning Stock route (Western Australian Museum Accession No. M1461). We suspected that this specimen may have been mis-labelled, as the bone fragment was 92 mm long, only slightly shorter than the 95 mm head-body length of the spinifex hopping mouse it was supposedly from . The sample appeared to be well preserved and in good condition.
Rufous Hare-wallaby or Mala (Lagorchestes hirsutus). Two DNA extractions were performed from bone (0.45 g) and tooth (0.48 g) material of a partially bleached and crushed skull which included the molar teeth (WA museum accession No. M47274) collected from Bernier Island, Western Australia in 1989. The age of the sample was unknown, but it appeared old and weathered, having been exposed to extreme ambient temperatures and periods of high humidity for an unknown length of time, similar to that described in the first specimen.
Preparation of bone and tooth samples (from Hummel 2003)
The outer surface (~0.5 mm) of the bone and teeth samples were removed using a dentist grinding drill (Horico Diamond Instruments, Model EWL K10) to remove possible surface contaminants. A small section of each sample (~0.5 g) was cut out and then pulverised in a mixing mill (Retsch Type MM2). The sample was decalcified by mixing 0.5 g of the powdered bone with 1.0 ml of 0.5 M EDTA (pH 8.3) via constant rotation for 18–24 h at room temperature. Samples were then centrifuged for 5 min at 3,000 rpm to pellet any remaining hard material. The supernatant was used for DNA extraction in an automated nucleic acid extractor (Gene Pure 341; Applied Biosystems) beginning with a Proteinase K (39 U/mg; lyophilised, Applied Biosystems) digestion step at 56°C for 1 h, and then followed by a standard phenol and chloroform extraction.
At the final automated step, samples were mixed with 5 μl silica particle solution (Glassmilk™, QBiogene), resulting in the DNA binding to the glass milk in the presence of iso-propanol (3.3 ml of 100% solution) and sodium acetate (100 μl of 2.0 M NaAc; pH 4.5; Applied Biosystems). The mixture was gently mixed for 10 min, and the silica particles collected on a filtration membrane (Applied Biosystems). The filtration membranes containing the DNA/silica samples were manually removed from the automated extractor and washed with 80% ethanol then allowed to air dry. The eluted DNA/silica samples were re-suspended in 50 μl of sterile water (Ampuwa™, Fresenius).
The quantity and quality of the DNA extract was determined using a scanning photometer (Secomam, Jouan). In order to remove the silica particles prior to spectrophotometry, the extracts were vortexed and agitated at 56°C for 10 min, then centrifuged for 10 s at 5,000 rpm to pellet the glass milk. DNA extract was used to measure the absorbance from λ 200 to 400 nm with DNA quantity determined at 260 nm. The distribution of the curve generated could be used to determine the quality of the extract, following the approach of Hummel . The extracts were ranked as being low, medium or high quality extracts. Low quality had poor DNA yield and associated co-purification of extraneous material and high quality had high DNA yield with little co-purification of other material, such as proteins (Table 1).
Samples and source material for non-ancient DNA analysis
In the same laboratory as the ancient DNA extractions were performed, a control DNA extraction (from human cheek cells) was also carried out using a Chelex™ protocol . This ‘contamination control sample’ was used in each PCR to investigate that the PCR-primers were not targeting human DNA (the most likely source of contamination; see below).
In a separate laboratory, DNA was extracted from a blood sample from the 21 marsupial species used in primer design using a standard salting out procedure  for use as reference samples.
We trialled the commonly used ‘universal’ cytochrome b primers [18, 24] on a range of ancient DNA extracts (n = 7) following the procedures in Alacs et al. . The success of these trials was very low (see results section) and so to improve amplification, primers were specifically designed to amplify relatively small DNA products, suitable for highly degraded DNA sources .
All PCRs for the three new ‘ancient’ DNA primer pairs (for fragments Macytb1, 2 and 3; Table 2) were initially carried out in a multiplex PCR of a total volume of 50 μl with 1U of AmpliTaqGold™ DNA polymerase (Applied Biosystems), approximately 100 ng of template DNA (which included the silica suspension), 1.0 pmol of each primer, 200 μM dNTPs (solutions of dATP, dCTP, dGTP, dTTP; Sigma–Aldrich), 2 mM MgCl2, and 1× polymerase buffer II (100 mM Tris–HCl; pH 8.3, 500 mM KCl) supplied by the manufacturer. The reaction mix was overlayed with Mineral oil (Nujol™; Applied Biosystems), which helped to reduced aerosol contamination when opening tubes. After an initial 10 min denaturation step at 94°C, the reaction tubes were exposed to 45 cycles of the following protocol: 1 min at 94°C; 1 min at 50°C; 1 min at 72°C, with a final extension step of 30 min at 64°C. These products were resolved on a 4% agarose gel (Fig. 2). All PCR amplification procedures included a negative and a non-marsupial (human DNA) control.
In a separate laboratory, the reference L. hirsutus sequence was obtained by PCR amplification using the cytochrome b universal primer L14724 (5′ GAAGCTTGATGAAAAACCATCGTTG 3′ ) and the new reverse primer Macytb3R (Fig. 2), with a final product size of 662 bp.
The multiplex PCR products were sequenced directly using Taq cycle sequencing. This included a re-amplification reaction for each of the three products. The re-amplifications are carried out separately each using one primer of the respective primer pair as a sequencing primer. One microliter of the initial PCR was used as a template for the cycle sequencing using the Big-Dye terminator™ cycle sequencing chemistry (ABI PRISM, Applied Biosystems). The PCR conditions were: 30 s. 96°, 15 s. 50°C, 4 min. 60°C, 30 cycles.
The cycle sequencing products were electrophoresed using an automated DNA sequencer (model 310; ABI systems, Bethesda, Md.). Other reference sequences were obtained from GenBank (see Table 2), and these were from the complete mitochondrial sequences of the euroo (Macropus robustus ) and the eastern grey kangaroo (Macropus giganteus ). All sequences were edited and aligned by eye using SeqEd (Applied Biosystems, Perkin-Elmer).
Samples and DNA extractions
Amplifiable DNA was successfully obtained from each bone and tooth sample (Fig. 2), although the quantity of the DNA varied widely, both with repeated extractions of a single specimen and among different specimens (Table 1). In general, bone material gave significantly greater yields of DNA than did tooth material (F = 410; df = 1; P = 0.003).
PCR primers and sequencing success
‘Universal’ primer trials
PCR amplifications using the widely utilised ‘universal primers’ [18, 21, 24] were attempted for the seven ancient DNA extracts (each sample run twice) and the control samples (negative and human). Only two PCR (662 bp) products were obtained and these were sequenced. One derived from the human DNA control, and the other from one of the Gö01-1 samples, which aligned using the BLAST search (http://www4.ncbi.nlm.nih.gov/BLAST/) with Macropus robustus (GenBank accession # Y10524). Despite the relatively high DNA concentration (160 μg/μl, Table 1) the fact that only one amplification attempt (from repeated PCRs) of the Gö01-1 sample was successful suggests that very few larger intact fragments were present in the extract. This corresponds to the general experiences in ancient and degraded DNA analysis.
New ‘degraded’ DNA primer trials
All of the extracts were amplified using the three newly designed primer sets. Again this was carried out with duplicate PCRs and included the negative and the human controls. In contrast to the amplification attempts using the “universal primers” of Kocher et al.  the human control sample remained blank with the newly designed primer set. Also in the negative control amplification products were not detectable.
Size of sequenced product and similarity to the most closely aligned GenBank sequence of the three new primers for amplifying the cytochrome b region in three macropod samples (given in Table 1)
Y10524 (Macropus robustus)
AY099273 (Lagorchestes hirsutus)
AY099274 (Lagorchestes hirsutus)
For the second specimen (the mis-labelled museum specimen, Gö02-1), only the first (cytb1) and third (cytb3) fragments could be amplified, despite repeated (four) amplification attempts. Nonetheless, for these two successfully amplified fragments, with a total sequence length of 306 bp, the resulting sequences showed 100% sequence identity to the rufous hare-wallaby (Lagorchestes hirsutus) reference sequence.
The third specimen, a partial skull from the Rufous hare-wallaby (Lagorchestes hirsutus, samples Gö03-1and Gö03-2) yielded PCR fragments from each of the three amplified regions (total sequence length of 494 bp). However, due to an obviously stronger degree of DNA degradation the fragments were not always obtained simultaneously from each sample but at least the two larger fragments were only amplified randomly (Fig. 2). This phenomenon is commonly described as stochastic amplification. The analysis of the resultant sequences of a total length of 494 bp confirmed the specimen to be near-identical (99.98%) to the L. hirsutus reference sequence.
Although the extraction and amplification of degraded DNA is well known, it remains underutilized and described in only a few reports investigating marsupial remains e.g. [8, 13, 14]. In this study we set out to develop a marsupial-specific approach to the analysis of degraded DNA and have successfully amplified DNA from marsupials that had been preserved or found in a variety of different states of preservation. Specimen sources ranged from appropriately curated museum vouchers to material that had been found in the field. Being able to obtain DNA from a variety of sources are important because an enormous amount of marsupial material are accessible as sub-fossil specimens only, and many of the existing material derives from species that are now extinct.
We described the development and utilisation of a set of three primer pairs for the amplification of cytochrome b PCR fragments suitable for amplifying degraded DNA from marsupial samples. The new primer set offers a number of advantages to more conventional primers in the approach to ancient and degraded DNA. Firstly, the simultaneously amplified PCR fragments are relatively short (164, 188 and 202 bp), and are therefore like the characteristics of degraded DNA. Secondly, the simultaneous amplification of different fragments in a multiplex approach saves valuable sample materials. Thirdly, the use of primers where the focus was on species-specificity, avoids the amplification of potentially present contaminants. The experiments showed that only a few mismatches at the 3′ ends of the primers are sufficient to discriminate against human DNA which is the most probable contaminant in ancient DNA analysis from field and museum specimens.
The importance of degraded DNA sources for investigating conservation questions with Australian marsupials will increase as more species experience decline. There are already a number of macropods with high conservation importance. To illustrate the use of this technology, there are four species of hare-wallabies of which all but one (L. conspicillatus) are either extinct (L. leporides and L. asomatus) or endangered (L. hirsutus). In mainland Australia, populations of the mala (L. hirsutus) persisted in the Great Sandy and Gibson Deserts until the 1950s. By 1960 only two small colonies of mainland populations of the mala remained in the Tanami Desert (about 500 km north–west of Alice Springs). One colony became extinct in late 1987, destroyed by a single fox. The second colony was wiped out by wildfire in 1991. The mala is now classified as endangered, and has been extinct on mainland Australia for over a decade . The species now persists in a single fenced enclosure in central Australia, and on three offshore islands. It should now be possible to exploit the vast amounts of museum and sub-fossil material to investigate historical and conservation questions in these and many other macropod species. An analysis system that combines primers specific for marsupials, small target sizes, and a multiplex PCR amplification approach will clearly be in favour in future studies using marsupial degraded DNA.
Wildlife forensic investigations are important for enforcing legal areas such as ‘truth in labelling’ of food, wildlife seizures and in monitoring the international trade in wildlife and its products.
Species identification is an important area of interest in wildlife forensics cases.
We describe a method that amplifies three short DNA fragments of the cytochrome b region of the mitochondrial DNA in a number of marsupial species.
They were designed as consensus sequences from 21 marsupial species. The primers also contained sequence intended to exclude human DNA, reducing the chance of amplifying contaminants.
The methods described in this manuscript offer a mechanism to generate data that may help define the past distribution of marsupials and place those distribution patterns in some context to climate regimes based on geological or paleontological studies.
We are very grateful for the comments and improvements made to the original manuscript by the reviewers and editor. This study received financial support from the Australian Academy of Sciences, Department of Environment and Conservation and Murdoch University (SRF and Animal Research Institute).